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Precision of the sediment quality values The precision of the values generated using each approach was estimated for selected components of uncertainty that could be quantified. The uncertainty of the equilibrium partitioning approach was estimated to range from less than one to six orders of magnitude of the calculated values, primarily because of uncertainty in the estimation of theoretical constants and the applicability of water quality criteria used in the approach. For a given set of field data, the uncertainty of the AET approach was estimated to range from much less than one to two orders of magnitude of the values generated, primarily because of potential misclassiflcatlon of nonlmpacted stations that are used to define the AET. A statistical evaluation of the precision of the SIX values was beyond the scope of the study, but has been evaluated elsewhere (Battelle 1986). Recommended uses of sediment quality values The sediment quality value study involved identification of a range of chemical values that can be applied in sediment management, but did not identify the specific values which agencies should adopt for regulation or how these values should be used In different regulatory programs. Interagency technical and management workgroups are currently in the process of evaluating the ranges of sediment quality values identified during the study and identifying specific values for different regulatory uses in Puget Sound. The U.S. EPA, U.S. Army Corps of Engineers and the Washington State Department's of Ecology and Natural Resources are in the process of adopting sediment quality values (based on application of the AET approach) that can be used 1n combination with biological tests to regulate the open-water disposal of contaminated dredged material. In the coming year it is anticipated that sediment quality values will also be identified for use as a tool In classifying and prioritizing areas for source control and remedial action, and in establishing discharge limits for particulates in effluent that are protective of marine sediment quality. Although sediment quality values are being Identified for use 1n Puget Sound, the agencies Involved consider the values to be interim. As additional laboratory Information concerning chemical/biological cause and effect relationships is developed, and as supplemental field data becomes available, recommended sediment quality values and the approaches to establishing and using those values are expected to change. References Battelle. 1985. Detailed chemical and biological analyses of selected sediment from Puget Sound. Draft Final Report. U.S. Environmental Protection Agency Region X, Seattle, WA. 300 pp. 637
63S Battelle. 1986. Sediment quality criteria methodology validation: calculation of screening level concentrations from field data. Final Report. Prepared for the U.S. Environmental Protection Agency, Criteria and Standards Division. Battelle, Washington, DC. 60 pp. plus appendices. Chan, S., H., Schiewe, and 0. Brown. 1985. Analyses of sediment samples for U.S. Amy Corps of Engineers Seattle harbor navigation project, operations and maintenance sampling and testing of Ouwamish River sediments. Draft Report. 15pp. plus appendices. Chan, S., M., Schiewe, and D. Brown. 1985. Analyses of sediment samples for U.S. Army Corps of Engineers East, West, and Duwamish Waterways navigation Improvement project, operations and maintenance sampling and testing of Duwamish River sediments. Unpublished. Comlskey, C.E., T.A. Farmer, C.C. Brandt, et al. 1984. Puget Sound benthic studies and ecological implications. Toxicant Pretreatment Planning Study. Tec. Report C2. Municipality of Metropolitan Seattle, Seattle, WA 373 pp. Osborn, J.G., D.E. Weltkamp, and T.H. Schadt. 1985. Alki wastewater treatment plant outfall Improvements predesign study. Tech. Report No. 6.0, Marine Biology. Municipality of Metropolitan Seattle. 50 pp. Romberg, G.P., S.P. Pavlou, and E.A. Crecelius. 1984. Presence, distribution, and fate of toxicants in Puget Sound and Lake Washington. METRO Toxicant Program Report No. 6A. Toxicant Pretreatment Planning Study Technical Report CI. Municipality of Metropolitan Seattle, Seattle, WA 231 pp. Tetra Tech. 1985. Commencement Bay nearshore/tideflats remedial investigation. Final Report. Prepared for the Washington Department of Ecology and U.S. Environmental Protection Agency. EPA-910/9-85-134b. 2 volumes plus appendices. Tetra Tech, Inc., Bellevue, WA. Trail, W., and J. Michaud. 1985. Alki wastewater treatment plant outfall improvements predesign study. Tech. Report No. 8.3, Water Quality. Huniclpality of Metropolitan Seattle. 89 pp. U.S. Department of the Navy. 1985. Final environmental impact statement. Carrier Battle Group Puget Sound region ship homeporting project. Technical Appendix, vol. 2. Prepared for U.S. Department of the Navy, Western Division, Naval Facilities Engineering Command, San, Bruno, CA.
