Hostname: page-component-cd9895bd7-p9bg8 Total loading time: 0 Render date: 2024-12-30T16:22:16.140Z Has data issue: false hasContentIssue false

TOXICITY OF THE INSECTICIDE PERMETHRIN IN WATER AND SEDIMENT TO NYMPHS OF THE BURROWING MAYFLY HEXAGENIA RIGIDA (EPHEMEROPTERA: EPHEMERIDAE)

Published online by Cambridge University Press:  31 May 2012

M. K. Friesen
Affiliation:
Freshwater Institute, Department of Fisheries and Oceans, Winnipeg, Manitoba R3T 2N6.
J. F. Flannagan
Affiliation:
Department of Entomology, University of Manitoba, Winnipeg, Manitoba R3T 2N2.
T. D. Galloway
Affiliation:
Freshwater Institute, Department of Fisheries and Oceans, Winnipeg, Manitoba R3T 2N6.

Abstract

The 6 LC50 for nymphs of Hexagenia rigida exposed to permethrin-contaminated water without sediment was estimated to lie between 0.58 and 2.06 μg/L. No nymphs survived a 6 h exposure to 7.63 μg/L. Laboratory simulated application of 7.3 g/ha permethrin to H. rigida nymphs in culture resulted in a final mortality of 88.0 ± 15.2% after a 1-day exposure, and 100.0% after a 7 day exposure; initial permethrin concentrations in water were estimated to be 7.63 μg/L and maximum mean concentrations in sediment, measured 1 and 7 days after application, were estimated to be approximately 50 μg/kg dry weight. Exposure of nymphs to sediment contaminated 8 days previously resulted in 100.0% mortality. An application of 0.6 g/ha resulted in final mortality of up to 45.0 ± 4.1%. Lethal effects occurred in some cases between 1 and 4 and possibly up to 10 weeks after application.

Résumé

Dans le cas des nymphes de Hexagenia rigida exposées à l'eau contaminée de perméthrine, sans sédimentation, au cours de l'expérience de 6 h LC50, on a estimé que le taux se situait entre 0.58 et 2.06 μg/L. Aucune nymphe n'a survécue à 6 h d'exposition à 7.63 μg/L. Une application simulée au laboratoire de 7.3 g/ha perméthrine à des nymphes de H. rigida en culture a eu pour résultat une mortalité finale de 88.0 ± 15.2% après exposition d'un jour, et 100% après exposition de 7 jours; on a estimé que les concentrations initiales de perméthrine dans l'eau furent estimées à 7.63 μg/L et des concentrations sédimentaires moyennes maximales mesurées 1 et 7 jours après application furent estimées à environs 50 μg/kg de poids sec. L'exposition des nymphes à des sédiments contaminés 8 jours auparavant a abouti à un taux de mortalité de 100.0%. Une application de 0.6 g/ha a eu pour effet un taux final de mortalité atteignant 45.0 ± 4.1%. Les effets mortels ont eu lieu, dans certains cas, entre 1 et 4, et possiblement jusqu'à 10 semaines après application.

Type
Articles
Copyright
Copyright © Entomological Society of Canada 1983

Access options

Get access to the full version of this content by using one of the access options below. (Log in options will check for institutional or personal access. Content may require purchase if you do not have access.)

