ࡱ>   I@\p Rick Greene Ba==hKL,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_);_(* \(#,##0.00\);_(* "-"??_);_(@_)0.0 mm/dd/yy 0.000 0.000000000                + ) , *      " ! " ! !  @ !  !  !X     !X !   h   !T !P  H   H "T  D   `iSample Description&Metals ǝPCBs$#Dioxins,Furans,Coplanar PCBsb OC Pesticides PAHsMethods and QA`i  U( 1.82 empc) U( 1.33 empc) U( 1.07 empc) U( .535 empc) U( .377 empc) U( 9.72 empc) U( 2.62 empc) U( 1.12 empc) U( 3.18 empc) U( 7.35 empc) U( 5.52 empc) U( 1.75 empc) U( 1.93 empc) U( 3.7 empc) U( 2.58 empc) U( 1.35 empc) U( .963 empc) U( 2.37 empc) U( 1.55 empc) U( 3.58 empc) U( 2.6 empc) U( 2.11 empc) U( .741 empc) U( 3.71 empc) U( 2.99 empc) U( 1.92 empc) U( .797 empc) U( 1.53 empc) U( 5.18 empc) U( 3.61 empc) U( 3.32 empc) U( 1.4 empc) U( 1.36 empc) U( 3.57 empc) U( 2.51 empc) U( .99 empc) U( 1.95 empc) U( 1.72 empc) U( 2.74 empc) U( 1.79 empc) U( 3.28 empc) U( 3.35 empc) U( 2.15 empc) U( 1.6 empc) U( 5.59 empc) U( 1.29 empc) U( 1.7 empc) U( 6.56 empc) U( 1.71 empc) U( 1.17 empc) U( 4.94 empc) U( 4.22 empc) U( 4.65 empc) U( .779 empc) U( 2.64 empc) U( 23 empc) U( 1.99 empc) U( 6.66 empc) U( 5.08 empc) U( 4.78 empc) U( .92 empc) U( 1.41 empc) U( .998 empc) U( .825 empc) U( 7.02 empc) U( 4.43 empc) U( 2.02 empc) U( 2.34 empc) U( 4.53 empc) U( 1.66 empc) U( 5.15 empc) U( 2.36 empc) U( 2.16 empc) U( 2.67 empc) U( .952 empc) U( 14.5 empc) U( 9.01 empc) U( 8.07 empc) U( 5.4 empc) U( 4.4 empc) U( 4.62 empc) U( 4.09 empc) U( .924 empc) U( 2.18 empc) U( 7.27 empc) U( 5.71 empc) U( 1.43 empc) U( 6.16 empc) U( 4.25 empc) U( 6.26 empc) U( 4.47 empc) U( 3.54 empc) U( 2.59 empc) U( 3.68 empc) U( 3.12 empc) U( 1.94 empc) U( 3.59 empc) U( 10.3 empc) U( .727 empc) U( 3.86 empc) U( 3.03 empc) U( 5.53 empc) U( 6.19 empc) U( 29.2 empc) U( 1.81 empc) U( 5.9 empc) U( 13.2 empc) U( 5.86 empc) U( 17.8 empc) U( 7.4 empc) U( 5.49 empc) U( 15.2 empc) U( 6.37 empc) U( 1.5 empc) U( 1.1 empc) U( 1.45 empc) U( 1.09 empc) U( .876 empc) U( 2.48 empc) U( .511 empc) U( .538 empc) U( .566 empc) U( 1.61 empc) U( .71 empc) U( .487 empc) U( .651 empc) U( .301 empc) U( .66 empc) U( .738 empc) U( 5.62 empc) U( 2.22 empc) U( 1.39 empc) U( 1.85 empc) U( 1.83 empc) U( 2.08 empc) U( 2.94 empc) U( 8.7 empc) U( 4.56 empc) U( 2.73 empc) U( 1.62 empc) U( 7.85 empc) U( .726 empc) U( 1.44 empc) U( 1.42 empc) U( 2.72 empc) U( 1.56 empc) U( 1.84 empc) U( 1.18 empc) U( .905 empc) U( .438 empc) U( .913 empc) U( 1.22 empc) U( .413 empc) U( .552 empc) U( .391 empc) U( .236 empc) U( .454 empc) U( .44 empc) U( .483 empc) U( .693 empc) U( 1.01 empc) U( .882 empc) U( .47 empc) U( .579 empc) U( 1.08 empc) U( .67 empc) U( .938 