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Search EURAS bioconcentration factor (BCF) Gold Standard Database
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863 records found
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#CASSubstance common nameReliability scoreSpeciesSpecies sex,M/F/MF/ndFish weight,gFish length,cmFish ageTemperature,CpHTOC,mg/Lflow-through/static/renewal,S/FT/R/ndExposure concentration,mg/Lfresh/marinek1,d-1Uptake phase duration1,dk2,d-1Elimination phase duration,dT95,dT80,dUptake>T80,y/n/probT50,elimElimination>5xT50,y/n/probTissue analyzedBCFss ww, Cf/Cw (L/kg)BCFss lipid,Cf lipid/Cw (L/kg)BCFk ww,k1/k2BCFk lipid,BCFk ww/lipid%Lipid,%Lipid methodStatisticsReferenceRemarksReason for reliability 3/4
191-20-3naphthalene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.0125marine1450361.4582.0689655171.103448276yes0.477931034yeswhole body7147360.824742999103079.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
291-20-3naphthalene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00134marine1137361.2782.3622047241.25984252yes0.545669291yeswhole body6927134.02061989592309.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
391-57-62-methylnaphthalene2Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.02363marine2659360.6284.8387096772.580645161yes1.117741935yeswhole body292130113.402064288442109.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
491-57-62-methylnaphthalene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00246marine2142360.6852.666666667yes1.155yeswhole body285229402.061863601371219.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
5575-41-71,3-dimethylnaphthalene2Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.02667marine2909360.3588.5714285714.571428571yes1.98nowhole body476149082.474238313856969.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
6575-41-71,3-dimethylnaphthalene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00274marine1854360.4786.3829787233.404255319yes1.474468085yeswhole body342635319.587633979410209.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
72027-17-02-isopropylnaphthalene2Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.0064marine4188360.09833.3333333317.77777778yes7.7nowhole body12405127886.5979465364797489.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
82027-17-02-isopropylnaphthalene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.0007marine3746360.16818.7510yes4.33125nowhole body13420138350.5155238592459709.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
985-01-8phenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00112marine1783360.883.752yes0.86625yeswhole body162316731.958762229229779.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
1085-01-8phenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00012marine680360.8483.5714285711.904761905yes0.825yeswhole body7007216.49484581083519.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
11883-20-59-methylphenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00135marine623360.7284.1666666672.222222222yes0.9625yeswhole body5956134.02061986689289.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
12883-20-59-methylphenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00014marine290360.883.752yes0.86625yeswhole body2242309.2783513637569.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
133674-75-79-ethylphenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.00051marine731360.5685.3571428572.857142857yes1.2375yeswhole body8759020.6185571306134669.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
143674-75-79-ethylphenanthrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.000062marine263360.6184.9180327872.62295082yes1.136065574yeswhole body2983072.16494842844159.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
15129-00-0pyrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.0001marine116361.1982.5210084031.344537815yes0.582352941yeswhole body53546.39175269710009.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
16129-00-0pyrene1Cyprinodon variegatus
(sheepshead minnow)
MF2.474.7adult25ndndFT0.000012marine129360.8983.3707865171.797752809yes0.778651685yeswhole body50515.463917514514959.7ndfirst order kinetic model[8] Jonsson G, Bechmann RK Bamber SD Baussant T. Bioconcentration, biotransformation, and elimination of polycyclic aromatic hydrocarbons in sheepshead minnows (Cyprinodon Variegatus) exposed to contaminated seawater. 2004; 23, (6): 1538-1548. fish exposed to mixture of 8 PAHs (total concentration 0.00757 mg/L); BCFss = Cf/Cw with Cf and Cw average concentrations from sampling days 4, 7 and 36
1787-61-61,2,3-trichlorobenzene2Poecilia reticulata
(guppy)
MF0.337ndnd23.507-AugndFT0.0212freshwater158460.43246.9444444443.703703704yes1.604166667nowhole body79456233666.66666725966.8345914.1205762ndfirst order kinetic model[93] de Wolf W, Seinen W Hermens JLM. Biotransformation and toxicokinetics of trichloroanilines in fish in relation to their hydrophobicity. 1993; 25, 110-117. fish exposed to mixture of 6 chlorobenzenes and chloroanilines
18634-67-32,3,4-trichloroaniline2Poecilia reticulata
(guppy)
