ࡱ> :789 I@\p Rick Greene Ba= =X\+8<@"1Arial1Arial1Arial1Arial1Arial1Arial1Arial1Arial1Arial"$"#,##0_);\("$"#,##0\)!"$"#,##0_);[Red]\("$"#,##0\)""$"#,##0.00_);\("$"#,##0.00\)'""$"#,##0.00_);[Red]\("$"#,##0.00\)7*2_("$"* #,##0_);_("$"* \(#,##0\);_("$"* "-"_);_(@_).))_(* #,##0_);_(* \(#,##0\);_(* "-"_);_(@_)?,:_("$"* #,##0.00_);_("$"* \(#,##0.00\);_("$"* "-"??_);_(@_)6+1_(* #,##0.00_);_(* \(#,##0.00\);_(* "-"??_);_(@_) mm/dd/yy0.0                + ) , *      " ! " ! # ! !P ! !  !  !X  !X !      h "T  D "T `Sample DescriptionTMetals ePCBs$~}Dioxins,Furans,Coplanar PCBsG OC Pesticides rPAHsAChlorobenzenesFMethods and QA`i  U( 6.51 empc) U( 4.84 empc) U( 9.95 empc) U( 3.33 empc) U( 5.74 empc) U( 12.1 empc) U( 6.11 empc) U( 8 empc) U( 19.1 empc) U( 1.71 empc) U( 5.37 empc) U( 4.9 empc) U( 3.85 empc) U( 11.6 empc) U( 6.14 empc) U( .996 empc) U( 6.52 empc) U( 6.22 empc) U( .897 empc) U( 3.18 empc) U( 3.82 empc) U( 8.63 empc) U( 3.49 empc) U( 8.03 empc) U( 15.8 empc) U( 13.6 empc) U( 6.73 empc) U( 4.08 empc) U( 8.65 empc) U( 3.91 empc) U( .647 empc) U( 3.94 empc) U( 5.21 empc) U( 8.4 empc) U( 36.4 empc) U( 3.88 empc) U( 5.29 empc) U( 1.14 empc) U( 1.17 empc) U( 2.22 empc) U( .903 empc) U( .185 empc) U( 6.96 empc) U( .674 empc) U( .302 empc) U( 2.32 empc) U( 6.26 empc) U( .556 empc) U( .875 empc) U( 1.31 empc) U( 1.66 empc) U( 3.25 empc) U( 4.03 empc) U( 5.12 empc) U( .6 empc) U( .721 empc) U( .702 empc) U( 1.94 empc) U( 1.42 empc) U( 2.02 empc) U( 1.9 empc) U( 1.61 empc) U( 5.11 empc) U( 2.79 empc) U( 2.49 empc) U( 12.8 empc) U( 15.3 empc) U( 19.3 empc) U( 1.4 empc) U( 3.51 empc) U( 4.45 empc) U( 1.74 empc) U( 8.61 empc) U( 4.92 empc) U( 2.92 empc) U( 4.89 empc) U( .921 empc) U( 3.92 empc) U( 5.03 empc) U( 3.98 empc) U( 2.25 empc) U( 7.87 empc) U( 6.42 empc) U( 2.13 empc) U( 1.59 empc) U( 6.06 empc) U( 13.7 empc) U( 1.77 empc) U( 3.8 empc) U( .536 empc) U( 1.27 empc) U( 1.22 empc) U( 1.67 empc) U( 2.42 empc) U( .701 empc) U( 3.62 empc) U( 1.41 empc) U( .96 empc) U( 2.11 empc) U( 3.76 empc) U( .902 empc) U( 2.54 empc) U( .224 empc) U( 1.52 empc) U( 1.57 empc) U( .817 empc) U( .641 empc) U( .846 empc) U( .545 empc) U( .402 empc) U( 2.19 empc) U( 18.4 empc) U( 1.49 empc) U( 1.47 empc) U( 1.11 empc) U( .994 empc) U( 3.2 empc) U( 2.9 empc) U( 1.81 empc) U( 2.07 empc) U( 1.75 empc) U( 2.69 empc) U( 1.18 empc) U( 3.06 empc) U( 5.64 empc) U( 2.09 empc) U( 16.4 empc) U( 2.21 empc) U( .462 empc) U( 1.34 empc) U( 3.55 empc) U( 5.78 empc) U( 2.38 empc) U( 5.67 empc) U( 4.96 empc) U( 4.12 empc) U( 5.16 empc) U( 3.87 empc) U( 3.43 empc) U( 3.39 empc) U( 21.7 empc) U( 2.91 empc) U( 1.72 empc) U( 5.01 empc) U( 2.74 empc) U( 5.53 empc) U( 1.04 empc) U( .635 empc) U( 2.4 empc) U( 4.35 empc) U( 9.09 empc) U( 2.89 empc) U( 12.6 empc) U( 17.5 empc) U( 1.79 empc) U( 4.4 empc) U( 5.48 empc) U( .884 empc) U( .946 empc) U( 3.02 empc) U( 6.2 empc) U( 7.72 empc) U( 5.15 empc) U( 3.24 empc) U( 4.26 empc) U( 3.14 empc) U( 5.95 empc) U( 1.64 empc) U( 3.15 empc) U( 2.56 empc) U( 9.92 empc) U( 1.24 empc) U( 8.69 empc) U( .926 empc) U( 3.95 empc) U( 8.42 empc) U( 1.7 empc) U( 7.9 empc) U( 2.37 empc) U( 11.1 empc) U( 9.32 empc) U( .599 empc) U( 3.46 empc) U( .328 empc) U( 7.47 empc) U( .804 empc) U( 1.89 empc) U( 14.1 empc) U( 2.2 empc) U( .475 empc) U( 1.54 empc) U( 41.2 empc) U( .675 empc) U( 15.2 empc) U( 5.57 empc) U( 1.23 empc) U( 7.48 empc) U( .48 empc) U( 4.94 empc) U( .712 empc) U( 3.12 empc) U( 1.5 empc) U( 4.61 empc) U( 9.26 empc) U( 1.21 empc) U( 31.6 empc) U( 8.51 empc) U( 3.65 empc) U( 16.5 empc) U( 6.55 empc) U( 7.66 empc) U( 1.92 empc) U( 7.26 empc) U( 6.34 empc) U( 3.4 empc) U( .609 