empc) U( .312 empc) U( 3.13 empc) U( 1.21 empc) U( 1.68 empc) U( .871 empc) U( .366 empc) U( .7 empc) U( .76 empc) U( .518 empc) U( .665 empc) U( 1.14 empc) U( 1.91 empc) U( 1.24 empc) U( 3.48 empc) U( 1.63 empc) U( 2.92 empc) U( .97 empc) U( 6.33 empc) U( 1.78 empc) U( .942 empc) U( 1.54 empc) U( 5.91 empc) U( 1.96 empc) U( .641 empc) U( 8 empc) U( 3.19 empc) U( 2.78 empc) U( .802 empc) U( 3.33 empc) U( .946 empc) U( 1.31 empc) U( 7.04 empc) U( 2.5 empc) U( 1.25 empc) U( .858 empc) U( 5.05 empc) U( 3.17 empc) U( .827 empc) U( .365 empc) U( .453 empc) U( .61 empc) U( .705 empc) U( .486 empc) U( 4.01 empc) U( 3.49 empc) U( 9.4 empc) U( 6.48 empc) U( 3.23 empc) U( 3.11 empc) U( 1.76 empc) U( 5.31 empc) U( 3.36 empc) U( 6.35 empc) U( 2.13 empc) U( 1.69 empc) U( 7.89 empc) U( 7.74 empc) U( 5.95 empc) U( 5.34 empc) U( 10.2 empc) U( 2.79 empc) U( 4.03 empc) U( 15.4 empc) U( 3.85 empc) U( 1.06 empc) U( 9.37 empc) U( 6.55 empc) U( 14.6 empc) U( 17.3 empc) U( 13.6 empc) U( 4.04 empc) U( 4.5 empc) U( 3.78 empc) U( 4.54 empc) U( 5.51 empc) U( 6.89 empc) U( 2.1 empc) U( .708 empc) U( .91 empc) U( .766 empc) U( 2.63 empc) U( 1.52 empc) U( 6.61 empc) U( .436 empc) U( .449 empc) U( 1.16 empc) U( 1.98 empc) U( .488 empc) U( 5.68 empc) U( 3.83 empc) U( 2.46 empc) U( 7.23 empc) U( .791 empc) U( 19.1 empc) U( 4.08 empc) U( 8.16 empc) U( 2.31 empc) U( 2 empc) U( 14.3 empc) U( .816 empc) U( 6.4 empc) U( .898 empc) U( .78 empc) U( .401 empc) U( .922 empc) U( .24 empc) U( 11.4 empc) U( 2.5 cdl) ND(5.0 cdl) U(5.0 cdl)1. U(# empc) = Compound not detected. Value in parentheses is an estimated maximum concentration (empc) detection limit based on an interference.^2. U(#)= Compound not detected. Value in parentheses is an instrumental noise detection limit.U( 11.4 empc) (1) U( 1.44) (2) U( 2.5 cdl) (3) 3. U(# cdl) = Compound not detected. Value in parentheses is a calculated detection limit (cdl) based on the lowest calibration standard. U(2.5 cdl) U(1.14 empc)U(2.5 cdl) (3) U(6.4 empc) (1)  U( .666) (2) QB. Non-Ortho Coplanar PCB Raw Data, pg/g wet weight basis, analyzed by HRGC/HRMS U( .406 empc) U( .329 empc) U( .234 empc) U( .571 empc) U( .596 empc) U( .265 empc) U( .157 empc) U( 3.3 empc) U( 22 empc) U( .74 empc) U( 2.88 empc) U( .77 empc) U( .805 empc) U( .973 empc) U( .806 empc) U( .729 empc) U( 2.54 empc) U( 1.34 empc) U( 4.23 empc) U( 6.94 empc) U( 24.3 empc) U( 21.8 empc) U( 6.75 empc) U( 8.47 empc) U( 4.14 empc) U( 8.36 empc) U( 7.52 empc) U( 3.77 empc) U( 20.8 empc) U( 3.67 empc) U( 4.33 empc) U( .884 empc) U( .666 empc) U( .796 empc) U( 2.39 empc) U( .717 empc) U( .862 empc) U( .653 empc) U( .763 empc) U( .885 