Hostname: page-component-586b7cd67f-gb8f7 Total loading time: 0 Render date: 2024-11-28T07:36:57.401Z Has data issue: false hasContentIssue false
  • English
  • Français

PERSISTENCE OF CARBARYL (SEVIN-4-OIL®) IN WOODLAND PONDS AND ITS EFFECTS ON POND MACROINVERTEBRATES FOLLOWING FOREST SPRAYING

Published online by Cambridge University Press:  31 May 2012

K. Elizabeth Gibbs ,
Terry M. Mingo  and
David L. Courtemanch
K. Elizabeth Gibbs
Affiliation:
Department of Entomology, University of Maine at Orono 04469
Terry M. Mingo
Affiliation:
Department of Entomology, University of Maine at Orono 04469
David L. Courtemanch
Affiliation:
Department of Entomology, University of Maine at Orono 04469
Get access Rights & Permissions [Opens in a new window]

Abstract

The impact of an experimental aerial application of carbaryl (Sevin-4-oil®) on the macroinvertebrate fauna of woodland ponds was studied in northern Maine. Carbaryl was applied at the rate of 840 g A.I./ha, the same rate as was used for control of spruce budworm, Choristoneura fumiferana (Clemens), damage. Four treated ponds and three untreated ponds were observed for up to 30 months following treatment. Maximum residue levels of 254 μg/L were found in the water and 53,793 μg/kg (dry weight) in the sediment. Residues were detectable in the water 14 months and in the sediment 16 months after treatment.

The most severe and persistent impact was on the Amphipoda with Hyallela azteca (Saussure) and Crangonyx richmondensis Ellis reduced to near 0/m2 and failing to recolonize in some of the ponds 30 months after treatment. Numbers of immature Ephemeroptera and Trichoptera were reduced immediately following spray application but this impact did not persist throughout the season nor into the following year. Immediate reduction in numbers of adult Ephemeroptera and Trichoptera emerging from the ponds was also found. Numbers of immature Odonata were reduced following treatment and remained low during the following year. The Chironomidae did not appear affected either as immatures or emerging adults.

Résumé

L'impact des applications aériennes de carbaryl (Sevin-4-oil®) sur la macro-faune invertébrée d'étangs du sous-bois a été étudié dans le nord du Maine. Le carbaryl a été appliqué à la dose de 840 g I.A./ha, soit la dose appliquée pour le contrôle des dommages causés par la tordeuse, Choristoneura fumiferana (Clemens). Des observations ont été faites dans quatre étangs traités et 3 étangs non-traités, jusqu'à 30 mois après le traitement. Des niveaux maximum de résidus de 254 μg/L ont été observés dans l'eau, et de 53,793 μg/kg (poids sec) dans les sédiments. Des niveaux détectables de résidus ont été trouvés 14 mois après le traitement dans l'eau, et 16 mois après le traitement dans les résidus.

L'impact le plus important et le plus persistant a été noté pour les Amphipoda, Hyallela azteca (Saussure) et Crangonyx richmondensis Ellis ayant été réduits à près de 0/m2, et la recolonisation n'ayant pas eu lieu dans certains étangs 30 mois après le traitement. Les nombres d'Ephemeroptera et de Trichoptera immatures ont été réduits immédiatement après l'arrosage, mais cet effet n'a pas persisté au cours de la saison, ni l'année suivante. Une réduction immédiate des nombres d'Ephemeroptera et de Trichoptera adultes ayant émergé des étangs a aussi été observée. Les nombres d'Odonata immatures ont été réduits après le traitement et sont demeurés bas l'année suivante. Les Chironomidae n'ont pas semblé affectés à l'état d'immatures, ni comme adultes émergés.

Type
Articles
Information
The Canadian Entomologist , Volume 116 , Issue 2 , February 1984 , pp. 203 - 213
Copyright
Copyright © Entomological Society of Canada 1984

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

Aly, O. M. and El-Dib, M. A.. 1971. Studies on the persistence of some carbamate insecticides in the aquatic environment. Water Res. 5: 1191–1205.Google Scholar
Blagg, A. H. and Rawls, J. L.. 1972. GLC analysis of carbamate pesticides and phenolic compounds in water. Am. Lab. 4: 17–20.Google Scholar
Bluzat, R. and Senge, J.. 1979. Effets de trois insecticides (lindane, fenitrothion et carbaryl): toxicité aiguë sur quatre espèces d'invertébrés. Environ. Pollut. 18: 51–70.CrossRefGoogle Scholar
Boethling, R. S. and Alexander, M.. 1979. Effect of concentration of organic chemicals on their biodegradation by natural microbial communities. Appl. Environ. Microbiol. 37: 1211–1215.Google Scholar
Burdick, G. E., Dean, H. J., and Harris, E. J.. 1960. The effect of Sevin upon the aquatic environment. Jl N.Y. Fish and Game 7: 14–25.Google Scholar
Butler, J. A., Millemann, R. E., and Stewart, N. E.. 1968. Effects of the insecticide Sevin on survival and growth of the cockle clam Climocardium nuttalli. J. Fish. Res. Bd Can. 25: 1621–1635.Google Scholar
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: 271–276.CrossRefGoogle Scholar
Hughes, L. B. Jr., 1971. Fate of carbaryl insecticide in surface waters. Diss. Abstr. Int. B, 32: 3108.Google Scholar
Johnson, W. W. and Finley, M. T.. 1980. Handbook of acute toxicity of chemicals to fish and aquatic invertebrates. U.S. Dep. Interior, Fish and Wildlife Serv., Resource Publ. 137. 98 pp.Google Scholar
Kanazawa, J. 1981. Bioconcentration potential of pesticides by aquatic organisms. Jap. Pestic. Inf. 39: 12–16.Google Scholar
Kuhr, R. J. and Dorough, H. W.. 1976. Carbamate Insecticides: Chemistry, Biochemistry and Toxicology. CRC Press. 301 pp.Google Scholar
Lawton, J. H., Thompson, B. A., and Thompson, D. J.. 1980. The effects of prey density on survival and growth of damselfly larvae. Ecol. Ent. 5: 39–51.CrossRefGoogle Scholar
Menzie, C. M. 1978. Metabolism of pesticides: Update 11. U.S. Fish and Wildlife Serv., Spec. Sci. Rep. 212. 381 pp.Google Scholar
Merritt, R. W. and Cummins, K. W.. 1978. Aquatic Insects of North America. Kendall-Hunt Publishing Co. 441 pp.Google Scholar
Romine, R. R., Bussian, R. A., and Meeker, R. L.. 1971. “Sevin” insecticide: The degradation of carbaryl after surface application to a farm pond. Res. and Dev. Dept., Agr. Prod. Div., Union Carbide Corp., South Charleston, W.V.Google Scholar
Sharom, M. S., Miles, J. R. W., Harris, C. R., and McEwen, F. L.. 1980. Behaviour of 12 insecticides in soil and aqueous suspensions of soil and sediment. Water Res. 14: 1095–1100.Google Scholar
Stanley, J. G. and Trial, J. G.. 1980. Disappearance constants of carbaryl from streams contaminated by forest spraying. Bull. Environ. Contam. Toxicol. 25: 771–776.Google Scholar
Wauchope, R. D. and Haque, R.. 1973. Effects of pH, light and temperature on carbaryl in aqueous media. Bull. Environ. Contam. Toxicol. 9: 251–260.Google Scholar