empc) U( 2.63 empc) U( 2.27 empc) U( 6.62 empc) U( .657 empc) U( .406 empc) U( 8.23 empc) 2,3,7,8-TCDD1,2,3,7,8-PeCDF2,3,4,7,8-PeCDF1,2,3,7,8-PeCDD1,2,3,4,7,8-HxCDF1,2,3,6,7,8-HxCDF2,3,4,6,7,8-HxCDF1,2,3,7,8,9-HxCDF1,2,3,4,7,8-HxCDD1,2,3,6,7,8-HxCDD1,2,3,7,8,9-HxCDD1,2,3,4,6,7,8-HpCDF1,2,3,4,7,8,9-HpCDF1,2,3,4,6,7,8-HpCDDOCDFOCDD 2,3,7,8-TCDF Total TCDF Total TCDD Total PECDF Total PECDD Total HXCDF Total HXCDD Total HPCDF Total HPCDD U( .685 empc) U( 8.85 empc) U( .764 empc) U( 2.18 empc) U( 5.35 empc) U( 3.26 empc) U( .83 empc) U( .952 empc) U( 10.8 empc) U( .331 empc) U( .18 empc) U( 5.75 empc) U( .816 empc) U( 2.65 empc) U( 287 empc) U( 3.09 empc) U( 5.43 empc) U( 27.9 empc) U( 14.9 empc) U( 13.9 empc) U( 9.54 empc) U( 7.99 empc) U( 5 empc) U( 12.4 empc) U( 9.64 empc) U( 14.5 empc) U( 9.62 empc) U( 23 empc) U( 11.2 empc) U( 1.15 empc) U( 6.54 empc) U( 7.28 empc) U( 1.1 empc) U( 2.33 empc) U( 4.25 empc) U( .524 empc) U( 8.47 empc) U( 2.98 empc) U( 5.07 empc) U( 2.64 empc) U( 2.51 empc) U( 4.69 empc) U( 4.06 empc) U( 9.22 empc)U( 11.1 empc) (1) U(1.25) (3) U(2.5) (3) U(3.75) (3) Coochs Bridge U( .233 cdl) U( .214 cdl) U( .278 cdl) U( .208 cdl) U( .242 cdl) U( .253 cdl) U( .244 cdl) U( .241 cdl) U( .251 cdl) U( .182 cdl) U( .25 cdl) U( .211 cdl) U( .2 cdl) U( .283 cdl) U( .217 cdl) U( .209 cdl) U( .206 cdl) U( .831 cdl) U( .839 cdl) U( 1.21 cdl) U( .944 cdl) U( 1.05 cdl) U( 1.09 cdl) U( 1.16 cdl) U( 1.12 cdl) U( 1.06 cdl) U( .527 cdl) U( 2.21 cdl) U( 2.69 cdl) U( 1.11 cdl) U( 1.08 cdl) U( 1.07 cdl) U( 1.03 cdl) U( .878 cdl) U( .847 cdl) U( .786 cdl) U( .774 cdl) U( 1.04 cdl) U( .966 cdl) U( .81 cdl) U( .933 cdl) U( .972 cdl) U( .897 cdl) U( .96 cdl) U( .862 cdl) U( .823 cdl) U( .749 cdl) U( .721 cdl) U( .829 cdl) U( .817 cdl) U( 1.15 cdl) U( .892 cdl) U( 2.25 cdl) U( 2.7 cdl) U( 1.01 cdl) U( .956 cdl) U( .89 cdl) U( .827 cdl) U( .695 cdl) U( .795 cdl) U( .991 cdl) U( .857 cdl) U( .93 cdl) U( .969 cdl) U( 1.02 cdl)81-TPCB77-TPCB 127-PePCB 126-PePCB 169-HxPCBRData and information in this spreadsheet were obtained from the following sources: Organochlorine Pesticide Results Concentrations in ng/g (ppb) wetChlordane (gamma) ND (3.09)Chlordane(alpha )DicofolDieldrin Endosulfan I Endosulfan IIEndrinHeptaclor epoxideHexachlorobenzeneLindaneMirexTrans Nonachlor Cis Nonachlor OxychlordaneMonoDi TriTetraPentaHexaHeptaOctaNonaSum of Homologs,A. PCB Congener Data, ng/g wet weight basis+B. PCB Homolog Data, ng/g wet weight basis A. Methods)Briefly with regard to chemical analyses,B. Quality AssuranceiSamples were collected by the Delaware Department of Natural Resources and Environmental Control (DNREC).iOrganic contaminants were analyzed by the Midwest Research Institute (MRI) under contract with the DNREC.TMetals were analyzed by the DNREC's Environmental Services Section (ESS) Laboratory.WLaboratory methods for metals are described in DNREC ESS Standard Operating Procedures.Midwest Reseach Institute. 1994. Analysis of Fish Tissue Samples for PCDDs, PCDFs, Congener-Specific PCBs, Pesticides, and PAHs for Assessing Pollutant Bioaccumulation from Selected Delaware Stream Basins, FY '94 Revised Final Report (MRI Project No. 3723-01). 39 07 33.7 75 31 04.7 39 36 18.8 75 37 50.2 39 33 08.0 75 39 02.5Dioxins, furans, and coplanar PCB congeners were analyzed by High Resolution Gas Chromatography/High Resolution Mass Spectrometry (HRGC/HRMS).