Vol. 62—2008 - NorthEastern Weed Science Society

Vol. 62—2008 - NorthEastern Weed Science Society Vol. 62—2008 - NorthEastern Weed Science Society

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P R O C E E D I N G S N O R T H E A S T E R N W E E D S C I E N C E S O C I E T Y VOL 62 2008 VOLUME 62 ____________________________________ PROCEEDINGS NORTHEASTERN WEED SCIENCE SOCIETY January 7, 8, 9, and 10, 2008 Sheraton Society Hill Philadelphia, PA 37212_newss_proceedings_nk.indd 1 12/13/2007 9:22:59 AM

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VOL<br />

62<br />

2008<br />

VOLUME 62<br />

____________________________________<br />

PROCEEDINGS<br />

NORTHEASTERN<br />

WEED SCIENCE<br />

SOCIETY<br />

January 7, 8, 9, and 10, 2008<br />

Sheraton <strong>Society</strong> Hill<br />

Philadelphia, PA<br />

37212_newss_proceedings_nk.indd 1<br />

12/13/2007 9:22:59 AM


Meeting Location<br />

Sheraton <strong>Society</strong> Hill Hotel<br />

One Dock Street<br />

Philadelphia, PA 19106<br />

(215) 238-6000<br />

Website:<br />

www.sheraton.com/society/hill<br />

Site of 2009 NEWSS Meeting<br />

Renaissance Harborplace Hotel<br />

Baltimore, MD<br />

* The cover photo of fragrant water lily (Nymphaea odorata) was the winning<br />

picture from our 2007 NEWSS <strong>Weed</strong> Photo Contest. This photo was provided by<br />

our contest winner, Dr. Robert Richardson of North Carolina State University.<br />

37212_newss_proceedings_nk.indd 2<br />

12/13/2007 9:22:59 AM


Proceedings<br />

of the<br />

Sixty-second Annual Meeting<br />

of the<br />

Northeastern <strong>Weed</strong> <strong>Science</strong> <strong>Society</strong><br />

Gregory R. Armel, Editor<br />

University of Tennessee<br />

Knoxville


SUSTAINING MEMBERS<br />

Platinum Level<br />

Gold Level<br />

Silver Level<br />

AMVAC<br />

BAAR Scientific LLC<br />

Gowan Company<br />

K-I Chemical USA<br />

IR-4<br />

OHP<br />

PBI Gordon Corporation<br />

Bronze Level<br />

ACDS Research<br />

Fore-Shore <strong>Weed</strong> Control<br />

LABServices Inc.<br />

IR-4 Project<br />

Marbicon, Inc.<br />

Reality Research<br />

Valent USA Corp<br />

USGA<br />

<strong>Weed</strong>s, Inc.<br />

ii


NORTHEASTERN WEED SCIENCE SOCIETY<br />

Sheraton <strong>Society</strong> Hill Hotel<br />

Philadelphia, PA<br />

EXECUTIVE COMMITTEE<br />

OFFICERS<br />

President<br />

President-Elect<br />

Vice President<br />

R.J. Keese<br />

Syngenta Crop Protection<br />

985 Arrowhead Drive<br />

Carmel, IN 46033<br />

J.J. Baron<br />

IR-4 Project<br />

500 College Rd. East, 201 West<br />

Princeton, NJ 08540<br />

D.E. Yarborough<br />

The University of Maine<br />

5722 Deering Hall<br />

Orono, ME 04469<br />

Secretary/Treasurer C.M. Becker<br />

BAAR Scientific LLC<br />

P.O. Box 34<br />

Romulus, NY 14541<br />

Past President<br />

W. S. Curran<br />

The Pennsylvania State University<br />

Dept. Crop and Soil <strong>Science</strong>s<br />

423 ASI Building<br />

University Park, PA 16802<br />

iii


COMMITTEES<br />

Editor<br />

Legislative<br />

Public Relations<br />

Research & Education<br />

Coordinator<br />

G.R. Armel<br />

The University of Tennessee<br />

2431 Joe Johnson Drive<br />

252 Ellington Plant <strong>Science</strong>s Bldg.<br />

Knoxville, TN 37996<br />

D.L. Kunkel<br />

IR-4 Headquarters, Rutgers University<br />

500 College Road East, Suite 201W<br />

Princeton, NJ 08540<br />

D.D. Lingenfelter<br />

The Pennsylvania State University<br />

Dept Crop and Soil <strong>Science</strong>s<br />

116 ASI Building<br />

University Park, PA 16802<br />

K.E. Kalmowitz<br />

BASF Corporation<br />

26 Davis Drive<br />

Research Triangle Park, NC 27709<br />

Sustaining Membership D.R. Spak<br />

Bayer Environmental <strong>Science</strong><br />

113 Willow Ridge<br />

New Holland, PA 17557<br />

CAST Representative<br />

Graduate Student Rep.<br />

WSSA Representative<br />

R.D. Sweet<br />

Cornell University<br />

Dept. of Horticulture<br />

Ithaca, NY 14853<br />

M. Ryan<br />

The Pennsylvania State University<br />

Dept. of Crop and Soil <strong>Science</strong>s<br />

University Park, PA 16802<br />

A. DiTommaso<br />

Cornell University<br />

Dept. of Crop and Soil <strong>Science</strong>s<br />

903 Bradfield Hall<br />

Ithaca, NY 14853<br />

iv


SECTION CHAIRS<br />

Agronomy<br />

Chair: G. Armel<br />

Chair-elect: G. Jordan<br />

Conservation, Forestry<br />

and Industrial<br />

Chair: N. Cain<br />

Chair-elect: A. Gover<br />

Graduate Student Contest<br />

Ornamentals<br />

Chair: D. Yarborough<br />

Moderator: M. Ryan<br />

Moderator: M. Goddard<br />

Moderator: V. Kumar<br />

Chair: M. Marshal<br />

Chair-elect: R. Prostak<br />

Research Posters<br />

Chair: C. Palmer<br />

Chair-elect: C. Judge<br />

Turfgrass and Plant<br />

Growth Regulators<br />

Chair: M. Agnew<br />

Chair-elect: S. Hart<br />

Vegetables and Fruit<br />

Chair: R. Lins<br />

Chair-elect: R. Chandran<br />

<strong>Weed</strong> Biology and Ecology<br />

Chair: M. VanGessel<br />

Chair-elect: D. Mortensen<br />

Effect of Climate Change on <strong>Weed</strong>s<br />

PGR Turfgrass Symposium<br />

Moderator: J. Barron<br />

Moderator: M. Agnew<br />

v


TABLE OF CONTENTS<br />

RESEARCH POSTERS<br />

EFFECTS OF TRIKETONE HERBICIDES ON SEEDED PERENNIAL RYEGRASS AND<br />

KENTUCKY BLUEGRASS. J.B. Willis and S.D. Askew .................................................. 1<br />

PENNSYLVANIA GIANT HOGWEED ERADICATION PROGRAM UPDATE. M.A.<br />

Bravo, M. Polach, R. Grieneisen, J. Diesing ................................................................... 2<br />

WEED CONTROL UNDER PLASTIC WITH FALL DAZOMET SOIL FUMIGANT<br />

APPLICATION. B.A. Scott, M.J. VanGessel, and Q.R. Johnson..................................... 3<br />

ASSESSING THE POTENTIAL OF LAKE GASTON VOLUNTEERS TO CREATE<br />

MANAGEMENT-QUALITY INVASIVE PLANT MAPS. B.R. Lassiter, R.J. Richardson,<br />

G.G. Wilkerson, and M.C. Sturgill ................................................................................... 4<br />

PROFESSIONAL LAWN CARE PROGRAMS UTILIZING MESOTRIONE. M.J. Goddard<br />

and S.D. Askew, and R.J. Keese and J.R. James .......................................................... 5<br />

PALE SWALLOW-WORT ESTABLISHMENT AND SURVIVAL ACROSS FOUR<br />

DISTURBANCE REGIMES. K. M. Averill, A. DiTommaso, C.L. Mohler, L.R. Milbrath.... 6<br />

THE RESPONSE OF ACTIVELY GROWING ORNAMENTAL CROPS TO<br />

DIMETHENAMID-P AND MESOTRIONE. M.W. Marshall and B.H. Zandstra................. 7<br />

MECHANICAL WEED MANAGEMENT IN HIGH RESIDUE CONSERVATION TILLAGE<br />

SYSTEMS. R.T. Bates, R.S. Gallagher, and W.S. Curran .............................................. 8<br />

WEED CONTROL STRATEGIES FOR ORGANIC FORAGE PRODUCTION: A FOUR-<br />

YEAR SUMMARY. J.M. Jemison, Jr. and M. Kirby ......................................................... 9<br />

EFFICACY OF HAND-HELD "WET BLADE" HERBICIDE APPLICATIONS ON SWEET<br />

GUM, MAPLE, AND TULIP POPLAR. D.A. Little, A.R. Post, and J.C. Neal,<br />

C.A. Judge .................................................................................................................... 10<br />

RESPONSE OF PERENNIAL RYEGRASS AND TALL FESCUE TO BYSPYRIBAC-<br />

SODIUM HERBICIDE. S.E. Hart and P.E. McCullough ................................................ 11<br />

MESOTRIONE AND HEXAZINONE COMBINATIONS FOR WEED CONTROL IN WILD<br />

BLUEBERRIES. D.E. Yarborough and J. D'Appollonio................................................. 12<br />

CONVERTING COOL-SEASON ATHLETIC FIELDS TO PATRIOT BERMUDAGRASS<br />

USING CHEMICALS AND ROW PLANTING. T.L. Mittlesteadt, J.M. Goatley, S.D.<br />

Askew, and M. Sullenberger ......................................................................................... 14<br />

vi


ROUGHSTALK BLUEGRASS CONTROL IN CREEPING BENTGRASS FAIRWAYS<br />

WITH BISPYRIBAC-SODIUM AND SULFOSULFURON. P.E. McCullough<br />

and S.E. Hart................................................................................................................. 15<br />

BROCCOLI AND CAULIFLOWER RESPONSES TO POSTEMERGENCE<br />

APPLICATIONS OF VINEGAR FOR WEED MANAGEMENT. C. B. Coffman, J.<br />

Radhakrishnan, and J. R. Teasdale .............................................................................. 16<br />

ORGANIC WEED MANAGEMENT: WHAT THE FARMERS THINK. M. R. Ryan, D. A.<br />

Mortensen, D. O. Wilson, and P. R. Hepperly ............................................................... 17<br />

A SIX-YEAR COMPARISON OF PREEMERGENCE CRABGRASS CONTROL WITH<br />

PROFESSIONAL TURF HERBICIDES. J.L. Jester, J.B. Willis, and S.D. Askew.......... 18<br />

EVALUATION OF THE IMPACT OF AN ADVENTITIOUS HERBIVORE ON AN<br />

INVASIVE PLANT, YELLOW TOADFLAX, IN COLORADO USA. J.F. Egan, and R. E.<br />

Irwin............................................................................................................................... 19<br />

EVALUATION OF AT-SEEDING GRANULAR HERBICIDES IN KENTUCKY<br />

BLUEGRASS TURF. R.S. Chandran and R.J. Keese.................................................. 20<br />

DOES SOIL PH INFLUENCE SWALLOW-WORT DISTRIBUTION IN ITS CURRENT<br />

RANGE? L.C. Magidow, A. DiTommaso, Q.M. Ketterings, and L.R. Milbrath ............... 21<br />

WAVYLEAF BASKETGRASS IN MARYLAND – An EDRR in Progress. K.L. Kyde and<br />

B.H. Marose .................................................................................................................. 22<br />

GRADUATE STUDENT CONTEST<br />

EFFECTS OF BUCKWHEAT COVER CROP ON WINTER WHEAT ESTABLISHMENT,<br />

YIELD, AND WEED SUPPRESSION. V. Kumar, D.C. Brainard, R.R. Bellinder, and R.R.<br />

Hahn.............................................................................................................................. 23<br />

BUSHKILLER BIOLOGY AND RESPONSE TO HERBICIDES. A.M. West, R.J.<br />

Richardson, A.P. Gardner, and J. Matthews ................................................................. 24<br />

PHRAGMITES RESPONSE TO SELECTED HERBICIDES. S.L. True, R.J. Richardson,<br />

A.P. Gardner, and P.L. Hipkins ..................................................................................... 25<br />

LONGEVITY OF WEED CONTROL IN CONTAINERS WITH BAS 659H. R.P.M.<br />

Atwood, L.C. Walker, J.C. Neal, C.A. Judge ................................................................. 26<br />

vii


CARDAMINE WEED SPECIES IN UNITED STATES NURSERIES. A.R. Post, J.C.<br />

Neal, A. Krings, B.R. Sosinski, and Q. Xiang ................................................................ 27<br />

AMICARBAZONE AND FLUCARBAZONE FOR WEED CONTROL IN TURFGRASS.<br />

M.J. Goddard, T.L. Mittlesteadt, and S.D. Askew, and L.D. Houseworth ...................... 28<br />

EFFECTS OF TOPDRESSING COLOR ON ESTABLISHMENT OF SPRIGGED<br />

PATRIOT BERMUDAGRASS. T.L. Mittlesteadt, J.L. Jester, and S.D. Askew .............. 29<br />

SPRAY ADJUVANTS INFLUENCE BISPYRIBAC-SODIUM EFFICACY FOR ANNUAL<br />

BLUEGRASS CONTROL IN COOL-SEASON TURFGRASS. P.E. McCullough and S.E.<br />

Hart ............................................................................................................................... 30<br />

PLANT GROWTH REGULATOR AND NITROGEN AFFECT SEASONAL<br />

CARBOHYDRATE PARTITIONING IN CREEPING BENTGRASS. D. Sarkar, P. C.<br />

Bhowmik, M. DaCosta................................................................................................... 31<br />

INFLUENCE OF BISPYRIBAC-SODIUM ON BROWN PATCH SEVERITY. A.I. Putman<br />

and J.E. Kaminski ......................................................................................................... 32<br />

THE POTENTIAL USE OF VINEGAR AS A BANDED APPLICATION, DIRECTED AT<br />

THE BASE OF TRANSPLANTED PEPPERS AND BRUSSEL SPROUTS. G.J. Evans<br />

and R.R. Bellinder ......................................................................................................... 33<br />

TOLERANCE OF BUTTERNUT SQUASH TO PREEMERGENCE AND<br />

POSTEMERGENCE APPLICATIONS OF HALOSULFURON-METHYL. .<br />

M. J.VanGessel, Q. R. Johnson, B. A. Scott, and H. P. Wilson..................................... 34<br />

THE INFLUENCE OF SMALL-SCALE ENVIRONMENTAL FACTORS ON SUCCESS<br />

OF JAPANESE STILTGRASS. A.N. Nord and D.A. Mortensen.................................... 35<br />

ROLLING RYE FOR WEED SUPPRESSION IN NO-TILL SOYBEANS. R. Mick, W.S.<br />

Curran, and S. Duiker.................................................................................................... 36<br />

MANIPULATION OF SOIL NITROGEN LEVELS AND ITS EFFECTS ON WEED VIGOR<br />

AND FECUNDITY. S.E. Whitehouse, A. DiTommaso, and C.L. Mohler........................ 37<br />

ORGANIC AND CONVENTIONAL WEED MANAGEMENT EFFICACY AND STABILITY<br />

IN A LONG-TERM CROPPING SYSTEM TRIAL. M.R. Ryan, D.A. Mortensen, W.S.<br />

Curran, R. Seidel, P.R. Hepperly, and J.R. Teasdale ................................................... 38<br />

WEEDS, ETHANOL, AND DISAPPEARING BEES; TALES OF LANDSCAPE<br />

BIODIVERSITY. N.B. DeBarros .................................................................................... 39<br />

viii


AGRONOMY I<br />

IS IT TIME TO RELINQUISH ATRAZINE IN CORN? W.S. Curran............................... 40<br />

LOOKING FOR POSTEMERGENCE SOLUTIONS TO TRIAZINE RESISTANCE<br />

WEEDS IN POTATOES. J.M. Jemison, Jr., P. Sexton, and L. Titus............................. 41<br />

ALS- AND ACCASE-RESISTANT ITALIAN RYEGRASS IN WESTERN NORTH<br />

CAROLINA. J.B. Beam and A.C. York .......................................................................... 42<br />

HALEX GT: NEW POSTEMERGENCE HERBICIDE FOR GLYPHOSATE<br />

TOLERANT CORN. G.D. Vail and C.M. Moseley ......................................................... 43<br />

HALEX GT WEED CONTROL IN GLYPHOSATE TOLERANT CORN. R.D. Lins, B.R.<br />

Miller, B.D. Black........................................................................................................... 44<br />

FALL BURNDOWN: DOES IT HAVE A FIT IN DELAWARE. M.J. VanGessel, Q.R.<br />

Johnson, and B.A. Scott................................................................................................ 45<br />

ORNAMENTALS I<br />

IR-4 AND ORNAMENTAL HORTICULTURE IN THE NORTHEAST. E. L. Lurvey ....... 46<br />

COMPETITION FROM BLACK COTTONWOOD IN NURSERY CONTAINERS. J.E.<br />

Altland ........................................................................................................................... 47<br />

EFFICACY AND PERSISTANCE OF GROWTH REGULATORS APPLIED TO<br />

ROOTED CUTTINGS OF TWO CULTIVARS OF RHODODENDRON BEFORE<br />

POTTING. S. Barolli ...................................................................................................... 48<br />

DIMETHENAMID-P: A NEW ACTIVE INGREDIENT FOR PREEMERGENCE WEED<br />

CONTROL IN PRODUCTION ORNAMENTALS. C.A. Judge, K.M. Kalmowitz, and J.<br />

Zawierucha.................................................................................................................... 49<br />

EFFICACY OF DIMETHENAMID-P + PENDIMETHALIN GRANULAR COMBINATIONS<br />

IN CONTAINERS. J.C. Neal ......................................................................................... 50<br />

ix


TURFGRASS AND PLANT GROWTH REGULATORS I<br />

ANNUAL BLUEGRASS CONTROL AND CREEPING BENTGRASS QUALITY AND<br />

COLOR IN FAIRWAY HEIGHT TURF AS INFLUENCED BY PLANT GROWTH<br />

REGULATOR PROGRAMS WITH BISPYRIBAC-SODIUM. S. J. McDonald................ 51<br />

EARLY POST-EMERGENT CONTROL OF SMOOTH CRABGRASS AND BULL<br />

PASPALUM WITH TANK-MIXES OF VARIOUS HERBICIDES. S.J. McDonald........... 52<br />

TOLERANCE OF SEEDLING BLUE GRAMMA AND LITTLE BLUESTEM TO<br />

POSTEMERGENCE HERBICIDES. J.L. Jester and S.D. Askew.................................. 53<br />

POSTEMERGENCE SMOOTH CRABGRASS AND WHITE CLOVER CONTROL WITH<br />

MESOTRIONE. P.H. Dernoeden and J. Fu................................................................... 54<br />

YELLOW NUTSEDGE CONTROL IN COOL-SEASON TURF. S.E. Hart, C. Mansue,<br />

and P.E. McCullough..................................................................................................... 55<br />

PREEMERGENCE YELLOW NUTSEDGE CONTROL IN SPRING SEEDED TALL<br />

FESCUE. P.H. Dernoeden and J. Fu ............................................................................ 57<br />

WEED BIOLOGY AND ECOLOGY<br />

A PRELIMINARY STUDY OF THE NON-NATIVE VASCULAR FLORA, R. Stalter, A.<br />

Jung, E. Youssef, J. Jelovic .......................................................................................... 58<br />

DEPLETING THE GERMINABLE WEED SEEDBANK WITH SOIL DISTURBANCE<br />

AND COVER CROPPING PRACTICES. S.B. Mirsky, E.R. Gallandt, D.A. Mortensen,<br />

W.S. Curran, and D.L. Shumway .................................................................................. 62<br />

HERBICIDE EFFECTIVENESS ON GIANT HOGWEED FOR PENNSYLVANIA<br />

ERADICATION PROGRAM. M.A. Bravo....................................................................... 63<br />

FIRST YEAR AFTER TREATMENT RESULTS: PILOT KUDZU ERADICATION<br />

PROGRAM IN PENNSYLVANIA. M.A. Bravo and P. Broady ....................................... 64<br />

BIOLOGY OF DODDER: A NOXIOUS WEED. P.C. Bhowmik and D. Sarkar............... 65<br />

RISKY ENERGY: BIOFUELS AND INVASIVE SPECIES. J. Barney and J. DiTomaso 66<br />

x


CONSERVATION, FORESTRY, AND INDUSTRIAL<br />

ACTIVITY REPORT FOR THE MASSACHUSETTS INVASIVE PLANT ADVISORY<br />

GROUP AND THE MASSACHUSETTS PROHIBITED PLANT LIST. R.G. Prostak, A.R.<br />

Bonanno, and B. Mitchell .............................................................................................. 67<br />

VEGETABLES AND FRUITS I<br />

SQUASH RESPONSE TO FOMESAFEN, HALOSULFURON, METOLACHLOR, AND<br />

TERBACIL APPLIED AT PLANTING. J.B. Beam, R.B. Batts, and W.E. Mitchem ....... 69<br />

POTENTIAL HERBICIDE PROGRAMS FOR SNAP BEANS. D.D. Lingenfelter, and M.J.<br />

VanGessel..................................................................................................................... 70<br />

EXPLORING THE POTENTIAL USE OF PREFIX IN MULTIPLE VEGETABLE<br />

CROPS. R.R. Bellinder and C.A. Benedict.................................................................... 71<br />

ANNUAL GRASS CONTROL IN SWEET CORN. D.H. Johnson and D.D. Lingenfelter,<br />

M.J. VanGessel, Q.R. Johnson, and B.A. Scott ............................................................ 72<br />

FLUMIOXAZIN USE AT PLANTING IN MATTED ROW STRAWBERRIES. S.D. Guiser<br />

and K. Demachak.......................................................................................................... 73<br />

PERENNIAL WEED CONTROL AND CROP TOLERANCE WITH MESOTRIONE AND<br />

TOPRAMEZONE IN CRANBERRIES. H.A. Sandler and K.M. Ghantous ..................... 75<br />

AGRONOMY II<br />

HERBICIDE-RESISTANT WEEDS IN THE UNITED STATES AND THEIR IMPACT ON<br />

EXTENSION. M.J. VanGessel and B.A. Scott .............................................................. 76<br />

ITALIAN RYEGRASS CONTROL IN WHEAT. R.L. Ritter and H. Menbere .................. 77<br />

NEW POSTEMERGENCE WEED CONTROL OPTIONS FOR USE IN CORN. H.<br />

Menbere and R.L. Ritter ................................................................................................ 78<br />

ANNUAL GRASS BURNDOWN IN CORN WITH HPPD INHIBITORS. R.R. Hahn and<br />

P.J. Stachowski............................................................................................................. 79<br />

xi


NEW POSTEMERGENCE WEED CONTROL OPTIONS FOR USE IN CORN. H.<br />

Menbere and R.L. Ritter ................................................................................................ 78<br />

ANNUAL GRASS BURNDOWN IN CORN WITH HPPD INHIBITORS. R.R. Hahn and<br />

P.J. Stachowski............................................................................................................. 79<br />

ORNAMENTALS II<br />

PREEMERGENCE CONTROL OF DOVEWEED IN NURSERY CROPS. J.F. Derr, and<br />

J.C. Neal .......................................................................................................................80<br />

TOLERANCE OF FRASER FIR TO HERBICIDES APPLIED BEFORE AND AFTER<br />

BUD BREAK. J. F. Ahrens and T. L. Mervosh .............................................................. 81<br />

TOLERANCES OF CONTAINER-GROWN ORNAMENTALS TO EXPERIMENTAL AND<br />

REGISTERED HERBICIDES. T. L. Mervosh and J. F. Ahrens .................................... 82<br />

SHOWCASE EFFICACY AND SAFETY IN CONTAINER GROWN NURSERY<br />

CROPS. D. A. Little and J. C. Neal ............................................................................... 83<br />

UPDATE ON 2007 WEED SCIENCE RESEARCH IN THE IR-4 ORNAMENTAL<br />

HORTICULTURE PROGRAM. C.L. Palmer, J. Baron, and E. Vea............................... 84<br />

TURFGRASS AND PLANT GROWTH REGULATORS II<br />

EFFECTS OF DITHIOPYR AND TRICLOPYR ON ANTICHROMATIC EFFECTS OF<br />

MESOTRIONE ON TURFGRASS AND SELECTED WEEDS. J.B. Willis, M.J. Goddard,<br />

and S.D. Askew............................................................................................................. 85<br />

BROADLEAF WEED CONTROL WITH FLUROXYPYR IN COOL-SEASON<br />

TURFGRASS. C. Mansue and S.E. Hart ...................................................................... 86<br />

TENACITY: A NEW HERBICIDE FOR TURFGRASS MANAGERS. R. J. Keese, J.<br />

Driver and D. Cox.......................................................................................................... 87<br />

PREEMERGENCE ANNUAL BLUEGRASS CONTROL. J.A. Borger<br />

and M.B. Naedel ........................................................................................................... 88<br />

PREEMERGENCE SMOOTH CRABGRASS CONTROL. M.B. Naedel<br />

and J.A. Borger ............................................................................................................. 89<br />

xii


PRE- AND EARLY-POSTEMERGENT CONTROL OF FALSE GREEN KYLLINGA IN<br />

SOUTHERN NEW ENGLAND. J.E. Kaminski............................................................... 90<br />

POSTEMERGENT CONTROL OF FALSE GREEN KYLLINGA IN SOUTHERN NEW<br />

ENGLAND. J.E. Kaminski ............................................................................................. 91<br />

USE OF MESOTRIONE HERBICIDE FOR ANNUAL BLUEGRASS CONTROL AT<br />

COOL-SEASON TURFGRASS ESTABLISHMENT. S.E. Hart, P.E. McCullough, and C.<br />

Mansue ......................................................................................................................... 92<br />

CRABGRASS CONTROL INFLUENCED BY GROWTH STAGE AND BROADLEAF<br />

WEED HERBICIDES. P.E. McCullough and S.E. Hart.................................................. 93<br />

VEGETABLES AND FRUIT II<br />

IR-4 IN THE NORTHEAST. E. L. Lurvey....................................................................... 94<br />

IR-4 PROJECT: UPDATE ON HERBICIDE REGISTRATION (FOOD USES).<br />

F.P. Salzman, D.L. Kunkel, and J.J. Baron. .................................................................. 95<br />

THE USE OF MESOTRIONE FOR WEED CONTROL IN MINOR CROPS. D. Lycan, V.<br />

Lengkeek, and G. Vail................................................................................................... 96<br />

THE ADVANTAGES TO USING THE GRANULAR FORMULATION OF FLUMIOXAZIN<br />

IN TOMATOES, POTATOES, AND SWEET POTATOES. B.A. Majek ........................ 97<br />

SNAP BEAN RESPONSE TO POSTEMERGENCE APPLICATIONS OF<br />

ACIFLUORFEN, BENTAZON, AND FOMESAFEN. R. B. Batts, R.W. Wallace, and A.K.<br />

Petty.............................................................................................................................. 98<br />

SYMPOSIUM: THE LATEST IN PLANT GROWTH REGULATORS FOR<br />

TURGRASS USE<br />

GROWTH REGULATORS AND TURFGRASSES---A HISTORICAL PERSPECTIVE.<br />

T.L. Watschke ............................................................................................................... 99<br />

FREQUENTLY ASKED QUESTIONS WITH PLANT GROWTH REGULATORS. D.P.<br />

Shepard....................................................................................................................... 100<br />

xiii


ANTHRACNOSE DISEASE MANAGEMENT WITH PLANT GROWTH REGULATORS.<br />

J.C. Inguagiato, J.A. Murphy, and B.B. Clarke ............................................................ 101<br />

ETIOLATED TILLER SYMPTOMS OF TURFGRASS AND PLANT GROWTH<br />

REGULATORS. M.A. Fidanza .................................................................................... 102<br />

USING PLANT GROWTH REGULATORS FOR ANNUAL BLUEGRASS REMOVAL. J.<br />

A. Borger and M. B. Naedel ........................................................................................ 103<br />

USE OF PLANT GROWTH REGULATORS ON SPORTS TURF. S.D. Askew .......... 104<br />

USING PLANT GROWTH REGULATORS ON GOLF COURSES IN THE MID-<br />

ATLANTIC REGION. S.J. Zontek................................................................................ 105<br />

REPORTS, AWARDS, MEMBERSHIP DIRECTORY, HERBICIDE LISTS,<br />

AND INDICES<br />

NEWSS EXECUTIVE COMMITTEE FINAL REPORT ................................................ 106<br />

NEWSS FINANCIAL STATEMENT FOR 2007 ........................................................... 116<br />

NEWSS PAST PRESIDENTS..................................................................................... 117<br />

AWARD OF MERIT..................................................................................................... 118<br />

DISTINGUISHED MEMBERS ..................................................................................... 120<br />

OUTSTANDING RESEARCHER AWARD .................................................................. 121<br />

OUTSTANDING EDUCATOR AWARD....................................................................... 121<br />

OUTSTANDING GRADUATE STUDENT PAPER CONTEST .................................... 122<br />

COLLEGIATE WEED CONTEST WINNERS .............................................................. 125<br />

RESEARCH POSTER AWARDS................................................................................ 129<br />

INNOVATOR OF THE YEAR ...................................................................................... 133<br />

OUTSTANDING APPLIED RESEARCH IN FOOD AND FEED CROPS..................... 133<br />

OUTSTANDING APPLIED RESEARCH IN TURF, ORNAMENTALS,........................ 133<br />

xiv


HERBICIDE NAMES: COMMON, TRADE, AND CHEMICAL .................................... 155<br />

COMMON PRE-PACKAGED HERBICIDES ............................................................... 173<br />

EXPERIMENTAL HERBICIDES.................................................................................. 178<br />

PLANT GROWTH REGULATORS.............................................................................. 178<br />

COMMON AND CHEMICAL NAMES OF HERBICIDE MODIFIERS........................... 179<br />

AUTHOR’S INDEX...................................................................................................... 180<br />

MAIN SUBJECT INDEX .............................................................................................. 182<br />

xv


xvi


EFFECTS OF TRIKETONE HERBICIDES ON SEEDED PERENNIAL RYEGRASS AND<br />

KENTUCKY BLUEGRASS. J.B. Willis and S.D. Askew, Virginia Tech, Blacksburg.<br />

ABSTRACT<br />

Initial screenings of topramezone and tembotrione revealed turfgrass tolerance<br />

and weed control comparable to mesotrione (Tenacity). Mesotrione will be the first<br />

HPPD inhibitor registered for use in turf and offers both preemergent and postemergent<br />

broad-spectrum weed control and weed control options during establishment of coolseason<br />

turfgrass. Our objectives are to determine the usefulness of topramezone and<br />

tembotrione during establishment of cool-season turfgrass. Three trials were conducted<br />

in Blacksburg, VA to evaluate rates and sequential treatments of topramezone and<br />

tembotrione during establishment of Kentucky bluegrass (Poa pratensis L.) (KBG) and<br />

perennial ryegrass (Lolium perenne) (PR). Two trials were seeded September 6, 2007<br />

with PR and KBG at the Glade Road Research Facility and one trial was strip seeded<br />

with PR and KBG on October 11, 2007 at the Turfgrass Research Center. Trials at the<br />

Glade Road Research Facility were mown three times per week at 0.6 inches and the<br />

trial at the Turfgrass Research Center was mown once per week at 2.5 inches.<br />

Treatments were topramezone at 0.016 and 0.05 lb ai/A, tembotrione at 0.12 and 0.37<br />

lb ai/A, mesotrione at 0.25 lb ai/A, quinclorac at 0.56 lb ai/A, and siduron at 6 lb ai/A<br />

each applied at seeding and at seeding with a 4 week after emergence sequential<br />

treatment. <strong>Weed</strong> control, turfgrass injury and color were all evaluated over the course<br />

of the trials. Topramezone and tembotrione when applied at seeding of Kentucky<br />

bluegrass did not cause turf injury. These herbicides controlled smooth crabgrass<br />

(Digitaria ischaemum), dandelion (Taraxacum officinale), henbit (Lamium amplexicaule),<br />

chickweed (Stellaria media), and broadleaf plantain (Plantago major). Mesotrione and<br />

tembotrione both injured perennial ryegrass when applied at seeding while<br />

topramezone, siduron, and quinclorac injured PR less than 20%. Only topramezone<br />

reduced establishment of PR by reducing turf cover 30%. Sequential treatments of<br />

quinclorac, mesotrione, tembotrione, and topramezone discolored Kentucky bluegrass<br />

as much as 26, 76, 83, and 29%, respectively and perennial ryegrass as much as 19,<br />

75, 89, and 55%, respectively depending on rate. Injury by these postemergence<br />

treatments was transient, occurring 4 days after treatment and lasting an additional 3<br />

weeks. Previous trials with these herbicides applied to mature turfgrass have rarely<br />

resulted in turfgrass injury in excess of 30%. Although more studies are needed,<br />

tembotrione and topramezone appear to be suited for use in cool-season turfgrass in<br />

ways similar to that of mesotrione.<br />

1


PENNSYLVANIA GIANT HOGWEED ERADICATION PROGRAM UPDATE. M.A.<br />

Bravo, M. Polach, R. Grieneisen, Pennsylvania Department Agriculture, Harrisburg and<br />

J. Diesing, USDA-APHIS, Carlisle.<br />

ABSTRACT<br />

Pennsylvania (PA) discovered its first wild population of giant hogweed<br />

(Heracleum mantegazzianum) (GH) in 1985 in Erie County, two years after the federal<br />

government (USDA) declared the plant a noxious weed. Undoubtedly GH was in<br />

Pennsylvania a number of years prior to the initial detection, but only in the last 20 years<br />

have wild populations been reported to officials. Currently, 16 states (WA, OR, WI, IL,<br />

IN, MI, OH, PA, MD, NJ, NY, CT, MA, NH, VT, ME) have confirmed finding giant<br />

hogweed. Giant hogweed seems especially well adapted to -20 to -10ºF or Plant<br />

Hardiness Zones 5 (USDA Plant Hardiness Zone MAP) with a few locations in Zone 6<br />

and Zone 7(MD, D.C).<br />

A joint effort between the PA Department of Agriculture (PDA) and the USDA in<br />

1998 established the Giant Hogweed Eradication Program. Pennsylvania's success has<br />

resulted from continued support (personnel and funding) from USDA-APHIS and PDA’s<br />

ability to utilize existing regional staff to launch the eradication program via the toll free<br />

hotline and Giant Hogweed Coordinator position. By 2005, Pennsylvania’s outreach<br />

efforts had identified more than 500 populations in 15 counties and helped identify<br />

previously undiscovered populations in neighboring northeastern Ohio. The number of<br />

new sites peaked in 2003 and has steadily dropped in subsequent years and the<br />

number of controlled sites has increased indicating the outreach and treatments have<br />

been successful at eradicating wild populations of giant hogweed. This has allowed<br />

Pennsylvania (USDA and PDA) to shift the work load of the Giant Hogweed Coordinator<br />

to 3 seasonal technicians working out of the Western area of the state. Outlying sites in<br />

other areas of the state are controlled by the Harrisburg office or staff at regional offices.<br />

All known sites of GH are visited during the growing season and viable plants are<br />

treated either with a 2.5% or a 5.0% v/v triclopyr aqueous based or THINVERT based<br />

solution. In previous years, fluroxypyr was added to the mixture. At the end of 2007,<br />

fluroxypyr was replaced with aminopyralid at a rate of 0.45% v/v after field plot<br />

comparisons showed significant root injury for plants treated with aminopyralid.<br />

Approximately 160 of 524 sites in 12 of 17 counties were viable in 2007. An effort to<br />

identify sites to be released indicates that more than 150 sites are no longer viable and<br />

can be released from the Pennsylvania program. Pennsylvania continues to assist<br />

neighboring states with training, data standardization and program outreach.<br />

2


WEED CONTROL UNDER PLASTIC WITH FALL DAZOMET SOIL FUMIGANT<br />

APPLICATION. B.A. Scott, M.J. VanGessel, and Q.R. Johnson, University of Delaware,<br />

Georgetown.<br />

ABSTRACT<br />

Dazomet is a soil fumigant used to control weeds, fungi, and nematodes. It has<br />

been used in turf, ornamentals, field nurseries including Christmas trees, and in<br />

strawberry and tomato production. Expanding the use of dazomet in vegetable<br />

production settings with the use of plasticulture needs to be investigated. In 2006, a<br />

field trial was initiated in Georgetown, DE. The objective was to determine the efficacy<br />

of fall dazomet application for weed control under plastic laid in the fall versus the<br />

standard practice of herbicide application and plastic mulch laid in the spring.<br />

Trial area was chisel plowed, disked and field cultivated in October 2006.<br />

dazomet (400 lbs/A) was applied with a drop spreader and incorporated. Dazomet<br />

treatments differed by incorporation methods. Dazomet was incorporated immediately<br />

with a roto-tiller (to a 6-inch depth) prior to bedding and laying plastic; no roto-till, but<br />

incorporated within 30 minutes by bedding procedure and laying plastic; or roto-tilled<br />

then water-sealed over a five day period with overhead irrigation. Water sealed<br />

treatments were bedded and plastic mulch laid in the spring. Comparison treatments<br />

included Sandea (0.67 oz wt/A) applied in the spring one day prior to bedding and<br />

laying plastic and no weed control under plastic mulch. All treatments involving laying<br />

plastic mulch in the spring were roto-tilled 5 inches deep to facilitate bedding. All plots<br />

had drip irrigation laid under the plastic mulch. ‘Millionaire’ seedless watermelons and<br />

pollinators were transplanted on May 10, 2007. Plots were 40 foot long, top of beds<br />

were 30 inches wide and each was on 8 foot centers. <strong>Weed</strong> control in row middles was<br />

treated the same for all plots. This study was arranged as a randomized complete block<br />

with five replications.<br />

At 7 weeks after transplanting (WATRP), dazomet with plastic mulch laid in the<br />

fall provided the most consistent weed control. <strong>Weed</strong> control evaluation showed poor<br />

large crabgrass (Digitaria sanguinalis) and common purslane (Portulaca oleracea)<br />

control in the spring plastic treatments. Common lambsquarter (Chenopodium album),<br />

pigweed species (Amaranthus spp.), and yellow nutsedge (Cyperus esculentus) control<br />

was reduced in the dazomet spring plastic treatment as compared to the two fall<br />

dazomet treatments and Sandea under plastic.<br />

At the end of each plot, one square foot sections of plastic were cut and removed<br />

at 3 WATRP to expose soil and allow for weed growth. At 9 WATRP, weed counts<br />

taken from the 1 ft 2 sections showed dazomet treatments with plastic laid in the fall<br />

provided the most consistent control.<br />

Watermelon yield in the dazomet, roto-tilled, with plastic mulch laid in the fall was<br />

significantly greater (>60%) than with Sandea under plastic, dazomet no roto-till with<br />

plastic in the fall, and the untreated check. Yield in the dazomet, plastic in the spring<br />

did not differ from any other treatment.<br />

Fall dazomet followed by roto-tilling and plastic provided the most consistent<br />

results across all the parameters. For the initial year, roto-tilling, plastic mulch in the fall<br />

improved the effectiveness of dazomet for weed control, watermelon health, and yield.<br />

3


ASSESSING THE POTENTIAL OF LAKE GASTON VOLUNTEERS TO CREATE<br />

MANAGEMENT-QUALITY INVASIVE PLANT MAPS. B.R. Lassiter, R.J. Richardson,<br />

G.G. Wilkerson, and M.C. Sturgill, North Carolina State University, Raleigh, NC.<br />

ABSTRACT<br />

Lake Gaston is a 20,000 acre multiple-use reservoir residing in both North<br />

Carolina and Virginia. This body of water has been infested in recent years with Hydrilla<br />

(Hydrilla verticillata), Egeria (Egeria densa), Eurasian watermilfoil (Myriophyllum<br />

spicatum), brittle naiad (Najas minor), and Lyngbya species. Approximately 3,000 acres<br />

of hydrilla were present in 2007 with smaller acreages of the other species. Yearly<br />

surveys of aquatic plant distributions are a key factor in the determination of specific<br />

management plans. A project was initiated in 2007 to determine the feasibility of<br />

equipping, training, and supporting a volunteer group to survey aquatic vegetation. An<br />

initial training session covered identification of approximately 8 key species and basic<br />

scouting and mapping techniques. GPS and PDA units were purchased and provided<br />

for distribution to the volunteers. <strong>Vol</strong>unteers selected a specific region of the lake to<br />

focus individual efforts and reported results to a central database. This database will be<br />

used for the generation of distribution maps for initial comparison to maps generated by<br />

a professional contractor. Effectiveness of this volunteer effort will be evaluated and<br />

implications for other management areas will be discussed.<br />

4


PROFESSIONAL LAWN CARE PROGRAMS UTILIZING MESOTRIONE. M.J. Goddard<br />

and S.D. Askew, Virginia Tech, Blacksburg and R.J. Keese and J.R. James, Syngenta<br />

Professional Products, Greensboro, NC.<br />

ABSTRACT<br />

Mesotrione is a triketone herbicide soon to be registered for use in turfgrass<br />

under the trade name Tenacity (Syngenta Professional Products). Tenacity will be<br />

a product offering control of many annual and perennial broadleaved and grassy weeds.<br />

Mesotrione can be applied as a pre or a post-emergence herbicide. This quality will<br />

serve as a major benefit to lawn care operators and their approach to weed control in<br />

cool season turfgrass. Two trials were initiated on lawn height Kentucky bluegrass (Poa<br />

pratensis) in 2007 at Virginia Tech's Turfgrass Research Center in Blacksburg, VA.<br />

These trials included 8 treatment options which combined and/or compared the use of<br />

mesotrione and standard preemergence and postemergence herbicides to provide<br />

broad-spectrum weed control through the growing season. A randomized complete<br />

block experimental design with 4 replications was used. Treatments were applied on<br />

April 3 (pre), May 15 (early post), July 1 (post), and September 1 (post). Treatments<br />

included 4 combinations of a granular formulation of mesotrione plus prodiamine<br />

followed by 3 applications of granular mesotrione at varying rates, a granular dithiopyr<br />

formulation followed by 3 applications of Trimec ® Herbicide (PBI Gordon Corp.) on a 22-<br />

0-4 fertilizer carrier, a 22-0-4 fertilizer applied with a foliar broadcast of liquid dithiopyr<br />

(Dimension ® 2EW, Dow Agro<strong>Science</strong>s LLC) followed by 2 applications of a 22-0-4<br />

fertilizer applied with foliar broadcast application of Triplet ® Sensitive Herbicide (Nufarm<br />

Turf & Specialty), 4 applications of a 22-0-4 fertilizer applied alone at 42.6 kg/ha<br />

throughout the season, and an untreated check. All of the treatments combining<br />

mesotrione with preemergence herbicides controlled smooth crabgrass (Digitaria<br />

ischaemum) and dandelion (Taraxacum officinale) 90 to 100% throughout the growing<br />

season. Treatments containing regular fertilizer applications alone increased turf quality<br />

and reduced weed pressure by 50% over the untreated check. Overall turfgrass quality<br />

was significantly greater in treated plots than in untreated plots. Mesotrione proved to<br />

be an effective addition to a lawn care operator’s management program providing an<br />

option for preeemergence and postemergence control of broadleaved and grassy<br />

weeds.<br />

5


PALE SWALLOW-WORT ESTABLISHMENT AND SURVIVAL ACROSS FOUR<br />

DISTURBANCE REGIMES. K. M. Averill, A. DiTommaso, C.L. Mohler, Cornell<br />

University, Ithaca, NY; and L.R. Milbrath USDA-ARS, Ithaca, NY.<br />

ABSTRACT<br />

Pale swallow-wort [Cynanchum rossicum (Kleopow) Borhidi] is an increasingly<br />

problematic invasive perennial vine in the northeastern U.S. and southeastern Canada.<br />

Currently, sufficient biological data on this herbaceous species is lacking. Such data<br />

are necessary for further development of a biological control program, already<br />

underway for this species. In November 2006, we planted pale swallow-wort seeds in<br />

old fields subjected to four disturbance regimes at two sites in central New York State.<br />

We hypothesized that emergence would be greater in treatments with greater<br />

disturbance. The treatments were: (1) an initial glyphosate (3.0 kg a.e. ha-1) and<br />

dicamba (1.9 kg a.e. ha-1) application followed by roto-tillage to 15 cm depth, (2) an<br />

initial glyphosate and dicamba application, (3) mowing to approximately 20 cm once per<br />

year, and (4) an undisturbed control. Here we present emergence and survival results<br />

from 2007. A concurrent seed stratification and germination trial for seeds collected at<br />

the same time and location as field-planted seeds was conducted under controlled<br />

conditions and resulted in 87 ± 4 % germination. Seedling emergence was lower under<br />

field conditions. At the Mount Pleasant (MTP) field site, total emergence in the following<br />

growing season was 18 ± 1 % and did not differ between treatments. At the Hanshaw<br />

(HS) field site, emergence varied by treatment (P < 0.001). At HS, mowed plots (21 ± 3<br />

%) had greater total seedling emergence than all other treatment plots: glyphosate +<br />

tilled (4 ± 1 %), glyphosate (7 ± 2 %), and control (11 ± 2 %). Control plots had greater<br />

emergence than glyphosate + tilled plots. At MTP, May seedling emergence (as a<br />

percentage of total seedling emergence) was greater in the glyphosate + tillage (61 ± 5<br />

%) and glyphosate (52 ± 11 %) treatment plots than in the control (5 ± 3 %) and mowed<br />

(4 ± 3 %) treatment plots (P < 0.001). At MTP, June seedling emergence did not vary<br />

between treatment plots, but in early July, control (33 ± 10 %) plots had greater<br />

emergence than the more closed glyphosate + tilled (4 ± 2 %) and glyphosate (3 ± 1 %)<br />

plots (P = 0.01). Thus, emergence was delayed in control plots relative to the more<br />

open glyphosate and glyphosate + tilled plots. At HS, seedling emergence was not<br />

affected by treatment in any of the months. At both sites, seedling emergence declined<br />

after the first large flush. Most mortality occurred within the first three weeks after<br />

emergence at both sites and in all treatments. At both sites, survival to September of<br />

May- and June-emerging seedling cohorts was not affected by treatment. At MTP,<br />

which is at a greater elevation and is better drained than HS, the May cohort survival<br />

was 73 ± 7 % and the June cohort had 88 ± 3 % survival. At HS, the May cohort<br />

survival was 40 ± 7 % and the June cohort had 43 ± 9 % survival. These first-year<br />

results indicate that pale swallow-wort emergence and survival varies depending on the<br />

site and extent of disturbance. Here, elevation and soil drainage appeared to be factors<br />

contributing to the variations in pale swallow-wort emergence and survival between<br />

sites.<br />

6


THE RESPONSE OF ACTIVELY GROWING ORNAMENTAL CROPS TO<br />

DIMETHENAMID-P AND MESOTRIONE. M.W. Marshall and B.H. Zandstra, Michigan<br />

State University, East Lansing.<br />

ABSTRACT<br />

Field studies were conducted in 2007 to evaluate tolerance of field grown<br />

ornamentals to various rates of dimethenamid-P and mesotrione. Treatments included<br />

dimethenamid-P at 1.09, 2.17, and 4.35 kg/ha and mesotrione at 0.21, 0.28, and 0.41<br />

kg/ha. An untreated control was included for comparison. Field grown ornamental<br />

species included burning bush (Euonymus alatus ‘Compactus’), azalea (Azalea<br />

‘Cannon’s Double’), boxwood, daylily (Hemerocallis ‘Evelyn Claar’), coral bells<br />

(Heuchera micrantha ‘Palace Purple’), hosta (Hosta fortunei 'Gold Standard'), and<br />

Shasta daisy (Leucanthemum x superbum 'Snowcap'). Dimethenamid-P was applied<br />

on May 30, 2007 and July 11, 2007 and mesotrione was applied on May 30, 2007.<br />

Experimental design was a randomized complete block design with 3 replications.<br />

Individual plot dimensions were 1.8 by 10.6 m. Plant injury ratings were evaluated 7<br />

and 28 days after treatment (DAT) on a 0 to 9 scale with 0 indicating no injury and 9<br />

equal to crop death. Herbicides were applied in water over-the-top of actively growing<br />

ornamentals at a carrier volume of 187 L/ha with a pressure of 207 KPa. Burning bush<br />

injury was less than 2.5 at 28 DAT, across the dimethenamid-P rates. However,<br />

significant burning bush, azalea, daylily, coral bell, hosta, and Shasta daisy injury was<br />

noted with the 0.37 lb/A rate of mesotrione (3.0 to 4.0). The 0.21 and 0.28 kg/ha rate of<br />

mesotrione was generally safe on burning bush, boxwood, azalea, daylily, coral bell,<br />

hosta, and Shasta daisy, regardless of timing. Boxwood injury from mesotrione<br />

appeared as white chlorosis at the leaf tips followed by leaf drop. Burning bush, azalea,<br />

boxwood, daylily, coral bell, hosta, and Shasta daisy were fairly tolerant of<br />

dimethenamid-P (2.17 kg/ha or lower rate) [less than 2.3]. The response of the<br />

ornamental species examined to postemergence applications of dimethenamid-P in<br />

order of the least sensitive was burning bush = boxwood = coral bell > azalea > hosta ><br />

daylily > Shasta daisy. Mesotrione response in order of most sensitive was Shasta<br />

daisy = daylily > coral bell > azalea > burning bush > hosta. Overall, woody and<br />

herbaceous ornamentals appeared to be tolerant of the low- and mid-range rate of<br />

dimethenamid-P and mesotrione. More testing is needed to ensure safety on other<br />

species and varieties of ornamental crops.<br />

7


MECHANICAL WEED MANAGEMENT IN HIGH RESIDUE CONSERVATION TILLAGE<br />

SYSTEMS. R.T. Bates, R.S. Gallagher, and W.S. Curran, Penn State University,<br />

University Park.<br />

ABSTRACT<br />

Various conservation tillage corn (Zea mays L.) and soybean [Glycine max (L.)<br />

Merr.] systems have been widely adopted by agricultural producers. These systems<br />

have reduced soil erosion, but have relied heavily on herbicides for weed control.<br />

Increase dependence on pesticides is leading to herbicide resistance in weeds and<br />

raises the potential for off site impacts. Integrated weed management can reduce<br />

negative effects of herbicides, while maintaining more realistic levels of weed control.<br />

The objective of our study is to evaluate surface tillage implements for their<br />

incorporation into an integrated weed management plan in high residue direct-seeded<br />

corn and soybean systems. Eight individual treatments have been created to evaluate a<br />

vertical coulter implement, a rotary harrow, a high residue rotary hoe, and a high<br />

residue row cultivator with pre-plant broadcast, pre-plant band, and post emerge<br />

herbicide applications incorporated into treatments. Results from our preliminary<br />

research shows a combination of the vertical coulter, a rotary harrow, and three timed<br />

passes of a rotary hoe or one pass of the high residue row cultivator can obtain similar<br />

weed control to the herbicide dependent corn system. We believe that this research will<br />

demonstrate that a combination of mechanical weed control while maintaining sufficient<br />

plant residue and herbicides can provide effective weed control while reducing the<br />

number of applications or the application area of herbicides. Crop residue levels will<br />

also illustrate the impact that the mechanical weed control implements have on soil<br />

erosion potential. The results from this research will help both organic farmers who<br />

desire to reduce tillage associated with weed management and conventional reduced<br />

tillage farmers who desire to use less herbicide.<br />

8


WEED CONTROL STRATEGIES FOR ORGANIC FORAGE PRODUCTION: A FOUR-<br />

YEAR SUMMARY. J.M. Jemison, Jr. and M. Kirby, University of Maine Cooperative<br />

Extension, Orono.<br />

ABSTRACT<br />

In much of New England, demand for organic milk exceeds supply. Water quality<br />

implications for increasing the number of organic dairies include reduced: 1) pesticide<br />

loss to surface and ground waters of the region; 2) nutrient loss to water resources due<br />

to slower nutrient release; and 3) soil loss from fields with continuous cropping.<br />

However, producing quality forage with minimal weed pressure remains the greatest<br />

challenge for organic dairy producers. Growers need information on effective crop<br />

rotations and cultivation methods to maximize forage yield and quality. The University of<br />

Maine Cooperative Extension initiated an experiment in 2004 to evaluate alternative<br />

cropping system strategies that might better balance crop emergence, growth, and time<br />

to canopy closure compared to organic silage corn. Our interest was to: 1) quantify<br />

yield, quality, and weed pressure of winter and spring small grains and brown midrib<br />

sorghum sudan grass (BMRSS) double crops compared to intensively cultivated organic<br />

silage corn; and 2) determine if narrow crop row spacing would more effectively control<br />

weeds compared to intensively cultivated organic corn. Corn was cultivated twice with a<br />

tine cultivator and twice with a row cultivator. No weed control was used in the small<br />

grain double crops. Small grains evaluated in at least three years of the study included<br />

spring barley, spring wheat, winter barley, winter wheat, and winter triticale. Comparing<br />

three of four production seasons, triticale and BMRSS provided equivalent yield to<br />

silage corn (10,830 vs. 10,504 lbs dry matter/acre). The winter wheat BMRSS double<br />

crop produced lower but substantial yield (9650 lbs DM/ac). <strong>Weed</strong> biomass was three<br />

times higher on a percentage of total yield over the four year period. Surviving weeds<br />

in the double crop system produce fewer weed seeds, improving the potential for longterm<br />

cropping system success. The greatest difference between the systems is forage<br />

energy. Corn silage consistently produced higher forage energy than any double crop<br />

system.<br />

9


EFFICACY OF HAND-HELD "WET BLADE" HERBICIDE APPLICATIONS ON SWEET<br />

GUM, MAPLE, AND TULIP POPLAR. D.A. Little, A.R. Post, and J.C. Neal, Department<br />

of Horticultural <strong>Science</strong>, North Carolina State University, Raleigh and C. A. Judge,<br />

BASF Corporation, Research Triangle Park, NC.<br />

ABSTRACT<br />

The control of herbaceous vegetation using hand-held wet-blade techniques has<br />

been shown to be effective. In 2005 and 2006, field studies were initiated in Goldsboro,<br />

N.C. to evaluate the efficiency of wet-blade applications on deciduous tree species. In<br />

April 2005, one year-old sweet gum (Liquidambar styraciflua), red maple (Acer rubrum),<br />

and tulip poplar (Liriodendron tulipifera) were transplanted in individual rows according<br />

to species. In November 2005, applications of triclopyr 3SC (50, 25, 10, 5, or 1% v/v),<br />

glyphosate 4SC (50, 25, 10, 5, or 1% v/v), or imazapyr 2AS (10, 5, 2.5, 1, or 0.5% v/v)<br />

were applied to individual stems of each species. Treatments were applied by applying<br />

5 ml of treatment solution to the cutting surface of lopping shears and each stem was<br />

cut about 10 cm above the ground. Plots were arranged in a randomized complete<br />

block design with four replications with one stem from each species making a plot. In<br />

November 2006, the study was repeated on new stems that were one year older than<br />

those treated in 2005. Regrowth heights were measured 10 months after treatments. A<br />

year by treatment interaction occurred for red maple and sweet gum but not for tulip<br />

poplar. In the 2005 study, triclopyr (50% v/v), glyphosate (50% v/v), and all rates of<br />

imazapyr suppressed regrowth in red maple. However, in the 2006 study, no treatment<br />

controlled red maple regrowth. Imazapyr (10, 5, 2.5, and 1% v/v) and triclopyr (50 and<br />

25%) suppressed regrowth of sweet gum in the 2005 study, but suppression in the 2006<br />

study was only observed with 5% and 10% imazapyr. Tulip poplar suppression was<br />

achieved using imazapyr (10, 5, 2.5, and 1% v/v) and glyphosate (50 and 10% v/v).<br />

Imazapyr (10 and 5% v/v) provided the most consistent suppression. These data<br />

demonstrate that tree age and or size will impact the efficacy of wet-blade applied<br />

herbicides.<br />

10


RESPONSE OF PERENNIAL RYEGRASS AND TALL FESCUE TO BYSPYRIBAC-<br />

SODIUM HERBICIDE. S.E. Hart and P.E. McCullough, Rutgers, The State University of<br />

New Jersey, New Brunswick.<br />

ABSTRACT<br />

Field studies were conducted in the summer of 2006 and 2007 to evaluate the<br />

response of tall fescue 'Avenger', and perennial ryegrass ‘Gator 3’ to bispyribac-sodium<br />

herbicide. Annual bluegrass control was also evaluated. In 2007, fine fescue<br />

‘Ambassodor’ was also included. Sequential applications of bispyribac-sodium were<br />

applied at rates ranging from 37 g ai/ha to 296 g/ha at approximately a three week<br />

interval. Experiments were initiated on May 30 and May 31 in 2006 and 2007,<br />

respectively. All treatments were applied using a single nozzle CO 2 pressured sprayer<br />

calibrated to deliver a total of 375 L/ha. Nozzles used were 9504E and CO 2 regulators<br />

were set for 220 kPa. Experimental design was a randomized complete block with four<br />

replications. Turfgrass chlorosis was rated on a percent scale where 0 equaled no<br />

chlorosis and 100 equaled complete desiccation. Annual bluegrass (Poa annua) cover<br />

was evaluated prior to herbicide application and 10 weeks after initial treatment (WAIT).<br />

In 2006, bispyribac-sodium caused some chlorosis to tall fescue and perennial<br />

ryegrass; however injury did not exceed 20%. The highest levels of chlorosis were<br />

observed 10 days following the sequential application of bispyribac-sodium at 222 and<br />

296 g/ha. All bispyribac-sodium treatments provide substantial control of annual<br />

bluegrass but rates exceeding 74 g/ha were required to obtain nearly complete control,<br />

especially in perennial ryegrass. In 2007, tall fescue and perennial ryegrass injury did<br />

not exceed 5% at any evaluation time. Fine fescue was not injured by bispyribacsodium.<br />

By 6 WAIT, annual bluegrass control was only 24, 65, and 78% in tall fescue<br />

when bispyribac-sodium was applied at 74, 148, and 222 g/ha, respectively. However,<br />

296 g/ha provided nearly complete control. Control levels in perennial ryegrass tended<br />

to be greater but rates above 74 g/ha were required to achieve 80% or greater control.<br />

11


MESOTRIONE AND HEXAZINONE COMBINATIONS FOR WEED CONTROL IN WILD<br />

BLUEBERRIES. D.E. Yarborough and J. D'Appollonio, Univ. of Maine, Orono.<br />

ABSTRACT<br />

Hexazinone has been the standard herbicide used on Maine wild blueberry<br />

(Vaccinium angustifolium) fields for over twenty years and shifts in weed populations<br />

have resulted in a lack of control of many weeds. A study to evaluate the effects of the<br />

herbicide mesotrione with and without hexazinone was initiated in 2006 and continued<br />

in 2007 with harvest of the 2006 blocks, and the addition of six split design blocks on six<br />

wild blueberry fields across Maine in order to account for soil type and weed species<br />

diversity. Blocks were established in the townships of Union, Northport, Orland,<br />

Penobscot, T19, and the Blueberry Hill Experimental Farm in Jonesboro. Each block<br />

measured 22 x 29 m and was comprised of four 7 x 22 m mesotrione treatments<br />

including 437 mL/ha pre-emergence; 217 mL/ha pre-emergence and post-emergence;<br />

217 mL/ha post-emergence application; and none (untreated control). At right angles to<br />

the mesotrione treatments, 1.1 kg/ha hexazinone was applied pre-emergence to half of<br />

each block. In 2007 pre-emergence treatments were applied on May 9 to 11, and postemergent<br />

treatments were applied on June 14 and 15. Blueberry and weed cover, as<br />

well as blueberry phytotoxicity, were assessed June 27 to July 9 and on August 17 to<br />

21. Treatment effects were assessed for blueberry, broadleaf weeds, grasses and ferns<br />

using a Daubenmire cover scale, and for phytotoxicity as percent injury. Broadleaf<br />

weed cover was highest in the untreated control treatment for both evaluations<br />

(Figure1). Mesotrione at 217 mL/ac post-emergence combined with hexazinone<br />

suppressed broadleaf weeds more so than other treatments at the June evaluation, but<br />

by the August evaluation broadleaf weed cover was not significantly different from any<br />

other herbicide treatment. Although amounts of broadleaf weed cover were not<br />

statistically different for either evaluation, the combination of hexazinone and<br />

mesotrione and/or pre- and post-emergence applications tended to suppress broadleaf<br />

weeds more effectively than a single herbicide or application. Grass cover was highest<br />

in the untreated control and the mesotrione 437 mL/ha pre-emergence treatment at the<br />

June evaluation, while at the August evaluation the mesotrione 217 mL/ac pre- and<br />

post-emergence treatment had the highest grass cover (Figure 2). Grass cover in the<br />

mesotrione 217 mL/ac pre-and post-emergence treatment with hexazinone was<br />

significantly lower than the former at the June evaluation, but did not differ from the<br />

hexazinone, mesotrione 437 mL/ha pre-emergence with hexazinone or 217 mL/ha postemergence<br />

with hexazinone treatments. Grass cover in the hexazinone, mesotrione<br />

437 mL/ha pre-emergence with hexazinone, 217 mL/ha pre-and post-emergence with<br />

hexazinone and 217 mL/ha post-emergence with hexazinone were significantly lower<br />

than the latter at the August evaluation, but did not differ from each other, the untreated<br />

control or remaining mesotrione treatments. Although for the most part the mesotrione<br />

treatments in combination with hexazinone did not significantly suppress grasses<br />

compared to mesotrione alone. Overall grass cover increased with time although there<br />

was a trend of better grass suppression when both herbicides were applied.<br />

12


Figure 1. Effect of hexazinone and mesotrione on broadleaf weeds.<br />

Figure 2. Effect of hexazinone and mesotrione on grass weeds.<br />

13


CONVERTING COOL-SEASON ATHLETIC FIELDS TO PATRIOT BERMUDAGRASS<br />

USING CHEMICALS AND ROW PLANTING. T.L. Mittlesteadt, J.M. Goatley, and S.D.<br />

Askew, Virginia Tech, Blacksburg and M. Sullenberger, Game Day, Inc., Arlington, VA.<br />

ABSTRACT<br />

Improved cold tolerance of 'Patriot' Bermudagrass (Cynodon dactylon) has<br />

increased the desire to convert cool-season athletic fields to bermudagrass in the<br />

transition zone and northern states. The goals of this experiment were to evaluate preplanting<br />

vegetation-management treatments as they affect the establishment of rowplanted<br />

‘Patriot’ bermudagrass and to determine if a cool-season turf can be converted<br />

to bermudagrass in a manner that minimizes effects on turf use. Trials were conducted<br />

at the Virginia Tech Turfgrass Research Center in Blacksburg, VA and Bridgewater<br />

College near Harrisonburg, VA in 2006. In 2007, the trial was repeated at the Virginia<br />

Tech Golf Course in Blacksburg. On May 19, 2006 and May 17, 2007, four pre-planting<br />

treatments were applied to the cool-season turf, which was a mixture of Kentucky<br />

bluegrass (Poa pratensis) and perennial ryegrass (Lolium perenne). These four<br />

treatments were: nontreated control, partially kill existing vegetation in 5 cm-wide strips<br />

on 15-cm centers using glyphosate at 4.5 kg ai/ha in 561 L/ha carrier volume,<br />

completely kill existing vegetation using glyphosate at 4.5 kg ai/ha in 280 L/ha, and<br />

regulate existing vegetation with trinexapac ethyl at 0.39 kg ai/ha in 281 L/ha. On May<br />

26, 2006 and May 24, 2007 ‘Patriot’ bermudagrass was sprigged at a level of 430<br />

sprigs/sq m. Visual estimations of percentage total cover of green turf and<br />

bermudagrass establishment, and quality ratings were made periodically.<br />

Results from these three trials indicate that totally killing the cool-season turf or<br />

partially killing turf in strips results in a quicker conversion to bermudagrass. However,<br />

turf quality and percentage of total ground cover are sacrificed up to 10 weeks after<br />

planting when totally killing existing turf. Nontreated and trinexapac ethyl resulted in<br />

similar bermudagrass establishment rates of 50 to 80% after 10 weeks. An advantage<br />

to these treatments is that total ground cover never dropped below 90% and turf could<br />

remain in use the entire time. Partial-kill plots were similar in that turf cover was at least<br />

70% for the duration of the study and could sustain moderate field use. Although<br />

sprigged bermudagrass can be rapidly established after killing existing vegetation, our<br />

results indicate that higher turfgrass quality can be maintained by row-planting<br />

bermudagrass sprigs directly into existing turf. Partially killing existing turf can<br />

substantially speed establishment while maintaining acceptable turf quality. Trinexapac<br />

ethyl and the nontreated plots maintained the highest turfgrass quality with the slowest,<br />

but acceptable, establishment rate.<br />

14


ROUGHSTALK BLUEGRASS CONTROL IN CREEPING BENTGRASS FAIRWAYS<br />

WITH BISPYRIBAC-SODIUM AND SULFOSULFURON. P.E. McCullough and S.E.<br />

Hart, Rutgers, The State University of New Jersey, New Brunswick.<br />

ABSTRACT<br />

Bispyribac-sodium and sulfosulfuron are new ALS-inhibiting herbicides registered<br />

for use in creeping bentgrass (Agrostis stolonifera L.) fairways for selective roughstalk<br />

bluegrass (Poa trivialis L.) control but limited comprehensive investigations have been<br />

conducted to evaluate efficacy for long-term management. Field experiments were<br />

conducted from June 2005 to October 2007 at New Jersey National Golf Club in<br />

Basking Ridge, NJ. Bispyribac-sodium was applied twice at 37, 74, or 111 g a.i./ha or<br />

thrice at 37 or 74 g/ha. Sulfosulfuron was applied twice or thrice at 6.5, 13, or 26 g<br />

a.i./ha or once at 26 g/ha. Applications were made in June and July at 220 L/ha and a<br />

nonionic surfactant was included at 0.25% v/v for sulfosulfuron treatments. Creeping<br />

bentgrass chlorosis from herbicides was acceptable (< 20%) by 2 to 3 weeks after<br />

applications while all treatments provided substantial reductions in roughstalk bluegrass<br />

cover (>90%) by late July. However, roughstalk bluegrass had regrown by October in<br />

both years suggesting herbicide applications visually eliminated foliage but did not<br />

control vegetative reproductive structures. Since roughstalk bluegrass has a wide<br />

genetic diversity, further investigations are needed to determine if these results are<br />

correlated with biotype tolerance to herbicide applications or from ineffective herbicide<br />

translocation. Overall, bispyribac-sodium and sulfosulfuron effectively eliminated<br />

roughstalk bluegrass ground cover in summer months but regrowth during fall months<br />

prevented long-term successful control.<br />

15


BROCCOLI AND CAULIFLOWER RESPONSES TO POSTEMERGENCE<br />

APPLICATIONS OF VINEGAR FOR WEED MANAGEMENT. C. B. Coffman, J.<br />

Radhakrishnan, and J. R. Teasdale, USDA-ARS, Beltsville, MD<br />

ABSTRACT<br />

According to a recent article in the Philadelphia Inquirer by Marilynn Marter dated<br />