empc) U( .734 empc) U( .765 empc) U( 3.2 empc) U( 33.4 empc) U( 49.6 empc) U( 26.8 empc) U( 14.9 empc) U( 4.58 empc) U( 50 empc) U( 15.6 empc) U( 13.3 empc) U( 10.1 empc) U( .807 empc) U( .965 empc) U( .72 empc) U( 2.76 empc) U( .634 empc) U( 7.25 empc) U( 1150 empc) U( 4.71 empc) U( 1.15) (2) U( .535 empc) (1)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 a curve based detection limit in pg/g.U( 2840 empc) (1) U( .484) (2)  p,p'- DDE U( 23.2 empc) U( 3.97 empc) U( 4.3 empc) U( 21.7 empc) U( 4.16 empc) U( 8.58 empc) U(4.62 empc) U( 3.05 empc) U( 7.54 empc) U( 15.7 empc) U( 19.3 empc) U( 19.7 empc) U(41.9empc) U( 48 empc) U( 94 empc) U( 206 empc) U( 160 empc) U( 247 empc) U( 146 empc) U(160empc) U( 28.1 empc) U( 68.8 empc) U( 70.5 empc) U( 18.1 empc) U( 158 empc) U( 192 empc) U( 9.97 empc) U( 44.8 empc) U( 225 empc) U( 259 empc) U( 37.9 empc) U( 9.9 empc) U( 16.4 empc) U( 37 empc) U( 15 empc) U( 19 empc) U( 21.9 empc) U( 4.18 empc) U( 28.4 empc) U( 55.9 empc) U( 7.31 empc) U( 6.41 empc) U( 21.3 empc) U( .945 empc) U( .669 empc) U( 3.76 empc) U( 1.97 empc) U( 4.19 empc) U( 6.25 empc) U( 7.12 empc) U(3.0 empc) U( .98 empc) U( 2.86 empc) U( .704 empc) U( .176 empc) U( 13.4 empc) U( .65 empc) U( 5.69 empc) U( 5.27 empc) U( 13.1 empc) U( 7.09 empc) U( 4.07 empc) U( 4 empc) U( 4.36 empc) U(15.0 empc) U( 8.53 empc) U( 7.34 empc) U( 6.31 empc) U( 7.36 empc) U( 8.6 empc) U( 6.81 empc) U( 4.52 empc) U( 3.65 empc) U( 5.17 empc) U( .192 empc) U( .432 empc) U( .237 empc) U(1.28 empc) U( .82 empc) U( .919 empc) U( .577 empc) U( .683 empc) U( .793 empc) U( .452 empc) U( .737 empc) U( .41 empc) U( .278 empc) U( .56 empc) U( 3.5 empc) U( 5.26 empc) U(12.2 empc) U( 8.52 empc) U( 23.3 empc) U( 15.1 empc) U( .753 empc) U( 5.13 empc) U( 40.8 empc) U( 117 empc) U( 1.59 empc) U(2.01 empc) U( 56.9 empc) U( 60.8 empc) U( 78.9 empc) U( .31 empc) U( 135 empc) U( 108 empc) U( 109 empc) U( 37.6 empc) U( 4.79 empc) U( 5.61 empc) U( 7.59 empc) U( 5.78 empc) U( 22.4 empc) U( 25 empc) U( 7.7 empc) U( 6.88 empc) U( 4.17 empc) U( 5.09 empc) U( 17.1 empc) U( 2.56 empc)U( 13.8 < empc) (1) U(3210) (2)Low Molecular Weight PAHs: High Molecular Weight PAHs: BDelaware Department of Natural Resources and Environmental Control 2. DNREC Laboratory Data Files.MeanMinimumMaximumDatePortion No. of FishLengthWeight Sample ID WaterbodyLocationLatitude LongitudeSampledSpeciesAnalyzed in Sample(cm)(gm) Appoquinimink1.5 mi. from MouthChannel CatfishFillet Skin OffOdessa 39 27 09.0 75 39 19.0 Silver Lake White PerchFillet Skin On BrandywineHagley Rock BassLargemouth Bass ChristinaDelaware EstuaryAugustine BeachMid-Bay 39 00 00.9 75 11 08.8 Blue