Effects of lambda‐cyhalothrln in two ditch microcosm systems of different trophic status

The fate and effects of the pyrethroid insecticide lambda-cyhalothrin were compared in mesotrophic (macrophyte-dominated) and eutrophic (phytoplankton-dominated) ditch microcosms (approximately 0.5 m3). Lambda-cyhalothrin was applied three times at one-week intervals at concentrations of 10, 25, 50, 100, and 250 ng/L. The rate of dissipation of lambda-cyhalothrin in the water column of the two types of test systems was similar. After 1 d, only 30% of the amount applied remained in the water phase. Initial, direct effects were observed primarily on arthropod taxa. The most sensitive species was the phantom midge (Chaoborus obscuripes). Threshold levels for slight and transient direct toxic effects were similar (10 ng/L) between types of test systems. At treatment levels of 25 ng/L and higher, apparent population and community responses occurred. At treatments of 100 and 250 ng/L, the rate of recovery of the macroinvertebrate community was lower in the macrophyte-dominated systems, primarily because of a prolonged decline of the amphipod Gammarus pulex. This species occurred at high densities only in the macrophyte-dominated enclosures. Indirect effects (e.g., increase of rotifers and microcrustaceans) were more pronounced in the plankton-dominated test systems, particularly at treatment levels of 25 ng/L and higher.

[1]  H. Voogd,et al.  Effects of nutrient loading and insecticide application on the ecology of Elodea-dominated freshwater microcosms. I. Water chemistry and responses of plankton. , 1995 .

[2]  K. Solomon,et al.  Probabilistic risk assessment of cotton pyrethroids: II. Aquatic mesocosm and field studies , 2001, Environmental toxicology and chemistry.

[3]  M. Scheffer Ecology of Shallow Lakes , 1997, Population and Community Biology Series.

[4]  G. Hallegraeff,et al.  Some Problems in the Estimation of Chlorophyll-a and Phaeopigments from Pre- and Post-acidification Spectrophotometrie Measurements , 1978 .

[5]  T. Brock,et al.  Fate and effects of the insecticide Dursban® 4E in indoor Elodea-dominated and macrophyte-free freshwater model ecosystems: III. Aspects of ecosystem functioning , 1993 .

[6]  M. Hamer,et al.  Bioavailability of lambda-cyhalothrin to Chironomus riparius in sediment-water and water-only systems , 1999 .

[7]  P. Williams,et al.  A life‐history approach to predicting the recovery of aquatic invertebrate populations after exposure to xenobiotic chemicals , 1999 .

[8]  Fred Heimbach,et al.  Community-level aquatic system studies - interpretation criteria , 2002 .

[9]  D. A. Williams,et al.  The comparison of several dose levels with a zero dose control. , 1972, Biometrics.

[10]  T. Brock,et al.  Ecological risks of pesticides in freshwater ecosystems; Part 2: insecticides , 2000 .

[11]  Paul J van den Brink,et al.  Aquatic risk assessment of a realistic exposure to pesticides used in bulb crops: A microcosm study , 2004, Environmental toxicology and chemistry.

[12]  I. R. Hill,et al.  A comparison of the fate and effects of two pyrethroid insecticides (lambda-cyhalothrin and cypermethrin) in pond mesocosms , 1995, Ecotoxicology.

[13]  I. R. Hill,et al.  Influences of aquatic plants on the fate of the pyrethroid insecticide Lambida‐cyhalothrin in aquatic environments , 2001, Environmental toxicology and chemistry.

[14]  J BrinkvandenP.,et al.  Effects of chronic low concentrations of pesticides chlorpyrifos and atrazine in indoor freshwater micro-cosms , 1995 .

[15]  J. L. Zajicek,et al.  Population‐, community‐ and ecosystem‐level responses of aquatic mesocosms to pulsed doses of a pyrethroid insecticide , 1992 .

[16]  R. Schulz,et al.  Effectiveness of a constructed wetland for retention of nonpoint-source pesticide pollution in the Lourens River catchment, South Africa. , 2001, Environmental science & technology.

[17]  Paul J. Van den Brink,et al.  Principal response curves: Analysis of time‐dependent multivariate responses of biological community to stress , 1999 .

[18]  K. Solomon,et al.  Impact of Permethrin on Zooplankton Communities in Limnocorrals , 1985 .

[19]  Lorraine Maltby,et al.  Insecticide species sensitivity distributions: Importance of test species selection and relevance to aquatic ecosystems , 2005, Environmental toxicology and chemistry.

[20]  Ter Braak,et al.  Canoco reference manual and CanoDraw for Windows user''s guide: software for canonical community ord , 2002 .

[21]  T. Hanazato,et al.  Influence of persistence period of an insecticide on recovery patterns of a zooplankton community in experimental ponds. , 1990, Environmental pollution.

[22]  Paul J. Van den Brink,et al.  Effects of the insecticide dursban® 4E (active ingredient chlorpyrifos) in outdoor experimental ditches: I. Comparison of short‐term toxicity between the laboratory and the field , 1996 .

[23]  M. Hamer,et al.  Aquatic ecotoxicology of the pyrethroid insecticide lambda‐cyhalothrin: considerations for higher‐tier aquatic risk assessment† , 1998 .

[24]  T. Brock,et al.  In situ studies on the breakdown ofNymphoides peltata (Gmel.) O. Kuntze (Menyanthaceae); Some methodological aspects of the litter bag technique , 1982, Hydrobiological Bulletin.

[25]  Minze Leistra,et al.  Fate of the insecticide lambda-cyhalothrin in ditch enclosures differing in vegetation density. , 2004, Pest management science.

[26]  N. Crossland Fate and biological effects of methyl parathion in outdoor ponds and laboratory aquaria. II. Effects. , 1984, Ecotoxicology and environmental safety.

[27]  Paul J. Van den Brink,et al.  Effects of the insecticide dursban® 4E (active ingredient chlorpyrifos) in outdoor experimental ditches: II. Invertebrate community responses and recovery , 1996 .

[28]  J. Terwoert,et al.  Fate and effects of the insecticide Dursban® 4E in indoor Elodea-dominated and macrophyte-free freshwater model ecosystems: II. Secondary effects on community structure , 1992, Archives of environmental contamination and toxicology.

[29]  S. Rowland,et al.  Partition of synthetic pyrethroid insecticides between dissolved and particulate phases , 1995 .