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HT 390 .C66 C66 1986 v.2 Thomas EBi
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Copyright® 1987 The Coastal Societ
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"PROPERTY OF NOAA COASTAL K_CE3 CEN
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PLENARY SESSIONS TABLE OF CONTENTS
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CHARACTERIZING A SYSTEM Choir. Char
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TRACKING TOXICS Chair Susan Harvey
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The Use ofthe NationalWater DataExc
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The Site Selection Process foraChes
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MANAGING LIVING RESOURCES Resource
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Estuarine and CoastalManagement - T
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398 the particular Interests, envir
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400 data, a developer may discover
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Estuarine and Coastal Management
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fortune to work with several coasta
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growth economics, local feelings ab
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410 unprotected coastal barriers wi
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412 caveats. The greatest concerns
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Estuarine and Coastal Management -
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Model of Resort Evolution R. Initia
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Pensacola Beach Like Fort Myers Bea
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had again contributed to serious en
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Estuarine andCoastal Management -To
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High altitude and oblique aerial ph
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Estuarineand Coastal Management•
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432 system, the LEO system is start
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434 b. Hind observations (Figure 5)
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436 LEO PERCENT OCCURRENCE OF WAVE
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438 Estuarine and Coastal Managemen
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440 appropriate variables and param
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STEPbTSB NBICHBOB SBCBDI CANDISC NE
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Estuarineand Coastal Management Too
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(figures 1 and 2). On a first order
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variables. This resulted in a set o
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Estuarine andCoastal Management •
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help canaands and dictionaries are
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Access to System All requests for a
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460 Why Is NOAA Unarmed In ftnMfal
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462 To test this procedure, a simpl
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464 Cowardln, L.M.. V. Carter, F.C.
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466 between the participating indiv
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468 Data Search Assistance Through
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470 Additional Information For addi
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472 Estuarine andCoastal Management
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474 FIGURE 2 OPDIN RESOURCES NMPIS
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476 means ot access, determination
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478 NMPPO. 1985b. Inventory of Non-
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EDUCATING DECISIONMAKERS William Ei
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prediction of the effects of changi
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Management Oommittee did slightly r
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The causes of the degradation of wa
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quality. For a commission to adopt
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496 authorities prior to any land d
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498 boon based largely on ono piece
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500 Interstate Agreement on Chesape
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Estuarine and Coastal Management -T
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In general, though, these relations
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meetings. Their recommendations ver
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etveen any other academic departmen
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Many of these same demands vere mad
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Estuarineand Coastal Management- To
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The private sector The motivation f
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It's more and more obvious: those w
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The Center's role is limited to ide
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County. The resulting roport, "Cons
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and shellflshing; to provide open s
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The COD is innovative as a performa
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Estuarine andCoastal Management - T
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provide adequate information for a
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Aquaculture project The most recent
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CHESAPEAKEBAY VirginiaTippie,Chair
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542 program with an investment of 2
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Estuarine andCoastalManagement - To
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methodology being proposed - develo
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major sections of the 1972 Clean Wa
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Prioritizing makes best use of the
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Degradation of the Bay has taken a
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558 federal agencies, additional tr
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560 ing system 1t would be helpful
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obtained, or shoreline changes-were
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SAV was sighted as well as water co
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canadensis and Zannlchelia palustri
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greatest percent increases occurrin
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Orth, R.J., K.L. Heck, Jr. and J. v
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Estuarineand Coastal Management- To
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Bromley (1978) considered (1) propo
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2. Rnyulntorv nrogram-i A number of
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Page 189 and 190: property rule. If Congress passed s
Page 191 and 192: nonpoint source water pollution con
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Page 195 and 196: cannot be granted unless there is u
Page 197 and 198: ecomes subject to cancellation. An
Page 199 and 200: REFERENCES Morrison, M.D. and M.K.