MF0.337ndnd23.507-AugndFT0.221freshwater146464.840.6250.333333333yes0.144375yeswhole body1007413052260.0513.49527665ndfirst order kinetic model[93] de Wolf W, Seinen W Hermens JLM. Biotransformation and toxicokinetics of trichloroanilines in fish in relation to their hydrophobicity. 1993; 25, 110-117. fish exposed to mixture of 6 chlorobenzenes and chloroanilines
19636-30-62,4,5-trichloroaniline2Poecilia reticulata
(guppy)
MF0.337ndnd23.507-AugndFT0.113freshwater163263.8440.781250.416666667yes0.18046875yeswhole body21415854253147.78037413.50157729ndfirst order kinetic model[93] de Wolf W, Seinen W Hermens JLM. Biotransformation and toxicokinetics of trichloroanilines in fish in relation to their hydrophobicity. 1993; 25, 110-117. fish exposed to mixture of 6 chlorobenzenes and chloroanilines
20634-93-52,4,6-trichloroaniline2Poecilia reticulata
(guppy)
MF0.337ndnd23.507-AugndFT0.107freshwater158460.69644.3103448282.298850575yes0.995689655nowhole body21416222275.86206917249.758313.19358816ndfirst order kinetic model[93] de Wolf W, Seinen W Hermens JLM. Biotransformation and toxicokinetics of trichloroanilines in fish in relation to their hydrophobicity. 1993; 25, 110-117. fish exposed to mixture of 6 chlorobenzenes and chloroanilines
21634-91-33,4,5-trichloroaniline2Poecilia reticulata
(guppy)
MF0.337ndnd23.507-AugndFT0.114freshwater196863.1240.9615384620.512820513yes0.222115385yeswhole body2291622630.76923084467.7191814.11837238ndfirst order kinetic model[93] de Wolf W, Seinen W Hermens JLM. Biotransformation and toxicokinetics of trichloroanilines in fish in relation to their hydrophobicity. 1993; 25, 110-117. fish exposed to mixture of 6 chlorobenzenes and chloroanilines
22328-84-73,4-dichlorobenzotrifluoride1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.000001freshwaternd90nd0ndndndndndwhole body150015822.78481ndnd9.48ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 8, 21, 38, 58, 90; lipid % is calculated as average after equilibrium
236639-30-12,4,5-trichlorotoluene1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.00000013freshwaternd90nd0ndndndndndwhole body480049079.7546ndnd9.78ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 21, 38, 58, 90; lipid % is calculated as average after equilibrium
2454135-80-72,3,4-trichloroanisole1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.0000009freshwaternd90nd0ndndndndndwhole body9209406.952965ndnd9.78ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 21, 38, 58, 90; lipid % is calculated as average after equilibrium
251825-31-61,4-dichloronaphthalene2Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.0000017freshwaternd90nd0ndndndndndwhole body560052582.15962ndnd10.65ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277.
2651892-26-32,4-dichlorodiphenyl-ether2Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.0000027freshwaternd90nd0ndndndndndwhole body930080172.41379ndnd11.6ndBCF=Cf/Cw on day 90, no equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277.
27108-36-11,3-dibromobenzene1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.0000054freshwaternd90nd0ndndndndndwhole body6006134.969325ndnd9.78ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 21, 38, 58, 90; lipid % is calculated as average after equilibrium
28626-39-11,3,5-tribromobenzene1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.00000032freshwaternd90nd0ndndndndndwhole body500049164.20846ndnd10.17ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 38, 58, 90; lipid % is calculated as average after equilibrium
29615-54-31,2,4-tribromobenzene1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.00000058freshwaternd90nd0ndndndndndwhole body430042281.21927ndnd10.17ndBCF=Cf/Cw, average after equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated as average BCFss from day 38, 58, 90; lipid % is calculated as average after equilibrium
30636-28-21,2,4,5-tetrabromobenzene1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.00000009freshwaternd90nd0ndndndndndwhole body630054310.34483ndnd11.6ndBCF=Cf/Cw on day 90, no equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated on day 90 (no equilibrium but exposure > 60 d); lipid % is the measured value from day 90
312050-68-24,4'-dichlorobiphenyl1Oncorhynchus mykiss
(rainbow trout)
nd277-746ndnd15ndndFT0.000019freshwaternd90nd0ndndndndndwhole body380032758.62069ndnd11.6ndBCF=Cf/Cw on day 90, no equilibrium[219] Oliver BG, Niimi AJ. Rainbow trout bioconcentration of some halogenated aromatics from water at environmental concentrations. 1984; 3, 271-277. fish exposed to mixture of 5 halogenated aromatics; no elimination phase; BCFss = Cf/Cw calculated on day 90 (no equilibrium but exposure > 60 d); lipid % is the measured value from day 90
32120-82-11,2,4-trichlorobenzene2Poecilia reticulata
(guppy)
MF0.48nd1-1.5 y20-227.8-8.2ndFT0.2freshwater49216.90.4956.122448983.265306122yes1.414285714nowhole body1139nd1004.081633ndndndBCF=Cf/Cw at steady state; first order kinetic model[224] van Eck JMC, Koelmans AA Deneer JW. Uptake and elimination of 1,2,4-trichlorobenzene in the guppy (poecilia reticulata) at sublethal and lethal aqueous concentrations. 1997; 34, (1): 2259-2270.