}All other organic compounds were analyzed by High Resolution Gas Chromatography/Low Resolution Mass Spectrometry (HRGC/LRMS).Field procedures for sample collection followed DNREC ESS Standard Operating Procedure No. 500 ("Field Procedures for Fish Sample Handling").Procedures for dissection, tissue grinding, and sample storage followed DNREC ESS Standard Operating Procedure No. 501 ("Processing of Finfish for Chemical Analyis"). CLaboratory methods for organic contaminants are fully described in:LMercury was analyzed using Cold Vapor Atomic Absorption Spectrometry (CVAA).Metals other than mercury and zinc were analyzed using Graphite Furnace Atomic Absorption (GFAA). Zinc was analyzed using Inductively Coupled Argon Plasma (ICAP). No.of FishDecaQuality assurance testing for metals included matrix spike and matrix spike duplicate analyses. Results of those analyses are on file at the DNREC ESS La< boratory.Quality assurance procedures for organic analyses included method blanks, matrix spikes, matrix spike duplicates, and percent recoveries for internal standardsBand surrogate standards. Results of QA testing are documented in:Report prepared by the Midwest Research Institute for the Delaware Department of Natural Resources and Environmental Control, Dover, DE. Report prepared by the Midwest Research Institute for the Delaware Department of Natural Resources and Environmental Control, Dover, DE.Sum of DDD,DDE,DDTGA. Dioxin/Furan Raw Data, pg/g wet weight basis, analyzed by HRGC/HRMSNotes:@ congeners not detected based on lowest calibration standard.QB. Non-Ortho Coplanar PCB Raw Data, pg/g wet weight basis, analyzed by HRGC/HRMSg3. Congeners calculated manually vs Phenanthrene d10 internal standard. Estimated detection limits for3. Target analytes calculated manually vs Phenanthrene d10 internal standard. Estimated detection limit for compounds not detected is 5 ng/g.1,3-Dichlorobenzene1,4-Dichlorobenzene1,2-Dichlorobenzene1,2,3-Trichlorobenzene1,2,4-Trichlorobenezene1,3,5-Trichlorobenzene1,2,3,4-Tetrachlorobenzene1,2,3,5-Tetrachlorobenzene1,2,4,5-TetrachlorobenzenePentachlorobenzeneNote: Polyaromatic Hydrocarbon Results AcenaphtheneAcenaphthylene AnthraceneBenzo (a) anthraceneBenzo (a) pyreneBenzo (b)fluorantheneBenzo (g,h,i)perylene 39 42 38.6 75 36 26.9Moores Lake TumbleholeBenzo (k) fluorantheneBenzo(e) PyreneBiphenyl1-Chloronaphthalene2-ChloronaphthaleneChyrseneDibenzo (a,h) anthraceneDimethyl naphthalene FluorantheneFluoreneIndeno (1,2,3, cd) pyrene1-Methylnaphthalene2-MethylnapthaleneMethyl Phenanthrene Naphthalene5-NitroacenaphthenePerylene PhenanthrenePyreneTrimethyl naphthaleneChlorobenzene ResultsBDelaware Department of Natural Resources and Environmental Control 2. DNREC Laboratory Data Files.MeanMinimumMaximumDatePortion No. of FishLengthWeight Sample ID WaterbodyLocationLatitude LongitudeSampledSpeciesAnalyzed in Sample(cm)(gm) Brandywine Smith Bridge White SuckerFillet Skin On ChristinaChristina ParkChannel CatfishFillet Skin OffNewportCooch's Bridge White ClayStantonThompson's Bridge Saint Jones Moore's LakeLargemouth Bass White PerchWyoming Mill PondCarpMoore's Lake TumbleholeBluegill AppoquiniminkOdessaRed LionRoute 9Brown Bullhead C&D CanalRoute 13 39 44 07.0 39 07 35.3 39 07 23.6 39 27 09.0 75 39 19.0Metals Results&Concentrations are in units of ppm wetArsenic Cadmium Copper Lead MercurySeleniumZinc (ppm)<0.2<0.02<0.12< 0.02 75 32 30.0 75 31 10.9 75 33 41.11 Mono3 Mono4 Di7 Di8 Di18 Tri28 Tri37 Tri44 Tetra47 Tetra49 Tetra52 Tetra60 Tetra66 Tetra70 Tetra74 Tetra80 Tetra82 Penta87 Penta95 Penta99 Penta 101 Penta 105 Penta 110 Penta 114 Penta118Penta 119 Penta 123 Penta128 Hexa137 Hexa 138,158 Hexa149 Hexa151 Hexa153 Hexa156 Hexa157 Hexa166 Hexa167 Hexa168 Hexa 170,190 Hepta 177 Hepta 179 Hepta 180 Hepta 183 Hepta 185 Hepta 187 Hepta 189 Hepta 191 Hepta194 Octa195 Octa 196,203 Octa200 Octa201 Octa205 Octa206 Nona207 Nona208 Nona209 DecaSum of CongenersND1. Midwest Reseach Institute. 