Effects of 2 Neonicotinoid Insecticides on Blood Cell Profiles and Corticosterone Concentrations of Wood Frogs (Lithobates sylvaticus)
Neonicotinoids are widely used insecticides that are detectable in agricultural waterways. These insecticides are of concern due to their potential impacts on nontarget organisms. Pesticides can affect development of amphibians and suppress the immune system, which could impact disease susceptibilit...
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creator | Gavel, Melody J. Richardson, Sarah D. Dalton, Rebecca L. Soos, Catherine Ashby, Brendan McPhee, Landon Forbes, Mark R. Robinson, Stacey A. |
description | Neonicotinoids are widely used insecticides that are detectable in agricultural waterways. These insecticides are of concern due to their potential impacts on nontarget organisms. Pesticides can affect development of amphibians and suppress the immune system, which could impact disease susceptibility and tolerance. No previous studies on amphibians have examined the effects of these insecticides on differential blood cell proportions or concentrations of corticosterone (a general stress hormone). We investigated the effects of chronic exposure to 2 neonicotinoids, thiamethoxam and clothianidin, on immunometrics of wood frogs (Lithobates sylvaticus). Frogs were exposed to single, chronic treatments of 2.5 or 250 µg/L of clothianidin or thiamethoxam for 7 wk from Gosner stages 25 to 46. The juvenile frogs were then maintained for 3 wk post metamorphosis without exposure to neonicotinoids. We measured water‐borne corticosterone twice: at 6 d and 8 wk after exposure in larval and juvenile frogs, respectively. We assessed differential blood cell profiles from juvenile frogs. Corticosterone was significantly lower in tadpoles exposed to 250 µg/L of thiamethoxam compared with other tadpole treatments, but no significant differences in corticosterone concentrations were found in treatments using juvenile frogs. Anemia was detected in all treatments compared with controls with the exception of tadpoles exposed to 2.5 µg/L of clothianidin. Neutrophil‐to‐leukocyte and neutrophil‐to‐lymphocyte ratios were elevated in frogs exposed to 250 µg/L of thiamethoxam. Collectively, these results indicate that chronic exposure to neonicotinoids has varied impacts on blood cell profiles and corticosterone concentrations of developing wood frogs, which are indicative of stress. Future studies should investigate whether exposure to neonicotinoids increases susceptibility to infection by parasites in both larval and adult wood frogs. Environ Toxicol Chem 2019;38:1273–1284. © 2019 Crown in the right of Canada. Published by Wiley Periodicals Inc. on behalf of SETAC. |
doi_str_mv | 10.1002/etc.4418 |
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These insecticides are of concern due to their potential impacts on nontarget organisms. Pesticides can affect development of amphibians and suppress the immune system, which could impact disease susceptibility and tolerance. No previous studies on amphibians have examined the effects of these insecticides on differential blood cell proportions or concentrations of corticosterone (a general stress hormone). We investigated the effects of chronic exposure to 2 neonicotinoids, thiamethoxam and clothianidin, on immunometrics of wood frogs (Lithobates sylvaticus). Frogs were exposed to single, chronic treatments of 2.5 or 250 µg/L of clothianidin or thiamethoxam for 7 wk from Gosner stages 25 to 46. The juvenile frogs were then maintained for 3 wk post metamorphosis without exposure to neonicotinoids. We measured water‐borne corticosterone twice: at 6 d and 8 wk after exposure in larval and juvenile frogs, respectively. We assessed differential blood cell profiles from juvenile frogs. Corticosterone was significantly lower in tadpoles exposed to 250 µg/L of thiamethoxam compared with other tadpole treatments, but no significant differences in corticosterone concentrations were found in treatments using juvenile frogs. Anemia was detected in all treatments compared with controls with the exception of tadpoles exposed to 2.5 µg/L of clothianidin. Neutrophil‐to‐leukocyte and neutrophil‐to‐lymphocyte ratios were elevated in frogs exposed to 250 µg/L of thiamethoxam. Collectively, these results indicate that chronic exposure to neonicotinoids has varied impacts on blood cell profiles and corticosterone concentrations of developing wood frogs, which are indicative of stress. Future studies should investigate whether exposure to neonicotinoids increases susceptibility to infection by parasites in both larval and adult wood frogs. Environ Toxicol Chem 2019;38:1273–1284. © 2019 Crown in the right of Canada. Published by Wiley Periodicals Inc. on behalf of SETAC.