3355-38-9fenthion2Oryzias latipes
(medaka)
MF0.21-0.332.3-2.8nd206.9-7.0ndFT0.0011freshwaternd64.820.6250.333333333yes0.144375yeswhole body154ndndndndndBCF=Cf/Cw at steady state; first order kinetic model for k2[177] Tsuda T, Kojima M Harada H Nakajima A Aoki S. Accumulation and excretion of fenthion, fenthion sulfoxide and fenthion sulfone by killifish (Oryzias latipes). 1996; 113, (1): 45-49.
3455-38-9fenthion2Oryzias latipes
(medaka)
MF0.21-0.332.3-2.8nd206.9-7.0ndFT0.0071freshwaternd64.820.6250.333333333yes0.144375yeswhole body170ndndndndndBCF=Cf/Cw at steady state; first order kinetic model for k2[177] Tsuda T, Kojima M Harada H Nakajima A Aoki S. Accumulation and excretion of fenthion, fenthion sulfoxide and fenthion sulfone by killifish (Oryzias latipes). 1996; 113, (1): 45-49.
353761-41-9fenthion sulfoxide2Oryzias latipes
(medaka)
MF0.21-0.332.3-2.8nd206.9-7.0ndFT0.0095freshwaternd65.7620.5208333330.277777778yes0.1203125yeswhole body1.7ndndndndndBCF=Cf/Cw at steady state; first order kinetic model for k2[177] Tsuda T, Kojima M Harada H Nakajima A Aoki S. Accumulation and excretion of fenthion, fenthion sulfoxide and fenthion sulfone by killifish (Oryzias latipes). 1996; 113, (1): 45-49.
363761-42-0fenthion sulfone2Oryzias latipes
(medaka)
MF0.21-0.332.3-2.8nd206.9-7.0ndFT0.0077freshwaternd63.8420.781250.416666667yes0.18046875yeswhole body3.2ndndndndndBCF=Cf/Cw at steady state; first order kinetic model for k2[177] Tsuda T, Kojima M Harada H Nakajima A Aoki S. Accumulation and excretion of fenthion, fenthion sulfoxide and fenthion sulfone by killifish (Oryzias latipes). 1996; 113, (1): 45-49.
3733857-26-02,7-dichlorodibenzo-p-dioxin2Poecilia reticulata
(guppy)
F0.079ndnd22ndndFT0.0066freshwater54381.51.721.066666667yes0.462nowhole body363nd3624826.6666677.5ndBCFss = Cf/Cw; k2 was estimated using 1st order kinetic modeling, k1 was derived from k1 = BCF x k2[98] Gobas FAPC, Schrap SM. Bioaccumulation of some polychlorinated dibenzo-p-dioxins and octachlorodibenzofuran in the guppy (poecilia reticulata). 1990; 20, (5): 495-512. Not enough info on exposure conditions, water quality, fish
3839227-58-21,2,4-trichlorodibenzo-p-dioxin2Poecilia reticulata
(guppy)
F0.079ndnd22ndndFT0.011freshwater60180.911.73.2967032971.758241758yes0.761538462nowhole body660nd660.43956048805.8608067.5ndBCFss = Cf/Cw; k2 was estimated using 1st order kinetic modeling, k1 was derived from k1 = BCF x k2[98] Gobas FAPC, Schrap SM. Bioaccumulation of some polychlorinated dibenzo-p-dioxins and octachlorodibenzofuran in the guppy (poecilia reticulata). 1990; 20, (5): 495-512. Not enough info on exposure conditions, water quality, fish
3915862-07-42,4,5-trichlorobiphenyl3Poecilia reticulata
(guppy)
F0.079ndnd22ndndFT0.001freshwater89080.0631.747.6190476225.3968254no11nowhole body14125nd14126.98413188359.78847.5ndBCFss = Cf/Cw; k2 was estimated using 1st order kinetic modeling, k1 was derived from k1 = BCF x k2[98] Gobas FAPC, Schrap SM. Bioaccumulation of some polychlorinated dibenzo-p-dioxins and octachlorodibenzofuran in the guppy (poecilia reticulata). 1990; 20, (5): 495-512. Not enough info on exposure conditions, water quality, fish. According to authors, steady state was reached, although k2-value suggests non-steady state.