1994. Analysis of Fish Tissue Samples for PCDDs, PCDFs, Congener-Specific PCBs, Pesticides, and PAHs U( .904 cdl) U( .837 cdl) U( .861 cdl) U( .98 cdl) U( .99 cdl) U( 1.18 cdl) U( .992 cdl) 39 38 24.4 75 44 10.4 U( 1.17 cdl) U( 1.3 cdl) U( .556 cdl) U( 2.14 cdl) U( 2.63 cdl) U( 1.13 cdl) U( 1.1 cdl) U( .879 cdl) U( .917 cdl) U( .92 cdl) U( .978 cdl) U( 1.19 cdl) U( .952 cdl) U( .935 cdl) U( .938 cdl) U( .784 cdl) U( .883 cdl) U( .91 cdl) U( .954 cdl) U( .509 cdl) U( 2 cdl) U( 2.43 cdl) U( 1 cdl) U( .789 cdl) U( .83 cdl) U( .82 cdl) U( .79 cdl) U( .86 cdl) U( .94 cdl) U( .848 cdl) U( .931 cdl) U( .925 cdl) U( .895 cdl) U( .97 cdl) U( .849 cdl) U( .882 cdl) U( .997 cdl) U( 1.38 cdl) U( 1.36 cdl) U( 1.33 cdl) U( 1.44 cdl) U( 1.28 cdl) U( 1.23 cdl) U( .578 cdl) U( 2.77 cdl) U( 1.34 cdl) U( 1.32 cdl) U( 1.27 cdl) U( 1.29 cdl) U( .887 cdl) U( .948 cdl) U( .915 cdl) U( 1.26 cdl) U( 1.14 cdl) U( 1.39 cdl) U( .989 cdl) U( 2.18 cdl) U( 2.57 cdl) U( 1.24 cdl) U( .903 cdl) U( 1.22 cdl) U( .998 cdl) U( .959 cdl) U( 1.87 cdl) U( 2.15 cdl) U( 2.55 cdl) U( 2.72 cdl) U( 2.32 cdl) U( 2.33 cdl) U( 2.35 cdl) U( 2.12 cdl) U( 2.61 cdl) U( 2.48 cdl) U( 2.1 cdl) U( 4.08 cdl) U( 4.87 cdl) U( 2.79 cdl) U( 2.44 cdl) U( 2.74 cdl) U( 2.41 cdl) U( 2.49 cdl) U( 2.54 cdl) U( 1.67 cdl) U( 1.7 cdl) U( 1.72 cdl) U( 2.09 cdl) U( 2.05 cdl) U( 1.91 cdl) U( 2.22 cdl) U( 2.26 cdl) U( 1.99 cdl) U( 2.52 cdl) U( 2.85 cdl) U( .535 cdl) U( .192 cdl) U( .186 cdl) U( .183 cdl) U( .207 cdl) U( .239 cdl) U( .191 cdl)U( .749 cdl) (1) U(1.25)U(2.5)U(6.75)U(6.25) U(1.25) (1)U( .633 empc) (2) U( .194 empc) U( .189 empc) U( .244 empc) U( .259 empc) U( .258 empc) U( .554 empc) U( .226 empc)1. U(# cdl)=Compound not detected. Value in parentheses is calculated detection limit (cdl) based on the low calibration standard.2. U(# empc)=Compound not detected. Value in parentheses is an estimated maximum possible concentration (empc) detection limit based on an interference.1. U(# empc)=Compound not detected. Value in parentheses is an estimated maximum possible concentration (empc) detection limit based on an interference.2. U(#)= Compound not detected. Value in parentheses is an instrumental noise detection limit (2.5 times the background noise). 39 50 15.8 75 34 44.41. U(#)=Compound not detected. Value in parentheses is a calculated detection limit for homolog based on the lowest homolog specific calibration standard. U(241) (2)U(121)U( 16.2)U( 7.65)U( 1.28)U( 58.9)U( 2.85 empc) (1) U( 220 empc) U( 149 empc) U( 10.9 empc) U( 9.55 empc) U( 7.54 empc) U( 3.17 empc)U( .73)U( .713) U( 388 empc)U( 1.0) U( 392 empc) U( 87.8 empc) U( 20.2 empc) U(214 empc) U( 10.4 empc) U( 8.43 empc)U(14.5)U(34.8) U( 46.9 empc) U(27.4 empc) U( 71.6 empc) U( 819 empc) U( 9.34 empc) U( 33.4 empc)U(23) U( 27.2 empc) U( 97.6 empc) U( 8.2 empc) U( 7.86 empc) U( 48 empc) U( 60.1 empc) U( 60.3 empc)U( 47.6)U(391)U( 298) U(38.3 empc)U( 114)U( 37.8)U( 32.1)U( 27.4)U( 19.4)U( 12.9)U( 58.2) U(157empc) U(93.2 empc)U(148)U( 40.1)U( 23)U( 28.4)U(100)U( 33.8) U(565 empc) U(52.9 empc)U( 20)U(13) U(133 empc)U( 160)U(207)U( 58.4)U( 54) U(46.6 empc)U(85.5)U( 31.3)U( 11.1)U( 19.8)U( 12)U( 17.5)U( 25.4) U(16.2 empc)U(6.56)U( 17.7) U( 4.71 empc) U( 15.9 empc) U( 8.72 empc) U( 24 empc) U( 5.82 empc) U( 25.1 empc) U( 16.8 empc) U( 5.77 empc) U( 9.04 empc) U( 7.95 empc) U( 5.33 empc) U( 27.5 empc)U(29) U( 7.98 empc) U( 35.4 empc) U( 6.79 empc) U( 5.18 empc) U( 4.97 empc) U(1.9 empc) U( 6.97 empc) U( .465 empc)U( 1.45) U( .583 empc) U( 2.8 empc) U( 49 empc) U( 4.91 