References

Courtemanch, D. L. and Gibbs, K. E.. 1980. Short-and long-term effects of forest spraying of carbaryl (Sevin-4-oil®) on stream invertebrates. Can. Ent. 112: 271276.CrossRefGoogle Scholar
Eidt, D. C. 1975. The effect of fenitrothion from large-scale forest spraying on benthos in New Brunswick headwaters streams. Can. Ent. 107: 743760.CrossRefGoogle Scholar
Elliott, M., Janes, N. F., and Potter, C.. 1978. The future of pyrethroids in insect control. A. Rev. Ent. 23: 443469.CrossRefGoogle Scholar
Flannagan, J. F. 1973. Field and laboratory studies of the effect of exposure to fenitrothion on freshwater aquatic invertebrates. Manitoba Ent. 7: 1525.Google Scholar
Friesen, M. K. 1981 a. Hexagenia rigida (McDunnough). pp. 127142in Lawrence, S. G. (Ed.), Manual for the Culture of Selected Freshwater Invertebrates. Can. Spec. Publ. Fish. Aquat. Sci. 54.Google Scholar
Friesen, M. K. 1981 b. Effects of the insecticide permethrin on the aquatic life stages of the burrowing mayfly Hexagenia rigida (Ephemeroptera: Ephemeridae). M.S. Thesis, Univ. of Manitoba. 75 pp.Google Scholar
Gill, S. S. 1977. Larvicidal activity of synthetic pyrethroids against Aedes albopictus (Skuse). SEast Asian J. trop. Med. Public Hlth 8: 510514.Google ScholarPubMed
Kingsbury, P. D. and Kreutzweiser, D. P.. 1979. Impact of double applications of permethrin on forest streams and ponds. For. Pest Manage. Inst., Sault Ste. Marie, Ontario. Inf. Rep. FPM-X-27. 42 pp.Google Scholar
Kingsbury, P. D. and Kreutzweiser, D. P.. 1980. Environmental impact assessment of a semi-operational permethrin application. For. Pest Manage. Inst., Sault Ste. Marie, Ontario. Inf. Rep. FPM-X-30. 47 pp.Google Scholar
Muir, D. C. G., Metner, D. A., Blouw, A. P., Grift, N. P., and Lockhart, W. L.. 1979. Effect of water chemistry on the uptake of organic pollutants by fish in river water. pp. 1226in Klaverkamp, J. F., Leonhard, S. L., and Marshall, K. E. (Eds.), Proc. 6th A. Aquat. Toxicity Workshop, Winnipeg, Manitoba, 1979. Can. Tech. Rep. Fish. Aquat. Sci. 975.Google Scholar
Muirhead-Thomson, R. C. 1978. Lethal and behavioural impact of permethrin (NRDC 143) on selected stream macroinvertebrates. Mosquito News 38: 185190.Google Scholar
Muirhead-Thomson, R. C. 1979. Experimental studies on macroinvertebrate predator-prey impact of pesticides. The reactions of Rhyacophila and Hydropsyche (Trichoptera) larvae to Simulium larvicides. Can. J. Zool. 57: 22642270.CrossRefGoogle Scholar
Rawn, G. P. 1981. Fate and degradation of permethrin in a model aquatic ecosystem. Ph.D. Thesis, Univ. of Manitoba. 130 pp.Google Scholar
Rawn, G. P., Webster, G. R. B., and Muir, D. C. G.. 1979. Bioactivity and degradation of permethrin in artificial pools. pp. 140149in Klaverkamp, J. F., Leonhard, S. L., and Marshall, K. E. (Eds.), Proc. 6th A. Aquat. Toxicity Workshop, Winnipeg, Manitoba, 1979. Can. Tech. Rep. Fish. Aquat. Sci. 975.Google Scholar
Rawn, G. P., Webster, G. R. B., and Muir, D. C. G.. 1980. Analysis and fate of (14C) permethrin in an aquatic ecosystem. pp. 2533in Cessna, A. J. (Ed.), Proc. 15th A. Pestic. Residue Analysts (Western Canada) Workshop, Regina, Sask., 1980. Can. Plains Res. Center, Univ. Regina, Sask.Google Scholar
Sharom, M. S. and Solomon, K. R.. 1981 a. Adsorption, desorption, distribution and degradation of permethrin in sediment-water system. p. 346in Bermingham, N., Blaise, C., Couture, P., Hummel, B., Joubert, G., and Speyer, M. (Eds.), Proc. 7th A. Aquat. Toxicity Workshop, Montreal, Que., 1980. Can. Tech. Rep. Fish. Aquat. Sci. 990.Google Scholar
Sharom, M. S. and Solomon, K. R.. 1981 b. Adsorption and desorption of permethrin and other pesticides on glass and plastic materials used in bioassay procedures. Can. J. Fish. Aquat. Sci. 38: 199204.CrossRefGoogle Scholar
Snedecor, G. W. and Cochran, W. G.. 1980. Statistical Methods, 7th ed. Iowa State Univ. Press. 507 pp.Google Scholar
Zimmerman, M. C. 1977. Aspects of the life history, feeding behavior, and nutritional dynamics of the burrowing mayfly, Hexagenia limbata in an Ohio pond. Ph.D. Thesis, Miami Univ., Ohio. 173 pp.Google Scholar