Literature DB >> 1174751

Uptake and excretion of organophosphorus and carbamate insecticides by fresh water fish, motsugo, Pseudorasbora parva.

J Kanazawa.   

Abstract

Fresh water fish, Motsugo was reared in aquarium water tank containing about 1 ppm of 3 organophosphorus and 3 carbamate insecticides for about 30 days. The persistence of these insecticides in water and uptake and excretion of insecticides by fish were examined. Among organophosphorus insecticides, malathion is the most unstable in water, and degraded more than 99% for 7 days. Fenitrothion is moderately stable, and degraded 97% for 29 days. Diazinon is the most stable, and degraded 72% for 30 days. Among carbamates, carbaryl is the most unstable in water, and degraded more than 95% for 6 days. BPMC is moderately stable, and degraded 80% for 32 days. XMC is the most stable, and degraded 45% for 34 days. As for the uptake of the pesticides by fish, organophosphorus insecticides were generally higher than carbamate insecticides. The concentration of diazinon in fish reached to 211 ppm of the maximum level after 3 days, and that of fenitrothion reached to 162 ppm of the maximum level after 4 days. Afterwards, the concentration of both the insecticides decreased gradually due to the metabolism and excretion of the insecticides in fish. Uptake of malathion was very low and metabolized rapidly, and its concentration became to less than 0.01 ppm after 7 days. Among carbamate insecticides, the concentration of carbaryl in fish after one day reached to 7.5 ppm which was the maximum level of uptake. On the other hand, the concentration of BPMC in fish after 4 days became to 4.8 ppm, which was the maximum level, and decreased gradually. The concentration of XMC in fish was only 1.4 ppm after one day, but the metabolism rate of XMC in fish was fairly slow. Therefore, 0.55 ppm of XMC in fish remained even after 34 days. Moreover, in the test tank of diazinon, fenitrothion and BPMC, the appearance of deformed fish with spinal curvature of back bone came out at the rate of 10 to 30%.

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Year:  1975        PMID: 1174751     DOI: 10.1007/bf01685649

Source DB:  PubMed          Journal:  Bull Environ Contam Toxicol        ISSN: 0007-4861            Impact factor:   2.151


  5 in total

1.  Fate of carbofuran in a model ecosystem.

Authors:  C C Yu; G M Booth; D J Hansen; J R Larsen
Journal:  J Agric Food Chem       Date:  1974 May-Jun       Impact factor: 5.279

2.  Bioactive compounds in the aquatic environment: uptake and loss of DDT and dieldrin by freshwater mussles.

Authors:  J W Bedford; M J Zabik
Journal:  Arch Environ Contam Toxicol       Date:  1973-07       Impact factor: 2.804

3.  Comparative metabolism of DDT, methylchlor, and ethoxychlor in mouse, insects, and in a model ecosystem.

Authors:  I P Kapoor; R L Metcalf; A S Hirwe; P Y Lu; J R Coats; R F Nystrom
Journal:  J Agric Food Chem       Date:  1972 Jan-Feb       Impact factor: 5.279

4.  Uptake of chlorinated paraffins and PCB from suspended solids and food by juvenile Atlantic salmon.

Authors:  V Zitko
Journal:  Bull Environ Contam Toxicol       Date:  1974-10       Impact factor: 2.151

5.  Biological magnification of a polychlorinated biphenyl (Aroclor 1254) from water by aquatic invertebrates.

Authors:  H O Sanders; J H Chandler
Journal:  Bull Environ Contam Toxicol       Date:  1972-05       Impact factor: 2.151

  5 in total
  12 in total

1.  The relationship of malathion and its metabolities to fish poisoning.

Authors:  G H Cook; J C Moore; D L Coppage
Journal:  Bull Environ Contam Toxicol       Date:  1976-09       Impact factor: 2.151

2.  Acute toxicity of the pesticide diazinon to the freshwater snail Gillia altilis.

Authors:  J B Robertson; C Mazzella
Journal:  Bull Environ Contam Toxicol       Date:  1989-03       Impact factor: 2.151

3.  Persistence of methyl parathion in a carp rearing pond.

Authors:  A K Sabharwal; D K Belsare
Journal:  Bull Environ Contam Toxicol       Date:  1986-11       Impact factor: 2.151

4.  In vivo metabolism of fenitrothion (0,0-dimethyl-0-(4-nitro-m-tolyl) phosphorothioate) in fresh water teleost (Tilapia mossambica).

Authors:  F Anjum; S S Qadri
Journal:  Bull Environ Contam Toxicol       Date:  1986-01       Impact factor: 2.151

5.  Biodegradation of carbaryl in simulated aquatic environment.

Authors:  D Liu; K Thomson; W M Strachan
Journal:  Bull Environ Contam Toxicol       Date:  1981-09       Impact factor: 2.151

6.  Disappearance constants of carbaryl from streams contaminated by forest spraying.

Authors:  J G Stanley; J G Trial
Journal:  Bull Environ Contam Toxicol       Date:  1980-11       Impact factor: 2.151

7.  Intake and excretion of diazinon in freshwater fishes.

Authors:  K Seguchi; S Asaka
Journal:  Bull Environ Contam Toxicol       Date:  1981-08       Impact factor: 2.151

8.  Uptake and excretion of fenitrothion by clams and mussels.

Authors:  D W McLeese; V Zitko; D B Sergeant
Journal:  Bull Environ Contam Toxicol       Date:  1979-08       Impact factor: 2.151

9.  Effects on reproduction in the guppy (Poecilia reticulata) under chronic exposure to temephos and fenitrothion.

Authors:  M Yasuno; S Hatakeyama; M Miyashita
Journal:  Bull Environ Contam Toxicol       Date:  1980-07       Impact factor: 2.151

10.  Distribution of fenitrothion residues in brook trout (Salvelinus fontinalis) and lake trout (Salvelinus namaycush) tissues following aerial applications to Lac Ste-Anne, Québec.

Authors:  S B Holmes; P D Kingsbury; G Mamarbachi; P Mathieu
Journal:  Bull Environ Contam Toxicol       Date:  1984-10       Impact factor: 2.151

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