</description><identifier>ISSN: 0730-7268</identifier><identifier>EISSN: 1552-8618</identifier><identifier>DOI: 10.1002/etc.4418</identifier><identifier>PMID: 30901102</identifier><language>eng</language><publisher>United States: Blackwell Publishing Ltd</publisher><subject>Agrochemicals ; Amphibians ; Anemia ; Animals ; Blood ; Blood Cells - drug effects ; Blood Cells - metabolism ; Canada ; Chronic exposure ; Corticosterone ; Corticosterone - blood ; Ecotoxicology ; Exposure ; Frogs ; Guanidines - toxicity ; Immune system ; Immunological tolerance ; Insecticides ; Insecticides - toxicity ; Larva - drug effects ; Leukocytes ; Linear Models ; Lithobates sylvaticus ; Lymphocytes ; Metamorphosis ; Neonicotinoid ; Neonicotinoid insecticides ; Neonicotinoids - toxicity ; Neutrophils ; Nontarget organisms ; Parasites ; Pesticides ; Ranidae - blood ; Thiamethoxam ; Thiamethoxam - toxicity ; Thiazoles - toxicity ; Water Pollutants, Chemical - analysis ; Waterways</subject><ispartof>Environmental toxicology and chemistry, 2019-06, Vol.38 (6), p.1273-1284</ispartof><rights>Published 2019 SETAC</rights><rights>Published 2019 SETAC.</rights><rights>2019 SETAC</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c4128-1a0a0d65f26f77facbd68fd2e724dbb7a5fa07073a822c646237ca5c065ffea63</citedby><cites>FETCH-LOGICAL-c4128-1a0a0d65f26f77facbd68fd2e724dbb7a5fa07073a822c646237ca5c065ffea63</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.1002%2Fetc.4418$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.1002%2Fetc.4418$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,776,780,1411,27901,27902,45550,45551</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/30901102$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Gavel, Melody J.</creatorcontrib><creatorcontrib>Richardson, Sarah D.</creatorcontrib><creatorcontrib>Dalton, Rebecca L.</creatorcontrib><creatorcontrib>Soos, Catherine</creatorcontrib><creatorcontrib>Ashby, Brendan</creatorcontrib><creatorcontrib>McPhee, Landon</creatorcontrib><creatorcontrib>Forbes, Mark R.</creatorcontrib><creatorcontrib>Robinson, Stacey A.</creatorcontrib><title>Effects of 2 Neonicotinoid Insecticides on Blood Cell Profiles and Corticosterone Concentrations of Wood Frogs (Lithobates sylvaticus)</title><title>Environmental toxicology and chemistry</title><addtitle>Environ Toxicol Chem</addtitle><description>Neonicotinoids are widely used insecticides that are detectable in agricultural waterways. These insecticides are of concern due to their potential impacts on nontarget organisms. Pesticides can affect development of amphibians and suppress the immune system, which could impact disease susceptibility and tolerance. No previous studies on amphibians have examined the effects of these insecticides on differential blood cell proportions or concentrations of corticosterone (a general stress hormone). We investigated the effects of chronic exposure to 2 neonicotinoids, thiamethoxam and clothianidin, on immunometrics of wood frogs (Lithobates sylvaticus). Frogs were exposed to single, chronic treatments of 2.5 or 250 µg/L of clothianidin or thiamethoxam for 7 wk from Gosner stages 25 to 46. The juvenile frogs were then maintained for 3 wk post metamorphosis without exposure to neonicotinoids. We measured water‐borne corticosterone twice: at 6 d and 8 wk after exposure in larval and juvenile frogs, respectively. We assessed differential blood cell profiles from juvenile frogs. Corticosterone was significantly lower in tadpoles exposed to 250 µg/L of thiamethoxam compared with other tadpole treatments, but no significant differences in corticosterone concentrations were found in treatments using juvenile frogs. Anemia was detected in all treatments compared with controls with the exception of tadpoles exposed to 2.5 µg/L of clothianidin. Neutrophil‐to‐leukocyte and neutrophil‐to‐lymphocyte ratios were elevated in frogs exposed to 250 µg/L of thiamethoxam. Collectively, these results indicate that chronic exposure to neonicotinoids has varied impacts on blood cell profiles and corticosterone concentrations of developing wood frogs, which are indicative of stress. Future studies should investigate whether exposure to neonicotinoids increases susceptibility to infection by parasites in both larval and adult wood frogs. Environ Toxicol Chem 2019;38:1273–1284. © 2019 Crown in the right of Canada. Published by Wiley Periodicals Inc. on behalf of SETAC.</description><subject>Agrochemicals</subject><subject>Amphibians</subject><subject>Anemia</subject><subject>Animals</subject><subject>Blood</subject><subject>Blood Cells - drug effects</subject><subject>Blood Cells - metabolism</subject><subject>Canada</subject><subject>Chronic exposure</subject><subject>Corticosterone</subject><subject>Corticosterone - blood</subject><subject>Ecotoxicology</subject><subject>Exposure</subject><subject>Frogs</subject><subject>Guanidines - toxicity</subject><subject>Immune system</subject><subject>Immunological tolerance</subject><subject>Insecticides</subject><subject>Insecticides - toxicity</subject><subject>Larva - drug effects</subject><subject>Leukocytes</subject><subject>Linear Models</subject><subject>Lithobates