empc)U( 9.75) U( 1270 empc) U( 25 empc) U( 14.8 empc) U( 8.84 empc) U( 8.94 empc) U( .734 empc) U( 45.2 empc) U( 52.9 empc) U( 3.89 empc) U( 5.5 empc) U( 9.94 empc) U( .589 empc) U( 4.83 empc) U( 19 empc) U( .427 empc) U( 1.03 empc) U( 2.53 empc) U(5.0) (3)  U(3.16)U(2.78)U(2.84)U( .623)U(3.41)U(4.3)U(3.8)U( .909)U(492)U(331)U( 107)U( 40.6)U( 11.5)U( 22)U( 21.2)U(84.1)U( 123)U( 97.6)U( 98.9)U(47.4)U(118)U( 16.7)U( 13.7)U( 15.4)< U( 23.2)U( 26.7)U( 44.5)U(94.3)U(76.3)U( 22.8)U( 25.6)U( 47.3)U( 38.3)U( 31.1)U( 32.5)U(62.9)U( 44.2)U( 86.7)U(164)U( 25.7)U(123)U( 18)U(50)U( 11.2)U( 12.2)U( 22.2)U( 18.6)U( 31.7)U( 76.3)U( 42.5)U( 74.8)Stanton Christiana Road 39 42 26.3 75 39 08.6Chambers Rock Road 39 43 58.4 75 45 34.7U(169)U( 60.4)U( 27.1)U( 30)U( 24.2)U( 16.9)U( 9.03)U(43.7)U( 69.8)U( 18.8)U(31.3)U( 6.64)U( .691)U( 1.81)U( 3.14)U(7.59)U(2.39)U(5.34)U(3.7)U(11.5)U(8.2)U( .858)U( 2.35)U( 3.04)U(4.56)U(9.77)U( .559)U(25.7)U(19.3)U( 17.9)U( .624)U( 2.76)U(4.86)U( 3.38)U( .963)U( 2.39)U( .345) U( 6.69 empc) U( 55 empc) U( 5.56 empc) U( 37.6 empc) U( 26.7 empc) U(23.2 empc) U( 17 empc) U( 159 empc) U( 25.2 empc) U( 297 empc) U( 44.5 empc) U( 46.3 empc) U( 574 empc) U( 314 empc) U( 248 empc) U( 8.04 empc) U( 93.1 empc) U( 66 empc) U(41.6 empc) U( 17.9 empc) U( 29.6 empc) U( 39 empc) U( 28.6 empc) U( 24.1 empc) U( 21.2 empc) U( 9.37 empc) U( 118 empc) U( 198 empc) U( 90.6 empc) U( 91.1 empc) U( 55.6 empc) U( 29 empc) U( 60.7 empc) U( 206 empc) U(51.7 empc) U(27.9 empc) U(1780 empc) U(43.8 empc) U(126 empc) U(174 empc) U(183 empc) U(26.4 empc) U(11.7 empc) U( 7.15 empc) U( 26.8 empc) U( 6.02 empc) U( 4.39 empc) U( 6.81 empc) U( 7.59 empc) U( .768 empc) U( 8.62 empc) U( 6.16 empc) U( 8.29 empc) U( 4.37 empc) U( 3.47 empc) U( 1.45 empc) U( .425 empc) U( 1.19 empc) U( 2.5 empc) U( 3.77 empc) U( 9.53 empc) U( 9.9 empc) U( 5.34 empc) U( 5.24 empc) U( 3.32 empc) U(2.6 empc) U( 3.71 empc) U( 2.39 empc) U( 17.1 empc) U( .95 empc) U( .305 empc) U( .891 empc) U( .557 empc) U( .297 empc) U( 2.55 empc) U( 20.9 empc) U( 5.06 empc) U( .981 empc) U( 7.13 empc) U( 6.1 empc) U( 7.78 empc) U( 4.58 empc) U( 11.9 empc) U( 3.58 empc) U( 9.63 empc) U( 9.18 empc) U( 5.86 empc) U(12.3 empc) U( 4.15 empc) U(17.2 empc) U( 5.26 empc) U( 25.3 empc) U( 26 empc) U( 6.95 empc) U( 278 empc) U( 25.5 empc) U( 4.6 empc) U( 18.6 empc) U( 9.43 empc) U( 12.2 empc) U( 6.05 empc) U( 4.5 empc) U( 5.13 empc) U( 7.93 empc) U( 47.5 empc) U( 8.48 empc) U(1.43 empc) U( .693 empc) U( .944 empc) U( 6.83 empc) U( 6.98 empc) U( 4.78 empc) U( 2.03 empc) U( .832 empc)0Dioxin, Furan, and Coplanar PCB Congener Results U( 1.87 empc) U( .803 empc) U( 3.6 empc) U( 2.94 empc) U(1.99 empc) U(223) (4) U(1350) (4) U(2320) (4) U(1630) (4)U( 40.6 empc) (1,5)U( 33.7 empc) (1,5)U( 33.9 empc) (1,5)U( 29 empc) (1,5) 4. ND=Compound not detected . High detection limit shown in parentheses is attributed to matrix interference for quantitation ion.5. Response was observed for target analyte. Poor baseline integration due to matrix effect resulted in empc (footnote 1) reporting value.1. U(# empc) = Compound not detected. Value in parentheses is an estimated maximum possible concentration (EMPC) detection limit based on an interference.U(<10)2.57 (2)1.39 (2)1.08 (2)2. Response observed above instrumental detection limit. However, value was below calibration range and the 10 ng/g reporting limit. for Assessing Pollutant Bioaccumulation from Selected Delaware Stream Basins, FY '94 Revised Final Report (MRI Project No. 3723-01). PCB Results$Concentrations are in ng/g (ppb) wet% Lipid!Concentrations in pg/g (pptr) wetU( 0)U( .19)U( .491)U( .467)U( 