17 May, 2007, the number of farmer's markets in the United States has risen from 1755<br />

in 1994 to 4385 in 2006. She further cites reports by The Farmers Markets Coalition<br />

that state some 30,000 farmers are now selling their products directly to more than 3<br />

million consumers a year at farmer’s markets. Broccoli (Brassica oleracea L. var.<br />

italica) and cauliflower (Brassica oleracea L. var. botrytis) are commonly grown by<br />

farmers who sell at farmer’s markets. Broccoli and cauliflower are generally grown as<br />

spring or fall crops in the mid-Atlantic. <strong>Weed</strong> control methods include synthetic<br />

herbicides as well as cultural practices such as crop rotation, cultivation, mulches, and<br />

cover crops. Experimental weed control methods have included essential oils, corn<br />

gluten, and vinegar. Fall broccoli and cauliflower response to vinegar application was<br />

investigated at the Beltsville Agricultural research Center in 2007. The objective was to<br />

evaluate crop responses to basal applications of 20% acetic acid vinegar for within-row<br />

weed control. Broccoli (var. 'Packman’) seeds were sown in the greenhouse 7 July,<br />

2007, and transplanted into a clean-cultivated field on 9 August. Broccoli plants were 18<br />

inches apart in five-foot wide, 20-foot long rows. Cauliflower (var. Snowball Y) seeds<br />

were sown in the greenhouse 21 June and transplanted on 26 July. Plants were 14<br />

inches apart in five-foot wide, 20-foot long rows. Treatments were applied to the center<br />

row of three row plots and included (1) vinegar applications, (2) un-weeded control, and<br />

(3) hand-weeded control. Treatments were replicated four times and were randomly<br />

placed in the field. Vinegar applications to broccoli and cauliflower were made on 12<br />

and 19 September, respectively, using a hand sprayer. Vinegar was applied to weeds<br />

to achieve complete coverage until runoff. Broccoli plants were 8 to 13 inches high<br />

when treatments were applied whereas cauliflower plants ranged from 14 to 26 inches<br />

high. <strong>Weed</strong>s between rows were controlled by cultivation. <strong>Weed</strong>s in the hand-weeded<br />

control were removed once during the growing season. Broccoli treatments were<br />

visually rated 17 September, and harvested 9 and 15 October. Mean broccoli injury<br />

score in the vinegar treatment was 52, which on a scale of 0 to 100, is unacceptable,<br />

and significantly higher than the score (0) for the hand-weeded and un-weeded<br />

treatments. Broccoli plants treated with vinegar showed diminished leaf turgor within 30<br />

minutes of application and chlorotic tissue within 24 hours. Mean cauliflower injury score<br />

in the vinegar treatment was 25, which is acceptable on the above rating scale. There<br />

was slight to no loss of leaf turgor or leaf chlorosis in cauliflower plants treated with<br />

vinegar. Broccoli head counts from plants in the vinegar treatment were 22% lower<br />

than the un-weeded and hand-weeded controls. Mean individual head weights were 12<br />

and 19% lower for the vinegar treatments than for the hand-weeded and un-weeded<br />

controls, respectively.<br />

16


ORGANIC WEED MANAGEMENT: WHAT THE FARMERS THINK. M. R. Ryan, D. A.<br />

Mortensen, Penn State University, University Park, D. O. Wilson, and P. R. Hepperly,<br />

The Rodale Institute, Kutztown, PA.<br />

ABSTRACT<br />

Organic farming is gaining popularity in ways few outside the organic farming<br />

community would have imagined only ten years ago. In the US, farmland planted to<br />

certified organic vegetables and grain crops increased 104% and 109%, respectively,<br />

from 1997 to 2005. To identify challenges to organic weed management and farmers’<br />

attitudes, a survey was conducted via the NewFarm.org website from March to July of<br />

2007. The majority of the respondents were from the US, and approximately 85% of the<br />

respondents indicated that they were farming organically or were in transition to organic<br />

production. A variety of diverse cropping systems were represented with 65% of the<br />

respondents indicating they grew vegetables, 41% grew fruits, 19% grew feed grains,<br />

and 15% grew food grains.<br />

Respondents indicated they use diverse weed management strategies with 85%<br />

indicating they use at least three weed management practices, and on average<br />

respondents identified six practices to manage weeds on their farms. Hand weeding<br />

was the most common practice. Mechanical control practices were listed as the second<br />

most common practice among respondents, and almost half of the respondents stated<br />

they use between-row cultivation. Other physical weed control practices commonly<br />

practiced include mulching, flame weeding, and stale seed bedding. Over half of the<br />

respondents use cover crops as a weed management tool, and approximately 40%<br />

have diverse rotations which help manage weed populations. Between 20 and 40% of<br />

respondents stated that they adjust seeding rates and row-width, manage fertility wisely,<br />

and alter planting dates to give crop plants a competitive advantage.<br />

‘Lack of time’, selected by 68% of respondents, was the top challenge to effective<br />

weed management. ‘Weather conditions’ was the next major obstacle, cited by almost<br />

half of participants. As part of the survey we asked respondents to indicate whether or<br />

not they agree with a series of statements to better gauge farmer attitudes toward<br />

farming and weed management. One of the strongest responses was in agreement with<br />

the statement ‘I am concerned that the use of chemicals in farming is a health risk to me<br />

and my family’. There was not a strong consensus in regard to the statement ‘<strong>Weed</strong><br />

management is my number one production constraint’; however, slightly more people<br />

agreed with the statement than disagreed, indicating that weed management is the top<br />

production constraint faced by approximately 50% of the responding farmers. Although,<br />

most respondents disagreed with the statement ‘Organic weed management practices<br />

cannot be as effective as conventional, chemical based ones’, respondents suggested a<br />

need for additional research on organic weed management.<br />

17


A SIX-YEAR COMPARISON OF PREEMERGENCE CRABGRASS CONTROL WITH<br />

PROFESSIONAL TURF HERBICIDES. J.L. Jester, J.B. Willis, and S.D. Askew, Virginia<br />

Tech, Blacksburg.<br />

ABSTRACT<br />

Crabgrass remains the most important weed of improved turfgrass based on<br />

dollars spent for preemergence and postemergence control. Despite numerous<br />

herbicides available for crabgrass control in lawns, lawn care professionals and home<br />

owners continue to report control failures. Professionals are particularly interested in<br />

crabgrass control programs that provide season-long control and consistency from one<br />

site to another and across seasons. Several preemergence herbicides have been<br />

evaluated at Virginia Tech annually between 2002 and 2007. The objectives are to<br />

determine herbicide effectiveness and application intervals that will provide the most<br />

consistent smooth crabgrass (Digitaria ischaemum) control late in the season.<br />

Field trials were conducted each year for six years on tall fescue or Kentucky<br />

bluegrass turf maintained at 2.5 inches in Blacksburg, VA. Studies were conducted as<br />

randomized complete block factorial designs with treatments replicated three times.<br />

Treatment factors included herbicide and application with 6 herbicides each applied<br />

once at a full rate or twice at reduced rates. A nontreated control was included for<br />

comparison. Herbicides included benefin at 1.5 lb ai/A and 1.5 followed by (fb) 1.5 lb<br />

ai/A, benefin plus trifluralin at 2.0 lb ai/A and 1.5 fb 1.5 lb ai/A, dithiopyr at 0.5 lb ai/A<br />

and 0.25 fb 0.25 lb ai/A, oxadiazon at 4.0 lb ai/A and 2.0 fb 2.0 lb ai/A, pendimethalin at<br />

3.0 lb ai/A and 1.5 fb 1.5 lb ai/A, and prodiamine at 0.94 lb ai/A and 0.66 fb 0.66 lb ai/A.<br />

Initial treatment times were based on GDD 50 between 70 and 140 and occurred<br />

between April 4th and April 27th depending on year. Repeat treatments were applied<br />

approximately eight weeks later and occurred between May 26 and June 7 depending<br />

on year. Crabgrass control was evaluated by visual estimation of crabgrass cover and<br />

percentage reduction in crabgrass compared to nontreated controls.<br />

In annual studies between 2002 and 2007, dithiopyr, pendimethalin, and<br />

prodiamine controlled smooth crabgrass between 80 and 100% when applied as two<br />

split-rate treatments and between 50 and 100% when applied as a single full-rate<br />

treatment with few exceptions. Consistency of weed control increased when sequential<br />

treatments were applied compared to single treatments for all herbicides except<br />

oxadiazon. In general, single applications performed better in years of limited rainfall<br />

and poorly in years of adequate or excessive rainfall. Benefin and benefin plus trifluralin<br />

controlled crabgrass less than dithiopyr, pendimethalin, and prodiamine in most years.<br />

18


EVALUATION OF THE IMPACT OF AN ADVENTITIOUS HERBIVORE ON AN<br />

INVASIVE PLANT, YELLOW TOADFLAX, IN COLORADO USA. J.F. Egan, Penn State<br />

University, State College and R. E. Irwin, Dartmouth College, Hanover, NH. Rocky<br />

Mountain Biological Lab, Crested Butte, CO.<br />

ABSTRACT<br />

Many invasive plants arrive into their new range without their associated<br />

herbivores. However for others, their herbivores arrive prior to, with, or after the<br />

introduction of the plant, re-establishing the link between natural enemies and invaders<br />

in the introduced range. Research documenting the effects of adventitiously introduced<br />

herbivores on their target plants in the introduced range, and the mechanisms by which<br />

those effects occur, can provide insight into biological weed control. We studied the<br />

effects of an accidentally introduced beetle Brachypterolus pulicarius on the growth and<br />

reproduction of its host, the invasive plant yellow toadflax (Linaria vulgaris), growing<br />

under field conditions from 2002-2004 across eight sites in western Colorado, USA. We<br />

found that feeding by B. pulicarius on yellow toadflax was variable among three years<br />

and across eight local sites. Variation in damage was partially explained by ramet<br />

density; sites with greater ramet density experienced more damage. In an observational<br />

study across two years, damage was positively correlated with estimates of sexual<br />

reproduction, ramet growth, and clonal shoot production. However, opposite trends<br />

were observed in an experimental study; damage by B. pulicarius decreased estimates<br />

of sexual reproduction. Differences between the results of the observations and<br />

experiments were likely driven by selective feeding by B. pulicarius on larger ramets.<br />

Nonetheless, the ability of B. pulicarius to control established yellow toadflax population<br />

growth remains uncertain under the environmental conditions we studied. In both the<br />

observational and experimental study, B. pulicarius did not affect yellow toadflax<br />

survival, and we found no evidence that established yellow toadflax populations were<br />

seed limited, suggesting that reductions in seeds may not translate into demographic<br />

changes in heavily infested populations. Interactions among insect foraging behavior,<br />

individual plant responses to damage, and the demographic consequences of seed<br />

production may help to explain the varying degrees to which herbivores affect plants<br />

and populations.<br />

19


EVALUATION OF AT-SEEDING GRANULAR HERBICIDES IN KENTUCKY<br />

BLUEGRASS TURF. R.S. Chandran, West Virginia University, Morgantown; and R.J.<br />

Keese, Syngenta Professional Products, Carmel, IN.<br />

ABSTRACT<br />

A field experiment established in Morgantown, WV, evaluated the herbicides<br />

mesotrione and siduron applied at the time of seeding Kentucky bluegrass (Poa<br />

pratensis L. 'Moonstruck') for turfgrass injury and weed control up to three months after<br />

seeding. The site had a silt loam soil and was seeded on May 1, 2007, and the<br />

fertilizer-based granular herbicides were applied the following day. Herbicide<br />

treatments consisted of mesotrione applied at 0.15, 0.2 or 0.6 lb ai/A, or siduron at 5 lb<br />

ai/A, or different rates of mesotrione applied along with siduron rates up to 15 lb ai/A.<br />

Fertilizer-treated and untreated plots were also established as control plots. Routine<br />

cultural practices were carried out during the establishment period. Injury ratings and<br />

weed control data were analyzed for variance (ANOVA) and means were separated<br />

using Least Significant Difference (LSD, p= 0.05). The highest rates of herbicides did<br />

not cause visual injury to turf at 4 weeks after treatment (WAT), however, they reduced<br />

percent turf cover by 25-30%. At 12 WAT, all treatments provided complete turf cover.<br />

Mesotrione applied at 0.6 lb ai/A provided >90% control of wild violet (Viola spp.), yellow<br />

wood sorrel (Oxalis stricta), and smooth crabgrass (Digitaria ischaemum) at 12 WAT,<br />

and >90% white clover (Trifolium repens) at 8 WAT. Addition of 15 lb ai/A of siduron to<br />

this treatment did not result in significant increases in weed control. A lower rate of<br />

mesotrione + siduron (0.45 + 7.5 lb ai/A) provided weed control similar to levels from<br />

mesotrione applied alone at 0.6 lb ai/A. Siduron applied alone at 5 lb ai/A did not<br />

provide acceptable levels of weed control at any of the evaluation timings. Fertilizertreated<br />

plots and untreated plots resulted in more than 75% weed cover, mostly smooth<br />

crabgrass, at 12 WAT.<br />

20


DOES SOIL PH INFLUENCE SWALLOW-WORT DISTRIBUTION IN ITS CURRENT<br />

RANGE? L.C. Magidow, A. DiTommaso, Q.M. Ketterings, Cornell University, Ithaca, NY<br />

and L.R. Milbrath, USDA-ARS, Ithaca, NY.<br />

ABSTRACT<br />

The perennial non-native vines, pale swallow-wort [Vincetoxicum rossicum<br />

(Kleopow) Barbar] and black swallow-wort [Vincetoxicum nigrum (L.) Moench], are<br />

established invaders in the northeastern United States and southeastern Canada, and<br />

are spreading westward. The swallow-worts typically colonize forest-field margins, road<br />

edges, tree nurseries, and rare limestone barrens. In open areas, they can form dense,<br />

monospecific stands where they out-compete and displace resident vegetation.<br />

Previous research and observations indicate that these vines may occupy distinct<br />

ranges, with pale swallow-wort associated with basic, limestone-based soils, while black<br />

swallow-wort is associated with more acidic soils. To gain a better understanding of the<br />

chemical characteristics of soils colonized by these two swallow-wort species, soil<br />

samples were collected by volunteers across the distribution range of these plants.<br />

Samples were then submitted to the Cornell Nutrient Analysis Laboratory for chemical<br />

analysis. As of October 2007, nearly 100 samples were received from over 25<br />

volunteers, with new samples arriving weekly. Preliminary results indicate that pale<br />

swallow-wort occurs on soils with an average pH = 6.7, and ranging from 4.7 to 7.9, and<br />

black swallow-wort occurs on soils with an average pH = 6.4, and ranging from 5.2 to<br />

8.0. Despite the similar range in pH of soils colonized by these two species, the<br />

geographic distributions of pale and black swallow-wort do appear distinct. These<br />

preliminary findings suggest that differences in pH of soils colonized by the two swallowwort<br />

species may not be an important factor influencing the current distribution pattern<br />

of these two invasive vines.<br />

21


WAVYLEAF BASKETGRASS IN MARYLAND – AN EDRR IN PROGRESS.<br />

K.L. Kyde, Maryland Department of Natural Resources, Annapolis and B.H. Marose,<br />

University of Maryland, College Park.<br />

ABSTRACT<br />

A Southeast Asian grass first discovered in a Maryland state park 10 years ago<br />

has spread to cover many hectares of forested land in central Maryland. This<br />

population is the only reported occurrence of Wavyleaf basketgrass (Oplismenus<br />

hirtellus ssp. Undulatifolius) on the North American continent. Perennial, stoloniferous,<br />

and highly shade-tolerant, this grass occupies the same mesic forest habitats as<br />

Japanese stiltgrass (Microstegium vimineum), and may be even more aggressive than<br />

that annual species. Wavyleaf basketgrass appears to spread both vegetatively and by<br />

seed via sticky awns, but little is known about its phenology, germination rate or rate of<br />

spread. Early fall applications of glyphosate achieved only 70% mortality in test plots.<br />

The Maryland Department of Natural Resources believes that eradication is necessary<br />

and possible. This presentation serves as an introduction to and warning about this<br />

invasive forest grass.<br />

22


EFFECTS OF BUCKWHEAT COVER CROP ON WINTER WHEAT ESTABLISHMENT,<br />

YIELD, AND WEED SUPPRESSION. V. Kumar, Cornell University, Ithaca, NY, D.C.<br />

Brainard, Michigan State University, East Lansing, R.R. Bellinder, and R.R. Hahn,<br />

Cornell University, Ithaca, NY<br />

ABSTRACT<br />

Cover crops offer both soil improvement and weed control benefits. Field and pot<br />

bioassay studies were conducted from 2005 through 2007 in Central NY to examine the<br />

potential of including buckwheat as a cover crop in a niche between harvest of early<br />

vegetable crops (in July) and planting of winter-wheat (in late September). The<br />

objectives of this research were to determine (1) in-season weed suppressive ability of<br />

buckwheat, and (2) the effects of buckwheat residue on establishment of weeds, winter<br />

wheat, and on the germinable weed seedbank. In a field study, buckwheat was sown<br />

either in mid July (early buckwheat) or early August (late buckwheat). At the second<br />

planting date, two buckwheat treatments were established to allow comparison of tilled<br />

versus no-till wheat planting in buckwheat residue following termination of buckwheat<br />

cover crop. A bare soil and 2 weedy control treatments (one for each planting date)<br />

were also included. Buckwheat was mowed 10-d after anthesis and either disked or left<br />

on the soil surface (buckwheat late, no-till). Wheat was sown with a no-till drill in all<br />

treatments on September 19. Immediately after buckwheat early incorporation, common<br />

chickweed, and shepherd’s purse were sown in bare soil and buckwheat early plots.<br />

Soil samples from buckwheat residue and bare soil plots were taken the following year<br />

in May for estimating weed seed banks. In a complementary growth chamber study,<br />

seeds of Powell amaranth, hairy galinsoga, barnyardgrass, common purslane, yellow<br />

rocket, corn chamomile, common chickweed, and shepherd’s-purse were sown in pots<br />

filled with field soil from buckwheat residue and bare soil plots taken 0 and 15-d after<br />

buckwheat incorporation. Emergence and growth of these species were monitored for<br />

20 days. During in-season, buckwheat reduced weed biomass ranging from 75-99%<br />

compared to weedy checks. In the 2005 pot study, fresh buckwheat residues reduced<br />

the emergence (27 to 72%) of all weed species except barnyardgrass, and reduced the<br />

dry weight of all weed species (66-94%). In 15 day old residue, only Powell amaranth<br />

suppression occurred. In 2006, fresh buckwheat residues suppressed emergence of<br />

Powell amaranth, common purslane, and common chickweed and had no effect on the<br />

dry weight of any weed species. In the field, emergence of common chickweed and<br />

shepherd’s-purse was reduced 35 and 57% in buckwheat compared to bare soil plots<br />

following buckwheat incorporation. Winter wheat emergence was not affected by<br />

buckwheat residue but early growth of winter wheat was reduced in buckwheat residue<br />

compared to non-residue plots in both years. However, no differences in yields of winter<br />

wheat were detected in either year. Germinable weed seedbank density was similar in<br />

buckwheat residue and bare soil plots in 2006, however, in 2007, pigweed seedbank<br />

density was 43% lower in buckwheat residue plots. Our results demonstrate that<br />

inclusion of buckwheat before wheat planting can contribute to weed management<br />

through direct interference with weeds and through residue mediated effects on weed<br />

emergence, growth and germinable seedbank density.<br />

23


BUSHKILLER BIOLOGY AND RESPONSE TO HERBICIDES. A.M. West, R.J.<br />

Richardson, A.P. Gardner, North Carolina State University, Raleigh, NC, and J.<br />

Matthews, Habitat Assessment and Restoration Program, Charlotte, NC.<br />

ABSTRACT<br />

Bushkiller [Cayratia japonica (Thunb. ex Murray) Gagnepain] is a perennial vine<br />

in the Vitaceae family. The genus is distributed primarily in tropical to sub-tropical<br />

regions of Africa, Australia, Asia and the Pacific Islands. Bushkiller has been reported<br />

in Louisiana, Mississippi, Texas, and North Carolina and is considered an invasive<br />

species. Research trials were conducted at NCSU to determine bushkiller response to<br />

selected herbicides and the regenerative capability of roots in response to planting<br />

depth. In the herbicide trial, bushkiller, Virginia creeper [Parthenocissus quinquefolia<br />

(L.) Planch.], and trumpetcreeper [Campsis radicans (L.) Seem. ex Bureau] were<br />

treated with triclopyr, 2,4-D, aminopyralid, and glyphosate either alone or applied in<br />

selected combinations. Control of bushkiller was at least 88% with all treatments<br />

containing triclopyr and with 2,4-D alone. Virginia creeper response was generally<br />

similar to that of bushkiller, while control of trumpetcreeper was generally lower. In the<br />

planting depth trial, bushkiller was planted at various depths with root length of 1, 2, or 4<br />

cm of uniform diameter. Plant size was affected by root length, but was less affected by<br />

planting depth. Bushkiller consistently emerged from planting depths of up to 20 cm.<br />

24


PHRAGMITES RESPONSE TO SELECTED HERBICIDES. S.L. True, R.J. Richardson,<br />

A.P. Gardner, North Carolina State University, Raleigh, NC, and P.L. Hipkins, Virginia<br />

Tech, Blacksburg, VA.<br />

ABSTRACT<br />

Research was conducted in 2006 and 2007 to determine the response of<br />

Phragmites or common reed [Phragmites australis (Cav.) Trin. ex Steud.] to selected<br />

herbicide applications. The first trial was applied in both North Carolina and Virginia. In<br />

North Carolina, treatments included imazapyr (160, 320, and 480 oz / 100 gal),<br />

glyphosate (160, 320, and 640 oz / 100 gal), triclopyr (640 and 1920 oz / 100 gal), and<br />

penoxsulam (7.1, 14.3, 28.6, and 57 oz / 100 gal) applied as spray to wet applications.<br />

In Virginia, treatments included imazapyr (0.5, 1.0, and 1.5 lb ai/A), glyphosate (1, 2,<br />

and 4 lb ai/A), triclopyr (3 and 9 lb ai/A), and penoxsulam (25, 50, and 100 g ai/A)<br />

applied as broadcast applications. A nonionic surfactant at 0.25% v/v was included with<br />

each treatment and certain herbicide mixtures were also applied. In North Carolina at 8<br />

WAT, phragmites control was greatest with triclopyr and 6.64% v/v glyphosate at 91 to<br />

100%. Control with treatments containing imazapyr ranged 50 to 80% and control was<br />

not visible from penoxsulam. At 16 WAT, control with all imazapyr, glyphosate, and<br />

triclopyr treatments was at least 87%. Phragmites was not controlled with the<br />

penoxsulam rates evaluated. In Virginia unmowed plots, only 9 lb ae/A triclopyr<br />

controlled Phragmites (80%). Control was 60 to 67% with 4 lb ae/A glyphosate and<br />

glyphosate plus penoxsulam at 16 WAT, but control with other treatments did not<br />

exceed 33%. In mowed plots, results were quite different. Control was 52 to 73% at 8<br />

WAT across all imazapyr and glyphosate treatments except glyphosate plus<br />

penoxsulam. At 12 WAT, control was greatest at 73 to 87% with all imazapyr<br />

treatments, as well as 2 and 4 lb ae/A glyphosate. Control with triclopyr and<br />

penoxsulam did not exceed 30%. In conclusion, Phragmites control was variable<br />

across sites and possibly affected by size at application (mowing), application method,<br />

and presence or absence of standing water.<br />

25


LONGEVITY OF WEED CONTROL IN CONTAINERS WITH BAS 659H. R.P.M.<br />

Atwood, University of Warwick, UK, L.C. Walker, J.C. Neal, North Carolina State<br />

University, Raleigh, and C. A. Judge, BASF Corp, Research Triangle Park, NC.<br />

ABSTRACT<br />

Nursery crop producers rely upon preemergence herbicides applied every 8-10<br />

weeks; yet, even with this frequent herbicide treatment regime, weeds emerge and must<br />

be removed by supplemental hand weeding. Prior research has demonstrated that the<br />

half-life of preemergence herbicides is generally shorter in container nurseries than in<br />

field soils. Furthermore, longevity of weed control in containers depends upon the<br />

herbicide used and the weed species present. Recent research has shown that a<br />

granular combination dimethenamid-P + pendimethalin controls many common nursery<br />

weeds however, the longevity of weed control in containers has not been evaluated. An<br />

experiment to determine the longevity of weed control in containers with BAS 659H<br />

1.75G (0.75% dimethenamid-P + 1% pendimethalin) compared with industry standards<br />

was conducted at Castle Hayne Research Station, NC. Pots were filled with pine bark +<br />

sand substrate on 9 May 2007 then treated on 8 June 2007 with 3 lb ai/A OH2 ® , 5 lb<br />

ai/A Snapshot ® TG, 0.38 lb ai/A Broadstar, and 1.75, 2.6 & 3.5 lb ai/A BAS 659H.<br />

Five weed species, hairy bittercress (Cardamine hirsuta), eclipta (Eclipta prostrata),<br />

large crabgrass (Digitaria sanguinalis), spotted spurge (Chamaesyce maculata) and<br />

doveweed (Murdannia nudiflora), were surface seeded 0, 4, 6 and 8 weeks after<br />

treatment; each species and seeding date in separate pots. Treatments were arranged<br />

in a randomized complete block design with 4 replications with 3 pots of each species<br />

per experimental unit. Visual ratings of the overall % weed control were recorded every<br />

two weeks after treatment using an abbreviated percent scale of 0 to 10, where 0 =no<br />

injury and 10 = dead plants (100% control). Data were subjected to ANOVA and means<br />

separation by seeding date and rating date. Additionally data were fit to a logistic nonlinear<br />

regression model and number of weeks above 80% control was estimated from<br />

the resulting regression equations. When seeded the day of treatment, all treatments<br />

except the lowest rate of BAS 659H provided at least 94% control of all weed species<br />

tested. <strong>Weed</strong> control decreased over time for all species and treatments except<br />

bittercress control with OH2 ® . OH2 ® provided about 8 weeks of >80% bittercress<br />

control whereas other treatments provided less than 4 weeks. Eight weeks after<br />

treatment the two higher rates of BAS 659H provided superior control of doveweed and<br />

spurge; and the high rate of BAS 659H provided significantly better control of crabgrass<br />

and eclipta compared to the other treatments. These data suggest that, compared to<br />

industry standard herbicides, BAS 659H may provide longer residual control of spurge,<br />

crabgrass, doveweed, and eclipta in containers. However, OH2 ® provided longer<br />

residual control of bittercress under the same conditions.<br />

26


CARDAMINE WEED SPECIES IN UNITED STATES NURSERIES. A.R. Post, J.C.<br />

Neal, A. Krings, B.R. Sosinski, and Q. Xiang, North Carolina State University, Raleigh.<br />

ABSTRACT<br />

Cardamine is one of the most common and problematic weeds of container<br />

nurseries in the United States. Historically, almost all Cardamine specimens collected<br />

from nurseries have been identified as Cardamine hirsuta L. However, the movement<br />

of nursery stock around the United States, and even worldwide, has likely resulted in<br />

the introduction and dispersion of several closely related Cardamine species. A<br />

previous study indicated that Cardamine flexuosa With. and Cardamine scutata Thunb.<br />

also occur in container nurseries. These species exhibit great morphological variability<br />

making them difficult to distinguish from the cosmopolitan Cardamine hirsuta. Due to<br />

reports of isoxaben-resistant haplotypes of Cardamine flexuosa in Europe, it is<br />

important that nurserymen correctly identify these species to ensure adequate control.<br />

For this study, Cardamine specimens were collected from 21 nurseries in California,<br />

New York, North Carolina, Mississippi, Missouri, and Oregon to determine which<br />

species of Cardamine were present. These species were then characterized<br />

morphologically through examination of voucher specimens, type specimens and<br />

additional herbarium sheets from material on loan from 12 herbaria. Identification was<br />

confirmed through analysis of molecular sequence data of each sample, in comparison<br />

with known sequences of each species. Preliminary results indicate Cardamine<br />

flexuosa and Cardamine oligosperma Nutt. occur in United States nurseries alongside<br />

the typical Cardamine hirsuta. One other species is present which has not previously<br />

been reported for the United States. It is also suspected that Cardamine pensylvanica<br />

Muhl. ex Willd. and Cardamine scutata may occur in United States nurseries but this<br />

has not yet been confirmed. Updated taxonomic keys are being developed to aid<br />

nurserymen in differentiating these species.<br />

27


AMICARBAZONE AND FLUCARBAZONE FOR WEED CONTROL IN TURFGRASS.<br />

M.J. Goddard, T.L. Mittlesteadt, and S.D. Askew, Virginia Tech, Blacksburg and L.D.<br />

Houseworth, Arysta Life<strong>Science</strong> North America, Fernandina Beach, FL.<br />

ABSTRACT<br />

Amicarbazone and flucarbazone (70 WG, Arysta Life<strong>Science</strong>) are both members<br />

of the triazolone chemical family and are being evaluated for use in the turfgrass<br />

industry. Amicarbazone inhibits photosynthesis at photosystem II and is registered in<br />

corn as an atrazine alternative. Flucarbazone inhibits branched chain amino acid<br />

production by inhibiting the enzyme acetolactate synthase (ALS), and is used in cereals<br />

for postemergence and preemergence control of grassy weeds and selected<br />

broadleaved weeds. Field trials conducted in Blacksburg, VA evaluated the use of<br />

amicarbazone and flucarbazone for control of annual grasses and broadleaved weeds,<br />

as well as turfgrass tolerance. A study to evaluate cool-season turfgrass tolerance of<br />

these herbicides in tall fescue (Festuca arundinacea), Kentucky bluegrass (Poa<br />

pratensis), fine fescue, and creeping bentgrass (Agrostis stolonifera) was initiated in<br />

2007. Treatments included single applications of flucarbazone applied at 21 and 42<br />

g/ha, and amicarbazone at 248, 495, and 743 g/ha, compared to currently labeled<br />

triazolone herbicides carfentrazone and sulfentrazone at 1 and 2 times label suggested<br />

rates to determine turfgrass tolerance. Amicarbazone treatments were the most<br />

injurious overall with the highest rates resulting in greater than 70% injury to creeping<br />

bentgrass and Kentucky bluegrass. Flucarbazone treatments resulted in minimal injury<br />

to fine fescue, Kentucky bluegrass, and creeping bentgrass, but unacceptable injury<br />

(chlorosis and stunted growth) to tall fescue. In two trials that evaluated amicarbazone<br />

applied preemergence at 743 g/ha and flucarbazone applied preemergence and<br />

postemergence at 42 g/ha for smooth crabgrass (Digitaria ischaemum) control in<br />

Kentucky bluegrass, neither of these two products significantly reduced crabgrass<br />

presence whether applied preemergence or postemergence. However, it was observed<br />

that both herbicides had activity on annual and perennial broadleaved weeds. It was<br />

also observed that amicarbazone injured Kentucky bluegrass more than 50% at both<br />

locations. In other trials, amicarbazone and flucarbazone applied at 743 g/ha and 42<br />

g/ha, respectively, were compared to Speedzone ® (PBI/Gordon Corporation), an<br />

industry standard, applied at 4.7 L/ha, for postemergence broadleaf control in lawn<br />

height tall fescue and Kentucky bluegrass. White clover (Trifolium repens) was<br />

controlled by amicarbazone 87 and 100%, flucarbazone 47 and 87%, and Speedzone ®<br />

100% in tall fescue and Kentucky bluegrass, respectively. Minimal injury was noticed in<br />

all treatments when applied to tall fescue, but amicarbazone injured Kentucky bluegrass<br />

90% or more.<br />

28


EFFECTS OF TOPDRESSING COLOR ON ESTABLISHMENT OF SPRIGGED<br />

PATRIOT BERMUDAGRASS. T.L. Mittlesteadt, J.L. Jester, and S.D. Askew, Virginia<br />

Tech, Blacksburg.<br />

ABSTRACT<br />

Bermudagrass is widely used on athletic fields because of its tolerances to<br />

drought, heat, and wear. The improved cold tolerance in some newer varieties of<br />

bermudagrass, such as 'Patriot', are allowing use of bermudagrass in athletic fields<br />

further north than in the past. The most common methods for establishing<br />

bermudagrass are: seeding, sprigging, and sod. Sprigging remains the most common<br />

approach due to availability and costs issues. Bermudagrass can be slow to establish<br />

from sprigs when compared to sod. Sand-based field construction is more common in<br />

recent years owing to improved drainage and compaction resistance with sand-based<br />

media. Due to costs of transportation, sand for field construction is typically limited to<br />

local quarries. In several instances, Virginia Tech researchers have observed slow<br />

establishment rates on white sand. We hypothesized that topdressing color could have<br />

an influence on the establishment rate. Therefore, a study was conducted to evaluate<br />

bermudagrass establishment when topdressed with particles of several colors and<br />

textures.<br />

A field trial was established July 19, 2007 on sprigged ‘Patriot’ bermudagrass at<br />

Virginia Tech’s turfgrass research center with each plot ranging from 20 to 30%<br />

bermudagrass cover. The trial area was constructed to simulate Worsham Field with<br />

respect to drainage, irrigation, and sand-based growing media with the exception that a<br />

modular substructure was not installed. The study was established as a randomized<br />

complete block design with six treatments and three replications. Two particle sizes<br />

included sand between 0.05 and 2 mm diameter and Turface between 6 and 9 mm<br />

diameter. The six treatments were: brown Turface, green Turface, red Turface,<br />

brown sand, white sand, and black sand each uniformly applied to a depth of 3.2 mm in<br />

1.2 by 1.8 m plots. Starting July 19, 2007 weekly ratings were taken for percentage<br />

bermudagrass cover using a 100-grid count and by visual estimation. Prior to<br />

bermudagrass dormancy on October 10, 10-cm diameter core samples were removed<br />

from each plot, dried, and weighed to determine biomass of stolons and leaves.<br />

The percent change of cover based on the 100-grid count revealed that plots<br />

treated with white sand actually displayed equivalent or faster establishment rates<br />

compared to other topdressing materials. However, visual percentage bermudagrass<br />

cover ratings revealed that plots treated with green Turface displayed the fastest<br />

establishment rates. Discrepancies between grid counts and visual estimations<br />

probably occurred due to high contrast between turfgrass tissue and white sand<br />

compared to the low contrast between turfgrass tissue and green Turface. Lateseason<br />

biomass of ‘Patriot’ bermudagrass was equivalent regardless of topdressing<br />

color during establishment and extrapolates to a range between 3.3 and 4.1 kg per<br />

square meter. Thus, white sand does not appear to actually deter bermudagrass<br />

growth but does leave the viewer with the impression that the bermudagrass is thin.<br />

This psychological effect should be considered as it could be the difference between<br />

praise and retribution for field managers.<br />

29


SPRAY ADJUVANTS INFLUENCE BISPYRIBAC-SODIUM EFFICACY FOR ANNUAL<br />

BLUEGRASS CONTROL IN COOL-SEASON TURFGRASS. P.E. McCullough and S.E.<br />

Hart, Rutgers, The State University of New Jersey, New Brunswick.<br />

ABSTRACT<br />

Field and laboratory experiments were conducted in New Jersey to investigate<br />

the influence of spray adjuvants on foliar absorption and efficacy of bispyribac-sodium<br />

on annual bluegrass (Poa annua), creeping bentgrass (Agrostis stolonifera), and<br />

perennial ryegrass (Lolium perenne). In laboratory experiments on annual bluegrass,<br />

14 C-bispyribac-sodium applied without an adjuvant had 25% foliar absorption by eight<br />

hours after treatment while absorption increased to 45, 46, and 75% when applied with<br />

crop oil concentrate, nonionic surfactant, and methylated seed oil, respectively. In<br />

creeping bentgrass fairways, bispyribac-sodium at 37 g ai/ha with spray adjuvants<br />

controlled annual bluegrass similarly to 74 g ai/ha without adjuvants. In perennial<br />

ryegrass, treatments with methylated seed oil and nonionic surfactant required 25 and<br />

50% lower bispyribac-sodium rates, respectively, to obtain annual bluegrass control<br />

levels comparable to bispyribac-sodium rates without adjuvants. Spray adjuvants did<br />

not exacerbate turfgrass discoloration from bispyribac-sodium. Overall, spray adjuvant<br />

use with bispyribac-sodium may allow practitioners to reduce application rates and<br />

enhance efficacy for annual bluegrass control.<br />

30


PLANT GROWTH REGULATOR AND NITROGEN AFFECT SEASONAL<br />

CARBOHYDRATE PARTITIONING IN CREEPING BENTGRASS. D. Sarkar, P. C.<br />

Bhowmik, M. DaCosta, University of Massachusetts, Amherst.<br />

ABSTRACT<br />

The concentrations of total nonstructural carbohydrates (TNC) in plants serve<br />

several important functions. The quantification of TNC in turfgrass has proven valuable<br />

in investigations of assimilate translocation and physiological response of turfgrass to<br />

environmental and cultural factors. The major TNC found in turfgrass shoots consists of<br />

the monosaccharides, glucose and fructose, the disaccharide sucrose, various<br />

oligosaccharides of the β-2→6 linked polyfructosylsucrose type, starch, and long chain<br />

fructans. Seasonal variations of TNC in turfgrass roots and shoots determine their<br />

performance under stress conditions. Furthermore, TNC content can be influenced by<br />

different turfgrass management practices, such as nitrogen fertilization. However,<br />

limited information is available on the effects of N fertility on TNC of creeping bentgrass<br />

(Agrostis stolonifera L.) under putting green conditions. Trinexapac-ethyl (TE), a<br />

gibberellic acid synthesis inhibitor is a widely utilized plant growth regulator for<br />

improving putting green quality and performance. Some reports indicated improved<br />

performance of TE-treated turf under abiotic stress conditions, but physiological and<br />

biochemical mechanisms for improved stress tolerance is not clearly understood. The<br />

objectives of this study were to determine the effects of N fertilization and TE on total<br />

nonstructural carbohydrate partitioning of creeping bentgrass ('Penncross') under<br />

putting green conditions. The study was initiated in the spring of 2006 on a 4-yr old<br />

sand based putting green at Joseph Troll Turf Research Center, South Deerfield, MA.<br />

This experiment was arranged as a split-plot design, with nitrogen fertilization as the<br />

main plot (3, 5, and 8 lb N/1000 ft -2 year -1 ) and TE as the sub-plot (with and without TE)<br />

with four replications. Nitrogen was applied monthly from May to October, and TE<br />

(Primo ® Maxx) was applied (0.125 fl. oz/ 1000 ft -2 ) in three applications from April to<br />

August. Root and shoot samples were collected from each plot at 15-d intervals. Root<br />

and shoot samples were washed to remove soil and then oven dried (80º C) for 5 days.<br />

TNC were extracted from leaves and roots and the absorbance of the extract was<br />

measured at 515 nm using a spectrophotometer. Higher visual turf quality (8.5 to 9) was<br />

observed with increasing nitrogen rate throughout the growing season. Visual turf<br />

quality was also improved 3 to 8 days after the each application of TE. Detailed results<br />

of seasonal carbohydrate partitioning as affected by nitrogen and TE application will be<br />

presented.<br />

31


INFLUENCE OF BISPYRIBAC-SODIUM ON BROWN PATCH SEVERITY. A.I. Putman<br />

and J.E. Kaminski, University of Connecticut, Storrs.<br />

ABSTRACT<br />

Bispyribac-sodium (BPS) can be used to selectively remove annual bluegrass<br />

(Poa annua L) and roughstalk bluegrass (Poa trivialis L.) from creeping bentgrass<br />

(Agrostis stolonifera L.). Although unacceptable levels of yellowing often occurs<br />

following the application of BPS, tank-mixing BPS with iron + N products have been<br />

shown to reduce or mask this discoloration. In addition to the ability to selectively<br />

control undesirable weed species, BPS has also been shown to reduce the incidence of<br />

dollar spot caused by Sclerotinia homoeocarpa F.T. Bennett. Limited information,<br />

however, is available regarding the positive or negative effects of BPS on other<br />

common turfgrass diseases. The objective of this study was to assess the influence of<br />

BPS and BPS tank-mixed with an iron + N product on brown patch (Rhizoctonia solani<br />

Kuhns) in colonial bentgrass (Agrostis capillaris L.). This field study was conducted in<br />

2007 at the University of Connecticut Plant <strong>Science</strong> Research and Education Facility in<br />

Storrs, CT. In September 2006, an area was seeded to 'Allister' colonial bentgrass.<br />

Turf was mowed 3 times per week to a height of 0.5 inches. Bispyribac-sodium was<br />

applied twice at 30 g ai/A or three times at 20 or 30 g ai/A. The aforementioned<br />

treatments were applied alone or in combination with Lesco’s 12-0-0 Chelated Iron Plus<br />

Micronutrients (Fe + N at 6.0 oz/1000 ft 2 ). All treatments were applied at 44 gpa using a<br />

CO 2 pressurized (40 psi) sprayer equipped with a flat-fan nozzle. Treatments were<br />

applied on 10 and 24 July and 7 August. Plots measured 3 ft x 6 ft and were arranged<br />

in a randomized complete block with 4 replications. Brown patch severity was visually<br />

rated on a percent scale in which 0 = no brown patch symptoms visible and 100 = entire<br />

plot area affected by R. solani.<br />

Trace levels of brown patch were observed when treatments were initiated on 10<br />

July. One week after treatment (WAT), brown patch severity was greater in plots<br />

receiving only BPS (19 to 25%), when compared to the untreated control (11%). By 24<br />

July (2 WAT), all plots treated with BPS and BPS tank-mixed with Fe + N plots generally<br />

had greater levels of brown patch when compared to the untreated control. Brown<br />

patch severity peaked approximately 2 weeks after the second application of BPS (6<br />

August). On 6 August, all BPS treatments contained between 23 and 34% brown patch<br />

and few differences existed among BPS treatments. All BPS treatments, however, had<br />

significantly greater levels of brown patch on 6 August when compared to the untreated<br />

control (11%). On 21 August, brown patch was greatest in plots receiving 3 applications<br />

of BPS or BPS tank-mixed with Fe + N at 30 g ai/A. Treatments in which BPS or BPS<br />

tank-mixed with Fe + N was applied twice or applied three times at 20 g ai/A had brown<br />

patch levels similar to the untreated control on 21 August. Results from this field study<br />

suggest that BPS may increase the severity of brown patch on highly susceptible<br />

turfgrass species such as colonial bentgrass and additional chemical management<br />

strategies may be necessary to adequately suppress disease symptoms.<br />

32


THE POTENTIAL USE OF VINEGAR AS A BANDED APPLICATION, DIRECTED AT<br />

THE BASE OF TRANSPLANTED PEPPERS AND BRUSSEL SPROUTS. G.J. Evans<br />

and R.R. Bellinder, Cornell University, Ithaca NY.<br />

ABSTRACT<br />

Vinegar (acetic acid) may aid in weed control. Vinegar works on contact to burn<br />

back exposed plant parts. Two limitations to its use in vegetable crops are: 1) injury to<br />

the crop, and; 2) the cost of the high volume needed for adequate weed control.<br />

Directed applications of vinegar below a crop canopy could minimize product contact<br />

with the crop. Banded vinegar applications in-row, coupled with between-row<br />

cultivation, could reduce product usage and expense. Field trials were conducted in<br />

2007 using 200-grain vinegar (20% acetic acid), at 68 GPA, in transplanted bell peppers<br />

and brussel sprouts. Treatments were applied as 10-in wide bands, centered on each<br />

crop row. Applications were made with a customized tractor-mounted sprayer, with<br />

nozzles oriented below, and to each side, of the crop canopy. This sprayer was fixed<br />

onto an S-tine cultivator to allow for simultaneous in-row spraying and between-row<br />

cultivation. Vinegar treatments were compared to between-row cultivation, betweenrow<br />

cultivation with in-row handweeding, and a weedy check. Applications were made<br />

to pepper varieties ‘Ace’ and ‘Lipstick’ either 27 or 33 days after transplanting. <strong>Weed</strong>s<br />

in the early and late treatments were, on average, at the 2-leaf or the 4-leaf stage,<br />

respectively. Initial injuries to the peppers 2 days after treatment (DAT) were less than<br />

10%, and included lower leaf dieback and scarring of the stem. However, by 29 DAT,<br />

the early injury to the stem facilitated a basal rot and subsequent death of a number of<br />

pepper plants. Yields were significantly reduced in both vinegar treatments.<br />

Applications were made to brussel sprouts ‘Oliver’ at either 28 or 34 days after<br />

transplanting. Injury was greater in the early vinegar application (43%, 2 DAT). An<br />

uneven soil surface and a small margin between the height of the sprayer nozzles and<br />

the height of the plants contributed to increased spray contact on the brussel sprouts.<br />

By the late application, the height differential between the sprayer nozzles and the plant<br />

apexes had increased, and only the lowest leaves were injured (10%, 2 DAT). Yields in<br />

both vinegar treatments were not significantly different from the handweeded treatment.<br />

In both crops, 2 days after the early application of vinegar, there was an 88% reduction<br />

in the number of in-row weeds present, relative to the weedy check. The later<br />

application of vinegar reduced the number of weeds in both crops by greater than 74%.<br />

By 15 DAT, the number of weeds in the early vinegar-in-pepper treatment was still 82%<br />

less than the weedy check. In comparison, 15 days after weeding the handweeded<br />

pepper treatment, there remained only a 47% reduction in the number of in-row weeds.<br />

Vinegar can provide adequate weed control and may offer a longer window of<br />

suppression than handweeding. However, crop injury remains an issue. Directed<br />

applications around more mature plants, particularly tough-stemmed plants like brussel<br />

sprouts, may reduce crop injury to tolerable levels. The use of spray shielding may also<br />

limit crop injury.<br />

33


TOLERANCE OF BUTTERNUT SQUASH TO PREEMERGENCE AND<br />

POSTEMERGENCE APPLICATIONS OF HALOSULFURON-METHYL. J. Wright, M.A.<br />

Isaacs, M.J. VanGessel, Q.R. Johnson, B.A. Scott, University of Delaware,<br />

Georgetown, H.P. Wilson, Virginia Tech, Painter.<br />

ABSTRACT<br />

A field study was conducted in 2007 at the University of Delaware Research and<br />

Education Farm, located in Georgetown, DE. The objective was to determine the<br />

tolerance of butternut squash (Cucurbita moschata) to PRE and POST applications of<br />

halosulfuron-methyl at selected rates. PRE application rates of halosulfuron-methyl<br />

included 0.0234 lb ai/A, 0.047 lb ai/A, and 0.094 lb ai/A. POST applications of<br />

halosulfuron-methyl also contained the aforementioned rates, but were also applied with<br />

0.25 % v/v nonionic surfactant. A randomized factorial design containing four<br />

replications was implemented, with the factors being halosulfuron-methyl rate,<br />

application timing, and butternut squash variety. Plots were 15 feet wide by 50 feet<br />

long. Two rows were centered in each plot, one containing Atlas butternut squash and<br />

the other containing Betternut butternut squash. Rows were planted with a Monosem<br />

planter 5 feet apart with approximately 36 inch seed spacing. To minimize weed<br />

competition or injury to butternut squash, a PRE application of ethalfluralin and<br />

clomazone (Strategy 2.5 pt/A) was applied. Cultivation and hoeing were performed in<br />

efforts to maintain the study as "weed-free" as possible, and plots were irrigated. Also,<br />

POST applications of mefenoxam and chlorothalonil were made weekly for disease<br />

control. All treatments were applied using a tractor-mounted sprayer with compressed<br />

air at 29 PSI and a spray volume of 25 GPA. PRE applications were applied one day<br />

after planting, and POST applications at the 10 to 12 leaf stage of squash (27 days after<br />

planting). Data collected included percent visual injury (stunting and overall biomass<br />

reduction) and yields number of squash and weights).<br />

Squash injury from PRE applications were rated 21, 28, 35, 42, 49, and 56 days<br />

after treatment (DAT). As expected, both the A and B squash varieties responded with<br />

progressively higher injury with increasing halosulfuron-methyl rates. Halosulfuronmethyl<br />

at 0.0234 lb ai/A, 0.047 lb ai/A, and 0.094 lb ai/A caused the following injury:<br />

variety A had 45, 65, and 80% injury 21 DAT and 12, 30, and 65% injury 56 DAT,<br />

respectively; variety B had 55, 56, and 83% injury 21 DAT and 14, 25, and 66% injury<br />

56 DAT, respectively. POST applications resulted in less injury than PRE and were<br />

rated 8, 15, 22 and 29 DAT. The same halosulfuron-methyl rates applied POST caused<br />

the following injury: variety A had 16, 29, and 44% injury 8 DAT and 1, 9, and 14%<br />

injury 29 DAT, respectively; variety B had 21, 35, and 50% injury 8 DAT and 4, 14, and<br />

15% injury 29 DAT, respectively. These results indicate that the squash were able to<br />

recover from early season herbicide injury. The number of squash harvested per plot<br />

did not significantly differ for any of the treatments for variety A; however, the total<br />

weight (wt)/plot and average wt/squash differed significantly based on herbicide rate<br />

alone. For variety B, # squash/plot significantly differed based solely on application<br />

timing, yet total wt/plot and avg. wt/squash were significantly different due to both<br />

halosulfuron-methyl rate and application timing.<br />

34


THE INFLUENCE OF SMALL-SCALE ENVIRONMENTAL FACTORS ON SUCCESS<br />

OF JAPANESE STILTGRASS. A.N. Nord* and D.A. Mortensen, Penn State University,<br />

University Park.<br />

ABSTRACT<br />

Most studies of invasive species consider only later stages of successful<br />

invasions. However, much insight into what fosters a successful invasion can be gained<br />

by monitoring the initial stages. Thirty patches of the invasive annual Japanese<br />

Stiltgrass (Microstegium vimineum) were planted in four habitats within a forested<br />

landscape in central Pennsylvania in 2003. Recruitment, seed production, and spatial<br />

spread were quantified in each patch until they were eradicated in July 2006. In general<br />

patches in the roadside habitat expanded most, while most populations under intact<br />

forest canopy declined. Wet meadow and disturbed forest habitats were intermediate.<br />

However, these differences were not statistically significant due to extremely high<br />

within-habitat variation in growth rates. Environmental measurements taken at each<br />

plot early in the experiment and repeated in the final year are being used in an attempt<br />

to explain this variability. Results suggest that small-scale environmental factors such<br />

as available light and soil chemistry have a large impact on the success of Japanese<br />

stiltgrass. Changes in population growth trajectories in response to small-scale<br />

environmental changes imply that habitat susceptibility to invasion by this species is not<br />

static.<br />

35


ROLLING RYE FOR WEED SUPPRESSION IN NO-TILL SOYBEANS. R. Mick, W.S.<br />

Curran, and S. Duiker. Penn State University, University Park.<br />

ABSTRACT<br />

A roller/crimper is used to manage cereal rye cover crops. The roller/crimper<br />

consists of a hollow drum with flat, blunt blades that crush plant's vascular tissue. The<br />

rolled cover crop lays flat upon the soil surface creating a uniform mat that can act as a<br />

suppressive barrier to weeds similar to any surface mulch. In this study, we compared<br />

weed suppression from rolling rye along with a burn-down herbicide to rolling along with<br />

a burn-down plus postemergence glyphosate application. This was done across two<br />

different planting dates (early and late) at two locations in Pennsylvania. For early and<br />

late plots, ‘Aroostook’ rye was drilled in late September at 157 kg/ha and burned-down<br />

with glyphosate (0.84 kg ae/ha) the following spring. A no-rye treatment was included<br />

for comparison. One to two days after burn-down the plots were rolled with a<br />

roller/crimper and planted to soybeans. Six weeks after planting the postemergence<br />

herbicide was applied. <strong>Weed</strong> counts were taken 4, 6, 8 and 10 weeks after planting and<br />

at 10 weeks weed biomass was collected from each plot. Soybean grain yield was<br />

collected from each plot in early to mid October.<br />

Total weed biomass was the greatest where no rye was planted. Using a burndown<br />

herbicide resulted in a ten-fold decrease in weed biomass compared to no rye. A<br />

second herbicide application further reduced weed biomass. Rolling and planting later<br />

may allow a producer to omit the postemergence herbicide application. This study will<br />

be repeated another field season and an economic cost/benefit analysis will be done to<br />

confirm findings.<br />

36


MANIPULATION OF SOIL NITROGEN LEVELS AND ITS EFFECTS ON WEED VIGOR<br />

AND FECUNDITY. S.E. Whitehouse, A. DiTommaso, and C.L. Mohler - Cornell<br />

University, Ithaca, NY.<br />

ABSTRACT<br />

Velvetleaf (Abutilon theophrasti), common lambsquarters (Chenopodium album),<br />

and giant foxtail (Setaria faberi) are three weed species which plague conventional and<br />

organic field grain farms alike in the Northeastern region of the United States. Growers<br />

employ a number of mechanical, chemical, and biological strategies to manage the<br />

impact these species have on crop loss. Manipulation of the available nitrogen and<br />

carbon: nitrogen ratios in the soil environment may be used as a possible method for<br />

weed control. The primary objectives of this experiment were (1) to document the<br />

growth, vigor, and fecundity of velvetleaf, common lambsquarters, and giant foxtail at<br />

three different nitrogen levels, and (2) to characterize the plasticity of the three species<br />

in various competition environments. We hypothesized that (1) with greater nitrogen<br />

availability, weed vigor and fecundity increase, and (2) weeds grown in weed-only<br />

environments demonstrate significant increases in vigor. Sections of a maize field were<br />

divided into three replicates using a randomized block design, each with three nitrogen<br />

fertilization treatments (0/15/50 kg/ha) and seven varying plant environments for each<br />

weed species (maize-only, weed-only, mixed stand). Hand-sown weed densities of 15<br />

plants / m 2 were observed in 2007. Initial statistical analyses demonstrated significant<br />

differences in height compared to nitrogen levels for velvetleaf and common<br />

lambsquarters in weed-only communities. Giant foxtail showed opposite results, with<br />

significant differences in height for mixed stand communities. However, conclusions<br />

may change when final weed biomass and seed production rates are analyzed and<br />

compared to height measurements and nitrogen levels. Further study of the growth and<br />

vigor of these species will continue in 2008, with possible investigation into the<br />

presence of pathogens.<br />

37


ORGANIC AND CONVENTIONAL WEED MANAGEMENT EFFICACY AND STABILITY<br />

IN A LONG-TERM CROPPING SYSTEM TRIAL. M.R. Ryan, D.A. Mortensen, W.S.<br />

Curran, Penn State University, University Park, R. Seidel, P.R. Hepperly, The Rodale<br />

Institute, Kutztown, PA, and J.R. Teasdale, USDA-ARS Beltsville, MD.<br />

Effective weed suppression can be achieved without the use of herbicides<br />

through strategic ecologically-based weed management. However, organic farmers<br />

have repeatedly stated that weed management is their primary production constraint as<br />

efficacy of organic weed management is often more variable than herbicide-based<br />

methods. Long-term studies are essential to assess the magnitude and source of<br />

variation in weed management efficacy and to quantify the effects of reduced efficacy in<br />

“poor” weed control years on crop yield and weed population trajectories. The Rodale<br />

Institute Farming Systems Trial (FST) was initiated in 1981, and provides a unique<br />

twenty-six year history of conventional and organic corn (Zea mays L.) and soybean<br />

[Glycine max (L.) Merr.] production and associated weed management. In this analysis,<br />

we used weed biomass in corn and soybean to define weed management efficacy.<br />

<strong>Weed</strong> biomass variation was greatest in organically managed corn and soybean and<br />

was sensitive to environmental stochasticity, specifically to fluctuations in rainfall timing<br />

and amount. <strong>Weed</strong> management efficacy was more stable and consistently high in the<br />

conventional system. Although corn yields were significantly higher in the single<br />

conventional system at the onset of the trial, within four years corn yields in the two<br />

organic systems equaled or exceeded conventional corn despite weed biomass<br />

averaging 6 times higher in organic corn. These results suggest that organically grown<br />

corn is well buffered in years of “poor” weed control and offers hope that further<br />

improvements in weed management could significantly increase organic corn yields.<br />

Although initially higher, organic soybean yield decreased to levels lower than<br />

conventional soybean. The result demonstrates the need for careful planning when<br />

developing an integrated cropping system to limit the negative effects of “poor” years<br />

when growing weed intolerant crops such as soybean.<br />

38


WEEDS, ETHANOL, AND DISAPPEARING BEES; TALES OF LANDSCAPE<br />

BIODIVERSITY. N.B. DeBarros, Penn State University, University Park.<br />

ABSTRACT<br />

Growing concerns over global climate change and dependence on foreign oil<br />

have sparked national interest in biofuels. Increased demand for agricultural land could<br />

have a significant impact on current landscapes, as field margins, woodlots, and forests<br />

are cleared to maximize crop production. Homogenization of the agricultural landscape<br />

in the Northeast could facilitate weed dispersal while negatively impacting local<br />

biodiversity and the ecological services provided by non-crop areas. In particular, native<br />

pollinator populations which are already on the decline may be further affected by<br />

habitat and resource loss. Existing literature on these topics will be summarized and<br />

their implications will be explored in a model-in-progress. In addition, proposed research<br />

on habitat management within farming systems will be addressed.<br />

39


IS IT TIME TO RELINQUISH ATRAZINE IN CORN? W.S. Curran, Penn State<br />

University, University Park.<br />

ABSTRACT<br />

Atrazine use continues to be controversial in agro-ecosystems. US corn<br />

producers rely heavily on the atrazine where it is ranked the second most widely used<br />

pesticides in the US after glyphosate. Atrazine continues to be detected in surface and<br />

ground water and was detected most frequently in aquifers underlying agricultural<br />

regions in studies conducted nationwide. Atrazine has more recently been linked to<br />

reduced amphibian fitness from hermaphrodism, increased susceptibility to infection,<br />

and overall reduced survivorship at ecologically relevant doses. Most notably, the<br />

triazine family of herbicides has been linked to growth inhibition and developmental<br />

anomalies in amphibians, mammals, and fish and has been identified as an endocrine<br />

disruptor. There is special concern since herbicide applications in the spring or early<br />

summer also coincide with amphibian breeding periods and have been related to the<br />

global amphibian population declines. Finally, atrazine along with the other triazines<br />

has been subject to resistance development and in corn/soybean systems in the<br />

Northeast, resistance to the triazine herbicides is quite prevalent. Do these negatives<br />

offset the advantages of this long-time corn herbicide standard and is it time to<br />

relinquish atrazine in corn?<br />

In 2006 and 2007, field trials were established in Pennsylvania examining the<br />

effectiveness of herbicide programs for corn. These programs examined both atrazine<br />

containing and non-atrazine based programs. <strong>Weed</strong> species included velvetleaf,<br />

common ragweed, common lambsquarters, giant foxtail, and yellow nutsedge. Nonatrazine<br />

alternatives included mesotrione, isoxaflutole, flumetsulam, rimsulfuron,<br />

halosulfuron, several plant growth regulators, and glyphosate. The results from these<br />

two trials showed that commercially acceptable weed control can be achieved both with<br />

soil applied programs and with two-pass programs that do not include atrazine. <strong>Weed</strong><br />

species prevalence certainly will help determine the effectiveness of the program. In<br />

addition, with any assessment, a complete economic analysis should be included that<br />

also considers environmental and ecological implications. In the end, atrazine use<br />

could be more limited to those areas not deemed sensitive and appropriate use<br />

restrictions imposed in areas with greater risk. Is it our responsibility as scientists and<br />

as an industry to ensure that we do not encourage the use of pesticides that have<br />

demonstrated negative performance, especially when acceptable alternatives exist?<br />

*Specific literature citations have been omitted due to page limitations, but are available<br />

from the author upon request.<br />

40


LOOKING FOR POSTEMERGENCE SOLUTIONS TO TRIAZINE RESISTANCE<br />

WEEDS IN POTATOES. J.M. Jemison, Jr., P. Sexton, University of Maine Cooperative<br />

Extension, Orono, and L. Titus, Ag Matters Consulting.<br />

ABSTRACT<br />

Throughout the potato production areas of Maine, triazine resistance is<br />

developing in broadleaf weeds, particularly lambsquarters (Chenopodium album L.).<br />

Metribuzin has long been a standard for broadleaf weed control in potato production.<br />

Despite the fact that potatoes are produced in a given field no more than one year in<br />

two (frequently one year in three), the intense mechanical cultivation and hilling, and<br />

that the most common rotation crop does not generally receive a triazine based<br />

herbicide, triazine resistant (TR) lambsquarters is becoming increasingly problematic to<br />

potato producers in Maine.<br />

While other broadleaf herbicides are available for potatoes, many growers may<br />

not know they have resistant weeds and use metribuzin anyway. We found producers<br />

in 2007 that had used alternative herbicides but still needed a postemergence material<br />

to control TR lambsquarters. There are no good materials available to control TR<br />

lambsquarters postemergence.<br />

A study was initiated in 2007 to study whether the addition of 2,4-D to Matrix ®<br />

(rimsulfuron) would provide improved control of TR lambsquarters. The farm where the<br />

trial was conducted was located in Corinna, Maine in the Central Maine potato<br />

production area. Herbicide combinations included applied Matrix at either 1 or 1.5 oz/ac<br />

with either 1.25, 2.5 or 5 oz/ac of 2,4-D and nonionic surfactant added at 0.25% v/v.<br />

We took weed ratings and apparent crop injury ratings at 7 and 14 days after treatment.<br />

Yield samples were taken from 15 feet of row. Potatoes were graded and rated for skin<br />

set and specific gravity.<br />

We found significant differences in the level of crop injury in the second rating (14<br />

DAT) between the 5 oz/ac application rate and the 2.5 oz rate. It did not affect yield but<br />

some leaf curling/cupping was noted. Differences were also found in lambsquarters,<br />

annual grass, and mustard control between those receiving 2,4-D and the control. No<br />

significant differences were found in US. No 1 or total potato yield, skin set or in specific<br />

gravity ratings. Yields averaged between 260 and 300 ctw/ac for this numbered Frito<br />

Lay variety. Use of 2,4-D postemergence in potato production appears to be an<br />

effective way to control TR lambsquarters. No yield reduction was seen, and only slight<br />

leaf injury was noted. More work is needed with other varieties to see if there are any<br />

other issues with this herbicide combination.<br />

41


ALS- AND ACCASE-RESISTANT ITALIAN RYEGRASS IN WESTERN NORTH<br />

CAROLINA. J.B. Beam and A.C. York, North Carolina State University, Lincolnton and<br />

Raleigh, NC.<br />

ABSTRACT<br />

Herbicide resistance in weeds has become more prevalent as farmers rely more<br />

on herbicides and less upon tillage and other means to control weeds. Herbicide<br />

resistance in Italian ryegrass (Lolium multiflorum Lam.) has been reported in Chile,<br />

France, Italy, the United Kingdom, and seven states in the United States<br />

(www.weedscience.org). Italian ryegrass resistant to diclofop (Hoelon) and<br />

sethoxydim was reported in western North Carolina in 1990. Resistance is now<br />

widespread in the state. For a number of years, growers used the ALS-inhibiting<br />

herbicides chlorsulfuron plus metsulfuron (Finesse) to suppress diclofop-resistant<br />

ryegrass. Mesosulfuron (Osprey), another ALS inhibitor, was registered in 2006 and<br />

is now widely used to control diclofop-resistant ryegrass. Pinoxaden (Axial), an<br />

ACCase inhibitor that sometimes controls diclofop-resistant ryegrass, was registered in<br />

2006. Growers in Lincoln and Union counties in North Carolina began reporting control<br />

failures with mesosulfuron and pinoxaden in the spring of 2007. Seed collected from<br />

eight fields were planted in greenhouse along with seed from a field with no history of<br />

any herbicide applications to ryegrass and another field where mesosulfuron worked<br />

very well. Plants were screened for response to pinoxaden, diclofop, and mesosulfuron<br />

applied at 0.25 to 32X rates. Ryegrass from Lincoln and Union counties survived 32X<br />

rates of mesosulfuron and diclofop and 8X rates of pinoxaden. This is the first report of<br />

mesosulfuron-resistant ryegrass in the United States and the first report of multiple<br />

herbicide resistance in North Carolina.<br />

42


HALEX GT: NEW POSTEMERGENCE HERBICIDE FOR GLYPHOSATE<br />

TOLERANT CORN. G.D. Vail and C.M. Moseley, Syngenta Crop Protection,<br />

Greensboro, NC.<br />

ABSTRACT<br />

Halex GT is the latest product in the Callisto ® Plant Technology family of<br />

herbicides. Halex GT is a new post-emergence corn herbicide specifically designed for<br />

glyphosate tolerant (GT) corn that provides the convenience of a one-pass, postemergence<br />

glyphosate program that also includes residual weed control. Halex GT<br />

was developed for growers committed to a total post-emergence weed control program.<br />

Five years of product development has demonstrated that Halex GT can deliver<br />

higher corn yield versus one application of glyphosate and equal or higher yield versus<br />

two applications of glyphosate. Because Halex GT controls emerged weeds and<br />

provides residual weed control, it is more flexible and effective than glyphosate alone.<br />

43


HALEX GT WEED CONTROL IN GLYPHOSATE TOLERANT CORN. R.D. Lins, B.R.<br />

Miller, B.D. Black, Syngenta Crop Protection, Greensboro, NC.<br />

ABSTRACT<br />

Halex GT is a new post-emergence corn herbicide specifically designed for<br />

glyphosate tolerant (GT) corn that provides the convenience of a one-pass, postemergence<br />

glyphosate program plus residual weed control. It combines the active<br />

ingredients mesotrione, s-metolachlor and glyphosate into a unique product with<br />

excellent crop safety that controls tough grass and broadleaf weeds in corn. The target<br />

use rate of 2.21 to 2.46 kg ai/H (3.6 to 4 pt/acre) controls the most important weeds<br />

including those that have developed resistance to glyphosate, triazine or ALS-inhibiting<br />

herbicides. Halex GT will require the addition of a nonionic surfactant (NIS) for<br />

optimal weed control. Halex GT can be tank mixed with atrazine for added broadleaf<br />

weed control or when glyphosate resistant broadleaf weeds are present or suspected.<br />

