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Bti sprays do not adversely affect non‐target aquatic invertebrates in French Atlantic coastal wetlands

Both the increase in human mobility and climate change contribute to the globalization of vector‐borne diseases. Some mosquito species are efficient disease vectors in Europe, thus increasing the risk of epidemic (re)emergence. Bacillus thuringiensis var. israelensis (Bti) is considered as the most...

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Published in:The Journal of applied ecology 2014-02, Vol.51 (1), p.102-113
Main Authors: Lagadic, Laurent, Roucaute, Marc, Caquet, Thierry, Arnott, Shelley
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Roucaute, Marc
Caquet, Thierry
Arnott, Shelley
description Both the increase in human mobility and climate change contribute to the globalization of vector‐borne diseases. Some mosquito species are efficient disease vectors in Europe, thus increasing the risk of epidemic (re)emergence. Bacillus thuringiensis var. israelensis (Bti) is considered as the most efficient larvicide to control mosquito populations with negligible environmental impacts. However, repeated field applications of Bti over many years raise the question of possible long‐term effects on non‐target invertebrates with putative subsequent alterations of food webs. Environmental effects of Bti have mainly been studied in continental freshwater wetlands. Much less is known for brackish water coastal wetlands. We investigated whether repeated treatments with Bti, applied as VectoBac® WG over seven consecutive years, may affect non‐target invertebrate communities in wetlands of the French Atlantic coast. Particular attention was devoted to invertebrates potentially used as food sources by shorebirds and wading birds. Invertebrates were sampled in the water and sediment of control and VectoBac®‐treated saltmarsh pools between 2006 and 2012. Taxa abundance data were used to calculate community descriptors and to analyse the potential structural changes due to VectoBac® using the principal response curve method and similarity analysis. Physicochemical parameters were measured in the same pools so that homogeneity of the environmental conditions between the control and treated areas could be tested. We demonstrated that long‐term use of VectoBac® WG in French Atlantic coastal wetlands had no influence on the temporal evolution of the taxonomic structure and taxa abundance of non‐target aquatic invertebrate communities, which is highly driven by abiotic factors. In addition, over the long term, the amount of invertebrates that could be used as food resources by birds is maintained in VectoBac®‐treated areas. Synthesis and applications. Reduced application rate and targeted spraying of VectoBac® WG in mosquito breeding sites minimize potential environmental impacts of Bacillus thuringiensis var. israelensis (Bti). Even so, surveillance of its possible primary side effects is needed, which requires comparable control and treated areas. Indeed, systematic temporal trends and subtle differences in the range of variation of abiotic factors result in discrepancies between control and treated area in terms of invertebrate abundance, which could be wrongly attribut
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Some mosquito species are efficient disease vectors in Europe, thus increasing the risk of epidemic (re)emergence. Bacillus thuringiensis var. israelensis (Bti) is considered as the most efficient larvicide to control mosquito populations with negligible environmental impacts. However, repeated field applications of Bti over many years raise the question of possible long‐term effects on non‐target invertebrates with putative subsequent alterations of food webs. Environmental effects of Bti have mainly been studied in continental freshwater wetlands. Much less is known for brackish water coastal wetlands. We investigated whether repeated treatments with Bti, applied as VectoBac® WG over seven consecutive years, may affect non‐target invertebrate communities in wetlands of the French Atlantic coast. Particular attention was devoted to invertebrates potentially used as food sources by shorebirds and wading birds. Invertebrates were sampled in the water and sediment of control and VectoBac®‐treated saltmarsh pools between 2006 and 2012. Taxa abundance data were used to calculate community descriptors and to analyse the potential structural changes due to VectoBac® using the principal response curve method and similarity analysis. Physicochemical parameters were measured in the same pools so that homogeneity of the environmental conditions between the control and treated areas could be tested. We demonstrated that long‐term use of VectoBac® WG in French Atlantic coastal wetlands had no influence on the temporal evolution of the taxonomic structure and taxa abundance of non‐target aquatic invertebrate communities, which is highly driven by abiotic factors. In addition, over the long term, the amount of invertebrates that could be used as food resources by birds is maintained in VectoBac®‐treated areas. Synthesis and applications. Reduced application rate and targeted spraying of VectoBac® WG in mosquito breeding sites minimize potential environmental impacts of Bacillus thuringiensis var. israelensis (Bti). Even so, surveillance of its possible primary side effects is needed, which requires comparable control and treated areas. Indeed, systematic temporal trends and subtle differences in the range of variation of abiotic factors result in discrepancies between control and treated area in terms of invertebrate abundance, which could be wrongly attributed to VectoBac®. Management decisions and mitigation measures may therefore benefit from (i) extending surveillance to a time frame that allows for coverage of the immense temporal variation in taxa abundance and diversity and (ii) the inclusion of environmental variables in the monitoring of non‐target animal communities potentially exposed to Bti.