40106-46-71,4-dichlorobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.057; 0.101; 0.233freshwater11241.4442.0833333331.111111111yes0.48125nowhole body780.2577.777777782508.9605733.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
41106-37-61,4-dibromobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.022; 0.0308; 0.0453freshwater27241.3242.2727272731.212121212yes0.525nowhole body2200.78206.06060616647.1163253.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
4287-61-61,2,3-trichlorobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.00385; 0.0808; 0.1322freshwater47041.142.7272727271.454545455yes0.63nowhole body4301.2427.272727313782.99123.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
43634-90-21,2,3,5-tetrachlorobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.0084; 0.012; 0.0201freshwater63140.4846.253.333333333yes1.44375nowhole body13204.31314.58333342405.913983.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
44615-54-31,2,4-tribromobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.0073; 0.0108; 0.0177freshwater104040.5845.1724137932.75862069yes1.194827586nowhole body18006.641793.10344857842.046723.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
45118-74-1hexachlorobenzene2Gambusia affinis
(mosquito fish)
MF0.192.75adult23.17.6ndFT0.0012; 0.0021; 0.0037freshwater185040.4946.122448983.265306122yes1.414285714nowhole body3730103775.510204121790.65173.120mL hexane excract solution first evaporated to dryness, then gone under stream of nitrogen at room temperature in a pre-weigheted baker. Estimation done after weighing to a steady weight.BCF = k1/k2, k1 and k2 were calculated using 1st order kinetics[178] Chaisuksant Y, Yu Q Connell DW. Bioconcentration of bromo- and chlorobenzenes by fish (Gambusia affinis). 1997; 31, (1): 61-68. Average of 3 steady state kinetic values at 3 different exposure concentrations
4685-68-7benzyl butyl phthalate2Lepomis macrochirus
(bluegill sunfish)
nd9.7264nd228.23ndFT0.034freshwaternd3.27nd0ndndndndndwhole body12.4ndndnd7.9ndBioconcentration was determined as BCFss = Cf/Cw[207] Carr KH, Coyle GT Kimerle RA. Bioconcentration of [14C]Butyl benzyl phthalate in bluegill sunfish (Lepomis macrochirus). 1997; 16, (10): 2200-2203. Not all details on water quality were reported. No elimination phase, but evidence that equilibrium was reached. No series of fish sampling during exposure performed (only at termination of exposure).
4776-44-8heptachlor2Leiostomus xanthurus
(spot)
ndnd3.2juvenile25ndndFT0.00014marinend24nd28ndndndndndwhole body2430ndndndndndBCF=Cf/Cw[388] Schimmel SC, Patrick Jr. JM Forester J. Heptachlor: uptake, depuration, retention, and metabolism by spot, Leiostomus xanthurus. 1976; 2, 169-178.
485103-74-2trans-chlordane2Leiostomus xanthurus
(spot)
ndnd3.2juvenile25ndndFT0.00004marinend24nd28ndndndndndwhole body3300ndndndndndBCF=Cf/Cw[388] Schimmel SC, Patrick Jr. JM Forester J. Heptachlor: uptake, depuration, retention, and metabolism by spot, Leiostomus xanthurus. 1976; 2, 169-178.
4957-74-9chlordane2Cyprinodon variegatus
(sheepshead minnow)
ndndndegg/embryo30ndndFT0.0013marinend28nd0ndndndndndwhole body8460ndndndndndBCF=Cf/Cw[389] Parrish PR, Schimmel SC Hansen DJ Patrick Jr. JM Forester J. Chlordane: effects on several estuarine organisms. 1976; 1, 485-494.