The mixture of active ingredients in Halex GT when tank mixed with atrazine provides<br />

an effective glyphosate resistance management strategy in GT corn.<br />

44


FALL BURNDOWN: DOES IT HAVE A FIT IN DELAWARE. M.J. VanGessel, Q.R.<br />

Johnson, and B.A. Scott, University of Delaware, Georgetown.<br />

No-till crop production has been popular in Delaware for a number of years.<br />

Typically, a non-selective herbicide is applied in the spring prior to planting to kill<br />

existing vegetation and provide a weed-free field at or shortly after planting. However, it<br />

is difficult to apply all non-selective treatments in a timely fashion in most springs, and<br />

as a result farmers are trying to control large winter annual weeds with higher herbicide<br />

rates and multiple herbicides tank mixed in combination. Fall herbicide applications are<br />

one approach to controlling weeds when they are small and lessen the spring workload.<br />

This will require a residual herbicide to increase the likelihood that the field is weed-free<br />

at planting time. At least 12 trials have been conducted in Delaware since 2002<br />

examining various herbicides for utility in a fall application approach with no-till<br />

production programs. Replicated small-plot research has examined glyphosate,<br />

paraquat, 2,4-D and dicamba for control of existing vegetation. Chlorimuron (alone or in<br />

combination with various prepackage mixtures), cloransulam, flumioxazin, metribuzin,<br />

simazine, sulfentrazone, and tribenuron have all been evaluated in at least three trials.<br />

The most common species evaluated include horseweed, field pansy, cress species,<br />

common chickweed, mouseear chickweed, and henbit or deadnettle.<br />

The residual herbicides included in these trials typically do not provide adequate<br />

control of emerged vegetation, and including only dicamba or 2,4-D often does not<br />

provide commercially acceptable control. The addition of paraquat or glyphosate is<br />

needed to provide effective control of emerged vegetation. Due to the size and<br />

susceptibility of weeds at time of fall application, reduced rates of glyphosate or<br />

paraquat provided excellent control. Chlorimuron plus tribenuron (at 0.04 lb ai/A) and<br />

simazine (1 lb ai/A) have provided the most consistent broad-spectrum weed control.<br />

Herbicide-resistance management is a concern with fall herbicide applications<br />

utilizing long residual products (particularly Group 2). The lack of a crop canopy<br />

intensifies selection pressure. Coupled with the fact that the most widely used<br />

herbicides in small grains are also Group 2, resistance management is important to the<br />

long-term utility of this approach.<br />

45


IR-4 AND ORNAMENTAL HORTICULTURE IN THE NORTHEAST. E. L. Lurvey,<br />

Northeast Region IR-4 Program, Cornell University, Geneva, NY.<br />

The mission of the IR-4 Program is to provide data in support of the registration<br />

of pest management tools for minor/specialty crops, including ornamental horticulture.<br />

Over the last few years, the process has been refined in order to more effectively focus<br />

our research. The emphasis has changed from individual chemical/crop combinations<br />

to specific pest/weed problems, then working on the solutions. The important<br />

pest/weed problems are identified, in part, with the use of survey available on the<br />

website (http://ir4.rutgers.edu/ornamentals.html), as well as hard copies distributed at<br />

meetings and conventions. Final decisions on research projects will be made every two<br />

years at an IR-4 Ornamental Horticulture Workshop. It is important, therefore, to work<br />

with me, your IR-4 Regional Coordinator for the Northeast, to insure that projects of<br />

importance you are selected for research. Contact information: Edith Lurvey, Tel. No.<br />

315-787-2308; E-mail ell10@cornell.edu.<br />

46


COMPETITION FROM BLACK COTTONWOOD IN NURSERY CONTAINERS. J.E.<br />

Altland, USDA/ARS, Application Technology Research Unit, Wooster, OH.<br />

ABSTRACT<br />

Cottonwood species (Populus spp.) are weedy in container nursery production<br />

throughout much of the U.S. Cottonwood species vary throughout the country, with<br />

black cottonwood (Populus trichocarpa Torr. & Gray) predominating Oregon and other<br />

parts of the Pacific Northwest U.S. Cottonwood release seed in early summer. After<br />

landing in a suitable environment, cottonwood seed germinate in 8 to 24 hours.<br />

Cottonwood can grow 6 to 8 ft in a single season with sufficient resources. The<br />

objective of this research was to document competition from one or more black<br />

cottonwood seedlings on growth of two common nursery shrubs.<br />

On May 15, 2006, hydrangea [Hydrangea macrophylla (Thunb.) Ser. ssp. serrata<br />

(Thunb.) Makino 'Nikko Blue'] and holly (Ilex x meserveae S. Y. Hu ‘Blue Girl’) were<br />

potted into #1 containers filled with 100% Douglas fir [Pseudotsuga menziesii (Mirbel)<br />

Franco] bark amended with 9.5 kg/m 3 Apex 18-6-12, 3.0/m 3 kg of dolomitic lime, and 0.9<br />

kg/m 3 Micromax micronutrients. Containers were placed on a wagon and moved<br />

beneath a mature black cottonwood tree in order to collect falling seed. The wagon was<br />

moved daily to the nursery production site and irrigated, then returned to beneath the<br />

tree. On June 5, containers were moved to the nursery production site and remained<br />

there until the conclusion of the experiment. The number of seedlings in each container<br />

was thinned to 0, 1, 3, or 5 seedlings, with three single plant replications per treatment<br />

and shrub species. On August 8, containers were irrigated thoroughly to saturation.<br />

Containers were weighed just after saturation, and then again 3, 6, and 24 hours after<br />

saturation. Percent water loss from the time of saturation was calculated (Table 1). On<br />

September 21, cottonwood and shrubs were harvested for shoot dry weight (SDW).<br />

Data were analyzed with repeated measures analysis of variance and means were<br />

separated with Tukey’s honest significant difference test.<br />

Water loss in holly and hydrangea was affected by an interaction between<br />

cottonwood seedling number and time, indicating different water loss response over<br />

time depending on the number of seedlings present. Among both species, water loss<br />

increased linearly with increasing number of cottonwood seedlings. By 24 hours, water<br />

loss in hydrangea and holly growing among five cottonwood seedlings was almost three<br />

times as much as those growing without cottonwood. By the conclusion of the study,<br />

SDW of poplar was similar regardless of whether 1, 3, or 5 seedlings were allowed to<br />

grow. This suggests that the #1 container (approximately 2.7 L) limited poplar growth<br />

such that one seedling grew equally large as five seedlings. Among holly, only 5<br />

seedlings reduced SDW compared to containers with no seedlings; however, contrast<br />

analyses (not shown) revealed that SDW of holly was less with 1, 3, or 5 seedlings<br />

compared to containers with no seedlings (p = 0.0683). Hydrangea SDW was reduced<br />

with either 1, 3, or 5 seedlings. These data demonstrate the competitive effects of<br />

cottonwood on water availability and growth of containerized nursery crops, especially<br />

those growing in small (#1 containers) with limited soil volume.<br />

47


EFFICACY AND PERSISTANCE OF GROWTH REGULATORS APPLIED TO<br />

ROOTED CUTTINGS OF TWO CULTIVARS OF RHODODENDRON BEFORE<br />

POTTING. S. Barolli, Imperial Nurseries, Granby, CT.<br />

ABSTRACT<br />

In growing rhododendrons, trimming and pinching take many hours of labor.<br />

Producing well branched, compact plants with plant growth regulators (PGR) could<br />

greatly reduce production costs. Previous studies have shown that certain PGR can<br />

greatly affect stem length and branching of rhododendron. We experimented on two<br />

cultivars of Rhododendron: 'Roseum Elegans’ and ‘PJM’ using GR on 2.5-inch cells of<br />

fully rooted cuttings taken in October 2006.<br />

For each application we treated 20 plants in each of four replications. There were<br />

a total of 16 treatments including 2 untreated. They included drenches and sprays,<br />

some early and some just before potting. For drenching, approximately 30 ml of solution<br />

was used for each cell by dipping the flat in a container for 20 seconds. The sprays<br />

were applied with a backpack spray at 60 gal/A, two passes, with an XR-8004-VS<br />

nozzle. The early applications were: 1) Untreated; 2) Bonzi ® (paclobutrazol) applied as<br />

a drench at 4 ppm; 3) Bonzi ® -10 ppm-drench; 4) Atrimmec ® (dikegulac-sodium )-spray<br />

20 ml/L; 5) Atrimmec-40 ml/L-spray; 6) Florel ® (ethephon)-spray 8 oz/gal; 7) Florel ® -16<br />

oz/gal-spray; 8) Bonzi ® - drench 4 ppm+Atrimmec ® -spray 20ml/L; 9) Bonzi ® -drench 4<br />

ppm+Atrimmec ® -spray 40 ml/L; 10) Bonzi ® -drench 4 ppm+Florel ® -spray 8 oz/gal; 11)<br />

Bonzi ® - drench 4 ppm+ Florel ® -spray 16 oz/gal; 12) cyclanilide 112 ppm+Surfix ®<br />

0.1oz/gal and 13) cyclanilide 223ppm+Surfix ® (-beta pinene polymer- nonionic spray<br />

adjuvant) 0.1 oz/gal as sprays. Number (12) and (13) were re-applied after one month.<br />

Bonzi ® treatments were applied on April 3rd and all the sprays on April 10th. ‘Roseum<br />

Elegans’ was not trimmed before treatment and did not have new growth. The PJMs<br />

were lightly trimmed 10 days prior to treatment and were actively growing. The two<br />

cultivars were kept in separate greenhouses. The later applications were on June 14th<br />

on finished liners: 14) Untreated; 15) the same as Bonzi ® #2 and 16) the same as<br />

Bonzi ® #3. At this point ‘Roseum Elegans’ had been trimmed twice and the ‘PJM’ three<br />

or more times. All other growing procedures were done as in normal practice.<br />

On June 19, 10 liners from each treatment were potted into 2 gal pots, replicated<br />

four times. Before potting all but the Bonzi ® treated rhododendron ‘Roseum Elegans’,<br />

were cut back because they were too tall. All plants were held to evaluate effects on<br />

growth, branching and flower buds. Measurements on number and length of branches<br />

and length of plants were taken in the flats and after potting. Injury rated on a 0 to 10<br />

scale.<br />

Only high rates of Atrimmec ® (5) and (9) caused early injury and these plants<br />

recovered later. Treatments (5) and (9) also caused the most branching. Growth<br />

reduction was the best with Bonzi ® (3), (16), (15), (8) and (9) and these effects persisted<br />

after potting. All others did not reduce growth significantly. All Bonzi ® treatments<br />

significantly increased the number of flower buds. Increased branching was also<br />

observed in the flats but no further effects were observed after potting.<br />

Further evaluation is needed of rates and timing of Bonzi ® and Atrimmec ® to<br />

ascertain that growth reduction does not persist into the 2nd season.<br />

48


DIMETHENAMID-P: A NEW ACTIVE INGREDIENT FOR PREEMERGENCE WEED<br />

CONTROL IN PRODUCTION ORNAMENTALS. C.A. Judge, K.M. Kalmowitz, and J.<br />

Zawierucha, BASF Corporation, Research Triangle Park, NC.<br />

ABSTRACT<br />

Dimethenamid-P is being developed for preemergence control of annual grasses,<br />

small-seeded broadleaves, and sedges in ornamentals. Dimethenamid-P is a<br />

chloroacetamide herbicide absorbed by emerging grass shoots and broadleaf shoots<br />

and roots controlling susceptible weeds as they germinate. Field container research<br />

trials have been implemented across the US to evaluate weed control and crop safety<br />

with a 1.75% combination granule containing dimethenamid-P (0.75%) and<br />

pendimethalin (1%) with the trade name FreeHand 1.75G. Research has indicated that<br />

in addition to the weeds controlled by pendimethalin such as annual bluegrass,<br />

crabgrass, chickweeds, spurge sp., and woodsorrel, the combination product provides<br />

additional control of weeds such as common groundsel, doveweed, eclipta, hairy<br />

bittercress, galinsoga, phyllanthus sp., liverwort, and sedges. Six to 10 weeks of<br />

residual weed control in container ornamental production has been observed from<br />

application rates ranging from 1.9 to 3.9 kg ai per ha. Furthermore, good crop tolerance<br />

has been observed in research trials from FreeHand 1.75G across many woody<br />

ornamentals, herbaceous perennials, and annual bedding plants.<br />

49


EFFICACY OF DIMETHENAMID-P + PENDIMETHALIN GRANULAR COMBINATIONS<br />

IN CONTAINERS. J.C. Neal, North Carolina State University, Raleigh.<br />

ABSTRACT<br />

There are currently no granular formulations of preemergence herbicides<br />

available for yellow nutsedge control in landscape plantings. Dimethenamid-P has been<br />

shown to provide yellow nutsedge control comparable to s-metolachlor. Recently a<br />

granular formulation of dimethenamid-P has been developed for use in ornamentals.<br />

Prior research demonstrated that combining dimethenamid with a dinitroanaline<br />

herbicide provided broader spectrum annual weed control than either product applied<br />

alone. Therefore, a series of dose-response experiments were conducted to evaluate<br />

the efficacy of granular formulations of dimethenamid-P applied alone or in combination<br />

with pendimethalin on common nursery and landscape weeds. In three studies,<br />

dimethenamid-P 2G @ 0.48, 0.73 and 0.97 lb ai/A was applied alone or in factorial<br />

combinations with pendimethalin 2G at 0, 2 or 3 lb ai/A. <strong>Weed</strong>s included in the tests<br />

were spotted spurge (Chamaesyce maculata), bittercress (Cardamine hirsuta),<br />

crabgrass (Digitaria sanguinalis), goosegrass (Eleusine indica), rice flat sedge (Cyperus<br />

iria), common groundsel (Senecio vulgaris), spiny sowthistle (Sonchus asper), and<br />

doveweed (Murdannia nudiflora). Pots were filled with a pine bark + sand (7:1 v/v)<br />

substrate, irrigated, then treated. Pots were irrigated after treatment then surface<br />

seeded with weeds. Treatments were arranged in a randomized complete block design<br />

with four replicates and three pots of each species per plot. Percent weed control was<br />

visually evaluated 4, 6 and 8 weeks after treatment. Increasing doses of dimethenamid-<br />

P improved control of most species. Applied alone, dimethenamid-P controlled spurge,<br />

rice flat sedge, and doveweed. Combinations with pendimethalin improved control of<br />

goosegrass, sowthistle, bittercress and crabgrass. Although, control of groundsel,<br />

sowthistle and bittercress improved with increasing doses and combinations, maximum<br />

control of these species was not adequate. A third experiment was conducted with a<br />

higher dose of dimethenamid-P, 1.5 lb ai/A, applied alone or in combination with<br />

pendimethalin at 0, 2 or 3 lb ai/A. At 1.5 lb ai/A dimethenamid controlled doveweed,<br />

eclipta (Eclipta prostrata), goosegrass, crabgrass, spotted spurge and American<br />

burnweed (Erechtites hieraciifolia). For these species, combining dimethenamid-P with<br />

pendimethalin did not improve control over dimethenamid-P at 1.5 lb ai/A. Long stalked<br />

phyllanthus (Phyllanthus tenellus) control was greater with combinations of<br />

pendimethalin + dimethenamid-P compared to either herbicide applied alone. These<br />

data demonstrate that a granular formulation of dimethenamid-P controls many<br />

common nursery and landscape weeds. Combinations with pendimethalin may<br />

enhance the control of some species particularly at lower dimethenamid-P doses.<br />

50


ANNUAL BLUEGRASS CONTROL AND CREEPING BENTGRASS QUALITY AND<br />

COLOR IN FAIRWAY HEIGHT TURF AS INFLUENCED BY PLANT GROWTH<br />

REGULATOR PROGRAMS WITH BISPYRIBAC-SODIUM. S. J. McDonald, Turfgrass<br />

Disease Solutions, LLC, Pottstown, PA.<br />

ABSTRACT<br />

Creeping bentgrass (Agrostis stolonifera Huds.) is one of the most commonly<br />

grown turf species for fairway turf. In creeping bentgrass fairways, annual bluegrass<br />

(Poa annua L.) (POAAN) is considered a grassy weed. Golf course superintendents<br />

employ many different plant growth regulator programs to fairway height turf. In coolseason<br />

turfgrass fairways, three different plant growth regulators are standard. These<br />

include: paclobutrazol (PB), flurprimodol (FP), and trinexapac-ethyl (TE). Furthermore,<br />

bispyribac-sodium (BPS) is labeled for the control of POAAN in fairway height creeping<br />

bentgrass. Research has shown that Velocity does have a potential to significantly<br />

reduce the population of POAAN in fairway height turf. One issue with the use of this<br />

herbicide is that if a stand is comprised of greater than 10% POAAN and the herbicide<br />

is applied, the area previously inhibited with POAAN becomes bareground. The<br />

purpose of this trial was to evaluate aggressive season long plant growth regulator<br />

programs with and without two mid-season applications of BPS for their effects on<br />

POAAN populations, turfgrass color, and percent bareground. The trial was conducted<br />

on turfgrass maintained as an actual golf course fairway at Brookside Country Club,<br />

located in Pottstown, PA. The experimental design was a randomized complete block<br />

with four replications. Plots were 2.5 x 6 ft. The site originally consisted of 75-85%<br />

creeping bentgrass, 15-20% POAAN, and minor (


EARLY POST-EMERGENT CONTROL OF SMOOTH CRABGRASS AND BULL<br />

PASPALUM WITH TANK-MIXES OF VARIOUS HERBICIDES. S.J. McDonald,<br />

Turfgrass Disease Solutions, LLC, Pottstown, PA.<br />

ABSTRACT<br />

Smooth crabgrass (Digitaria ischaemum) and Paspalum species are problematic<br />

grassy weeds in cool-season turfgrass. In southeastern Pennsylvania, bull or thin<br />

paspalum (Paspalum setaceum Michx.) has been observed inhibiting many lowmaintenance<br />

areas. Two sequential applications of MSMA are the standard approach<br />

employed to control paspalum species. In a pilot study conducted in 2006, it was<br />

observed that sequential applications of mesotrione at various rates + 0.25% v/v<br />

nonionic surfactant caused significant injury to mature bull paspalum and smooth<br />

crabgrass. Other researchers have reported that there are possible synergistic effects<br />

of mixing mesotrione with other herbicides. Therefore, the objective of this trial was to<br />

evaluate mesotrione applied alone and tank-mixed with selected herbicides and<br />

compare those treatments to the commercial standard (MSMA) for their ability to postemergently<br />

control smooth crabgrass and bull paspalum in a stand of fine fescue turf.<br />

Including the untreated control, there were a total of twelve treatments in this<br />

experiment. Mesotrione (8.0 fl oz/A) was applied alone and tank mixed with quinclorac<br />

(1 lb product/A), fenoxaprop (20 fl oz/A), carfentrazone (6.7 fl oz/A), sulfentrazone (4.0 fl<br />

oz/A), and fluazifop (24.0 fl oz/A). Sulfentrazone (4.0 fl oz/A) was applied alone and<br />

tank-mixed with quinclorac (1 lb product/A). Carfentrazone (6.7 fl oz/A) and quinclorac<br />

(1 lb product/A) were also applied alone. Nonionic surfactant and spray adjuvant were<br />

added as suggested by individual product labels.<br />

Initially, the site consisted of 70-85% cover by fine fescue. Treatments were<br />

initially applied on 13 June 2007 when smooth crabgrass was in the 6-7 leaf stage with<br />

2-3 tillers and paspalum was in the 2-4 leaf stage. Treatments were first applied 17<br />

days after paspalum emergence. All treatments were re-applied on 1 July 2007. The<br />

experimental design was a randomized complete block design with three replications.<br />

The site was mowed weekly at 3 inches with a rotary mower.<br />

One week after treatment (1 WAT), plots treated with mesotrione-alone or any<br />

combination of mesotrione plus another herbicide induced significant injury to both<br />

crabgrass and paspalum (>2.0 on 0 to 5 scale). The level of injury was equal the<br />

MSMA treated plots. At 2 WAT, the highest level of treatment induced injury to<br />

crabgrass and paspalum was observed in plots treated with mesotrione-alone,<br />

mesotrione + fenoxaprop, mesotrione + fluazifop and MSMA-alone. The highest level of<br />

desirable turf (fine fescue) injury occurred in plots treated with mesotrione mixed with<br />

quinclorac and MSMA.<br />

In this trial, few distinct differences between the mesotrione-alone and the<br />

mixtures in the level of crabgrass and paspalum control were observed. Two<br />

applications of mesotrione-alone at (8.0 fl oz/A) provided a high level of control of<br />

smooth crabgrass and bull paspalum. Plots treated alone with carfentrazone-alone,<br />

sulfentrazone-alone, and quinclorac-alone had equal percent plot area covered by<br />

paspalum as the untreated control throughout the entire trial.<br />

52


TOLERANCE OF SEEDLING BLUE GRAMMA AND LITTLE BLUESTEM TO<br />

POSTEMERGENCE HERBICIDES. J.L. Jester and S.D. Askew, Virginia Tech,<br />

Blacksburg.<br />

ABSTRACT<br />

The addition of adaptable perennial grasses typically referred to as "native<br />

species" to golf courses is a relatively new practice. Unlike conservation efforts, golf<br />

courses must establish cover quickly for aesthetics and weed control. Utilizing methods<br />

such as increased seeding rates and scheduled watering can expedite the maturation of<br />

the stand but weeds still pose a constant problem. Herbicides are critical to promote<br />

development of slow-maturing perennial grasses by reducing weed competition. The<br />

selection of herbicide depends on its effectiveness and level of tolerance by the grass<br />

species. Evaluating the effects of commonly used herbicides on blue grama grass<br />

(Bouteloua gracilis) and little bluestem grass (Schizachyrium scoparium) can provide<br />

data necessary to make herbicide selection easier while protecting the developing<br />

stand. Our objectives were to evaluate 25 herbicides or herbicide combinations for<br />

effects on blue gramma grass and little bluestem.<br />

Little bluestem and blue grama grass were seeded in rows at 50 pounds of seed<br />

per acre on June 22, 2007 in Blacksburg, VA. Initial plant densities ranged from 1 to 78<br />

blue grama plants and 18 to 103 little bluestem plants per plot. The study was<br />

established as a randomized complete block design with 3 replications and 26<br />

treatments. Little bluestem and blue grama grass had a minimum of three leaves at<br />

time of application. Herbicides included in this study are: Amicarbazone; aminopyralid;<br />

bentazon; carfentrazone; carfentrazone + 2,4-D + MCPP + dicamba; chlorsulfuron; 2,4-<br />

D + MCPP + dicamba; fenoxaprop; flazasulfuron; fluazifop; flucarbazone; foramsulfuron;<br />

halosulfuron; imazapic; mesotrione; metsulfuron; nicosulfuron; primisulfuron; quinclorac;<br />

simazine; sulfentrazone; sulfosulfuron; tembotrione; topramezone; and trifloxysulfuron.<br />

All herbicides were applied with appropriate adjuvant and at label-recommended rates<br />

for crops on which the products are registered. Blue grama grass and little bluestem<br />

injury and plant densities were assessed weekly for 6 week by visually estimating plant<br />

discoloration stand reduction, and stunting compared to the non-treated control and by<br />

plant counts.<br />

Little bluestem was not significantly injured by the following: aminopyralid;<br />

bentazon; carfentrazone; carfentrazone + 2,4-D + MCPP + dicamba; chlorsulfuron; 2,4-<br />

D + MCPP + dicamba; fenoxaprop; flazasulfuron ; fluazifop; foramsulfuron; ;<br />

halosulfuron; imazapic; nicosulfuron; primisulfuron; simazine; sulfentrazone;<br />

sulfosulfuron and topramezone. Amicarbazone; flucarbazone; mesotrione; metsulfuron;<br />

tembotrione and trifloxysulfuron injured little bluestem 40% or more. Blue grama grass<br />

was not significantly injured by the following herbicides: bentazon; carfentrazone; 2,4-D<br />

+ MCPP + dicamba; fenoxaprop; fluazifop; flucarbazone; and simazine. All other<br />

herbicides caused unacceptable injury to blue grama grass. These data indicate that<br />

several herbicides are safe to use on these adaptable perennial grasses.<br />

53


POSTEMERGENCE SMOOTH CRABGRASS AND WHITE CLOVER CONTROL WITH<br />

MESOTRIONE. P.H. Dernoeden and J. Fu, University of Maryland, College Park.<br />

ABSTRACT<br />

Smooth crabgrass (Digitaria ischaemum) and white clover (Trifolium repens) are<br />

among the most common and invasive turf weeds. Mesotrione has broad-spectrum<br />

activity on diverse weed species, but effective use rates and timings for postemergence<br />

crabgrass and white clover control in summer has not been established in Maryland. In<br />

the crabgrass study, various herbicide rates were applied once or twice in two timings<br />

as follows: mid-post when crabgrass was in the 4-leaf to 2-tiller stage (28 June;<br />

sequential 12 July 2007) and late-post when crabgrass was in the 3- to 8-tiller stage (18<br />

July; sequential 1 August 2007). In the white clover study, mesotrione was applied three<br />

times beginning 28 June 2007. Fenoxaprop and quinclorac were applied as standards.<br />

Mesotrione and quinclorac were tank-mixed with 0.25% v/v X-77 nonionic surfactant<br />

and 1% v/v methylated seed oil, respectively. Herbicides were applied in 50 GPA using<br />

a CO 2 pressurized (35 psi) sprayer equipped with an 8004 flat fan nozzle. The study<br />

areas were irrigated within 48 hrs of each application and thereafter to prevent drought<br />

stress. Soil was a Keyport silt loam with a pH of about 5.7 and 2.2% OM. Plots were 5<br />

ft x 5 ft and were arranged in a randomized complete block (crabgrass study) or were<br />

completely randomized (white clover study) with four replications. Tall fescue (Festuca<br />

arundinacea) color and percent of plot area covered by crabgrass and white clover were<br />

assessed visually. Crabgrass and white clover pressure were uniform and severe<br />

across the sites. Data were subjected to the analysis of variance and significantly<br />

different means were separated at P≤0.05 using Fisher's least significant difference test.<br />

Treatments providing commercially acceptable crabgrass control (i.e., < 5%<br />

cover) by 31 August 2007 included: mesotrione applied at 0.250+0.250 lb ai/A mid- and<br />

late-post and fenoxaprop (0.125+0.125 lb ai/A) and quinclorac (0.5+0.5 lb ai/A) applied<br />

late-post. Treatments providing statistically equivalent control to the aforementioned<br />

were: mesotrione applied at 0.187+0.187 lb ai/A mid-and late-post (8% crabgrass<br />

cover); mesotrione applied at 0.125+0.125 lb ai/A late-post (19% crabgrass cover); and<br />

fenoxaprop (0.09 lb ai/A) and quinclorac (0.75 lb ai/A) in the mid-post timing (14-15%<br />

crabgrass cover). Mesotrione (0.250 lb ai/A) applied once performed better in the midpost<br />

versus the late-post timing. Data indicated that the lowest effective rate of<br />

mesotrione in a sequential application, given the conditions of the study, was 0.187<br />

+0.187 lb ai/A. Mesotrione elicited an objectionable level of chlorosis in tall fescue for<br />

about 20 days. Mesotrione slowly reduced white clover cover following two applications<br />

on 28 June and 12 July, but the level of control was unacceptable. Following a third<br />

application on 1 August, plots treated with 0.125, 0.187 and 0.250 lb ai/A mesotrione<br />

had white clover cover ratings ranging from 0 to 6%, which were statistically equivalent<br />

to white clover levels in plots treated once with quinclorac at 0.75 lb ai/A on 28 June<br />

(1% white clover cover).<br />

54


YELLOW NUTSEDGE CONTROL IN COOL-SEASON TURF. S.E. Hart, C. Mansue,<br />

and P.E. McCullough, Rutgers, The State University of New Jersey, New Brunswick,<br />

NJ.<br />

ABSTRACT<br />

Field experiments were conducted in 2006 and 2007 in Adelphia, NJ to evaluate<br />

postemergence applications of halosulfuron, sulfosulfuron, sulfentrazone, and V-10142<br />

for yellow nutsedge (Cyperus esculentus) control in perennial ryegrass (Lolium perenne<br />

L. 'Manhattan II'). All herbicide treatments were applied once or twice on an<br />

approximately 5 week interval. Halosulfuron was applied at 35 or 70 g ai/ha,<br />

sulfosulfuron was applied at 13, 26, and 39 g ai/ha, sulfentrazone was applied at 140,<br />

280 or 420 g ai/ha, and V-10142 was applied at 280, 560, or 840 g ai/ha. Halosulfuron,<br />

sulfosulfuron and V-10142 treatments included nonionic surfactant at 0.25% v/v.<br />

Herbicide application dates were June 20 and July 24 in 2006 and July 2 and August 13<br />

in 2007. Turfgrass injury and yellow nutsedge control were evaluated 3 weeks after<br />

initial treatment (WAIT), prior to sequential applications, and 9 and 12 WAIT.<br />

Treatments were applied to 0.9 by 3 m plots with a single-nozzle CO 2 backpack sprayer<br />

system utilizing a 9504EVS nozzle tip which delivered 374 L/ha of spray solution at 221<br />

kPa. Experimental design was a randomized complete block with 4 replications per<br />

treatment. In 2006, prior to the sequential application yellow nutsedge control ranged<br />

from 89 to 95% for halosulfuron, 56 to 86% for sulfosulfuron, 63 to 90% for<br />

sulfentrazone, and 60 to 71% for V-10142. There was no turfgrass injury detected from<br />

any of the herbicide treatments. At 9 WAIT, perennial ryegrass injury from sequential<br />

sulfosulfuron treatments ranged from 15 to 31%. Injury from these treatments increased<br />

substantially at 12 WAIT and ranged from 26 to 50%. Injury observed was in the form of<br />

chlorosis and stand thinning. At 12 WAIT halosulfuron provided 87 to 98% yellow<br />

nutsedge control. Sequential treatments of halosulfuron did not increase yellow<br />

nutsedge control relative to single applications. Single applications of sulfosulfuron<br />

provided 60 to 74% yellow nutsedge control but sequential applications increased<br />

yellow nutsedge control to 85 to 96%. Single applications of sulfentrazone provided 70<br />

to 90% control but sequential applications at 240 and 420 g ai/ha improved control to 93<br />

and 97%, respectively. Single applications of V-10142 provided 43 to 51% control but<br />

sequential applications improved control to 76 to 80%. In 2007, prior to the sequential<br />

application yellow nutsedge control ranged from 78 to 91% for halosulfuron, 44 to 85%<br />

for sulfosulfuron, 28 to 88% for sulfentrazone, and 35 to 45% for V-10142. There was<br />

no turfgrass injury detected from any of the herbicide treatments. At 9 WAIT, no<br />

turfgrass injury was detected from any of the sequential herbicide treatments. At 12<br />

WAIT, halosulfuron provided 77 to 84% yellow nutsedge control. Sequential treatments<br />

of halosulfuron increased control to 91 to 94%. Single applications of sulfosulfuron<br />

performed much better in 2007 providing 84 to 90% and sequential applications at all<br />

three rates 96 to 97% control. Single applications of sulfentrazone provided 75 to 82%<br />

control, similar to observations in 2006. Sequential applications at 240 and 420 g ai/ha<br />

improved control to 91 and 93%, respectively. Single applications of V-10142 provided<br />

62 to 70% control but sequential applications improved control to 80 to 90%. The results<br />

of these studies suggest that sulfosulfuron and sulfentrazone may provide a viable<br />

55


alternative to halosulfuron for yellow nutsedge control especially when applied<br />

sequentially. It does not appear that single applications of V-10142 can provide<br />

commercially acceptable levels of yellow nutsedge control and sequential applications<br />

provided significantly less control than sequential applications of halosulfuron,<br />

sulfentrazone, and sulfosulfuron.<br />

56


PREEMERGENCE YELLOW NUTSEDGE CONTROL IN SPRING SEEDED TALL<br />

FESCUE. P.H. Dernoeden and J. Fu, University of Maryland, College Park.<br />

ABSTRACT<br />

Yellow nutsedge (Cyperus esculentus) (CYPES) is a common weed in turfgrass,<br />

which generally is controlled postemergence. Yellow nutsedge can be an aggressive<br />

competitor in spring seeded turfgrass and using a herbicide safely and effectively to<br />

control this weed at the time of seeding would be advantageous. In this study, three<br />

herbicides were applied at the time of seeding a stand of tall fescue (Festuca<br />

arundinacea) (TF) in spring 2007. The site was treated with glyphosate on 5 April and<br />

disk-seeded to Cochise III TF on 10 April 2007. The herbicides were applied<br />

preemergence to both TF and CYPES on 20 April and sequential applications of some<br />

treatments were made 21 May 2007. The herbicides and rates evaluated were as<br />

follows: mesotrione (0.25, 0.125 + 0.125, and 0.187 + 0.187 lb ai/A); sulfentrazone (0.25<br />

and 0.125 + 0.125 lb ai/A); and a pre-packaged mixture of sulfentrazone + prodiamine<br />

(0.57 and 0.75 lb ai/A). Soil was a Keyport silt loam with a pH of 5.7 and 2.1% OM. Turf<br />

was maintained at a height of 2.5 inches and the site was irrigated frequently during<br />

summer to prevent drought stress. Herbicides were applied in 50 GPA using a CO 2<br />

pressurized (35 psi) backpack sprayer equipped with an 8004 flat fan nozzle. Plots were<br />

5 ft by 5 ft and arranged in a randomized complete block with four replications. Tall<br />

fescue and CYPES cover were assessed visually on a linear 0 to 100% scale where 0 =<br />

no CYPES or TF and 100 = entire plot area covered with CYPES or TF. Data were<br />

subjected to the analysis of variance and significantly different means were separated<br />

using Fisher's LSD test at P≤ 0.05.<br />

Tall fescue seedlings and shoots of CYPES emanating from tubers began<br />

emerging in late April and early May 2007. In plots treated with mesotrione, CYPES<br />

shoots emerged and turned white and many plants died over a period of weeks. In plots<br />

treated with sulfentrazone and sulfentrazone + prodiamine, emerging shoots of CYPES<br />

were not observed. On 31 May, 10 days had passed since sequential applications were<br />

made and all treatments had reduced CYPES levels. Plots treated with sulfentrazone<br />

and sulfentrazone + prodiamine had lower CYPES levels than plots treated with<br />

mesotrione on 31 May. By 1 August, plots treated with mesotrione at 0.125 + 0.125 and<br />

0.187 + 0.187 lb ai/A (3 to 11% CYPES cover) had CYPES levels statistically equivalent<br />

to sulfentrazone and sulfentrazone + prodiamine (trace to 10% CYPES cover). Plots<br />

treated with sulfentrazone at 0.125 + 0.125 lb ai/A, however, were almost free of<br />

CYPES on 1 August. While sulfentrazone and sulfentrazone + prodiamine provided<br />

effective preemergence CYPES control, they adversely affected TF seedling<br />

emergence. On 1 August, sulfentrazone-treated plots had 48 to 70% TF cover;<br />

whereas, plots treated with sulfentrazone + prodiamine had only 8 to 18% TF cover.<br />

Conversely, mesotrione had no adverse effects on TF seedlings and plots treated twice<br />

at 0.125 and 0.187 lb ai/A achieved 72 to 85% TF cover by 8 June, respectively, and<br />

retained this cover level the entire summer.<br />

57


A PRELIMINARY STUDY OF THE NON-NATIVE VASCULAR FLORA, R. Stalter, A.<br />

Jung, E. Youssef, J. Jelovic. Brookhaven National Laboratory, Long Island, New York.<br />

ABSTRACT<br />

This preliminary study was conducted at Brookhaven National Laboratory, Long<br />

Island, New York. The objective of this three year study was to collect and document<br />

the native and non-native vascular flora at the laboratory. Collecting trips were made to<br />

the laboratory at two week intervals beginning in April, 2007, terminating on August 15,<br />

2007. Over 500 species were collected. The preliminary list of the non-native vascular<br />

flora includes 103 species, 37% of the flora. Families with the greatest numbers of nonnative<br />

species were the Poaceae and Asteraceae with 19 and 16 species respectively.<br />

Plant families composed exclusively of alien taxa were the Alliaceae, Commelinaceae,<br />

Elaeagnaceae and Molluginaceae. The study will be completed in October, 2009.<br />

INTRODUCTION<br />

Brookhaven National Laboratory (BNL) is situated in eastern central Long Island,<br />

New York (40.9°N Latitude 72.9°W Longitude). The laboratory extends North from the<br />

Long Island Expressway Service Road (exit 68) and borders the William Floyd Parkway<br />

on the West. Brookhaven National Laboratory is composed of approximately 2,226<br />

hectares of terrestrial habitat including several small ephemeral freshwater ponds.<br />

Little change in the forest vegetation where the laboratory is situated today<br />

occurred during the first two centuries of European habitation beginning in 1651. The<br />

land was logged extensively in the 1850’s. A severe fire burned hundreds of hectares of<br />

the site in 1865. In 1917, a portion of the site was developed to house Camp Upton, a<br />

major training center for World War 1 veterans. Camp Upton was utilized by the Civilian<br />

Conservation Corps (CCP) in the 1930’s. The CCP planted white pine (Pinus strobus)<br />

and red pine (Pinus resinosa) on approximately 162 ha; these stands exist today. In<br />

1947 the Cold War necessitated the development of Brookhaven National Laboratory as<br />

a research facility to counter the bellicose actions of the Soviet Union.<br />

PLANT COMMUNITIES<br />

Seven Plant communities occur here. These are the Pinus rigida /Quercus spp.)<br />

community; the Quercus dominated forest; ruderal (disturbed sites) including lawns,<br />

roadsides, disturbed/developed areas including the sewage treatment plant, retention<br />

basins and additional lightly cleared areas; successional fields; planted pine plantations;<br />

ponds, streams and wetlands. The most unique community, the “Gamma Forest”, was<br />

the site of the Woodwell’s Ce-137 irradiated Pine Oak woodland (Woodwell and<br />

Rebuck, 1967). The senior author, Stalter, is currently comparing the vascular flora at<br />

the four irradiated communities described by Woodwell and Rebuck (1967) with the<br />

vascular plant species present at these sites in 2007. The objective of the present<br />

preliminary study was to collect and identify the non-native vascular plant species at<br />

Brookhaven National Laboratory.<br />

58


CLIMATE<br />

The climate at Brookhaven National Laboratory is humid continental (Garwood<br />

1996). Detailed climatological data for the laboratory is provided by an on-site National<br />

Oceanic and Atmospheric Administration weather center. July is the warmest month<br />

averaging 22 degrees Celsius, while January, the coldest month averages -1.5 degrees<br />

Celsius. The average length of the growing season is 185 days. Generally, the last frost<br />

in spring occurs around April 22, while the first frost in autumn occurs on October 15.<br />

Mean annual rainfall is 959 mm.<br />

METHODS<br />

Collecting trips were made to study area approximately twice a month beginning<br />

April 2007 through August 15, 2007. Additional trips to the site will be made through<br />

October 2009, when the study will be completed. Objectives for each trip included the<br />

collection of voucher specimens and an accumulation of information on abundance and<br />

apparent habitat preference for each species. Classification of the vascular plant<br />

species follows Gleason and Cronquist (1991). Bailey (1949) and Gleason and<br />

Cronquist (1991) were used to determine the non- native status of the plant species at<br />

BNL (Table 1). Families with large numbers of non-native vascular plant species and/or<br />

composed exclusively of non-native taxa are presented in Table 2. Potentially<br />

aggressive alien taxa are presented in Table 3.<br />

RESULTS AND DISCUSSION<br />

The preliminary list of the vascular flora at Brookhaven National Laboratory,<br />

based on collections from 15 April to 15 August, 2007, was composed of 278 species in<br />

201 genera in 83 families. One hundred three species, 37% of the flora, were not native<br />

to the region (Table 1). This percentage of non-native vascular plant species was<br />

slightly higher than New York States’ non-native plant species, 35%.<br />

The Asteraceae, 37 species, and Poaceae, 32 species, were the largest families<br />

in the flora. The Cyperaceae ranked third with 15 species. The largest genera were<br />

Carex and Quercus, each with 7 species. Plant families with the greatest number of<br />

non-native taxa were the Asteraceae and Poaceae with 19 and 16 species respectively.<br />

More than half of the Asteraceae and 50% of the Poaceae were composed of nonnative<br />

species. Non-native dicots (81) were more abundant then alien monocots (18),<br />

and composed (+/- 40%) of the dicot flora. Four families, the Alliaceae (formerly the<br />

Liliaceae), Commelinaceae, Elaeagnaceae and Molluginaceae were composed<br />

exclusively of non-native taxa (Table 2). Two thirds of the Gymnosperms, were not<br />

native to the site.<br />

Several non-native taxa pose a threat to BNL’s native flora (Table 3). Eragrostis<br />

curvula is the dominant taxon at the roadside right-of-way bordering the William Floyd<br />

Parkway. The well established shrub, Gaylussacia baccata, has (and will) prevent the<br />

alien E. curvula from becoming established in the Oak and Pine-Oak forest<br />

59


communities. Periodic mowing may prevent and/or restrict the E. curvula from invading<br />

the ruderal areas in the future.<br />

Alliaria petiolata and Celastrus orbiculatus are two recent invaders; both have<br />

become well established at Brookhaven and are now a dominant part of the flora.<br />

Neither species can be eradicated except pulled by hand in small local plots. Celastrus<br />

may also be treated with herbicides where it has become established locally in fields.<br />

Celastrus orbiculatus is the most abundant woody alien invader, festooning trees and<br />

shrubs, especially along roadside borders. This woody vine may occupy a greater<br />

portion of the BNL’s fields and woodlands in the future.<br />

Berberis vulgaris is a common understory shrub in woodlands and also thrives on<br />

roadsides and fields. Coronaria varia is common in fields and roadsides. Elaeagnus<br />

angustifolia has become established in successional fields and may be controlled by<br />

herbicides and/or cutting and brush-hogging. Phragmites australis has invaded<br />

wetlands and moist open sites, and may pose a bigger threat to native wetland species<br />

in the future.<br />

Polygonum cuspidatum occurs in pure stands along roadsides and successional<br />

fields. It may become more abundant at these sites in the future. Rosa multiflora is<br />

abundant at BNL. Favoring roadsides and fields like P. cuspidatum and Phragmites, this<br />

non-native woody shrub may become more widespread in the future.<br />

LITERATURE CITED<br />

1. Bailey L. H., 1949. Manual of Cultivated Plants. Macmillan, New York. 1116 pp.<br />

2. Garwood, A. N. 1996. Weather America Milpitas California 217-223<br />

3. Gleason, H. D. and A. Cronquist. 1991. Manual of Vascular Plants of<br />

Northeastern United States and adjacent Canada. 2nd ed. The New<br />

York Botanical Garden, Bronx.<br />

4. Woodwell, G. and A. Rebuck. 1967. Effects of chronic gamma radiation on<br />

the structure and diversity of an oak-pine forest. Ecological Monographs 37:<br />

53-69.<br />

Table 1. A preliminary summary of the native and non-native vascular plant species at<br />

Brookhaven National Laboratory.<br />

Spore<br />

Plants<br />

Gymnosperms Dicots Monocots Total<br />

Families 4 2 65 12 83<br />

Genera 7 4 147 43 201<br />

Species 8 6 203 61 278<br />

Introduced<br />

species<br />

Native<br />

Species<br />

0 4 81 18 103<br />

8 2 122 43 175<br />

60


Table 2. Plant families with large numbers of non-native vascular plants species, and<br />

families exclusively composed of non-native species.<br />

Family Number of Alien Taxa Percent Alien Taxa<br />

Alliaceae 1 100<br />

Asteraceae 19 51<br />

Poaceae 16 50<br />

Commelinaceae 1 100<br />

Elaeagnaceae 2 100<br />

Molluginaceae 1 100<br />

Table 3. A list of aggressive or potentially aggressive non-native vascular plant species<br />

at Brookhaven National Laboratory.<br />

Species<br />

Alliaria petiolata<br />

Berberis vulgaris<br />

Coronaria varia<br />

Celastrus orbiculatus<br />

Elaeagnus angustifolia<br />

Eragrostis curvula<br />

Phragmites australis<br />

Polygonum cuspidatum<br />

Rosa multiflora<br />

61


DEPLETING THE GERMINABLE WEED SEEDBANK WITH SOIL DISTURBANCE<br />

AND COVER CROPPING PRACTICES. S.B. Mirsky, E.R. Gallandt, D.A. Mortensen,<br />

W.S. Curran, and D.L. Shumway, Penn State University, University Park.<br />

ABSTRACT<br />

Ecologically based weed management is more variable than chemical weed<br />

management and often results in additions of seed to the soil seedbank. Low initial<br />

weed seedbank densities have been suggested to be critical to successful<br />

implementation of low external input or organic weed management practices. Therefore,<br />

to improve the likelihood of successful reduced external input and organic weed<br />

management, methods of accomplishing seedbank depletion are needed. In this study,<br />

we assess the impact of soil disturbance frequency and cover cropping practices on the<br />

germinable seedbank of common lambsquarters (Chenopodium album), velvetleaf<br />

(Abutilon theophrasti), and foxtail spp. (Setaria spp.) whose initial seedbank densities<br />

were experimentally manipulated. The effects of varying initial weed seed population<br />

levels on efficacy of weed management was tested in five cover and cash cropping<br />

systems. Seedbanks were established at four densities in Pennsylvania and Maine in<br />

the fall of 2003 and 2005. Cover crops, tine weeding and inter-row crop cultivation<br />

comprised the integrated weed management systems. There was a positive linear<br />

relationship between weed seedling recruitment and initial seedbank density. Of the six<br />

cover cropping systems studied, the summer fallow and yellow mustard (Brassica<br />

juncea) / buckwheat (Fagopyrum sagittatum) / winter canola (Brassica napus) were the<br />

only cover cropping system that consistently decreased seedbanks of the target weeds<br />

at both locations. In addition to a high soil disturbance frequency, a quality of both<br />

systems was late season disturbance preempting weed seed rain. In the case where<br />

weeds reached reproductive maturity, the deficit to the seedbank from early season soil<br />

disturbances was overwhelmed by the subsequent seed rain.<br />

62


HERBICIDE EFFECTIVENESS ON GIANT HOGWEED FOR PENNSYLVANIA<br />

ERADICATION PROGRAM. M.A. Bravo, Pennsylvania Department of Agriculture,<br />

Harrisburg.<br />

ABSTRACT<br />

Since the discovery of wild populations of giant hogweed [Heracleum<br />

mantegazzianum Sommier & Levier] in Pennsylvania and elsewhere in the United<br />

States several states have begun eradication programs for this Federal Noxious <strong>Weed</strong>.<br />

Pennsylvania began its program in 1998 and relied on a triclopyr solution in a<br />

THINVERT carrier as the core herbicide program. As the program evolved across the<br />

country and additional states (16) discovered wild populations of giant hogweed,<br />

questions regarding the most effective herbicide chemistry for giant hogweed control<br />

have surfaced. Unfortunately, due to the isolated location of the wild populations and<br />

difficulty germinating plants for greenhouse experiments, little herbicide efficacy data is<br />

available for giant hogweed control in the United States. Triclopyr has remained the<br />

core herbicide treatment in Pennsylvania and has proven effective at 2.5% v/v rates. In<br />

2007 a field trial was conducted on a 92 x 40 foot section of a wild population in Carter<br />

Camp, Pennsylvania containing more than 100 giant hogweed plants. The site was<br />

mowed for the first time on May 16 th of 2007 and herbicide treatments were applied on<br />

May 29, 2007. Foliar treatments (aminopyralid, clopyralid, glyphosate and imazapyr)<br />

were applied to 3 stages of giant hogweed plants: cotyledons consisting of 1 leaf<br />

treated; perennial rosettes with 2 leaves treated; and perennial rosettes with 5 leaves<br />

treated. In addition to the test plot, a 2.5% (v/v) triclopyr and 0.75% (v/v) clopyralid<br />

solution was foliarly applied to 228 giant hogweed plants on the same day as part of the<br />

eradication program efforts in this area of Potter County. Treatments were evaluated on<br />

June 19 th and control ratings were taken based on visual appraisal of foliar injury and<br />

root tissue damage.<br />

At the rates used in this study, glyphosate controlled all above ground biomass<br />

and some evidence of translocation of the herbicide to the roots was apparent.<br />

Imazapyr plants showed classic arrested growth and leaf chlorosis but roots appeared<br />

unaffected by the treatments, however, imazapyr is known to translocated slowly and<br />

the herbicide may not have translocated to the roots at the time of the evaluations.<br />

Classic epinastic twisting of all treated foliage was evident in all aminopyralid and<br />

clopyralid treatments and a few plants still attempted to produce flower umbels. Only 1<br />

of 4 clopyralid treated plants showed any evidence of root injury while all aminopyralid<br />

treated plants showed significant root damage. Evaluation of the 228 triclopyr/clopyralid<br />

solution treated plants indicated that plants with high above ground biomass were not<br />

controlled by the 3% solution while smaller plants were effectively killed.<br />

63


FIRST YEAR AFTER TREATMENT RESULTS: PILOT KUDZU ERADICATION<br />

PROGRAM IN PENNSYLVANIA. M.A. Bravo and P. Broady. Pennsylvania Department<br />

of Agriculture, Harrisburg.<br />

ABSTRACT<br />

Due to its known noxious and invasive status in the Southern states, limited<br />

distribution in Pennsylvania (PA), ability to produce viable seed in PA and to prevent<br />

further establishment of this species, kudzu [Pueraria montana var. lobata (Willd.)<br />

Maesen & S.M. Almeida] became a PA Noxious <strong>Weed</strong> in 1989. Current sites in PA are<br />

most often roadside banks, forest-edge, quarries, slag mine deposits, homeowner<br />

property boundaries and rarely open space locations such as pipelines. Kudzu is a host<br />

for soybean rust, therefore renewed interest in limiting the spread of kudzu began in PA.<br />

During the summer of 2006 PDA began confirming all known locations of kudzu in the<br />

state and expanded upon this with a state wide hotline in the summer of 2007. As of<br />

October, 115 sites consisting of 80 spatially distinct populations of kudzu are known in<br />

PA. The current distribution of kudzu in PA seems limited to Zone 6 of the USNA Plant<br />

Hardiness Zone Map (primarily in southern PA counties).<br />

Due to the complexity of control options and the expansiveness of kudzu growth,<br />

most property owners are not equipped to manage kudzu eradication without technical<br />

assistance. PDA began assisting property owners in Pittsburgh and Cornwall in 2000<br />

and these efforts have evolved into the state-wide Pilot Kudzu Eradication Program. As<br />

of July 2007, 28 sites in 15 counties are enrolled in the program. Herbicides used in the<br />

program since 2000 include aminopyralid, clopyralid, imazapyr, metsulfuron and<br />

triclopyr. Mechanical control is also an integrated component of the program. The goal<br />

of the Pilot program is to treat sites for 3 consecutive years to assist property owners in<br />

eradicating kudzu.<br />

Treatments at 6 sites in Cornwall, Lebanon County are being used as a research<br />

plot to collect base line data on clopyralid efficacy, rate and longevity. Based on the<br />

results in 2006, regardless of the coverage and effectiveness of the initial high volume<br />

foliar application, several repeat visits to "find" and treat every mature, woody, kudzu<br />

crown with a cut stump application is necessary to maintain season long control. The 1<br />

YAT results indicate the 2006 treatment regiment is controlling 95% of the above<br />

ground biomass and successful eradication of the root system at treated sites has either<br />

been achieved or is expected after 3 consecutive years of treatments.<br />

Historical information and the physical data collected at each site suggests all<br />

current kudzu sites in PA are at least 30 years old if not older and were purposely<br />

planted for soil stabilization or other recommended uses promoted in the late 1930's.<br />

Based on the rings in the large woody vines and historical data collected, PDA believes<br />

that many sites date back to at least the 1960’s. Sites are self-seeding underneath the<br />

canopy of the current “parent” populations and seeds are viable. Wherever soil<br />

disturbance and removal of the parent canopy has occurred, new seedlings are<br />

emerging. This is especially true where developers have bulldozed large infestations<br />

and distributed the soil and seed into open space areas.<br />

64


BIOLOGY OF DODDER: A NOXIOUS WEED. P.C. Bhowmik and D. Sarkar, University<br />

of Massachusetts, Amherst.<br />

ABSTRACT<br />

Dodder [Cuscuta spp.] is a rootless, leafless, parasitic plant, with annual or<br />

sometimes perennial life cycle. Dodder is classified as a member of the morningglory<br />

family (Convolvulaceae) or as a member of a separate dodder family (Cuscutaceae).<br />

The genus contains more than 150 twinning species that are widely distributed<br />

throughout the temperate and tropical regions of the world. Dodder is widely distributed<br />

all over the United States and it is listed as a noxious weed. Dodder is also present<br />

throughout the state of Massachusetts. Dodder parasitizes various kinds of wild and<br />

cultivated plants, and is especially destructive to alfalfa, lespedeza, flax, clover,<br />

potatoes and ornamental plants. The yield loss due to dodder infestation can go up to<br />

57% in case of forage yield of alfalfa, and 50% in case of cranberry production. They<br />

can rapidly colonize disturbed areas, where they grow in patches. Dodder probably<br />

contains some chlorophyll in the buds, fruits and stems, but the amount of food<br />

manufactured in the tissue is of little significance to the survival of the plant.<br />

Dodder embryos and seedlings have no cotyledons, but have a small, swollen<br />

root-like organ, which persist only a few days after emergence, and a shoot. Dodder<br />

seedlings must attach to a suitable host within a few days of germination or they die.<br />

After germination, seedlings of dodder undergo a non-parasitic phase of growth,<br />

dependent on seed reserve, for 2-3 weeks. Like other holoparasites, Cuscuta plants<br />

lack leaves and roots, so take water and minerals directly from host through a mass of<br />

tissue known as “inner haustorium”, which penetrates and invades the host phloem and<br />

xylem tissues. Host recognition of dodder is mediated by a phototrophic mechanism.<br />

Dodder produces numerous white, pink, or yellowish, small flowers during early June to<br />

the end of the growing season. Most of the flowers open in the morning, and a few<br />

during the day. The fruit is about 1/8 inch in diameter, with thin papery walls and contain<br />

1 to 4 seeds. A single plant of dodder can produce 16,000 seeds. Seeds are yellow to<br />

brown or black, nearly round and have a fine rough surface with one round and two flat<br />

sides. Dodder produces seed that drops to the ground and germinate in the next<br />

growing season if a suitable host is present. Without suitable host, seeds may remain<br />

dormant at least 10 yr in the field. The principle means of dodder seed dispersal is<br />

through contaminated crop seeds.<br />

Its wide host range and the long life of its dormant seeds make dodder hard to<br />

control and nearly impossible to eradicate. Preemergent herbicides such as trifluralin<br />

applied to the soil prior to seed germination will limit the infestation. Extensive research<br />

is going on to find out the suitable bio-control agent for dodder management. Detailed<br />

studies on the biology of this species and effective control measures of this parasitic<br />

weed should be developed to prevent future infestation in different habitats.<br />

65


RISKY ENERGY: BIOFUELS AND INVASIVE SPECIES. J. Barney and J. DiTomaso,<br />

University of California, Davis.<br />

ABSTRACT<br />

In an effort to reduce greenhouse gas emissions, expand domestic energy<br />

production, and maintain economic growth, public and private investments are being<br />

used to pursue dedicated feedstock crops for biofuel production. The leading<br />

candidates for lignocellulose-based energy are primarily perennial rhizomatous grasses,<br />

most of which are not native to the region for which production is proposed. From an<br />

agronomic perspective, the life history characteristics, rapid growth rates, and tonnage<br />

of biomass produced by these non-native grasses make them ideal feedstock crops.<br />

Biofuel feedstocks grown as dedicated energy crops are being selected, bred, and<br />

engineered from non-native taxa to possess few resident pests, tolerate poor growing<br />

conditions, and produce highly competitive monospecific stands – traits which typify<br />

much of our invasive flora. We used a weed risk assessment protocol, which<br />

categorizes the risk of becoming invasive based on biogeography, history, and biology<br />

and ecology, to qualify the potential invasiveness of three leading biofuel candidate<br />

crops – switchgrass (Panicum virgatum), giant reed (Arundo donax), and miscanthus<br />

(Miscanthus x giganteus) – under various assumptions. Switchgrass was found to have<br />

a high invasive potential (‘reject’) in California, unless sterility was introduced (‘accept’).<br />

Giant reed has a high invasive potential in Florida where large plantations are proposed,<br />

while miscanthus poses little threat of escape in the United States. Additionally, each<br />

biofuel crop shares many characteristics with established invasive weeds of similar life<br />

history. Based on our qualitative assessment, we propose a target region by genotype<br />

specific pre-introduction screen that comprises risk analysis, climate-matching<br />

modeling, and ecological studies of fitness responses to various environmental<br />

scenarios. This screening procedure will provide reasonable assurance that<br />

economically beneficial biofuel crops will be environmentally benign with minimal risk of<br />

escaping to native and managed environs.<br />

66


ACTIVITY REPORT FOR THE MASSACHUSETTS INVASIVE PLANT ADVISORY<br />

GROUP AND THE MASSACHUSETTS PROHIBITED PLANT LIST. R.G. Prostak, A.R.<br />

Bonanno, University of Massachusetts, Amherst, and B. Mitchell Massachusetts<br />

Department of Agricultural Resources, Boston.<br />

ABSTRACT<br />

The Massachusetts Invasive Plant Advisory Group (MIPAG) was formed in 1999<br />

by the Ad Hoc Native Plant Advisory Committee to begin addressing the invasive plant<br />

issue in Massachusetts. The Massachusetts Executive Office of Environmental Affairs<br />

recognized it as part of the Massachusetts Council on Invasive Species which is<br />

intended to serve as a coordinating mechanism for the various invasive-speciesmanagement<br />

activities undertaken by state agencies, federal agencies, and private<br />

organizations. MIPAG is a voluntary collaboration among public and private<br />

organizations concerned about the problem of invasive plants in Massachusetts.<br />

Eighteen entities are represented on MIPAG, including state and federal governmental<br />

agencies in fish and wildlife, agriculture, and natural resources; the horticulture industry;<br />

academic science institutions; and land management and nonprofit conservation<br />

organizations.<br />

In order to determine which plant species are invasive in Massachusetts, MIPAG<br />

worked with Leslie Mehrhoff of the University of Connecticut to adopt definitions, create<br />

a list of plant to be evaluated, and develop a set of biologically based criteria upon<br />

which to evaluate objectively plants suspected to be invasive in the Commonwealth.<br />

The group contracted with Leslie Mehrhoff to gather existing data about selected<br />

species and help the group assess which currently are invasive and which have the<br />

potential to become problematic. A total of 85 species were evaluated and identified as<br />

Invasive, Likely Invasive, or Potentially Invasive. Species evaluated in which sufficient<br />

information or evidence is currently lacking for an adequate evaluation were designated<br />

as Do not list at this time. An annotated list of all species evaluated was developed.<br />

Upon the completion of plant species evaluations, MIPAG developed and outlined<br />

invasive-plant-management objectives for the Commonwealth in Strategic<br />

Recommendations for Managing Invasive Plants in Massachusetts.<br />

The Massachusetts Department of Agricultural Resources (MDAR), working<br />

closely with the Massachusetts Nursery and Landscape Association, on January 1,<br />

2006, under Massachusetts General Law Chapter 128 Section 2 and 16 - 31A, began a<br />

two-step ban on the importation and sale of invasive plants in the Commonwealth. The<br />

ban used the Massachusetts Prohibited Plant List which combines species from the<br />

MIPAG list and the Federal Noxious <strong>Weed</strong> List. In order to minimize financial impacts<br />

on Massachusetts agribusinesses, the regulation provides a "phase-out" exception for<br />

14 species that are commonly sold in the ornamental trade. This “phase-out” allows an<br />

extension until January 1, 2007 for herbaceous species and January 1, 2009 for woody<br />

species. These 14 species cannot be imported in to the Commonwealth, but existing<br />

instate nursery stock can be propagated and sold until the “phase-out” date. The ban is<br />

limited to the importation, sale, trade, and distribution of listed plants and does not<br />

impact existing plantings. MDAR nursery inspectors annually inspect every retail<br />

nursery to ensure that pests are not brought into and/or spread throughout the<br />

67


Commonwealth. Inspections for prohibited plants have become part of this annual<br />

process. MDAR investigates all reports of illegal sales with many reports originating<br />

from individuals in the general public who are interested in the issue of invasive plants.<br />

During the 2006 and 2007 growing season, businesses that were in violation were<br />

asked either to destroy or to send back illegal nursery stock. Beginning in 2008, MDAR<br />

will issue fines for violation of the regulation.<br />

68


SQUASH RESPONSE TO FOMESAFEN, HALOSULFURON, METOLACHLOR, AND<br />

TERBACIL APPLIED AT PLANTING. J.B. Beam, R.B. Batts, and W.E. Mitchem, North<br />

Carolina State University, Lincolnton and Raleigh, NC.<br />

ABSTRACT<br />

Summer squash is a labor intensive, high value crop in western, North Carolina.<br />

Most summer squash growers rely upon conventional tillage and hand hoeing for weed<br />

control in the early season before crop canopy. While cultivation is effective at<br />

controlling weeds in row middles, hoeing is needed to control weeds in row and neither<br />

one provides any residual weed control. Tests were conducted from 2005 to 2007 in<br />

Lincoln County, NC to determine potential herbicide rates and timings for summer<br />

squash production in the area. Herbicides tested included bentazon (0.5 lb ai/A),<br />

chlorimuron (0.125 lb ai/A), cloransulam (0.026 lb ai/A), ethalfluralin (0.26) plus<br />

clomazone (0.78 lb ai/A), fomesafen (0.25 lb ai/A), flumioxazin (0.0318 to 0.057 lb ai/A),<br />

halosulfuron (0.02 to 0.03 lb ai/A), metolachlor (0.72 to 1.43 lb ai/A), pendimethalin<br />

(1.05 lb ai/A), pyrithiobac (0.03 lb ai/A), and terbacil (0.1 to 0.4 lb ai/A). A non-treated<br />

comparison treatment was included in each experiment. Chlorimuron, cloransulam,<br />

flumioxazin, pendimethalin, pyrithiobac, and terbacil, applied at rates above 0.25 lb ai/A,<br />

severely injured squash when applied at planting. Bentazon applied POST with a<br />

nonionic surfactant (0.25% v/v) did not injure squash in 2005, but stunted squash in<br />

2006. Fomesafen, halosulfuron, metolachlor, and terbacil at 0.1 lb ai/A applied at<br />

planting did not alter the number of squash plants per plot and injured squash less than<br />

10% in 8 experiments from 2005 to 2007. Yields taken in 2006 and 2007 showed that<br />

total squash weight per plot and squash weight per plant were not different from the<br />

nontreated when fomesafen, halosulfuron, metolachlor, or terbacil were applied.<br />

In 2006 and 2007 metolachlor plus halosulfuron, metolachlor plus terbacil, and<br />

metolachlor plus fomesafen did not increase squash injury and increased morningglory<br />

species (Ipomoea sp.) and carpetweed (Mollugo verticillata L.) control compared to<br />

metolachlor alone.<br />

In 2007, ethalfluralin (0.26) plus clomazone (0.78 lb ai/A) (Strategy) was<br />

applied as a comparison treatment to fomesafen at 0.25 lb, metolachlor at 1.0 lb,<br />

halosulfuron at 0.023, and terbacil at 0.1 lb ai/A. No squash injury was noted by any<br />

product either through visual estimation, plant counts, or yield. Fomesafen and terbacil<br />

provided the best moringglory control, but control was less than 60%.<br />

In 2007, fomesafen was applied at 0.125, 0.25, and 0.5 lb ai/A and metolachlor<br />

was applied at 0.5, 1.0, and 2.0 lb ai/A. Neither fomesafen nor metolachlor injured<br />

squash, decreased plant counts, nor impacted yield at any rate tested.<br />

Fomesafen, halosulfuron, metolachlor, and terbacil were deemed safe to squash<br />

at the rates tested on western NC clay soils.<br />

69


POTENTIAL HERBICIDE PROGRAMS FOR SNAP BEANS. D.D. Lingenfelter, Penn<br />

State University, University Park and M.J. VanGessel, University of Delaware,<br />

Georgetown.<br />

ABSTRACT<br />

Field studies were conducted in 2006 and 2007 in Pennsylvania (Rock Springs)<br />

and Delaware (Georgetown) to evaluate various herbicide programs for snap bean<br />

(Phaseolus vulgaris) response and annual weed control. Studies were arranged in a<br />

randomized complete block design with three replications. Snap bean (var. ‘Dusky’ in<br />

PA and ‘Tapia’ in DE) was planted in early to mid-June. Most PRE treatments contained<br />

s-metolachlor (1.67 lb ai/A) in combination with one of the following: clomazone (0.25<br />

lb); halosulfuron (0.0314 lb); pendimethalin H 2 O (1.19 lb); imazethapyr (0.0234 lb);<br />

cloransulam (0.0315 lb); and rimsulfuron (0.0156 lb). Other PRE treatments<br />

combinations contained s-metolachlor plus fomesafen premix (1.33 and 2 lb);<br />

fomesafen (0.312 lb); KIH-485 85WG (0.187 lb) and metolachlor (1.67 lb). POST<br />

treatments included halosulfuron (0.0314 lb); bentazon (0.52 lb ai); imazamox (0.0313<br />

lb); and clethodim (0.121 lb). POST treatments were applied to 1 to 2-trifoliate snap<br />

bean (about 3-4 WAP) and necessary adjuvants were included in the spray mixtures.<br />

Visual weed control and crop phytotoxicity ratings were taken periodically throughout<br />

the growing period. Snap bean yield data were also collected.<br />

Both locations contained pigweed (Amaranthus spp.), common ragweed<br />

(Ambrosia artemisiifolia) and common lambsquarters (Chenopodium album). The PA<br />

location also had velvetleaf (Abutilon theophrasti) and giant foxtail (Setaria faberi), while<br />

the DE location had annual morningglory (Ipomoea spp.) and large crabgrass (Digitaria<br />

sanguinalis). The PRE treatments of s-metolachlor plus fomesafen premix, s-<br />

metolachlor or KIH-485 plus halosulfuron always provided >90% control of ragweed,<br />

lambsquarters, pigweed, and velvetleaf. The treatments containing clomazone,<br />

pendimethalin, rimsulfuron, and KIH-485 (alone) provided inconsistent ragweed control<br />

across the studies ranging from 43 to 92%, while the other treatments ranged from 85 to<br />