1.22)U( .86)U( .874)U( .254)U( .63)U( .952)U( .819)U( .386)U( 1.25)U( .604)U( 1.05)U( 1.13)U( 3.41)U( 2.24)U( 3.44)U( 2.55)U( 1.3)U( .649)U( 2.73) U( .466)bU( 1.63)U( 2.32)U( 1.53)U( 2.47) U( .51 mpc)U( 3.28)U( 1.21)U( .805)U( .93)U( .993)U( 2.13)U( 1.74)U( 1.87)U( 1.85)U( 2.44)U( .442)U( .317)U(1.23)U( 2.43)U( 1.6)U( .212)U( 3.9)U( 1.26)U( .843)U( .974)U( 1.82)U( 1.96)U( 1.94)U( .926)U( 2.56)U( 1.64)U( 1.16)U( 2.42)U( 1.34)U( 1.39)U( .914)U( 1.69)U( 5.22)U( 4.54)U( 3.47)U( 1.02)U( 1)U( 1.1)U( .545)U( 1.73)U( 3.07)U(3.95)U( 2.92)U( 1.42)U( .951)U( 1.2)U( 1.31)U( .35)U(3.22)U( 14.8)U( 4.05)U( 3.37)U(4.92)U(10.6)U( .45)U( 1.43)U( 4.44)U(3.59)U( 2.82)U( 12.1)U( 8.13)U( 11.4)U( 7.93)U( 6.62)U( 2.45)U( 3.52)U( 7.89)U( 5.5)U( 2.36)U(20)U( 11.8)U( 7.92)U( 7.72)U( 3.32)U( 7.94)U( 16.6)U( 2.34)U( 2.95)U( 27.6)U( 6.59)U( 11.6)U(2.77)o,p'-DDDp,p'-DDDo,p'-DDEp,p'-DDEo,p'-DDTp,p'-DDTU( 4.74)U( 2.94)U( 19.3)U( 4.71)U( 4.6)U( 3.6)U( .823)U( 3.66)U( 7.64)U( 6.65)U( 7.14)U( .948)U( .992)U( 4.89)U( .296)U( .515)U( .291)U( 2.72)U( .407)U( 1.38)U( 1.04)U( 1.08)U( .4)U( .978)U( 1.36)U( 3.13)U( 4.39)U( 1.9)U( 1.95)U( 12.7)U( 4.64)U( 3.12)U( 4.36)U( .645)U( 2.38)U( 3.24)U( 1.18)U( .544)U( 5.46)U( 10.7)U( 4.68)U( 6.56)U( 2.91)U( 19)U( 6.92)U( 4.65)U( 6.51)U( 3.55)U( 4.84)U( 1.76)U( 5.8)U( 11.3)U(1.0)U( 2.15)U( 3.08)U( 20.2)U( 7.35)U(2.32)U( 5.53)U(2.69)U(1.32)U( 7.01)U( 6.6)U( 1.98)U( 10)U( 14.3)U( 14.2)U( 7.99)U( 3.56)U( 4.9)U( 8.93)U( 6.09)U( 5.78)U( 3.96)U( 5.11)U( 8.41)U( 2.52)U( 5.73)U( 5.28)U( 2.09)U( 2.65)U( 2.97)U( 2.2)U( 11)U( 1.93)U( 8.07)U( 13.3)U( 4.19)U( 7.39)U( 5.3)U( 4.53)U( 2.75)U( 3.03)U(2.14)U( 9.07)U( 10.1)U( 9.55)U( 6)U( 4.96)U( 3.02)U( 12.5)U( 2.19)U( 4.24)U( 6.23)U( 3.91)U( 3.23)U( 5.18)U( 5.1)U(1.1)U( 4.41)U( 4.37)U( 2.02)U( 2.26)U( 2.49)U( 1.68)U(1.59)U( 1.47)U( 2.37)U( 5.88)U( 7.67)U( 8.81)U( 12.6)U( 2.79)U( 7.03)U( 4.31)U( 7.86)U( 4.5)U( 7.4)U( 2.22)U( 5.04)U( 1.84)U( 2.61)U( 2.88)U( 1.7)U( 3.58)U( 1.99)U( 1.8)U( 2.01)U( 5.6)U( 6.26)U( 4.27)U( 2.77)U( 5.89)U( 1.77)U( 3.7)U( 3.06)U( 1.86)U( 2.08)U( 1.54)U(1.42)U( 1.35)U( 4.46)U( 5.81)U( 6.68)U( 2.12)U( 2.3)U( 2.8)U( 9.49)U( .938)U( .234)U( .699)U( 5.33)U( 3.82)U( 3.27)U( 5.96)U( 3.86)U( 2.64)U( 5.61)U( 3.53)U( 1.4)U( 2.18)U( 1.29)U( .356)U( .751)U( .929)U( .635)U( 1.58)U( 1.91)U( 1.66)U( .834)U( 1.51)U( 2.46)U( 5.07)U( 2.98)U( 2.05)U(1.09)U( 2.71)U( 3.39)U( 6.9)U( 3.26)U( 3.19)U(3.63)U( .824)U( 3.65)U( 8.03)U( .863)U( 2.62)U( 3.17)U( 4.85)U( 4.08)U( 7.77)U(3.73)U( 1.06)U( 3.34)OFY '94 Toxics in Biota Monitoring Data for the Delaware Estuary and TributariesU( 2.1)U( 2.81)U( 2.63)U( 1.57)U( .552)U( 2.48)U( .288)U(1.27)U(0.914)U( 1.33)U( 2.33)U( 1.46)U( 1.83)U( 3.73)U( 4.03)U( 2.29)U( 1.72)U( .429)U(3.31)U(2.87)U( 1.23)U( .79)U( .586)U( 3.33)U( .614)U( .43)U(3.35)U( 2.31)U( .506)U(2.33)U(2.19)U( 2.07)U( .904)U( 1.24)U( 2.66)U( 5.49)U( .658)U( 4)U(5.35)U( 2.6)U(7.13)U( 4.01)U( 3.93)U( 2.86)U( 4.18)U( 7.05)U( 4.83)U( 3.79)U( 8.1)U(6.23)U( 29.9)U( 4.2)U( 7.08)U( 3.81)U( 9.83)U( 3.94)U( 6.43)U( 1.89)U( 1.44)U( 2.7)U(8.1)U( 1.37)U( 9.79)U( 2.78)U( 4.32)U( 3.5)U( 7.48)U( 9.04)U(3.58)U( 3.63)U( 4.07)U( 4.73)U( 3.11)U( 5.64)U( 5.82)U( 4.57)U( 9.76)U( 2.96)U( 7.71)U( 9.21)U( 3.4)U( 7.09)U( 4.7)U( 4.86)U( 9.84)U( 2)U(4.82)<U( 25.8)U( 6.12)U( 4.06)U( 3.29)U( 8.49)U( 5.55)U( 1.55)U( 6.63)U(2.18)U( 3.42)U(1.96)U( 2.11)U( 3.16)U( 2.57)U( 3.35)U( 1.15)U( 6.02)U( 4.12)U( 6.91)U( 8.36)U( 6.52)U( 2.17)U( 4.15)U( 4.51)U( .522)U( 3.36)U( 2.06)U( 4.76)U( 4.42)U( 21.3)U( 4.87)U( 4.55)U( 8.94)U( 8.71)U( 5.63)U( 6.44)U( 9.93)U( 9.27)U( .861)U( 8.2)U( 10.2)U( 9.82)U( 4.26)U( 4.23)U( 2.68)U( .41)U( 16.1)U( 3.67)U( 3.43)U( 15.5)U( 