5027323-18-8aroclor 12542Pimephales promelas
(fathead minnow)
Mndndembryo/adult24ndndFT0.00052freshwaternd240nd0ndndndndndwhole body156000ndndndndnd[398] Nebeker AV, Puglisi FA DeFoe DL. Effect of polychlorinated biphenyl compounds on survival and reproduction of the fathead minnow and flagfish. 1974; 103, (3): 562-568.
5127323-18-8aroclor 12542Pimephales promelas
(fathead minnow)
Fndndembryo/adult24ndndFT0.00052freshwaternd240nd0ndndndndndwhole body201000ndndndndnd[398] Nebeker AV, Puglisi FA DeFoe DL. Effect of polychlorinated biphenyl compounds on survival and reproduction of the fathead minnow and flagfish. 1974; 103, (3): 562-568.
5227323-18-8aroclor 12542Pimephales promelas
(fathead minnow)
Mndndembryo/adult24ndndFT0.00023freshwaternd240nd0ndndndndndwhole body196000ndndndndnd[398] Nebeker AV, Puglisi FA DeFoe DL. Effect of polychlorinated biphenyl compounds on survival and reproduction of the fathead minnow and flagfish. 1974; 103, (3): 562-568.
5327323-18-8aroclor 12542Pimephales promelas
(fathead minnow)
Fndndembryo/adult24ndndFT0.00023freshwaternd240nd0ndndndndndwhole body235000ndndndndnd[398] Nebeker AV, Puglisi FA DeFoe DL. Effect of polychlorinated biphenyl compounds on survival and reproduction of the fathead minnow and flagfish. 1974; 103, (3): 562-568.
54298-04-4disulfoton2Cyprinus carpio
(carp)
nd2511nd236ndFT0.009freshwaternd56nd4ndndndndndwhole body369ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. Tested as pure compound; average of 4 steady state BCFs (days 7, 14, 28, 56)
55298-04-4disulfoton2Cyprinus carpio
(carp)
nd2511nd236ndFT0.001freshwaternd56nd4ndndndndndwhole body397ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
56298-04-4disulfoton2Cyprinus carpio
(carp)
nd2511nd236ndFT0.01freshwaternd56nd4ndndndndndwhole body496ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
5706.7.2497disulfoton sulfoxide2Cyprinus carpio
(carp)
nd2511nd236ndFT0.006freshwaternd56nd4ndndndndndwhole body<1ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
5806.7.2497disulfoton sulfoxide2Cyprinus carpio
(carp)
nd2511nd236ndFT0.06freshwaternd56nd4ndndndndndwhole body<1ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
5905.6.2497disulfoton sulfone2Cyprinus carpio
(carp)
nd2511nd236ndFT0.003freshwaternd56nd4ndndndndndwhole body<1ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
6005.6.2497disulfoton sulfone2Cyprinus carpio
(carp)
nd2511nd236ndFT0.03freshwaternd56nd4ndndndndndwhole body4.8ndndndndnd[400] Takase I, Oyama H. Uptake and bioconcentration of disulfoton and its oxidation compounds in carp, Cyprinus carpio L. 1985; 10, (1): 47-53. tested as mixture, average of 5 steady state BCFs (days 3, 7, 14, 28, 56)
6177-47-4hexachloropentadiene2Pimephales promelas
(fathead minnow)
ndndnd1 d257.2-7.7ndFT0.0037freshwaternd30nd0ndndndndndwhole body<11ndndndndndBCF=Cf/Cw[465] Spehar RL, Veith GD DeFoe DL Bergstedt BV. Toxicity and bioaccumulation of hexachlorocyclopentadiene, hexachloronorbornadiene and heptachloronorbornene in larval and early juvenile fathead minnows, Pimephales promelas. 1979; 21, 576-583. exposure concentration close to acute LC50, but no negative effects observed in 30d study
6228680-44-6hexachloronorbornadiene3Pimephales promelas
(fathead minnow)
ndndnd1 d257.2-7.7ndFT0.0384freshwaternd30nd0ndndndndndwhole body6400ndndndndndBCF=Cf/Cw[465] Spehar RL, Veith GD DeFoe DL Bergstedt BV. Toxicity and bioaccumulation of hexachlorocyclopentadiene, hexachloronorbornadiene and heptachloronorbornene in larval and early juvenile fathead minnows, Pimephales promelas. 1979; 21, 576-583. negative effects observed at exposure concentration
632440-02-0heptachloronorbornene3Pimephales promelas
(fathead minnow)
ndndnd1 d257.2-7.7ndFT0.04freshwaternd30nd0ndndndndndwhole body11200ndndndndndBCF=Cf/Cw[465] Spehar RL, Veith GD DeFoe DL Bergstedt BV. Toxicity and bioaccumulation of hexachlorocyclopentadiene, hexachloronorbornadiene and heptachloronorbornene in larval and early juvenile fathead minnows, Pimephales promelas. 1979; 21, 576-583. negative effects observed at exposure concentration