FishWeakfish MispillionMilford, Above Police Station MurderkillConfl. of Kent C STP White CatfishMcCauleys Pond White ClayAbove Dam at Papermill Rd. White Sucker PCB Results$Concentrations are in ng/g (ppb) wet,A. PCB Congener Data, ng/g wet weight basis!Concentrations in pg/g (pptr) wetGA. Dioxin/Furan Raw Data, pg/g wet weight basis, analyzed by HRGC/HRMS Organochlorine Pesticide Results Concentrations in ng/g (ppb) wet Polyaromatic Hydrocarbon ResultsMetals Results&Concentrations are in units of ppm wetArsenic Cadmium Copper Lead MercurySeleniumZinc (ppm)< 0.02<0.12<0.2<0.02Field IDLipid % 1 Mono3 MonoU( 1.44)U( .329)U( .667)U( 1.01)U( .346)U( .261)U( .592)U( .381)U( .661)U( .256)U( .593)U( .671)U( .427)U( .274)U( .134)U( .885)U( .472)U( .32)U( .304)U( .296)U( .395)U( .373)U( .305)4 Di U( 1.22E-04)U( 2.02)U( .886)U( .365)U( .422)U( .35)U( .838)U( .825)U( 2.56)U( 1.04)U( .398)U( .494)U( .509)U( .408)7 DiU( .352) U( 6.82E-05)U( 1.12)U( .179)U( .203)U( .235)U( .195)U( .295)U( .421)U( .486)U( .467)U( .297)U( .459)U( .192)U( 1.43)U( .221)U( .171)U( .578)U( .154)U( .26)U( .227)8 DiU( .312) U( 6.05E-05)U( .995)U( .438)U( .159)U( .18)U( .208)U( .173)U( .431)U( .414)U( .264)U( .17)U( 1.26)U( .512)U( .196)U( .137)18 TriU( 3.07)U( 2.42)U( .949)U( 1.3)U( 1.14)U( .654)U( .962)U( .5)U( .361)U( 1.05)U( .806)U( .733)U( .364)U( .513)28 TriU( .334)U( .782)U( .688)U( .579)U( .252)U( .217)37 TriU( 1.13)U( 1.82)U( .933)U( .562)U( .77)U( .894)U( .492)U( 2.99)U( .62)U( .357)U( .434)U( .215)42 TetraU( 1.58)U( 1.53)U( 1.96)U( .735)U( .627)U( 1.37)U( .91)U( 1.06)U( 1.33)U(2.77)U( .698)U( 1.18)U( 2.23)44 TetraU( 1.8)U( 1.1)U(1.55)U(2.42)U(2.45)U( 1.17)U( 2.21)47 TetraU( 1.29)U( .738)U( .446)U( .755)U( 1.59)49 TetraU( 1.71)U(2.59)U( .791)U( .998)U( 1.11)U( 2.1)52 TetraU( 1.61)U( 1.73)U( .937)U( 1.97)60 TetraU(1.78)U(2.4)U(1.68)U( .675)U( .934)U(2.37)U( .647)U( 1.36)64 TetraU(3.49)U( .637)U( .744)U( 1.56)66 TetraU( 1.32)U( .845)U( 1.72)U( .42)U( 1.03)U( 1.52)U( .926)U( 1.28)U( .651)U( 1.64)U( .867)U( .614)U( .524)U( .836)U( .635)U( .76)U( .887)U( .643)U( .803)U( .619)U( .583)U( .779)U( 1.86)70 Tetra74 TetraU(0.683)U( .759)80 TetraU( .473)U( .511)U(1.3)82 PentaU( 1.19)U( 1.74)U( .751)U( 1.89)U( 1.78)U( 3.64)U( .959)U( 3.04)U( .786)U( 1.27)U( 1.5)U( .869)U( .892)U( .81)84 Penta86 PentaU( .814)U( 1.22)U( 2.77)U( .631)U( 2.49)U( .881)U( .8)U( .963)U( .763)U( 1.08)U( 2.07)U( .55)U( .536)U( .868)U( 1.02)U( .61)U( .608)U( .552)U( .796)U( 1.34)87 PentaU(5.89)U( 3.45)U( 3.09)U( 1.2)U( 2.58)U( .757)U( 1.15)U( 1.67)91 Penta92 Penta95 PentaU( 3.95)U( 3.55)U( 2.96)U( .785)U( .766)U( .788)U( 1.92)97 PentaU(5.26)U( 1.9)U( 1.79)U( 4.06)U( 