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Search EURAS bioconcentration factor (BCF) Gold Standard Database
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Species=Poecilia reticulata10 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
187-61-61,2,3-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
2634-67-32,3,4-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
3636-30-62,4,5-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
4634-93-52,4,6-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
5634-91-33,4,5-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
6120-82-11,2,4-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.
733857-26-02,7-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
839227-58-21,2,4-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
915862-07-42,4,5-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.
102921-88-2chlorpyrifos2Poecilia reticulata
(Guppy)
MFndnd2-3 months20.5.202308.8.2005ndFT0.002freshwater7000200.447.54yes1.7325nowhole bodynd1750017500194444.44449Zöllner and Kirsch method, with test kitdCw/dt=(k1Cw-k2Cf ). Least-square criterion used to find best fit value of k1;k2. Simulation Tool for Easy Modeling (ReMeDy System Modellin-1991) software was used.[91] Deneer JW. Uptake and elimination of chlorpyrifos in the guppy at sublethal and lethal aqueous concentrations. 1993; 26, (9): 1607-1616. k1;k2 are graphically estimated by the authors. Values expressed on lipid weight. BCF lw: calculated by the reviewer (=k1/k2)
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