6415087-24-83-benzylidene camphor2Pimephales promelas
(fathead minnow)
MF95-33623.7-32.8adult257.2-7.9ndR0.0005freshwaternd21nd0ndndndndndwhole body399ndndndndndBCF=Cf/Cw[466] Kunz PY, Gries T Fent K. The ultraviolet filter 3-benzylidene camphor adversely affects reproduction in fathead minnows (Pimephales promelas). 2006; 93, (2): 311-321. concentration decreasing during every renewal to >18% of nominal ones, medians taken for calculations, whole body minus gonads
6515087-24-83-benzylidene camphor2Pimephales promelas
(fathead minnow)
MF95-33623.7-32.8adult257.2-7.9ndR0.003freshwaternd21nd0ndndndndndwhole body102ndndndndndBCF=Cf/Cw[466] Kunz PY, Gries T Fent K. The ultraviolet filter 3-benzylidene camphor adversely affects reproduction in fathead minnows (Pimephales promelas). 2006; 93, (2): 311-321. concentration decreasing during every renewal to >18% of nominal ones, medians taken for calculations, whole body minus gonads
6615087-24-83-benzylidene camphor2Pimephales promelas
(fathead minnow)
MF95-33623.7-32.8adult257.2-7.9ndR0.033freshwaternd21nd0ndndndndndwhole body230ndndndndndBCF=Cf/Cw[466] Kunz PY, Gries T Fent K. The ultraviolet filter 3-benzylidene camphor adversely affects reproduction in fathead minnows (Pimephales promelas). 2006; 93, (2): 311-321. concentration decreasing during every renewal to >18% of nominal ones, medians taken for calculations, whole body minus gonads
6715087-24-83-benzylidene camphor2Pimephales promelas
(fathead minnow)
MF95-33623.7-32.8adult257.2-7.9ndR0.074freshwaternd21nd0ndndndndndwhole body493ndndndndndBCF=Cf/Cw[466] Kunz PY, Gries T Fent K. The ultraviolet filter 3-benzylidene camphor adversely affects reproduction in fathead minnows (Pimephales promelas). 2006; 93, (2): 311-321. concentration decreasing during every renewal to >18% of nominal ones, medians taken for calculations, whole body minus gonads
6815087-24-83-benzylidene camphor2Pimephales promelas
(fathead minnow)
MF95-33623.7-32.8adult257.2-7.9ndR0.285freshwaternd21nd0ndndndndndwhole body344ndndndndndBCF=Cf/Cw[466] Kunz PY, Gries T Fent K. The ultraviolet filter 3-benzylidene camphor adversely affects reproduction in fathead minnows (Pimephales promelas). 2006; 93, (2): 311-321. concentration decreasing during every renewal to >18% of nominal ones, medians taken for calculations, whole body minus gonads
69108-70-31,3,5-trichlorobenzene2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.00267freshwaternd56nd0ndndyndndwhole body53713840.20619ndnd3.88Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
70608-93-5pentachlorobenzene2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.000313freshwaternd56nd0ndndyndndwhole body5656171914.8936ndnd3.29Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
71208-96-8acenaphthylene2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.00455freshwaternd28nd0ndndyndndwhole body27111630.90129ndnd2.33Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
726165-51-11,4-dimethyl-2-(1-phenylethyl)benzene2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.0000947freshwaternd42nd0ndndyndndwhole body72322110.09174ndnd3.27Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
735707-44-84-ethylbiphenyl2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.000193freshwaternd42nd0ndndyndndwhole body66720778.8162ndnd3.21Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
7492-86-44,4'-dibromobiphenyl2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.0000107freshwaternd56nd0ndndyndndwhole body8350309259.2593ndnd2.7Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
7550-29-3ddt2Cyprinus carpio
(common carp)
nd5.96-15.957.7-10.6yearlings25ndndFT0.00000548freshwaternd56nd0ndndyndndwhole body19600612500ndnd3.2Bligh & Dyer 1959BCF=Cf/Cw[467] Yakata N, Sudo Y Tadokoro H. Influence of dispersants on bioconcentration factors of seven organic compounds with different lipophilicities and structures. 2006; 64, 1885-1891. also data available for tests with dispersants added, not significantly different from values reported here