sylvaticus</subject><subject>Lymphocytes</subject><subject>Metamorphosis</subject><subject>Neonicotinoid</subject><subject>Neonicotinoid insecticides</subject><subject>Neonicotinoids - toxicity</subject><subject>Neutrophils</subject><subject>Nontarget organisms</subject><subject>Parasites</subject><subject>Pesticides</subject><subject>Ranidae - blood</subject><subject>Thiamethoxam</subject><subject>Thiamethoxam - toxicity</subject><subject>Thiazoles - toxicity</subject><subject>Water Pollutants, Chemical - analysis</subject><subject>Waterways</subject><issn>0730-7268</issn><issn>1552-8618</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kMFOxCAURYnR6Dia-AWmiRtdVB-0pZ2lTmZ0kom60LhsKAXFVFCgmvkBv9tXR925Irx37iUcQg4onFIAdqaiPM1zWm2QES0KllacVptkBGUGacl4tUN2Q3gGoHwymWyTnQwmQCmwEfmcaa1kDInTCUuulbNGumisM22ysAFXRppW4d4mF51zbTJVXZfceqdNh2NhceI8Ui5E5Z1VeLVS2ehFNM5-Fz8Mubl3jyE5Xpr45BoRMRtW3TtCsg8ne2RLiy6o_Z9zTO7ns7vpVbq8uVxMz5epzCmrUipAQMsLzbguSy1k0_JKt0yVLG-bphSFFlDit0XFmOQ5Z1kpRSEBI1oJno3J0br31bu3XoVYP7veW3yyZiyDDAXBQB2vKeldCF7p-tWbF-FXNYV6EF6j8HoQjujhT2HfvKj2D_w1jEC6Bj7Q1-rfohqZ78Iv1OyLRA</recordid><startdate>201906</startdate><enddate>201906</enddate><creator>Gavel, Melody J.</creator><creator>Richardson, Sarah D.</creator><creator>Dalton, Rebecca L.</creator><creator>Soos, Catherine</creator><creator>Ashby, Brendan</creator><creator>McPhee, Landon</creator><creator>Forbes, Mark R.</creator><creator>Robinson, Stacey A.</creator><general>Blackwell Publishing Ltd</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QO</scope><scope>7SN</scope><scope>7SS</scope><scope>7ST</scope><scope>7T7</scope><scope>7TK</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>K9.</scope><scope>P64</scope><scope>RC3</scope><scope>SOI</scope></search><sort><creationdate>201906</creationdate><title>Effects of 2 Neonicotinoid Insecticides on Blood Cell Profiles and Corticosterone Concentrations of Wood Frogs (Lithobates sylvaticus)</title><author>Gavel, Melody J. ; 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These insecticides are of concern due to their potential impacts on nontarget organisms. Pesticides can affect development of amphibians and suppress the immune system, which could impact disease susceptibility and tolerance. No previous studies on amphibians have examined the effects of these insecticides on differential blood cell proportions or concentrations of corticosterone (a general stress hormone). We investigated the effects of chronic exposure to 2 neonicotinoids, thiamethoxam and clothianidin, on immunometrics of wood frogs (Lithobates sylvaticus). Frogs were exposed to single, chronic treatments of 2.5 or 250 µg/L of clothianidin or thiamethoxam for 7 wk from Gosner stages 25 to 46. The juvenile frogs were then maintained for 3 wk post metamorphosis without exposure to neonicotinoids. We measured water‐borne corticosterone twice: at 6 d and 8 wk after exposure in larval and juvenile frogs, respectively. We assessed differential blood cell profiles from juvenile frogs. Corticosterone was significantly lower in tadpoles exposed to 250 µg/L of thiamethoxam compared with other tadpole treatments, but no significant differences in corticosterone concentrations were found in treatments using juvenile frogs. Anemia was detected in all treatments compared with controls with the exception of tadpoles exposed to 2.5 µg/L of clothianidin. Neutrophil‐to‐leukocyte and neutrophil‐to‐lymphocyte ratios were elevated in frogs exposed to 250 µg/L of thiamethoxam. Collectively, these results indicate that chronic exposure to neonicotinoids has varied impacts on blood cell profiles and corticosterone concentrations of developing wood frogs, which are indicative of stress. Future studies should investigate whether exposure to neonicotinoids increases susceptibility to infection by parasites in both larval and adult wood frogs. Environ Toxicol Chem 2019;38:1273–1284. © 2019 Crown in the right of Canada. Published by Wiley Periodicals Inc. on behalf of SETAC.</abstract><cop>United States</cop><pub>Blackwell Publishing Ltd</pub><pmid>30901102</pmid><doi>10.1002/etc.4418</doi><tpages>12</tpages></addata></record> |
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subjects | Agrochemicals Amphibians Anemia Animals Blood Blood Cells - drug effects Blood Cells - metabolism Canada Chronic exposure Corticosterone Corticosterone - blood Ecotoxicology Exposure Frogs Guanidines - toxicity Immune system Immunological tolerance Insecticides Insecticides - toxicity Larva - drug effects Leukocytes Linear Models Lithobates sylvaticus Lymphocytes Metamorphosis Neonicotinoid Neonicotinoid insecticides Neonicotinoids - toxicity Neutrophils Nontarget organisms Parasites Pesticides Ranidae - blood Thiamethoxam Thiamethoxam - toxicity Thiazoles - toxicity Water Pollutants, Chemical - analysis Waterways |
title | Effects of 2 Neonicotinoid Insecticides on Blood Cell Profiles and Corticosterone Concentrations of Wood Frogs (Lithobates sylvaticus) |
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