Proceedings of the Sixty-first Annual Meeting of the Northeastern ...
Proceedings of the Sixty-first Annual Meeting of the Northeastern ... Proceedings of the Sixty-first Annual Meeting of the Northeastern ...
22 GIANT HOGWEED ERADICATION IN PENNSYLVANIA AND SURROUNDING STATES. M.A. Bravo, Pennsylvania Department of Agriculture, Harrisburg. ABSTRACT Heracleum mantegazzianum introduction to Europe, from its native Caucasus Mountains, dates back to 1817. By the late 1840's reports of wild populations of giant hogweed were documented in the United Kingdom. Currently 21 European countries have reported wild populations of giant hogweed. In the United States an increase in reports of wild populations is also occurring. Giant hogweed was added to the federal noxious weed list in 1983. Giant Hogweed is in its element here in the temperate region of the Northeastern states. In the last decade, 16 states (WA, OR, MI, IA, IN, WI, OH, PA, NY, NH, ME, VT, MA, CT, NJ, MD) have confirmed finding giant hogweed. PA first discovered giant hogweed in 1985 in Erie County. A joint effort between PDA and USDA in 1998 established the Giant Hogweed Eradication Program. Currently, PA has less than 600 sites with viable hogweed populations in 12 counties. Federal support for the project has been strong and as a result of the PA efforts, many other States are actively searching for Giant Hogweed and conducting outreach programs. In the fall of 2005, the Program Review Committee for Giant Hogweed met in Pennsylvania and outlined the following goals for 2006. Goals for Pennsylvania and other States in the Region for 2006 were 1) eradicating persisting, but isolated populations in outlying counties 2) developing a standardized database to assist in evaluating the successful of the eradication programs 3) acquiring regional staffing and funding to implement control measures in adjoining states 4) emphasizing the risk of infestations becoming established in riparian areas and 5) encouraging local and regional research on the ecology an biology of giant hogweed to assist the eradication program in understanding the long term population dynamics of this invasive species. Like most invasive primers, giant hogweed’s reproductive potential is enormous. Plants reproduce by seed and perenniating crown and rootbuds and have a high regeneration ability to set seed if seed heads are removed prior to maturity. A single plant is capable of yielding more than 100,000 seeds, primarily by out-crossing. Rosettes of giant hogweed can persist for as long as 12 years before flowering and understanding the biology of giant hogweed is critical to implementing a successful eradication program. 4
23 DOES POLYEMBRYONY CONFER GREATER COMPETITIVE ABILITY IN THE NON- NATIVE INVASIVE VINE, PALE SWALLOW-WORT? M.L. Blanchard, A. DiTommaso, K.M. Averill, C.L. Mohler, and J.N. Barney, Cornell Univ., Ithaca, NY. ABSTRACT Pale swallow-wort (Vincetoxicum rossicum (Kleopow) Barbar) is a non-native invasive vine in the Asclepiadaceae that has colonized natural systems in many Northeastern States and several Canadian provinces. It is a twining herbaceous perennial vine that can spread vegetatively, but reproduces primarily by seeds, some of which exhibit polyembryony (i.e., a condition where a single seed can produce multiple seedlings). Polyembryony occurs in a significant percentage of pale swallow-wort seeds, and may allow the plant to more effectively colonize areas as well as outcompete other plants for resources. Little is known about how polyembryony in this invasive plant affects competitive outcomes. Thus, the effect of polyembryony in pale swallow-wort on intra- and inter-specific competition was evaluated in a greenhouse experiment using a modified replacement series design. Pale swallow-wort plants from three polyembryonic classes; singles, doubles, and triples (i.e., one, two, and three seedlings per seed, respectively) were grown with each other in all combinations and with the native species, Canada goldenrod (Solidago canadensis L.) and common milkweed (Asclepias syriaca L.). A total density of 2 plants per pot was used. The height and number of nodes (rosette width for goldenrod) were recorded for pale swallow-wort and milkweed plants every two weeks for 10 weeks, and then 4 weeks later at the end of the experiment. After this 14-wk period, all plants were harvested and above- and below-ground biomass determined. In general, pale swallow-wort plants consisting of one seedling (singles) had significantly lower total biomass when competing with pale swallow-wort plants having two or three seedlings and with goldenrod and milkweed than with other single-seedling swallow-wort plants. These reductions in growth of single-seedling plants were most evident for belowground biomass. There was no significant difference between goldenrod and milkweed in their negative effect on pale swallow-wort. These findings suggest that the production of more than one seedling via polyembryony in pale swallow-wort may be advantageous in competitive environments. 5
- Page 1 and 2: 1 Proceedings of the Sixty-first An
- Page 3 and 4: 3 NORTHEASTERN WEED SCIENCE SOCIETY
- Page 5 and 6: 5 SECTION CHAIRS Agronomy Chair: J.
- Page 7 and 8: 7 CARFENTRAZONE AND QUINCLORAC FOR
- Page 9 and 10: 9 THE EFFICACY AND CROP TOLERANCE O
- Page 11 and 12: 11 EVALUATION OF HERBICIDES FOR CON
- Page 13 and 14: 13 BEING HEARD BY THE IR-4 PROJECT.