76206-44-0fluoranthene3Pimaphales promelas
(fathead minnow)
ndndnd4 d22.17.6ndFT0.0168freshwater8476815.7110.5253940460.280210158yes0.121366025yeswhole body14836nd14845.53415ndndndtwo-component uptake and elimination model[472] Cho E, Bailer AJ Oris JT. Effect of methyl tert-butyl ether on the bioconcentration and photoinduced toxicity of fluoranthene in fathead minnow larvae (Pimephales promelas). 2003; 37, 1306-1310. Concentration too close to LC50
7766230-04-4s-fenvalerate3Cyprinus carpio
(common carp)
ndFeb-80ndnd24ndndR0.0005-0.001freshwaternd7nd25ndndprob5yeswhole body747-1494ndndndndndBCF=Cf/Cw[401] Ohkawa H, Kikuchi R Miyamoto J. Bioaccumulation and biodegradation of the (S)-acid isomer of fenvalerate (Sumicidin) in an aquatic model ecosystem. 1980; 5, 11-22. BCF calculated with minimum and maximum measured concentrationConcentration too close to LC50, information for assessment missing, no flow-through and no TOC/DOC data
7850-29-3ddt3Cyprinus carpio
(common carp)
ndFeb-80ndnd24ndndR0.00025-0.0008freshwaternd7nd25ndndndndndwhole body21625-6920ndndndndndBCF=Cf/Cw[401] Ohkawa H, Kikuchi R Miyamoto J. Bioaccumulation and biodegradation of the (S)-acid isomer of fenvalerate (Sumicidin) in an aquatic model ecosystem. 1980; 5, 11-22. BCF calculated with minimum and maximum measured concentrationConcentration too close to LC50, information for assessment missing, no flow-through and no TOC/DOC data
79119168-77-3tebufenpyrad2Cyprinus carpio
(common carp)
nd13-24ndnd25-25.97.3-7.8ndFT0.00118freshwaternd28nd14ndndprob0.5yeswhole body13.5ndndndndndBCF=Cf/Cw, average after equilibrium[403]
8026306-61-62,4,6-trichloro-4'-aminophenyl ether4Cyprinus carpio
(common carp)
nd26.2-34.309.5.2011nd23ndndFT0.0039freshwaternd14nd0ndndprobndndmuscle90ndndndndndBCF=Cf/Cw[404] Tsuda T, Aoki S Kojima M Harada H. Accumulation and metabolism of 2,4,6-trichlorophenyl-4'-aminophenyl ether by carp. 1990; 96, (1): 17-21. No info on solubility and acute toxicity
811912-24-9atrazine4Tilapia sparmanii
(banded tilapia)
nd7115.6nd23ndndFT0.32freshwaternd3nd0ndndndndndmuscle2.5ndndndndndBCF=Cf/Cw[405] du Preez HH, van Vuren JHJ. Bioconcentration of atrazine in the banded tilapia, Tilapia sparrmanii. 1992; 101, (3): 651-655. Concentration too close to LC50, information for assessment missing, not clear whether equilibrium was reached
821912-24-9atrazine4Tilapia sparmanii
(banded tilapia)
nd8516.6nd23ndndFT1.45freshwaternd3nd0ndndndndndmuscle5.1ndndndndndBCF=Cf/Cw[405] du Preez HH, van Vuren JHJ. Bioconcentration of atrazine in the banded tilapia, Tilapia sparrmanii. 1992; 101, (3): 651-655. Concentration too close to LC50, information for assessment missing, not clear whether equilibrium was reached
831912-24-9atrazine4Tilapia sparmanii
(banded tilapia)
nd7716.2nd23ndndFT4.76freshwaternd3nd0ndndndndndmuscle1.4ndndndndndBCF=Cf/Cw[405] du Preez HH, van Vuren JHJ. Bioconcentration of atrazine in the banded tilapia, Tilapia sparrmanii. 1992; 101, (3): 651-655. Concentration too close to LC50, information for assessment missing, not clear whether equilibrium was reached
841912-24-9atrazine4Tilapia sparmanii
(banded tilapia)
nd7715.8nd23ndndFT6.67freshwaternd3nd0ndndndndndmuscle0.9ndndndndndBCF=Cf/Cw[405] du Preez HH, van Vuren JHJ. Bioconcentration of atrazine in the banded tilapia, Tilapia sparrmanii. 1992; 101, (3): 651-655. Concentration too close to LC50, information for assessment missing, not clear whether equilibrium was reached
851461-22-9tri-n-butyltin chloride2Carassius auratus
(goldfish)
nd1.6-2.93.5-4.0nd237.1-7.2ndFT0.00013freshwaternd28nd0ndndprobndndwhole body1976ndndndndndBCF=Cf/Cw, average after equilibrium[406] Tsuda T, Aoki S Kojima M Harada H. Accumulation of tri-n-butyltin chloride and triphenyltin chloride by oral and via gill intake of goldfish (Carassius auratus). 1991; 99, (1/2): 69-72.