3.65)U( .96)U( 1.41)U( .807)U( .787)U( .893)U( .811)99 PentaU( 2.57)U( .682)U( .666)U( .363)U( .988) 101 PentaU(2.43)U( 1.09) 105 PentaU( .727)U( .488)U(2.91)U( .553)U( .502) 110 PentaU( .57) 114 PentaU( .907)U( .51)U( 1.21)U( 2.76)U( .629)U( 2.47)U( .534)U( .865)U( .607)U( .888)U( .591)U( .606)118PentaU( 1.76) 119 PentaU( 2.46)U( .781)U( .58)U( .709)U( .854)U( .677)U( .487)U( .476)U( .906)U( .526)U( .54)U( .49) 120 Penta 123 Penta128 HexaU(1.33)U( .226)U( .561)U( .254)U( .551)U( .396)U( 1.81)U( .237)U( .246)U( .314)U( .257)U( .238)137 HexaU( .37)U( .424)U(.95)U(0.95)U(1.03)U(1.27)U( .942)U( .808)U( .676)U( .405)U( .406) 138,158 Hexa141 HexaU(3.41)U( .641)U(1.37)U( .653)U( .922)U( .662)U( .586)U(1.88)U( .442)U( .615)146 Hexa149 Hexa151 HexaU(1.02)U(1.57)U( 1.88)153 Hexa156 HexaU( .349)U( .575)U( .905)U( .41)U(1.14)U( .366)U(.601)U( .505)157 HexaU(.785)U( .701)U(.705)U(2.1)U(.494)U( .236)U(.997)U(0.803)U(.755)U(.383)U(.315)166 HexaU(1.46)U(2.55)U(.612)U( 2.24)U(.668)U(.491)U( .388)U(.469)167 HexaU(1.34)U(.726)U(.678)U(.437)U(.85)U(.571)U(.903)U(.882)U( .198)U(.634)168 Hexa 170,190 HeptaU( .914)U( .871)U( .903)U(.941)171HeptaU(2.73)U( .831)U( .725)U( .861)U( .752)U( .726)U( .97)U( .977)U( 1.16)U( 1.23)U( 1.24) 174 HeptaU( .938)U( .805)U(1.24)U(1.81) 177 HeptaU(2.21)U( .966)U( 1.31)U( .829)U( .909) 179 HeptaU( .822)U(.867)U(.909)U( .961)U(.97)U(1.29)U( .599)U( .658)U( .837) 180 Hepta 183 HeptaU( .598)U( .856) 185 HeptaU(1.38)U(1.13)U(1.25)U( .772)U( .602)U( .655)U( .506)U( .877)U( .883) 187 HeptaU( .86) 189 HeptaU( .756)U( .34)U( .499)U( .4)U( .858)U( .436)U( .624)U( .847)U( .535)U( .419)U( .587)U( .747) 191 HeptaU( .302)U( .64)U(.402)U( .423)U( .339)U(.455)U( .528)U( .718)U( .453)U(.47)U( .383)U( .285)U( .497)U( .493)U( .633)194 OctaU( .636)U( 1.51)U( 4.38)U( 1.42)U( 2.35)U( 2.22)U( 1.65)U( 1.69)U( 1.39)U( 3.74)U( .945)U( 1.46)U( .898)195 OctaU( 1.66)U( 2.04)U( 5.93)U( 2.74)U( 2.36)U( 3.19)U( 3.01)U( 2.29)U( 1.07)U( 1.75)U( 5.07) 196,203OctaU( .74)U( 4.05)U( 2.18)U( 1.57)U(2.8) U( 3.89)U(1.58)198 OctaU( 2.69)U( 2.05)U( 4.54)200 OctaU( .543)U( .495)U( .38)U( .387)U( .455)201 Octa205 OctaU( .866)U( .566)U( 3.1)U( .84)U( 2.64)206 NonaU( 4.95)U( 1.94)U(4.02)U( 5.47)U( 3.46)U(4.97)U(2.96)U( 1.83)207 NonaU(1.79)U( .826)U( 1)U( 2.09)U( .932)208 NonaU(2.13)U(1.61)209 DecaU( .621)U( .754)Sum of CongenersNotes:Lipid %U( .125)U( .124)U( .123)U( .122)U( .507)U( .185)U( .174)U( .126)U( .622)U( .623)U( .616)U( .609)U( 4.18)U( .626)U( 2.44)U( .604)U( 2.68)U( 2.08)U( .728)U( 2.17)U( 2.31)U( .983)U( 3.36)U( 3.43)U( 2.67)U( 2.12)U( .7)U( .674)U( 1.95)U( .605)U( 2.7)U( 1.25)U( .188)U(4.18)U(.621)U(.624)U( 2.59)U( 