- Page 15 and 16: 15 ABSTRACTS FROM THE 7 TH CONFEREN
- Page 17: 17 HERBICIDE NAMES: COMMON, TRADE,
- Page 20 and 21: 20 INTEGRATING WEED CONTROL STRATEG
- Page 24 and 25: 24 EFFECTS OF EMERGENCE PERIODICITY
- Page 26 and 27: 26 PRODUCER AND PRODUCTION IMPACTS
- Page 28 and 29: 28 A SIMPLE METHOD FOR CLEANING TUF
- Page 30 and 31: 30 EMERGENCE AND PERFORMANCE OF TWO
- Page 32 and 33: 32 CARFENTRAZONE AND QUINCLORAC FOR
- Page 34 and 35: 34 2006 NEWSS SUMMER WEED CONTEST R
- Page 36 and 37: 36 INVASIVE AQUATIC WEEDS IN NORTH
- Page 38 and 39: 38 AMMONIUM PELARGONATE AS A BIOHER
- Page 40 and 41: 40 TRINEXAPAC-ETHYL INFLUENCES EFFI
- Page 42 and 43: 42 Table 1. Insect feeding damage,
- Page 44 and 45: 44 WEED CONTROL WITH TOPRAMEZONE PR
- Page 46 and 47: 46 ROTARY HOE EFFICACY IN CORN: INF
- Page 48 and 49: 48 ALFALFA/GRASS FORAGE MIXTURES US
- Page 50 and 51: 50 CONTROL OF NEW WEED SPECIES IN T
- Page 52 and 53: 52 Table 1. Results of 2006 contain
- Page 54 and 55: 54 TOLERANCES OF ORNAMENTAL SHRUBS
- Page 56 and 57: 56 2006 WEED MANAGEMENT TRIALS IN C
- Page 58 and 59: 58 THE RESPONSE OF FIELD AND CONTAI
- Page 60 and 61: 60 THE EFFICACY AND CROP TOLERANCE
- Page 62 and 63: 62 Table 2. Plant quality ratings o
- Page 64 and 65: 64 EVALUATION OF PROLINE-LINKED PEN
- Page 66 and 67: 66 ANNUAL BLUEGRASS AND DOLLAR SPOT
- Page 68 and 69: 68 Table 1. Autumn 2005 versus spri
- Page 70 and 71: 70 A PRELIMINARY STUDY OF THE NON-N
22<br />
GIANT HOGWEED ERADICATION IN PENNSYLVANIA AND SURROUNDING<br />
STATES. M.A. Bravo, Pennsylvania Department <strong>of</strong> Agriculture, Harrisburg.<br />
ABSTRACT<br />
Heracleum mantegazzianum introduction to Europe, from its native Caucasus<br />
Mountains, dates back to 1817. By <strong>the</strong> late 1840's reports <strong>of</strong> wild populations <strong>of</strong> giant<br />
hogweed were documented in <strong>the</strong> United Kingdom. Currently 21 European countries<br />
have reported wild populations <strong>of</strong> giant hogweed. In <strong>the</strong> United States an increase in<br />
reports <strong>of</strong> wild populations is also occurring. Giant hogweed was added to <strong>the</strong> federal<br />
noxious weed list in 1983. Giant Hogweed is in its element here in <strong>the</strong> temperate region<br />
<strong>of</strong> <strong>the</strong> Nor<strong>the</strong>astern states. In <strong>the</strong> last decade, 16 states (WA, OR, MI, IA, IN, WI, OH,<br />
PA, NY, NH, ME, VT, MA, CT, NJ, MD) have confirmed finding giant hogweed. PA <strong>first</strong><br />
discovered giant hogweed in 1985 in Erie County. A joint effort between PDA and<br />
USDA in 1998 established <strong>the</strong> Giant Hogweed Eradication Program. Currently, PA has<br />
less than 600 sites with viable hogweed populations in 12 counties. Federal support for<br />
<strong>the</strong> project has been strong and as a result <strong>of</strong> <strong>the</strong> PA efforts, many o<strong>the</strong>r States are<br />
actively searching for Giant Hogweed and conducting outreach programs. In <strong>the</strong> fall <strong>of</strong><br />
2005, <strong>the</strong> Program Review Committee for Giant Hogweed met in Pennsylvania and<br />
outlined <strong>the</strong> following goals for 2006. Goals for Pennsylvania and o<strong>the</strong>r States in <strong>the</strong><br />
Region for 2006 were 1) eradicating persisting, but isolated populations in outlying<br />
counties 2) developing a standardized database to assist in evaluating <strong>the</strong> successful<br />
<strong>of</strong> <strong>the</strong> eradication programs 3) acquiring regional staffing and funding to implement<br />
control measures in adjoining states 4) emphasizing <strong>the</strong> risk <strong>of</strong> infestations becoming<br />
established in riparian areas and 5) encouraging local and regional research on <strong>the</strong><br />
ecology an biology <strong>of</strong> giant hogweed to assist <strong>the</strong> eradication program in understanding<br />
<strong>the</strong> long term population dynamics <strong>of</strong> this invasive species. Like most invasive primers,<br />
giant hogweed’s reproductive potential is enormous. Plants reproduce by seed and<br />
perenniating crown and rootbuds and have a high regeneration ability to set seed if<br />
seed heads are removed prior to maturity. A single plant is capable <strong>of</strong> yielding more<br />
than 100,000 seeds, primarily by out-crossing. Rosettes <strong>of</strong> giant hogweed can persist<br />
for as long as 12 years before flowering and understanding <strong>the</strong> biology <strong>of</strong> giant<br />
hogweed is critical to implementing a successful eradication program.<br />
4