86639-58-7triphenyltin chloride2Carassius auratus
(goldfish)
nd1.6-2.93.5-4.0nd237.1-7.2ndFT0.00014freshwaternd28nd0ndndprobndndwhole body1384ndndndndndBCF=Cf/Cw, average after equilibrium[406] Tsuda T, Aoki S Kojima M Harada H. Accumulation of tri-n-butyltin chloride and triphenyltin chloride by oral and via gill intake of goldfish (Carassius auratus). 1991; 99, (1/2): 69-72.
87333-41-5diazinon2Cyprinus carpio
(common carp)
nd24.4-34.910.0-10.8nd25ndndFT0.0015-0.0024freshwaternd7nd3ndndndndndmuscle20.9ndndndndndBCF=Cf/Cw, average after equilibrium, k2: 2nd order kinetics[407] Tsuda T, Aoki S Kojima M Harada H. Bioconcentration and excretion of diazinon, IBP, malathion and fentrothion by carp. 1990; 96, (1): 23-26.
8813286-32-3ibp2Cyprinus carpio
(common carp)
nd24.4-34.910.0-10.8nd25ndndFT0.005-0.0083freshwaternd72430.1250.066666667yes0.028875yesmuscle4.3ndndndndndBCF=Cf/Cw, average after equilibrium, k2: 1st order kinetics[407] Tsuda T, Aoki S Kojima M Harada H. Bioconcentration and excretion of diazinon, IBP, malathion and fentrothion by carp. 1990; 96, (1): 23-26.
89121-75-5malathion2Cyprinus carpio
(common carp)
nd24.4-34.910.0-10.8nd25ndndFT0.004-0.0062freshwaternd7nd3ndndndndndmuscle6ndndndndndBCF=Cf/Cw, average after equilibrium, k2: 2nd order kinetics[407] Tsuda T, Aoki S Kojima M Harada H. Bioconcentration and excretion of diazinon, IBP, malathion and fentrothion by carp. 1990; 96, (1): 23-26.
90122-14-5fenitrothion2Cyprinus carpio
(common carp)
nd24.4-34.910.0-10.8nd25ndndFT0.0018-0.0029freshwaternd7nd3ndndndndndmuscle36ndndndndndBCF=Cf/Cw, average after equilibrium, k2: 2nd order kinetics[407] Tsuda T, Aoki S Kojima M Harada H. Bioconcentration and excretion of diazinon, IBP, malathion and fentrothion by carp. 1990; 96, (1): 23-26.
9160-57-1dieldrin2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndgill323ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9260-57-1dieldrin2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndmuscle421ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9360-57-1dieldrin2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndintestine63ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9460-57-1dieldrin2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndliver15380ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9550-29-3ddt2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndgill632ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9650-29-3ddt2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndmuscle4342ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9750-29-3ddt2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndintestine761ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9850-29-3ddt2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndkidney9890ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
9950-29-3ddt2Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.001freshwaternd30nd0ndndndndndliver89100ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortality
100309-00-2aldrin3Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.005freshwaternd30nd0ndndndndndgill83.4ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortalityConcentration too close to LC50, information for assessment missing (LC50 based on US-EPA Ecosar model)
101309-00-2aldrin3Puntius ticto
(carp)
ndndndnd28-307.4-8.4ndFT0.005freshwaternd30nd0ndndndndndmuscle58ndndndndndFirst order uptake model, steady state BCF calculated based the 30 days exposure[61] Satyanarayan S, Ramakant. Bioaccumulation kinetics and bioconcentration factor of chlorinated pesticides in tissue of Puntius ticto (Ham.). 2004; 39, (2): 321-332. few information on tets species and mortalityConcentration too close to LC50, information for assessment missing (LC50 based on US-EPA Ecosar model)