2.26)U( .484)U( .479)U( .501)U( .498)U( .496)U( .485)U( .491)U( .504) 127-PePCBU( .953) 126-PePCB 169-HxPCB o,p'- DDD p,p'- DDD o,p'- DDEU( 2.2) o,p'- DDTU( 5.39)U(5.92)U( 1.93)U( 4.61)U( 2.37)U( 1.49) p,p'- DDTU(6.39)U( 3.34)U(7.4)Sum of DDD ,DDE, DDT cis-ChlordaneU(24.8)U(25.2)U(3.74)U( .67)<>trans-ChlordaneU( 9.84)U( 3.57)U( 3.12)U(3.84)U( .39)U( 2.34)U( 2.03)U( 25.2)U( .863)U( .972)cis- Nonachlortrans -Nonachlor OxychlordaneSum of Chlordanes:DicofolU(130)U(113)U(11)DieldrinU( 19.3)U(25.8)U(8.82)U( 29)U( 6.33) Endosulfan IU( 183)U(27.8) U(58)U(2580)U( 205)U(190)U(495)U(62.1)U( 211)U( 32.6)U( 24.9)U(9.64)U(166)U(241)U(35.6)U( 8.45)U( 99.6)U(238)U(133)U( 10.1)U( 27.6)U( 435) Endosulfan IIU( 39.2)U( .917)U( .584)U( 49.3)U( 20.1)U(1.16)U( 2.39)U( 3.17)U( 3.68)U( .776) U( 4.26E-04)U( 2.13)EndrinU( 16)U( 17.9)U(32.1)U( 18.3)U( 12.9)U( 24.6)U(32.9)U( 4.53)U( 31)U( 13.2)U( 4.89)U(20.5)U( 13.4)U( 3.24)U( 2.83)U( 19.2)U(26)U( 37.1)U( 2.73)U( 4.55)U( 13.3)Heptaclor epoxideU( 0)HexachlorobenzeneU( .521)LindaneMirex AcenaphtheneAcenaphthylene AnthraceneBiphenyl1-Chloronaphthalene2-ChloronaphthaleneDimethylnaphthaleneFluorene1-Methylnaphthalene2-MethylnaphthaleneMethylphenanthrene Naphthalene5-Nitroacenaphthalene PhenanthreneTrimethylnaphthaleneTotal LMW PAHsBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(e)pyreneBenzo(g,h,i)peryleneBenzo(k)fluorantheneChryseneDibenzo(a,h)anthracene FluorantheneIndeno(1,2,3-cd)pyrenePyrenePeryleneTotal HMW PAHs Total PAHs+B. PCB Homolog Data, ng/g wet weight basisMonoDi Tri TetraPentaHexaHeptaOctaNonaDeca U( 10.8 empc) U( 24.5 empc) U( 19.2 empc) U( 8.94 empc) U( 9.03 empc) U( 14.7 empc) U( 35.6 empc) U( 20.1 empc) U( 22.7 empc) U( 10.5 empc) U( 11 empc) U( 22.1 empc) U( 13.9 empc) U( 12.6 empc) U( 7.6 empc) U( 13 empc) U( 11.8 empc) U( 12.2 empc) U( 11.5 empc) U( 12.5 empc) U( 10.9 empc) U( 13.5 empc) U( 10.4 empc) U( 14.1 empc) U( 12.1 empc) U( 10.7 empc) U( 6.46 empc) U( .489 empc) U( 1.03 empc) U( 1.37 empc) U( .824 empc) U( .509 empc) U( .562 empc) U( .894 empc) U( 1.32 empc) U( .771 empc) U( .901 empc) U( 1.28 empc) U( .587 empc) U( .379 empc) U( .295 empc) U( .296 empc) U( .256 empc) U( .368 empc) U( .637 empc) U( .23 empc) U( .561 empc) U( 2.24 empc) U( 1.49 empc) U( 2.47 empc) U( 2.65 empc) U( 2.53 empc) U( 2.04 empc) U( 2.21 empc) U( .931 empc) U( .678 empc) U( 9.33 empc) U( 3.94 empc) U( 3.92 empc) U( 2.96 empc) U( 3.47 empc) U( 2.57 empc) U( .961 empc) U( 1.47 empc) U( 2.23 empc) U( 2.07 empc) U( .748 empc) U( .774 empc) U( .385 empc) U( 4.12 empc) U( 2.09 empc) U( 1.05 empc) U( 5.58 empc) U( .586 empc) U( .628 empc) U( .378 empc) U( 1.38 empc) U( .418 empc) U( 