100% control. All PRE treatments except those containing cloransulam, rimsulfuron,<br />

and KIH-485 (alone) provided >90% control of lambsquarters. PRE treatments that<br />

included pendimethalin, imazethapyr, cloransulam, rimsulfuron, KIH-485, halosulfuron,<br />

fomesafen, and the POST treatment containing bentazon and imazamox provided<br />

>90% control of pigweed. Of all the treatments, metolachlor and s-metolachlor plus<br />

halosulfuron and s-metolachlor plus cloransulam provided the best suppression of<br />

morningglory, ranging from 76 to 79%, while the other treatments ranged from 30 to<br />

73%. The s-metolachlor plus fomesafen premix, and those combinations containing<br />

pendimethalin, rimsulfuron, and KIH-485 always provided >90% control of foxtail and<br />

crabgrass.<br />

In summary, since the number of active ingredients used in snap bean herbicide<br />

products is limited, it is important that currently registered products are used judiciously<br />

and new herbicide modes of action are identified. Cloransulam and KIH-485 could<br />

potentially be used in snap bean production; however more research is needed to<br />

identify sensitive varieties. Rimsulfuron provides effective control of certain weeds, but<br />

generally causes unacceptable snap bean injury.<br />

70


EXPLORING THE POTENTIAL USE OF PREFIX IN MULTIPLE VEGETABLE<br />

CROPS. R.R. Bellinder and C.A. Benedict, Cornell University, Ithaca, NY.<br />

ABSTRACT<br />

Field testing of the preemergence herbicide, Prefix, previously CGA-77102,<br />

began in 2005 in New York State. It is a tank mix of s-metolachlor (81%) and<br />

fomesafen (19%) and the expected 1X use rate will be 2 pt/A (1.33 lb ai/A). Evaluation<br />

of fomesafen and other diphenylethers for preemergence use began in beans in the late<br />

1980's. IR-4 coordinated a multi-state trial with lactofen, acifluorfen and fomesafen in<br />

snap beans in 1990. Fomesafen proved to have the greatest crop tolerance of the three<br />

herbicides in these trials. Between 1991 and 2004, in addition to bean crops,<br />

fomesafen has been tested preemergence in peas (5 trials), potatoes (5 trials), and<br />

tomatoes (1 trial). From 2005 to 2007 Prefix treatments have been tested in all of<br />

these crops and additionally in transplanted pumpkins. The preemergence registration<br />

of fomesafen in snap and dry beans should be completed by the beginning of the 2008<br />

growing season, enabling the use of Prefix. In only one year of pea trials (2006) did<br />

fomesafen rates of 0.25, 0.375, and 0.5 lb cause transitory injury greater than 15%.<br />

Usually no injury was observed. In 2006, a very wet season, s-metolachlor (0.94 lb)<br />

and Prefix (1.33 lb) caused 20 and 17% injury respectively; yields were marginally<br />

reduced with Prefix, only. Potatoes showed zero injury in 6 of 8 trials and less than<br />

10% injury in the remaining 2 trials. Potato yields were consistently greater than or<br />

equivalent to a chemical standard. Similarly, tomatoes and transplanted pumpkins (3<br />

years) have consistently shown 0 -17% transitory injury without yield reductions in either<br />

crop. Fomesafen residue trials have been conducted in peas, potatoes, and tomatoes<br />

and the preparation of registration packages is in process. Crop safety with fomesafen<br />

in the 4 crops is very good and with the possible exception of peas, Prefix will be a<br />

welcome weed management tool for growers of these crops. The concern with peas is<br />

that heavy rainfall and cool weather at the time of emergence in early plantings may<br />

cause injury due to preemergence use of s-metolachlor under these conditions.<br />

71


ANNUAL GRASS CONTROL IN SWEET CORN. D.H. Johnson and D.D. Lingenfelter,<br />

Penn State University, Manheim and University Park, M.J. VanGessel, Q.R. Johnson,<br />

and B.A. Scott, University of Delaware, Georgetown.<br />

ABSTRACT<br />

<strong>Weed</strong> control in sweet corn (Zea mays) from several current and potential<br />

products were tested in at two locations in Pennsylvania and one in Delaware. Sweet<br />

corn (cv. BC0805 (Bt and Liberty Link) was planted in Lancaster (Landisville) and<br />

Centre (Rock Springs) Counties, PA, and Sussex County (Georgetown), DE. Several<br />

herbicides were applied preemergence just after planting, followed by postemergence<br />

herbicides approximately one month later. The focus of this work was the efficacy of<br />

the relatively new HPPD inhibitors mesotrione (Callisto ® ), topramezone (Impact ® ), and<br />

tembotrione (Laudis ® ) on annual grass weeds. These herbicides were applied in a<br />

sequential program following s-metolachlor + atrazine (Bicep II Magnum ® ). Total post<br />

programs included topramezone, topramezone + nicosulfuron (Accent ® ), and<br />

mesotrione + nicosulfuron. These products were tank mixed with atrazine and<br />

adjuvants as directed on the labels. Additionally, mesotrione + s-metolachlor + atrazine<br />

(Lumax ® ), KIH-485, glufosinate (Liberty ® ), and dicamba + diflufenzopyr + the safener<br />

isoxadifen-ethyl (Status ® ) plus nicosulfuron were included. The plots were evaluated for<br />

weed control and yield measured at Georgetown and Landisville. Deer damage<br />

prevented yield measurements at Rock Springs.<br />

Most herbicide programs controlled annual grasses very well at Rock Springs<br />

and Georgetown. At Rock Springs, all two-pass programs gave at least 95% giant<br />

foxtail (Setaria faberi) and large crabgrass (Digitaria sanguinalis) control. Large<br />

crabgrass control was similar at Georgetown, except for Bicep II Magnum ® followed by<br />

mesotrione + atrazine, which only gave 83% control of this weed. Grass weed control<br />

was less at Landisville, where populations were extremely high. The only treatments<br />

providing at least 95% season-long control of giant foxtail and large crabgrass were<br />

Lumax ® , Bicep II Magnum ® followed by topramezone + atrazine and Bicep II Magnum ®<br />

followed by glufosinate. Bicep II Magnum ® followed by tembotrione + atrazine gave<br />

excellent control early and mid-season, but giant foxtail control was less (84%) at<br />

harvest time. The Status ® + nicosulfuron program gave at least 90% grass weed<br />

control at Rock Springs and Georgetown, but control was poor (


FLUMIOXAZIN USE AT PLANTING IN MATTED ROW STRAWBERRIES. S.D. Guiser<br />

and K. Demachak, Penn State University, Doylestown and University Park.<br />

ABSTRACT<br />

A limited number of herbicides are labeled for use at the time of planting in<br />

matted row strawberry production. Flumioxazin (Chateau ® 51WDG) is labeled for<br />

strawberries but not for use in matted row production systems at planting. This<br />

experiment was designed to evaluate the safety of flumioxazin in matted row<br />

strawberries when applied at planting.<br />

Dormant Earliglow strawberries (Fragaria x ananassa 'Earliglow') were planted<br />

in a Klinesville shaly silt loam soil in Bedminster, Pennsylvania on April 25, 2007. The<br />

intention was to apply flumioxazin immediately after planting, before growth began.<br />

However, rainfall (2.5 inches) delayed application until four days after planting. At this<br />

time, some green tissue had emerged from the plants.<br />

On April 29, flumioxazin was applied at the rate of .063 and .188 pounds per acre<br />

(1 and 3 ounces of product per acre) to plots which were replicated five times in a<br />

randomized complete block design. Treatments were applied with a Solo 475 backpack<br />

sprayer, fitted with 0C04 nozzles in a boom and operated at 30 PSI which delivered 24<br />

GPA of spray solution. To achieve the .188 pounds per acre rate, plots were sprayed<br />

three times at the .063 pounds per acre rate, resulting in 72 GPA. Check plots were not<br />

sprayed. Rainfall of .1 inches occurred within 24 hours of application and .4 within four<br />

days of application.<br />

Phytotoxicity was rated on May 22, June 24 and July 22, 2007, which was 23, 56<br />

and 84 days after treatment, respectively. <strong>Weed</strong> control was rated on June 3, 35 days<br />

after treatment. Both the .063 and .188 pounds per acre rates of flumioxazin provided<br />

excellent weed control (98 and 100 % respectively) when rated 35 days after treatment.<br />

Both the .063 and .188 pounds per acre rates caused phytotoxicity (Table 1) The .188<br />

pounds per acre rate resulted in severe injury in the form of stunting, leaf spotting and<br />

necrosis. Injury was evident at the initial rating and plants did not recover from the<br />

injury. The .063 pounds per acre rate caused moderate injury of the same nature.<br />

Untreated plants grew normally.<br />

While flumioxazin provided excellent weed control in this study, it resulted in<br />

phytotoxicity that would be considered unacceptable to strawberry growers. Since the<br />

herbicide has potential to provide excellent weed control, investigating the effects when<br />

plants are fully dormant by making pre-plant applications or application immediately<br />

after planting is still of interest.<br />

73


Table 1. Injury to matted row strawberries following application of .063 lb and .188 of<br />

flumioxazin (Chateau ® 51 WDG) per acre four days after planting. 1= no injury; 10 =<br />

dead.<br />

Rating Date<br />

Product rate (lb/a) May 22 June 24 July 22<br />

0 1.0 a 1 1.0 a 1.0 a<br />

.063 3.0 b 2.0 b 2.4 b<br />

.188 7.0 c 6.0 c 7.2 c<br />

1<br />

Means within columns followed by the same letter are not different at the 5 % level of<br />

significance (DMRT).<br />

74


PERENNIAL WEED CONTROL AND CROP TOLERANCE WITH MESOTRIONE AND<br />

TOPRAMEZONE IN CRANBERRIES. H.A. Sandler and K.M. Ghantous, University of<br />

Massachusetts Cranberry Station, East Wareham.<br />

ABSTRACT<br />

Several field trials were established in 2006 and 2007 to generate efficacy and<br />

crop tolerance data for two herbicides that are not currently registered for use in<br />

cranberry (Vaccinium macrocarpon), mesotrione (Callisto ® ) and topramezone (Impact ® ).<br />

Cranberry had excellent tolerance of mesotrione but was injured at all tested rates of<br />

topramezone. Leaves had turned yellow when evaluated 16 days after treatment<br />

(DAT), but partially recovered by 49 DAT. Leaves appeared smaller than usual and fruit<br />

size was reduced. Topramezone provided good to excellent control of grasses.<br />

Mesotrione provided very good to excellent control of nutsedge (Cyperus dentatus) (NS)<br />

in several trials with no detrimental impact on yield. Postemergence applications can<br />

cause injury to silverleaf sawbrier (Smilax glauca), dewberry (Rubus spp.),<br />

narrowleaved goldenrod (Euthamia tenuifolia) (NLGR), and yellow loosestrife<br />

(Lysmachia terrestris) (YLS). In 2006, mesotrione was applied as a postemergence<br />

spray at 8 and 12 oz product/A (0.25 and 0.375 lb ai/A), two sprays of 8 oz/A, and one<br />

spray of 12 oz/A followed by a spray of 4 oz/A (0.125 lb ai/A) to cranberry vines infested<br />

with NS. A nonionic surfactant (X-77 ® ) was added to all sprays at 0.25% v:v.<br />

Applications were made by CO 2 -powered backpack sprayer with a flat fan nozzle<br />

simulating 30 gal water/A on 7 July and 28 July 2006. By 38 DAT, all treatments<br />

provided good to excellent control of NS. In another study, mesotrione was applied<br />

postememergence at 4, 8, 12, and 16 oz/A (one application) and two applications of 8<br />

oz/A to infestations of sawbrier, dewberry, NLGR, and YLS. Applications were made 14<br />

July and 11 August 2006. Two applications of 8 oz/A gave the highest injury rating for<br />

the four weeds.<br />

In the first year of a 2-year trial, these four weeds and cinquefoil (Potentilla<br />

canadensis) were treated with one application of 4, 8, 12, and 16 oz/A or 2 applications<br />

of 4 oz/A mesotrione postemergence. Applications were made 10 July and 26 July<br />

2007. Two applications of 4 oz/A reduced the percent cover of cinquefoil, NLGR and<br />

sawbrier and caused significant weed injury. The plots have been marked and will<br />

receive the same herbicide treatments in 2008 and will be re-evaluated for weed control<br />

and percent weed cover.<br />

In a trial conducted in 2007, topramezone was applied as a single<br />

postemergence application at 1, 2, and 4 oz product/A plus methylated seed oil (1%)<br />

and urea ammonium nitrate (2.5%). Mesotrione (8 oz/A + 0.25% v:v X-77 ® ) was<br />

included in the treatments along with an untreated check. The application was made as<br />

described above on 10 July. By 16 DAT, cranberry leaves were injured (starkly yellow)<br />

for all rates of topramezone. By 48 DAT, the vines had recovered their color somewhat<br />

but were still given higher injury ratings than the check and the mesotrione treatments.<br />

Fruit treated with any rate of topramezone were smaller than fruit treated with<br />

mesotrione or left untreated.<br />

75


HERBICIDE-RESISTANT WEEDS IN THE UNITED STATES AND THEIR IMPACT ON<br />

EXTENSION. M.J. VanGessel and B.A. Scott, University of Delaware, Georgetown.<br />

ABSTRACT<br />

Chemical weed control is the mainstay of weed management in American<br />

agriculture. The loss or reduction in the utility of herbicides is a concern to researchers,<br />

agronomists, agribusiness, and farmers alike. Resistance is one mechanism of<br />

reducing the utility of a herbicide. Since the early 1970's, herbicide resistance has been<br />

an important issue for weed management. However, in the past few years resistance<br />

has become a focal point of extension programming. A survey of University extension<br />

personnel in the US conducted in the summer of 2007 revealed that herbicide-resistant<br />

weeds have impacted educational programs. Over 80% of those responding said they<br />

are spending more effort on herbicide resistance than they were ten years ago and<br />

almost 70% said they expect herbicide resistance to continue to impact their extension<br />

programming in the next five years. The two main issues extension is addressing are<br />

management of a specific resistant biotype and resistance management to avoid the<br />

development of herbicide-resistant biotypes. Glyphosate and ALS-resistance are the<br />

two modes of action that university extension specialists are targeting for education on<br />

herbicide resistance management. While triazines were mentioned as the third most<br />

problematic biotypes, it lagged well behind glyphosate and ALS mode of action in terms<br />

of extension programming. The most often mentioned weeds as troublesome were<br />

pigweed species (Amaranthus spp.), horseweed (Conyza Canadensis), common<br />

ragweed (Ambrosia artemisiifolia), common lambsquarters (Chenopodium album),<br />

foxtail species (Setaria spp.), kochia (Kochia scoparia), ryegrass species (Lolium spp.),<br />

wild oats (Avena fatua), and sorghum species (Sorghum spp.) also mentioned with<br />

some frequency. Most of the extension specialists responding said alternate modes of<br />

action were the most common method of resistance management, and weeds with few<br />

herbicide options were the species they were most concerned about for resistance<br />

management. Herbicide resistance is likely to increase in the United States. <strong>Weed</strong><br />

management approaches need to change in order to limit further development and<br />

spread of herbicide-resistant weeds. A determined and long-term effort is needed by all<br />

involved in agriculture for successful resistance management.<br />

76


ITALIAN RYEGRASS CONTROL IN WHEAT. R.L. Ritter and H. Menbere, University of<br />

Maryland, College Park.<br />

ABSTRACT<br />

Studies have been conducted at the Central Maryland Research and Education<br />

Center located in Beltsville, MD, for the control of Italian ryegrass (Lolium multiflorum<br />

Lam.) in wheat (Triticum aestivum L.). Early research demonstrated the utility of<br />

preemergence (PRE) applications of s-metolachlor or flufenacet + metribuzin for Italian<br />

ryegrass control in wheat with minimal injury to wheat. Flufenacet has been examined<br />

as a PRE treatment with good Italian ryegrass control. However, wheat injury and<br />

resulting yield loss were experienced as rates of flufenacet increased. Pendimethalin<br />

has also been examined as a PRE treatment. Depending upon rate and time of<br />

application, pendimethalin provided good Italian ryegrass control, no wheat injury, and<br />

resulted in good yields. KIH-485 has also been examined as a PRE and delayed-PRE<br />

application. Injury has been observed with both types of applications, but may be rain<br />

dependent. In some years, better control was obtained with the delayed-PRE<br />

applications, but this also may be rain dependent. Mesosulfuron-methyl and pinoxaden<br />

have been examined for postemergence (POST) control of Italian ryegrass control in<br />

wheat. Both products have provided excellent weed control, good crop tolerance, and<br />

resulting good yields. Chlorsulfuron + flucarbazone-sodium have also been investigated<br />

for control of Italian ryegrass control in wheat. Applications were made early fall, midfall,<br />

and early spring. Injury was noted with all rates and timings. However, excellent<br />

Italian ryegrass control was noted with no loss in wheat yield.<br />

77


NEW POSTEMERGENCE WEED CONTROL OPTIONS FOR USE IN CORN. H.<br />

Menbere and R.L. Ritter, University of Maryland, College Park.<br />

ABSTRACT<br />

Postemergence (POST) herbicides continue to be utilized in corn (Zea mays L.)<br />

throughout the mid-Atlantic region of the U. S. <strong>Weed</strong>s escapes such as triazineresistant<br />

weed species continue to plague farmers throughout the region. While many<br />

older products such as 2,4-D and dicamba continue to be used, newer products such as<br />

mesotrione, primisulfuron-methyl plus the sodium salt of dicamba, and newer<br />

formulations of dicamba are taking their fair share of the market. A number of growers<br />

have experimented with total POST programs. While glyphosate is available for overtop<br />

applications in glyphosate-tolerant corn, choices are becoming more available for nonglyphosate-tolerant<br />

corn. The pre-packaged mix of nicosulfuron plus rimsulfuron plus<br />

atrazine is one of the choices many growers have chosen. It is generally recommended<br />

that dicamba be added for additional broadleaf weed control. Other recent additions to<br />

the POST arsenal include rimsulfuron, which can be applied preemergence (PRE) or<br />

POST. The package-mix of nicosulfuron plus thifensulfuron is another new entry in the<br />

POST market. Recently, we have seen a lot of activity within the agricultural chemical<br />

industry, exploring the POST use of the HPPD inhibitors. This started with mesotrione<br />

by Syngenta, topramezone by AMVAC, and tembotrione by Bayer. While all three<br />

products seem to provide good broadleaf weed control, there are differences in the level<br />

of grass control they provide.<br />

78


ANNUAL GRASS BURNDOWN IN CORN WITH HPPD INHIBITORS. R.R. Hahn and<br />

P.J. Stachowski. Cornell University, Ithaca, NY.<br />

ABSTRACT<br />

Three HPPD inhibitors and a sulfonylurea premix were evaluated for burndown<br />

potential of large crabgrass [Digitaria sanguinalis (L.) Scop.] and giant foxtail (Setaria<br />

faberi Herrm.) in corn (Zea mays L.). Postemergence burndown applications of 0.094 lb<br />

ai/A of mesotrione, 0.082 lb ai/A of tembotrione, or 0.016 lb ai/A of topramezone were<br />

compared with 0.035 lb ai/A of a 2:1 ratio premix of nicosulfuron / rimsulfuron in 2007.<br />

All applications were made in 20 gal/A of water with 1% (v/v) of either crop oil<br />

concentrate or methylated seed oil and 2.5% (v/v) of 28% urea ammonium nitrate.<br />

Large crabgrass experiments were conducted near Valatie, NY. One experiment<br />

compared early postemergence (EPOST) and mid-postemergence (MPOST)<br />

applications of the HPPD inhibitors and the sulfonylurea premix in combinations with 0.5<br />

lb ai/A of atrazine. Applications were made when large crabgrass was 0.5 and 4 inches<br />

tall. When applied EPOST, large crabgrass burndown 4 weeks after treatment (WAT)<br />

averaged 89% for mesotrione, tembotrione, and nicosulfuron/rimsulfuron. EPOST<br />

burndown with topramezone was 70% 4 WAT. Large crabgrass burndown with MPOST<br />

HPPD inhibitor applications averaged 91% compared with 68% with nicosulfuron /<br />

rimsulfuron 3WAT. Grain corn yields averaged 127 Bu/A for these EPOST and MPOST<br />

burndown treatments and there were no differences among treatments. The other large<br />

crabgrass experiment compared EPOST residual combinations of 1 lb/A of atrazine plus<br />

0.95 lb ai/A of s-metolachlor, 1.43 lb ai/A of pendimethalin, or 1.78 oz ai/A of KIH-485<br />

alone and tank-mixed with the burndown herbicides. EPOST burndown was 78% with<br />

s-metolachlor plus atrazine or KIH-485 plus atrazine 3 WAT while pendimethalin plus<br />

atrazine provided 68% burndown. When the residual combinations were tank mixed<br />

with the HPPD inhibitors or nicosulfuron/rimsulfuron, burndown averaged 98% 3 WAT.<br />

Yield with EPOST application of the residual combinations alone averaged 126 Bu/A<br />

while the average yield with burndown herbicides was 145 Bu/A. Experiments at<br />

Valatie and Aurora, NY compared burndown of giant foxtail with s-metolachlor plus<br />

atrazine or pendimethalin plus atrazine alone and in combinations with two HPPD<br />

inhibitors or the sulfonylurea premix. At Aurora, EPOST applications were made when<br />

giant foxtail averaged 2.5 inches tall. Burndown of giant foxtail with EPOST residual<br />

combinations of metolachlor plus atrazine or pendimethalin plus atrazine increased from<br />

58 and 42%, respectively, by 2 WAT to an average of 98 and 97%, respectively, when<br />

tembotrione, topramezone, or nicosulfuron / rimsulfuron was included in the tank-mixes.<br />

Corn yields averaged 135 Bu/A with the residual combinations alone and 161 Bu/A<br />

when HPPD inhibitors or the nicosulfuron / rimsulfuron premix were added to these<br />

residual combinations. At Valatie, similar treatments were applied MPOST when giant<br />

foxtail was 4 inches tall. The residual s-metolachlor plus atrazine or pendimethalin plus<br />

atrazine combinations provided 31% burndown 3 WAT. When applied with<br />

topramezone or nicosulfuron/rimsulfuron, burndown averaged 93%. With tembotrione,<br />

these residual combinations provided 81% giant foxtail burndown. Corn yield with the<br />

residual combinations averaged 77 Bu/A while the average yield of the residual<br />

combinations with burndown herbicides was112 Bu/A.<br />

79


PREEMERGENCE CONTROL OF DOVEWEED IN NURSERY CROPS. J.F. Derr,<br />

Virginia Tech, Virginia Beach, and J.C. Neal, North Carolina State University, Raleigh.<br />

ABSTRACT<br />

Several new weed species have appeared in the nursery industry, including<br />

doveweed [Murdannia nudiflora (L.) Brenan] (DW). DW is a summer annual in the<br />

Commelinaceae or spiderwort family that grows well in containers as well as in gravel<br />

areas underneath pots. This weed germinates in hot, wet weather and forms a dense<br />

mat. Leaves are 2 to 5 inches long and ¼ to ½ inch wide with parallel veins and<br />

resemble grass leaves. Stems are succulent, trailing, and can root at the nodes.<br />

Purplish 3-petaled flowers form in mid-summer until fall. DW propagates strictly by<br />

seed. Little information is available on the control of this weed species. Development of<br />

control programs now will allow nursery producers to manage this weed before<br />

doveweed becomes established. Studies were established in Virginia and North<br />

Carolina to determine the effectiveness of preemergence herbicides currently used in<br />

container production for controlling doveweed. Experiments were conducted in 1 gallon<br />

containers utilizing either 100% pine bark or pine bark plus sand (8:1, v/v) substrates.<br />

Three pots of each weed species were seeded per plot. The herbicides tested were the<br />

single active ingredient herbicides dimethenamid, flumioxazin, isoxaben, s-metolachlor,<br />

oxyfluorfen, oryzalin, pendimethalin, prodiamine, and trifluralin, as well as the<br />

combination products OH2 ® , Rout ® , Regal O-O ® , and Snapshot ® TG, at maximum userates.<br />

In addition, Snapshot ® and oxadiazon were applied at 2.5 and 2.0 lb ai/A<br />

respectively.<br />

In trials conducted in VA and NC, dimethenamid, flumioxazin, and s-metolachlor<br />

all gave excellent control of DW (95% or greater) by 4 to 8 weeks after treatment. In the<br />

VA trial, OH2 ® , Rout ® , oxadiazon (only the 4 lb/A rate), and oryzalin reduced stand of<br />

doveweed at 19 DAT, but these chemicals all provided less than 55% control at 4<br />

weeks. Similarly, in the NC trial, 4 lb ai/A oxadiazon or oryzalin provided about 50%<br />

suppression of DW; however in that trial, OH2 ® did not. In both VA and NC trials, Regal<br />

O-O ® , isoxaben, oxyfluorfen, Snapshot ® , Showcase, pendimethalin, prodiamine, and<br />

trifluralin did not control DW.<br />

In other trials, OH2 ® at 3.0 lb/A, Showcase and Snapshot ® at 3.75 and 5.0 lb<br />

/A reduced DW stand at 20 DAT but all provided less than 20% control at 35 DAT.<br />

Oxadiazon at 3.0 lb ai/A did not reduce DW stand. In that study, Rout ® at 3 lb/A caused<br />

greater reduction in DW stand than OH2 ® , with 43% control seen at 35 DAT compared<br />

to 5% control with OH2 ® . Flumioxazin at 0.38 lb/A provided 83% control. Spray<br />

applications of oryzalin at 2.0 lb/A, dithiopyr at 0.5 lb/A, isoxaben at 1.0 lb/A, oryzalin<br />

plus isoxaben, and dithiopyr plus isoxaben did not reduce stand of DW. S-metolachlor<br />

at 2.5, 5.0, and 10.0 lb/A provided 95% or greater control of DW, while pendimethalin at<br />

2, 4, and 8.0 lb/A and Snapshot ® at 2.5, 5.0, and 10.0 lb/A all provided less than 20%<br />

control.<br />

Only three herbicides, dimethenamid, flumioxazin, and s-metolachlor, provide<br />

acceptable control of DW, with only flumioxazin and s-metolachlor currently available to<br />

nursery producers. Other preemergence herbicides available to container producers<br />

might reduce DW stand, but they do not provide acceptable control of this weed.<br />

80


TOLERANCE OF FRASER FIR TO HERBICIDES APPLIED BEFORE AND AFTER<br />

BUD BREAK. J. F. Ahrens and T. L. Mervosh, Connecticut Agricultural Experiment<br />

Station, Windsor.<br />

ABSTRACT<br />

Herbicides were evaluated in 2007 in a Christmas tree plantation of fraser fir<br />

[Abies fraseri (Pursh) Poir.] on a silt loam soil in Somers, CT. Some treatments<br />

followed an IR-4 protocol and others were added to verify findings from earlier<br />

experiments. Plots consisted of five or six trees (2- to 3-ft height) spaced 6 ft apart.<br />

Sprays were applied over the top using a hand-held boom with 8003VS TeeJet nozzles<br />

calibrated to deliver 30 gal/A. Treatments were replicated four times in randomized<br />

complete blocks. The predominant weeds were large crabgrass [Digitaria sanguinalis<br />

(L.) Scop.] and common ragweed (Ambrosia artemisiifolia L.). Horseweed [Conyza<br />

canadensis ( L.). Cronq.], in the rosette stage in May, was also prevalent in some plots.<br />

Dimethenamid-P [BAS 656h (63.9% EC)] was applied at 0.97, 1.94 and 3.9 lb<br />

ai/A on May 7, before emergence of crabgrass and ragweed, when fir buds were<br />

swollen but unopened. These treatments were reapplied over the same plots 10 weeks<br />

later on July 18, when fir shoot growth was still expanding. Crabgrass was controlled in<br />

June at all application rates, but ragweed was controlled only at the highest rate. The<br />

firs were moderately injured in May only by the highest rate, but they recovered by late<br />

June. No injury was observed following the second applications. Dimethenamid-P plus<br />

pendimethalin 3.8CS was also applied on May 7 and on July 18 at 0.9 + 1.5 lb ai/A, 1.8<br />

+ 3 lb ai/A and 2.7+ 4.5 lb ai/A. Ragweed control in June was poor to fair, but crabgrass<br />

control was excellent at all rates. No firs were injured by any of these treatments.<br />

Mesotrione 4SC was applied on May 7 at 0.187, 0.25 and 0.375 lb ai/A. These<br />

treatments were repeated 4 weeks later (June 7), when the firs were rapidly growing.<br />

Before the June applications, control of ragweed was good at 0.187 and 0.25 lb/A and<br />

excellent at 0.375 lb/A. Crabgrass control was excellent at all rates. The second set of<br />

treatments enhanced control of both weeds. No fir injury was observed in any<br />

mesotrione treated plots. Imazasulfuron 75WG was applied at 1 lb ai/A to separate<br />

plots on May 10, June 7 and June 28. The May application provided excellent<br />

preemergence control of both ragweed and crabgrass, but the postemergence<br />

applications in June were less effective. Only the June 7 application during rapid fir<br />

growth caused moderate injury, in the form of persistent needle chlorosis.<br />

Prior work showed that low-rate combinations of glyphosate, oxyfluorfen and<br />

clopyralid in early to mid June effectively controlled seedling weeds in conifer plantings.<br />

We compared a “standard” combination of glyphosate at 0.125 lb ai/A + oxyfluorfen 4F<br />

at 0.25 lb ai/A + clopyralid at 0.09 lb ai/A (4 + 8 + 4 oz product/A) with the same<br />

herbicides combined at either double these rates, or at higher rates of glyphosate only<br />

(0.25 or 0.375 lb ai/A). Five weeks after treatment, the “standard” treatment gave<br />

excellent control of ragweed and horseweed, but only fair control of mature crabgrass.<br />

Increasing the rate of glyphosate to 0.375 lb/A improved crabgrass control but also<br />

slightly injured the firs when sprayed over the top. Semi-directed sprays, where only<br />

basal foliage of trees is treated, could reduce injury from this herbicide combination.<br />

81


TOLERANCES OF CONTAINER-GROWN ORNAMENTALS TO EXPERIMENTAL AND<br />

REGISTERED HERBICIDES. T. L. Mervosh and J. F. Ahrens, Connecticut Agricultural<br />

Experiment Station, Windsor.<br />

ABSTRACT<br />

Based on protocols from the IR-4 Ornamental Horticulture Program, we<br />

conducted an experiment to evaluate tolerances of four woody plants to herbicides<br />

considered for possible ornamental use registrations. The shrubs were planted in 1-<br />

gallon containers (6-in diameter) on May 22, 2007. All plants were less than 1 ft tall<br />

when potted. Plants were juniper (Juniperus squamata ‘Blue Star’), emerald green<br />

arborvitae (Thuja occidentalis ‘Smargd’), spirea (Spiraea x bumalda ‘Gold Mound’) and<br />

doublefile viburnum (Viburnum plicatum ‘Shasta’). Each plot contained three plants of<br />

each species. Treatments were replicated four times in randomized complete blocks.<br />

Sprayable treatments consisted of dimethenamid-P 5.9EC [BAS 656h] at 0.97, 1.94 and<br />

3.88 lb ai/A, and mesotrione 4SC at 0.187, 0.25 and 0.375 lb ai/A. Granular treatments<br />

consisted of pendimethalin plus dimethenamid-P 1.75G [BAS 659h] at 2.65, 5.3 and<br />

10.6 lb ai/A, prodiamine plus sulfentrazone 0.3G [F-6875] at 0.375, 0.75 and 1.5 lb ai/A,<br />

and flumioxazin 0.25G [BroadStar] at 0.375 lb ai/A as a standard. All herbicides were<br />

applied over the top of actively growing plants on May 30. Mesotrione treatments were<br />

applied a second time over the same plots on June 27. All other treatments were reapplied<br />

on July 26. Herbicide sprays were applied in a volume of 30 gal/A using a CO 2 -<br />

pressurized sprayer with two 8003VS nozzle tips. Treatments were sprayed over the<br />

top of pre-wetted plants. Plants were watered 20 to 30 min later by overhead irrigation<br />

for 30 min. Granular herbicides were applied over dry foliage. F-6875 granules<br />

(amount per 10 ft 2 ) and sieved sand of like size were mixed in a shaker jar and applied<br />

uniformly over plants within a 10-ft 2 frame. The other granular treatments were applied<br />

using a calibrated auger-feed drop spreader. Overhead irrigation began 20 to 50 min<br />

after application of granules, and plants were watered for a 30-min period.<br />

Plant injury (0 = no injury; 10 = dead) was evaluated periodically up to 8 weeks<br />

after treatment applications. Juniper was tolerant of all herbicides except mesotrione,<br />

which caused dose-dependent chlorosis after the second application (injury ratings of<br />

1.0 to 2.9). Arborvitae was not injured by any granular treatment. The high dose of<br />

BAS 656h caused slight injury (1.1) to arborvitae after the second spray. All doses of<br />

mesotrione resulted in significant whitening of arborvitae and some foliar necrosis at the<br />

middle and high doses (injury of 2.9 to 6.2 on August 9). Spirea tolerated the granular<br />

herbicides, except that two applications of F-6875 at the high dose caused some injury<br />

(1.8). After the second spray of BAS 656h at the high dose, minor injury (1.3) was<br />

observed on spirea foliage. All mesotrione treatments were injurious to spirea (injury of<br />

2.4 to 5.4 on August 9). Viburnum was tolerant of all the granular herbicide treatments.<br />

BAS 656h sprays were slightly injurious to viburnum (injury of 0.9 to 1.6 after two<br />

applications). Mesotrione caused severe whitening, stunting and/or death to viburnum<br />

plants, with injury ratings of 4.7 to 8.8 on August 9. In summary, all four shrubs in this<br />

experiment were susceptible to mesotrione sprays, whereas these species were quite<br />

tolerant of the other herbicide treatments.<br />

82


SHOWCASE EFFICACY AND SAFETY IN CONTAINER GROWN NURSERY<br />

CROPS. D. A. Little and J. C. Neal. North Carolina State University, Raleigh.<br />

ABSTRACT<br />

Showcase 2.5G (oxyfluorfen 0.25G + isoxaben 0.25G + trifluralin 2G) has been<br />

recently registered for use in container grown nursery crops but few reports are<br />

available that have compared its safety and efficacy with currently labeled herbicides.<br />

Two studies were conducted at the Castle Hayne Research Station, Castle Hayne, N.C.<br />

in 2006 and 2007, evaluating the safety and efficacy of Showcase 2.5G on 17<br />

container grown ornamentals and eight weed species. Crops tested in 2006 were Ilex<br />

vomitoria 'Nana', Ilex cornuta ‘Burfordii Nana’, Viburnum tinus ‘Compacta’, Lirope<br />

muscari ‘Variegata’, Coloneaster horizontallis, Spirea japonica ‘Little Princes’,<br />

Rhododendron x ‘Pink Gumpo’, and Lagerstroemia x ‘Tuscarora’. Crops tested in 2007<br />

were Juniperus ‘Parsonii’, Buxus ‘Wintergreen’, Thuja orientalis ‘Green Giant’, Viburnum<br />

x ‘Pragense’, Viburnum odoratissimum, Lagerstroemia ‘Muskogee’, Lantana x ‘New<br />

Gold’, Loropetalum chinensis ‘Rudy’, and Rosa ‘Flower Carpet Red’. <strong>Weed</strong> species<br />

tested both years were Cardamine hirsuta, Murdannia nudiflora, Phyllanthus tenellus,<br />

Eclipta prostrata, Digitaria sanguinalis. Chamaesyce maculata was included in 2006<br />

only. Chamaesyce nutans and Eupatorium capillifolium were tested in 2007.<br />

Treatments in 2006 included Showcase (4.2 and 5.6 kg ai/ha), Snapshot ® TG<br />

(isoxaben 0.5G + trifluralin 2G) (4.2 and 5.6 kg ai/ha), OH2 ® (oxyfluorfen 2G +<br />

pendimethalin 1G) (3.4 kg ai/ha), and BroadStar (flumioxazin 0.25G) (0.42 kg ai/ha).<br />

In 2007 three rates of Showcase (2.8, 4.2, and 5.6 kg ai/ha) were compared to<br />

treatments of OH2 ® (3.4 kg ai/A), Rout ® (oryzalin 1G + oxyfluorfen 2G) (3.4 kg ai/ha),<br />

Ronstar ® (oxadiazon 2G) (3.4 kg ai/ha), Regal O-O ® (oxadiazon 1G + oxyfluorfen<br />

2G)(3.4 kg ai/ha) and Regalstar ® G (oxadiazon 1G + prodiamine 0.2G) (2.7 kg ai/ha).<br />

Treatments were arranged in randomized complete block designs with three to four<br />

replications and three pots of each species per plot. Herbicides were applied over the<br />

top of crops using a hand-held shaker jar then irrigated. <strong>Weed</strong>s were seeded the day of<br />

treatment. Data were recorded bi-weekly for eight weeks using a visual scale from 0-10<br />

(0=no crop injury, no weed control and 10=complete crop death, complete weed<br />

control). At six weeks after treatment (WAT), the weed pots were sprayed with<br />

glyphosate (1.12 kg ai/ha) plus glufosinate (1.68 kg ai/ha). At eight weeks after<br />

treatments, pots were hand-weeded and treatments were re-applied and evaluated for<br />

an additional eight weeks. Only slight injury was observed on Lantana ‘New Gold’ and<br />

variegated Lirope with the 4.2 and 5.6 kg ai/ha rates of Showcase. No injury was<br />

observed on the other 15 crop species. Showcase (4.2 and 5.6 kg ai/ha) provided<br />

greater than 80% control of Cardamine hirsuta, Chamaesyce maculata, Chamaesyce<br />

nutans, Digitaria sanguinalis, and Eupatorium capillifolium. Showcase did not control<br />

Murdannia nudiflora and Eclipta prostrata and provided inconsistent control of<br />

Phyllanthus tenellus. BroadStar was the only treatment to control Murdannia<br />

nudiflora and provide consistent control of Phyllanthus tenellus. Data show that<br />

Showcase was relatively safe on the crop species tested, while providing good control<br />

of five major container weeds with results similar to other herbicides commonly used in<br />

container nursery crops.<br />

83


UPDATE ON 2007 WEED SCIENCE RESEARCH IN THE IR-4 ORNAMENTAL<br />

HORTICULTURE PROGRAM. C.L. Palmer, J.J. Baron, and E. Vea. IR-4 Project,<br />

Princeton, NJ<br />

ABSTRACT<br />

The 2007 IR-4 Ornamental Horticulture Research Program sponsored crop<br />

safety testing of over-the-top applications on four different products: BAS 656 EC<br />

(dimethenamid), BAS 659 G (dimethenamid + pendimethalin), F6875 0.3G<br />

(sulfentrazone + prodiamine), and mesotrione 4SC. All four products were applied to<br />

woody ornamental crops. BAS 659 G and F6875 0.3G were also applied to herbaceous<br />

perennial crops. In the results received to date, BAS 656 EC exhibited some level of<br />

injury with at least one of the rates tested in 11 out of 25 woody ornamental crops; this<br />

injury tended to be slight to moderate and occurring at the highest tested rate. Sixteen<br />

out of 38 crops showed some level of injury with BAS 659 G, but most crops were<br />

herbaceous perennials. F6875 0.3G caused injury on 16 of 43 crops, both woody and<br />

herbaceous perennials. Twenty-two of 31 crops were injured with mesotrione 4SC with<br />

symptoms becoming more severe over time. The results from this research will aid in<br />

the development of the labels for these products and will help growers and landscape<br />

care professionals make more informed product choices.<br />

84


EFFECTS OF DITHIOPYR AND TRICLOPYR ON ANTICHROMATIC EFFECTS OF<br />

MESOTRIONE ON TURFGRASS AND SELECTED WEEDS. J.B. Willis, M.J. Goddard,<br />

and S.D. Askew, Virginia Tech, Blacksburg.<br />

ABSTRACT<br />

Mesotrione will be the first p-hydroxyphenylpyruvate dioxygenase inhibitor<br />

(HPPD) registered for used in turfgrass. When HPPD inhibitors are applied to<br />

susceptible plants, their foliage turns white. Susceptible plant response to HPPD<br />

inhibitors has been described as antichromatic due to complete loss of color in treated<br />

foliage. Many turfgrass managers have indicated that their clientele may be displeased<br />

with the antichromatic response caused by mesotrione. Combinations of mesotrione<br />

and triclopyr had better turf color than vegetation treated with mesotrione alone in<br />

research at Virginia Tech. We speculate that dithiopyr, another pyridine herbicide, may<br />

have the same response. Our objectives were to evaluate mesotrione plus triclopyr and<br />

dithiopyr for effects on turfgrass and weed control.<br />

Field trials evaluated mesotrione at 0.13 lb ai/A plus triclopyr at 1.0 lb ai/A<br />

compared to each product alone for injury to Kentucky bluegrass, perennial ryegrass,<br />

tall fescue, and fine fescue. Turfgrass injury, color, and weed control were evaluated at<br />

2 and 4 WAT (weeks after treatment). A randomized complete block experimental<br />

design was used with 3 replications. Greenhouse trials were conducted using 2- to 4-<br />

tiller smooth crabgrass in 4-inch pots evaluated color and amount of white foliage. A 3<br />

by 8 factorial arrangement of treatments with 3 levels of mesotrione including 0, 0.13,<br />

and 0.25 lb ai/A and 8 levels of pyridine herbicide including dithiopyr at 0.06, 0.13, 0.25<br />

and 0.50 lb ai/A and triclopyr at 0.13, 0.25, 0.50, and 1.0 lb ai/A. Additional comparison<br />

treatments were mesotrione at 0, 0.13, and 0.25 lb ai/A and nonionic surfactant (NIS) at<br />

0.25% v/v alone. All treatments including mesotrione were applied with NIS at 0.25 %<br />

v/v.<br />

Injury observed in these trials was only temporary and complete recovery was<br />

noted by 4 WAT. The combination of mesotrione and triclopyr significantly controlled<br />

white clover, corn speedwell, and dandelion postemergent, and crabgrass preemergent.<br />

Crabgrass color was significantly reduced by mesotrione alone. Tank-mixing triclopyr at<br />

0.50 and 1.0 lb ai/A with mesotrione improved turfgrass color by reducing the amount of<br />

white foliage on individual plants. Nontreated plants and mesotrione treated plants had<br />

observed color ratings of 6.3 and 2.3, respectively. Leaf counts indicate that only 3 to<br />

18 % of crabgrass was white when triclopyr at 0.50 and 1.0 lb ai/A was included with<br />

mesotrione while 40% of crabgrass foliage was white when mesotrione was used alone.<br />

Single applications of mesotrione will not control crabgrass and tank-mixtures rarely<br />

improved crabgrass control or decrease fresh weight. However, triclopyr at 0.50 and<br />

1.0 lb ai/A addition to mesotrione significantly reduced the amount of white crabgrass<br />

foliage compared to mesotrione alone. Mesotrione plus triclopyr is a promising<br />

combination for improving broadleaf weed control while reducing antichromatic effects<br />

of mesotrione toward grass species.<br />

85


BROADLEAF WEED CONTROL WITH FLUROXYPYR IN COOL-SEASON<br />

TURFGRASS. C. Mansue and S.E. Hart, Rutgers, The State University of New Jersey,<br />

New Brunswick.<br />

ABSTRACT<br />

Field experiments have been conducted from 2004 to 2007 to evaluate<br />

fluroxypyr, applied alone or in combination with other herbicides for broadleaf weed<br />

control in cool-season turfgrass. Treatments were applied to 0.9 by 3 m plots with a<br />

single-nozzle CO 2 backpack sprayer system utilizing a 9504EVS nozzle tip which<br />

delivered 374 L/ha of spray solution at 221 kPa. Experimental design was a<br />

randomized complete block with 4 replications per treatment in all experiments. In 2004,<br />

fluroxypyr applied alone at 0.26 kg ai/h provided complete control of white clover 6<br />

weeks after treatment (WAT) but only controlled dandelion and buckhorn plantain 70<br />

and 67%, respectively. The addition of 2,4-D at 1.1 kg ai/h was required to obtain<br />

complete control of these two weeds. In a 2005 timing study an experimental ester<br />

combination of fluroxypyr + 2,4-D + dicamba provided nearly complete control of<br />

dandelion, white clover, buckhorn plantain and mouseear chickweed when applied on<br />

April 14, April 28, or May 27. In 2006 and 2007 experiments, the combination of<br />

fluroxypyr + 2,4-D + dicamba applied in May continued to provide nearly complete<br />

control of dandelion, buckhorn plantain and white clover 8 WAT. In some cases white<br />

clover control was superior to control obtained with a combination of 2,4-D + MCPP +<br />

dicamba and a combination of 2,4-D and triclopyr. In additional studies in 2007 the<br />

combination of fluroxypyr + 2,4-D + dicamba provided 98% oxalis control 4 WAT while<br />

all other herbicide combinations tested only provided 65% or less control with the<br />

exception of a combination of 2,4-D + MCPP + dicamba + carfentrazone which provided<br />

86% control. One weed that the combination of fluroxypyr + 2,4-D + dicamba was not<br />

completely effective on was prostrate knotweed were only 70% control was obtained 8<br />

WAT. The results of these studies over the last four years suggest that fluroxypyr can<br />

provide very high and consistent levels of white clover control. Fluroxypyr was also<br />

effective at providing nearly complete oxalis control<br />

86


TENACITY : A NEW HERBICIDE FOR TURFGRASS MANAGERS. R. J. Keese, J.<br />

Driver, and D. Cox, Syngenta Professional Products, Carmel, IN<br />

ABSTRACT<br />

Tenacity, comprised of the active ingredient mesotrione, is a new active<br />

ingredient for the turfgrass market. The structure of mesotrione is based on<br />

leptospermone, a naturally occurring compound with allelopathic activity which was<br />

found around the bottlebrush plant (Callistemon citrinus). Mesotrione belongs to the<br />

triketone herbicide family, and the mode of action belongs with the HPPD inhibitors (phydroxyphenylpyruvate<br />

dioxygenase) which blocks formation of plastoquinone and<br />

subsequent carotenoid production. The typical symptom observed from a Tenacity <br />

application is bleaching, followed by necrosis and plant death.<br />

Tenacity is safe when applied to cool season grasses such as Kentucky<br />

bluegrass and tall fescue. Application rates up to 8 fl oz pr/A are allowed on these<br />

species. On perennial ryegrass and fine fescues a maximum rate of 5 fl oz pr/A is<br />

allowed. Tenacity has both foliar and soil activity. Sixteen (16) fl oz pr/A/year is the<br />

maximum application, so users will need to plan their treatments according to what they<br />

hope to accomplish, and keep in mind that a sequential application 3 weeks after the<br />

initial treatment will be required.<br />

The weed spectrum is varied, as Tenacity has both pre-emergence and postemergence<br />

activity, and is active on grassy weed species, broadleaves and nutsedge.<br />

Nimblewill control is excellent with Tenacity , and a unique fit for the turf markets. Preemergence<br />

nutsedge activity is also unique. Tenacity will also selectively remove<br />

bentgrass from cool season turf species such as bluegrass and fescues; three<br />

applications of 4 oz pr/A are required, at 2-3 week intervals, to effectively remove the<br />

bentgrass competition.<br />

The most unique characteristic of Tenacity is the ability to prevent weed<br />

competition when applied at seeding. No reduction in turf stand or interference with<br />

emergence has been observed in 3-years of testing. Improved stands and turf quality<br />

have been obtained due to removal of the weed competition. Seeding can be<br />

accomplished in spring, early summer or fall.<br />

87


PREEMERGENCE ANNUAL BLUEGRASS CONTROL. J.A. Borger and M.B. Naedel<br />

Penn State University, University Park.<br />

ABSTRACT<br />

Two separate studies were conducted using different materials and application<br />

timings. Both studies evaluated the percent cover of newly seeded turfgrass. The first<br />

study employed 'Amazing GS' perennial ryegrass (Lolium perenne L.) the second was a<br />

patch mix material that consisted of ‘Nexus" and ‘Renaissance’ perennial ryegrass,<br />

‘Clearwater’ and ‘Barron’ Kentucky bluegrass (Poa pratensis L.), and ‘Boreal’ creeping<br />

red fescue (Festuca ruba ssp. littoralis). Both of these studies were conducted at the<br />

Valentine Turfgrass Research Center, Penn State University, University Park, Pa. The<br />

objective of these studies was to determine the control of the annual bluegrass (Poa<br />

annua L.) during the establishment of turfgrass. The studies were a randomized<br />

complete block design with three replications. Treatments of the first study were<br />

applied on June 29 (4 WBS), July 12 (2 WBS), July 26 (SEED), August 24 (3 WAS),<br />

and September 6 (5 WAS), 2007 using a three foot CO 2 powered boom sprayer<br />

calibrated to deliver 40 gpa using one, flat fan, 11004E nozzle at 40 psi. Treatments of<br />

the second study were applied on June 29 (4 WBS), July 12 (2 WBS), July 26 (SEED),<br />

August 9 (2 WAS), August 22 (4 WAS), and September 13 (6 WAS), 2007 using a<br />

shaker box. Glyphosate was applied to both test sites at a rate of 3 qts/A on June 6,<br />

2007 prior to the application of test materials and was seeded July 26, 2007. Perennial<br />

ryegrass germination was first noted on the first study on September 1, 2007 and on<br />

September 2, 2007 for the second study. Once established, the new turf was mowed<br />

once weekly at 2 inches with a rotary mower with clippings returned to the site.<br />

Perennial ryegrass cover, of the first study, was evaluated four times during the study.<br />

All treated turfgrass revealed some level of perennial ryegrass growth during the study.<br />

On the final rating date, September 19th, there was 90% or greater perennial ryegrass<br />

cover of treated or non treated turfgrass. Turfgrass cover, of the second study, was<br />

rated six times during the study. On the final rating date, October 5th, all treated and<br />

non treated turfgrass had at least 78% cover or greater. The percent cover of annual<br />

bluegrass, of the first study, was rated on September 25th. All Tenacity treated<br />

turfgrass had significantly less annual bluegrass cover when compared to non treated<br />

turfgrass. The percent cover of annual bluegrass, of the second study, was rated on<br />

October 5th. Turfgrass treated with Lockup at 150 lb/A (penoxsulam 0.015 lb ai/A +<br />

2,4-D at 1.5 lb ae/A) applied 4 WBS or 2 WBS, and 6 WAS had significantly less annual<br />

bluegrass cover when compared to non treated turfgrass.<br />

88


PREEMERGENCE SMOOTH CRABGRASS CONTROL. M.B. Naedel and J.A. Borger<br />

Penn State University, University Park.<br />

ABSTRACT<br />

Preemergence control of smooth crabgrass (Digitaria ischaemum) was evaluated<br />

on a mature stand of 'Jet Elite' perennial ryegrass (Lolium perenne L.) at the Valentine<br />

Turfgrass Research Center, Penn State University, University Park, PA. The objectives<br />

of the study were to determine the efficacy of selected preemergence herbicides for the<br />

control of smooth crabgrass when applied early in the growing season compared to<br />

normal application timing, the rates of materials, and the safety to desired turfgrass<br />

species. This study was a randomized complete block design with three replications.<br />

Treatments were applied on March 27, 2007 (EARLY), April 26 (PRE), and June 7 (1-<br />

2LF), 2007 using a three foot CO 2 powered boom sprayer calibrated to deliver 80 gpa<br />

using one, flat fan, 11008E nozzle at 40 psi. After the second and third application the<br />

entire test site received approximately 0.5 inch of water. On May 8, 2007, 0.5 lb N/M<br />

was applied from urea and 0.5 lb N/M from a 31-0-0 IBDU fertilizer was applied to the<br />

entire test area. The site was mowed once per week with a rotary mower at one inch<br />

with clippings returned to the site. The test site was over-seeded with a native source of<br />

smooth crabgrass seed in the fall of at least two of the pervious growing seasons. The<br />

test site had approximately 90% cover of smooth crabgrass in the non treated areas at<br />

the conclusion of the study. Smooth crabgrass germination was first noted in the non<br />

treated areas of the test site on May 1, 2007. Turfgrass phytotoxicity was evaluated four<br />

times during the study (Table 1). No phytotoxicity was found during the study. The<br />

percent control of smooth crabgrass was evaluated on August 6th (Table 2). All treated<br />

turfgrass, except that treated with Pendulum ® 3.8CS at 0.5 lb ai/A applied early, had<br />

significantly less crabgrass than non treated turfgrass. Turfgrass treated with<br />

Dimension ® 40WP three times (EARLY/PRE/1-2LF) with a total of 0.5 lb ai/A applied<br />

was not significantly different that turfgrass treated once with Dimension ® 40WP at 0.5<br />

lb ai/A applied PRE. But, when Dimension ® was applied three times (EARLY/PRE/1-<br />

2LF) with a total of 0.375 lb ai/A applied total was compared to turfgrass treated once<br />

with Dimension ® 40WP at 0.5 lb ai/A applied PRE no significant difference was found in<br />

the control of crabgrass. Turfgrass treated with Pendulum ® 3.8CS at 0.5 lb ai/A EARLY<br />

plus Dimension ® 40WP at 0.5 lb ai/A 1-2 LF had significantly more control of crabgrass<br />

compared to turfgrass treated with Pendulum ® 3.8CS at 0.5 lb ai/A EARLY plus<br />

Dimension ® 40WP at 0.25 lb ai/A 1-2 LF. Turfgrass treated with Betasan ® 4E at 7.4<br />

oz/M PRE was not significantly different than turfgrass treated with Betasan ® 4E at 3.7<br />

oz/M EARLY plus Dimension ® 40WP at 0.5 lb ai/A 1-2 LF or Betasan ® 4E at 3.7 oz/M<br />

EARLY plus Dimension ® 40WP at 0.25 lb ai/A 1-2 LF. Turfgrass treated with Barricade ®<br />

65WG at 0.25 lb ai/A applied EARLY plus mesotrione 4SC at 0.125 lb ai/A applied<br />

PRE/1-2 LF was not significantly different than turfgrass treated with Barricade ® 65WG<br />

at 0.25 lb ai/A applied EARLY plus mesotrione 4SC at 0.125 lb ai/A applied 1-2 LF.<br />

89


PRE- AND EARLY-POSTEMERGENT CONTROL OF FALSE GREEN KYLLINGA IN<br />

SOUTHERN NEW ENGLAND. J.E. Kaminski, University of Connecticut, Storrs.<br />

ABSTRACT<br />

Although false green kyllinga (Kyllinga gracillima L.) (FGK) is a common weed<br />

problem on golf courses in the southern region of the United States, its presence in<br />

southern New England is rare. A severe infestation of FGK, however, has been<br />

observed for several years at a golf course located in Greenwich, CT. Although a<br />

perennial, FGK populations in CT appear to disappear during the winter months only to<br />

regenerate by seed and/or surviving stolons in the spring. No information currently is<br />

available with regards to herbicide efficacy or application timing to control FGK in the<br />

northern United States. The objective of this study was to evaluate sulfentrazone,<br />

sulfentrazone + prodiamine, prodiamine, and mesotrione for selective control of FGK<br />

when applied at a preemergent (PRE) and early-postemergent (EP) timing. In 2007, a<br />

field trial was conducted in a golf course rough at Burning Tree Country Club located in<br />

Greenwich, CT. The turfgrass area was dominated by Kentucky bluegrass (Poa<br />

pratensis L.), but also contained small percentages of annual bluegrass (Poa annua L.)<br />

and perennial ryegrass (Lolium perenne L.). The area was mowed approximately 2<br />

times per week to a height of 2.0 inches. Sulfentrazone (0.125 and 0.250 lb ai/A),<br />

sulfentrazone + prodiamine 4SC and 0.3G (0.375 and 0.750 lb ai/A), prodiamine (0.5 lb<br />

a.i./A) and mesotrione (0.125, 0.188, and 0.250 lb ai/A) were applied in two timings (1<br />

and 17 May) just prior to and immediately following the emergence of FGK. All<br />

mesotrione and carfentrazone treatments were applied with the nonionic surfactant X-<br />

77 ® at 0.25% (v/v). All sprayable treatments were applied in 44 gpa using a CO 2<br />

pressurized (40psi) sprayer equipped with a flat-fan nozzle. Granular treatments were<br />

applied using a shaker bottle. Plots measured 6 ft x 6 ft and were arranged in a<br />

randomized complete block design with 4 replications. Control of FGK was rated on a<br />

percent scale where 0 = no visible FGK and 100 = entire plot area covered with FGK.<br />

Populations of FGK in the untreated control plots averaged 70% on the final<br />

rating date (17 July). At this time, excellent control (92 to 99%) was achieved in plots<br />

treated at the PRE timing with sulfentrazone (0.25 lb ai/A), sulfentrazone + prodiamine<br />

0.3G (0.750 lb ai/A), and all rates of mesotrione. Only moderate to good FGK<br />

suppression (56 to 85%) was achieved from the PRE timing of sulfentrazone (0.125 lb<br />

ai/A), sulfentrazone + prodiamine 4SC (0.375 and 0.750 lb ai/A) and 0.3G (0.375 lb<br />

ai/A). When treatments were applied to newly emerging plants in the EP timing,<br />

excellent control (92 to 97%) was achieved in plots treated with sulfentrazone (0.125<br />

and 0.250 lb ai/A) and the highest rate of sulfentrazone + prodiamine (SC and G<br />

formulations) and mesotrione. Moderate (59 to 73%) FGK control was achieved within<br />

plots receiving the 0.375 lb ai/A and 0.188 lb ai/A rates of sulfentrazone + prodiamine<br />

4SC and mesotrione, respectively. When applied at the EP timing, no FGK suppression<br />

was achieved within plots treated with sulfentrazone + prodiamine 0.3G (0.375 lb ai/A),<br />

prodiamine (0.50 lb ai/A), and mesotrione (0.125 lb ai/A), when compared to the<br />

untreated control. Our results suggest that FGK growing in the northeastern United<br />

States can be effectively suppressed with a single application of sulfentrazone or<br />

mesotrione when applied prior to or shortly after plant emergence.<br />

90


POSTEMERGENT CONTROL OF FALSE GREEN KYLLINGA IN SOUTHERN NEW<br />

ENGLAND. J.E. Kaminski, University of Connecticut, Storrs.<br />

ABSTRACT<br />

Although uncommon in New England, a severe infestation of false green kyllinga<br />

(Kyllinga gracillima L.) (FGK) has been observed for several years on a golf course<br />

located in southwestern Connecticut. No information currently is available with regards<br />

to postemergent control of this weed species in the northeastern United States. The<br />

objectives of this study were to determine the ability of single and sequential<br />

postemergent applications of sulfentrazone, mesotrione, halosulfuron-methyl, and<br />

carfentrazone to control mature FGK.<br />

A field study was conducted in a golf course rough at Burning Tree Country Club<br />

in Greenwich, CT. The site was dominated by Kentucky bluegrass (Poa pratensis L.),<br />

but also contained small percentages of annual bluegrass (Poa annua L.) and perennial<br />

ryegrass (Lolium perenne L.). All sites were mowed approximately 2 times per week to<br />

a height of 2.0 inches. Sulfentrazone (0.125, 0.188, and 0.250 lb ai/A), mesotrione<br />

(0.125, 0.188 and 0.250 lb ai/A), halosulfuron-methyl (0.021, 0.031, and 0.062 lb ai/A),<br />

and carfentrazone (0.013, 0.038, and 0.099 lb ai/A), and halosulfuron-methyl +<br />

carfentrazone (0.021 lb ai/A + 0.038 lb ai/A) were applied on 3 June. In addition to the<br />

single application treatments, sequential applications of sulfentrazone and mesotrione<br />

also were applied on 24 June. All mesotrione, carfentrazone, and halosulfuron-methyl<br />

treatments were applied with the nonionic surfactant X-77 ® at 0.25% (v/v). All<br />

treatments were applied in 44 gpa using a CO 2 pressurized (40psi) sprayer equipped<br />

with a flat-fan nozzle. Plots measured 3 ft x 6 ft and were arranged in a randomized<br />

complete block design with 4 replications. Control of FGK was rated periodically<br />

throughout the study on a percent scale where 0 = no visible FGK and 100 = entire plot<br />

area covered with FGK.<br />

Shortly after the initial application, all treatments except carfentrazone resulted in<br />

injury to the FGK. Recovery of FGK, however, was observed in all plots receiving only<br />

a single herbicide application by the final rating date (18 September). On 18<br />

September, there were no differences in FGK populations among single application<br />

treatments and the untreated control. Plots receiving sequential applications of<br />

sulfentrazone (0.188 and 0.250 lb ai/A) and mesotrione (0.250 lb ai/A) resulted in good<br />

(78 to 86%) suppression of FGK. Our results suggest that sequential applications of<br />

mesotrione or sulfentrazone at higher rates likely is necessary when attempting to<br />

control mature FGK in the northeastern United States. The long term efficacy of these<br />

herbicides on the regeneration of FGK in subsequent years, however, remains<br />

unknown.<br />

91


USE OF MESOTRIONE HERBICIDE FOR ANNUAL BLUEGRASS CONTROL AT<br />

COOL-SEASON TURFGRASS ESTABLISHMENT. S.E. Hart, P.E. McCullough, and C.<br />

Mansue, Rutgers, The State University of New Jersey, New Brunswick.<br />

ABSTRACT<br />

Field studies were conducted in the fall of 2006 and 2007 to evaluate the<br />

response of newly seeded and seedling Kentucky bluegrass, perennial ryegrass, and<br />

tall fescue to mesotrione applied at planting (PRE), four weeks after turfgrass<br />

emergence (4 WAE) and a sequential treatment at both timings. Mesotrione was<br />

applied at rates ranging from 0.14 to 0.56 kg ai/ha using a single nozzle CO2 pressured<br />

sprayer calibrated to deliver a total 375 L/ha. Nozzles used were 9504E and CO2<br />

regulators were set for 220 kPa. Experimental design was a split-block with four<br />

replications. Treatments were a factorial combination of four seedings (main plots, 1.8 x<br />

68-m) with 12 mesotrione applications (sub-plots, 1 x 7.2-m). A non-seeded check strip<br />

was also included as a main plot for weed control evaluations. Turfgrass chlorosis was<br />

rated on a percent scale where 0 equaled no chlorosis and 100 equaled complete<br />

chlorosis. Turfgrass and weed cover were rated visually on a percent scale. Overall,<br />

mesotrione caused minimal turfgrass cover reductions applied PRE. However, 4 WAE<br />

applications at the higher mesotrione rates tended to cause chlorosis on both tall fescue<br />

and perennial ryegrass and in some experiments significant stand reductions especially<br />

on Kentucky bluegrass and tall fescue. Control of winter annual broadleaf weeds such<br />

as chickweed and henbit were nearly complete with all mesotrione treatments.<br />

Mesotrione exhibited potential to selectively control annual bluegrass applied PRE<br />

especially at the 0.28 and 0.56 kg/ha application rate. Annual bluegrass control was<br />

lower with 4 WAE applications than PRE applications. The most complete annual<br />

bluegrass control was observed with PRE applications followed by sequential<br />

applications 4 WAE at 0.28 and 0.56 kg/ha. In the fall 2005 and 2006 experiments these<br />

treatments provided 94 to 99 and 73 to 91% annual bluegrass control the following<br />

spring.<br />

92


CRABGRASS CONTROL INFLUENCED BY GROWTH STAGE AND BROADLEAF<br />

WEED HERBICIDES. P.E. McCullough and S.E. Hart, Rutgers, The State University of<br />

New Jersey, New Brunswick.<br />

ABSTRACT<br />

Field experiments investigated influence of crabgrass growth stage on<br />

mesotrione efficacy. Mesotrione at 0.28 kg ai/ha applied at the one leaf stage, multileaf,<br />

and one-tiller stages controlled crabgrass similar to quinclorac at 0.84 kg ai/ha and<br />

fenoxaprop at 0.1 kg ai/ha. However, mesotrione applied to multi-tiller crabgrass was<br />

less efficacious than fenoxaprop. In other field experiments, fenoxaprop efficacy was<br />

investigated for crabgrass control when tank-mixed with broadleaf weed herbicides.<br />

2,4-D, clopyralid, dicamba, and triclopyr antagonized efficacy of fenoxaprop at 0.2 kg/ha<br />

on six, five, two, and three dates, respectively. Crabgrass control from fenoxaprop at<br />

0.1 kg/ha was minimal while antagonism from broadleaf weed herbicides was<br />

inconsistent. Fluroxypyr did not reduce efficacy of fenoxaprop at either rate for<br />

crabgrass control. Overall, fluroxypyr was the only broadleaf weed herbicide that did<br />

not antagonize fenoxaprop efficacy for crabgrass control in turf.<br />

93


IR-4 IN THE NORTHEAST. E. L. Lurvey, Northeast Region IR-4 Program, Cornell<br />

University, Geneva, NY<br />

ABSTRACT<br />

The mission of the IR-4 Program is to provide data in support of the registration<br />

of pest management tools for minor/specialty crops. The research selection process is<br />

being refined to better serve that mission and its clients. IR-4 depends on the input<br />

from growers, grower groups, agricultural researchers and extension personnel to<br />

identify the important needs with potential solutions. As always, submitting a Project<br />

Clearance Request (http://ir4.rutgers.edu/FoodUse/FOODRequestForm.cfm) is the first<br />

step towards getting a new product or use on the IR-4 list of potential projects. Each<br />

fall, the research projects are selected for the coming year. To focus attention on<br />

projects of real importance, a nominating system was instituted two years ago. A<br />

project must be nominated before it will be considered for research. The list of research<br />

projects is generally posted on the IR-4 website in August Nominations are then take<br />

until about two weeks prior to the IR-4 Food Use Workshop (September 16 – 18, 2008,<br />

Sacramento, CA). Please work with me, your IR-4 Regional Coordinator for the<br />

Northeast, to insure that projects of importance to you are actually selected for<br />

research. Contact information: Edith Lurvey, Tel. No. 315-787-2308; E-mail<br />

ell10@cornell.edu.<br />

94


IR-4 PROJECT: UPDATE ON HERBICIDE REGISTRATION (FOOD USES).<br />

M. Arsenovic, F.P. Salzman, D.L. Kunkel, and J.J. Baron. IR-4 Project, Rutgers, The<br />

State University of New Jersey, Princeton.<br />

ABSTRACT<br />

The IR-4 Project is a publicly funded effort to support the registration of pest<br />

control products on specialty crops. The IR-4 Project continues to meet specialty-crop<br />

grower’s needs for weed control options despite the challenges of a mature market for<br />

herbicides and the selectivity of specialty crops to many of the more-recently-introduced<br />

herbicides. The Pesticide Registration Improvement Act (PRIA) continues to effect IR-4<br />

submissions and EPA reviews of packages.<br />

IR-4 submitted herbicide petitions to the EPA from October 2006 to September<br />

