Atrazine concentrations, gonadal gross morphology and histology in ranid frogs collected in Michigan agricultural areas

The triazine herbicide atrazine has been suggested to be a potential disruptor of normal sexual development in male frogs. The goals of this study were to collect native ranid frogs from sites in agricultural and non-agricultural areas and determine whether hypothesised atrazine effects on the gonad...

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Veröffentlicht in:Aquatic toxicology 2006-03, Vol.76 (3), p.230-245
Hauptverfasser: Murphy, M.B., Hecker, M., Coady, K.K., Tompsett, A.R., Jones, P.D., Du Preez, L.H., Everson, G.J., Solomon, K.R., Carr, J.A., Smith, E.E., Kendall, R.J., Van Der Kraak, G., Giesy, J.P.
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container_end_page 245
container_issue 3
container_start_page 230
container_title Aquatic toxicology
container_volume 76
creator Murphy, M.B.
Hecker, M.
Coady, K.K.
Tompsett, A.R.
Jones, P.D.
Du Preez, L.H.
Everson, G.J.
Solomon, K.R.
Carr, J.A.
Smith, E.E.
Kendall, R.J.
Van Der Kraak, G.
Giesy, J.P.
description The triazine herbicide atrazine has been suggested to be a potential disruptor of normal sexual development in male frogs. The goals of this study were to collect native ranid frogs from sites in agricultural and non-agricultural areas and determine whether hypothesised atrazine effects on the gonads could be observed at the gross morphological and histological levels. Juvenile and adult green frogs ( Rana clamitans), bullfrogs ( R. catesbeiana) and leopard frogs ( R. pipiens) were collected in the summers of 2002 and 2003. Atrazine concentrations were below the limit of quantification at non-agricultural sites, and concentrations did not exceed 2 μg/L at most agricultural sites. One concentration greater than 200 μg atrazine/L was measured once at one site in 2002. Hermaphroditic individuals with both male and female gonad tissue in either one or both gonads, were found at a low incidence at both non-agricultural and agricultural sites, and in both adults and juveniles. Testicular oocytes (TO) were found in male frogs at most of the sites, with the greatest incidence occurring in juvenile leopard frogs. TO incidence was not significantly different between agricultural and non-agricultural sites with the exception of juveniles collected in 2003. Atrazine concentrations were not significantly correlated with the incidence of hermaphroditism, but maximum atrazine concentrations were correlated with TO incidence in juvenile frogs in 2003. However, given the lack of a consistent relationship between atrazine concentrations and TO incidence, it is more likely the TOs observed in this study result from natural processes in development rather than atrazine exposure.
doi_str_mv 10.1016/j.aquatox.2005.09.010
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The goals of this study were to collect native ranid frogs from sites in agricultural and non-agricultural areas and determine whether hypothesised atrazine effects on the gonads could be observed at the gross morphological and histological levels. Juvenile and adult green frogs ( Rana clamitans), bullfrogs ( R. catesbeiana) and leopard frogs ( R. pipiens) were collected in the summers of 2002 and 2003. Atrazine concentrations were below the limit of quantification at non-agricultural sites, and concentrations did not exceed 2 μg/L at most agricultural sites. One concentration greater than 200 μg atrazine/L was measured once at one site in 2002. Hermaphroditic individuals with both male and female gonad tissue in either one or both gonads, were found at a low incidence at both non-agricultural and agricultural sites, and in both adults and juveniles. Testicular oocytes (TO) were found in male frogs at most of the sites, with the greatest incidence occurring in juvenile leopard frogs. TO incidence was not significantly different between agricultural and non-agricultural sites with the exception of juveniles collected in 2003. Atrazine concentrations were not significantly correlated with the incidence of hermaphroditism, but maximum atrazine concentrations were correlated with TO incidence in juvenile frogs in 2003. However, given the lack of a consistent relationship between atrazine concentrations and TO incidence, it is more likely the TOs observed in this study result from natural processes in development rather than atrazine exposure.</description><identifier>ISSN: 0166-445X</identifier><identifier>EISSN: 1879-1514</identifier><identifier>DOI: 10.1016/j.aquatox.2005.09.010</identifier><identifier>PMID: 16300839</identifier><identifier>CODEN: AQTODG</identifier><language>eng</language><publisher>Amsterdam: Elsevier B.V</publisher><subject>agricultural land ; Agrochemicals - analysis ; Agrochemicals - toxicity ; Amphibia. 