2.35 empc) U( 1 empc) U( 2.95 empc) U( .481 empc) U( 3.14 empc) U( .317 empc) U( .254 empc) U( .624 empc) U( 1.73 empc) U( 2.61 empc) U( 3.07 empc) U( 1.26 empc) U( 2.4 empc) U( 2.14 empc) U( .89 empc) U( 1.46 empc) U( 3.21 empc) U( .776 empc) U( 1.11 empc) U( 4.24 empc) U( .633 empc) U( 2.33 empc) U( 3.75 empc) U( 3.82 empc) U( 2.42 empc) U( 1.51 empc) U( 9.53 empc) U( .857 empc) U( 1.2 empc) U( 3.64 empc) U( 1.15 empc)A1. U(<10)=Compound not detected above reporting limit of 10 ng/g.H2. U<# = Compound not detected above instrumental noise shown as < valueU<22 (2)U<15U<21U<36 U<50.07U<10.85 A. MethodsiSamples were collected by the Delaware Department of Natural Resources and Environmental Control (DNREC).TMetals were analyzed by the DNREC's Environmental Services Section (ESS) Laboratory.iOrganic contaminants were analyzed by the Midwest Research Institute (MRI) under contract with the DNREC.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"). WLaboratory methods for metals are described in DNREC ESS Standard Operating Procedures.CLaboratory methods for organic contaminants are fully described in:)Briefly with regard to chemical analyses,Metals other than mercury and zinc were analyzed using Graphite Furnace Atomic Absorption (GFAA). Zinc was analyzed using Inductively Coupled Argon Plasma (ICAP).LMercury was analyzed using Cold Vapor Atomic Absorption Spectrometry (CVAA).Dioxins, 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).B. Quality AssuranceQuality assurance testing for metals included matrix spike and matrix spike duplicate analyses. Results of those analyses are on file at the DNREC ESS Laboratory.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:RData and information in this spreadsheet were obtained from the following sources: Total TCDF Total TCDD Total PECDF Total PECDD Total HXCDF Total HXCDD Total HPCDF Total HPCDD 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-TCDF79-TCB78-TCB81-TCB77-TCB U(10) (1)U(10)1. Midwest Reseach Institute. 1995. Analysis of Fish Tissue and Sediment Samples for PCDDs, PCDFs, Congener-Specific PCBs, Pesticides, PAHs, TOC, and Metals from Selected Delaware Stream Basins, FY '95 Final Report (MRI Project No. 4047-01). Report prepared by the w Midwest Research Institute for the Delaware Department of Natural Resources and Environmental Control, Dover, DE.Midwest Reseach Institute. 1995. Analysis of Fish Tissue and Sediment Samples for PCDDs, PCDFs, Congener-Specific PCBs, Pesticides, PAHs, TOC, and Metals from Selected Delaware Stream Basins, FY '95 Final Report (MRI Project No. 4047-01). 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