2007 for: MCPB on mint; oxyfluorfen on rhubarb, cucurbit vegetable group, fruiting<br />

vegetable group except tomato, okra, clover, and hearts of palm; pronamide on<br />

cranberry; and sethoxydim on multiple oilseed crops; and thiobencarb on wild rice.<br />

From October 2006 through September 2007, EPA has published Notices of<br />

Filing in the Federal Register for: chlorimuron on cranberry; dichlobenil on rhubarb,<br />

caneberry subgroup, and bushberry subgroup; dimethenamid on winter squash,<br />

pumpkin, radish, rutabaga, turnip, and hops; flumioxazin on the bushberry subgroup,<br />

asparagus, okra, dry bean, melon subgroup, fruiting vegetable group, and tree nut<br />

group; fluroxypyr on pome fruit group and millet; pronamide on chicory, dandelion,<br />

Belgian endive, and berry group.<br />

EPA established tolerances from October 2006 though September 2007 for:<br />

clethodim on leafy green subgroup, legume vegetable group, herb subgroup,<br />

asparagus, flax, hops, safflower, and sesame; desmedipham on garden beets (roots<br />

and tops) and spinach; dicamba on sweet corn; dimethenamid on grasses (seed);<br />

diuron on prickly pear cactus and mint; fluroxypyr on dry bulb onion; foramsulfuron on<br />

sweet corn and pop corn (exemption from tolerance); glufosinate on pistachio;<br />

glyphosate on sunflower, safflower, dry pea, Indian mulberry, and legume vegetable<br />

group; lactofen on the fruiting vegetable crop group and okra; linuron on celeriac and<br />

rhubarb; pendimethalin on Brassica head and stem subgroup, artichoke, asparagus,<br />

and grape; phenmedipham on spinach; pronamide on chicory, dandelion, Belgian<br />

endive, and berry group; sethoxydim on buckwheat, okra, borage, dill, turnip greens,<br />

and root and tuber vegetable group; and tribenuron on sunflower.<br />

95


THE USE OF MESOTRIONE FOR WEED CONTROL IN MINOR CROPS. D. Lycan, V.<br />

Lengkeek, and G.D. Vail, Syngenta Crop Protection, Greensboro, NC.<br />

ABSTRACT<br />

Field studies were initiated in 2004 to evaluate mesotrione for use in minor crops.<br />

Trials in 2005, 2006 and 2007 were conducted to further refine the level of crop<br />

tolerance and weed control from mesotrione. These field trials confirm that mesotrione<br />

is effective for control of weeds in asparagus, blackberry, blueberry, cranberry, flax,<br />

grasses grown for seed (tall fescue, Kentucky bluegrass, perennial ryegrass), millet<br />

(proso and pearl), oats, okra, raspberry, rhubarb, sugarcane, sorghum (grain and<br />

sweet).<br />

96


THE ADVANTAGES TO USING THE GRANULAR FORMULATION OF FLUMIOXAZIN<br />

IN TOMATOES, POTATOES, AND SWEET POTATOES. B.A. Majek, Rutgers, The<br />

State University of New Jersey, Bridgeton.<br />

ABSTRACT<br />

Flumioxazin, formulated as Valor ® and Chateau ® 51WDG, has been evaluated<br />

for use in transplanted tomatoes (Lycopersicon lycopersicum Mill. 'Sunbeam'), white<br />

potatoes (Solanum tuberosum L. ‘Superior’), and sweet potatoes [Ipomoea batatas (L.)<br />

Lam. ‘Beauregard’]. In tomatoes and white potatoes, the primary need for weed control<br />

that flumioxazin can fill is nightshade (Solanum species) control and in white potatoes,<br />

late season annual broadleaf weed control. The weeds than need to be controlled in<br />

sweet potatoes with flumioxazin are annual broadleaf species. The 51WDG formulation<br />

of flumioxazin applied to tomatoes pre-transplant, or as a directed and shielded spray<br />

post-transplant or postemergence has resulted in unacceptable crop injury.<br />

Applications to white potatoes preemergence or after drag-off, but before crop<br />

emergence, have not provided late season weed control in fields where cultivation and<br />

hilling are practiced after the crop has emerged. Treatments applied to sweet potatoes<br />

pre-transplant also have not provided late season weed control in fields where<br />

cultivation and hilling are practiced. Flumioxazin, formulated as BroadStar 0.5G, and<br />

applied to tomatoes, white potatoes, and sweet potatoes postemergence when the<br />

foliage was dry about the time the last cultivation or hilling did not cause injury to any of<br />

the three crops.<br />

97


SNAP BEAN RESPONSE TO POSTEMERGENCE APPLICATIONS OF<br />

ACIFLUORFEN, BENTAZON, AND FOMESAFEN. R. B. Batts, North Carolina State<br />

University, Raleigh, R. W. Wallace and A. K. Petty, Texas A&M University, Lubbock.<br />

ABSTRACT<br />

<strong>Weed</strong> control, crop injury and yield were evaluated in 2007 for processing snap<br />

beans grown in North Carolina and Texas by comparing selected rates of acifluorfen<br />

(0.188, 0.25 and 0.375 lb ai/A) and fomesafen ( 0.188, 0.25, and 0.31 lb ai/A) to<br />

bentazon (0.75 lb ai/A) when applied postemergence (POST) 21 days after planting<br />

(DAP). Trifluralin applied pre-plant incorporated (PPI) at 0.75 lb ai was used as a<br />

grower standard alone (without POST herbicides), and was applied over the entire test<br />

site at both locations. <strong>Weed</strong> populations in North Carolina were low and no ratings<br />

were recorded. In Texas, Palmer amaranth (Amaranthus palmeri S. Wats.) and<br />

common sunflower (Helianthus annuus L.) were controlled by all three herbicide<br />

treatments at 97% or better, regardless of rate. Crop injury (leaf chlorosis or necrosis)<br />

with bentazon rated 28 DAP was higher (13%) in North Carolina, while no injury was<br />

observed in Texas. In North Carolina, crop injury with all three rates of acifluorfen<br />

ranged from 24 to 36%, while injury with fomesafen was 7.5% or less. In contrast, injury<br />

from acifluorfen and fomesafen in Texas was 6.3% or less, regardless of rate.<br />

Differences in crop injury between states may have been a factor of the choice of snap<br />

bean variety (North Carolina = Bronco; Texas = Titan) as well as relative humidity<br />

(North Carolina = high; Texas = low). While injury from acifluorfen observed in North<br />

Carolina was high, yields from all treatments were equal to or greater than trifluralin<br />

applied alone. Lower yields in the trifluralin alone treatment may have been due to<br />

season-long weed pressure (even though it was low). There were no significant<br />

differences in yields for any of the treatments applied in Texas; however, yields in<br />

acifluorfen-treated plots averaged 25% less than the trifluralin alone or bentazon<br />

treatments. Average yields in plots treated with fomesafen were equivalent to trifluralin<br />

alone and the bentazon treatments. These results indicate that POST applications of<br />

fomesafen to snap beans is safe within the range of rates tested, and that while<br />

acifluorfen may cause significant early injury, yields may not necessarily be decreased.<br />

However, as seen in the Texas trial, although weeds were successfully controlled and<br />

bean injury low, yields may still be reduced, and this may prohibit its use under these<br />

conditions.<br />

98


GROWTH REGULATORS AND TURFGRASSES---A HISTORICAL PERSPECTIVE.<br />

T.L. Watschke, Penn State University, University Park.<br />

ABSTRACT<br />

The first plant growth regulator applied to turf was done by Dr. Ralph Engel of<br />

Rutgers University in 1959. Dr. Engel applied maleic hydrazide (MH) to ‘Merion’<br />

Kentucky bluegrass in an attempt to suppress seedheads. Although the seedhead<br />

suppression was mostly successful, the side effects were not (phytotoxicity). However,<br />

since that time, many growth regulating compounds have been used successfully, for a<br />

variety of objectives, on turfgrass. One of these compounds trinexapac-ethyl (Primo ®<br />

MAXX) was actually synthesized specifically for use on turf.<br />

Over the years since Dr. Engel applied MH, there has been a significant amount<br />

of research conducted to assess growth regulators as to how they might be used to<br />

manage turfgrass. The chronology of such products as to their impact on the<br />

managerial use patterns of turfgrass practitioners will be presented.<br />

99


FREQUENTLY ASKED QUESTIONS WITH PLANT GROWTH REGULATORS. D.P.<br />

Shepard, Syngenta Professional Products, Franklin, TN.<br />

ABSTRACT<br />

Plant growth regulators (PGRs) are used on many of the estimated 17,000 golf<br />

courses in the U.S. The PGRs that are used on high quality turf areas act by either<br />

slowing the production of gibberellic acid, by slowing cell division, or by enhancing the<br />

production of ethylene. Their primary uses on turfgrass include slowing turfgrass<br />

growth, reducing clippings, mowing, and equipment wear, use in hard to mow areas for<br />

safety, to improve turfgrass quality, suppress seedheads, enhance turf stress tolerance,<br />

manage annual bluegrass (Poa annua L.), and use on putting greens to increase speed<br />

and maintain putting consistency throughout the day. Questions often arise on which<br />

PGR product(s) work best on various turfgrass species and cultivars for the intended<br />

goal. The primary turfgrass species used on golf courses are bermudagrass, bentgrass,<br />

annual bluegrass, perennial ryegrass, and Kentucky bluegrass with other species such<br />

as seashore paspalum, kikuyugrass and fine fescue finding limited use. Each turf<br />

species has numerous cultivars which can vary in their response to PGRs, turfgrass<br />

management practices and environmental stresses. Several questions that turf<br />

managers often ask will be addressed. Examples include: 1) When should PGR<br />

applications begin and when should they stop? 2) Do PGR application rates vary<br />

throughout the year? 3) What other types of products can PGRs be mixed with? 4)<br />

What types of spray nozzles and water volume are best for PGR applications? 5) What<br />

is a good PGR program for suppressing annual bluegrass seedheads? 6) What effect<br />

do PGRs have on seed germination and development? 8) How does turfgrass respond<br />

to over-application of PGRs? Additional questions will be addressed.<br />

100


ANTHRACNOSE DISEASE MANAGEMENT WITH PLANT GROWTH REGULATORS.<br />

J.C. Inguagiato, J.A. Murphy, and B.B. Clarke. Rutgers, The State University of New<br />

Jersey, New Brunswick.<br />

ABSTRACT<br />

The frequency and severity of anthracnose epiphytotics, caused by the fungus<br />

Colletotrichum cereale, on golf course putting greens has increased over the past<br />

decade. Concurrently, plant growth regulation has become an integral component of<br />

putting green management, although their use has been suggested to encourage<br />

anthracnose. Mefluidide (ME) and ethephon (ET) are applied in the spring to suppress<br />

seedhead formation in annual bluegrass (ABG) putting green turf. Trinexapac-ethyl<br />

(TE) is applied throughout the growing season to improve playability by reducing vertical<br />

shoot growth and improving uniformity. More recently, TE has been increasingly used<br />

at rates and intervals exceeding label recommendations. Growth regulator effects on<br />

anthracnose development are currently unknown. The objectives of this study were to<br />

determine TE rate and interval effects on anthracnose, evaluate spring regulation<br />

influences on seedheads and disease, and to identify potential interactions between<br />

seedhead and vegetative regulation practices relative to anthracnose development.<br />

The study was conducted on an ABG putting green at the Horticultural Research<br />

Farm II in North Brunswick, NJ from 2005 through 2007. The area was mowed daily at<br />

3.2-mm and nitrogen was applied at 4.9 kg ha -1 every 14-d. Treatments were arranged<br />

in a randomized complete block design with four replications. TE was applied at various<br />

rates (0.3-, 0.4-, and 0.6-L ha -1 ) and intervals (7-,14-d) April to September 2005, March<br />

to September 2006, and March to August 2007. ME (2.2-L ha -1 ) or ET (15.9-L ha -1 ) was<br />

applied twice in late-March and early-April each year both without and with TE (0.4-L ha -<br />

1 ) applied at two intervals (7- or 14-d) throughout the season. Comparisons of treatment<br />

effects were made by planned F-tests.<br />

TE did not affect anthracnose severity in the first year of study. However, TE<br />

reduced disease in 2006 at rates ranging from 0.3 – 0.6 L ha -1 applied every 7- or 14-d.<br />

Turf incurred 11 – 27% less anthracnose when treated with TE than untreated turf.<br />

More frequent application of TE (i.e., 7- vs. 14-d) reduced disease on 3- and 21-July<br />

2006 at both 0.4- and 0.6-L ha -1 . Anthracnose severity declined linearly with increasing<br />

rate of TE in 2006, but not in 2005 or 2007. There was no interaction between<br />

application interval and rate. Tolerance of ABG to low mowing heights may be<br />

enhanced due to the reduced shoot elongation of TE treated turf reducing stress<br />

associated with routine low mowing thus, reducing anthracnose.<br />

The average ME treatment effect reduced anthracnose 6 – 21% relative to<br />

untreated turf in 2005 and 2006, but had no effect in 2007. Whereas, ME-alone had 14<br />

– 32% more disease compared to combinations of ME and TE over all three years.<br />

ME+TE reduced disease 5 – 11% in 2005 and 2006 compared to TE-alone, but were no<br />

different in 2007. The average ET treatment effect reduced anthracnose 13 – 35%<br />

relative to untreated turf in 2005 and 2006. ET+TE reduced disease 16 – 35%<br />

compared to ET-alone and 5 – 18% compared to TE-alone. Programs combining spring<br />

seedhead suppression with season-long vegetative regulation provided the most<br />

dramatic reduction of anthracnose.<br />

101


ETIOLATED TILLER SYMPTOMS OF TURFGRASS AND PLANT GROWTH<br />

REGULATORS. M.A. Fidanza, Penn State University, Berks Campus, Reading.<br />

ABSTRACT<br />

"Mad tiller" symptoms, or more correctly described as “rapid etiolation” in coolseason<br />

turfgrass, or “etiolated tiller symptoms” in turfgrass, has become a common,<br />

visual nuisance on golf course fairways and greens. On the golf course, the<br />

appearance of elongated or etiolated tillers and leaf blades can disrupt playability (i.e.,<br />

ball roll) and contributes to a significant increase in mowing, since symptomatic turf<br />

areas need to be mowed more often to provide a uniform and smooth playing surface.<br />

At some locations, fungal pathogens (i.e., 'Ascocyta' spp., 'Fusarium' spp., 'Pythium'<br />

spp., 'Rhizoctonia' spp.) have been associated with necrotic turf stands, and turf that<br />

has collapsed in patches, which have exhibited prolonged etiolated tiller symptoms.<br />

From a plant physiology perspective, an etiolated leaf blade is often the result of<br />

excessive gibberellic acid production triggered by low light intensity (i.e., shade or<br />

prolonged overcast and cloudy weather). The name “mad tiller” is attributed to bakanae<br />

disease of rice, which translates to “mad tiller” disease of rice. The causal agent of<br />

bakanae disease of rice is the soil-borne fungus 'Fusarium moniliforme'. This fungal<br />

organism contributes to the production of gibberellic acid in the rice plant and ultimately<br />

causes the plant to malfunction and produce an over-elongated tiller, which results in a<br />

serious decrease in yield. At this time, the relationship between a Fusarium sp., or<br />

other fungal pathogen, and etiolated tiller symptoms in turfgrass has not been<br />

determined conclusively (i.e. pathogenicity proven by Koch's postulates). Currently,<br />

unsubstantiated anecdotal evidence attempts to associate the occurrence of etiolated<br />

tiller symptoms in cool-season turfgrass with the use of plant growth regulators. In<br />

many cases, golf course superintendents use plant growth regulators to suppress or<br />

minimize etiolated symptoms in turfgrass. However, other cultural and chemical<br />

practices are often used in conjunction with plant growth regulators, and therefore the<br />

exact cause of etiolated tiller symptoms in turfgrass can not be determined at this time.<br />

Therefore, this etiolated tiller complex in turfgrass warrants further study to determine<br />

the cause as well as possible management practices to help mitigate etiolated tiller<br />

symptoms in turfgrass.<br />

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USING PLANT GROWTH REGULATORS FOR ANNUAL BLUEGRASS REMOVAL. J.<br />

A. Borger and M. B. Naedel, Penn State University, University Park.<br />

ABSTRACT<br />

Most often, annual bluegrass (Poa annua L.) is considered a weed when growing<br />

in golf course fairways or greens and can be difficult to manage. Annual bluegrass is<br />

susceptible to adverse winter conditions, consequentially, there is a potential for voids in<br />

the sward being present in the spring of the year. Annual bluegrass is not drought<br />

tolerant. This can cause an increased irrigation demand during droughty periods in<br />

order to sustain the annual bluegrass population. Annual bluegrass has a low tolerance<br />

of many diseases. As a result, fairways and greens containing significant annual<br />

bluegrass must be managed for such diseases in addition to those of the creeping<br />

bentgrass (Agrostis stolonifera L.). The aforementioned disadvantages of annual<br />

bluegrass have an adverse impact on the aesthetics and playability of the turfgrass site<br />

and could increase the cost of maintaining a turfgrass community. The selective post<br />

emergence control of annual bluegrass has been quite varied over the years. Some<br />

compounds have worked well in certain locations and conditions, but have not been as<br />

successful in others. This variation will most likely persist, but there is a continued need<br />

for research to assess plant growth regulators (PGRs) and strategies for the selective<br />

post emergence control of annual bluegrass. Paclobutrazol (Trimmit ® ), flurprimidol<br />

(Cutless), ethofumesate (Prograss ® ), and bispyribac-sodium (Velocity ® ) are the most<br />

common PGRs employed to control annual bluegrass in a post emergence setting.<br />

Rates, application timing, and product rotation are only some of the factors to evaluate<br />

when using these products.<br />

103


USE OF PLANT GROWTH REGULATORS ON SPORTS TURF. S.D. Askew, Virginia<br />

Tech, Blacksburg.<br />

ABSTRACT<br />

The science of sports turf management continues to evolve. Plant growth<br />

regulators (PGRs) have been an important part of that evolution in the past 10 years.<br />

There are several ways in which plant growth regulators are used on sports fields with<br />

most uses aimed at reduction of clippings and reducing scalping. Trinexapac ethyl is<br />

the most common product in use but flurprimidol, paclobutrazol, ethephon, and<br />

mefluidide all have varying uses on different types of fields. Benefits of PGRs in athletic<br />

fields include reduced scalping, less equipment wear, fewer clippings on the field, faster<br />

mowing time, increased turfgrass density, improved stress tolerance, improved turfgrass<br />

color, pre-stress conditioning, and improved establishment of over-seeded grasses.<br />

Use of PGRs is more common on bermudagrass fields than on cool-season fields. With<br />

dense bermudagrass types, such as Tifway or Patriot, bermudagrass scalping is an<br />

issue any time mowing is delayed and especially in the fall when bermudagrass<br />

morphology changes due to changes in light quality and the peak in bermudagrass<br />

density is reached.<br />

Patriot bermudagrass has been widely adopted in Virginia and other states in the<br />

northern transition zone due to cold tolerance, aggressive growth and density. Because<br />

of Patriot’s aggressive growth habit, PGRs are becoming an important tool in managing<br />

this bermudagrass cultivar. Scalping is one of the most important issues with Patriot<br />

bermudagrass. Scalping issues increase with decreasing mowing height, increasing<br />

fertility applications, and irregular mowing frequency. PGRs such as trinexapac ethyl<br />

can reduce scalping but will not eliminate the problem. Athletic field managers in<br />

Virginia are finding that an “attitude adjustment” is in order to manage scalping of Patriot<br />

bermudagrass in the fall. The angle of a reel mower’s bed knife to the ground is called<br />

the “attitude.” As the angle is increased the attitude becomes more “aggressive” and as<br />

the angle is decreased the attitude becomes more “flat.” For putting green<br />

management, flat attitude is discouraged because it can cause streaks as the bedknife<br />

rubs the turf. At taller heights of cut, such as 1 to 2 cm, a flat attitude will not pose<br />

problems like it does on putting greens. Patriot bermudagrass becomes so dense in<br />

late summer that the bulk of its canopy is stolons capped with only a thin layer of<br />

leaves. Thus, routine PGR use, regular mowing, decreased fertility, and flat attitude are<br />

the best combination to combat scalping.<br />

When a PGR program is discontinued, turfgrass growth increases much beyond<br />

that of turfgrass that was not on a PGR program. Field mangers will use this<br />

phenomenon to advantage by discontinuing a PGR program briefly in conjunction with<br />

stressful events such as concerts or increased field use. PGRs are also useful to<br />

reduce growth of existing turfgrass when establishing an over-seeded species. PGR<br />

rates may be doubled and applied 1 to 7 days prior to over-seeding. Trinexapac ethyl is<br />

the best product for this use because it does not affect germination or emergence of<br />

seeded grasses. Ethephon, mefluidide, and paclobutrazol continue to be important<br />

PGRs in situations where cool-season fields are infested with annual bluegrass and<br />

seedhead production in spring reduces field quality during the sporting event.<br />

104


USING PLANT GROWTH REGULATORS ON GOLF COURSES IN THE MID-<br />

ATLANTIC REGION. S.J. Zontek, Director, USGA Green Section, Mid-Atlantic Region,<br />

Glenn Mills, PA.<br />

ABSTRACT<br />

Plant growth regulators (PGR) have become an essential part of golf course<br />

turfgrass management in the Mid-Atlantic region of the USA as well as in other parts of<br />

North America. In fact, the use of plant growth regulators has now extended to include<br />

the British Isles and the Republic of Ireland. Golf course turfgrass managers, once they<br />

experience the benefits from the use of plant growth regulators, they have readily been<br />

adopted into their golf course maintenance and management programs.<br />

This was not always the case. Initially, PGRs were used to control annual<br />

bluegrass (Poa annua) seedheads. Results were variable and some turf damage even<br />

occurred. When they did work, the results were spectacular. Turf managers began to<br />

see the utility of these materials. Research continued to a point where PGRs are used<br />

for any number of purposes on a golf course. These include; annual bluegrass<br />

seedhead suppression and control; annual bluegrass suppression and control; annual<br />

bluegrass maintenance; to regulate growth rates (and clipping production) on greens,<br />

tees, fairways and increasingly, in roughs.<br />

Plant growth regulators have become essential products in the maintenance of<br />

golf courses in the Mid-Atlantic region of the USA and beyond.<br />

105


NEWSS Executive Committee Final Report<br />

January 2007<br />

William Curran, President<br />

Over the past year it has been a pleasure to serve as your President. The Executive<br />

committee has discussed a number of issues and the key ones include the Future<br />

Committee Report and subsequent survey that will directly impact our future. You will<br />

fill out a survey at the annual meeting in an attempt to gauge your views and opinions<br />

about where our society should be headed. As an example of a new activity discussed<br />

by the EC, we are hosting an Awards Luncheon this year, so let us know what you<br />

think. With the guidance of David Spak, our Sustaining Membership Representative,<br />

we also developed a new sustaining membership fee structure; Jacob Barney<br />

championed a new Outstanding Graduate Student award, and several other key issues<br />

were addressed during the year.<br />

For 2007, Jerry Baron, VP and Program Chair with the help of many others have<br />

developed a great program at the Renaissance Harborplace in Baltimore. Although we<br />

tried to develop joint programs with a number of other organizations for 2007, we were<br />

unable to identify a successful partner that impacted our program in a significant way.<br />

This is the first year in several years that is a NEWSS program without other<br />

organizational involvement. Having said this, we all look forward to building more<br />

bridges and doing what we need to do to make this annual conference even more<br />

successful.<br />

We will be selling NEWSS Polo shirts for $30 at the annual meeting this year. These<br />

are great shirts that help support the society and also allow you to look smart while<br />

representing the NEWSS. Please support the NEWSS and buy a shirt.<br />

Finally, we are interested in conducting an annual invasive plants workshop for federal,<br />

state, and local people involved in invasive plant management. There is a strong need<br />

for this and we would like to discuss this potential opportunity at the annual meeting.<br />

We will be meeting on Friday at 1:30 pm to discuss this potential activity. Please join<br />

us.<br />

Renee Keese, President Elect<br />

Thank you letters were sent to all session chairs and the invited speakers immediately<br />

following the 2006 conference. The Collegiate <strong>Weed</strong> Contest was planned and<br />

implemented on August 1, 2006, sponsored by Greg Armel and DuPont and held at<br />

their Stine Haskell research facility in Newark, DE. We investigated several locations<br />

for the 2008 conference including the Cambridge Marriot and Long Wharf Marriott in<br />

Boston, the Westin Providence, and the Marriot, Loews, and Sheraton <strong>Society</strong> Hill in<br />

Philadelphia. The 2008 annual NEWSS Conference was booked at the Sheraton<br />

<strong>Society</strong> Hill in Philadelphia, PA for January 7-10th.<br />

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Joint meeting possibilities for 2008 appear slim. The NE-ESA and NE-APMS are not<br />

available. Dialog was opened with the Canadian weed science group, but they already<br />

have a site for 2008. Other options we could pursue still include training sessions<br />

perhaps with invasive species organizations. In 2007, the Collegiate <strong>Weed</strong> Contest will<br />

be hosted by the <strong>Weed</strong> <strong>Science</strong> group at Virginia Tech. Shawn Askew will be the key<br />

contact and they look forward to this opportunity and are seeking input for the event.<br />

For 2008, a Collegiate <strong>Weed</strong> Contest Site has not officially been determined, but Bayer<br />

and NCSU have discussed hosting a co-sponsored event. The Editor position on the<br />

Executive Committee will be filled by Greg Armel of DuPont, starting in January 2007.<br />

Jerry Baron, Vice President<br />

The theme for this January’s NEWSS Annual meeting in Baltimore, MD is Expanding<br />

our <strong>Weed</strong> <strong>Science</strong> Horizons. With that we have a full day general session as well at<br />

three exciting symposiums, one workshop and the traditional breakout sessions. The<br />

general session will include the traditional Presidential Address by Bill Curran entitled<br />

“The Times They Are A-Changing’”. Other speakers in this general session include Dr.<br />

Janice McFarland of Syngenta Crop Protection discussing Where is the next generation<br />

of <strong>Weed</strong> Scientists being trained?, Dr. Rich Bonanno discussing the NEWSS Futures<br />

Committee Recommendations, Dr. Leonard Gianessi of Crop Life America Foundation<br />

on The War of the <strong>Weed</strong>s, and myself speaking on New Technology in <strong>Weed</strong><br />

Management. The general session ends with a panel discussion on Government<br />

Influence in <strong>Weed</strong> <strong>Science</strong>: Legislation, Regulation and <strong>Science</strong> Funding. The is<br />

moderated by Dr. Daniel Kunkel and the participants include Dr. Rob Hedberg, USDA-<br />

CSREES, Mr. Donald Stubbs, US EPA and Dr. Lee Van Wychen. Also included in the<br />

General Session is an Awards Luncheon.<br />

On Friday, January 5 th , we have scheduled three exciting symposia. The topics of the<br />

symposia are (1) New and innovative herbicides compounds for turf and how they<br />

impact golf course maintenance; (2) An invasive weeds symposium with the theme of<br />

reforesting invaded riparian corridors; and (3) A horseweed biology/ecology symposium<br />

to lead to better ways of managing this troublesome biotype. We are inviting participants<br />

from outside the NEWSS to attend and participate in these symposiums. Please pass<br />

the information about these symposiums on to other you think that might have interest.<br />

Also on Friday, January 5 th is an organizational meeting to discuss the potential for an<br />

Invasive Plant Management Course in the Northeast. The Western <strong>Society</strong> of <strong>Weed</strong><br />

<strong>Science</strong> currently offers an invasive plant course that is very popular and well attended.<br />

Here we want to open the dialogue to discuss the need for an invasive plant course<br />

similar to the one offered by the WSWS, determine if the Northeast <strong>Weed</strong> <strong>Science</strong><br />

<strong>Society</strong> would like to sponsor/participate in such a course, identify a task<br />

group/committee that will plan, determine curriculum, instructors and organize and<br />

identify partners, organizations for development and sponsorship of the course.<br />

Chris Becker, Secretary/Treasurer<br />

107


The 60 th Annual Meeting of the Northeastern <strong>Weed</strong> <strong>Science</strong> <strong>Society</strong> was held (jointly<br />

with the Northeast Aquatic Plant Management <strong>Society</strong>) at the Westin Hotel in<br />

Providence, RI on January 3-6, 2006. The theme of the meeting was “Bridging<br />

Technology with Partnerships in Aquatic and Terrestrial <strong>Weed</strong> Control.” In addition to<br />

the typical seven sections, the conference was highlighted by three symposia:<br />

“Education and Outreach”, “Recent Advances in Nursery <strong>Weed</strong> Management”, and<br />

“Aquatic & Terrestrial <strong>Weed</strong> Control” (the latter brought together both societies and<br />

contained an aquatic plant and algae ID workshop). There were 196 people in<br />

attendance including 171 NEWSS members, 3 invited speakers, 7 attending only the<br />

Aquatics workshop, and 14 attending only the ornamentals workshop.<br />

Due to Brian Manley’s relocation to Switzerland, the EC acted according to the <strong>Society</strong><br />

Constitution and nominated a new Secretary/Treasurer to complete the term. Chris<br />

Becker accepted the responsibility and all files have been successfully transferred to<br />

him.<br />

A new address was set up for NEWSS secretary or treasurer related activities and<br />

correspondence and it is as follows:<br />

NEWSS<br />

PO Box 34; Romulus, NY 14541<br />

Timothy Dutt, Past President<br />

The Westin Providence Hotel was an excellent facility and venue for the 60 th Annual<br />

Meeting held in Rhode Island. We had a successful joint meeting with the Northeast<br />

Aquatic Plant Management <strong>Society</strong> (NEAPMS) with a total meeting attendance of 326<br />

which included 130 in attendance from NEAPMS. We met our room night commitment,<br />

and the hotel gave us a last minute concession which was not in our contract that saved<br />

both organizations considerable money in sponsoring the social. The total group bill for<br />

NEWSS from the hotel was settled at $10,282.<br />

The Awards Committee members for the 2007 annual meeting were: Tim Dutt (Chair),<br />

Robin Bellinder, Scott Glenn, Dave Mayonado, and Jeff Derr. We received and<br />

reviewed nominations for Distinguished Member, Outstanding Researcher, and<br />

Outstanding Educator. No nominations were received for the Award of Merit.<br />

Recommendations were submitted to the Executive Committee for approval at the<br />

October Board meeting. The Awards Committee also reviewed a proposal for a new<br />

award for Outstanding Graduate Student. The student paper contest judges at the 2007<br />

meeting will be Tim Dutt (Chair), Scott Glenn, Dave Mayonado, Jeff Derr, and Brian<br />

Olson. Dave Johnson will chair the Poster Judging Committee and Grant Jordon will<br />

chair the Photo Judging Committee. Roy Johnson chaired the Committee of Past<br />

Presidents.<br />

The archives for my year as President were given to the Archivist, Dan Kunkel. Items<br />

included the 2006 Program, <strong>Vol</strong>ume 60 Proceedings, the Awards Presentation of the<br />

60 th Annual Meeting, Newsletters (April, August, and November), minutes of the EC<br />

108


meetings (2006 Annual Business Meeting and EC meetings for January, March, July,<br />

and October), nomination letters for the <strong>Society</strong>’s Awards recipients, and the WSSA<br />

poster on History of the Northeastern <strong>Weed</strong> <strong>Science</strong> <strong>Society</strong> (1947-2006). Items for the<br />

awards brochure were prepared and plaques for the award recipients and the out-going<br />

President were purchased. No revisions were made to the MOP (Manual of Operating<br />

Procedures) with the last revisions made in October 2005 by Robin Bellinder.<br />

Hilary Sandler, Editor<br />

Two publications were produced for the 2007 Annual Meeting: the meeting program and<br />

the Annual Proceedings. The program (compiled by Jerry Baron) was 44 pages long<br />

with 103 titles (23 poster and 80 oral presentations), 20 symposia talks, and an<br />

organizational meeting for an Invasive Plant Management course. Three hundred and<br />

fifty (350) copies were purchased at a cost of $1,760. The programs were mailed out to<br />

current members in early December by the editor using first-class postage. The<br />

proceedings were 252 pages long and 225 copies were printed. One-hundred and fifty<br />

books were delivered to the hotel and 75 books were sent to Riverhead, NY for standing<br />

orders. Eighty-nine abstracts were printed in <strong>Vol</strong>ume 61. In addition, the Presidential<br />

address from the 2006 meeting and 2 abstracts from the Providence meeting were<br />

published in the supplement to the proceedings. The supplement also included 17<br />

abstracts from the Northeastern Aquatic Plant Management <strong>Society</strong> (joint meeting in<br />

Providence, RI in 2006). In 2007, approximately 86% of the authors who submitted<br />

titles also submitted abstracts (excluding symposium presentations). Instructions for<br />

Authors were modified slightly from the previous year.<br />

Approximately 210 programs were mailed to those currently registered as NEWSS<br />

members and to invited speakers; this was 160 fewer programs mailed than in 2005<br />

($100 savings in stamps alone). Members who received their program in the mail were<br />

strongly encouraged to bring the program to the meeting as fewer copies would be<br />

available. We received 250 proceedings for the 2007 meeting (we had requested 225<br />

copies, but received an extra 25 copies to due an administrative error).<br />

We successfully transferred our web site host server functionality to Small Orange in the<br />

spring 2006. This switch represents a significant cost savings to the society<br />

(approximately $45 per month for hosting services alone). We have engaged the<br />

services of Mr. Robert Dickerson of Penn State University to oversee the web site.<br />

After a small amount of initial confusion over passwords (carryover from Host Depot<br />

days), most members successfully submitted their abstracts and titles via the web site.<br />

We are still considering other options for web host service, such as banding with WSSA<br />

or other regions, but current plans are to stay with Small Orange until other financially<br />

viable options are available.<br />

Dwight Lingenfelter, Public Relations<br />

Over the last year, I have compiled and edited three NEWSS Newsletters and<br />

distributed them via email and on the web. I submitted two NEWSS News articles to the<br />

109


WSSA Newsletter (July and October) and took photos at major NEWSS events for<br />

inclusion in newsletters, website, and other media. At the 2006 annual meeting, I<br />

produced CD versions of Proceedings for interested individuals. For 2007, I directed<br />

the design and production of the NEWSS polo shirt. I also worked with Hilary Sandler in<br />

moving the website server (A Small Orange) to Penn State (Rob Dickerson) and have<br />

continued to work with our Webmaster and Editor.<br />

Kathie Kalmowitz, Research and Education Coordinator<br />

The Research and Education Committee has worked with the Program Chair in<br />

assisting organization for the symposiums that will be offered through the annual<br />

meeting in Baltimore. Organizers of the symposiums (Mark VanGessel- Horseweed;<br />

Turfgrass-Larry Norton; Riparian Management-Art Gover; and, a workshop focused on<br />

Research Methods in Ornamental <strong>Weed</strong> Control-James Altland) will have help from the<br />

society to publicize their session to attract both members and outside participants into<br />

the Annual Meeting. Symposium/Workshop Sessions invitations will target outside<br />

groups in the MidAltantic who may want to participate in these educational events such<br />

as the surrounding area GCSAA golf associations, the USGA Agronomists, Extension<br />

personnel and other turfgrass managers; also, for the Riparian symposium groups such<br />

as Mid Atlantic EPPC, Anacostia Watershed <strong>Society</strong>, Nature Conservancy and<br />

Wissahickon Restoration <strong>Vol</strong>unteers and others will be notified on the educational<br />

opportunities. The Ornamental Workshop designed for sharing research methods will<br />

have an open format with moderators chosen to lead topics with audience participation<br />

encouraged. Using fliers and direct contacts with outside groups, notification of these<br />

opportunities and the Annual Meeting program of the Northeast <strong>Weed</strong> <strong>Society</strong> meeting<br />

will be extended to groups of interest up until the date of the meeting in January. Oneday<br />

special non-member fees will be used on all fliers to encourage outreach<br />

participation. Application for Pesticide License CEU’s in states from Maine to North<br />

Carolina have been applied to as well as Agronomy <strong>Society</strong> sponsored Crop Advisor<br />

certification points. For all turfgrass participants who are members of the GCSAA,<br />

recertification credits have been applied for and the appropriate paperwork will be<br />

available at the Symposium.<br />

David Spak, Sustaining Membership<br />

The revised NEWSS Sustaining Membership fee structure was sent to all current<br />

sustaining members and prospective members for the year 2007. The tiered fee<br />

structure included platinum, gold, silver and bronze levels. The new fee system is<br />

attempting to simplify the process of sponsorship of the annual meeting and weed<br />

competition. Some of the proposed benefits will include increased recognition at the<br />

annual meeting, complimentary conference registrations, and weed competition<br />

sponsorship (see below).<br />

We have received commitment from 21 organizations for 2007 Sustaining Membership.<br />

This represents an increase in one member from 2006; a few members decided not to<br />

contribute this year for various reasons, and several new members are now on board.<br />

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Membership level was as follows: 2-Platinum, 5-Gold, 5-Silver, 9-Bronze for a total<br />

commitment of $13,750 and an increase in income of $5850 compared to 2006.<br />

Request had gone out to all sustaining members for company logos for recognition at<br />

the annual meeting, and most have been received. Several posters are being produced<br />

which will be displayed at the annual meeting. The posters will recognize the<br />

Sustaining members and their level of membership. Also, a PowerPoint slide is being<br />

made which will be given to Section Chairs to be used as a background.<br />

Membership<br />

Level<br />

Total<br />

Contribution*<br />

Includes<br />

Complimentary<br />

Conference<br />

Registration(s)**<br />

Includes<br />

Collegiate<br />

<strong>Weed</strong> Contest<br />

Support<br />

Platinum $2000 2 $1000<br />

Gold $1000 1 $500<br />

Silver $500 1 none<br />

Bronze $250 none none<br />

*Supports social events, coffee breaks, and general meeting costs.<br />

** Approximate value $160 per registration.<br />

Jacob Barney, Graduate Student Representative<br />

Survey of <strong>Weed</strong> Contest participants was conducted via email to all students and<br />

coaches. I received about 5 replies to the survey (a typical response rate). Results of<br />

this survey will be presented to the <strong>Weed</strong> Contest Committee in January.<br />

Dialogue began with the EC and coaches of weed contest teams regarding alcohol and<br />

student behavior at the weed contest. This will also be a topic of discussion during the<br />

meeting of the <strong>Weed</strong> Contest Committee.<br />

I proposed a new award to recognize Outstanding Graduate Students in NEWSS. The<br />

OGSA will recognize a maximum of one masters and one doctoral student annually<br />

based on specified criteria and will be based on nominations. The proposal for OGSA<br />

was unanimously approved by the EC and was sent to the Awards Committee for final<br />

approval and incorporation into the 2007 NEWSS program.<br />

My replacement as NEWSS GSR will be Matt Ryan from Penn State, who will be<br />

assuming responsibility in January.<br />

Toni DiTommaso, WSSA Representative<br />

The 47 th WSSA Annual meeting to be held at the Riverwalk Hyatt Regency Hotel in San<br />

Antonio, TX February 4-8, 2007. The annual meeting will begin on Monday, February 5<br />

at 4:15 p.m. with the General Session and Awards Ceremony followed by the<br />

Awardees Reception. Dr. Gale Buchanan, USDA Under Secretary for Research,<br />

Education, and Economics has accepted our invitation to share his vision on the future<br />

of Agricultural Research at the general session. On Wednesday, plan on attending the<br />

111


society business meeting followed by our second member reception. Additional<br />

program highlights include:<br />

Graduate Student Activities: John Willis, President, and the Graduate Student<br />

Organization are making plans for a symposium titled “Employment Opportunities and<br />

How to make Yourself More Marketable” Tuesday morning followed by a luncheon<br />

meeting. One of the presentations will be made by Holly Menninger of the American<br />

Institute of Biological <strong>Science</strong>s on “Techniques and Tips for Communicating Your<br />

<strong>Science</strong> to the Media”. The students also plan to initiate a Student Night Out Activity<br />

where non-student members pair with students to become acquainted over dinner and<br />

discussion. This has been a successful and popular activity at the Western <strong>Society</strong> of<br />

<strong>Weed</strong> <strong>Science</strong> annual meeting since it was proposed by Steve Dewey in 2002.<br />

Symposia: Three symposia, in addition to the graduate student symposium, are<br />

planned for the meeting. The <strong>Weed</strong> Biology and Physiology Sections have joined to<br />

offer a symposium “Using Emerging Technologies to Study <strong>Weed</strong> Biology: an<br />

educational forum” on Tuesday afternoon. James V. Anderson and Wun S. Chao are<br />

organizing this session and plan to invite vendors whose products complement the<br />

topics to display at the meeting. Debanjan Sanyal is organizing the second symposium<br />

“Integrated <strong>Weed</strong> Management Revisited” which will be held on Wednesday afternoon.<br />

Finally, a day long symposium “Nursery Stock vs. Invasive Plant: Which is it, and why<br />

do we care?” will be held on Thursday and is being organized by Alan Tasker and<br />

Nelroy Jackson in conjunction with the Turf and Ornamentals, Wildland and Aquatic<br />

Invasives and Regulatory Affairs sections. They will be advertising this symposium to<br />

attract a broad audience including local residents.<br />

Roundtable Discussions and Mini-Symposia: The board of directors is planning a noontime<br />

Roundtable discussion to provide information and obtain member input about the<br />

proposed new society journal “Journal of Invasive Plant <strong>Science</strong> and Management”.<br />

Fred Salzman, Chair, is planning a Specialty Crop Roundtable Discussion as part of the<br />

Horticulture Section of the meeting. This will be an informal discussion of research<br />

results and issues that are common across the regions. Susan Sun is planning a panel<br />

discussion: Building Bridges between Industry and Academia in Formulation and<br />

Adjuvant Technology as part of the Formulation, Adjuvant, and Application Technology<br />

session. The Education and Extension session Thursday afternoon will include a minisymposium<br />

that discusses first year results of a multi-state project designed to<br />

investigate long-term weed shifts in Roundup Ready crops.<br />

National Research Initiative Project Meeting: Michael A. Bowers, CSREES<br />

National Program Leader-Ecology is chairing the 2007 Project Director meeting for the<br />

NRI Program, Biology of <strong>Weed</strong>y and Invasive Species in Agro-ecosystems at the WSSA<br />

meeting. Project directors will be presenting their research within the poster session. In<br />

addition, the directors will participate in a discussion session and poster session<br />

Tuesday afternoon that is open to all society members.<br />

112


Jill Schroeder, Program Chair for the 2007 WSSA Annual Meeting, as well as program<br />

section chairs and symposium organizers have worked hard to develop a strong<br />

program for the meeting and they look forward to seeing you in warm San Antonio in<br />

February! The WSSA website can be found at www.wssa.net .<br />

Robert Sweet, CAST Rep<br />

This past year was one of significant changes which have resulted in: improved morale<br />

of paid staff, closing of the expensive D.C. Office, a wider area of outreach, several<br />

shorter but timely publications. Unfortunately no improvement in the tight budget<br />

situation.<br />

CAST had been slowly losing productivity so in January the EVP left. The position was<br />

widely advertised and 21 worthy applications were received. The EC narrowed the list<br />

to 3 who were invited to the spring board meeting. The decision was difficult because<br />

they were excellent. Finally Dr. James Bonner an animal scientist from “Land of Lakes”<br />

was selected. He came on the job July 1st and has already proven to be a fine choice.<br />

On August l, the office manager left under a cloud. No replacement yet.<br />

To help ease the budget problems a serious effort is being made to increase<br />

memberships in all classes, including individuals and local agricultural businesses.<br />

Dan Kunkel, Legislative Liaison and Lee Van Wychen, WSSA Director of <strong>Science</strong><br />

Policy<br />

Beginning, Mid-Career, and Retired <strong>Weed</strong> Scientists: Apply for AAAS Fellowship<br />

The American Association for the Advancement of <strong>Science</strong> (AAAS) solicits candidates<br />

from a broad array of disciplinary backgrounds to apply for a year-long <strong>Science</strong> and<br />

Technology Policy Fellowship in Washington DC. Fellows come from a range of<br />

sectors, including academia, industry, and non-profits, representing a spectrum of<br />

career stages, from recent PhD graduates to faculty on sabbatical, to retired scientists<br />

and engineers. The age span in the past five classes of Fellows has been from the late<br />

twenties to early seventies. The AAAS also serves as the “umbrella” organization for<br />

other scientific societies that sponsor a Fellow, such as the Agronomy, Crop and Soil<br />

<strong>Science</strong> Societies.<br />

The Fellowship is a great opportunity to work closely with federal decision-makers in<br />

agencies such as the USDA, EPA and the National <strong>Science</strong> Foundation among others.<br />

Fellows receive a stipend of up to $87,000 for the year, which is based on years of<br />

professional experience. Relocation expenses of up to $3500 are also provided. The<br />

deadline for applications for the 2007-2008 Fellowship class is December 20, 2006. For<br />

more information, please visit: http://fellowships.aaas.org<br />

Applying for Federal Job Related to <strong>Weed</strong> <strong>Science</strong><br />

113


In June, the Office of Personnel Management (OPM) rejected the proposal for a federal<br />

job series classification of weed science. In fact, OPM rejected every one of the job<br />

series classifications requested by USDA and combined or eliminated some other job<br />

series. There are several factors for this, but if you look at the newest federal job series<br />

created, they are in the technology sector like “Information Technology Specialist”.<br />

OPM has been working to “simplify” jobs to cater to the “re-toolable generalist”<br />

approach. This is OPM’s final decision in a project that began in 1997 to develop a Job<br />

Family Position Classification Standard (JFS) for professional work in the Biological<br />

<strong>Science</strong>s Group, 0400. The new GS-400 classification standard can be viewed at:<br />

http://www.opm.gov/fedclass/gs0400p.pdf. This 99 page document describes OPM’s<br />

decisions in detail.<br />

Not to panic weed scientists. The upside of this is anyone graduating with a degree<br />

related to weed science or invasive plant management will qualify for just about any job<br />

listed under the “GS-401: General Natural Resources and Biological <strong>Science</strong>s” job<br />

series. In addition, many weed science graduates qualify for other GS-400 series jobs<br />

such as agronomy, horticulture, botany, plant physiology, forestry, rangeland, and<br />

ecology positions. To search all Federal jobs, please visit USA jobs at:<br />

http://www.usajobs.gov<br />

I will continue to work with the Federal Agencies that hire and employ individuals<br />

required to have more specialized training in weed science and invasive plant<br />

management in order to help them include more specific language that defines the<br />

knowledge, skills, and abilities necessary in our discipline.<br />

WSSA Submits Comments on APHIS Plant Protection and Quarantine Rule<br />

In June, I worked with the WSSA’s Federal Noxious and Invasive <strong>Weed</strong>s Committee<br />

(E4) to gather comments on how the USDA Animal and Plant Health Inspection Service<br />

(APHIS) can improve their Plant Protection and Quarantine (PPQ) Regulations. Thanks<br />

to Jen <strong>Vol</strong>lmer for her extensive remarks. Under the Plant Protection Act, states cannot<br />

enact more stringent regulations governing a pest or weed than the rules that APHIS<br />

has imposed. However, when APHIS is silent, states may act. The Plant Protection Act<br />

provides that States may obtain an exemption from the Secretary of Agriculture if that<br />

State faces a particularly severe threat - but no State has yet been granted such an<br />

exemption.<br />

The overall goal of this rule was to better define the process that States would pursue to<br />

petition APHIS. The WSSA urged APHIS to delete proposed language requiring that<br />

subdivisions of State act only through the State, and instead implement the Plant<br />

Protection Act’s broader exemption that extends to allow political subdivisions to make<br />

requests to APHIS directly. We also urged APHIS to add language to articulate the<br />

agency’s process in circumstances where insufficient evidence may be present, and to<br />

provide additional guidance regarding the quantity and quality of data required by<br />

APHIS to support a Special Needs Request.<br />

114


USDA-ARS Software Available for Site-Specific <strong>Weed</strong> Management<br />

Scientists in the USDA-ARS Water Management Research Unit at Fort Collins, CO<br />

have developed a software program to assist farmers in determining the best sitespecific<br />

weed management (SSWM) strategy for their fields. The software, called<br />

“<strong>Weed</strong>Site” was co-developed by WSSA member Lori Wiles and can be downloaded for<br />

free at: http://arsagsoftware.ars.usda.gov<br />

Growers draw weed maps of their fields based on a simple low-cost method that uses a<br />

digital camera and a GPS unit. The software identifies weeds within the photographs,<br />

and then constructs a weed map with links to the photos. <strong>Weed</strong>Site then uses that<br />

information to calculate the effects of various SSWM practices.<br />

EPA Publishes New Pesticide Container and Containment Rule<br />

In August, the EPA published its final rule establishing standards for pesticide<br />

containers and containment. The rule, which will be implemented over the next 3 to 5<br />

years, establishes standards for refillable and non-refillable containers, including design<br />

specifications for rinsing, durability, and standardized closures. Triple rinsing or<br />

pressure rinsing to the 99.99 percent removal standard was considered an important<br />

adoption in the final regulations. The rule also requires pesticide labels to provide<br />

instructions on how to properly clean containers before disposal or recycling.<br />

The regulations affect registrants, distributors, dealers, commercial applicators, and<br />

custom blenders, but do not extend to containment at individual farms. The rule is<br />

intended to promote the safe refill and reuse of refillable containers and to ensure that<br />

pesticides will be stored and transferred under conditions that prevent spills and<br />

releases of pesticides into the environment. Additional information about the rule and<br />

who is affected can be found at:<br />

http://www.epa.gov/pesticides/regulating/containers.htm<br />

USDA Awards $4.1 Million in Grants to Manage Invasive Species Affecting Grazing<br />

Lands<br />

On July 28, USDA Under Secretary for Natural Resources and Environment Mark Rey<br />

awarded $4.1 million to fund projects to manage and control invasive plants, animals or<br />

insects that adversely affect private and tribal grazing lands. Twenty-seven projects in<br />

20 states received grants ranging from $50,000 to $300,000. This is the first year for<br />

this grant program.<br />

All of the 27 projects involved some aspect of invasive weed management. Grant<br />

awardees ranged from county weed control and management districts to non-profit<br />

groups, universities, and state departments of agriculture. The funds are administered<br />

through the NRCS Grazing Lands Conservation Initiative (GLCI). To view the full listing<br />

of grants and to get more information about the GLCI, please visit:<br />

www.nrcs.usda.gov/programs/glci.<br />

115


Category<br />

NEWSS Financial Statement for 2006<br />

November 1, 2006 to October 31, 2007<br />

Prepared by Chris Becker<br />

Revenue<br />

Amount<br />

Annual Meeting Registration $9,905.00<br />

Coffee Break Support $2,400.00<br />

Individual Membership $2,850.00<br />

Interest Income $793.15<br />

Proceedings $4,545.81<br />

CD's $220.00<br />

Sustaining Membership $3,000.00<br />

Symposium $750.00<br />

<strong>Weed</strong> Contest $2,500.00<br />

Total Revenue $26,963.96<br />

Expenses<br />

Administration $610.00<br />

Annual Meeting $11,540.86<br />

Annual Meeting Awards $1,565.78<br />

CAST $1,328.80<br />

Insurance $233.89<br />

Newsletter $0.00<br />

Proceedings $3,018.16<br />

Programs (Annual Meeting) $1,622.00<br />

Student Room Reimbursement $2,217.12<br />

Website $767.50<br />

<strong>Weed</strong> Contest $402.00<br />

WSSA Director of <strong>Science</strong> Policy $994.90<br />

Total Expenses $24,301.01<br />

Total Revenue - Expenses (Excess or Deficit) $2,662.95<br />

October 31, 2005 Savings Certificate Accounts (IDS - Ameriprise Financial) $22,669.10<br />

October 31, 2005 Bank of America Savings Account $22,839.26<br />

October 31, 2005 Bank of America Checking Account $176.62<br />

Total Net Worth October 31, 2005 $45,684.98<br />

October 31, 2006 Savings Certificate Accounts (IDS - Ameriprise Financial) $23,274.67<br />

October 31, 2006 Bank of America Savings Account $27,687.43<br />

October 31, 2006 Bank of America Checking Account $2,922.19<br />

Total Net Worth October 31, 2006 $53,884.29<br />

The Northeastern <strong>Weed</strong> <strong>Science</strong> <strong>Society</strong> Checking Account, Savings Account and Money Market<br />

Accounts were reviewed by the undersigned and are in order.<br />

David Johnson<br />

Melissa Bravo<br />

116


NEWSS PAST PRESIDENTS<br />

Gilbert H. Ahlgren 1947-49<br />

Robert D. Sweet 1949-50<br />

Howard L. Yowell 1950-51<br />

Stephen M. Raleigh 1951-52<br />

Charles E. Minarik 1952-53<br />

Robert H. Beatty 1953-54<br />

Albin O. Kuhn 1954-55<br />

John Van Geluwe 1955-56<br />

L. Danielson 1956-57<br />

Charles L. Hovey 1957-58<br />

Stanford N. Fertig 1958-59<br />

Gordon Utter 1959-60<br />

E. M. Rahn 1960-61<br />

Lawrence Southwick 1961-62<br />

Donald A. Shallock 1962-63<br />

Anthony J. Tafuro 1963-64<br />

Robert A. Peters 1964-65<br />

Gideon D. Hill 1965-66<br />

Richard D. Ilnicki 1966-67<br />

John E. Gallagher 1967-68<br />

John A. Meade 1968-69<br />

Homer M. Lebaron 1969-70<br />

John F. Ahrens 1970-71<br />

George H. Bayer 1971-72<br />

Arthur Bing 1972-73<br />

Ralph Hansen 1973-74<br />

Walter A. Gentner 1974-75<br />

Henry P. Wilson 1975-76<br />

Richard J. Marrese 1976-77<br />

C. Edward Beste 1977-78<br />

James D. Riggleman 1978-79<br />

James V. Parochetti 1979-80<br />

M. Garry Schnappinger 1980-81<br />

Raymond B. Taylorson 1981-82<br />

Stephan Dennis 1982-83<br />

Thomas L. Watschke 1983-84<br />

James C. Graham 1984-85<br />

Russell R. Hahn 1985-86<br />

Edward R. Higgins 1986-87<br />

Maxwell L. McCormack 1987-88<br />

Roy R. Johnson 1988-89<br />

Stanley F. Gorski 1989-90<br />

John B. Dobson 1990-91<br />

Prasanta C. Bhowmik 1991-92<br />

Stanley W. Pruss 1992-93<br />

Ronald L. Ritter 1993-94<br />

Wayne G. Wright 1994-95<br />

Bradley A. Majek 1995-96<br />

Thomas E. Vrabel 1996-97<br />

Joseph C. Neal 1997-98<br />

David B. Vitolo 1998-99<br />

A. Richard Bonanno 1999-00<br />

Brian D. Olson 2000-01<br />

Jeffrey F. Derr 2001-02<br />

David J. Mayonado 2002-03<br />

D. Scott Glenn 2003-04<br />

Robin R. Bellinder 2004-05<br />

Timothy E. Dutt 2005-06<br />

William S. Curran 2006-07<br />

117


AWARD OF MERIT<br />

1971 Gilbert H. Ahlgren Rutgers University<br />

Homer Neville<br />

L.I. Ag. & Tech, Farmingdale, NY<br />

Claude E. Phillips<br />

University of Delaware<br />

M. S. Pridham Cornell University<br />

Stephen A. Raleigh<br />

Penn State University<br />

1972 Robert Bell University of Rhode Island<br />

Stuart Dunn<br />

University of New Hampshire<br />

Alfred Fletcher<br />

NJ State Dept. of Health<br />

Frank N. Hewetson<br />

Penn Fruit Res. Lab.<br />

Madelene E. Pierce<br />

Vassar College<br />

Collins Veatch<br />

West Virginia University<br />

Howard L. Yowell<br />

Esso Research Lab.<br />

1973 Moody F. Trevett University of Maine<br />

1974 Robert H. Beatty Amchem Products, Inc.<br />

Arthur Hawkins<br />

University of Connecticut<br />

1975 Philip Gorlin NY City Environ. Cont.<br />

Herb Pass<br />

CIBA-GEIGY Corp.<br />

Robert D. Sweet<br />

Cornell University<br />

1976 C. E. Langer University of New Hampshire<br />

Charles E. Minarik<br />

US Dept. of Agriculture-ARS<br />

Herb Pass<br />

CIBA-GEIGY Corp.<br />

1977 L. L. Danielson US Dept. of Agriculture-ARS<br />

Madelene E. Pierce<br />

Vassar College<br />

Lawrence Southwick<br />

Dow Chemical Company<br />

John Stennis<br />

US Bureau of Fish & Wildlife<br />

1978 None Awarded<br />

1979 Carl M. Monroe Shell Chemical Company<br />

Charles Joseph Noll<br />

Penn State University<br />

Jonas Vengris<br />

University of Massachusetts<br />

1980 Otis F. Curtis, Jr. NY Agricultural Experiment Sta.<br />

Theodore R. Flanagan<br />

University of Vermont<br />

Oscar E. Shubert<br />

Virginia University<br />

1981 Dayton L. Klingman US Dept. of Agriculture-ARS<br />

Hugh J. Murphy<br />

University of Maine<br />

John Van Geluwe<br />

CIBA-GEIGY Corp.<br />

1982 Robert D. Shipman Penn State University<br />

1983 Arthur Bing Cornell University<br />

William E. Chappel<br />

Virginia Tech<br />

Barbara H. Emerson<br />

Union Carbide Agricultural Prod.<br />

1984 William H. Mitchell University of Delaware<br />

Roger S. Young<br />

West Virginia University<br />

1985 John A. Jagschitz University of Rhode Island<br />

1986 John R. Havis University of Massachusetts<br />

1987 None Awarded<br />

118


1988 J. Lincoln Pearson University of Rhode Island<br />

1989 Robert A. Peter University of Connecticut<br />

1990 Bryant L. Walworth American Cyanamid Co.<br />

1991 Don Warholic Cornell University<br />

1992 Robert Duel Rutgers University<br />

Richard Ilnicki<br />

Rutgers University<br />

William V. Welker<br />

USDA/ARS<br />

1993 None Awarded<br />

1994 John F. Ahrens CT Agricultural Experiment Sta.<br />

John B. Dobson<br />

American Cyanamid<br />

J. Ray Frank USDA-ARS/IR-4<br />

1995 Francis J. Webb University of Delaware<br />

1996 Robert M. Devlin University of Massachusetts<br />

Wilber F. Evans<br />

Rhone-Poulenc Ag. Co.<br />

Raymond B. Taylorson<br />

University of Rhode Island<br />

S. Wayne Bingham Virginia Tech<br />

1997 Jean P. Cartier Rhone-Poulenc Ag. Co.<br />

1998 Stan Pruss Novartis Crop Protection<br />

Max McCormack, Jr.<br />

University of Maine<br />

1999 None Awarded<br />

2000 Richard J. Marrese Hoechst-NorAm<br />

2001 Nathan L. Hartwig Penn State University<br />

Edward R. Higgins<br />

Novartis Crop University<br />

2002 Garry Schnappinger Syngenta Crop Protection<br />

2003 None Awarded<br />

2004 C. Edward Beste University of Maryland-Emeritus<br />

James C. Graham<br />

Monsanto (retired)<br />

2005 Thomas L. Watschke Penn State University<br />

2006 Steve Dennis Syngenta Crop Protection<br />

2007 None awarded<br />

119


DISTINGUISHED MEMBERS<br />

1979 George H. Bayer Agway, Inc.<br />

Robert A. Peters<br />

University of Connecticut<br />

Robert D. Sweet<br />

Cornell University<br />

1980 John F. Ahrens CT Agricultural Experiment Sta.<br />

John E. Gallagher<br />

Union Carbide Agric. Prod.<br />

Richard Ilnicki<br />

Rutgers University<br />

1981 Robert H. Beatty Amchem Products, Inc.<br />

Arthur Bing<br />

Cornell University<br />

John A. Meade<br />

Rutgers University<br />

1982 Walter A. Gentner US Dept. of Agriculture-ARS<br />

Hugh J. Murphy<br />

University of Maine<br />

1983 L. L. Danielson US Dept. of Agriculture-ARS<br />

1984 Barbara H. Emerson Union Carbide Agric. Prod.<br />

Henry P. Wilson<br />

Virginia Tech<br />

1985 None Awarded<br />

1986 Chiko Haramaki Penn State University<br />

Dean L. Linscott<br />

USDA-ARS/Cornell University<br />

1987 Gideon D. Hill E. I. DuPont DeNemours<br />

Williams V. Welker<br />

US Dept. of Agric-ARS<br />

1988 Wendell R. Mullison Dow Chemical<br />

James V. Parochetti<br />

US Dept. of Agriculture-CSRS<br />

1989 None Awarded<br />

1990 Robert M. Devlin University of Massachusetts<br />

1991 John (Jack) B. Dobson American Cyanamid<br />

Robert D. Shipman<br />

Penn State University<br />

1992 Gary Schnappinger Ciba-Geigy Corp.<br />

1993 Steve Dennis Zeneca Ag. Products<br />

James Graham<br />

Monsanto Ag. Co.<br />

1994 Russell Hahn Cornell University<br />

Maxwell McCormick<br />

University of Maine<br />

1995 Richard Ashly University of Connecticut<br />

Richard Marrese<br />

Hoechst-NorAm<br />

1996 Roy R. Johnson Waldrum Specialist Inc.<br />

Edward R. Higgins<br />

Ciba Crop Protection<br />

1997 Raymond B. Taylorson UDSA-ARS<br />

Wayne G. Wright<br />

DowElanco<br />

Stanley F. Gorski<br />

Ohio State University<br />

1998 Prasanta Bhowmik University of Massachusetts<br />

1999 C. Edward Beste University of Maryland<br />

2000 J. Ray Frank IR-4 Project<br />

Stanley W. Pruss<br />

Ciba Crop Protection<br />

2001 Ronald L. Ritter University of Maryland<br />

120


DISTINGUISHED MEMBERS<br />

2002 Bradley A. Majek Rutgers University<br />

Thomas L. Watschke<br />

Penn State University<br />

2003 Nathan L. Hartwig Penn State University<br />

2004 C. Benjamin Coffman USDA<br />

Joseph C. Neal<br />

North Carolina State University<br />

2005 David Vitolo Syngenta Crop Protection<br />

2006 A. Richard Bonnano University of Massachusetts<br />

Thomas Vrabel<br />

Eco Soil Systems, Central H.S.<br />

2007 Larry Kuhns Penn State University<br />

Brian Olsen<br />

Dow Agrosciences<br />

OUTSTANDING RESEARCHER AWARD<br />

1999 Garry Schnappinger Novartis Crop Protection<br />

2000 Prasanta C. Bhowmik University of Massachusetts<br />

2001 Robin Bellinder Cornell University<br />

2002 Jerry J. Baron IR-4 Project, Rutgers University<br />

2003 Arthur E. Gover Penn State University<br />

2004 Mark J. VanGessel University of Delaware<br />

2005 Bradley A. Majek Rutgers University<br />

2006 Grant Jordan ACDS Research<br />

2007 Peter Dernoeden University of Maryland<br />

OUTSTANDING EDUCATOR AWARD<br />

1999 Douglas Goodale SUNY Cobleskill<br />

2000 Thomas L. Watschke Penn State University<br />

2001 C. Edward Beste University of Maryland<br />

2002 E. Scott Hagood Virginia Tech University<br />

2003 Andrew F. Senesac Cornell University<br />

2004 William S. Curran Pennsylvania State University<br />

2005 Antonio DiTomasso Cornell University<br />

2006 Russell Hahn Cornell University<br />

2007 Prasanta Bhowmik University of Massachusetts<br />

121


OUTSTANDING GRADUATE STUDENT PAPER CONTEST<br />

1979 1 Bradley Majek Cornell University<br />

2 Betty J. Hughes Cornell University<br />

1980 1 John Cardi Penn State University<br />

2 Timothy Malefyt Cornell University<br />

1981 1 A. Douglas Brede Penn State University<br />

2 Ann S. McCue Cornell University<br />

1982 1 Thomas C. Harris University of Maryland<br />

2 Barbara J. Hook University of Maryland<br />

HM L. K. Thompson Virginia Tech<br />

HM Timothy Malefyt Cornell University<br />

1983 1 Anna M. Pennucci University of Rhode Island<br />

2 Michael A. Ruizzo Ohio State University<br />

HM I. M. Detlefson Rutgers University<br />

1984 1 Robert S. Peregoy University of Maryland<br />

2 Ralph E. DeGregorio University of Connecticut<br />

1985 1 Stephan Reiners Ohio State University<br />

2 Erin Hynes Penn State University<br />

1986 1 Elizabeth Hirsh University of Maryland<br />

2 (tie) Ralph E. DeGregorio University of Connecticut<br />

2 (tie) Avraham Y. Teitz Ohio State University<br />

1987 1 Russell W. Wallace Cornell University<br />

2 (tie) Daniel E. Edwards Penn State University<br />

2 (tie) Frank J. Himmelstein University of Massachusetts<br />

1988 1 William K. Vencill Virginia Tech<br />

2 Lewis K. Walker Virginia Tech<br />

HM Scott Guiser Penn State University<br />

HM Frank J. Himmelstein University of Massachusetts<br />

1989 1 Frank S. Rossi Cornell University<br />

1 Amy E. Stowe Cornell University<br />

1990 1 William J. Chism Virginia Tech<br />

2 Russell W. Wallace Cornell University<br />

122


1991 1 Elizabeth Maynard Cornell University<br />

2 Daniel L. Kunkel Cornell University<br />

1992 1 J. DeCastro Rutgers University<br />

2 Ted Blomgren Cornell University<br />

3 Fred Katz Rutgers University<br />

1993 1 Eric D. Wilkens Cornell University<br />

2 Henry C. Wetzel University of Maryland<br />

1994 1 Jed B. Colquhoun Cornell University<br />

2 Eric D. Wilkins Cornell University<br />

1995 1 Sydha Salihu Virginia Tech<br />

2 John A. Ackley Virginia Tech<br />

HM Jed B. Colquhoun Cornell University<br />

1996 1 Dwight Lingenfelter Penn State University<br />

2 Mark Issacs University of Delaware<br />

HM Jed B. Colquhoun Cornell University<br />

1997 1 David Messersmith Penn State University<br />

2 Sowmya Mitra University of Massachusetts<br />

HM Mark Issacs University of Delaware<br />

1998 1 Dan Poston Virginia Tech<br />

2 Travis Frye Penn State University<br />

3 David B. Lowe Clemson University<br />

1999 1 Hennen Cummings North Carolina State University<br />

2 John Isgrigg North Carolina State University<br />

2000 1 Matthew Fagerness North Carolina State University<br />

2 Steven King Virginia Tech<br />

3 Gina Penny North Carolina State University<br />

2001 1 Robert Nurse University of Guelph<br />

2 (tie) W. Andrew Bailey Virginia Tech<br />

2 (tie) Steven King Virginia Tech<br />

2002 1. G. Michael Elston University of Massachusetts<br />

2. Caren A. Judge North Carolina State University<br />

2003 1. Matt Myers Penn State University<br />

2. J. Scott McElroy North Carolina State University<br />

3. Robert Nurse Cornell University<br />

123


2004 1. Whitnee L. Barker Virginia Poly Inst. & State Univ.<br />

2. Caren A. Judge North Carolina State University<br />

3. Erin R. Haramoto University of Maine<br />

2005 1. Jacob Barney Cornell University<br />

2. Steven Mirsky Penn State University<br />

2006 1. Steven Mirsky Penn State University<br />

1. Robert Shortell Rutgers University<br />

2. Bryan Dillehay Penn State University<br />

2007 1. Bryan Dillehay Penn State University<br />

2. John Willis Virginia Poly Inst. & State Univ.<br />

3. Glenn Evans Cornell University<br />

124


COLLEGIATE WEED CONTEST WINNERS<br />

1983 - Wye Research Center, Maryland<br />

Graduate Team: University of Guelph<br />

Undergraduate Team: Penn State University<br />

Graduate Individual: Mike Donnelly, University of Guelph<br />

Undergraduate Individual: Bob Annet, University of Guelph<br />

1984 - Rutgers Research and Development Center, Bridgeton, New Jersey<br />

Graduate Team: University of Guelph<br />

Undergraduate Individual: D. Wright, University of Guelph<br />

Graduate Individual: N. Harker, University of Guelph<br />

1985 – Rohm and Haas, Spring House, Pennsylvania<br />

Graduate Team: University of Maryland<br />

Undergraduate Individual: Finlay Buchanan, University of Guelph<br />

Graduate Individual: David Vitolo, Rutgers University<br />

1986 - FMC, Princeton, New Jersey<br />

Graduate Team:<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: R. Jain, Virginia Tech<br />