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Page 203 and 204: 600 requirements for dumping of ves
Page 205 and 206: 602 oatorlal in the future. The oil
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Page 209 and 210: Application of the doctrine of Impl
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Page 216 and 217: compilation of existing data. Areas
Page 218 and 219: To rank areas based on observed con
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Page 224 and 225: satellites to the reserve system, a
Page 226 and 227: types of geomorphological features
Page 228 and 229: Manao-gmgnr conaldpratH onn — The
Page 230 and 231: productivity. The National Estuarin
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Page 234 and 235: equired to validate the sensitivity
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Page 242 and 243: Independent variable that is assume
Page 244 and 245: Possible outcomes of the experiment
Page 246 and 247: PREPARING FOR EMERGENCIES James McQ
Page 248 and 249: 648 The evacuation of more than 500
Page 250 and 251: 650 terminal; $220,000 for an oil s
Page 252 and 253: 652 U.S. Highway 98 damage estimate
Page 254 and 255: 654 Spangenbcrg, T. 1986. Personal
Page 256 and 257: LOUISIANA'S BATTLEWITH THE SEA; ITS
Page 260 and 261: Qco ISLES DERltt^ km & Figure 2. Hi
Page 262 and 263: Objectives The first objective of t
Page 264 and 265: STATION NUMBER STATION NAME TABLE 1
Page 266 and 267: The St. Petersburg tide gauge stati
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Page 270 and 271: elative sea level rise is 0.33 cm/y
Page 272 and 273: References Byrne, P., Borengasser,
Page 276 and 277: these times that the increase in vu
Page 278 and 279: econstruction projects. Conclusion
Page 280 and 281: RESOLVING CONFLICTS/ASSESSING RISKS
Page 282 and 283: 686 lightering is estimated at $69
Page 284 and 285: BEACH EVOLUTION AFTER CAUSEWAY CONS
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Inextricably wound up with religion
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ethics is that advocated by Leopold
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laboratory animals, lower animals a
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Estuarine andCoastal Management-Too
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Estuarine and Coastal Management To
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708 these projects. Our criteria fo
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710 S. alternlflora established on
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712 Additional compensation by ropl
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714 to the question of placement (l
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716 criteria adequate to achieve th
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718 Nixon, S. W. 1980. Between coas
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720 of them because of this distanc
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722 Light penetration Is probably o
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Estuarine and CoastalManagement-Too
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management emphasis Is now affectin
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734 assemblages; Juvenile fish and
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-J 736 The heavy material falls out
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738 Future Harsh Creation. We are n
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Estuarine andCoastal Management -To
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This site also satisfied several ot
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successful implementation of such a
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750 I.C.R.R Fig. I
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752 More lumber companieslaunched o
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754 the track. When ties nasoed rep
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756 Schlleder spared no expense, no
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758 Stover, j. F. 1955. The Railroa
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Estuarineand Coastal Management•
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contain detailed Information about
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production Is uncertain. Thus, the
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Estuarine and Coastal Management To
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MANAGING LIVING RESOURCES
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776 seagrasses and associated biota
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778 FLORIDA BIG BEND SEAGRASS HABIT
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780 Barle, S. A. 1972. Benthic alga
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Estuarine andCoastal Management-Too
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The Florida alligator nuisance prog
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In Louisiana, a computer simulation
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Florida Game and Fresh Water Fish C
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Estuarine and CoastalManagement - T
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794 Mississippi Born * Island Petit
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796" important means of preserving
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f 798 man-modified environments. Th
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