Dietary accumulation and depuration of hydrophobic organochlorines: Bioaccumulation parameters and their relationship with the octanol/water partition coefficient

Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout (Oncorhynchus mykiss) was studied with the objective of obtaining relationships between bioaccumulation parameters and the octanol/water partition coefficient (Kow). A wide range of OCs were used including 16 poly...

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Published inEnvironmental toxicology and chemistry Vol. 17; no. 5; pp. 951 - 961
Main Authors Fisk, Aaron T., Norstrom, Ross J., Cymbalisty, Chris D., Muir, Derek C.G.
Format Journal Article
LanguageEnglish
Published Hoboken Wiley Periodicals, Inc 01.05.1998
SETAC
Subjects
Agnatha. Pisces
Animal, plant and microbial ecology
Applied ecology
Biological and medical sciences
Dietary accumulation
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on vertebrates
Fundamental and applied biological sciences. Psychology
Hydrophobic organochlorines
Octanol/water partition coefficient
Oncorhynchus mykiss
Toxaphene congeners
Tris(4-chlorophenyl)methane
Salmonidae
Water
Insecticide
Octanol
Hydrophobic compound
Partition coefficient
Oncorhynchus mykiss
Polychlorobiphenyl
Vertebrata
Organochlorine compounds
Chlorocarbon
Pisces
Camphechlor
Biological accumulation
Biomagnification
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Abstract Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout (Oncorhynchus mykiss) was studied with the objective of obtaining relationships between bioaccumulation parameters and the octanol/water partition coefficient (Kow). A wide range of OCs were used including 16 polychlorinated biphenyls (PCBs 18, 28, 44, 52, 66, 101, 105, 118, 128, 138, 153, 187, 189, 195, 206, and 209), hexachlorobenzene, mirex, tris(4‐chlorophenyl)methane (TCPMe), tris(4‐chlorophenyl)methanol (TCPMeOH), and three toxaphene congeners (Cl7‐chlorobornane [CHB] [Hp‐sed], Cl8‐CHB [T2], and Cl9‐CHB [T12]). Tris(4‐chlorophenyl)methane (half‐life [t1/2] = 65 d) was more persistent than TCPMeOH (t1/2 = 20 d), and TCPMe was not biotransformed to TCPMeOH by rainbow trout. Cl7‐chlorobornane (t1/2 = 32 d) was more rapidly eliminated, and appears to be more readily metabolized, than Cl8‐CHB (t1/2 = 43 d) and Cl9‐CHB (t1/2 = 42 d). With the exception of TCPMeOH, Cl7‐CHB, and PCB 18, all of the OCs had biomagnification factors (BMFs) >1, implying a potential to biomagnify. Half‐lives had a significant curvilinear relationship with Kow (R2 = 0.85, p < 0.001), with a maximum t1/2 for OCs with log Kow ∼ 7.0. Decreasing t1/2 for OCs of log Kow > 7.0 may be related to slow kinetics of these super hydrophobic OCs and the short exposure phase, which results in insufficient time for the super hydrophobic OCs to reach slower clearing compartments of the rainbow trout. Assimilation efficiency was not as well described by Kow as by t1/2 and BMF, although a significant curvilinear relationship was observed (R2 = 0.53, p = 0.004). The BMF had a significant curvilinear relationship with log Kow (R2 = 0.84, p < 0.001). Recalcitrant OCs with a log Kow of ∼7.0 would appear to have the greatest potential for food chain biomagnification in fish.
AbstractList Juvenile rainbow trout were exposed to dietary concentrations of 23 organochlorines, which are tabulated, to determine bioaccumulation parameters. The data were used to develop dietary accumulation parameter octanol/water partition coefficient relationships. Results are presented for PCBs, mirex, hexachlorobenzene, tris(4-chlorophenyl)methane, tris(4-chlorophenyl)methanol, and toxaphene congeners in terms of bioaccumulation parameter octanol/water partition coefficient relationships, depuration rate constant octanol/water partition coefficient relationships, assimilation efficiency octanol/water partition coefficient relationships, and biomagnification factor octanol/water partition relationships. The data show that organochlorine compounds with a log octanol/water partition coefficient of approximately 7, which are not biotransformed, have the greatest persistence and biomagnification in fish.
Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout (Oncorhynchus mykiss) was studied with the objective of obtaining relationships between bioaccumulation parameters and the octanol/water partition coefficient (K sub(ow)). A wide range of OCs were used including 16 polychlorinated biphenyls (PCBs 18, 28, 44, 52, 66, 101, 105, 118, 128, 138, 153, 187, 189, 195, 206, and 209), hexachlorobenzene, mirex, tris(4-chlorophenyl)methane (TCPMe), tris(4-chlorophenyl)methanol (TCPMeOH), and three toxaphene congeners (Cl sub(7)-chlorobornane [CHB] [Hp-sed], Cl sub(8)-CHB [T2], and Cl sub(9)-CHB [Tl2]). Tris(4-chlorophenyl)methane (half-life [t sub(1/2)] = 65 d) was more persistent than TCPMeOH (t sub(1/2) = 20 d), and TCPMe was not biotransformed to TCPMeOH by rainbow trout. Cl sub(7)-chlorobornane (t sub(1/2) = 32 d) was more rapidly eliminated, and appears to be more readily metabolized, than Cl sub(8)-CHB (t sub(1/2) = 43 d) and Cl sub(9)-CHB (t sub(1/2) = 42 d). With the exception of TCPMeOH, Cl sub(7)-CHB, and PCB 18, all of the OCs had biomagnification factors (BMFs) > 1, implying a potential to biomagnify. Half-lives had a significant curvilinear relationship with K sub(ow) (R super(2) = 0.85, p < 0.001), with a maximum t sub(1/2) for OCs with log K sub(ow) similar to 7.0. Decreasing t sub(1/2) for OCs of log K sub(ow) > 7.0 may be related to slow kinetics of these super hydrophobic OCs and the short exposure phase, which results in insufficient time for the super hydrophobic OCs to reach slower clearing compartments of the rainbow trout. Assimilation efficiency was not as well described by K sub(ow) as by t sub(1/2) and BMF, although a significant curvilinear relationship was observed (R super(2) = 0.53, p = 0.004). The BMF had a significant curvilinear relationship with log K sub(ow) (R super(2) = 0.84, p < 0.001). Recalcitrant OCs with a log K sub(ow) of similar to 7.0 would appear to have the greatest potential for food chain biomagnification in fish.
Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout ( Oncorhynchus mykiss ) was studied with the objective of obtaining relationships between bioaccumulation parameters and the octanol/water partition coefficient ( K ow ). A wide range of OCs were used including 16 polychlorinated biphenyls (PCBs 18, 28, 44, 52, 66, 101, 105, 118, 128, 138, 153, 187, 189, 195, 206, and 209), hexachlorobenzene, mirex, tris(4‐chlorophenyl)methane (TCPMe), tris(4‐chlorophenyl)methanol (TCPMeOH), and three toxaphene congeners (Cl 7 ‐chlorobornane [CHB] [Hp‐sed], Cl 8 ‐CHB [T2], and Cl 9 ‐CHB [T12]). Tris(4‐chlorophenyl)methane (half‐life [ t 1/2 ] = 65 d) was more persistent than TCPMeOH ( t 1/2 = 20 d), and TCPMe was not biotransformed to TCPMeOH by rainbow trout. Cl 7 ‐chlorobornane ( t 1/2 = 32 d) was more rapidly eliminated, and appears to be more readily metabolized, than Cl 8 ‐CHB ( t 1/2 = 43 d) and Cl 9 ‐CHB ( t 1/2 = 42 d). With the exception of TCPMeOH, Cl 7 ‐CHB, and PCB 18, all of the OCs had biomagnification factors (BMFs) >1, implying a potential to biomagnify. Half‐lives had a significant curvilinear relationship with K ow ( R 2 = 0.85, p < 0.001), with a maximum t 1/2 for OCs with log K ow ∼ 7.0. Decreasing t 1/2 for OCs of log K ow > 7.0 may be related to slow kinetics of these super hydrophobic OCs and the short exposure phase, which results in insufficient time for the super hydrophobic OCs to reach slower clearing compartments of the rainbow trout. Assimilation efficiency was not as well described by K ow as by t 1/2 and BMF, although a significant curvilinear relationship was observed ( R 2 = 0.53, p = 0.004). The BMF had a significant curvilinear relationship with log K ow ( R 2 = 0.84, p < 0.001). Recalcitrant OCs with a log K ow of ∼7.0 would appear to have the greatest potential for food chain biomagnification in fish.
Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout (Oncorhynchus mykiss) was studied with the objective of obtaining relationships between bioaccumulation parameters and the octanol/water partition coefficient (Kow). A wide range of OCs were used including 16 polychlorinated biphenyls (PCBs 18, 28, 44, 52, 66, 101, 105, 118, 128, 138, 153, 187, 189, 195, 206, and 209), hexachlorobenzene, mirex, tris(4‐chlorophenyl)methane (TCPMe), tris(4‐chlorophenyl)methanol (TCPMeOH), and three toxaphene congeners (Cl7‐chlorobornane [CHB] [Hp‐sed], Cl8‐CHB [T2], and Cl9‐CHB [T12]). Tris(4‐chlorophenyl)methane (half‐life [t1/2] = 65 d) was more persistent than TCPMeOH (t1/2 = 20 d), and TCPMe was not biotransformed to TCPMeOH by rainbow trout. Cl7‐chlorobornane (t1/2 = 32 d) was more rapidly eliminated, and appears to be more readily metabolized, than Cl8‐CHB (t1/2 = 43 d) and Cl9‐CHB (t1/2 = 42 d). With the exception of TCPMeOH, Cl7‐CHB, and PCB 18, all of the OCs had biomagnification factors (BMFs) >1, implying a potential to biomagnify. Half‐lives had a significant curvilinear relationship with Kow (R2 = 0.85, p < 0.001), with a maximum t1/2 for OCs with log Kow ∼ 7.0. Decreasing t1/2 for OCs of log Kow > 7.0 may be related to slow kinetics of these super hydrophobic OCs and the short exposure phase, which results in insufficient time for the super hydrophobic OCs to reach slower clearing compartments of the rainbow trout. Assimilation efficiency was not as well described by Kow as by t1/2 and BMF, although a significant curvilinear relationship was observed (R2 = 0.53, p = 0.004). The BMF had a significant curvilinear relationship with log Kow (R2 = 0.84, p < 0.001). Recalcitrant OCs with a log Kow of ∼7.0 would appear to have the greatest potential for food chain biomagnification in fish.
The dietary accumulation of 23 hydrophobic organochlorines (OC) by juvenile rainbow trout (Oncorhynchus mykiss) was studied to determine relationships between bioaccumulation parameters and the octanol/water partition coefficient (Kow). Three toxaphene congeners, Cl(7)-chlorobornane (CHB), Cl(8)-CHB and Cl(9)-CHB were tested, together with tris(4-chlorophenyl)methane (TCPMe) and TCP-methanol, giving half-life values of 32, 43, 42, 65 and 20 d, respectively. Cl(7)-CHB was more rapidly eliminated, and more readily metabolized than Cl(8)- or Cl(9)-CHB. All 16 polychlorinated biphenyls (PCB), except PCB-18, had biomagnification factors (BMF) greater than 1. Decreasing half-lives for OC with Kow greater than 7.0 were related to slow kinetics of the superhydrophobic compounds. Half-lives had a significant curvilinear relationship with Kow. The BMF had a similar relationship indicating that the internal kinetics of contaminants in fish play a significant role in their fate and the length of exposure of superhydrophobic OC effects the half-life. There are 57 references.