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Psychology ; General aspects ; gonads ; Gonads - anatomy &amp; histology ; Gonads - drug effects ; Gonads - pathology ; Gonads - ultrastructure ; Herbicides - analysis ; Herbicides - toxicity ; Hermaphrodite ; hermaphroditism ; histology ; Incidence ; Limb Deformities, Congenital - chemically induced ; Limb Deformities, Congenital - epidemiology ; Limb Deformities, Congenital - veterinary ; Male ; Michigan ; oocytes ; Rana ; Rana catesbeiana ; Rana clamitans ; Ranidae - anatomy &amp; histology ; Ranidae - physiology ; sexual development ; Testicular oocyte ; Time Factors ; Triazine herbicides ; Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution ; Water - chemistry ; Water Pollutants, Chemical - analysis ; Water Pollutants, Chemical - toxicity ; water pollution</subject><ispartof>Aquatic toxicology, 2006-03, Vol.76 (3), p.230-245</ispartof><rights>2005 Elsevier B.V.</rights><rights>2006 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c448t-70651071a532e0100065ecdff1ed3f888478839e1ef4c82e9011c3534a46136b3</citedby><cites>FETCH-LOGICAL-c448t-70651071a532e0100065ecdff1ed3f888478839e1ef4c82e9011c3534a46136b3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktohtml>$$Uhttps://www.sciencedirect.com/science/article/pii/S0166445X05003474$$EHTML$$P50$$Gelsevier$$H</linktohtml><link.rule.ids>314,776,780,3537,27901,27902,65306</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&amp;idt=17537166$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/16300839$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Murphy, M.B.</creatorcontrib><creatorcontrib>Hecker, M.</creatorcontrib><creatorcontrib>Coady, K.K.</creatorcontrib><creatorcontrib>Tompsett, A.R.</creatorcontrib><creatorcontrib>Jones, P.D.</creatorcontrib><creatorcontrib>Du Preez, L.H.</creatorcontrib><creatorcontrib>Everson, G.J.</creatorcontrib><creatorcontrib>Solomon, K.R.</creatorcontrib><creatorcontrib>Carr, J.A.</creatorcontrib><creatorcontrib>Smith, E.E.</creatorcontrib><creatorcontrib>Kendall, R.J.</creatorcontrib><creatorcontrib>Van Der Kraak, G.</creatorcontrib><creatorcontrib>Giesy, J.P.</creatorcontrib><title>Atrazine concentrations, gonadal gross morphology and histology in ranid frogs collected in Michigan agricultural areas</title><title>Aquatic toxicology</title><addtitle>Aquat Toxicol</addtitle><description>The triazine herbicide atrazine has been suggested to be a potential disruptor of normal sexual development in male frogs. The goals of this study were to collect native ranid frogs from sites in agricultural and non-agricultural areas and determine whether hypothesised atrazine effects on the gonads could be observed at the gross morphological and histological levels. Juvenile and adult green frogs ( Rana clamitans), bullfrogs ( R. catesbeiana) and leopard frogs ( R. pipiens) were collected in the summers of 2002 and 2003. Atrazine concentrations were below the limit of quantification at non-agricultural sites, and concentrations did not exceed 2 μg/L at most agricultural sites. One concentration greater than 200 μg atrazine/L was measured once at one site in 2002. Hermaphroditic individuals with both male and female gonad tissue in either one or both gonads, were found at a low incidence at both non-agricultural and agricultural sites, and in both adults and juveniles. Testicular oocytes (TO) were found in male frogs at most of the sites, with the greatest incidence occurring in juvenile leopard frogs. TO incidence was not significantly different between agricultural and non-agricultural sites with the exception of juveniles collected in 2003. Atrazine concentrations were not significantly correlated with the incidence of hermaphroditism, but maximum atrazine concentrations were correlated with TO incidence in juvenile frogs in 2003. However, given the lack of a consistent relationship between atrazine concentrations and TO incidence, it is more likely the TOs observed in this study result from natural processes in development rather than atrazine exposure.</description><subject>agricultural land</subject><subject>Agrochemicals - analysis</subject><subject>Agrochemicals - toxicity</subject><subject>Amphibia. Reptilia</subject><subject>Amphibian</subject><subject>animal morphology</subject><subject>Animal, plant and microbial ecology</subject><subject>Animals</subject><subject>Applied ecology</subject><subject>atrazine</subject><subject>Atrazine - analysis</subject><subject>Atrazine - toxicity</subject><subject>bioaccumulation</subject><subject>Biological and medical sciences</subject><subject>Disorders of Sex Development - chemically induced</subject><subject>Disorders of Sex Development - epidemiology</subject><subject>Disorders of Sex Development - veterinary</subject><subject>Ecotoxicology, biological effects of pollution</subject><subject>Female</subject><subject>Field study</subject><subject>Freshwater</subject><subject>frogs</subject><subject>Fundamental and applied biological sciences. 