Undergraduate Individual: Bill Litwin, University of Guelph<br />

1987 - DuPont, Newark, Delaware<br />

Graduate Team: University of Guelph<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Lewis Walker, Virginia Tech<br />

Undergraduate Individual: Allen Eadie, University of Guelph<br />

1988 - Ciba-Geigy Corp., Hudson, New York<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: University of Guelph<br />

Undergraduate Individual: Del Voight, Penn State University<br />

Graduate Individual: Carol Moseley, Virginia Tech<br />

1989 - American Cyanamid, Princeton, New Jersey<br />

Graduate Team: Cornell University<br />

Undergraduate Team: SUNY Cobleskill<br />

125


Graduate Individual: Paul Stachowski, Cornell University<br />

Undergraduate Individual: Anita Dielman, University of Guelph<br />

1990 - Agway Farm Research Center, Tully, New York<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: SUNY Cobleskill<br />

Graduate Individual: Brian Manley, Virginia Tech<br />

Undergraduate Individual: Dwight Lingenfelter, Penn State University<br />

1991 - Rutgers University, New Brunswick, New Jersey<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Carol Moseley, Virginia Tech<br />

Undergraduate Individual: Tim Borro, University of Guelph<br />

1992 - Ridgetown College, Ridgetown, Ontario, CANADA<br />

Graduate Team: Michigan State University<br />

Undergraduate Team: Ohio State<br />

Graduate Individual: Troy Bauer, Michigan State University<br />

Undergraduate Individual: Jeff Stackler, Ohio State University<br />

1993 - Virginia Tech, Blacksburg, Virginia<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: SUNY Cobleskill<br />

Graduate Individual: Brian Manley, Virginia Tech<br />

Undergraduate Individual: Brian Cook, University of Guelph<br />

1994 - Lower Eastern Shore Research and Education Center, Salisbury, Maryland<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Brian Manley, Virginia Tech<br />

Undergraduate Individual: Robert Maloney, University of Guelph<br />

1995 - Thompson Vegetable Research Farm, Freeville, New York<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Dwight Lingenfelter, Penn State University<br />

Undergraduate Individual: Jimmy Summerlin, North Carolina<br />

State University<br />

126


1996 - Penn State Agronomy Farm, Rock Springs, Pennsylvania<br />

Graduate Team: Michigan State University<br />

Undergraduate Team: SUNY, Cobleskill<br />

Graduate Individual: John Isgrigg, North Carolina State University<br />

Undergraduate Individual: Mark Brock, University of Guelph<br />

1997 - North Carolina State University, Raleigh, North Carolina<br />

Graduate Team: Michigan State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Brett Thorpe, Michigan State University<br />

1998 - University of Delaware, Georgetown, Delaware<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Shawn Askew, North Carolina State University<br />

Undergraduate Individual: Kevin Ego, University of Guelph<br />

1999 - Virginia Tech, Blacksburg, Virginia<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: Nova Scotia Agricultural College<br />

Graduate Individual: Rob Richardson, Virginia Tech<br />

Undergraduate Individual: Keith Burnell, North Carolina State University<br />

2000 - University of Guelph, Guelph, Ontario, CANADA<br />

Graduate Team: Virginia Tech<br />

Undergraduate Team: Ohio State University<br />

Graduate Individual: Shawn Askew, North Carolina State University<br />

Undergraduate Individual: Luke Case, Ohio State University<br />

2001 - University of Connecticut, Storrs, Connecticut<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: Penn State University<br />

Graduate Individual: Matt Myers, Penn State University<br />

Undergraduate Individual: Shawn Heinbaugh, Penn State University<br />

2002 - ACDS Research Facility, North Rose, New York<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: North Carolina State University<br />

Graduate Individual: Scott McElroy, North Carolina State University<br />

Undergraduate Individual: Sarah Hans, North Carolina State University<br />

127


2003 – Syngenta Crop Protection, Eastern Region Technical Center, Hudson, NY<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Andrew MacRae, North Carolina State University<br />

Undergraduate Individual: Jonathan Kapwyk, University of Guelph<br />

2004 – North Carolina University, Raleigh, NC<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: John Willis, Virginia Tech<br />

Undergraduate Individual: Jenny English, University of Guelph<br />

2005 – Pennsylvania State University, Landisville, PA<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: John Willis, Virginia Tech<br />

Undergraduate Individual: Gerard Pynenborg, University of Guelph<br />

2006 – DuPont Crop Protection, Stine Haskell Research Center, Newark, DE<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: Virender Kumar, Cornell University<br />

Undergraduate Individual: Adam Pfeffer, University of Guelph<br />

2007 - Virginia Tech, Blacksburg, Virginia<br />

Graduate Team: North Carolina State University<br />

Undergraduate Team: University of Guelph<br />

Graduate Individual: George Place, North Carolina State University<br />

Undergraduate Individual: Craig Reid, University of Guelph<br />

128


RESEARCH POSTER AWARDS<br />

1983 1. Herbicide Impregnated Fertilizer of <strong>Weed</strong> Control in No-Tillage Corn - R.<br />

Uruatowski and W. H. Mitchell, Univ. of Delaware, Newark<br />

2. Effect of Wiper Application of Several Herbicides and Cutting on Black<br />

Chokeberry - D. E. Yarborough and A. A. Ismail, Univ. of Maine, Orono<br />

HM. Corn Chamomile Control in Winter Wheat - R. R. Hahn, Cornell Univ., Ithaca,<br />

New York and P. W. Kanouse, New York State Cooperative Extension, Mt.<br />

Morris<br />

1984 1. Herbicide Programs and Tillage Systems for Cabbage - R. R. Bellinder,<br />

Virginia Tech, Blacksburg, and T. E. Hines and H. P. Wilson, Virginia Truck<br />

and Ornamental Res. Station, Painter<br />

2. Triazine Resistant <strong>Weed</strong>s in New York State - R. R. Hahn, Cornell<br />

Univ., Ithaca, NY<br />

HM. A Roller for Applying Herbicides at Ground Level - W. V. Welker and D. L.<br />

Peterson, USDA-ARS, Kearneysville, WV<br />

1985 1. No-Tillage Cropping Systems in a Crown Vetch Living Mulch - N. L. Hartwig,<br />

Penn State Univ., University Park<br />

2. Anesthetic Release of Dormancy in Amaranthus retroflexus Seeds - R. B.<br />

Taylorson, USDA-ARS, Beltsville, MD and K. Hanyadi, Univ. of Agricultural<br />

<strong>Science</strong>, Keszthely, Hungary<br />

2. Triazine Resistant <strong>Weed</strong> Survey in Maryland - B. H. Marose, Univ. of<br />

Maryland, College Park<br />

HM. Wild Proso Millet in New York State - R. R. Hahn, Cornell Univ., Ithaca, NY<br />

1986 1. Discharge Rate of Metolachlor from Slow Release Tablets - S. F. Gorski, M.<br />

K. Wertz and S. Refiners, Ohio State Univ., Columbus<br />

2. Glyphosate and Wildlife Habitat in Maine - D. Santillo, Univ. of Maine, Orono<br />

1987 1. Mycorrhiza and Transfer of Glyphosate Between Plants - M. A. Kaps and L.<br />

J. Khuns, Penn State Univ., University Park<br />

2. Redroot Pigweed Competition Study in No-Till Potatoes - R. W. Wallace, R.<br />

R. Bellinder, and D. T. Warholic, Cornell Univ., Ithaca, NY<br />

1988 1. Growth Suppression of Peach Trees With Competition - W. V. Welker and D.<br />

M. Glenn, USDA-ARS, Kearneysville, WV<br />

2. Smooth Bedstraw Control in Pastures and Hayfields - R. R. Hahn, Cornell<br />

Univ., Ithaca, NY<br />

1989 1. Burcucumber Responses to Sulfonylurea Herbicides - H. P. Wilson and T. E.<br />

Hines, Virginia Tech, Painter, VA<br />

2. Water Conservation in the Orchard Environment Through Management - W.<br />

V. Welker, Jr., USDA-ARS Appalachian Fruit Res. Sta., Kearneysville, WV<br />

129


1990 1. Reduced Rates of Postemergence Soybean Herbicides - E. Prostko, J. A.<br />

Meade, and J. Ingerson-Mahar, Rutgers Coop. Ext. Mt. Holly, NJ<br />

2. The Tolerance of Fraxinus, Juglans, and Quercus Seedings to Imazaquin and<br />

Imazethapyr - L. J. Kuhns and J. Loose, Penn State Univ., University Park<br />

1991 1. Johnsongrass Recovery from Sulfonylurea Herbicides - T. E. Hines and H. P.<br />

Wilson, Virginia Tech, Painter, VA<br />

2. Growth Response to Young Peach Trees to Competition With Several Grass<br />

Species - W. V. Welker and D. M. Glenn, USDA-ARS, Kearneysville, WV<br />

1992 1. Teaching <strong>Weed</strong> Identification with Videotape - B. Marose, N. Anderson, L.<br />

Kauffman-Alfera, and T. Patten, Univ. of Maryland, College Park<br />

2. Biological Control of Annual Bluegrass (Poa annua L. Reptans) with<br />

Xanthomonas campestris (MYX-7148) Under Field Conditions - N. D. Webber<br />

and J. C. Neal, Cornell Univ., Ithaca, NY<br />

1993 1. Development of an Identification Manual for <strong>Weed</strong>s of the Northeastern<br />

United States - R H. Uva and J. C. Neal, Cornell Univ., Ithaca, NY<br />

2. Optimum Time of Cultivation for <strong>Weed</strong> Control in Corn - Jane Mt. Pleasant,<br />

R. Burt and J. Frisch, Cornell Univ., Ithaca, NY<br />

1994 1. Herbicide Contaminant Injury Symptoms on Greenhouse Grown Poinsettia<br />

and Geranium - M. Macksel and A. Senesac, Long Island Horticultural Res.<br />

Lab, Riverhead, NY and J. Neal, Cornell Univ., Ithaca, NY<br />

2. Mow-kill Regulation of Winter Cereals Grown for Spring No-till Crop<br />

Production - E. D. Wilkins and R. R. Bellinder, Cornell Univ., Ithaca, NY<br />

1995 1. A Comparison of Broadleaf and Blackseed Plantains Identification and<br />

Control - J. C. Neal and C. C. Morse, Cornell Univ., Ithaca, NY<br />

2. Using the Economic Threshold Concept as a Determinant for Velvetleaf<br />

Control in Field Corn - E. L. Werner and W. S. Curran, Penn State Univ.,<br />

University Park<br />

1996 1. Preemergence and Postemergence <strong>Weed</strong> Management in 38 and 76 cm<br />

Corn - C. B. Coffman, USDA-ARS, Beltsville, MD<br />

2. Common Cocklebur Response to Chlorimuron and Imazaquin - B. S.<br />

Manley, H. P. Wilson and T. E. Hines, Virginia Tech, Blacksburg, VA<br />

1997 None Awarded<br />

1998 1. <strong>Weed</strong> Control Studies with Rorippa sylvestris - L. J. Kuhns and T. Harpster,<br />

Penn State Univ., University Park, PA<br />

2. Postemergence Selectivity and Safety of Isoxaflutole in Cool Season<br />

Turfgrass - P. C. Bhowmik and J. A. Drohen, Univ. of Massachusetts,<br />

Amherst, MA<br />

130


1999 1. Winter Squash Cultivars Differ in Response to <strong>Weed</strong> Competition - E. T.<br />

Maynard, Purdue Univ., Hammond, IN<br />

2. Effectiveness of Row Spacing, Herbicide Rate, and Application Method on<br />

Harvest Efficiency of Lima Beans - S. Sankula, M. J. VanGessel, W. E. Kee,<br />

and J. L. Glancey, Univ. of Delaware, Georgetown, DE<br />

2000 1. <strong>Weed</strong> Control and Nutrient Release With Composted Poultry Litter Mulch in a<br />

Peach Orchard - P. L. Preusch, Hood College, Frederick, MD; and T. J.<br />

Tworkoski, USDA-ARS, Hearneysville, WV<br />

2 The Effect of Total Postemergence Herbicide Timings on Corn Yield - D. B.<br />

Vitolo, C. Pearson, M. G. Schnappinger, and R. Schmenk, Novartis Crop<br />

Protection, Hudson, NY<br />

2 Pollen Transport from Genetically Modified Corn – J. M. Jemison and M.<br />

Vayda, Univ. of Maine, Orono, ME<br />

2001 1. Evaluation of methyl bromide alternatives for yellow nutsedge control in<br />

plasticulture tomato - W. A. Bailey, H. P. Wilson, and T. E. Hines, Virginia<br />

Tech, Painter, VA.<br />

2. Evaluation of alternative control methods for annual ryegrass in typical<br />

Virginia crop rotations - S. R. King and E. S. Hagood, Virginia Tech,<br />

Blacksburg, VA.<br />

2002 1. Effectiveness of mesotrione to control weeds in sweet corn. J. M. Jemison,<br />

Jr. and A. Nejako, Univ. Maine, Orono.<br />

2. Flufenacet plus metribuzin for italian ryegrass control in Virginia wheat. W.<br />

A. Bailey, H. P. Wilson, and T. E. Hines, Virginia Tech, Painter.<br />

2003 1. Comparison of two methods to estimate weed populations in field-scale<br />

agricultural research. R. D. Stout, M. G. Burton, and H. M. Linker, North<br />

Carolina State Univ.<br />

2. Diquat plus glyphosate for rapid-symptom vegetation control in turf. W. L.<br />

Barker, S. D. Askew, J. B. Beam, Virginia Tech, Blacksburg; and D. C. Riego,<br />

Monsanto Co., Carmel, IN.<br />

2004 1. Biology of the invasive plant pale swallow-wort. L. Smith, S. Greipsson, and<br />

A. DiTommaso. Cornell Univ.<br />

2. Evaluating perennial groundcovers for weed suppression: Roadside trials and<br />

demonstrations. A. Senesac, I. Tsontakis-Bradley, J. Allaire, and L. Weston.<br />

Cornell Univ.<br />

2005 1. Cover crop management impacts on the weed seed predator, Harpalus<br />

rufipes. A. Shearin, S.C. Reberg-Horton, E. Gallandt, and F. Drummond,<br />

Univ. Maine, Orono.<br />

131


2. Carfentrazone, quinclorac, and trifloxysulfuron effects on seeded<br />

bermudagrass establishment and crabgrass control. J. Willis, D.B. Ricker,<br />

and S.D. Askew. Virginia Tech, Blacksburg.<br />

2006 1. Mesotrione for preemergence broadleaf weed control in turf. D. Ricker, J.<br />

Willis, S. Askew, Virginia Tech, Blacksburg.<br />

2. Using a wet blade mower for pest control, fertility, and growth retardation in<br />

fine turfgrass. J. Willis and S.D. Askew. Virginia Tech, Blacksburg.<br />

2007 1. Effects of emergence periodicity on growth and fecundity of horseweed. J.<br />

Dauer. Penn State University, College Park.<br />

2. Vascular weed control in container production using selected non-chemical<br />

top-dress treatments. A. Burtt. University of Vermont, Burlington.<br />

132


INNOVATOR OF THE YEAR<br />

1986 Nathan Hartwig Penn State University<br />

1987 Thomas Welker USDA/ARS Appl. Fruit Res. Sta.<br />

1988 None Awarded<br />

1989 John E. Waldrum Union Carbide Agric. Prod.<br />

1990 None Awarded<br />

1991 Thomas L. Watschke Penn State University<br />

1992 E. Scott Hagood Virginia Tech<br />

Ronald L. Ritter<br />

University of Maryland<br />

1993 None Awarded<br />

1994 George Hamilton Penn State University<br />

1995 Kent D. Redding DowElanco<br />

1996 James Orr Asplundh Tree Expert Co.<br />

1997 George Hamilton Penn State University<br />

1998 None Awarded<br />

1999 Award Discontinued<br />

OUTSTANDING APPLIED RESEARCH IN FOOD AND FEED CROPS<br />

1991 Russell R. Hahn Cornell University<br />

1992 Henry P. Wilson Virginia Tech<br />

1993 None Awarded<br />

1994 Robin Bellinder Cornell University<br />

1995 None Awarded<br />

1996 E. Scott Hagood Virginia Tech<br />

1997 Ronald L. Ritter University of Maryland<br />

1998 None Awarded<br />

1999 Award Discontinued<br />

OUTSTANDING APPLIED RESEARCH IN TURF, ORNAMENTALS,<br />

AND VEGETATION MANAGEMENT<br />

1991 Wayne Bingham Virginia Tech<br />

1992 John F. Ahrens CT Agricultural Experiment Sta.<br />

1993 Joseph C. Neal Cornell University<br />

1994 Prasanta C. Bhowmik University of Massachusetts<br />

1995 Andrew F. Senesac Long Island Hort. Research Lab<br />

1996 Larry J. Kuhns Penn State University<br />

1997 Jeffrey F. Derr Virginia Tech<br />

1998 None Awarded<br />

1999 Award Discontinued<br />

133


OUTSTANDING PAPER AWARDS<br />

1954 Studies on Entry of 2,4-D into Leaves - J. N. Yeatman, J. W. Brown, J. A.<br />

Thorne and J. R. Conover, Camp Detrick, Frederick, MD<br />

The Effect of Soil Organic Matter Levels on Several Herbicides - S. L. Dallyn,<br />

Long Island Vegetable Research Farm, Riverhead, NY<br />

Experimental Use of Herbicides Impregnated on Clay Granules for Control of<br />

<strong>Weed</strong>s in Certain Vegetable Crops - L. L. Danielson, Virginia Truck Expt.<br />

Station, Norfolk, VA<br />

Cultural vs. Chemical <strong>Weed</strong> Control in Soybeans - W. E. Chappell, Virginia<br />

Polytechnic Institute, Blacksburg, VA<br />

Public Health Significance of Ragweed Control Demonstrated in Detroit - J.<br />

H. Ruskin, Department of Health, Detroit, MI<br />

1955 A Comparison of MCP and 2,4-D for <strong>Weed</strong> Control in Forage Legumes - M.<br />

M. Schreiber, Cornell Univ., Ithaca, NY<br />

1956 None Awarded<br />

1957 Herbicidal Effectiveness of 2,4-D, MCPB, Neburon and Others as Measured<br />

by <strong>Weed</strong> Control and Yields of Seedling Alfalfa and Birdsfoot Trefoil - A. J.<br />

Kerkin and R. A. Peters, Univ. of Connecticut, Storrs<br />

Progress Report #4 - Effects of Certain Common Brush Control Techniques<br />

and Material on Game Food and Cover on a Power Line Right-of-Way - W. C.<br />

Bramble, W. R. Byrnes, and D. P. Worley, Penn State Univ., University Park<br />

1958 Effects of 2,4-D on Turnips - C. M. Switzer, Ontario Agricultural College,<br />

Guelph, Canada<br />

Ragweed Free Areas in Quebec and the Maritimes - E. E. Compagna,<br />

Universite Laval at Ste-Anne-de-la-Pocatiere, Quebec, Canada<br />

1959 Yields of Legume-Forage Grass Mixtures as Affected by Several Herbicides<br />

Applied Alone or in a Combination During Establishment - W. G. Wells and R.<br />

A. Peters, Univ. of Connecticut, Storrs<br />

Influence of Soil Moisture on Activity of EPTC, CDEC and CIPC - J. R. Havis,<br />

R. L. Ticknor and P. F. Boblua, Univ. of Massachusetts, Amherst<br />

1960 The Influence of Cultivation on Corn Yields When <strong>Weed</strong>s are Controlled by<br />

Herbicides - W. F. Meggitt, Rutgers Univ., New Brunswick, NJ<br />

134


1961 Preliminary Investigation of a Growth Inhibitor Found in Yellow Foxtail<br />

(Setaria glauca L.) - H. C. Yokum, M. J. Jutras, and R. A. Peters, Univ. of<br />

Connecticut, Storrs<br />

1962 The Effects of Chemical and Cultural Treatment on the Survival of Rhizomes<br />

and on the Yield of Underground Food Reserves of Quackgrass - H. M.<br />

LeBaron and S. N. Gertig, Cornell Univ., Ithaca, NY<br />

Observations on Distribution and Control of Eurasian Watermilfoil in<br />

Chesapeake Bay, 1961 - V. D. Stotts and C. R. Gillette, Annapolis, MD<br />

1963 The Relation of Certain Environmental Conditions to the Effectiveness of<br />

DNBP of Post-Emergence <strong>Weed</strong> Control in Peas - G. R. Hamilton and E. M.<br />

Rahn, Univ. of Delaware, Newark<br />

The Influence of Soil Surface and Granular Carrier Moisture on the Activity of<br />

EPTC - J. C. Cialone and R. D. Sweet, Cornell Univ., Ithaca, NY<br />

The Determination of Residues of Kuron in Birdsfoot Trefoil and Grasses - M.<br />

G. Merkle and S. N. Fertig, Cornell Univ., Ithaca, NY<br />

1964 Control of Riparian Vegetation with Phenoxy Herbicides and the Effect on<br />

Streamflow Quality - I. C. Reigner, USDA-Forest Service, New Lisbon, NJ; W.<br />

E. Sopper, Penn State Univ., University Park; and R. R. Johnson, Amchem<br />

Products, Inc., Ambler, PA<br />

EPTC Incorporation by Band Placement and Standard Methods in<br />

Establishment of Birdsfoot Trefoil - D. L. Linscott and R. D. Hagin, Cornell<br />

Univ., Ithaca, NY<br />

1965 1. Corn Chamomile (Anthemis arvensis L.) Responses to Some Benzoic Acid<br />

Derivatives - Barbara M. Metzger, Judy K. Baldwin and R. D. Ilnicki, Rutgers<br />

Univ., New Brunswick, NJ<br />

2. The Physical Properties of Viscous Sprays for Reduction of Herbicide Drift -<br />

J. W. Suggitt, The Hydro-Electric Power Commission of Ontario, Canada<br />

1966 1. <strong>Weed</strong> Control Under Clear Plastic Mulch - Carl Bucholz, Cornell Univ., Ithaca,<br />

NY<br />

2. A Chemical Team For Aerial Brush Control on Right-of-Way - B. C. Byrd and<br />

C. A. Reimer, Dow Chemical Co<br />

135


1967 1. Influence of Time of Seeding on the Effectiveness of Several Herbicides<br />

Used for Establishing an Alfalfa-Bromegrass Mixture - R. T. Leanard and R.<br />

C. Wakefield, Univ. of New Hampshire, Durham<br />

2. <strong>Weed</strong> Competition in Soybeans - L. E. Wheetley and R. H. Cole, Univ. of<br />

Delaware, Newark<br />

1968 None Awarded<br />

1969 1. <strong>Weed</strong> and Crop Responses in Cucumbers and Watermelons - H. P. Wilson<br />

and R. L. Waterfield, Virginia Truck and Orn. Res. Sta., Painter<br />

2. Effect of Several Combinations of Herbicides on the Weight and<br />

Development of Midway Strawberry Plants in the Greenhouse - O. E.<br />

Schubert, West Virginia Univ., Morgantown<br />

1970 1. Effects of RH-315 on Quackgrass and Established Alfalfa - W. B. Duke,<br />

Cornell Univ., Ithaca, NY<br />

1971 1. Activity of Nitralin, Trifluralin and ER-5461 on Transplant Tomato and<br />

Eggplant - D. E. Broaden and J. C. Cialone, Rutgers Univ., New Brunswick,<br />

NJ<br />

2. Field Investigations of the Activities of Several Herbicides for the Control of<br />

Yellow Nutsedge - H. P. Wilson, R. L. Waterfield, Jr., and C. P. Savage, Jr.,<br />

Virginia Truck and Orn. Res. Sta., Painter<br />

1972 1. Study of Organisms Living in the Heated Effluent of a Power Plant - M. E.<br />

Pierce, Vassar College and D. Allessandrello, Marist College<br />

2. Effect of Pre-treatment Environment on Herbicide Response and<br />

Morphological Variation of Three Species - A. R. Templeton and W. Hurtt,<br />

USDA-ARS, Fort Detrick, MD<br />

1973 1. A Simple Method of Expressing the Relative Efficacy of Plant Growth<br />

Regulators - A. R. Templeton and W. Hurtt, USDA-ARS, Fort Detrick, MD<br />

2. Agronomic Factors Influencing the Effectiveness of Glyphosate for<br />

Quackgrass Control –F. E. Brockman, W. B. Duke, and J. F. Hunt, Cornell<br />

Univ., Ithaca, NY<br />

1974 1. <strong>Weed</strong> Control in Peach Nurseries - O. F. Curtis, Cornell Univ., Ithaca, NY<br />

2. Persistence of Napropamide and U-267 in a Sandy Loam Soil - R. C. Henne,<br />

Campbell Institute for Agr. Res., Napoleon, OH<br />

136


1975 1. Control of Jimsonweed and Three Broadleaf <strong>Weed</strong>s in Soybeans - J. V.<br />

Parochetti, Univ. of Maryland, College Park<br />

HM. The Influence of Norflurazon on Chlorophyll Content and Growth of<br />

Potomogeton pectinatus - R. M. Devlin and S. J. Karcyzk, Univ. of<br />

Massachusetts, East Wareham<br />

HM. Germination, Growth, and Flowering of Shepherdspurse - E. K. Stillwell and<br />

R. D. Sweet, Cornell Univ., Ithaca, NY<br />

1976 1. Top Growth and Root Response of Red Fescue to Growth Retardants - S. L.<br />

Fales, A. P. Nielson and R. C. Wakefield, Univ. of Rhode Island, Kingston<br />

HM. Selective Control of Poa annua in Kentucky Bluegrass - P. J. Jacquemin, O.<br />

M. Scott and Sons, and P. R. Henderlong, Ohio State Univ., Columbus<br />

HM. Effects of DCPA on Growth of Dodder - L. L. Danielson, USDA ARS,<br />

Beltsville, MD<br />

1977 1. The Effects of Stress on Stand and Yield of Metribuzin Treated Tomato<br />

Plants - E. H. Nelson and R. A. Ashley, Univ. of Connecticut, Storrs<br />

HM. The Influence of Growth Regulators on the Absorption of Mineral Elements -<br />

R. M. Devlin and S. J. Karcyzk, Univ. of Massachusetts, East Wareham.<br />

HM. Quantification of S-triazine Losses in Surface Runoff: A Summary - J. K. Hall,<br />

Penn State Univ., University Park<br />

1978 1. Annual <strong>Weed</strong>y Grass Competition in Field Corn - Jonas Vengris, Univ. of<br />

Massachusetts, Amherst<br />

HM. Metribuzin Utilization with Transplanted Tomatoes - R. C. Henne, Campbell<br />

Institute of Agr. Res., Napoleon, OH<br />

1979 1. Herbicides for Ground Cover Plantings - J. F. Ahrens, Connecticut Agric.<br />

Expt. Station, Windsor<br />

2. <strong>Weed</strong> Control Systems in Transplanted Tomatoes - R. C. Henne, Campbell<br />

Institute of Agr. Res. Napoleon, OH<br />

1980 1. Integrated <strong>Weed</strong> Control Programs for Carrots and Tomatoes - R. C. Henne<br />

and T. L. Poulson, Campbell Institute of Agr. Res. Napoleon, OH<br />

2. Suppression of Crownvetch for No-Tillage Corn - J. Carina and N. L. Hartwig,<br />

Penn State Univ., University Park<br />

137


HM. Effect of Planting Equipment and Time of Application on Injury to No-tillage<br />

Corn from Pendimethalin-Triazine Mixtures - N. L. Hartwig, Penn State Univ.,<br />

University Park<br />

1981 1. <strong>Weed</strong> Control in Cucumbers in Northwest Ohio - R. C. Henne and T. L.<br />

Poulson, Campbell Institute of Agr. Res. Napoleon, OH<br />

2. Prostrate Spurge Control in Turfgrass Using Herbicides - J. A. Jagschitz,<br />

Univ. of Rhode Island, Kingston<br />

HM. Some Ecological Observations of Hempstead Plains, Long Island - R. Stalter,<br />

St. John's Univ., Jamaica, NY<br />

1982 1. Differential Growth Responses to Temperature Between Two Biotypes of<br />

Chenopodium album - P. C. Bhowmik, Univ. of Massachusetts, Amherst<br />

2. Chemical Control of Spurge and Other Broadleaf <strong>Weed</strong>s in Turfgrass - J. S.<br />

Ebdon and J. A. Jagschitz, Univ. of Rhode Island, Kingston<br />

HM. Influence of Norflurazon on the Light Activation of Oxyfluorfen - R. M. Devlin,<br />

S. J. Karczmarczyk, I. I. Zbiec and C. N. Saras, Univ. of Massachusetts, East<br />

Wareham<br />

HM. Analysis of <strong>Weed</strong> Control Components for Conventional, Wide-row Soybeans<br />

in Delaware - D. K. Regehr, Univ. of Delaware, Newark<br />

1983 1. Comparisons of Non-Selective Herbicides for Reduced Tillage Systems - R.<br />

R. Bellinder, Virginia Tech, Blacksburg and H. P. Wilson, Virginia Truck and<br />

Orn. Res. Station, Painter<br />

2. The Plant Communities Along the Long Island Expressway, Long Island, New<br />

York - R. Stalter, St. John's Univ., Jamaica, NY<br />

HM. Effect of Morning, Midday and Evening Applications on Control of Large<br />

Crabgrass by Several Postemergence Herbicides - B. G. Ennis and R.<br />

A. Ashley, Univ. of Connecticut, Storrs<br />

1984 1. Pre-transplant Oxyfluorfen for Cabbage - J. R. Teasdale, USDA-ARS,<br />

Beltsville, MD<br />

2. Herbicide Programs and Tillage Systems for Cabbage - R. R. Bellinder,<br />

Virginia Tech, Blacksburg and T. E. Hines and H. P. Wilson, Virginia Truck<br />

and Orn. Res. Station, Painter<br />

1985 1. Peach Response to Several Postemergence Translocated Herbicides - B. A.<br />

Majek, Rutgers Univ., Bridgeton, NJ<br />

138


1986 1. Influence of Mefluidide Timing and Rate on Poa annua Quality Under Golf<br />

Course Conditions - R. J. Cooper, Univ. of Massachusetts, Amherst; K. J.<br />

Karriok, Univ. of Georgia, Athens, and P. R. Henderlong and J. R. Street,<br />

Ohio State Univ., Columbus<br />

2. The Small Mammal Community in a Glyphosate Conifer Release Treatment<br />

in Maine - P. D'Anieri, Virginia Tech, Blacksburg; M. L. McCormack, Jr., Univ.<br />

of Maine, Orono; and D. M. Leslie, Oklahoma State Univ., Stillwater<br />

HM. Field Evaluation of a Proposed IPM Approach for <strong>Weed</strong> Control in Potatoes -<br />

D. P. Kain and J. B. Sieczka, Cornell Univ., Long Island Horticultural<br />

Research Laboratory, Riverhead, NY and R. D. Sweet, Cornell Univ., Ithaca,<br />

NY<br />

1987 None Awarded<br />

1988 1. Bentazon and Bentazon-MCPB Tank-mixes for <strong>Weed</strong> Control in English Pea<br />

- G. A. Porter, Univ. of Maine, Orono; A. Ashley, Univ. of Connecticut, Storrs;<br />

R. R. Bellinder and D. T. Warholic, Cornell Univ., Ithaca, NY; M. P.<br />

Mascianica, BASF Corp., Parsippany, NJ; and L. S. Morrow, Univ. of Maine,<br />

Orono<br />

2. Effects of Herbicide Residues on Germination and Early Survival of Red Oak<br />

Acorns - R. D. Shipman and T. J. Prunty, Penn State Univ., University Park<br />

2. Watershed Losses of Triclopyr after Aerial Application to Release Spruce Fir -<br />

C. T. Smith, Univ. of New Hampshire, Durham and M. L. McCormack, Jr.,<br />

Univ. of Maine, Orono<br />

1989 None Awarded<br />

1990 None Awarded<br />

1991 Award Discontinued<br />

139


NORTHEASTERN WEED SCIENCE SOCIETY<br />

2007 MEMBERSHIP DIRECTORY<br />

Michael L. Agnew<br />

Syngenta<br />

302 Rose Glen Lane<br />

Kennett Square, PA 19348<br />

(610) 444-2063<br />

(610) 444-2093<br />

michael.agnew@syngenta.com<br />

John F. Ahrens<br />

Connecticut Agricultural Exp<br />

Station<br />

PO Box 248<br />

Windsor, CT 06095<br />

(860) 683-4985<br />

(860) 683-4987<br />

john.ahrens@po.state.ct.us<br />

James Altland<br />

Ohio State University<br />

Columbus, Ohio 43210<br />

(330) 263-3854<br />

altland.1@osu.edu<br />

Gregory R. Armel<br />

University of Tennessee<br />

2431 Joe Johnson Dr.<br />

252 Ellington Plant <strong>Science</strong>s<br />

Bldg.<br />

Knoxville, TN 37996-4561<br />

phone: 865-974-8829<br />

email:garmel@utk.edu<br />

Marija Arsenovic<br />

Rutgers University<br />

681 US Highway No 1,South<br />

New Brunswick, NJ 08902-<br />

(732) 932-9575<br />

(732) 932-8481<br />

arsenovic@aesop.rutgers.edu<br />

James Ashley<br />

AshGrow Crop Man<br />

11913 Simsbury Place<br />

Glen Allen,VA 23059<br />

(804) 747-7148<br />

(804) 747-7249<br />

jeashley@ashgrow.com<br />

Shawn Askew<br />

Virginia Tech<br />

435 Old Glade Road<br />

Blacksburg, VA 24061<br />

(540) 231-5807<br />

(540) 231-5755<br />

saskew@vt.edu<br />

John Atwood<br />

ADAS<br />

Boxworth Cambridgeshire<br />

CB3 8NN United Kingdom<br />

(147) 382-3460<br />

(147) 382-3460<br />

J.Atwood@ADAS.co.uk<br />

Kristine Averill<br />

Cornell University<br />

905 Bradfield Hall<br />

Ithaca, NY 14853<br />

(607) 255-4747<br />

kma25@cornell.edu<br />

Mark Barczewski<br />

DuPont Stine Haskell Res Center<br />

1090 Elkton Rd<br />

Newark, DE 19711<br />

(302) 451-4616<br />

(302) 366-6120<br />

mark.j.barzewski@usa.dupont.com<br />

Robert D. Baker<br />

Scotts Company<br />

14111 Scottslawn Rd<br />

Marysville, OH 43041<br />

(937) 645-2628<br />

(937) 644-7153<br />

robert.baker@scotts.com<br />

Whitnee Barker<br />

Virginia Tech<br />

Glade Road Research F<br />

435 Old Glade Road<br />

Blacksburg, VA 24061<br />

(540) 231-5835<br />

(540) 231-5755<br />

wbarker@vt.edu<br />

Gary A. Barkman<br />

Montgomery <strong>Weed</strong><br />

2 Sandy Spring Ct. #2<br />

Thurmont MD 21788<br />

(301) 271-4247<br />

gba-kmansr@msn.com<br />

Jacob Barney<br />

Cornell University<br />

134A Plant <strong>Science</strong><br />

Dept. of Horticulture<br />

Ithaca, NY 14853<br />

(607) 255-0883<br />

(607) 255-9998<br />

jnb22@cornell.edu<br />

Sali Barolli<br />

Imperial Nurseries<br />

90 Salmon Brook St PO Box 120<br />

Granby, CT 06035<br />

(860) 653-1509<br />

(860) 844-8609<br />

saizba@yahoo.com<br />

Jerry J. Baron<br />

IR-4 Rutgers University<br />

681 US Highway 1 So<br />

North Brunswick, NJ 08902<br />

(732) 932-95<br />

(757)932-8481<br />

jbaron@aesop.rutgers.edu<br />

M. Barrett<br />

Argyle Country Club<br />

14600 Argyle Club Rd<br />

Silver Spring, MD 20906<br />

(240) 876-9465<br />

Rodger Batts<br />

North Carolina State University<br />

POBOX 7609<br />

NCSU Campus<br />

Raleigh, NC 27695<br />

(919) 515-1668<br />

roger.batts@ncsu.edu<br />

140


David A. Baxter<br />

DuPont Crop Prot<br />

Stine-Haskell Research<br />

1090 Elkton Road,<br />

Newark, DE 19711<br />

(302) 366-5065<br />

david.a.baxter@usa.dupont.com<br />

Chris M. Becker<br />

BAAR Scientific LLC<br />

6374 Rte. 89<br />

Romulus, NY 14541<br />

(607) 342-3610<br />

(315) 548-9259<br />

becker89@fltg.net<br />

Robin R. Bellinder<br />

Cornell University<br />

Dept. of Horticulture<br />

164 Plant <strong>Science</strong> Bld<br />

Ithaca, NY 14853<br />

(607) 255-7890<br />

(607) 255-0599<br />

rrb3@cornell.edu<br />

Chris Benedict<br />

Cornell University<br />

146A Plant <strong>Science</strong> Building<br />

Ithaca, NY 14850<br />

(607) 255-9085<br />

cab223@cornell.edu<br />

Diane L. Benoit<br />

Agriculture & Ag<br />

430 Gouin Blvd<br />

Saint-Jean-sur-Riche<br />

Quebec J3B 3E6<br />

CANADA<br />

(450) 346-4494<br />

(450) 346-7740<br />

benoitdl@agr.gc.ca<br />

Dan Beran<br />

BASF 1422 57th Place<br />

Des Moines, IA 50311<br />

(402) 669-5157<br />

(515) 279-0916<br />

berand@basf.com<br />

Dana Berner<br />

USDA ARS FDWSRU<br />

1301 Ditto Avenue<br />

Fort Detrick, MD 21702<br />

(301) 619-7316<br />

(301) 619-2880<br />

dana.berner@ars.usda.gov<br />

C. Edward Beste<br />

University of Maryland<br />

27664 Nanticoke Road<br />

Salisbury, MD 21801<br />

(410) 742-8788<br />

(410) 742-1922<br />

cbeste@umd.edu<br />

Prasanta C. Bhowmik<br />

University of Massachusetts<br />

Stockbridge Hall Box 37245<br />

Amherst, MA 01003<br />

(413) 545-5223<br />

(413) 545-3958<br />

pbhowmik@psis.umass.edu<br />

Michele Bigger<br />

Ohio State University<br />

2001 FYFFE Ct Howlett Hall<br />

Columbus, OH 43210<br />

(614) 488-6816<br />

bigger.1@osu.edu<br />

David Bilyea<br />

Ridgetown Coll Univ of Guelph<br />

120 Main Street East<br />

Ridgetown Ontario N0P 2C0<br />

(519) 674-1638<br />

(519) 674-1600<br />

dbilyea@ridgetownc.uoguelph.ca<br />

Clifford Blessing<br />

Delaware Dept. of Agriculture<br />

2320 S. Dupont Highway<br />

Dover, DE 19901<br />

(302) 698-4582<br />

(302) 687-4468<br />

Paul.Blessing@state.de.us<br />

Nola Bobsin<br />

Rutgers Univ<br />

Dept. of Plant Pathology<br />

l59 Dudley Road<br />

New Brunswick, NJ 08901<br />

(732) 932-9711<br />

(732) 932-9441<br />

bobsin@aesop.rutgers.edu<br />

A. Richard Bonanno<br />

University of Mass<br />

255 Merrimack Street<br />

Methuen, MA 01844<br />

(978) 682-9563<br />

(978) 685-6691<br />

rbonanno@umext.umass.edu<br />

Jeffrey Borger<br />

Penn State Univ<br />

244 ASI Bld<br />

University Drive Ex<br />

University Park, PA 16802<br />

(814) 865-3005<br />

(814) 863-7043<br />

jab267@psu.edu<br />

Daniel Brainard<br />

A440A Plant and Soil Sci<br />

Michigan State Univ<br />

East Lansing, MI 48824<br />

(517) 355-5191x1417<br />

brainar9@msu,edu<br />

Melissa A. Bravo<br />

Penn Dept of Agriculture<br />

2301 North Cameron Street<br />

Harrisburg, PA 17110<br />

(717) 787-7204<br />

mbravo@state.pa.us<br />

William L. Bruckart<br />

USDA - ARS FDWSR<br />

1301 Ditto Avenue<br />

Ft. Detrick, MD 21702<br />

(301) 619-2846<br />

(301) 619-2880<br />

wbruckart@fdwsr.ars.usda.gov<br />

Patrick Burch<br />

Dow Agro<strong>Science</strong>s<br />

3425 Elk Creek Drive<br />

Christiansburg, VA 24073<br />

(540) 382-3062<br />

plburch@dow.com<br />

Michael Burton<br />

North Car St Univ<br />

Crop <strong>Science</strong> Dept.<br />

Box 7620, 4402 Will<br />

Raleigh, NC 27695<br />

(919) 513-2860<br />

(919) 515-5315<br />

mike_burton@ncsu.edu<br />

R. Andrew Burtt<br />

University of Vermont<br />

105 Carrigan Dr<br />

Burlington, VT 05405<br />

(802) 656-0467<br />

onfnvt@yahoo.com<br />

141


Nancy Cain<br />

Cain Vegetation<br />

4 Spruce Blvd.<br />

Acton Ontario L7J ZYZ<br />

(519) 853-3081<br />

(519) 853-0352<br />

cain.vegetation@sympatico.ca<br />

J. Boyd Carey<br />

Monsanto<br />

800 North Lindbergh BF2EA<br />

St. Louis, MO 63376<br />

(314) 694-8684<br />

(314) 694-4249<br />

boyd.j.carey@monsanto.com<br />

Luke Case<br />

Ohio State Univ<br />

2001 Fyffe Ct.<br />

Columbus, OH 43210<br />

(614) 292-0209<br />

(614) 292-3505<br />

case.49@osu.edu<br />

Mark S. Casini<br />

DuPont Crop Protect<br />

Stine-Haskell Research<br />

1090 Elkton Road<br />

Newark, DE 19711<br />

(302) 451-0828<br />

(302) 366-6120<br />

mark.s.casini@usa.dupont.com<br />

Craig Cavin<br />

USDA-ARS<br />

Foreign Disease <strong>Weed</strong><br />

1301 Ditto Avenue-F<br />

Frederick, MD 21702<br />

(301) 619-2308<br />

(301) 619-2313<br />

ccavin@fdwsr.arsusda.gov<br />

Darlene Caviness<br />

Home Nursery,<br />

PO Box 307<br />

Edwardsville, IL 62025<br />

(800) 628-1966<br />

(877) 731-9319<br />

darlenec@homenursery.com<br />

Joseph Chamberlin<br />

Valent USA Corp.<br />

2386 Clower Street Ste. E 100B<br />

Snellville, GA 30078<br />

(770) 985-0303<br />

(925) 817-5097<br />

jcham@valent.com<br />

Rakesh S. Chandran<br />

West Virginia Univ<br />

1076 Agricultural Sci<br />

PO Box 6108<br />

Morgantown, WV 26506<br />

(304) 293-6131<br />

(304) 293-6954<br />

rschandran@mail.wvu.edu<br />

William Chism<br />

US EPA PO Box 258<br />

Point of Rocks, MD 21777<br />

(703) 308-8136<br />

(301) 874-6380<br />

chism.bill@epa.gov<br />

Kenneth Chisholm<br />

Nichino America INC<br />

4550 New Linden Hill Rd<br />

Suite 501<br />

Wilmington, DE 19808<br />

(302) 636-9001<br />

(302) 636-9122<br />

kchiiz@nichino.net<br />

Diana Cochran<br />

Auburn University<br />

101 Funchess Hall<br />

Auburn, AL 36849<br />

(334) 844-4087<br />

cochrdr@auburn.edu<br />

Benjamin Coffman<br />

USDA-ARS Bld 001<br />

10300 Baltimore Ave<br />

Beltsville, MD 20705<br />

(301) 504-5398<br />

(301) 504-8370<br />

Ben.coffman@ars.usda.gov<br />

Ronald T. Collins<br />

USDA, ARS<br />

10300 Baltimore Ave.<br />

Bldg. 050, Rm 118A<br />

Beltsville, MD 20705<br />

(301) 352-9696<br />

(301) 504-5823<br />

rcollins@asrr.arsusda.gov<br />

Eryn Cramer<br />

Oregon State Univ<br />

15210 NE Miley Road<br />

Aurora, OR 97002<br />

(503) 515-1243<br />

cramere@onid.orst.edu<br />

John R. Cranmer<br />

Valent USA Corp<br />

110 Iowa Lane Suite 201<br />

Cary, NC 27511<br />

(919) 467-6293<br />

(919) 481-3599<br />

jcran@valent.com<br />

William S. Curran<br />

Penn State University<br />

Dept. Crop & Soil Sci<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 863-1014<br />

(814) 863-7043<br />

wcurran@psu.edu<br />

Gary Custis<br />

PBI Gordon Corp<br />

1217 W. 12th Street<br />

Kansas City, MO 64101<br />

(816) 460-6215<br />

(816) 460-3715<br />

gcustis@pbigordon.com<br />

Sara da Silva<br />

Nelson, Pope, & Vorhis<br />

572 Walt Whitman Rd<br />

Melville, NY 11747<br />

(631) 427-5665<br />

(631) 427-5620<br />

sdasilva@nelsonpope.com<br />

Joseph T. Dauer<br />

Penn State Univ<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

jdauer@psu.edu<br />

Paul J. David<br />

Gowan Company<br />

343 Rumford Road<br />

Lititz, PA 17543<br />

(717) 560-8352<br />

(717) 560-9796<br />

pdavid@gowanco.com<br />

Todd Davis<br />

Delaware Dept. of Agr.<br />

2320 S. Dupont Highway<br />

Dover, DE 19901<br />

(302) 698-4581<br />

(302) 697-4468<br />

Todd.Davis@state.de.us<br />

142


Henry Davis<br />

The <strong>Weed</strong> Doctor<br />

204 S Cedar Crest Blvd<br />

Allentown, PA 18104<br />

(610) 439-2454<br />

drweed@aol.com<br />

Nelson DeBarros<br />

38 Worcester St<br />

Taunton, MA 02780<br />

(774) 218-3820<br />

ndebarros@gmail.com<br />

Peter H. Dernoeden<br />

University of Maryland<br />

Dept. of Natural Resources<br />

1112 H.J. Petersen<br />

College Park, MD 20742<br />

(301) 405-1337<br />

(301) 314-9041<br />

pd9@umail.umd.edu<br />

Jeffrey F. Derr<br />

Virginia Tech<br />

Hampton Roads AREC<br />

1444 Diamond Spring<br />

Virginia Beach, VA 23455<br />

(757) 363-3912<br />

(757) 363-3950<br />

jderr@vt.edu<br />

Robert A. DeWaine<br />

Monsanto Co<br />

505 W. Noyes Blvd.<br />

Sherrill, NY 13461<br />

(315) 363-3903<br />

(315) 363-3903<br />

bob.dewaine@monsanto.com<br />

David A. Dick<br />

West Virginia Dept Agr<br />

Plant Industries Division<br />

1900 Kanawha Blvd.,<br />

Charleston, WV 25305<br />

(304) 558-2212<br />

ddick@ag.state.wv.us<br />

Bryan Dillehay<br />

Penn State Univ Dept Crop Soil<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 863-7607<br />