Author Fisk, Aaron T.
Muir, Derek C.G.
Cymbalisty, Chris D.
Norstrom, Ross J.
Author_xml – sequence: 1
  givenname: Aaron T.
  surname: Fisk
  fullname: Fisk, Aaron T.
  organization: Department of Soil Science, University of Manitoba, Winnipeg, Manitoba R3T 2N2, Canada
– sequence: 2
  givenname: Ross J.
  surname: Norstrom
  fullname: Norstrom, Ross J.
  organization: National Wildlife Research Center, Environment Canada, 100 Gamelin Boulevard, Hull, Quebec K1A 0H3, Canada
– sequence: 3
  givenname: Chris D.
  surname: Cymbalisty
  fullname: Cymbalisty, Chris D.
  organization: Freshwater Institute, Department of Fisheries and Oceans, 501 University Crescent, Winnipeg, Manitoba R3T 2N6, Canada
– sequence: 4
  givenname: Derek C.G.
  surname: Muir
  fullname: Muir, Derek C.G.
  email: derek.muir@cciw.ca
  organization: Freshwater Institute, Department of Fisheries and Oceans, 501 University Crescent, Winnipeg, Manitoba R3T 2N6, Canada
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IsPeerReviewed true
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Issue 5
Keywords Salmonidae
Water
Insecticide
Octanol
Hydrophobic compound
Partition coefficient
Oncorhynchus mykiss
Polychlorobiphenyl
Vertebrata
Organochlorine compounds
Chlorocarbon
Pisces
Camphechlor
Biological accumulation
Biomagnification
Language English
License CC BY 4.0
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PublicationCentury 1900
PublicationDate May 1998
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PublicationTitle Environmental toxicology and chemistry
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PublicationYear 1998
Publisher Wiley Periodicals, Inc
SETAC
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1993; 26
1995; 52
1982; 16
1979; 36
1991; 10
1988; 16
1988; 17
1989; 8
1988; 103
1996; 93
1996; 30
1993
1992
1994; 28
1992; 11
1993; 1
1996; 15
1994; 20
1996; 33
1985; 19
1993; 12
1990; 47
1997; 31
1997; 37
1984; 7
1991; 20
1986; 5
1988; 22
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e_1_2_6_43_2
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Snippet Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout (Oncorhynchus mykiss) was studied with the objective of obtaining...
Dietary accumulation of 23 hydrophobic organochlorines (OCs) by juvenile rainbow trout ( Oncorhynchus mykiss ) was studied with the objective of obtaining...
The dietary accumulation of 23 hydrophobic organochlorines (OC) by juvenile rainbow trout (Oncorhynchus mykiss) was studied to determine relationships between...
Juvenile rainbow trout were exposed to dietary concentrations of 23 organochlorines, which are tabulated, to determine bioaccumulation parameters. The data...
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wiley
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StartPage 951
SubjectTerms Agnatha. Pisces
Animal, plant and microbial ecology
Applied ecology
Biological and medical sciences
Dietary accumulation
Ecotoxicology, biological effects of pollution
Effects of pollution and side effects of pesticides on vertebrates
Fundamental and applied biological sciences. Psychology
Hydrophobic organochlorines
Octanol/water partition coefficient
Oncorhynchus mykiss
Toxaphene congeners
Tris(4-chlorophenyl)methane
Title Dietary accumulation and depuration of hydrophobic organochlorines: Bioaccumulation parameters and their relationship with the octanol/water partition coefficient
URI https://api.istex.fr/ark:/67375/WNG-X8SGQ813-C/fulltext.pdf
https://onlinelibrary.wiley.com/doi/abs/10.1002%2Fetc.5620170526
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https://search.proquest.com/docview/14480125
https://search.proquest.com/docview/16395182
Volume 17
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