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Reptilia</topic><topic>Amphibian</topic><topic>animal morphology</topic><topic>Animal, plant and microbial ecology</topic><topic>Animals</topic><topic>Applied ecology</topic><topic>atrazine</topic><topic>Atrazine - analysis</topic><topic>Atrazine - toxicity</topic><topic>bioaccumulation</topic><topic>Biological and medical sciences</topic><topic>Disorders of Sex Development - chemically induced</topic><topic>Disorders of Sex Development - epidemiology</topic><topic>Disorders of Sex Development - veterinary</topic><topic>Ecotoxicology, biological effects of pollution</topic><topic>Female</topic><topic>Field study</topic><topic>Freshwater</topic><topic>frogs</topic><topic>Fundamental and applied biological sciences. 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The goals of this study were to collect native ranid frogs from sites in agricultural and non-agricultural areas and determine whether hypothesised atrazine effects on the gonads could be observed at the gross morphological and histological levels. Juvenile and adult green frogs ( Rana clamitans), bullfrogs ( R. catesbeiana) and leopard frogs ( R. pipiens) were collected in the summers of 2002 and 2003. Atrazine concentrations were below the limit of quantification at non-agricultural sites, and concentrations did not exceed 2 μg/L at most agricultural sites. One concentration greater than 200 μg atrazine/L was measured once at one site in 2002. Hermaphroditic individuals with both male and female gonad tissue in either one or both gonads, were found at a low incidence at both non-agricultural and agricultural sites, and in both adults and juveniles. Testicular oocytes (TO) were found in male frogs at most of the sites, with the greatest incidence occurring in juvenile leopard frogs. TO incidence was not significantly different between agricultural and non-agricultural sites with the exception of juveniles collected in 2003. Atrazine concentrations were not significantly correlated with the incidence of hermaphroditism, but maximum atrazine concentrations were correlated with TO incidence in juvenile frogs in 2003. However, given the lack of a consistent relationship between atrazine concentrations and TO incidence, it is more likely the TOs observed in this study result from natural processes in development rather than atrazine exposure.</abstract><cop>Amsterdam</cop><pub>Elsevier B.V</pub><pmid>16300839</pmid><doi>10.1016/j.aquatox.2005.09.010</doi><tpages>16</tpages></addata></record>
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identifier ISSN: 0166-445X
ispartof Aquatic toxicology, 2006-03, Vol.76 (3), p.230-245
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1879-1514
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subjects agricultural land
Agrochemicals - analysis
Agrochemicals - toxicity
Amphibia. Reptilia
Amphibian
animal morphology
Animal, plant and microbial ecology
Animals
Applied ecology
atrazine
Atrazine - analysis
Atrazine - toxicity
bioaccumulation
Biological and medical sciences
Disorders of Sex Development - chemically induced
Disorders of Sex Development - epidemiology
Disorders of Sex Development - veterinary
Ecotoxicology, biological effects of pollution
Female
Field study
Freshwater
frogs
Fundamental and applied biological sciences. Psychology
General aspects
gonads
Gonads - anatomy & histology
Gonads - drug effects
Gonads - pathology
Gonads - ultrastructure
Herbicides - analysis
Herbicides - toxicity
Hermaphrodite
hermaphroditism
histology
Incidence
Limb Deformities, Congenital - chemically induced
Limb Deformities, Congenital - epidemiology
Limb Deformities, Congenital - veterinary
Male
Michigan
oocytes
Rana
Rana catesbeiana
Rana clamitans
Ranidae - anatomy & histology
Ranidae - physiology
sexual development
Testicular oocyte
Time Factors
Triazine herbicides
Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution
Water - chemistry
Water Pollutants, Chemical - analysis
Water Pollutants, Chemical - toxicity
water pollution
title Atrazine concentrations, gonadal gross morphology and histology in ranid frogs collected in Michigan agricultural areas
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