Literature DB >> 15195804

Comparison of laboratory single species and field population-level effects of the pyrethroid insecticide lambda-cyhalothrin on freshwater invertebrates.

A F W Schroer1, J D M Belgers, T C M Brock, A M Matser, S J Maund, P J Van den Brink.   

Abstract

The toxicity of the pyrethroid insecticide lambda-cyhalothrin to freshwater invertebrates has been investigated using data from short-term laboratory toxicity tests and in situ bioassays and population-level effects in field microcosms. In laboratory tests, patterns of toxicity were consistent with previous data on pyrethroids. The midge Chaoborus obscuripes was most sensitive (48- and 96-h EC50 = 2.8 ng/L). Other insect larvae (Hemiptera, Ephemeroptera) and macrocrustacea (Amphipoda, Isopoda) were also relatively sensitive, with 48- and 96-h EC50 values between 10 and 100 ng/L. Generally, microcrustacea (Cladocera, Copepoda) and larvae of certain insect groups (Odonata and Chironomidae) were less sensitive, with 48-h EC50 values higher than 100 ng/L. Mollusca and Plathelminthes were insensitive and were unaffected at concentrations at and above the water solubility (5 microg/L). Generally, the EC50 values based on initial population responses in field enclosures were similar to values derived from laboratory tests with the same taxa. Also, the corresponding fifth and tenth percentile hazard concentrations (HC5 and HC10) were similar (laboratory HC5 = 2.7 ng/L and field HC5 = 4.1 ng/L; laboratory and field HC10 = 5.1 ng/L), at least when based on the same sensitive taxonomic groups (insects and crustaceans) and when a similar concentration range was taken into account. In the three field enclosure experiments and at a treatment level of 10 ng/L, consistent effects were observed for only one population (Chaoborus obscuripes), with recovery taking place within 3 to 6 weeks. The laboratory HC5 (2.7 ng/L) and HC10 (5.1 ng/L) based on acute EC50 values of all aquatic arthropod taxa were both lower than this 10 ng/L, a concentration that might represent the "regulatory acceptable concentration." The HC5 and HC10 values in this study in The Netherlands (based on static laboratory tests with freshwater arthropods) were very similar to those derived from a previous study in the United Kingdom (1.4 and 3.3 ng/L). This suggests that for pesticides like lambda-cyhalothrin, HC5 values based on static laboratory tests may provide a conservative estimate of the potential for community-level effects under field conditions. While these HC5 values are conservative for initial effects, they do not provide information on recovery potential, which may be important for regulatory decision-making.

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Year:  2004        PMID: 15195804     DOI: 10.1007/s00244-003-2315-3

Source DB:  PubMed          Journal:  Arch Environ Contam Toxicol        ISSN: 0090-4341            Impact factor:   2.804


  15 in total

1.  Impact of triphenyltin acetate in microcosms simulating floodplain lakes. II. Comparison of species sensitivity distributions between laboratory and semi-field.

Authors:  I Roessink; J D M Belgers; S J H Crum; P J van den Brink; T C M Brock
Journal:  Ecotoxicology       Date:  2006-07       Impact factor: 2.823

2.  Evaluation of suitable endpoints for assessing the impacts of toxicants at the community level.

Authors:  Francisco Sánchez-Bayo; Kouchi Goka
Journal:  Ecotoxicology       Date:  2011-11-26       Impact factor: 2.823

3.  Sublethal and sex-specific cypermethrin effects in toxicity tests with the midge Chironomus riparius Meigen.

Authors:  Willem Goedkoop; Nicole Spann; Nina Akerblom
Journal:  Ecotoxicology       Date:  2010-06-05       Impact factor: 2.823

Review 4.  Threshold levels for effects of insecticides in freshwater ecosystems: a review.

Authors:  René P A Van Wijngaarden; Theo C M Brock; Paul J Van den Brink
Journal:  Ecotoxicology       Date:  2005-04       Impact factor: 2.823

5.  Metabolism, bioaccumulation, and toxicity of pesticides in aquatic insect larvae.

Authors:  Toshiyuki Katagi; Hitoshi Tanaka
Journal:  J Pestic Sci       Date:  2016-05-20       Impact factor: 1.519

6.  Pyrethroid pesticide effects on behavioral responses of aquatic isopods to danger cues.

Authors:  Carolyn K Huynh; Signe R Poquette; W Lindsay Whitlow
Journal:  Environ Sci Pollut Res Int       Date:  2014-01-05       Impact factor: 4.223

7.  Effects of the pyrethroid insecticide gamma-cyhalothrin on aquatic invertebrates in laboratory and outdoor microcosm tests.

Authors:  René P A van Wijngaarden; Ian Barber; Theo C M Brock
Journal:  Ecotoxicology       Date:  2008-11-04       Impact factor: 2.823

8.  Effect of parathion-methyl on Amazonian fish and freshwater invertebrates: a comparison of sensitivity with temperate data.

Authors:  Andreu Rico; Rachel Geber-Corrêa; Paola S Campos; Marcos V B Garcia; Andrea V Waichman; Paul J van den Brink
Journal:  Arch Environ Contam Toxicol       Date:  2009-10-22       Impact factor: 2.804

Review 9.  Comparative aquatic toxicity of the pyrethroid insecticide lambda-cyhalothrin and its resolved isomer gamma-cyhalothrin.

Authors:  Jeffrey M Giddings; Ian Barber; William Warren-Hicks
Journal:  Ecotoxicology       Date:  2008-11-13       Impact factor: 2.823

10.  Linking sub-individual and population level toxicity effects in Daphnia schoedleri (Cladocera: Anomopoda) exposed to sublethal concentrations of the pesticide α-cypermethrin.

Authors:  Fernando Martínez-Jerónimo; Mario Arzate-Cárdenas; Rocío Ortiz-Butrón
Journal:  Ecotoxicology       Date:  2013-05-10       Impact factor: 2.823

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