</description><identifier>ISSN: 0021-8901</identifier><identifier>EISSN: 1365-2664</identifier><identifier>DOI: 10.1111/1365-2664.12165</identifier><identifier>CODEN: JAPEAI</identifier><language>eng</language><publisher>Oxford: John Wiley &amp; Sons Ltd</publisher><subject>adverse effects ; Animal and plant ecology ; Animal communities ; Animal, plant and microbial ecology ; application rate ; Applied ecology ; aquatic invertebrates ; Aves ; Bacillus thuringiensis ; Bacillus thuringiensis israelensis ; Bacillus thuringiensis subsp. israelensis ; Biological and medical sciences ; bird food resources ; brackish water ; Brackish water ecosystems ; brackish water pools ; breeding ; breeding sites ; Climate change ; coastal water ; Culicidae ; disease vectors ; environmental factors ; environmental impact ; evolution ; Flood control ; food webs ; foods ; freshwater ; Fundamental and applied biological sciences. Psychology ; General aspects ; globalization ; Insect larvae ; Invasive speices and pest management ; Invertebrata ; Invertebrates ; larvicide ; Life Sciences ; long‐term field biomonitoring ; Medically important nuisances and vectors, pests of stored products and materials: population survey and control ; monitoring ; Mosquito control ; Mosquitoes ; Mosquitos ; non‐target invertebrates ; Pathogens ; physicochemical properties ; risk ; Salinity ; salt marshes ; saltmarshes ; sediments ; spraying ; Synecology ; Taxa ; taxonomic richness and diversity ; temporal variation ; Vectors. Intermediate hosts ; Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution ; water birds ; Wetlands</subject><ispartof>The Journal of applied ecology, 2014-02, Vol.51 (1), p.102-113</ispartof><rights>2014 British Ecological Society</rights><rights>2013 The Authors. Journal of Applied Ecology © 2013 British Ecological Society</rights><rights>2015 INIST-CNRS</rights><rights>Copyright Blackwell Publishing Ltd. 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Some mosquito species are efficient disease vectors in Europe, thus increasing the risk of epidemic (re)emergence. Bacillus thuringiensis var. israelensis (Bti) is considered as the most efficient larvicide to control mosquito populations with negligible environmental impacts. However, repeated field applications of Bti over many years raise the question of possible long‐term effects on non‐target invertebrates with putative subsequent alterations of food webs. Environmental effects of Bti have mainly been studied in continental freshwater wetlands. Much less is known for brackish water coastal wetlands. We investigated whether repeated treatments with Bti, applied as VectoBac® WG over seven consecutive years, may affect non‐target invertebrate communities in wetlands of the French Atlantic coast. Particular attention was devoted to invertebrates potentially used as food sources by shorebirds and wading birds. Invertebrates were sampled in the water and sediment of control and VectoBac®‐treated saltmarsh pools between 2006 and 2012. Taxa abundance data were used to calculate community descriptors and to analyse the potential structural changes due to VectoBac® using the principal response curve method and similarity analysis. Physicochemical parameters were measured in the same pools so that homogeneity of the environmental conditions between the control and treated areas could be tested. We demonstrated that long‐term use of VectoBac® WG in French Atlantic coastal wetlands had no influence on the temporal evolution of the taxonomic structure and taxa abundance of non‐target aquatic invertebrate communities, which is highly driven by abiotic factors. In addition, over the long term, the amount of invertebrates that could be used as food resources by birds is maintained in VectoBac®‐treated areas. Synthesis and applications. Reduced application rate and targeted spraying of VectoBac® WG in mosquito breeding sites minimize potential environmental impacts of Bacillus thuringiensis var. israelensis (Bti). Even so, surveillance of its possible primary side effects is needed, which requires comparable control and treated areas. Indeed, systematic temporal trends and subtle differences in the range of variation of abiotic factors result in discrepancies between control and treated area in terms of invertebrate abundance, which could be wrongly attributed to VectoBac®. 