(814) 863-7043<br />

BLD169@psu.edu<br />

Antonio DiTommaso<br />

Cornell Univ 903 Bradfield Hall<br />

Dept. of Crop & Soil<br />

Ithaca, NY 14853<br />

(607) 254-4702<br />

(607) 255-3207<br />

ad97@cornell.edu<br />

Jeffrey H. Dobbs<br />

Olympic Horticulture<br />

1095 Applecross Dr.<br />

Roswell, GA 30075<br />

(770) 992-0121<br />

(770) 992-5564<br />

jdobbs@ohp.com<br />

John B. Dobson<br />

2815 Lake Road<br />

Williamson, NY 14589<br />

(315) 589-8940<br />

crispjack@aol.com<br />

Lisa Doricchi<br />

DuPont Crop Prot<br />

Stine-Haskell Res<br />

1090 Elkton Road, S<br />

Newark, DE 19711<br />

(302) 366-5722<br />

lisa.doricchi@usa.dupont.com<br />

Cameron Douglass<br />

Cornell University<br />

134A Plant <strong>Science</strong> Bld<br />

Dept Horticulture<br />

Ithaca, NY 14853<br />

(607) 255-0884<br />

chd7@cornell.edu<br />

Richard M. Dunst<br />

Cornell Univ<br />

Vineyard Research Lab<br />

412 East Main Street<br />

Fredonia, NY 14063<br />

(716) 672-6464<br />

(716) 672-8615<br />

rmd7@cornell.edu<br />

Timothy E. Dutt<br />

LABServices<br />

342 South Third Street<br />

Hamburg, PA 19526<br />

(610) 562-5055<br />

(610) 562-5066<br />

tedutt@ptd.net<br />

Donna R. Ellis<br />

University of Conn<br />

Dept. of Plant Sci-Unit 4163<br />

Storrs, CT 06269<br />

(860) 486-6448<br />

(860) 486-0534<br />

donna.ellis@uconn.edu<br />

Rick Ekins<br />

FMC Professional Solutions<br />

1735 Market Street<br />

Philadelphia, PA 19103<br />

(215) 299-5836<br />

rick.ekins@fmc.com<br />

Greg A. Elmore<br />

Monsanto<br />

800 North Lindbergh B<br />

Mail Stop C3NE<br />

St. Louis, MO 63167<br />

(314) 694-4379<br />

greg.a.elmore@monsanto.com<br />

Barbara Emeneau<br />

19 Pine Grove Park<br />

Winchester, MA 01890<br />

(781) 729-0725<br />

(781) 729-0678<br />

apismno@aol.com<br />

Jill England<br />

Imperial College<br />

Department of Agr<br />

Wye Campus, Wye,<br />

AsKent TN24 9AJ<br />

United Kingdom<br />

(020) 759-4269<br />

jill.england@imperial.ac.uk<br />

Farivar Eskandari<br />

USDA-ARS-FDWSRU<br />

1301 Ditto Ave<br />

Fort Detrick, MD 21702<br />

(301) 619-2333<br />

(301) 619-2890<br />

feskandari@fdwsr.ars.usda.gov<br />

Glenn J. Evans<br />

Cornell Univ<br />

134A Plant Sci Bldg.<br />

Ithaca, NY 14850<br />

(607) 342-0128<br />

gje2@cornell.edu<br />

143


Glenn B. Fain<br />

USDA-ARS Southern<br />

PO Box 287<br />

Poplarville, MS 39059<br />

(601) 795-8751<br />

(601) 795-4965<br />

gfain@ars.usda.gov<br />

Steven Farrington<br />

Gowan<br />

1425 W Yale St<br />

Orlando, FL 32804<br />

(407) 841-6892<br />

sfarrington@gowanco.com<br />

Jason Fausey<br />

Valent USA<br />

Corp Office Park West<br />

530 South Creyts SuiteC<br />

Lansing, MI 48917<br />

(517) 321-7380<br />

(517) 321-7216<br />

jason.fausey@valent.com<br />

Stanford Fertig<br />

Rutgers Univ<br />

16919 Melbourne Drive<br />

Laurel, MD 20707<br />

301-776-2527<br />

tfertig@iopener.net<br />

Mike Fidanza<br />

Penn State Univ<br />

Berks Campus<br />

PO Box 7009<br />

Reading, PA 19610<br />

(610) 396-6330<br />

(610) 396-6024<br />

maf100@psu.edu<br />

Eric Gallandt<br />

Univ of Maine<br />

5722 Deering Hall<br />

Orono, ME 04469<br />

(207) 581-2913<br />

(207) 581-2999<br />

gallandt@maine.edu<br />

Travis Gannon<br />

N Carolina State U<br />

Campus Box 7620<br />

Raleigh, NC 27695<br />

(919) 513-4655<br />

(919) 515-7075<br />

travis_gannon@ncsu.edu<br />

Donald D. Ganske<br />

DuPont Company<br />

125 Cotton Ridge Road<br />

Winchester, VA 22603<br />

(540) 662-6011<br />

(540) 662-6011<br />

donald.d.ganske@usa.dupont.com<br />

Saikat Ghosh<br />

Univ of Massachusetts<br />

Room 22, Stockbridge Hall<br />

Amherst, MA 01003<br />

(413) 545-2739<br />

sghosh@psis.umass.edu<br />

Leonard Gianessi<br />

CropLife Foundation<br />

1156 15th Street NW<br />

Washington, DC 20005<br />

(202) 872-3865<br />

(202) 463-0474<br />

lgianessi@croplifefoundation.org<br />

Charles Gilliam<br />

Auburn Univ<br />

101 Funchess Hall<br />

Auburn, AL 36849<br />

(334) 844-3045<br />

(334) 844-3131<br />

gillic1@auburn.edu<br />

Les Glasgow<br />

Syngenta<br />

410 Swing Road<br />

Greensboro, NC 27419<br />

(336) 632-5501<br />

(336) 632-6087<br />

les.glasgow@syngenta.com<br />

Scott Glenn<br />

Univ of Maryland NRSL Dept.<br />

0115 HJ Patterson Hall,<br />

College Park, MD 20742<br />

(301) 405-1331<br />

(301) 314-9042<br />

sglenn@umd.edu<br />

Arthur E. Gover<br />

Penn State University<br />

LMRC, Orchard Road<br />

University Park, PA 16802<br />

(814) 863-1184<br />

(814) 863-1184<br />

aeg2@psu.edu<br />

James Graham<br />

12381 Country Glen Lane<br />

St. Louis, MO 63141<br />

314-878-9815<br />

314-469-5951<br />

jcgrah@charter.net<br />

Jeffrey Gregos<br />

GEC 113 Great Oaks Drive<br />

Moon Township, PA 15108<br />

(412) 299-0211<br />

jeff@GECTURF.com<br />

Kerry FL Guiseppe<br />

University of Maine<br />

5722 Deering Hall<br />

Orono, ME 04473<br />

(207) 581-2924<br />

klough@maine.edu<br />

Scott Guiser<br />

Penn State Coop Ext<br />

Neshaminy Manor Center<br />

1282 Almshouse Road<br />

Doylestown, PA 18901<br />

(215) 345-3283<br />

(215) 343-1653<br />

sxg6@psu.edu<br />

Todd Hagenbuch<br />

Alenza<br />

100 North Conahan Drive<br />

Hazelton, PA 18201<br />

(570) 459-5048<br />

(570) 459-5500<br />

thagenbuch@dbiservices.com<br />

Russell R. Hahn<br />

Cornell Univ<br />

238A Emerson Hall - CSS<br />

Ithaca, NY 14853<br />

607-255-1759<br />

(607) 255-2644<br />

rrh4@cornell.edu<br />

Jim Haldeman<br />

Monsanto<br />

269 Pine View Lane<br />

York, PA 17403<br />

(717) 747-9923<br />

(717) 747-9844<br />

jim.haldeman@monsanto.com<br />

144


Richard Hanrahan<br />

Bayer Env 100 E Palisade Ave<br />

C-42<br />

Englewood, NJ 07631<br />

(201) 394-5217<br />

rich.hanrahan@bayercropscience.<br />

com<br />

Erin Haramoto<br />

University of Maine<br />

5722 Deering Hall<br />

Orono, ME 04469<br />

(207) 581-2972<br />

(207) 581-2999<br />

erin.haramoto@umit.maine.edu<br />

Tracey Harpster<br />

Penn State Univ<br />

102 Tyson Bld<br />

University Park, PA 16802<br />

(814) 865-3190<br />

(814) 863-6139<br />

tlh8@psu.edu<br />

Stephen E. Hart<br />

Rutgers Univ Plant Sci Dept.<br />

F59 Dudley Road<br />

New Brunswick, NJ 08901<br />

(732) 932-9711(732) 932-9441<br />

hart@aesop.rutgers.edu<br />

Brian Hearn<br />

University of De1<br />

6684 County Seat Hwy<br />

Georgetown, DE 19947<br />

(302) 856-1997<br />

(302) 856-1994<br />

bhearn@udel.edu<br />

Jo Anna Hebberger<br />

1446 Auction Road Penn State<br />

Manheim, PA 17545<br />

(717) 653-1052<br />

jhebberger@yahoo.com<br />

Robert Hedberg<br />

USDA/CSREES<br />

<strong>Science</strong> Policy and Legis Aff<br />

334-A Whitten Build<br />

Washington, DC 20002<br />

(202) 720-4118<br />

rhedberg@csrees.usda.gov<br />

Lane K. Heimer<br />

Maryland Dept. of Agr<br />

13506 Little Antietam Road<br />

Hagerstown, MD 21742<br />

(301) 791-5766<br />

lane_heimer@att.net<br />

Gerald M. Henry<br />

N Carolina St Univ<br />

4401 Williams Hall<br />

Raleigh, NC 27695<br />

(919) 515-5654<br />

(919) 515-5315<br />

gmhenry@ncsu.edu<br />

Robert M. Herrick<br />

FMC<br />

1735 Market Street<br />

Philadelphia, PA 19103<br />

(215) 299-6967<br />

(215) 299-6810<br />

bob_herrick@FMC.com<br />

Dwayne Hess<br />

J.C. Ehrlich PO Box 13848<br />

Reading, PA 19612<br />

(610) 372-9700<br />

(610) 378-9744<br />

dwayne.hess@jcehrlich.com<br />

Thomas E. Hines<br />

Eastern Shore AR<br />

33446 Research Drive<br />

Painter, VA 23420<br />

(757) 414-0724<br />

(757) 414-0730<br />

thhines@vt.edu<br />

Adam C. Hixson<br />

N Carolina St Univ<br />

4401 Williams Hall<br />

Raleigh, NC 27695<br />

(919) 515-5654<br />

(919) 515-5315<br />

achixson@ncsu.edu<br />

Duane Hodges<br />

The Scotts Company<br />

12640 SR 736<br />

Marysville, OH 43040<br />

(937) 644-7021<br />

duane.hodges@scotts.com<br />

Ronald J. Hoover<br />

Penn State Univ<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6672<br />

(814) 863-7043<br />

rjh7@psu.edu<br />

Todd Horton<br />

BASF Corporation<br />

3 Eason Circle P.O. Box 70<br />

Macon, NC 27551<br />

(252) 257-0245<br />

(252) 257-2040<br />

hortonc@basf.com<br />

LeRoy F. Houck<br />

DuPont Crop Prot<br />

Stine-Haskell Research<br />

1090 Elkton Road, S210/170-23<br />

Newark, DE 19711<br />

(302) 366-5571<br />

(302) 366-6120<br />

Leroy.F.Houck@usa.dupont.com<br />

Judith Hough-Gol<br />

Univ. of Delaware<br />

Dept. Entomology & Wildlife<br />

Ecology<br />

Newark, DE 19717<br />

(302) 831-2526<br />

(302) 831-8889<br />

jhough@udel.edu<br />

Lewis S. Howell<br />

DuPont Crop Prot Stine-Haskell<br />

Research<br />

1090 Elkton Road, S210/170-48<br />

Newark, DE 19711<br />

(302) 366-6104<br />

Lewis.S.Howell@usa.dupont.com<br />

Leslie Huffman<br />

Ontario Ministry<br />

2585 Country Road 20<br />

Harrow Ontario N0R 1G0<br />

(519) 738-2251<br />

(519) 738-4564<br />

leslie.huffman@omaf.gov.on.ca<br />

Andrew G. Hulting<br />

Penn State Univ<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

agh11@psu.edu<br />

145


Kris Hunter<br />

BAAR Scientific LLC<br />

PO Box 143<br />

Phelps, NY 14532<br />

(315) 664-2020<br />

kristhehunter@hotmail.com<br />

Richard Ilnicki<br />

Rutgers Univ<br />

403 Georges Rd<br />

Dayton, NJ 08810<br />

(732) 329-2858<br />

hirich@msn.com<br />

Marc Imlay<br />

Anacostia Waters<br />

2321 Woodberry Drive<br />

Bryans Road, MD 20616<br />

(301) 283-0808<br />

ialm@erols.com<br />

Mark Isaacs<br />

University of Del<br />

Research & Education<br />

16684 County Seat H<br />

Georgetown, DE 19947<br />

(302) 856-1997<br />

(302) 856-1994<br />

isaacs@udel.edu<br />

Jordi Izqvierdo<br />

Politechnical Un187,<br />

Urgell Escola<br />

Superior D'A08036<br />

Barcelona Catalonia<br />

SPAIN<br />

(814) 863-7638<br />

jordi.izqvierdo@upc.es<br />

Susan Jelinek<br />

No Carolina St Univ<br />

PO Box 7620<br />

Raleigh, NC 27695<br />

(919) 515-3492<br />

(919) 515-5855<br />

susan_jelinek@ncsu.edu<br />

John M. Jemison<br />

University of Maine<br />

495 College Avenue<br />

Orono, ME 04473<br />

(207) 581-3241<br />

(207) 581-1301<br />

jemison@maine.edu<br />

W. Wynn John<br />

Stine-Haskell Research<br />

PO Box 30<br />

Newark, DE 19714<br />

(302) 366-5383<br />

(302) 351-7179<br />

w-wynn.John@usa.dupont.com<br />

Roy R. Johnson<br />

Waldrum Speciali1ty<br />

727 E Butler Pike<br />

Ambler, PA 19002<br />

(215) 817-0637<br />

(215) 348-5541<br />

rjoh834880@aol.com<br />

Quintin R. Johnson<br />

University of De1aware<br />

6684 County Seat Highway<br />

Georgetown, DE 19947<br />

(302) 856-7303<br />

(302) 856-1845<br />

quintin@udel.edu<br />

Dave Johnson<br />

Penn State Univ<br />

1446 Auction Road<br />

Manheim, PA 17545<br />

(717) 653-4728<br />

(717) 653-6308<br />

dhj3@psu.edu<br />

Jon Johnson<br />

Pennsylvania State Univ<br />

LMRL, Orchard Road<br />

University Park, PA 16802<br />

(814) 863-1184<br />

(814) 863-1184<br />

jmj5@psu.edu<br />

Brian Jones<br />

Penn State Univ<br />

Dept of Crop & Soil Sci<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

(814) 863-7043<br />

bpj2@psu.edu<br />

Grant L. Jordan<br />

A. C. D. S. Res<br />

9813 Glenmark Road<br />

North Rose, NY 14516<br />

(315) 587-2240<br />

(315) 587-2145<br />

gjjordan@usadatanet.net<br />

Caren Judge<br />

BASF Corp<br />

26 Davis Drive<br />

RTP, NC 27709<br />

(919) 547-2380<br />

(919) 547-2488<br />

carrie.judge@basf.com<br />

Jerry Kahl<br />

J. C. Ehrlich Co<br />

PO Box 13848<br />

Reading , PA 19612<br />

(610) 372-9700<br />

(610) 378-9744<br />

jerry.kahl@jcehrlich.com<br />

Kathie E. Kalmowitz<br />

BASF Corporation<br />

3955 Stags Leap Circle<br />

Raleigh, NC 27612<br />

(919) 547-2642<br />

(919) 547-2410<br />

kalmowk@basf.com<br />

John E. Kaminski<br />

University of Conn<br />

Dept. of Plants and Soil<br />

1376 Storrs Road,<br />

Storrs, CT 06269<br />

(860) 486-0162<br />

john.kaminski@uconn.edu<br />

Renee J. Keese<br />

Syngenta Crop Protection<br />

985 Arrowwood Drive<br />

Carmel, IN 46033<br />

(317) 846-8812<br />

(317) 846-8832<br />

renee.keese@syngenta.com<br />

Richard Kersberge<br />

University of Maine<br />

992 Waterville Rd<br />

Waldo, ME 04915<br />

(207) 342-5971<br />

richardk@umext.maine.edu<br />

Steven E. King<br />

Virginia Tech<br />

Glade Road Research<br />

C435 Old Glade Road<br />

Blacksburg, VA 24061<br />

(540) 231-2463<br />

(540) 231-5755<br />

stking4@vt.edu<br />

146


Hiromu Kobayashi<br />

Nissan Chemical<br />

1291 Cumberland Ave.,<br />

Unit D<br />

West Lafayette, IN 47906<br />

(765) 497-1161<br />

(765) 497-7917<br />

kobayashi@nissan.wintek.com<br />

Hyesuk Kong<br />

USDA/ARS/SASL<br />

Building 001, Room 242<br />

Beltsville, MD 20705<br />

(301) 504-6846<br />

(301) 504-6491<br />

kongh@ba.ars.usda.gov<br />

Justin Kozak<br />

Penn State University<br />

116 ASI Building<br />

University Park, PA 16801<br />

(814) 865-6679<br />

justinkozak@yahoo.com<br />

Larry J. Kuhns<br />

Penn State Univ<br />

103 Tyson Bldg<br />

University Park, PA 16802<br />

(814) 863-2197<br />

(814) 863-6139<br />

ljk@psu.edu<br />

Virender Kumar<br />

Cornell Univ<br />

149 Plant <strong>Science</strong> Bld<br />

Department of Horticulture<br />

Ithaca, NY 14853<br />

(607) 255-1786<br />

vk63@cornell.edu<br />

Dan Kunkel<br />

IR4 Headqt., Rutgers Univ.<br />

500 College Rd East, 201W<br />

Princeton, NJ 08540<br />

(732) 932-9575<br />

(732) 932-8481<br />

kunkel@aesop.rutgers.edu<br />

Kerrie L. Kyde<br />

MD Dept. of Natural Res<br />

580 Taylor Avenue, E-1<br />

Annapolis, MD 21401<br />

(410) 260-8534<br />

(410) 260-8596<br />

kkyde@dnr.state.md.us<br />

Brent A. Lackey<br />

Syngenta Crop Prot<br />

140 Prescott Ridge<br />

Madison, MS 39110<br />

(601) 427-2774<br />

(601) 427-2455<br />

brentlackey@farmassist.com<br />

Brian G. Lackey<br />

<strong>Weed</strong>s Inc.<br />

250 Bodley Road<br />

Aston, PA 19014<br />

(610) 358-9430<br />

(610) 358-9438<br />

Calvin W. Layton<br />

Northern Tree Service<br />

PO Box 790<br />

Palmer, MA 01069<br />

(800) 232-6132<br />

(413) 283-9283<br />

layton@northerntree.com<br />

Rachel Lightfoot<br />

CMS Inc<br />

PO Box 510<br />

Hereford, PA 18056<br />

(610) 767-1944<br />

(610) 767-1925<br />

cms1@fast.net<br />

Dwight Lingenfelter<br />

Penn State Univ<br />

Dept. of Crop & Soil<br />

116 ASI Bldg<br />

University Park, PA 16802<br />

(814) 865-2242<br />

(814) 863-7043<br />

dxl18@psu.edu<br />

Ryan Lins<br />

Syngenta Crop Prot<br />

959 Sudlersville Road<br />

Clayton, DE 19938<br />

(410) 490-4514<br />

ryan.lins@syngenta.com<br />

Daniel Little<br />

Michigan State Univ<br />

A432 Plant & Soil <strong>Science</strong><br />

East Lansing, MI 48824<br />

(517) 974-3000<br />

msuturf01@hotmail.com<br />

Henry Lohmann<br />

PO Box 22<br />

Bellport, NY 11713<br />

(631) 286-1078<br />

(631) 286-1078<br />

halohmann@aol.com<br />

Kerry Lough<br />

University of Maine<br />

5722 Deering Hall<br />

Orono, ME 04469<br />

(207) 581-2924<br />

(207) 581-2941<br />

klough@maine.edu<br />

Daniel L. Loughner<br />

Dow Agro<strong>Science</strong>s<br />

497 Leonard Road<br />

Huntingdon Valley, PA 19006<br />

(215) 947-0721<br />

(215) 947-1921<br />

dloughner@dow.com<br />

Rosanna Louie<br />

USEPA/OPP/SRRD<br />

1200 Pennsylvania Ave<br />

Mail Code 7508C<br />

Washington, DC 20460<br />

(703) 308-0037<br />

(703) 308-8005<br />

louie.rosanna@ea.gov<br />

Sarah Low<br />

Wissahickon Rest<br />

3721 Midvale Avenue<br />

Philadelphia, PA 19119<br />

(215) 951-0342<br />

(215) 951-0342<br />

sarah1@rhd.org<br />

Edith Lurvey<br />

Northeast IR-4<br />

Dept. of Food <strong>Science</strong><br />

630 West North St.<br />

Geneva, NY 14456<br />

(315) 787-2308<br />

(315) 787-2397<br />

ell10@cornell.edu<br />

Darren Lycan<br />

Syngenta Crop Pr<br />

3002 Village Blvd. South<br />

Baldwinsville, NY 13027<br />

(315) 635-2818<br />

darren.lycan@syngenta.com<br />

147


John Lydon<br />

USDA/ARS/SASL<br />

Building 001, Rm. 272<br />

Beltsville, MD 20705<br />

(301) 504-5379<br />

(301) 504-6491<br />

LydonJ@ba.ars.usda.gov<br />

Bruce Maddy<br />

Dow Agro<strong>Science</strong>s<br />

102 Queensbury Ct.<br />

Noblesville, IN 46060<br />

(317) 877-3100<br />

(317) 877-3068<br />

bemaddy@dow.com<br />

Matthew J. Mahoney<br />

Bayer Crop <strong>Science</strong>s<br />

4773 Sailors Retreat Road<br />

Oxford, MD 21654<br />

(410) 822-5215<br />

(410) 819-0286<br />

matt.mahoney@bayercropscience<br />

.com<br />

Bradley A. Majek<br />

Rutger University<br />

Rutgers A.R.E.C.<br />

121 Northville Road<br />

Bridgeton, NJ 08302<br />

(856) 455-3100<br />

(856) 455-3133<br />

majek@aesop.rutgers.edu<br />

Mili Mandal<br />

West Virginia Univ<br />

Department of Agriculture<br />

Room #1070,<br />

Morgantown, WV 26505<br />

(304) 685-4690<br />

milimandal@yahoo.com<br />

Brian S. Manley<br />

Syngenta Crop Pr<br />

WRO 1004.7.34<br />

Schwarzwaldallee 21Basel 4058<br />

Switzerland<br />

(061) 323-9195<br />

(061) 323-6855<br />

brian.manley@syngenta.com<br />

Carrie Mansue<br />

Rutgers University<br />

Plant Biology & Pathology<br />

59 Dudley Rd<br />

New Brunswick, NJ 08901<br />

(732) 932-9711<br />

cmansue@aesop.rutgers.edu<br />

Betty H. Marose<br />

University of Maryland<br />

Dept. of Entomology<br />

3138 Plant <strong>Science</strong><br />

College Park, MD 20742<br />

(301) 405-3929<br />

(301) 314-9290<br />

marose@umd.edu<br />

Michael W. Marshall<br />

Michigan State Univ<br />

A438 Plant & Soil <strong>Science</strong> Bldg.<br />

East Lansing, MI 48824<br />

(517) 355-5191<br />

(517) 432-2242<br />

mmarshal@msu.edu<br />

Hannah Mathers<br />

Ohio State Univ<br />

248C Howlett Hall<br />

2001 Fyffe Ct.<br />

Columbus, OH 43210<br />

(614) 247-6195<br />

(614) 292-3505<br />

mathers.7@osu.edu<br />

Brian Maynard<br />

Univ of Rhode Island<br />

Dept. of Plant <strong>Science</strong>s<br />

Kingston, RI 02881<br />

(401) 874-5372<br />

(401) 874-2494<br />

bmaynard@uri.edu<br />

David J. Mayonado<br />

Monsanto Company<br />

6075 Westbrooke Drive<br />

Salisbury, MD 21801<br />

410-726-4222<br />

410-219-3202<br />

david.j.mayonado@monsanto.com<br />

David McCall<br />

Virginia Tech<br />

119 Price Hall<br />

Blacksburg, VA 24061<br />

(540) 231-9598<br />

dsmccall@vt.edu<br />

Michael McComrick<br />

DuPont Crop Protection<br />

Stine-Haskell Research<br />

1090 Elkton Road, S<br />

Newark, DE 19711<br />

(302) 366-5154<br />

(302) 366-6120<br />

michael.c.mccomrick@usa.dupo<br />

nt.com<br />

Maxwell L. McCormack<br />

PO Box 644<br />

Deer Isle, ME 04627<br />

207-348-5243<br />

(207) 348-5243<br />

MLM@midmaine.com<br />

Patrick E. McCullough<br />

Rutgers Univ<br />

59 Dudley Road<br />

New Brunswick, NJ 08901<br />

(732) 932-9711<br />

(732) 932-9441<br />

mccullough@aesop.rutgers.edu<br />

Steven McDonald<br />

University of Maryland<br />

1112 H.J. Patterson Hall<br />

College Park, MD 20742<br />

(610) 633-1878<br />

McDSJ@umed.edu<br />

Brian McDonnell<br />

NPS NE Exotic Plant Mgt Team<br />

Delaware Water Gap NRA River<br />

Rd<br />

Bushkill, PA 18324<br />

(570) 588-0534<br />

(570) 588-0590<br />

brian_mcdonnell@nps.gov<br />

Chris McGill<br />

FMC Corporation<br />

1109 Old Post Circle<br />

Garnet Valley, PA 19061<br />

(215) 299-6590<br />

(215) 299-6100<br />

Christopher.mcgill@fmc.com<br />

Kristen McNaughton<br />

Ridgetown College<br />

120 Main St. E<br />

Ridgetown Ontario N0P 2C0<br />

CANADA<br />

(519) 674-1638<br />

(519)674-1600<br />

kmcnaugh@ridgetownc.uoguelph.ca<br />

148


Hiwot Menbere<br />

University of Maryland<br />

7741 Patuxent Oak Ct.<br />

Elkridge, MD 21075<br />

(301) 405-1334<br />

(301) 314-9041<br />

hm@umd.edu<br />

Todd L. Mervosh<br />

Connecticut Agric Exp Sta<br />

153 Cook Hill Road<br />

PO Box 248<br />

Windsor, CT 06095<br />

(860) 683-4984<br />

(860) 683-4987<br />

Todd.Mervosh@po.state.ct.us<br />

Lindsey R. Milbrath<br />

USDA-ARS US Plant, Soil &<br />

Nutrtion<br />

Ithaca, NY 14853<br />

(607) 254-7268<br />

(607) 255-1132<br />

lrm32@cornell.edu<br />

Kyle Miller<br />

BASF<br />

14000 Princess Mary Road<br />

Chesterfield, VA 23838<br />

(804) 739-6044<br />

(804) 739-7498<br />

millerkj@basf.com<br />

Mario R. Miranda-Sazo<br />

Cornell University<br />

146A Plant <strong>Science</strong> Bld<br />

Ithaca, NY 14853<br />

(607) 255-9085<br />

mrm67@cornell.edu<br />

Steven Mirsky<br />

Penn State Univ<br />

Dept. of Crop & Soil<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

(814) 863-7043<br />

sbm138@psu.edu<br />

Charles L. Mohler<br />

Cornell Univ<br />

Dept. of Crop & Soil<br />

907 Bradfield Hall<br />

Ithaca, NY 14853<br />

(607) 255-0199<br />

clm11@cornell.edu<br />

Thomas Molloy<br />

University of Maine<br />

5722 Deering Hall<br />

Orono, ME 04469<br />

(207) 581-2926<br />

Thomas.Molloy@unit.maine.edu<br />

David A. Mortensen<br />

Pennsylvania State Univ<br />

Dept. of Crop and Soil<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-1906<br />

(814) 863-7043<br />

dmortensen@psu.edu<br />

Aboud Mubareka<br />

Sprout-Less Vegetation<br />

1125 Power Road<br />

St. Joseph de Madawa<br />

New Brunswick CANADA<br />

E7B 2M3<br />

(506) 739-6447<br />

(506) 735-7033<br />

samco@sprout-less.com<br />

Meredith Murray<br />

Pennsylvania State Univ<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 863-7607<br />

mjm58@psu.edu<br />

Matt Naedel<br />

Penn State University<br />

mbn112@psu.edu<br />

Joseph Neal<br />

North Carolina State University<br />

Dept. of Horticultural <strong>Science</strong><br />

262 Kilgore Hall, Box 7609<br />

Raleigh, NC 27695<br />

(919) 515-9379<br />

(919) 515-7747<br />

joe_neal@ncsu.edu<br />

Larry Norton<br />

Bayer Environmental <strong>Science</strong><br />

739 Blair Road<br />

Bethlehem, PA 18017<br />

(610) 814-6220<br />

(610) 814-6221<br />

larry.norton@bayercropscience.com<br />

Rob Nurse<br />

Agriculture & Ag<br />

2585 County Rd. 20<br />

Harrow Ontario, NOR 1G0<br />

CANADA<br />

(519) 738-2251<br />

(519) 738-2929<br />

ren8@cornell.edu<br />

Judith Okay<br />

Chesapeake Bay Program<br />

410 Severn Dr Suite 209<br />

Annapolis, MD 21403<br />

(410) 295-1311<br />

(410) 267-5777<br />

jokay@chesapeakebay.net<br />

Brian D. Olson<br />

Dow Agro<strong>Science</strong>s<br />

PO Box 753<br />

Geneva, NY 14456<br />

(315) 781-0140<br />

(315) 781-0387<br />

dolson@dow.com<br />

William B O'Neal<br />

AMVAC Corp<br />

102 Bay View Drive<br />

Chapel Hill, NC 27516<br />

(919) 968-7776<br />

(919) 968-7763<br />

boneal@sprynet.com<br />

Marc Pacchioli<br />

Crop Management Strategies<br />

PO Box 510<br />

Hereford, PA 18056<br />

(610) 767-1944<br />

(610) 767-1925<br />

cms1@fast.net<br />

W.H. Butch Palmer<br />

Reality Research Co<br />

916 South Avenue<br />

Williamson, NY 14589<br />

(315) 945-0945<br />

(315) 589-4096<br />

whpalmer@computerconnection.net<br />

Cristi Palmer<br />

IR4 Headqt., Rutgers Univ.<br />

500 College Rd East, 201W<br />

Princeton, NJ 08540<br />

(782) 932-9575<br />

(732) 932-8481<br />

palmer@aesop.rutgers.edu<br />

149


Philip D. Pannill<br />

Maryland Forest<br />

1260 Maryland Avenue<br />

Hagerstown, MD 21740<br />

(301) 791-4010<br />

(301) 791-0173<br />

ppannill@dnr.state.md.us<br />

James V. Parochetti<br />

USDA-CSREES<br />

Mail Stop 2220<br />

14th & Independence<br />

Washington, DC 20250<br />

(202) 401-4354<br />

(202) 401-4888<br />

jparochetti@csrees.usda.gov<br />

Stephanie Parrish<br />

USDA-NRCS<br />

52 Boyden Road, #100<br />

Holden, MA 01520<br />

(508) 829-4477<br />

(508) 829-9508<br />

stephanie.parrish@ma.usda.gov<br />

Charles Pearson<br />

Syngenta Crop Protection<br />

PO Box 18300<br />

Greensboro, NC 27419<br />

(336) 632-5979<br />

(336) 632-6950<br />

charles.pearson@syngenta.com<br />

Annamarie Pennucci<br />

Northeast Turf<br />

4 Englewood Drive<br />

Raymond, NH 03077<br />

(603) 895-8460<br />

(603) 672-6332<br />

aapennuci@yahoo.com<br />

Nora Peskin<br />

Pennsylvania State University<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

hup111@psu.edu<br />

Paul W. Peters<br />

3A Merrow Road<br />

Storrs, CT 06268<br />

(860) 429-6962<br />

Robert A. Peters<br />

Univ. of Connecticut<br />

238 Maple Road<br />

Storrs, CT 06268<br />

860-429-4065<br />

Bill Phillips<br />

US EPA<br />

Ariel Rios Bldg<br />

1200 Pennsylvania A<br />

Washington, DC 20460<br />

(703) 308-8099<br />

Phillips.Bill@epa.gov<br />

David Pieczarka<br />

Gowan Company<br />

1630 Berry Rd<br />

LaFayette, NY 13084<br />

(315) 447-0560<br />

(315) 683-9405<br />

dpieczarka@gowanco.com<br />

Jenny Pope<br />

Ohio State Univ<br />

248A Howlett Hall<br />

2001 Fyffe Ct.<br />

Columbus, OH 43210<br />

(614) 292-0209<br />

(614) 292-3505<br />

pope.71@osu.edu<br />

Peter Porpiglia<br />

Kumiai America<br />

11 Martine Ave Suite 970<br />

White Plains, NY 10606<br />

(914) 682-8934<br />

(914) 682-9050<br />

peter@kichem-usa.com<br />

Angela Post<br />

North Carolina State Univ<br />

POBOX 7609 227 Kilgore Hall<br />

Raleigh, NC 27695<br />

(919) 625-9850<br />

arricha3@ncsu.edu<br />

Randall Prostak<br />

University of Mass<br />

Dept. of Plant & Soil<br />

French Hall, Room 2<br />

Amherst, MA 01033<br />

(413) 577-1738<br />

(413) 545-3075<br />

rprostak@umext.umass.edu<br />

Daniel Ramsdell<br />

Crop Management<br />

PO Box 510<br />

Hereford, PA 18056<br />

(610) 767-1944<br />

(610) 767-1925<br />

cms_glp@fast.net<br />

Patrick L. Rardon<br />

DuPont Crop Protection<br />

1090 Elkton Road, S210/170<br />

Newark, DE 19711<br />

(302) 366-5546<br />

Patrick.L.Rardon@usa.dupont.com<br />

Julie Ream<br />

Oregon State Univ<br />

15210 NE Miley Road<br />

Aurora, OR 97002<br />

(503) 329-2414<br />

Chris Reberg-Horton<br />

North Carolina State Univ<br />

NCSU Campus Box 7620<br />

Raleigh, NC 27695<br />

(919) 515-7597<br />

chris_reberg-horton@ncsu.edu<br />

Robert J. Richardson<br />

North Carolina State Univ<br />

Box 7620,<br />

Williams Hall<br />

Raleigh, NC 27695<br />

(919) 515-5653<br />

(919) 515-5315<br />

rob_richardson@ncsu.edu<br />

Dan Ricker<br />

Virginia Tech<br />

435 Old Glade Road<br />

Glade Road Research<br />

Blacksburg, VA 24061<br />

(540) 231-5835<br />

(540) 231-5755<br />

dricker@vt.edu<br />

Domingo C. Riego<br />

Monsanto Company<br />

1307 Cottonwood Ct<br />

Carmel, IN 46033<br />

(317) 575-8769<br />

(317) 574-9157<br />

domingo.c.riego@monsanto.com<br />

150


Mike Riffle<br />

Valent<br />

9196 Shoal Creek Drive<br />

Tallahassee, FL 32312<br />

(850) 386-6453<br />

mriff@valent.com<br />

Ronald L. Ritter<br />

University of Maryland<br />

12901 North Point Lane<br />

Laurel, MD 20708<br />

(301) 405-1329<br />

(301) 490-3754<br />

rlritter@umd.edu<br />

Don R. Robbins<br />

Maryland Dept. of Agr<br />

50 Harry S. Truman Parkway<br />

Annapolis, MD 21401<br />

(410) 841-5871<br />

(410) 841-5835<br />

robbindr@mda.state.md.us<br />

Darren E. Robinson<br />

Ridgetown College<br />

120 Main Street East<br />

Ridgetown Ontario<br />

N0P 2C0 CANADA<br />

(519) 674-1604<br />

(519) 674-1600<br />

drobinso@ridgetownc.uoguelph.ca<br />

Greg S. Rogers<br />

Dupont Crop Protection<br />

58 Mary Jane Lane<br />

Elkton, MD 21921<br />

(443) 309-0148<br />

(302) 451-4840<br />

gregory.s.rogers@usa.dupont.co<br />

m<br />

John Roy<br />

RWC, Inc.<br />

PO Box 876<br />

248 Lockhouse Rd<br />

Westfield, MA 01086<br />

(413) 562-5681<br />

(413) 568-5584<br />

Marc Ruggiero<br />

DuPont Crop Protection<br />

Stine-Haskell Research<br />

1090 Elkton Road, S<br />

Newark, DE 19711<br />

(302) 366-5513<br />

Marc.Ruggiero@usa.Dupont.com<br />

Peter O. Rupp<br />

Maryland Dept. of Agr<br />

6624 Mountain Church Road<br />

Middletown, MD 21769<br />

(301) 371-5317<br />

PRupp81132@aol.com<br />

Matthew Ryan<br />

Penn State Univ<br />

116 ASI Building<br />

University Park, PA 16802<br />

(814) 865-6679<br />

Sue Salmons<br />

National Park Service<br />

Exotic Plant Management<br />

4598 MacArthur Blvd NW<br />

Washington, DC 2007<br />

(202) 342-1443 X 217<br />

sue_salmon@nps.gov<br />

James Saik<br />

Fingerlakes Agro<br />

4467 Jordan Road<br />

Skaneateles, NY 13152<br />

(315) 952-9955<br />

saikj@aol.com<br />

Joe Sandbrink<br />

Monsanto Company<br />

800 N. Lindbergh Blvd.<br />

St. Louis, MO 63167<br />

(314) 694-1200<br />

joseph.j.sandbrink@monsanto.co<br />

m<br />

Hilary Sandler<br />

University of Mass<br />

PO Box 569<br />

E Wareham, MA 02538<br />

(508) 295-2212<br />

(508) 295-6387<br />

hsandler@umext.umass.edu<br />

Sujatha Sankula<br />

NCFAP<br />

1616 P Street NW 1st Flr<br />

Washington, DC 20036<br />

(202) 328-5057<br />

(202) 328-5133<br />

sankula@ncfap.org<br />

Debanjan Sanyal<br />

University of Mass<br />

16 Stockbridge Hall<br />

Amherst, MA 01003<br />

(413) 545-3072<br />

(413) 545-3958<br />

debanjan@psis.umass.edu<br />

Dipayan Sarkar<br />

University of Mass<br />

Dept. of Plant & Soil<br />

Stockbridge Hall<br />

Amherst, MA 01003<br />

(413) 545-3072<br />

dsarkar@psis.umass.edu<br />

David W. Saunders<br />

DuPont Crop Protection<br />

2401 230th Street<br />

Dallas Ctr., IA 50063<br />

(515) 334-4485<br />

Carl D. Sawyer<br />

University of Rhode Island<br />

Dept. of Plant <strong>Science</strong><br />

9 East Alumni Ave<br />

Kingston, RI 02881<br />

(401) 874-2937<br />

(401) 874-2494<br />

ltn101@urc.edu<br />

Charles F. Scheer<br />

JHalf Hollow Nursery<br />

P.O. Box 563<br />

Laurel, NY 11948<br />

(631) 298-9183<br />

(631) 298-5722<br />

hhn2@optonline.net<br />

M. Gary Schnappinger<br />

930 Starr Road<br />

Centreville, MD 21617<br />

(410) 758-1419<br />

(410) 758-0656<br />

schnapg@toadmail.com<br />

William Sciarappa<br />

Rutgers Cooperative Ext<br />

20 Court Street<br />

Freehold, NJ 07728<br />

(732) 431-7260<br />

(732) 409-4813<br />

sciarappa@aesop.rutgers.edu<br />

151


Rene Scoresby<br />

The Scotts Co<br />

14111 Scottslawn Road<br />

Mt. Vernon, OH 43050<br />

(937) 644-7563<br />

(937) 644-7153<br />

rene.scoresby@scotts.com<br />

Barbara Scott<br />

Univ of Delaware Res & Edu<br />

16684 County Seat H<br />

Georgetown, DE 19947<br />

(302) 856-7303<br />

(302) 856-1845<br />

bascott@udel.edu<br />

Leroy Sellman<br />

Maryland Dept. of Agr<br />

11212 Liberty Road<br />

Owings Mills, MD 21117<br />

(410) 841-5871<br />

(410) 841-5835<br />

csellman@erols.com<br />

Andrew F. Senesac<br />

Cornell Coop Ext -<br />

LIHRELIHREC,<br />

3059 Sound Ave<br />

Riverhead, NY 11901<br />

(631) 727-3595<br />

(631) 727-3611<br />

afs2@cornell.edu<br />

Scott Serafin<br />

DOD G3/Range Division<br />

6034 Pickett Road<br />

Ft. Knox, KY 40121<br />

(270) 268-0178<br />

scot.serafin@know.army.mil<br />

Thomas Serensits<br />

Virginia Tech<br />

Hampton Roads Ag Res<br />

1444 Diamond Spring<br />

Virginia Beach, VA 23455<br />

(610) 360-5985<br />

tseren@vt.edu<br />

Amanda Shearin<br />

University of Maine<br />

26 Deering Hall<br />

Orono, ME 04469<br />

(207) 581-2935<br />

amanda.shearin@umit.maine.edu<br />

Sandra L. Shinn<br />

FMC<br />

1735 Market Street<br />

Philadelphia, PA 19103<br />

Robert Shortell<br />

Rutgers University<br />

16 Hilltop Road<br />

Milford, NJ 08848<br />

(908) 797-8387<br />

shortell@eden.rutgers.edu<br />

Margaret Siligato<br />

University Rhode Island<br />

3 East Alumni Ave<br />

Kingston, RI 02881<br />

(401) 874-5997<br />

siligato@uri.edu<br />

Andrew Z. Skibo<br />

University of De1eware<br />

6684 County Seat Highway<br />

Georgetown, DE 19947<br />

(302) 462-0022<br />

(302) 856-1994<br />

zskibo@aol.com<br />

Larissa Smith<br />

Cornell University<br />

Dept. of Crop & Soil<br />

905 Bradfield Hall<br />

Ithaca, NY 14853<br />

(607) 351-2770<br />

(607) 255-3207<br />

lls14@cornell.edu<br />

Mark Smith<br />

Maryland Dept. of Agriculture<br />

50 Harry S Truman Parkway<br />

Annapolis, MD 21401<br />

(410) 841-5932<br />

(410) 841-5835<br />

John Snitzer<br />

Hood College<br />

PO Box 38<br />

Dickerson, MD 20842<br />

(301) 349-2002<br />

navajuela@earthlink.net<br />

David R. Spak<br />

Bayer Environmental <strong>Science</strong><br />

2 TW Alexander Drive<br />

RTP, NC 27719<br />

david.spak@bayercropscience.com<br />

Paul Stachowski<br />

Cornell University<br />

Dept. of CSS,<br />

107 LelCaldwell Road<br />

Ithaca, NY 14853<br />

(607) 255-7701<br />

(607) 255-2644<br />

pjs16@cornell.edu<br />

Richard Stalter<br />

St. John's University<br />

Dept. of Biology<br />

8000 Utopia Parkway<br />

Jamaica, NY 11439<br />

(718) 990-6288<br />

(718) 990-5958<br />

stalterr@stjohns.edu<br />

Michelle Starke<br />

Monsanto Company<br />

800 N Lindbergh Blvd A2NA<br />

St. Louis, MO 63167<br />

(314) 694-6913<br />

(314) 694-4928<br />

Mark Starrett<br />

Univ of Vermont<br />

105 Carrigan Dr<br />

Burlington, Vt 05405<br />

(802) 656-0467<br />

mark.starrett@uvm.edu<br />

Jennifer Steele<br />

West Virginia University<br />

PO Box 6108<br />

Morgantown, WV 26506<br />

(304) 293-6131<br />

(304) 293-6954<br />

jksteele@mail.wvu.edu<br />

James Steffel<br />

LABServices<br />

342 South Third Street<br />

Hamburg, PA 19526<br />

(610) 562-5055<br />

(610) 562-5066<br />

jim@labservices.com<br />

Stephen Strachan<br />

DuPont Crop Protection<br />

Stine Haskell Res Center<br />

1090 Elkton Rd<br />

Newark, DE 19711<br />

(302) 366-5067<br />

(302) 366-6120<br />

Stephen.d.strachan.1@usa.dupont<br />

.com<br />

152


Robert D. Sweet<br />

Cornell University<br />

Dept. Horticulture<br />

167 Plant <strong>Science</strong> Bld<br />

Ithaca, NY 14853<br />

(607) 273-7106<br />

607-255-0599<br />

sdt1@cornell.edu<br />

Andrea M. Szylvian<br />

US EPA - Region 1<br />

Congress Street CPT Suite 1100<br />

Boston, MA 02114<br />

(617) 918-1198<br />

(617) 918-1505<br />

szylvian.andrea@epa.gov<br />

Alan V. Tasker<br />

USDA APHIS<br />

4700 River Road,<br />

Unit 134 5A45<br />

Riverdale, MD 20737<br />

(301) 734-5708<br />

(301) 734-8584<br />

Alan.V.Tasker@aphis.usda.gov<br />

Raymond B. Taylorson<br />

University of Rhode Island<br />

Department of Plant <strong>Science</strong><br />

Kingston, RI 02881<br />

(401) 874-2106<br />

(401) 874-2494<br />

raymondtaylorson@msn.com<br />

John R. Teasdale<br />

USDA-ARS<br />

Bld 001, Room 245<br />

Beltsville, MD 20705<br />

(301) 504-5504<br />

(301) 504-6491<br />

teasdale@ba.ars.usda.gov<br />

Nishanth Tharayil<br />

Univ of Massachusetts<br />

16 Stockbridge Hall<br />

Dept. of Plant & Soil Sci<br />

Amherst, MA 01003<br />

(413) 545-3072<br />

nishanth@psis.umass.edu<br />

Gar Thomas<br />

BASF Corporation<br />

1002 Bethel Road<br />

Chesapeake City, MD 21915<br />

(410) 885-5920<br />

(410) 885-5975<br />

thomasgg@basf.com<br />

Stewart Throop<br />

FMC Corporation<br />

1735 Market St Room 1935<br />

Philadelphia, PA 19103<br />

(215) 299-6847<br />

(215) 299-6810<br />

stu_throop@fmc.com<br />

Robert Trumbule<br />

Maryland Dept of Agr<br />

50 Harry S Truman Prkwy<br />

Annapolis, MD 21401<br />

(301) 982-3224<br />

(301) 982-3269<br />

rtrumble@erols.com<br />

Robert Uhlig<br />

Michigan State University<br />

5844 Haverhill Drive<br />

Lansing, MI 48911<br />

(517) 272-0106<br />

uhlig@msu.edu<br />

Mark J. Van Gessel<br />

University of Delaware<br />

Research & Education<br />

16684 County Seat H<br />

Georgetown, DE 19947<br />

(302) 856-7303<br />

(302) 856-1845<br />

mjv@udel.edu<br />

Terry Van Horn<br />

Delaware Dept. of Agriculture<br />

2320 S. Dupont Highway<br />

Dover, DE 19901<br />

(302) 698-4580<br />

(302) 697-4468<br />

Terry.VanHorn@state.de.us<br />

Lee Van Wychen<br />

National and Regional<br />

900 2nd St. NE Suite 205<br />

Washington, DC 20002<br />

(202) 408-5388<br />

(202) 408-5385<br />

Lee.VanWychen@<strong>Weed</strong><strong>Science</strong><br />

Orgs.com<br />

Ely Vea<br />

IR-4 Hdqt. Rutgers Univ.<br />

500 College Rd East, 201W<br />

Princeton, NJ 08540<br />

Christina Venable<br />

West Virginia University<br />

Morgantown, WV 26506<br />

(304) 685-9667<br />

clvenable@yahoo.com<br />

Daniel Vincent<br />

DuPont Crop Protection<br />

1090 Elkton Rd<br />

Newark, DE 19771<br />

(302) 451-4802<br />

Daniel.r.vincent@usa.dupont.com<br />

David Vitolo<br />

Syngenta Crop Protection<br />

2109 9th Avenue<br />

Sacramento, CA 95818<br />

(916) 316-6951<br />

david.vitolo@syngenta.com<br />

F. R. Bobby Walls<br />

FMC Corporation<br />

501 Parkwood Lane<br />

Goldsboro, NC 27530<br />

(919) 735-3862<br />

(919) 736-2686<br />

bobby_walls@fmc.com<br />

Thomas L. Watschke<br />

Penn State University<br />

425 ASI Bldg<br />

University Park, PA 16802<br />

(814) 863-7644<br />

(814) 863-7043<br />

tlw3@psu.edu<br />

Cory M. Whaley<br />

Virginia Tech<br />

33446 Research Drive<br />

Painter, VA 23420<br />

(757) 414-0724<br />

cwhaley@vt.edu<br />

Tim White<br />

CMS<br />

PO BOX 510<br />

Hereford, PA 18056<br />

(610) 767-1944<br />

cms1@fast.net<br />

John Willis<br />

Virginia Tech<br />

435 Old Glade Road<br />

Glade Road Research Station<br />

Blacksburg, VA 24061<br />

(540) 231-5835<br />

(540) 231-5755<br />

jbwillis@vt.edu<br />

153


Sam Wilson<br />

FMC<br />

117 Tealight Lane<br />

Cary, NC 27513<br />

(919) 469-1249<br />

sam_wilson@fmc.com<br />

Henry P. Wilson<br />

Virginia Tech<br />

Eastern Shore AREC<br />

33446 Research Drive<br />

Painter, VA 23420<br />

(757) 414-0724<br />

(757) 414-0730<br />

hwilson@vt.edu<br />

Robert E.Wooten<br />

North Carolina State Univer<br />

Dept. of Horticulture Box 7609<br />

Raleigh, NC 27695<br />

(919) 515-2650<br />

(919) 515-7747<br />

rob_wooten@ncsu.edu<br />

Joe Zawierucha<br />

BASF Corporation<br />

26 Davis Drive<br />

Research Triangle Park, NC<br />

27709<br />

(919) 547-2095<br />

zawierj@basf.com<br />

Magdalena Zazirska<br />

Oregon State University<br />

North Willamette Res.<br />

15210 NE Miley Road<br />

Aurora, OR 97002<br />

(503) 678-1264<br />

(503) 678-5986<br />

Stanley Zontek<br />

USGA Mid Atlantic<br />

485 Baltimore Pike, Suite 203<br />

Glen Mills, PA 19342<br />

(610) 696-4747<br />

(610)-696-4810<br />

zontek@usga.org<br />

Deneen Wortham<br />

USDA-CREES<br />

1400 Independence Ave SW<br />

RM 304A<br />

Washington, DC 20250<br />

Jeff Wright<br />

University of Delaware<br />

16483 County Seat Highway<br />

Georgetown, DE 19947<br />

(302) 856-7303<br />

wrightj@udel.edu<br />

David Yarborough<br />

University of Maine<br />

5722 Deering Hall<br />

Rm 414<br />

Orono, ME 04469<br />

207-581-2923<br />

207-581-2941<br />

davidy@maine.edu<br />

Kevin Young<br />

Four Points Sheraton<br />

35 Scudder Ave<br />

Hyannis, MA 02601<br />

(508) 862-6977<br />

kevin.young@fourpoints.com<br />

154


HERBICIDE NAMES: COMMON, TRADE, AND CHEMICAL<br />

Common and Chemical Names of Herbicides Approved by The <strong>Weed</strong> <strong>Science</strong><br />

<strong>Society</strong> of America<br />

Common Name Trade Name Chemical Name<br />

acetochlor Breakfree;Harnes<br />

s, Surpass,<br />

Topnotch,<br />

Degree<br />

2-chloro-N-(ethoxymethyl)-N-(2-ethyl-6-methylphe<br />

nyl) acetamide<br />

acifluorfen<br />

acrolein<br />

alachlor<br />

allyl alcohol<br />

Blazer, Status<br />

Blazer Ultra<br />

Intrro, MicroTech,<br />

Partner; many<br />

5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenz<br />

oic acid<br />

2-propenal<br />

2-chloro-N-(2,6-diethylphenyl)-N-(methoxymethyl)<br />

acetamide<br />

2-propen-l-ol<br />

alloxydim Clout methyl 2,2-dimethyl-4,6-dioxo-5-[1-[(2-<br />

propenyloxy)amino]butylidene]cyclohexanecarboxy<br />

late<br />

ametryn Evik N-ethyl-N'-(1-methylethyl)-6-(methylthio)-1,3,5-triaz<br />

ine-2,4- diamine<br />

amicarbazone Dinamic 4-amino-N-(1,1-dimethylethyl)-4,5-dihydro-3-(1-<br />

methylethyl)-5-oxo-1H-1,2,4-triazole-1-<br />

carboxamide<br />

aminopyralid Milestone 2-pyridine carboxylic acid, 4-amino-3,6-dichloro-<br />

2-pyridinecarboxylic acid<br />

amitrole<br />

Amitrol, Amizol, 1H-1,2,4-triazol-3-amine<br />

Azolan<br />

asulam Asulox methyl[(4-aminophenyl)sulfonyl]carbamate<br />

atraton Gesatamin N-ethyl-6-methoxy-N'-(1-methylethyl)-1,3,5-<br />

triazine-2,4-diamine<br />

atrazine Aatrex, many 6-chloro-N-ethyl-N’-(1-methylethyl)-1,3,5-triazine-<br />

2,4-diamine<br />

azafenidin<br />

2-[2,4-dichloro-5-(2-propynyloxy)phenyl]-5,6,7,8-<br />

tetrahydro-1,2,4-triazolo[4,3-a]pyridin-3(2H)-one<br />

azimsulfuron Gulliver N-[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]-1<br />

-methyl-4-<br />

(2-methyl-2H-tetrazol-5-yl)-1H-pyrazole-5-<br />

sulfonamide<br />

barban<br />

Carbyne,<br />

Neoban, Oatax,<br />

many<br />

4-chloro-2-butynyl 3-chlorophenylcarbamate<br />

155


Common Name Trade Name Chemical Name<br />

BCPC<br />

1-methylpropyl 3-chlorophenylcarbamate<br />

beflubutamid<br />

2-[4-fluoro-3-(trifluoromethyl)phenoxy]-N-<br />

(phenylmethyl)butanamide<br />

benazolin Galtak, Dasen, 4-chloro-2-oxo-3(2H)-benzothiazoleacetic acid<br />

Rescate<br />

benefin Balan N-butyl-N-ethyl-2,6-dinitro-4-(trifluoromethyl)<br />

benzenamine<br />

bensulfuron Londax 2-[[[[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]<br />

amino]sulfonyl]methyl]benzoic acid<br />

bensulide<br />

bentazon<br />

Bensumec,<br />

Betason, Prefar<br />

Basagran,<br />

Lescogran<br />

O,O-bis(1-methylethyl)S-[2-[(phenylsulfonyl)amino]<br />

ethyl]phosphorodithioate<br />

3-(1-methylethyl)-(1H)-2,1,3-benzothiadiazin-4(3H)<br />

-one 2,2-dioxide<br />

benzadox Topcide [(benzoylamino)oxy]acetic acid<br />

benzfendizone<br />

methyl 2-[2-[[4-[3,6-dihydro-3-methyl-2,6-dioxo-4-<br />

(trifluoromethyl)-1(2H)pyrimidinyl)phenoxy]methyl]-<br />

5-ethylphenoxy]propanoic acid<br />

benzipram<br />

3,5-dimethyl-N-(1-methylethyl)-N-<br />

(phenylmethyl)benzamide<br />

benzofenap Yukawide 2-[4-(2,4-dichloro-m-toluoyl)-1,3-dimethylpyrazol-5-<br />

yloxy]-4’-methy-lacetophenone<br />

benzofluor<br />

N-[4-(ethylthio)-2-<br />

(trifluoromethyl)phenyl]methanesulfonamide<br />

benzoylprop Suffix N-benzoyl-N-(3,4-dichlorophenyl)-DL-alanine<br />

benzthiazuron Gatnon N-2-benzothiazolyl-N'-methylurea<br />

bifenox Fox methyl 5-(2,4-dichlorophenoxy)-2-nitrobenzoate<br />

borax<br />

sodium tetraborate<br />

bispyribac Velocity,<br />

Regiment<br />

2,6-bis[(4,6-dimethoxy-2-pyrimidinyl)oxy]benzoic<br />

acid<br />

bromacil Hyvar 5-bromo-6-methyl-3-(1-methylpropyl)-2,4(1H,<br />

3H)pyrimidinedione<br />

bromofenoxim Faneron 3,5-dibromo-4-hydroxybenzaldehyde O-(2,4-<br />

dinitrophenyl) oxime<br />

bromoxynil Brominal, Buctril,<br />

Moxy<br />

3,5-dibromo-4-hydroxybenzonitrile<br />

butachlor<br />

Butanox,<br />

Pilarsete, many<br />

N-(butoxymethyl)-2-chloro-N-(2,6-<br />

diethylphenyl)acetamide<br />

butafenacil Inspire 2-chloro-5-(3-methyl-2,6,dioxo-4-triflouromethyl-<br />

3,6-dihydro-2H-pyrimidyl)-benzoic acid 1-<br />

allylocycarbonyl-1-methyl-ethyl-ester<br />

156


Common Name Trade Name Chemical Name<br />

butam<br />

2,2-dimethyl-N-(1-methylethyl)-N-(phenylmethyl)<br />

propanamide<br />

butamifos Cremart O-ethyl O-(5-methyl-2-nitrophenyl) 1-<br />

methylpropylphosphoramidothioate<br />

buthidazole<br />

3-[5-(1,1-dimethylethyl)-1,3,4-thiadiazol-2-yl]-4-<br />

hydroxy-1-methyl-2-imidazolidinone<br />

butralin<br />

AMEX-820,<br />

TAMEX<br />

4-(1,1-dimethylethyl)-N-(1-methylpropyl)-2,6-<br />

dinitrobenzenamine<br />

buturon<br />

butylate<br />

cacodylic acid<br />

cambendichlor<br />

carbetamide<br />

Butafume,<br />

Deccotane,<br />

Tutane<br />

Sutan+, Genate<br />

Plus<br />

Cotton-aide,<br />

Montar, Phytar<br />

560<br />

Carbetamex,<br />

Legurame,<br />

Pradone<br />

N'-(4-chlorophenyl)-N-methyl-N-(1-methyl-2-<br />

propynyl)urea<br />

S-ethyl bis(2-methylpropyl)carbamothioate<br />

dimethyl arsinic acid<br />

(phenylimino)di-2,1-ethanediyl bis(3,6-dichloro-2-<br />

methoxybenzoate)<br />

N-ethyl-2-<br />

[[(phenylamino)carbonyl]oxy]propanamide (R)-<br />

isomer<br />

CDAA Randox 2-chloro-N,N-di-2-propenylacetamide<br />

carfentrazone Aim, Affinity,<br />

QuickSilver IVM,<br />

Stingray<br />

α,2-dichloro-5-[4-(difluoromethyl)-4,5-<br />

dihydro-3-methyl-5-oxo-1H-1,2,4-triazol-1-yl]<br />

-4-fluorobenzenepropanoic acid<br />

CDEA<br />

2-chloro-N,N-diethylacetamide<br />

CDEC Vegadex 2-chloro-2-propenyl diethylcarbamodithioate<br />

CEPC<br />

2-chloroethyl (3-chlorophenyl)carbamate<br />

chloramben Amiben, Amilon, 3-amino-2,5-dichlorobenzoic acid<br />

Dynoram,<br />

Vegiben<br />

chlorazine<br />

6-chloro-N,N,N',N'-tetraethyl-1,3,5-triazine-2,4-<br />

diamine<br />

chlorbromuron Maloran N'-(4-bromo-3-chlorophenyl)-N-methoxy-Nmethylurea<br />

chlorbufam Alicep, Alipur, 1-methyl-2-propynyl (3-chlorophenyl)carbamate<br />

Trixabon<br />

chlorflurenol Maintain, CF 125 2-chloro-9-hydroxy-9H-fluorene-9-carboxylic acid<br />

chlorimuron Classic 2-[[[[(4-chloro-6-methoxy-2-pyrimidinyl)amino]carb<br />

onyl]a-mino]sulfonyl]benzoic acid<br />

157


Common Name Trade Name Chemical Name<br />

chloroxuron Norex, Tenoran N'-[4-(4-chlorophenoxy)phenyl]-N,N-dimethylurea<br />

chlorpropham Gro-stop, Unicrop 1-methylethyl 3-chlorophenylcarbamate<br />

chlorsulfuron<br />

chlorthiamid<br />

chlortoluron<br />

cinmethylin<br />

cisanilide<br />

clethodim<br />

Corsair, Glean,<br />

Telar,<br />

Glean,Lesco<br />

TFCr<br />

Alert, Culmus,<br />

Tolurex, Toluron<br />

Prism, Select,<br />

Envoy<br />

2-chloro-N-[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)<br />

amino]carbonyl] benzenesulfonamide<br />

2,6-dichlorobenzenecarbothiamide<br />

N'-(3-chloro-4-methylphenyl)-N,N-dimethylurea<br />

exo-(±)-1-methyl-4-(1-methylethyl)-2-[(2-<br />

methylphenyl) methoxy]-7-<br />

oxabicyclo[2.2.1]heptane<br />

cis-2,5-dimethyl-N-phenyl-1-<br />

pyrrolidinecarboxamide<br />

(E,E)-(±)-2-[1-[[(3-chloro-2-propenyl)oxy]imino]prop<br />

yl]-5-[2-(ethylthio)propyl]-<br />

3-hydroxy-2-cyclohexen-1-one<br />

clofop Alopex 2-[4-(4-chlorophenoxy)phenoxy]propanoic acid<br />

clomazone Command 2-[(2-chlorophenyl)methyl]-4,4-dimethyl-3-isoxazoli<br />

dinone<br />

cloproxydim<br />

(E,E)-2-[1-[[(3-chloro-2-propenyl)oxy]imino]butyl]-<br />

5-[2-(ethylthio)propyl]-3-hydroxy-2-cyclohexen-1-<br />

one<br />

clopyralid Reclaim, Stinger, 3,6-dichloro-2-pyridinecarboxylic acid<br />

Transline, Lontrel<br />

cloransulam FirstRate 3-chloro-2-[[(5-ethoxy-7-fluoro[1,2,4]triazolo[1,5-c]<br />

pyrimidin-2yl)sulfonyl]amino]benzoic acid<br />

copper sulfate Copper Sulfate copper sulfate<br />

4-CPA<br />

Marks 4-CPA, (4-chlorophenoxy)acetic acid<br />

Poltomat,<br />

Tomadorane<br />

4-CPB<br />

4-(4-chlorophenoxy)butyric acid<br />

CPMF<br />

1-chloro-N'-(3,4-dichlorophenyl)-N-Ndimethylformamidine<br />

4-CPP<br />

2-(4-chlorophenoxy)propionic acid<br />

CPPC<br />

2-chloro-1-methylethyl (3-chlorophenyl)carbamate<br />

cyanazine Bladex 2-[[4-chloro-6-(ethylamino)-1,3,5-triazin-2-<br />

yl]amino]-2-methylpropanenitrile<br />

cycloate Ro-Neet S-ethyl cyclohexylethylcarbamothioate<br />

158


Common Name Trade Name Chemical Name<br />

cyclosulfamuron Ichiyonmaru,<br />

Nebiros<br />

N-[[[2-(cyclopropylcarbonyl)phenyl]amino]sulfonyl]-<br />

N'-(4,6-dimethoxy-2- pyrimidinyl)urea<br />

Double-Up<br />

cycluron<br />

cyhalofop Clincher (R)-2-[4-(4-cyano-2-fluorophenoxy)phenoxy]propa<br />

noic acid<br />

cyperquat<br />

1-methyl-4-phenylpyridinium<br />

cyprazine Prefox, Outfox 6-chloro-N-cyclopropyl-N'-(1-methylethyl)-1,3,5-<br />

triazine-2,4-diamine<br />

cyprazole<br />

N-[5-(2-chloro-1,1-dimethylethyl)-1,3,4-thiadiazol-<br />

2-yl] cyclopropanecarboxamide<br />

cypromid Clobber N-(3,4-dichlorophenyl)cyclopropanecarboxamide<br />

2,4-D many (2,4-dichlorophenoxy)acetic acid<br />

3,4-DA<br />

(3,4-dichlorophenoxy)acetic acid<br />

dalapon<br />

Dalapon,<br />

2,2-dichloropropanoic acid<br />

Devipon,<br />

Dalacide,<br />

Depoxim, many<br />

dazomet Basamid tetrahydro-3,5-dimethyl-2H-1,3,5-thiadiazine-2-thio<br />

ne<br />

2,4-DB<br />

Butoxone, 4-(2,4-dichlorophenoxy)butanoic acid<br />

Butyrac<br />

3,4-DB<br />

4-(3,4-dichlorophenoxy)butanoic acid<br />

DCB<br />

1,2-dichlorobenzene<br />

DCPA Dacthal dimethyl<br />

2,3,5,6-tetrachloro-1,4-benzenedicarboxylate<br />

DCU Crag 2 N,N'-bis(2,2,2-trichloro-1-hydroxyethyl)urea<br />

2,4-DEB<br />

2-(2,4-dichlorophenoxy)ethyl benzoate<br />

delachlor<br />

2-chloro-N-(2,6-dimethylphenyl)-N-[(2-<br />

methylpropoxy)methyl] acetamide<br />

2,4-DEP<br />

tris[2-(2,4-dichlorophenoxy)ethyl]phosphite<br />

desmedipham Betanex ethyl[3-[[(phenylamino)carbonyl]oxy]phenyl]carbam<br />

ate<br />

desmetryn Semeron N-methyl-N'-(1-methylethyl)-6-(methylthio)-1,3,5-<br />

triazine-2,4-diamine<br />

diallate<br />

dicamba<br />

Avadex, Botrizel,<br />

Pyardex, many<br />

Banvel, Clarity,<br />

Vanquish<br />

S-(2,3-dichloro-2-propenyl) bis(1-<br />

methylethyl)carbamothioate<br />

3,6-dichloro-2-methoxybenzoic acid<br />

159


Common Name Trade Name Chemical Name<br />

dichlobenil Barrier, Casoron, 2,6-dichlorobenzonitrile<br />

Dyclomec,<br />

Norosac<br />

dichlormate Rowmate 3,4-dichloro benzenemethanol methylcarbamate<br />

dichlorprop <strong>Weed</strong>one 2,4-DP (±)-2-(2,4-dichlorophenoxy)propanoic acid<br />

diclofop Hoelon, Illoxan (±)-2-[4-(2,4-dichlorophenoxy)phenoxy]propanoic<br />

acid<br />

diclosulam Strongarm N-(2,6-dichlorophenyl)-5-ethoxy-7-fluoro[1,2,4]triaz<br />

olo[1,5-c] pyrimidine-2-sulfonamide<br />

dicryl<br />

N-(3,4-dichlorophenyl)-2-methyl-2-propenamide<br />

diethatyl Antor N-(chloroacetyl)-N-(2,6-diethylphenyl)glycine<br />

difenopenten<br />

(E)-(±)-4-[4-[4-(trifluoromethyl)phenoxy]phenoxy]-<br />

2-pentenoic acid<br />

difenoxuron Lironion, Pinoran N'-[4-(4-methoxyphenoxy)phenyl]-N,Ndimethylurea<br />

difenzoquat Avenge 1,2-dimethyl-3,5-diphenyl-1H-pyrazolium<br />

diflufenzopyr 2-[1-[[[(3,5-<br />

difluorophenyl)amino]carbonyl]hydrazono]ethyl]-3-<br />

pyridinecarboxylic acid<br />

dimethachlor Ohric 2-chloro-N-(2,6-dimethylphenyl)-N-(2-<br />

methoxyethyl) acetamide<br />

dimethametryn Dimepax N-(1,2-dimethylpropyl)-N'-ethyl-6-(methylthio)-<br />

1,3,5-triazine-2,4-diamine<br />

dimethenamid Frontier 2-chloro-N-(2,4-dimethyl-3-thienyl)-N-(2-methoxy-<br />

1-methylethyl)acetamide<br />

dimethenamid-P Outlook (S)-2-chloro-N-(2,4-dimethyl-3-thienyl)-N-(2-<br />

methoxy-1-methylethyl)acetamide<br />

dinitramine Cobexo N 3 ,N 3 -diethyl-2,4-dinitro-6-(trifluoromethyl)-1,3-<br />

benzenediamine<br />

dinosam Sinox general 2-(1-methylbutyl)-4,6-dinitrophenol<br />

dinoseb<br />

Basanite, 2-(1-methylpropyl)-4,6-dinitrophenol<br />

Dynamyte,<br />

Dyanap, many<br />

dinoterb Herbogil 2-(1,1-dimethylethyl)-4,6-dinitrophenol<br />

diphenamid Enide N,N-dimethyl-a-phenyl benzeneacetamide<br />

dipropetryn Cotofor, Sancap 6-(ethylthio)-N,N'-bis(1-methylethyl)-1,3,5-triazine-<br />

2,4-diamine<br />

diquat<br />

Diquat, Reglone,<br />

Reward<br />

6,7-dihydrodipyrido[1,2-a:2',1'-c]pyrazinediiumion<br />

160


Common Name Trade Name Chemical Name<br />

dithiopyr Dimension S,S-dimethyl<br />

2-(difluoromethyl)-4-(2-methylpropyl)-6-<br />

trifluoromethyl)- 3,5-pyridinedicarbothioate<br />

diuron Karmex, Direx N'-(3,4-dichlorophenyl)-N,N-dimethylurea<br />

DNOC<br />

Trifocide, Trifinox, 2-methyl-4,6-dinitrophenol<br />

Trifrina<br />

3,4-DP<br />

2-(3,4-dichlorophenoxy) propanoic acid<br />

DSMA Ansar, many disodium salt of MAA<br />

EBEP<br />

ethyl bis (2-ethylhexyl)phosphinate<br />

eglinazine<br />

N-(4-chloro-6-ethylamino-1,3,5-triazin-2-yl)glycine<br />

endothall Aquathol, 7-oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid<br />

Accelerate,<br />

Desicate, H-273<br />

EPTC<br />

Eptam, Eradicane S-ethyl dipropyl carbamothioate<br />

Extra, Genep,<br />

Genep Plus<br />

erbon Baron, Novege 2-(2,4,5-trichlorophenoxy)ethyl-2,2-<br />

dichloropropanoate<br />

ethalfluralin<br />

Sonalan, Curbit,<br />

Edge<br />

N-ethyl-N-(2-methyl-2-propenyl)-2,6-dinitro-4-(triflu<br />

oro-methyl)benzenamine<br />

ethametsulfuron Muster 2-[[[[[4-ethoxy-6-(methylamino)-1,3,5-triazin-2-yl]a<br />

mino] carbonyl]amino]sulfonyl]benzoic acid<br />

ethidimuron Ustilon N-(5-ethylsulfonyl-1,3,4-thiadiazol-2-yl)-N,N'-<br />

dimethylurea<br />

ethiolate Outfox, Prefox S-ethyl diethylcarbamothioate<br />

ethofumesate Nortron (±)-2-ethoxy-2,3-dihydro-3,3-dimethyl-5-benzofura<br />

nyl methanesulfonate<br />

EXD<br />

diethyl thioperoxydicarbonate<br />

fenac<br />

Fenatrol, Rack,<br />

Trifene<br />

2,3,6-trichlorobenzeneacetic acid<br />

fenoxaprop<br />

Acclaim, Horizon,<br />

Puma, Whip<br />

(±)-2-[4-[(6-chloro-2-benzoxazolyl)oxy]phenoxy]pro<br />

panoic acid<br />

fenuron Dozer, Urab N,N-dimethyl-N'-phenylurea<br />

flamprop Barnon, Suffix N-benzoyl-N-(3-chloro-4-fluorophenyl)-DL-alanine<br />

BW, Mataven L<br />

flazasulfuron Mission N-[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]-<br />

3-(trifluoromethyl)-2-pyridinesulfonamide<br />

florasulam Primus, Boxer N-(2,6-difluorophenyl)-8-fluoro-5-<br />

ethoxy[1,2,4]triazolo[1,5-c]pyrimidine-2-<br />

sulfonamide<br />

161


Common Name Trade Name Chemical Name<br />

fluazifop Fusilade,<br />

Horizon,<br />

Ornamec<br />

(R)-2-[4-[[5-(trifluoromethyl)-2-pyridinyl]oxy]phenox<br />

y]-propanoic acid<br />

fluazifop-p<br />

Fusilade II,<br />

Venture<br />

(R)-2-[4-[[5-(trifluoromethyl)-2-<br />

pyridinyl]oxy]phenoxy] propanoic acid<br />

flucarbazone Everest 4,5-dihydro-3-methoxy-4-methyl-5-oxo-N-[[2-<br />

(trifluoromethoxy)phenyl]sulfonyl]-1H-1,2,4-<br />

triazole-1-carboxamide<br />

fluchloralin Basalin, Flusol N-(2-chloroethyl)-2,6-dinitro-N-propyl-4-<br />

(trifluoromethyl) benzenamine<br />

flufenacet Define N-(4-fluorophenyl)-N-(1-methylethyl)-2-[[5-<br />

(trifluoromethyl)-1,3,4-thiadiazol-2-<br />

yl]oxy]acetamide<br />

flumetsulam Python N-(2,6-difluorophenyl)-5-methyl[1,2,4]triazolo[1,5-a<br />

] pyrimidine-2-sulfonamide<br />

flumiclorac Resource [2-chloro-4-fluoro-5-(1,3,4,5,6,7-hexahydro-1,3-dio<br />

xo-2H- isoindol-2-yl)phenoxy]acetic acid<br />

flumioxazin<br />

Broadstar,<br />

Flumizin,<br />

Sumisoya, Valor,<br />

SureGuard<br />

2-[7-fluoro-3,4-dihydro-3-oxo-4-(2-propynyl)-2H-1,4<br />

-<br />

benzoxazin-6-yl]-4,5,6,7-tetrahydro-1H-insoindole-<br />

1,3(2H)- dione<br />

fluometuron Cotoran N,N-dimethyl-N'-[3-(trifluoromethyl)phenyl]urea<br />

fluorochloridone Racer, Talis 3-chloro-4-(chloromethyl)-1-[3-<br />

(trifluoromethyl)phenyl]-2-pyrrolidinone<br />

fluorodifen Preforan 2-nitro-1-(4-nitrophenoxy)-4-<br />

trifluoromethylbenzene<br />

fluoroglycofen Compete carboxymethyl 5-[2-chloro-4-<br />

(trifluoromethyl)phenoxy]-2-nitrobenzoate<br />

flupoxam<br />

1-[4-chloro-3-[(2,2,3,3,3-<br />

pentafluoropropoxy)methyl]- phenyl]-5-phenyl-1H-<br />

1,2,4-triazole-3-carboxamide<br />

flupropacil<br />

1-methylethyl<br />

2-chloro-5-[3,6-dihydro-3-methyl-2,6-dioxo-4-(triflu<br />

oromethyl)-1(2H)-pyrimidinyl]benzoate<br />

flupyrsulfuron Lexus 2-[[[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]a<br />

mino]sulfonyl]-6-trifluoromethyl)-3-pyridinecarboxyli<br />

c acid<br />

fluridone Avast, Sonar 1-methyl-3-phenyl-5-[3-(trifluoromethyl)phenyl]-4(1<br />

H)- pyridinone<br />

162


Common Name Trade Name Chemical Name<br />

fluroxypyr Starane,<br />

Spotlight,<br />

Tomahawk, Vista<br />

[(4-amino-3,5-dichloro-6-fluoro-2-pyridinyl)oxy]acet<br />

ic acid<br />

flurtamone<br />

Bacara, Carat,<br />

Cline, Nikeyl,<br />

Ingot, Benchmark<br />

(±)-5-(methylamino)-2-phenyl-4-[3-<br />

(trifluoromethyl)phenyl]-3 (2H)-furanone<br />

fluthiacet Action, Appeal [[2-chloro-4-fluoro-5-[(tetrahydro-3-oxo-1H,3H-<br />

[1,3,4]thiadiazolo[3,4-a]pyridazin-1-<br />

ylidene)amino]phenyl]thio]acetic acid<br />

fomesafen Reflex, Flexstar 5-[2-chloro-4-(trifluoromethyl)phenoxy]-N-(methyls<br />

ulfonyl)-2-nitrobenzamide<br />

foramsulfuron Option, Revolver 2-[[[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]<br />

amino]sulfonyl]-4-(formylamino)-N,Ndimethylbenzamide<br />

fosamine Krenite ethyl hydrogen (aminocarbonyl)phosphonate<br />

glufosinate Finale, Liberty, 2-amino-4-(hydroxymethylphosphinyl)butanoic acid<br />

Rely<br />

glyphosate Glyphomax, N-(phosphonomethyl)glycine<br />

Glyphos,<br />

Roundup,<br />

Touchdown;<br />

many<br />

halosafen<br />

5-[2-chloro-6-fluoro-4-(trifluoromethyl)phenoxy]-N-<br />

(ethylsulfonyl)-2-nitrobenzamide<br />

haloxyfop Vulkan, Verdict (±)-2-[4-[[3-chloro-5-(trifluoromethyl)-2-<br />

pyridinyl]oxy] phenoxy]propanoic acid<br />

halosulfuron<br />

Manage, Permit,<br />

Sandea, Sempra,<br />

Sedgehammer<br />

3-chloro-5-[[[[(4,6-dimethoxy-2-<br />

pyrimidinyl)amino]carbonyl]amino]sulfonyl]-1-<br />

methyl-1H-pyrazole-4-carboxylic acid<br />

hexaflurate<br />

potassium hexafluoroarsenate<br />

hexazinone Pronone, Velpar 3-cyclohexyl-6-(dimethylamino)-1-methyl-1,3,5-tria<br />

zine-2,4(1H,3H)-dione<br />

imazamethabenz Assert (±)-2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-oxo<br />

-1H- imidazol-2-yl]-4(and 5)-methylbenzoic acid<br />

(3:2)<br />

imazamox ClearCast,<br />

Raptor, Odessey<br />

2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-oxo-1H<br />

- imiazol-2-yl]-5-<br />

(methoxymethyl)-3-pyridinecarboxylic acid<br />

imazapic Cadre, Plateau (±)-2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-<br />

oxo-1H-imidazol-2-yl]-5-methyl-3-<br />

pyridinecarboxylic acid<br />

163


Common Name Trade Name Chemical Name<br />

imazapyr Arsenal,<br />

Chopper, Stalker,<br />

(±)-2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-oxo<br />

-1H -imidazol-2-yl]-3-pyridinecarboxylic acid<br />

Habitat<br />

imazaquin Image, Scepter 2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-oxo-1H<br />

- imidazol-2-yl]-3-quinolinecarboxylic acid<br />

imazethapyr NewPath, Pursuit 2-[4,5-dihydro-4-methyl-4-(1-methylethyl)-5-oxo-1H<br />

- imidazol-2-yl]-5-ethyl-3-pyridinecarboxylic acid<br />

iodosulfuron Autumn, Husar 4-iodo-2-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-<br />

yl)amino]carbonyl]amino]sulfonyl]benzoic acid<br />

ioxynil<br />

Actil, Axall, 4-hydroxy-3,5-diiodobenzonitrile<br />

Brittox, Bentrol,<br />

Oxytril, many<br />

ipazine Gesabal 6-chloro-N,N-diethyl-N'-(1-methylethyl)-1,3,5-<br />

triazine-2,4-diamine<br />

IPX Goodrite n.i.x O-(1-methylethyl)carbonodithioate<br />

isocarbamid Merpelan AZ N-(2-methylpropyl)-2-oxo-1-<br />

imidazolidinecarboxamide<br />

isocil<br />

5-bromo-6-methyl-3-(1-methylethyl)-2,4(1H,3H)-<br />

pyrimidinedione<br />

isomethiozin Tantizon 6-(1,1-dimethylethyl)-4-[(2-<br />

methylpropylidene)amino]-3-(methylthio)-1,2,4-<br />

triazin-5-(4H)-one<br />

isopropalin Paarlan 4-(1-methylethyl)-2,6-dinitro-N,Ndipropylbenzenamine<br />

isoproturon Zodiac, Crip, N,N-dimethyl-N'-[4-(1-methylethyl)phenyl]urea<br />

Ingot<br />

isouron<br />

N'-[5-(1,1-dimethylethyl)-3-isoxazolyl]-N,Ndimethylurea<br />

isoxaben Gallery N-[3-(1-ethyl-1-methylpropyl)-5-isoxazolyl]-2,6-dim<br />

eth- oxybenzamide<br />

isoxaflutole<br />

karbutilate<br />

ketospiradox<br />

KOCN<br />

Balance, Balance<br />

Pro<br />

Backup, Tandex,<br />

Tanzene<br />

(5-cyclopropyl-4-isoxazolyl)[2-(methylsulfonyl)-4-<br />

(trifluoromethyl)-phenyl]methanone<br />

3-[[(dimethylamino)carbonyl]amino]phenyl (1,1-<br />

dimethylethyl)carbamate<br />

2-[(2,3dihydro-5,8-dimethyl-1,1-dioxidospiro[4H-1-<br />

benzothiopyran-4,2’-[1,3]dioxolan]-6-yl)carbonyl]-<br />

1,3-cyclohexanedione ion(1-)<br />

potassium cyanate<br />

lactofen Cobra (±)-2-ethoxy-1-methyl-2-oxoethyl<br />

5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenz<br />

oate<br />

164


Common Name Trade Name Chemical Name<br />

lenacil<br />

Lenazar, Venar,<br />

Lanslide,<br />

3-cyclohexyl-6,7-dihydro-1H-cyclopentapyrimidine-<br />

2,4 (3H,5H)-dione<br />

Pyaracur, many<br />

linuron<br />

Lorox, Linex, N'-(3,4-dichlorophenyl)-N-methoxy-N-methylurea<br />

Afolan<br />

MAA<br />

methylarsonic acid<br />

MAMA<br />

monoammonium salt of MAA<br />

maleic hydrazide Royal MH30, 1,2-dihydro-3,6-pyridazinedione<br />

Royal Slo-Gro<br />

MCPA many (4-chloro-2-methylphenoxy)acetic acid<br />

MCPB Cantrol, Thistrol 4-(4-chloro-2-methylphenoxy)butanoic acid<br />

mecoprop Mecomec, Super (±)-2-(4-chloro-2-methylphenoxy)propanoic acid<br />

Chickweed Killer<br />

mefluidide Embark, Vistar N-[2,4-dimethyl-5-[[(trifluoromethyl)sulfonyl]amino]<br />

phenyl]acetamide<br />

mesotrione Callisto 2-(4-mesyl-2-nitrobenzoyl)-3-hydroxycyclohex-2-<br />

enone<br />

metamifop<br />

(R)-2-[4-(6-chloro-1,3-benzoxazol-2-<br />

yloxy)phenoxy]-2′-fluoro-N-methylpropionanilide<br />

metamitron Seismic,<br />

4-amino-3-methyl-6-phenyl-1,2,4-triazin-5(4H)-one<br />

Tornado,<br />

Danagan, many<br />

methalpropalin<br />

N-(2-methyl-2-propenyl)-2,6-dinitro-N-propyl-4-<br />

(trifluoromethyl)benzenamine<br />

metham Vapam methylcarbamodithioic acid<br />

methazole Probe 2-(3,4-dichlorophenyl)-4-methyl-1,2,4-<br />

oxadiazolidine-3,5-dione<br />

methibenzuron Tribull, Tribunil, N-(2-benzothiazolyl-N,N'-dimethylurea<br />

Trilixon<br />

methoprotryn Gesaran N-(3-methoxypropyl)-N'-(1-methylethyl)-6-<br />

(methylthio)-1,3,5-triazine-2,4-diamine<br />

methyl bromide Rotox, Metabrom, bromomethane<br />

Pestmaster,<br />

many<br />

metobromuron Patoran,<br />

N'-(4-bromophenyl)-N-methoxy-N-methylurea<br />

Pattonex<br />

metolachlor Dual, Pennant 2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-<br />