6.74)U( .826)U( 6.83)U( 3.25)U( 6.98)U( 4.66)U( 3.45)U( 6.17)U( .287)U(3.75)U( 17.2)U( 1.62)U( .305)U( .311)U( 7.19)U( 7.61)U( .962)U( .882)U( 5.66)U( .692)U( 4.98)U( 3.69)U( .301)U( .307)U( 5.97)U( 2.54)U( 11.7)U( 4.59)U( 4.93)U( 8.28)U( 8.26)U( 3.64)U(2.58)U( .935)U( .72)U( .518)U(6.64)U( 3.1)U U( .411) (2)  U( 8.17 empc) U( 4.63 empc) U( 9.75 empc) U( 10.7 empc) U( 13.4 empc) U( 26.9 empc) U( 9.58 empc) U( 12.9 empc) U( 16 empc) U( 8.08 empc) U( 81.9 empc) U( 8.91 empc) U( 8.92 empc) U( 21.1 empc) U( 19.2 empc) U( 15.7 empc)Sample Description U( 20 empc) U( 28.7 empc) U( 13.5 empc) U( 11.4 empc) U( 11.7 empc) U( 11.3 empc) U( 4.67 empc) U( 14.7 empc) U( 12.7 empc) U( 10.2 empc) U( 5.49 empc) U( 10.3 empc) U( 21.4 empc) U( 5.28 empc) U( 9.44 empc)U( 7.59 empc)a U( .178 empc) U( .692 empc) U( 2.48 empc) U( 1.33 empc) U( 1.01 empc) U( .793 empc) U( .77 empc) U( .485 empc) U( .537 empc) U( .188 empc) U( .379 empc) U( .193 empc) U( 1.05 empc) U( .474 empc) U( .134 empc) U( .292 empc) U( .432 empc) U( 1.73 empc) U( .842 empc) U( .481 empc) U( .407 empc) U( 7.32 empc) U( 5.85 empc) U( 7.53 empc) U( 2.29 empc) U( 5.27 empc) U( 1.51 empc) U( 1.53 empc) U( 1.55 empc) U( .943 empc) U( 1.32 empc) U( 1.35 empc) U( 2.76 empc) U( 3.05 empc) U( 1.44 empc) U( .144 empc) U( 1.26 empc) U( .594 empc) U( 1.29 empc) U( 1.2 empc) U( 1.36 empc) U( 1.6 empc) U( 3.75 empc) U( 1.97 empc) U( 2.84 empc) U( .415 empc) U( .307 empc) U( .369 empc) U( 1.12 empc) U( 1.99 empc) U( .51 empc) U( .442 empc) U( 1.48 empc) U( 1.08 empc) U( .377 empc) U( 1.39 empc) U( .887 empc) U( .28 empc) U( .874 empc) U( 1.58 empc) U( .766 empc) U( .688 empc) U( 1.38 empc) U( 1.93 empc) U( .649 empc) U( .988 empc) U( .268 empc) U( 1.98 empc) U( 2.77 empc) U( .84 empc) U( .825 empc) U( 2.23 empc) U( 1.37 empc) U( 2.35 empc) U( 1.07 empc) U( .833 empc) U( 1.62 empc) U( 1.46 empc) U( .728 empc) U( 2.3 empc) U( .44 empc) U( 2.68 empc) U( 4.85 empc) U( 27.6 empc) U( 15.5 empc) U( 7.3 empc) U( 14.3 empc) U( 1.16 empc) U( 5.14 empc) U( .841 empc) U( 2.05 empc) U( 2.44 empc) U( 2.15 empc) U( 6.17 empc) U( 1.96 empc) U( 2.34 empc) U( 1.13 empc) U( 5.44 empc) U( 6.82 empc) U( .927 empc) U( 2.16 empc) U( 1.83 empc) U( 1 empc) U( 16.3 empc) U( 32.4 empc) U( 17.3 empc) U( 13.2 empc) U( 18.7 empc) U( 6.23 empc) U( 5.46 empc) U( 1.68 empc) U( 3.48 empc) U( 2.04 empc) U( 1.8 empc) U( .656 empc) U( .691 empc) U( 1.09 empc) U( 2.52 empc) U( .872 empc) U( 3.36 empc) U( 5.25 empc) U( 3.21 empc) U( 1.06 empc) Moores Lake U( 7.71 empc) U( 4.05 empc) U( 60.6 empc) U( 17.2 empc) U( 2.83 empc) U( .769 empc) U( 3.16 empc) U( 4.55 empc) U( 1.43 empc) U( 3.66 empc) U( 3.93 empc) U( 4.27 empc) U( .883 empc) U( 6 empc) U( 8.67 empc) U( 10.1 empc) U( 15 empc) U( 5.88 empc) U( 8.77 empc) U( 6.08 empc) U( 4.14 empc) U( 13.8 empc) U( 27.1 empc) U( 34.9 empc) U( 1.78 empc) U( 8.07 empc) U( .899 empc) U( 3.11 empc) U( 6.47 empc) U( 2.41 empc) U( 1.86 empc) U( 9.03 empc) U( 6.18 empc) U( 3.67 empc) U( 9.23 empc) U( 4.21 empc) U( 4.88 empc) U( 2.31 empc) U( 15.1 empc) U( 17.4 empc) U( 1.95 empc) U( 3.61 empc) U( .571 empc) U( 4.72 empc) U( 16.1 empc) U( 5.45 empc) U( 5.02 empc) U( 19.5 empc) U( 4.41 empc) U( 3.34 empc) U( 6.88 empc) U( 22.9 empc) U( 24.9 empc) U( 47.3 empc) U( 5.7 empc) U( 4.19 empc) U( 1.69 empc) U( 4.24 empc) U( 4.22 empc) U( 7.77 empc) U( 20.7 empc) U( 12.3 empc) U( 38 empc) U( 32.3 empc) U( 2.88 empc) U( 11 empc) U( 18.5 empc) U( 2.6 empc) U( 2.96 empc) U( .922 empc) U( .905 empc) U( 2.08 empc) U( 2.26 empc) U( 13 empc) U( 9.46 empc) U( 7.45 empc) U( 14.2 empc) U( 1.91 empc) U( 2.46 empc) U( 6.43 empc) U( 7.03 empc) U( 5.9 empc) U( 