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Psychology</subject><subject>General aspects</subject><subject>globalization</subject><subject>Insect larvae</subject><subject>Invasive speices and pest management</subject><subject>Invertebrata</subject><subject>Invertebrates</subject><subject>larvicide</subject><subject>Life Sciences</subject><subject>long‐term field biomonitoring</subject><subject>Medically important nuisances and vectors, pests of stored products and materials: population survey and control</subject><subject>monitoring</subject><subject>Mosquito control</subject><subject>Mosquitoes</subject><subject>Mosquitos</subject><subject>non‐target invertebrates</subject><subject>Pathogens</subject><subject>physicochemical properties</subject><subject>risk</subject><subject>Salinity</subject><subject>salt marshes</subject><subject>saltmarshes</subject><subject>sediments</subject><subject>spraying</subject><subject>Synecology</subject><subject>Taxa</subject><subject>taxonomic richness and diversity</subject><subject>temporal variation</subject><subject>Vectors. 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Some mosquito species are efficient disease vectors in Europe, thus increasing the risk of epidemic (re)emergence. Bacillus thuringiensis var. israelensis (Bti) is considered as the most efficient larvicide to control mosquito populations with negligible environmental impacts. However, repeated field applications of Bti over many years raise the question of possible long‐term effects on non‐target invertebrates with putative subsequent alterations of food webs. Environmental effects of Bti have mainly been studied in continental freshwater wetlands. Much less is known for brackish water coastal wetlands. We investigated whether repeated treatments with Bti, applied as VectoBac® WG over seven consecutive years, may affect non‐target invertebrate communities in wetlands of the French Atlantic coast. Particular attention was devoted to invertebrates potentially used as food sources by shorebirds and wading birds. Invertebrates were sampled in the water and sediment of control and VectoBac®‐treated saltmarsh pools between 2006 and 2012. Taxa abundance data were used to calculate community descriptors and to analyse the potential structural changes due to VectoBac® using the principal response curve method and similarity analysis. Physicochemical parameters were measured in the same pools so that homogeneity of the environmental conditions between the control and treated areas could be tested. We demonstrated that long‐term use of VectoBac® WG in French Atlantic coastal wetlands had no influence on the temporal evolution of the taxonomic structure and taxa abundance of non‐target aquatic invertebrate communities, which is highly driven by abiotic factors. In addition, over the long term, the amount of invertebrates that could be used as food resources by birds is maintained in VectoBac®‐treated areas. Synthesis and applications. Reduced application rate and targeted spraying of VectoBac® WG in mosquito breeding sites minimize potential environmental impacts of Bacillus thuringiensis var. israelensis (Bti). Even so, surveillance of its possible primary side effects is needed, which requires comparable control and treated areas. Indeed, systematic temporal trends and subtle differences in the range of variation of abiotic factors result in discrepancies between control and treated area in terms of invertebrate abundance, which could be wrongly attributed to VectoBac®. Management decisions and mitigation measures may therefore benefit from (i) extending surveillance to a time frame that allows for coverage of the immense temporal variation in taxa abundance and diversity and (ii) the inclusion of environmental variables in the monitoring of non‐target animal communities potentially exposed to Bti.</abstract><cop>Oxford</cop><pub>John Wiley &amp; Sons Ltd</pub><doi>10.1111/1365-2664.12165</doi><tpages>12</tpages><oa>free_for_read</oa></addata></record>
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ispartof The Journal of applied ecology, 2014-02, Vol.51 (1), p.102-113
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subjects adverse effects
Animal and plant ecology
Animal communities
Animal, plant and microbial ecology
application rate
Applied ecology
aquatic invertebrates
Aves
Bacillus thuringiensis
Bacillus thuringiensis israelensis
Bacillus thuringiensis subsp. israelensis
Biological and medical sciences
bird food resources
brackish water
Brackish water ecosystems
brackish water pools
breeding
breeding sites
Climate change
coastal water
Culicidae
disease vectors
environmental factors
environmental impact
evolution
Flood control
food webs
foods
freshwater
Fundamental and applied biological sciences. Psychology
General aspects
globalization
Insect larvae
Invasive speices and pest management
Invertebrata
Invertebrates
larvicide
Life Sciences
long‐term field biomonitoring
Medically important nuisances and vectors, pests of stored products and materials: population survey and control
monitoring
Mosquito control
Mosquitoes
Mosquitos
non‐target invertebrates
Pathogens
physicochemical properties
risk
Salinity
salt marshes
saltmarshes
sediments
spraying
Synecology
Taxa
taxonomic richness and diversity
temporal variation
Vectors. Intermediate hosts
Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution
water birds
Wetlands
title Bti sprays do not adversely affect non‐target aquatic invertebrates in French Atlantic coastal wetlands
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