1- methylethyl)acetamide<br />

165


Common Name Trade Name Chemical Name<br />

s-metolachlor Cinch, Dual<br />

Magnum<br />

2-chloro-N-(2-ethyl-6-methylphenyl)-N-(2-methoxy-<br />

1- methylethyl)acetamide, S-enantiomer<br />

Pennant Magnum<br />

metosulam Barko N-(2,6-dichloro-3-methylphenyl)-5,7-dimethoxy[1,2,<br />

4] triazolo[1,5-a]pyrimidine-2- sulfonamide<br />

metoxuron Dosaflo, Deftor, N'-(3-chloro-4-methoxyphenyl)-N,N-dimethyl urea<br />

many<br />

metribuzin Sencor 4-amino-6-(1,1-dimethylethyl)-3-(methylthio)-1,2,4-<br />

triazin-5(4H)-one<br />

metsulfuron<br />

Ally, Blade,<br />

Cimarron, Escort,<br />

Manor<br />

2-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)amino]<br />

carbonyl]amino]sulfonyl]benzoic acid<br />

molinate Ordram S-ethyl hexahydro-1H-azepine-1-carbothioate<br />

monalide Potablan N-(4-chlorophenyl)-2,2-dimethylpentanamide<br />

monolinuron Aresin, Afesin, N'-(4-chlorophenyl)-N-methoxy-N-methylurea<br />

Monamex,<br />

Premalin<br />

monuron Borea, Monurex, N'-(4-chlorophenyl)-N,N-dimethylurea<br />

Telvar<br />

MSMA<br />

Ansar, Bueno, monosodium salt of MAA<br />

Daconate<br />

napropamide Devrinol N,N-diethyl-2-(1-naphthalenyloxy)propanamide<br />

naptalam Alanap 2-[(1-naphthalenylamino)carbonyl]benzoic acid<br />

neburon Granurex, N-butyl-N'-(3,4-dichlorophenyl)-N-methylurea<br />

Propuron,<br />

Neburex, many<br />

nicosulfuron Accent 2-[[[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]a<br />

mino]<br />

sulfonyl]-N,N-dimethyl-3-pyridinecarboxamide<br />

nitralin Planavin 4-(methylsulfonyl)-2,6-dinitro-N,Ndipropylbenzenamine<br />

nitrofen Trizilin 2,4-dichloro-1-(4-nitrophenoxy)benzene<br />

nitrofluorfen<br />

2-chloro-1-(4-nitrophenoxy)-4-<br />

(trifluoromethyl)benzene<br />

norea Herban N,N-dimethyl-N'-(octahydro-4,7-methano-1Hinden-5-yl)urea<br />

3aa,4a,5a,7a,7aa-isomer<br />

norflurazon<br />

Evital, Solicam,<br />

Predict, Zorial<br />

4-chloro-5-(methylamino)-2-(3-(trifluoromethyl)phe<br />

nyl)-3 (2H)-pyridazinone<br />

2,3,4,4,5,5,6,6-octachloro-2-cyclohexen-1-one<br />

OCH<br />

oryzalin Surflan 4-(dipropylamino)-3,5-dinitrobenzenesulfonamide<br />

166


Common Name Trade Name Chemical Name<br />

oxadiargyl TopStar 3-[2,4-dichloro-5-(2-propynyloxy)phenyl]-5-(1,1-<br />

dimethylethyl)-1,3,4-oxadiazol-2(3H)-one<br />

oxadiazon Ronstar 3-[2,4-dichloro-5-(1-methylethoxy)phenyl]-5-(1,1-<br />

dimethylethyl)-1,3,4-oxadiazol-2-(3H)-one<br />

oxaziclomefone<br />

oxyfluorfen<br />

paraquat<br />

PBA<br />

PCP<br />

Homerun,<br />

Samurai,<br />

Thoroughbred<br />

Goal<br />

GoalTender<br />

Boa, Cyclone,<br />

Gramoxone,<br />

Starfire<br />

Dowicide, Penta,<br />

Permatox,<br />

Santophen, many<br />

3-[1-(3,5-dichlorophenyl)-1-methylethyl]-2,3-<br />

dihydro-6-methyl-5-phenyl-4H-1,3-oxazin-4-one<br />

2-chloro-1-(3-ethoxy-4-nitrophenoxy)-4-(trifluorome<br />

thyl) benzene<br />

1,1'-dimethyl-4,4'-bipyridiniumion<br />

chlorinated benzoic acid<br />

pentachlorophenol<br />

pebulate Tillam S-propyl butylethylcarbamothioate<br />

pelargonic acid Scythe nonanoic acid<br />

pendimethalin<br />

Pentagon,<br />

PendiMax,<br />

Pendulum, Prowl,<br />

Prowl H2O, many<br />

N-(1-ethylpropyl)-3,4-dimethyl-2,6-dinitrobenzena<br />

mine<br />

penoxsulam Granite, Grasp 2-(2,2-difluoroethoxy)-N-(5,8-dimethoxy<br />

[1,2,4]triazolo[1,5-c]pyrimidin-2-yl)-6-<br />

(trifluoromethyl)<br />

benzenesulfonamide<br />

perfluidone Destun 1,1,1-trifluoro-N-[2-methyl-4-<br />

(phenylsulfonyl)phenyl] methanesulfonamide<br />

phenisopham Diconal, Verdinal 3-[[(1-methylethoxy)carbonyl]amino]phenyl<br />

ethylphenylcarbamate<br />

phenmedipham Spin-Aid 3-[(methoxycarbonyl)amino]phenyl<br />

(3-methylphenyl)carbamate<br />

picloram Tordon, Grazon 4-amino-3,5,6-trichloro-2-pyridinecarboxylic acid<br />

pinoxaden Axial 8-(2,6-diethyl-4-methylphenyl)-1,2,4,5-tetrahydro-<br />

7-oxo-7H-pyrazolo[1,2-d][1,4,5]oxadiazepin-9-<br />

yl2,2-dimethylpropanoate<br />

piperophos Rilof, Avirosan S-[2-(2-methyl-1-piperidinyl)-2-oxoethyl]O,Odipropyl<br />

phosphorodithioate<br />

PMA<br />

Seedtox,<br />

Mersolite, many<br />

(acetato-O)phenylmercury<br />

167


Common Name Trade Name Chemical Name<br />

primisulfuron Beacon, Rifle 2-[[[[[4,6-bis(difluoromethoxy)-2-pyrimidinyl]amino]<br />

carbonyl]amino]sulfonyl]benzoic acid<br />

procyazine<br />

2-[[4-chloro-6-(cyclopropylamino)-1,3,5-triazine-2-<br />

yl]amino]-2 -methylpropanenitrile<br />

prodiamine<br />

Barricade, Factor,<br />

RegalKade<br />

2,4 dinitro-N3,N3-dipropyl-6-(trifluoromethyl)-1,3-<br />

benzenediamine<br />

profluralin Tolban N-(cyclopropylmethyl)-2,6-dinitro-N-propyl-4-<br />

(trifluoromethyl)benzenamine<br />

proglinazine<br />

N-[4-chloro-6-(1-methylethylamino)-1,3,5-triazine-<br />

2-yl]glycine<br />

prometon Pramitol 6-methoxy-N,N'-bis(1-methylethyl)-1,3,5-triazine-2,<br />

4- diamine<br />

prometryn<br />

Caparol, Cotton<br />

Pro<br />

N,N'-bis(1-methylethyl)-6-(methylthio)-1,3,5-triazin<br />

e-2,4- diamine<br />

pronamide Kerb 3,5-dichloro (N-1,1-dimethyl-2-propynyl)benzamide<br />

propachlor Ramrod 2-chloro-N-(1-methylethyl)-N-phenylacetamide<br />

propanil<br />

Propanil, Stam,<br />

Superwham<br />

N-(3,4-dichlorophenyl)propanamide<br />

propaquizafop<br />

propazine<br />

propham<br />

Falcon, Shogun,<br />

Prilan<br />

Milogard,<br />

Milocep, Milo-<br />

Pro, Gesamil<br />

Beet-Kleen,<br />

Quintex,<br />

Premalox, many<br />

(R)-2-[[(1-methylethylidene)amino]oxy]ethyl 2-[4-<br />

[(6-chloro-2-quinoxalinyl)oxy]phenoxy]propanoate<br />

6-chloro-N,N'-bis(1-methylethyl)-1,3,5-triazine-2,4-<br />

diamine<br />

1-methylethyl phenylcarbamate<br />

prosulfalin<br />

N-[[4-(dipropylamino)-3,5-dinitrophenyl]sulfonyl]-<br />

S,S-dimethylsulfilimine<br />

prosulfuron Peak N-[[(4-methoxy-6-methyl-1,3,5-triazin-2-<br />

yl)amino]carbonyl]-2-(3,3,3-<br />

trifluoropropyl)benzenesulfonamide<br />

prynachlor Basamaize 2-chloro-N-(1-methyl-2-propynyl)-Nphenylacetamide<br />

pyraflufen ET [2-chloro-5-[4-chloro-5-(difluoromethoxy)-1-methyl-<br />

1H-pyrazol-3-yl]-4-fluorophenoxy]acetic acid<br />

pyrazon Pyramin 5-amino-4-chloro-2-phenyl-3(2H)-pyridazinone<br />

pyrasulfatole<br />

(5-hydroxyl-1,3-dimethyl-1H-pyrazol-4-yl)[2-<br />

(methylsulfonyl)-4-<br />

(trifluoromethyl)phenyl]methanone<br />

168


Common Name Trade Name Chemical Name<br />

pyrazolynate Kusakarin 4-(2,4-dichlorobenzoyl)-1,3-dimethylpyrazol-5-ylp-<br />

toluenesulfonate(2,4-dichloropheyl)[1,3-dimethyl-5-<br />

[[4-methylphenyl)sulfonyl]oxy]-1H-pyrazol-4-<br />

yl]methanone<br />

pyribenzoxium Pyanchlor diphenylmethanone O-[2,6-bis[(4,6-dimethoxy-2-<br />

pyrimidinyl)oxy]benzoyl]oxime<br />

pyrichlor Daxtron 2,3,5-trichloro-4-pyridinol<br />

pyridate Lentagran, Tough O-(6-chloro-3-phenyl-4-pyridazinyl) S-octyl<br />

carbonothioate<br />

pyrithiobac Staple 2-chloro-6-[(4,6-dimethoxy-2-pyrimidinyl)thio]benzo<br />

ic acid<br />

quinclorac Drive, Facet 3,7-dichloro-8-quinolinecarboxylic acid<br />

quinmerac Rebell, Fiesta, 7-chloro-3-methyl-8-quinolinecarboxylic aci<br />

Largo, many<br />

quinonamid<br />

2,2-dichloro-N-(3-chloro-1,4-dihydro-1,4-dioxo-2-<br />

naphthalenyl)acetamide<br />

quizalofop Assure II, Targa (±)-2-[4-[(6-chloro-2-quinoxalinyl)oxy]phenoxy]prop<br />

anoic acid<br />

rimsulfuron Matrix, Tranxit N-[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]-3<br />

- (ethylsulfonyl)-2-pyridinesulfonamide<br />

secbumeton Etazine, Sumitol N-ethyl-6-methoxy-N'-(1-methylpropyl)-1,3,5-<br />

triazine-2,4-diamine<br />

sethoxydim Poast 2-[1-(ethoxyimino)butyl]-5-[2-(ethylthio)propyl]-3-<br />

hydroxy-2-cyclohexen-1-one<br />

sesone Crag I 2-(2,4-dichlorophenoxy)ethyl hydrogen sulfate<br />

siduron Tupersan N-(2-methylcyclohexyl)-N'-phenylurea<br />

silvex<br />

AquaVex, Kuron, 2-(2,4,5-trichlorophenoxy)propanoic acid<br />

many<br />

simazine Aquazine, 6-chloro-N,N'-diethyl-1,3,5-triazine-2,4-diamine<br />

Princep; many<br />

simeton Gesadural N,N'-diethyl-6-methoxy-1,3,5-triazine-2,4-diamine<br />

simetryn Gy-bon N,N'-diethyl-6-(methylthio)-1,3,5-triazine-2,4-<br />

diamine<br />

sodium chlorate Defol sodium chlorate<br />

solan<br />

Solan<br />

N-(3-chloro-4-methylphenyl)-2-methylpentanamide<br />

(pentanochlor)<br />

sulcotrione Galleon 2-[2-chloro-4-(methylsulfonyl)benzoyl]-1,3-<br />

cyclohexanedione<br />

169


Common Name Trade Name Chemical Name<br />

sulfentrazone Authority,<br />

Spartan<br />

N-[2,4-dichloro-5-[4-(difluoromethyl)-4,5-dihydro-3-<br />

methyl-5-oxo-1H-1,2,4-triazol-1-yl]<br />

phenyl]methanesulfonamide<br />

sulfometuron Oust 2-[[[[(4,6-dimethyl-2-pyrimidinyl)amino]carbonyl]am<br />

ino] sulfonyl]benzoic acid<br />

sulfosulfuron<br />

swep<br />

2,4,5-T<br />

2,4,5-TB<br />

2,3,6-TBA<br />

TCA<br />

Maverick,<br />

Outrider,<br />

Certainty<br />

Brush Killer,<br />

Super D<br />

<strong>Weed</strong>one, many<br />

Benzac, Trysben,<br />

many<br />

Revenge, Varitox,<br />

many<br />

N-[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]-<br />

2-(ethylsulfonyl)imidazo[1,2-a]pyridine-3-<br />

sulfonamide<br />

methyl(3,4-dichlorophenyl)carbamate<br />

(2,4,5-trichlorophenoxy)acetic acid<br />

4-(2,4,5-trichlorophenoxy)butanoic acid<br />

2,3,6-trichlorobenzoic acid<br />

trichloroacetic acid<br />

tebuthiuron Spike N-[5-(1,1-dimethylethyl)-1,3,4-thiadiazol-2-yl]-N,N'-<br />

dimethylurea<br />

tembotrione Laudis 2-[2-chloro-4-(methylsulfonyl)-3-[(2,2,2-<br />

(trifluoroethoxy)methyl]benzoyl]-1,3-<br />

cyclohexanedione<br />

terbacil Sinbar 5-chloro-3-(1,1-dimethylethyl)-6-methyl-2,4(1H,3H)<br />

- pyrimidinedione<br />

terbuchlor<br />

N-(butoxymethyl)-2-chloro-N-[2-(1,1-<br />

dimethylethyl)-6-methylphenyl]acetamide<br />

terbumeton Caragard N-(1,1-dimethylethyl)-N'-ethyl-6-methoxy-1,3,5-<br />

triazine-2,4-diamine<br />

terbuthylazine<br />

Gardoprim, Click,<br />

Azimut, many<br />

6-chloro-N-(1,1-dimethylethyl)-N'-ethyl-1,3,5-<br />

triazine-2,4-diamine<br />

terbutol Azac, Azak, Azar 2,6-bis(1,1-dimethylethyl)-4-methylphenyl<br />

methylcarbamate<br />

terbutryn<br />

Ternit, Terbutrex,<br />

Sunter, Shortstop,<br />

many<br />

N-(1,1-dimethylethyl)-N'-ethyl-6-(methylthio)-1,3,5-<br />

triazine-2,4-diamine<br />

tetrafluron Tomilon N,N-dimethyl-N'-[3-(1,1,2,2-<br />

tetrafluoroethoxy)phenyl]urea<br />

thiazafluron Dropp N,N'-dimethyl-N-[5-(trifluoromethyl)-1,3,4-thiadiazol<br />

-2-yl] urea<br />

170


Common Name Trade Name Chemical Name<br />

thiazopyr Mandate, Visor methyl2-(difluoromethyl)-5-(4,5-dihydro-2-thiazolyl)<br />

-4-(2-methylpropyl) -6-(trifluoromethyl)-3-<br />

pyridinecarboxylate<br />

thifensulfuron Harmony GT 3-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)amino]<br />

carbonyl]amino]sulfonyl]-2-thiophenecarboxylic<br />

acid<br />

thiobencarb Bolero S-[(4-chlorophenyl)methyl]diethylcarbamothioate<br />

2,2,3-TPA<br />

2,2,3-trichloropropionic acid<br />

tralkoxydim Achieve 2-[1-(ethoxyimino)propyl]-3-hydroxy-5-(2,4,6-<br />

trimethylphenyl)-2-cyclohexen-1-one<br />

triallate<br />

Far-Go, Avadex,<br />

Showdown<br />

S-(2,3,3-trichloro-2-propenyl) bis(1-methylethyl)<br />

carbamothioate<br />

triasulfuron Amber 2-(2-chloroethoxy)-N-[[(4-methoxy-6-methyl-1,3,5-t<br />

riazin-2-yl)amino]carbonyl] benzenesulfonamide<br />

tribenuron Express 2-[[[[(4-methoxy-6-methyl-1,3,5-triazin-2-yl)methyla<br />

mino] carbonyl]amino]sulfonyl]benzoic acid<br />

tricamba<br />

2,3,5-trichloro-6-methoxy benzoic acid<br />

triclopyr<br />

Garlon,<br />

[(3,5,6-trichloro-2-pyridinyl)oxy]acetic acid<br />

Grandstand,<br />

Pathfinder,<br />

Remedy, Turflon,<br />

Renovate<br />

tridiphane Tandem 2-(3,5-dichlorophenyl)-2-(2,2,2-<br />

trichloroethyl)oxirane<br />

trietazine Bronox, Gesafloc,<br />

Pre-empt<br />

6-chloro-N,N,N'-triethyl-1,3,5-triazine-2,4-diamine<br />

trifloxysulfuron<br />

trifluralin<br />

Enfield, Envoke,<br />

Monument<br />

Treflan, Tri-4,<br />

Trilin; many<br />

N-[[(4,6-dimethoxy-2-pyrimidinyl)amino]carbonyl]-<br />

3-(2,2,2-trifluoroethoxy)-2-pyridinesulfonamide<br />

2,6-dinitro-N,N-dipropyl-4-(trifluoromethyl)benzena<br />

mine<br />

triflusulfuron UpBeet 2-[[[[[4-(dimethylamino)-6-(2,2,2-trifluoroethoxy)-1,<br />

3,5- triazin-2-yl]amino]carbonyl]amino]sulfonyl]-3-<br />

methylbenzoic acid<br />

trimeturon<br />

methyl N'-(4-chlorophenyl)-N,Ndimethylcarbamidate<br />

tritac<br />

1-[(2,3,6-trichlorophenyl)methoxy]-2-propanol<br />

topramezone Impact [3-(4,5-dihydo-3-isoxazolyl)-2-methyl-4-<br />

(methylsulfonyl) phenyl](5-hydoxy-1-methyl-1Hpyrazol-4-yl)methanone<br />

vernolate Vernam S-propyl dipropylcarbamothioate<br />

171


Common Name Trade Name Chemical Name<br />

xylachlor<br />

2-chloro-N-(2,3-dimethylphenyl)-N-(1-<br />

methylethyl)acetamide<br />

172


COMMON PRE-PACKAGED HERBICIDES<br />

Common Pre-packaged Herbicides and Common Name of the Component<br />

Chemicals<br />

Trade Name<br />

Accent Gold<br />

Affinity Broadspec<br />

Affinity Tank Mix<br />

Agility SG<br />

Ally Extra<br />

Atrabute+<br />

Authority First<br />

Authority MTZ<br />

Axiom<br />

Backdraft<br />

Basis<br />

Basis Gold<br />

Betamix<br />

Bicep II Magnum<br />

Bicep Lite II Magnum<br />

Bison<br />

Boundary<br />

Brawl II ATZ<br />

Breakfree ATZ<br />

Breakfree ATZ Lite<br />

Bromac<br />

Bronate<br />

Brox-M<br />

Brozine<br />

Brushmaster<br />

Brush-Rhap<br />

Buckle<br />

Bullet<br />

Cadence ATZ<br />

Cadence ATZ Lite<br />

Camix<br />

Campaign<br />

Canopy<br />

Canopy XL<br />

Canopy EX<br />

Celebrity<br />

Celebrity Plus<br />

Charger MAX<br />

Charger MAX Lite<br />

Chaser<br />

Cheyenne<br />

Cimarron Max<br />

Common Name of Individual Herbicides<br />

clopyralid + flumetsulam + nicosulfuron + rimsulfuron<br />

tribenuron + thifensulfuron<br />

tribenuron + thifensulfuron<br />

tribenuron + thifensulfuron + metsulfuron + dicamba<br />

tribenuron + thifensulfuron + metsulfuron<br />

atrazine + butylate<br />

sulfentrazone + cloransulam-methyl<br />

sulfentrazone + metribuzin<br />

flufenacet + metribuzin<br />

glyphosate + imazaquin<br />

rimsulfuron + thifensulfuron<br />

atrazine + nicosulfuron + rimsulfuron<br />

desmedipham + phenmedipham<br />

atrazine + s-metolachlor<br />

atrazine + s-metolachlor<br />

bromoxynil + MCPA<br />

s-metolachlor + metribuzin<br />

s-metolachlor + atrazine<br />

acetochlor + atrazine<br />

acetochlor + atrazine<br />

bromoxynil + MCPA<br />

bromoxynil + MCPA<br />

bromoxynil + MCPA<br />

bromoxynil + atrazine<br />

dicamba + 2,4-D + 2,4-DP<br />

dicamba + 2,4-D<br />

triallate + trifluralin<br />

alachlor + atrazine<br />

acetochlor + atrazine<br />

acetochlor + atrazine<br />

s-metolachlor + mesotrione<br />

glyphosate + 2,4-D<br />

chlorimuron + metribuzin<br />

chlorimuron + sulfentrazone<br />

chlorimuron + tribenuron<br />

dicamba + nicosulfuron<br />

dicamba + nicosulfuron + diflufenzopyr<br />

s-metolachlor + atrazine<br />

s-metolachlor + atrazine<br />

triclopyr + 2,4-D<br />

fenoxaprop + MCPA + thifensulfuron + tribenuron<br />

dicamba + metsulfuron + 2,4-D<br />

173


Trade Name<br />

Cinch ATZ<br />

Clarion<br />

CleanWave<br />

Colt<br />

Confidence Xtra<br />

Confront<br />

Cool Power<br />

Commando<br />

Commando M<br />

CoStarr<br />

Crossbow<br />

Crossroad<br />

Curtail<br />

Curtail M<br />

Cutback<br />

Cutback M<br />

Dakota<br />

Degree Xtra<br />

Dissolve<br />

Distinct<br />

Domain<br />

Double Team<br />

Eclipse<br />

Enlite<br />

Envive<br />

Epic<br />

Equip<br />

Establish ATZ<br />

Establish Lite<br />

Event<br />

Exceed<br />

Expert<br />

Extreme<br />

Fallow Master<br />

Fallow Star<br />

FieldMaster<br />

Finesse<br />

Finesse Grass and Broadleaf<br />

Fire Power<br />

Forefront<br />

Fuego<br />

Frontrow<br />

FulTime<br />

Fusion<br />

Gangster<br />

GlyKamba<br />

Grazon P+D<br />

Guardsman Max<br />

Common Name of Individual Herbicides<br />

atrazine + s-metolachlor<br />

nicosulfuron + rimsulfuron<br />

aminopyralid + fluroxypyr<br />

clopyralid + fluroxypyr<br />

acetochlor + atrazine<br />

clopyralid + triclopyr<br />

dicamba + MCPA + triclopyr<br />

clopyralid + 2,4-D<br />

clopyralid + MCPA<br />

glyphosate + dicamba<br />

triclopyr + 2,4-D<br />

triclopyr + 2,4-D<br />

clopyralid + 2,4-D<br />

clopyralid + MCPA<br />

clopyralid + 2,4-D<br />

clopyralid + MCPA<br />

fenoxaprop + MCPA<br />

acetochlor + atrazine<br />

mecoprop + 2,4-D + 2,4-DP<br />

dicamba + diflufenzopyr<br />

flufenacet + metribuzin<br />

acetochlor + atrazine<br />

clopyralid + MCPA + 2,4-DP<br />

chlorimuron + thifensulfuron + flumioxazin<br />

chlorimuron + thifensulfuron + flumioxazin<br />

flufenacet + isoxaflutole<br />

mesosulfuron(AEF-130060) + iodosulfuron<br />

dimethenamid-P + atrazine<br />

dimethenamid-P + atrazine<br />

imazapyr + imazethapyr<br />

primisulfuron + prosulfuron<br />

s-metolachlor + atrazine + glyphosate<br />

glyphosate + imazethapyr<br />

glyphosate + dicamba<br />

glyphosate + dicamba<br />

acetochlor + atrazine + glyphosate<br />

chlorsulfuron + metsulfuron<br />

chlorsulfuron + flucarbazone-sodium<br />

glyphosate + oxyfluorfen<br />

aminopyralid + 2,4-D<br />

dicamba + triasulfuron<br />

cloransulam-methyl + flumetsulam<br />

acetochlor + atrazine<br />

fenoxaprop + fluazifop<br />

flumioxazin + cloransulam-methyl<br />

glyphosate + dicamba<br />

picloram + 2,4-D<br />

atrazine + dimethenamid<br />

174


Trade Name<br />

Gunslinger<br />

Halex GT<br />

Harmony Extra<br />

Harness Xtra<br />

HiredHand P+D<br />

Horizon 2000<br />

Hornet<br />

Horsepower<br />

Huskie<br />

Journey<br />

Kambamaster<br />

Kansel Plus<br />

Keystone, Keystone LA<br />

Krovar<br />

Laddok S-12<br />

Landmark XP<br />

Landmaster<br />

Lariat<br />

Layby Pro<br />

Lexar<br />

Liberty ATZ<br />

Lightning<br />

Lumax<br />

Marksman<br />

Medal II AT<br />

Milestone VM Plus<br />

Millennium Ultra<br />

Momentum<br />

NorthStar<br />

Oasis<br />

OneStep<br />

OH2 (Ornamental Herbicide)<br />

Olympus Flex<br />

Oustar<br />

Oust Extra<br />

Outlaw<br />

Overdrive<br />

Parallel Plus<br />

PastureGard<br />

Pathway<br />

PD 2<br />

Power Zone<br />

PrePair<br />

Prefix<br />

Preview<br />

Priority<br />

Prompt<br />

Progress<br />

Common Name of Individual Herbicides<br />

picloram + 2,4-D<br />

s-metolachlor + glyphosate + mesotrione<br />

thifensulfuron + tribenuron<br />

acetochlor + atrazine<br />

picloram + 2,4-D<br />

fenoxaprop + fluazifop<br />

clopyralid + flumetsulam<br />

dicamba + triclopyr + 2,4-D<br />

pyrasulfatole + bromoxynil<br />

glyphosate + imazapic<br />

dicamba + 2,4-D<br />

oxadiazon + pendimethalin<br />

acetochlor + atrazine<br />

bromacil + diuron<br />

atrazine + bentazon<br />

chlorsulfuron + sulfometuron<br />

glyphosate + 2,4-D<br />

alachlor + atrazine<br />

linuron + diuron<br />

s-metolachlor + atrazine + mesotrione<br />

atrazine + glufosinate<br />

imazapyr + imazethapyr<br />

atrazine + mesotrione + s-metolachlor<br />

atrazine + dicamba<br />

s-metolachlor + atrazine<br />

aminopyralid + triclopyr<br />

clopyralid + dicamba + 2,4-D<br />

clopyralid + triclopyr + 2,4-D<br />

dicamba + primisulfuron<br />

imazapic + 2,4-D<br />

imazapyr + glyphosate<br />

oxyfluorfen + pendimethalin<br />

propoxycarbazone-sodium + mesosulfuron-methyl<br />

hexazinone + sulfometuron<br />

metsulfuron + sulfometuron<br />

dicamba + 2,4-D<br />

dicamba + diflufenzopyr<br />

metolachlor + atrazine<br />

triclopyr + fluroxypyr<br />

picloram + 2,4-D<br />

picloram + 2,4-D + dicamba<br />

carfentrazone + dicamba+ mecoprop + MCPA<br />

napropamide + oxadiazon<br />

s-metolachlor + fomesafen.<br />

chlorimuron + metribuzin<br />

carfentrazone-ethyl + halosulfuron-methyl<br />

atrazine + bentazon<br />

phenmedipham + desmedipham + ethofumesate<br />

175


Trade Name<br />

Pursuit Plus<br />

Q4<br />

QuikPro<br />

Radius<br />

Rage D-Tech<br />

Range Star<br />

Rave<br />

Ready Master ATZ<br />

Recoil<br />

Redeem R&P<br />

Refute<br />

Regal O-O<br />

RegalStar<br />

Resolve SG<br />

Rhino<br />

Rifle D<br />

Rifle Plus<br />

Rimfire<br />

Rout<br />

Sahara<br />

Salute<br />

Sequence<br />

Shotgun<br />

Showcase<br />

Simazat<br />

Snapshot<br />

Sonic<br />

Speed Zone<br />

Spirit<br />

Squadron<br />

Stampede<br />

Starane NXT<br />

Starane + Saber<br />

Starane + Salvo<br />

Starane + Sword<br />

Status<br />

Steadfast<br />

Steadfast ATZ<br />

Steel<br />

Stellar<br />

Sterling Plus<br />

Stout<br />

Strategy<br />

Strike 3<br />

Strike 3 Ultra<br />

Strike 3 Ultra 2<br />

Stronghold<br />

SuperBrush Killer<br />

Common Name of Individual Herbicides<br />

imazethapyr + pendimethalin<br />

quinclorac + sulfentrazone + 2,4-D + dicamba<br />

diquat + glyphosate<br />

flufenacet + isoxaflutole<br />

carfentrazone + 2,4-D<br />

dicamba + 2,4-D<br />

triasulfuron + dicamba<br />

atrazine + glyphosate<br />

glyphosate + 2,4-D<br />

clopyralid + triclopyr<br />

clopyralid + triclopyr<br />

oxadiazon + oxyfluorfen<br />

oxadiazon + prodiamine<br />

dicamba + imazethapyr<br />

atrazine + butylate<br />

2,4-D + dicamba<br />

atrazine + dicamba<br />

propoxycarbazone-sodium + mesosulfuron-methyl<br />

oryzalin + oxyfluorfen<br />

diuron + imazapyr<br />

metribuzin + trifluralin<br />

s-metolachlor + glyphosate<br />

atrazine + 2,4-D<br />

trifluralin + isoxaben + oxyfluorfen<br />

atrazine + simazine<br />

isoxaben + trifluralin<br />

cloransulam + sulfentrazone<br />

carfentrazone + dicamba + mecoprop + 2,4-D<br />

primisulfuron + prosulfuron<br />

imazaquin + pendimethalin<br />

MCPA + propanil<br />

fluroxypyr + bromoxynil<br />

fluroxypyr + 2,4-D<br />

fluroxypyr + 2,4-D<br />

fluroxypyr + MCPA<br />

dicamba + diflufenzopyr (plus isoxadifen-ethyl safener)<br />

nicosulfuron + rimsulfuron<br />

atrazine + nicosulfuron + rimsulfuron<br />

imazaquin + imazethapyr + pendimethalin<br />

flumiclorac + lactofen<br />

atrazine + dicamba<br />

nicosulfuron + thifensulfuron<br />

clomazone + ethalfluralin<br />

2,4-D + dicamba + mecoprop-p<br />

2,4-D + clopyralid + dichlorprop-p<br />

2,4-D + fluroxypyr + dichlorprop-p<br />

imazapyr + imazethapyr + mefluidide<br />

2,4-D, dichlorprop + dicamba<br />

176


Trade Name<br />

Suprend<br />

SureStart<br />

Surge<br />

Surmount<br />

Synchrony STS<br />

STS Broadleaf<br />

Tailspin<br />

Team<br />

Telone C17, Telone C35<br />

Thunder Master<br />

Tiller<br />

Tordon 101M<br />

Tordon RTU<br />

Total<br />

Throttle XP<br />

Triamine<br />

Triangle<br />

Tri-Ester<br />

Trimec 992<br />

Trimec Bentgrass Formula<br />

Trimec Classic<br />

Trimec Plus<br />

Trimec Super<br />

Tri-Scept<br />

Trupower<br />

Typhoon<br />

Valor XLT<br />

Velpar Alfamax<br />

Velpar K-4<br />

Vengeance<br />

<strong>Vol</strong>ley ATZ<br />

<strong>Vol</strong>ley ATZ Lite<br />

<strong>Weed</strong> Blast<br />

<strong>Weed</strong>master<br />

Westar<br />

Widematch<br />

Wildcard Xtra<br />

Wil-Power<br />

XL 2G<br />

Yukon<br />

Common Name of Individual Herbicides<br />

prometryn + trifloxysulfuron<br />

acetochlor + flumetsulam + clopyralid<br />

2,4-D, mecoprop-p, dicamba, sulfentrazone<br />

picloram + fluroxypyr<br />

chlorimuron + thifensulfuron<br />

chlorimuron + thifensulfuron<br />

fluroxypyr + triclopyr<br />

benefin + trifluralin<br />

chloropicrin + dichloropropene<br />

glyphosate + imazethapyr<br />

fenoxaprop + MCPA + 2,4-D<br />

picloram + 2,4-D<br />

picloram + 2,4-D<br />

bromacil + diuron + sodium chlorate + sodium metaborate<br />

chlorsulfuron + sulfometuron + sulfentrazone<br />

mecoprop + 2,4-D + 2,4-DP<br />

metolachlor + atrazine<br />

mecoprop + 2,4-D + 2,4-DP<br />

dicamba + mecoprop + 2,4-D<br />

dicamba + mecoprop + 2,4-D<br />

dicamba + mecoprop + 2,4-D<br />

dicamba + mecoprop + 2,4-D + MSMA<br />

dicamba + dichlorprop + 2,4-D<br />

imazaquin + trifluralin<br />

clopyralid + dicamba + MCPA<br />

fluazifop + fomesafen<br />

flumioxazin + chlorimuron-ethyl<br />

hexazione + diuron<br />

hexazione + diuron<br />

dicamba + MCPA<br />

acetochlor + atrazine<br />

acetochlor + atrazine<br />

bromacil + diuron<br />

dicamba + 2,4-D<br />

hexazinone + sulfometuron<br />

clopyralid + fluroxypyr<br />

bromoxynil + MCPA<br />

MCPA + triclopyr + dichlorprop-p<br />

benefin + oryzalin<br />

dicamba + halosulfuron<br />

177


EXPERIMENTAL HERBICIDES<br />

Experimental Number<br />

Common Name (Proposed),<br />

Trade Name, Company Name<br />

AC-900001.............................................................. picolinafen/Pico, BASF<br />

BAS 620.............................. tepraloxydim/Aramo, Equinox, Honest, BASF<br />

BAY MKH 6561.................... propoxycarbazone/Attribute, Olympus, Bayer<br />

BK-800 ............................................................................................Uniroyal<br />

CGA-277476 ................................................oxasulfuron/Dynam, Syngenta<br />

F6875……………………………………….sulfentrazone + prodiamine, FMC<br />

KIH-485.............................................................................................Kumiai<br />

V-3153 .............................................................................flufenapyr, Valent<br />

F4113..................................................... carfentrazone + glyphosate, FMC<br />

PLANT GROWTH REGULATORS<br />

Common Name<br />

Trade Name<br />

AVG .................................................................................................. Retain<br />

6-benzyl adenine............................................................................. BAP-10<br />

chlorflurecol.................................................................................... Maintain<br />

chlormequat chloride.......................................................................Cycocel<br />

clofencet..................................................................................... Detasselor<br />

copper ethylenediamine................................................................... Inferno<br />

diphenylamine..............................................................................................<br />

diminozide......................................................................................... B-nine<br />

ethephon .............................................................................................Florel<br />

forchlorfenuron.............................................................................................<br />

GA 4 7/G BA ................................................................. Promalin, Rite Size<br />

GABA ...............................................................................................Auxigro<br />

MBTA ............................................................................................... Ecolyst<br />

mepiquat chloride.............................................Mepex, Mepex Gin Out, Pix<br />

paclobutrazol.......................................................... Bonzi, Clipper, Trimmet<br />

prohexadione .................................................................................. Apogee<br />

sodium nitrophenolate........................................................................Atonik<br />

trinexapac ...........................................................................Palisade, Primo<br />

uniconazole………… ......................................................... Prunit, Sumagic<br />

178


COMMON AND CHEMICAL NAMES OF HERBICIDE MODIFIERS<br />

Common Name<br />

Chemical Name<br />

benoxacor ............................. (RS)-4-dichloroacetyl-3,4-dihydro-3-methyl-2H-1,4-benzoxazine<br />

cloquintocet........................... (5-chloroquinolin-8-yloxy)acetic acid<br />

cyometrinil............................. (Z)-α-[(cyanomethoxy)imino]benzeneacetonitrile<br />

dichlormid ............................. 2,2-dichloro-N,N-di-2-propenylacetamide<br />

dicyclonon ............................. 1-(dichloroacetyl)hexahydro-3,3,8a-trimethylpyrrolo[1,2-<br />

α]pyrimidin-6(2H)-one<br />

dietholate ............................. O,O-diethyl O-phenyl phosphorothioate<br />

fenchlorazole......................... 1-(2,4-dichlorophenyl)-5-(trichloromethyl)-1H-1,2,4-triazole-3-<br />

carboxylic acid<br />

fenclorim ............................... 4,6-dichloro-2-phenylpyrimidine<br />

flurazole ............................... phenylmethyl-chloro-4-(trifluoromethyl)-5-thiazolecarboxylate<br />

fluxofenim.............................. 1-(4-chlorophenyl)-2,2,2-trifluoroethanone O-(1,3-dioxolan-2-<br />

ylmethyl)oxime<br />

furilazole................................ 3-(dichloroacetyl)-5-(2-furanyl)-2,2-dimethyloxazolidine<br />

isoxadifen.............................. 4,5-dihydro-5,5-diphenyl-3-isoxazolecarboxylic acid<br />

mefenpyr ............................... 1-(2,4-dichlorophenyl)-4,5-dihydro-5-methyl-1H-pyrazole-3,5-<br />

dicarboxylic acid<br />

mephenate ........................... 4-chlorophenyl methylcarbamate<br />

naphthalic anhydride ............ 1H,3H-naphtho[1,8-cd]-pyran-1,3-dione<br />

oxabetrinil.............................. α-[(1,3-dioxolan-2-yl)methoxyimino]benzeneacetonitrile<br />

Disclaimer<br />

Names for chemicals in these lists are correct to the best of the Editor’s ability and current information<br />

available at the time of printing. This information is provided as a courtesy to our members and readers<br />

of the Proceedings. Compounds may be added or removed from the market at any time. All persons<br />

using this information for official or other purposes should always verify the validity of the product<br />

information contained in these lists.<br />

179


AUTHOR’S INDEX<br />

A<br />

Ahrens, J.F., 81, 82<br />

Altland, J.E., 47<br />

Arsenovic, M., 95<br />

Askew, S.D., 1, 5, 14, 18, 28, 29, 53, 85, 104<br />

Atwood, R.P.M., 26<br />

Averill, K.M., 6<br />

B<br />

Barney, J., 66<br />

Barolli, S., 48<br />

Baron, J.J., 84, 95<br />

Bates, R.T., 8<br />

Batts, R.B., 69, 98<br />

Beam, J.B., 42, 69<br />

Bellinder, R.R., 23, 33, 71<br />

Benedict, C.A., 71<br />

Bhowmik, P.C., 31, 65<br />

Black, B.D., 44<br />

Bonanno, A.R., 67<br />

Borger, J.A., 88, 89, 103<br />

Brainard, D.C., 23<br />

Bravo, M.A., 2, 63, 64<br />

Broady, P., 64<br />

C<br />

Chandran, R.S., 20<br />

Clarke, B.B., 101<br />

Coffman, C.B., 16<br />

Cox, D., 87<br />

Curran, W.S., 8, 36, 38, 40, 62<br />

D<br />

DaCosta, M., 31<br />

D'Appollonio, J., 12<br />

DeBarros, N.B., 39<br />

Demachak, K., 73<br />

Dernoeden, P.H., 54, 57<br />

Derr, J.F., 80<br />

Diesing, J., 2<br />

DiTomaso, J., 66<br />

DiTommaso, A., 6, 21, 37<br />

Driver, J., 87<br />

Duiker, S., 36<br />

E<br />

Egan, J.F., 19<br />

Evans, G.J., 33<br />

F<br />

Fidanza, M.A., 102<br />

Fu, J., 54, 57<br />

G<br />

Gallagher, R.S., 8<br />

Gallandt, E.R., 62<br />

Gardner, A.P., 24, 25<br />

Ghantous, K.M., 75<br />

Goatley, J.M., 14<br />

Goddard, M.J., 5, 28, 85<br />

Grieneisen, R., 2<br />

Guiser, S.D., 73<br />

H<br />

Hahn, R.R., 23, 79<br />

Hart, S.E., 11, 15, 30, 55, 86, 92, 93<br />

Hepperly, P.R., 17, 38<br />

Hipkins, P.L., 25<br />

Houseworth, L.D., 28<br />

I<br />

Inguagiato, J.C., 101<br />

Irwin, R.E., 19<br />

Isaacs, M.A., 34<br />

J<br />

James, J.R., 5<br />

Jelovic, J., 58<br />

Jemison, J.M., 9, 41<br />

Jester, J.L., 18, 29, 53<br />

Johnson, D.H., 72<br />

Johnson, Q.R., 3, 34, 45, 72<br />

Judge, C.A., 10, 26, 49<br />

Jung, A., 58<br />

K<br />

Kalmowitz, K.M., 49<br />

Kaminski, J.E., 32, 90, 91<br />

Keese, R.J., 5, 20, 87<br />

Ketterings, Q.M., 21<br />

Kirby, M., 9<br />

Krings, A., 27<br />

Kumar, V., 23<br />

Kunkel, D.L., 95<br />

Kyde, K.L., 22<br />

L<br />

Lassiter, B.R., 4<br />

Lengkeek, V., 96<br />

Lingenfelter, D.D., 70, 72<br />

Lins, R.D., 44<br />

Little, D.A., 10, 83<br />

Lurvey, E.L., 46, 94<br />

180


Lycan, D., 96<br />

M<br />

Magidow, L.C., 21<br />

Majek, B.A., 97<br />

Mansue, C., 55, 86, 92<br />

Marose, B.H., 22<br />

Marshall, M.W., 7<br />

Matthews, J., 24<br />

McCullough, P.E., 11, 15, 30, 55, 92, 93<br />

McDonald, S.J., 51, 52<br />

Menbere, H., 77, 78<br />

Mervosh, T.L., 81, 82<br />

Mick, R., 36<br />

Milbrath, L.R., 6, 21<br />

Miller, B.R., 44<br />

Mirsky, S.B., 62<br />

Mitchell, B., 67<br />

Mitchem, W.E., 69<br />

Mittlesteadt, T.L., 14, 28, 29<br />

Mohler, C.L., 6, 37<br />

Mortensen, D.A., 17, 35, 38, 62<br />

Moseley, C.M., 43<br />

Murphy, J.A., 101<br />

N<br />

Naedel, M.B., 88, 89, 103<br />

Neal, J.C., 10, 26, 27, 50, 80, 83<br />

Nord, A.N., 35<br />

P<br />

Palmer, C.L., 84<br />

Petty, A.K., 98<br />

Polach, M., 2<br />

Post, A.R., 10, 27<br />

Prostak, R.G., 67<br />

Putman, A.I., 32<br />

R<br />

Radhakrishnan, J., 16<br />

Richardson, R.J., 4, 24, 25<br />

Ritter, R.L., 77, 78<br />

Ryan, M.R., 17, 38<br />

Sturgill, M.C., 4<br />

Sullenberger, M., 14<br />

T<br />

Teasdale, J.R., 16, 38<br />

Titus, L., 41<br />

True, S.L., 25<br />

V<br />

Vail, G.D., 43, 96<br />

VanGessel, M.J., 3, 34, 45, 70, 72, 76<br />

Vea, E., 84<br />

W<br />

Walker, L.C., 26<br />

Wallace, R.W., 98<br />

Watschke, T.L., 99<br />

West, A.M., 24<br />

Whitehouse, S.E., 37<br />

Wilkerson, G.G., 4<br />

Willis, J.B., 1, 18, 85<br />

Wilson, D.O., 17<br />

Wilson, H.P., 34<br />

Wright, J., 34<br />

X<br />

Xiang, Q., 27<br />

Y<br />

Yarborough, D.E., 12<br />

York, A.C., 42<br />

Youssef, E., 58<br />

Z<br />

Zandstra, B.H., 7<br />

Zawierucha, J., 49<br />

Zontek, S.J., 105<br />

S<br />

Salzman, F.P., 95<br />

Sandler, H.A., 75<br />

Sarkar, D., 31, 65<br />

Scott, B.A., 3, 34, 45, 72, 76<br />

Seidel, R., 38<br />

Sexton, P., 41<br />

Shepard, D.P., 100<br />

Shumway, D.L., 62<br />

Sosinski, B.R., 27<br />

Stachowski, P.J., 79<br />

Stalter, R., 58<br />

181


MAIN SUBJECT INDEX (Herbicides, <strong>Weed</strong>s, Crops, Non-crops, and Subjects)<br />

A<br />

Abies fraseri, 81<br />

Abutilon theophrasti, 37, 62, 70, 72<br />

Acer rubrum, 10<br />

acetic acid, 33<br />

acifluorfen, 98<br />

Agrostis capillaris, 32<br />

Agrostis stolonifera, 15, 28, 30, 32, 103<br />

Alliaceae, 58<br />

Alliaria petiolata, 60<br />

ALS-inhibiting, 44<br />

ALS-inhibiting herbicides, 15<br />

ALS-resistance, 76<br />

Amaranthus hybridus, 72<br />

Amaranthus palmeri, 98<br />

Amaranthus spp, 3, 70, 76<br />

Ambrosia artemisiifolia, 70, 72, 76, 81<br />

American burnweed, 50<br />

Amicarbazone, 28, 53<br />

aminopyralid, 2, 24, 53, 63, 64<br />

annual bedding plants, 49<br />

annual bluegrass, 11, 30, 32, 49, 51, 88, 90, 91, 92,<br />

100, 101, 103, 105<br />

annual morningglory, 70<br />

antagonize, 93<br />

antichromatic, 85<br />

aquatic, 4<br />

Arundo donax, 66<br />

Asteraceae, 58<br />

atrazine, 40, 44, 72, 78, 79<br />

Avena fatua, 76<br />

azalea, 7<br />

B<br />

barnyardgrass, 23<br />

BAS 656, 84<br />

BAS 656h, 81, 82<br />

BAS 659 G, 84<br />

Benefin, 18<br />

bentazon, 53, 69, 70, 98<br />

bentgrass, 87<br />

Berberis vulgaris, 60<br />

bermudagrass, 14, 29, 104<br />

biofuels, 39, 66<br />

bispyribac-sodium, 11, 15, 30, 32, 51, 103<br />

bittercress, 50<br />

black cottonwood, 47<br />

black swallow-wort, 21<br />

blue grama grass, 53<br />

Bouteloua gracilis, 53<br />

boxwood, 7<br />

Brachypterolus pulicarius, 19<br />

Brassica juncea, 62<br />

Brassica napus, 62<br />

Brassica oleracea, 16<br />

brittle naiad, 4<br />

broadleaf plantain, 1<br />

broccoli, 16<br />

brown patch, 32<br />

brussel sprouts, 33<br />

buckhorn plantain, 86<br />

buckwheat, 23, 62<br />

bull paspalum, 52<br />

burn-down, 36<br />

burning bush, 7<br />

Bushkiller, 24<br />

butternut squash, 34<br />

Buxus, 83<br />

C<br />

Campsis radicans, 24<br />

carbohydrate partitioning, 31<br />

cardamine, 27<br />

Cardamine flexuosa, 27<br />

Cardamine hirsuta, 26, 27, 50, 83<br />

Cardamine oligosperma, 27<br />

Cardamine pensylvanica, 27<br />

Cardamine scutata, 27<br />

Carex, 59<br />

carfentrazone, 28, 52, 53, 86, 91<br />

carpetweed, 69<br />

cauliflower, 16<br />

Cayratia japonica, 24<br />

Celastrus orbiculatus, 60<br />

Chamaesyce maculata, 26, 50, 83<br />

Chamaesyce nutans, 83<br />

Chenopodium album, 3, 37, 41, 62, 70, 72, 76<br />

chickweed, 1, 49<br />

chlorimuron, 45, 69, 95<br />

chloroacetamide, 49<br />

chlorosis, 7, 11, 15, 16, 28, 54, 55, 63, 81, 82, 92, 98<br />

chlorsulfuron, 42, 53, 77<br />

cinquefoil, 75<br />

clethodim, 95<br />

climate change, 39<br />

clomazone, 69, 70<br />

clopyralid, 63, 64, 81, 93<br />

cloransulam, 45, 69, 70<br />

Coloneaster horizontallis, 83<br />

colonial bentgrass, 32<br />

Commelinaceae, 58<br />

182


common chickweed, 23<br />

common groundsel, 49, 50<br />

common lambsquarters, 3, 37, 40, 41, 62, 70, 72, 76<br />

common purslane, 3, 23<br />

common ragweed, 40, 70, 72, 76, 81<br />

common reed, 25<br />

common sunflower, 98<br />

Convolvulaceae, 65<br />

Conyza canadensis, 76, 81<br />

coral bells, 7<br />

corn, 8, 38, 43, 44, 78, 79<br />

corn chamomile, 23<br />

Coronaria varia, 60<br />

cover crop, 23, 62<br />

crabgrass, 18, 49, 50, 93<br />

cranberry, 75<br />

creeping bentgrass, 15, 28, 30, 32, 103<br />

creeping red fescue, 88<br />

crimper, 36<br />

crop oil concentrate, 30, 79<br />

crop rotation, 9, 16<br />

Cucurbita moschata, 34<br />

cultivation, 9, 16, 17, 33, 34, 41, 62, 69, 97<br />

cultivator, 8<br />

cultural practices, 16<br />

Cuscuta spp, 65<br />

Cuscutaceae, 65<br />

cyclanilide, 48<br />

Cynanchum rossicum, 6<br />

Cynodon dactylon, 14<br />

Cyperus dentatus, 75<br />

Cyperus esculentus, 3, 55, 57<br />

Cyperus iria, 50<br />

D<br />

2,4-D, 24, 41, 45, 53, 78, 86, 88, 93<br />

dandelion, 1, 5, 86<br />

daylily, 7<br />

dazomet, 3<br />

desmedipham, 95<br />

dewberry, 75<br />

dicamba, 45, 53, 72, 78, 86, 93, 95<br />

dichlobenil, 95<br />

diclofop, 42<br />

diclofop-resistant ryegrass, 42<br />

diflufenzopyr, 72<br />

Digitaria ischaemum, 1, 5, 18, 20, 28, 52, 54, 89<br />

Digitaria sanguinalis, 3, 26, 50, 70, 72, 79, 81, 83<br />

dikegulac-sodium, 48<br />

dimethenamid, 7, 26, 49, 50, 80, 81, 82, 84, 95<br />

dithiopyr, 5, 18, 85<br />

diuron, 95<br />

dodder, 65<br />

dollar spot, 32<br />

doublefile viburnum, 82<br />

Douglas fir, 47<br />

doveweed, 26, 49, 50, 80<br />

E<br />

eclipta, 26, 49, 50<br />

Eclipta prostrata, 26, 50, 83<br />

Egeria, 4<br />

Egeria densa, 4<br />

Elaeagnaceae, 58<br />

Elaeagnus angustifolia, 60<br />

Eleusine indica, 50<br />

emerald green arborvitae, 82<br />

Eragrostis curvula, 59<br />

Erechtites hieraciifolia, 50<br />

establishment, 14, 29<br />

establishment period, 20<br />

ethalfluralin, 69<br />

ethephon, 48, 101, 104<br />

ethofumesate, 103<br />

etiolated tiller, 102<br />

Euonymus alatus, 7<br />

Eupatorium capillifolium, 83<br />

Eurasian watermilfoil, 4<br />

Euthamia tenuifolia, 75<br />

extension, 76<br />

F<br />

F6875, 84<br />

Fagopyrum sagittatum, 62<br />

fall burndown, 45<br />

false green kyllinga, 90, 91<br />

fecundity, 37<br />

feedstock crops, 66<br />

fenoxaprop, 52, 53, 54, 93<br />

Festuca arundinacea, 28, 54, 57<br />

Festuca ruba, 88<br />

fine fescue, 11, 28, 87<br />

flame weeding, 17<br />

flazasulfuron, 53<br />

fluazifop, 52, 53<br />

flucarbazone, 28, 53, 77<br />

flumetsulam, 40<br />

flumioxazin, 45, 69, 73, 80, 82, 83, 95, 97<br />

fluroxypyr, 2, 86, 93, 95<br />

flurprimidol, 51, 103, 104<br />

fomesafen, 69, 70, 71, 98<br />

forage, 9<br />

foramsulfuron, 53, 95<br />

foxtail species, 62, 76<br />

fraser fir, 81<br />

fungal pathogens, 102<br />

G<br />

galinsoga, 49<br />

germination, 6<br />

giant foxtail, 37, 40, 70, 72, 79<br />

giant hogweed, 2, 63<br />

giant reed, 66<br />

glufosinate, 72, 83, 95<br />

Glycine max, 8, 38<br />

glyphosate, 6, 10, 14, 22, 24, 25, 36, 40, 43, 44, 45,<br />

63, 76, 81, 83, 88, 95<br />

glyphosate resistant, 44<br />

glyphosate tolerant, 43, 44<br />

goosegrass, 50<br />

183


growth regulator, 31<br />

Gymnosperms, 59<br />

H<br />

habitat management, 39<br />

hairy bittercress, 26, 49<br />

hairy galinsoga, 23<br />

halosulfuron, 34, 40, 53, 55, 69, 70, 91<br />

hand weeding, 16, 17, 33<br />

Helianthus annuus, 98<br />

Hemerocallis, 7<br />

henbit, 1<br />

Heracleum mantegazzianum, 2, 63<br />

herbaceous perennials, 49<br />

herbicide-resistant biotypes, 76<br />

herbivores, 19<br />

Heuchera micrantha, 7<br />

Hexazinone, 12<br />

hilling, 41, 97<br />

hoeing, 34, 69<br />

holly, 47<br />

horseweed, 76, 81<br />

hosta, 7<br />

Hosta fortunei, 7<br />

HPPD inhibitors, 1, 78, 79, 85, 87<br />

hydrangea, 47<br />

Hydrangea macrophylla, 47<br />

hydrilla, 4<br />

Hydrilla verticillata, 4<br />

I<br />

Ilex cornuta, 83<br />

Ilex vomitoria, 83<br />

Ilex xmeserveae, 47<br />

imazamox, 70<br />

imazapic, 53<br />

imazapyr, 10, 25, 63, 64<br />

Imazasulfuron, 81<br />

imazethapyr, 70<br />

invasive vine, 6, 21<br />

invasive plant, 19, 35, 64, 67<br />

invasive potential, 66<br />

Ipomoea batatas, 97<br />

Ipomoea spp, 69, 70<br />

IR-4, 46, 82, 84, 94, 95<br />

isoxaben, 80, 83<br />

isoxadifen-ethyl, 72<br />

isoxaflutole, 40<br />

Italian ryegrass, 42, 77<br />

J<br />

Japanese stiltgrass, 22, 35<br />

juniper, 82<br />

Juniperus, 83<br />

Juniperus squamata, 82<br />

K<br />

Kentucky bluegrass, 1, 5, 14, 20, 28, 87, 88, 90, 91,<br />

92, 99<br />

KIH-485, 70, 72, 77, 79<br />

kochia, 76<br />

Kochia scoparia, 76<br />

kudzu, 64<br />

Kyllinga gracillima, 90, 91<br />

L<br />

lactofen, 95<br />

Lagerstroemia, 83<br />

Lamium amplexicaule, 1<br />

landscape, 67, 84<br />

Lantana, 83<br />

large crabgrass, 3, 26, 70, 72, 79, 81<br />

Leucanthemum x superbum, 7<br />

Linaria vulgaris, 19<br />

linuron, 95<br />

Liquidambar styraciflua, 10<br />

Liriodendron tulipifera, 10<br />

Lirope muscari, 83<br />

little bluestem grass, 53<br />

liverwort, 49<br />

Lolium multiflorum, 42, 77<br />

Lolium perenne, 1, 14, 30, 55, 88, 89, 90, 91<br />

Lolium spp, 76<br />

Loropetalum chinensis, 83<br />

Lycopersicon lycopersicum, 97<br />

Lyngbya species, 4<br />

Lysmachia terrestris, 75<br />

M<br />

Maine wild blueberry, 12<br />

maleic hydrazide, 99<br />

MCPP, 53, 86<br />

mefluidide, 101, 104<br />

mesosulfuron, 42, 77<br />

mesosulfuron-resistant ryegrass, 42<br />

mesotrione, 1, 5, 7, 12, 20, 40, 44, 52, 53, 54, 57, 72,<br />

75, 78, 79, 81, 82, 84, 85, 87, 89, 90, 91, 92, 93,<br />

96<br />

methylated seed oil, 30, 54, 75, 79<br />

metolachlor, 69<br />

metribuzin, 45<br />

metsulfuron, 42, 53, 64<br />

Microstegium vimineum, 22, 35<br />

minor crops, 46, 94, 96<br />

miscanthus, 66<br />

Miscanthus x giganteus, 66<br />

Molluginaceae, 58<br />

Mollugo verticillata, 69<br />

morningglory species, 69<br />

mouseear chickweed, 86<br />

mowing, 6<br />

MSMA, 52<br />

mulching, 17<br />

Murdannia nudiflora, 26, 50, 80, 83<br />

184


mustard, 62<br />

Myriophyllum spicatum, 4<br />

N<br />

Najas minor, 4<br />

narrowleaved goldenrod, 75<br />

necrosis, 73, 82, 87, 98<br />

nicosulfuron, 53, 72, 78, 79<br />

nightshade, 97<br />

nimblewill, 87<br />

nitrogen availability, 37<br />

nonionic surfactant, 15, 25, 30, 34, 41, 44, 48, 52, 54,<br />

55, 69, 75, 85, 90, 91<br />

non-native taxa, 59<br />

no-till, 45<br />

noxious weed, 2, 64, 65<br />

nurseries, 27, 47, 67, 80<br />

nutsedge, 75, 87<br />

O<br />

Oplismenus hirtellus, 22<br />

organic weed management, 9, 17, 38<br />

ornamentals, 7, 46, 67, 82, 83, 84<br />

oryzalin, 80<br />

oxadiazon, 18, 80, 83<br />

Oxalis stricta, 20<br />

oxyfluorfen, 80, 81, 95<br />

P<br />

paclobutrazol, 48, 51, 103, 104<br />

pale swallow-wort, 6, 21<br />

Palmer amaranth, 98<br />

Panicum virgatum, 66<br />

paraquat, 45<br />

parasitic plant, 65<br />

Parthenocissus quinquefolia, 24<br />

Paspalum setaceum, 52<br />

peas, 71<br />

pendimethalin, 18, 26, 49, 50, 69, 70, 79, 80, 81, 82,<br />

84, 95<br />

penoxsulam, 25, 88<br />

pepper, 33<br />

perennial weed, 21, 24<br />

perennial ryegrass, 1, 11, 14, 30, 55, 87, 88, 89, 90,<br />

91, 92<br />

Phaseolus vulgaris, 70<br />

phenmedipham, 95<br />

photosystem II, 28<br />

Phragmites, 25<br />

Phragmites australis, 25, 60<br />

phyllanthus sp, 49<br />

Phyllanthus tenellus, 83<br />

phytotoxicity, 12, 70, 73, 89, 99<br />

pigweed species, 3, 70, 76<br />

pinoxaden, 42, 77<br />

Pinus resinosa, 58<br />

Pinus rigida, 58<br />

Pinus strobus, 58<br />

plant growth regulators, 40, 48, 51, 100, 102, 103,<br />

104, 105<br />

Plantago major, 1<br />

plastic mulch, 3<br />

Poa annua, 11, 30, 32, 51, 88, 90, 91, 100, 103, 105<br />

Poa pratensis, 1, 5, 14, 20, 28, 88, 90, 91<br />

Poa trivialis, 15, 32<br />

Poaceae, 58<br />

pollinator, 39<br />

Polygonum cuspidatum, 60<br />

Populus trichocarpa, 47<br />

Portulaca oleracea, 3<br />

potato, 41, 71, 97<br />

Potentilla canadensis, 75<br />

Powell amaranth, 23<br />

primisulfuron-methyl, 53, 78<br />

prodiamine, 5, 18, 57, 80, 82, 83, 84, 90<br />

pronamide, 95<br />

prostrate knotweed, 86<br />

Pseudotsuga menziesii, 47<br />

Pueraria montana, 64<br />

pumpkins, 71<br />

pyridine herbicide, 85<br />

pyrithiobac, 69<br />

Q<br />

Quercus, 58<br />

quinclorac, 1, 52, 53, 54, 93<br />

R<br />

red maple, 10<br />

red pine, 58<br />

resistance, 42, 76<br />

resistance management, 45<br />

Rhizoctonia solani, 32<br />

rhododendron, 48<br />

Rhododendron, 83<br />

rice flat sedge, 50<br />

rimsulfuron, 40, 41, 70, 78, 79<br />

roller, 36<br />

Rosa, 83<br />

Rosa multiflora, 60<br />

rotary harrow, 8<br />

rotary hoe, 8<br />

roughstalk bluegrass, 15, 32<br />

Rubus spp, 75<br />

rye, 36<br />

ryegrass species, 76<br />

S<br />

safener, 72<br />

Schizachyrium scoparium, 53<br />

Sclerotinia homoeocarpa, 32<br />

sedges, 49<br />

seed stratification, 6<br />

seedbank, 23, 62<br />

Senecio vulgaris, 50<br />

Setaria faberi, 37, 70, 72, 79<br />

185


Setaria spp, 62, 76<br />

sethoxydim, 95<br />

Shasta daisy, 7<br />

shepherd’s-purse, 23<br />

siduron, 1, 20<br />

silage corn, 9<br />

silverleaf sawbrier, 75<br />

simazine, 45, 53<br />

small grains, 9<br />

s-metolachlor, 44, 70, 71, 72, 79, 80<br />

Smilax glauca, 75<br />

smooth crabgrass, 1, 5, 18, 20, 28, 52, 54, 89<br />

smooth pigweed, 72<br />

snap bean, 70, 98<br />

soil fumigant, 3<br />

Solanum, 97<br />

Solanum tuberosum, 97<br />

Sonchus asper, 50<br />

Sorghum spp, 76<br />

soybean, 8, 38<br />

specialty crops, 46, 94, 95<br />

spectrophotometer, 31<br />

spiny sowthistle, 50<br />

Spiraea x bumalda, 82<br />

spirea, 82<br />

Spirea japonica, 83<br />

spotted spurge, 26, 50<br />

Sprigging, 29<br />

spring barley, 9<br />

spring wheat, 9<br />

spurge sp, 49<br />

squash, 69<br />

stale seed bedding, 17<br />

Stellaria media, 1<br />

strawberries, 73<br />

sudan grass, 9<br />

sulfentrazone, 28, 45, 52, 53, 55, 57, 82, 84, 90, 91<br />

sulfonylurea, 79<br />

sulfosulfuron, 15, 53, 55<br />

survey, 17, 76<br />

sweet corn, 72<br />

sweet gum, 10<br />

sweet potatoes, 97<br />

switchgrass, 66<br />

T<br />

tall fescue, 11, 28, 54, 57, 87, 92<br />

Taraxacum officinale, 1, 5<br />

tembotrione, 1, 53, 72, 78, 79<br />

terbacil, 69<br />

thifensulfuron, 78<br />

thin paspalum, 52<br />

Thuja occidentalis, 82<br />

Thuja orientalis, 83<br />

tillage, 6, 8<br />

tomato, 71, 97<br />

topdressing, 29<br />

topramezone, 1, 53, 72, 75, 78, 79<br />

transition zone, 14<br />

triazine resistant, 41<br />

triazines, 40, 44<br />

triazolone, 28<br />

tribenuron, 45, 95<br />

triclopyr, 2, 10, 24, 63, 64, 85, 86, 93<br />

trifloxysulfuron, 53<br />

trifluralin, 18, 80, 83<br />

Trifluralin, 98<br />

Trifolium repens, 20, 28, 54<br />

triketone, 5<br />

trinexapac ethyl, 14, 31, 51, 99, 101, 104<br />

Triticum aestivum, 77<br />

trumpetcreeper, 24<br />

tulip poplar, 10<br />

turfgrass, 1, 5, 11, 18, 20, 29, 30, 31, 32, 51, 55, 86,<br />

87, 88, 89, 92, 93, 100, 102, 105<br />

turfgrass diseases, 32<br />

U<br />

urea ammonium nitrate, 75, 79<br />

V<br />

V-10142, 55<br />

Vaccinium angustifolium, 12<br />

Vaccinium macrocarpon, 75<br />

vascular flora, 58<br />

vegetable production, 3, 33<br />

velvetleaf, 40, 62, 70, 72<br />

Velvetleaf, 37<br />

Viburnum, 83<br />

Viburnum odoratissimum, 83<br />

Viburnum plicatum, 82<br />

Viburnum tinus, 83<br />

Vincetoxicum nigrum, 21<br />

Vincetoxicum rossicum, 21<br />

vinegar, 16, 33<br />

Viola spp, 20<br />

Virginia creeper, 24<br />

Vitaceae, 24<br />

W<br />

wavyleaf basketgrass, 22<br />

wet-blade, 10<br />

wetlands, 60<br />

wheat, 23, 77<br />

white clover, 20, 28, 54, 86<br />

white pine, 58<br />

wild oats, 76<br />

wild violet, 20<br />

winter barley, 9<br />

winter canola, 62<br />

winter triticale, 9<br />

winter wheat, 9<br />

woodsorrel, 49<br />

woody ornamentals, 49<br />

woody shrub, 60<br />

woody vine, 60<br />

186


Y<br />

yellow loosestrife, 75<br />

yellow nutsedge, 3, 40, 55, 57<br />

yellow rocket, 23<br />

yellow toadflax, 19<br />

yellow wood sorrel, 20<br />

Z<br />

Zea mays, 8, 38, 72, 78, 79<br />

187


188

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