3.19 empc) U( 8.64 empc) U( 9.27 empc) U( 7.29 empc) U( 7.02 empc) U( 2.81 empc) U( 2.78 empc) U( 1.3 empc) U( 2.67 empc) U( 7.21 empc) U( 8.79 empc) U( 13.3 empc) U( 9.3 empc) U( 2.93 empc) U( 2.86 empc) U( 4.09 empc) U( 1.02 empc) U( 3.5 empc) U( 1.28 empc) U( 5.8 empc) U( .834 empc) U( 1.84 empc) U( 3.68 empc) U( 7.22 empc) U( 4.28 empc) U( 3.45 empc) U( 2.24 empc) U( 7.08 empc) U( 5.69 empc) U( 9.1 empc) U( 4.93 empc) U( 1.88 empc) U( 2.85 empc) U( 1.85 empc) U( 7.82 empc) U( 2.1 empc) U( 4.99 empc) U( 3.1 empc) U( 3.07 empc) U( 4.73 empc) U( 5.42 empc) U( 1.25 empc) U( 21.5 empc) U( 5.81 empc) U( 2.36 empc) U( 22.1 empc) U( 6.4 empc) U( 5.19 empc) U( 6.56 empc) U( 6.03 empc) U( 4.1 empc) U( 8.35 empc) U( 4.36 empc) U( 9.24 empc)@1. U(10)=Compound not detected above reporting limit of 10 ng/g. U(10) (1)U(10) U( 4.56 empc) U( 6.32 empc) U( 8.41 empc) U( 6.91 empc) U( 3.53 empc) U( 2.58 empc) U( 9.77 empc) U( 7.05 empc) U( 8.01 empc) U( 15.4 empc) U( 44.6 empc) U( 7.09 empc) U( 6.84 empc) U( 8.76 empc) U( 8.13 empc) U( 7.1 empc) U( 4.54 empc) U( 4.95 empc) U( 4.01 empc) U( 2.14 empc) U( 3.78 empc) U(8.1 empc) U( 5.38 empc) U( 62.5 empc) U( 7.79 empc) U( 2.59 empc) U( 10.6 empc) U( 3.3 empc) U( 5.66 empc) U( 9.76 empc) U( 5.41 empc) U( 4.42 empc) U( 6.92 empc) U( 4.17 empc) U( 10 empc) U( 33.2 empc) U( 5.36 empc) U( 9.11 empc) U( 1.82 empc) U( 5.22 empc) U( 5.59 empc) U( 7.56 empc) U( 6.27 empc) U( 3.44 empc) U( 4.74 empc) U( 7.37 empc) U( 3.42 empc) U( 2.71 empc) U( 6.44 empc) U( 3.08 empc) U( 7.33 empc)           7"sB'~, \.t/01x2 P3h 4* 4 f5~ %6= a7yI8a19I:3 ;#;<=@LBd4CLDDjE`FxOGg=HUHICJ;JKmLeaMYXNPPOHKPCJQBCR; dS\ V XXiYaZZj[b\\s]k ^^u_m!``xap&bbcw.d&de|ft$ggzhr(iijb4kklo`m<an=bo>ap=aq=^r: ]s9 Zt6 Yu5 Uv1 Sw/Nx*Ny*Mz)H{$E|!A}>~oKiEeAc? I@ 7  dMbP?_*+%(?)(\?MHP LaserJet 8000 Series PSw odXXgs_/, $dCustom page 1CDCustom page 2CDCustom page 3CD"dXX??U} }  } }  } $ }  } } }  I } }  7;;       n ^ B     J                                         ~ P~,A   ( (~  @  0@B@@B@@B@~ 8   ( (~  @  0@@@   ~ T~,A   ( (~  @  0...~ 8   ( (~  @  0<@<@<@~ X~,A   ( (~  @  0@@@nnn~ y,A     ~ @  0@F@@F@@F@F F F ~ F8     ~ @  0@@@~ y,A     ~ @  0~ N8     ~ @  0@@@~ y,A     ~ @  0~ y,A   ( (~  @  0@@@   ~ 8   ( (~  @  0~ y,A   ( (~  @  0@@@BBB~ 8   ( (~  @  0@@@~ y,A   ( (~  @  0@@@bbbBZX   T~ !"#$%&'()*+,-./0123456~ h|,A  ' f g~ @@  0 8@8@8@~ !8 ! !' !f !g~ !@@ ! !0! @ @ @   ~ "l|,A " "' "f "g~ "@@ " "0"L@L@L@ZZZ~ #8 # #' #f #g~ #@@ # #0#@@@~ $p|,A $ $' $f $g~ $@@ $ $0$:@:@:@"""~ % y,A % % % %~ %@ % %0%RRR~ &8 & & & &~ &@ & &0&~ 'y,A ' ' ' '~ '@ ' '0'~ (&8 ( ( ( (~ (@ ( (0(?@?@?@~ )y,A ) ) ) )~ )@ ) )0)@@@:::~ *8 * * * *~ *@ * *0*>@>@>@~ +y,A + + + +~ +@ + +0+;@;@;@666~ ,8 , , , ,~ ,@ , ,0,:@:@:@~ -y,A - - - -~ -@ - -0-;@;@;@JJJ~ .8 . . . .~ .@ . .0.rrr~ /s,A / / /  / ~ /@ / /0/@@@'?@'@}@'Py@'@~ 0^8 0 0 0  0 ~ 0@ 0 0004@'Ȟ@'@'W@'@`@~ 1s,A 1 1 1 1!~ 1@ 1 1012@'2@'3@@'R@'Y@~ 2f8 2 2 2 2!~ 2@ 2 202Z@'@I@'@K@'@'̠@~ 3s,A 3 3 3 3~ 3@ 3 303@'p@'/@@'>@'R@~ 4^8 4 4 4 4~ 4 @ 4 404'@@'A@'`s@'z@~ 50v,A 5 5 5 5~ 5@@ 5  505^'6@'8@@'b@'d@~ 6z,A 6  6  6 6~ 6@ 6 606°@'D@'@F@܉@'@'@@2>@7 I@ ,  dMbP?_*+%"??U} } $} I} m } m } } } m } m ,                                            ~ P~,A   ) )~  @  ~     ~  I@   +η?<@@~ 8   ) )~  @  ~     ~  K@   !rh?A@@~ T~,A   ) )~  @  ~      G@2@  /$??@@~ 8   ) )~  @  ~   ~ O@  /$? >@@@~ X~,A   ) )~  @  ~   @O@  /$? ;@@~ y,A     ~ @  ~    @T@<@  /$? 6@0@~ F8     ~ @  ~    :@6@  /$? 6@`@~ y,A     ~ @  ~   ~ B@  |?5^? ?(@~ N8     ~ @  ~      E@E@  !rh? ~ @~ y,A     ~ @  ~     ~  :@   X9v? ~ @~ y,A   ) )~  @  ?@  ~  ?   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