Invasion potential of hornets (Hymenoptera: Vespidae: Vespa spp.)
Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies u...
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Published in | Frontiers in insect science Vol. 3; p. 1145158 |
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Main Authors | , , |
Format | Journal Article |
Language | English |
Published |
Switzerland
Frontiers Media S.A
09.05.2023
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Subjects | |
Online Access | Get full text |
ISSN | 2673-8600 2673-8600 |
DOI | 10.3389/finsc.2023.1145158 |
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Abstract | Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies using local food and nest materials. Of the 22 species in the genus
Vespa
, five species are now naturalized far from their endemic populations and another four have been detected either in nature or during inspections at borders of other countries. By far the most likely pathway of long-distance dispersal is the transport of gynes in transoceanic shipments of goods. Thereafter, natural dispersal of gynes in spring and accidental local transport by humans cause shorter-range expansions and contribute to the invasion process. Propagule pressure of hornets is unquantified, although it is likely low but unrelenting. The success of introduced populations is limited by low propagule size and the consequences of genetic founder effects, including the extinction vortex linked to single-locus, complementary sex determination of most hymenopterans. Invasion success is enhanced by climatic similarity between source locality and introduction site, as well as genetic diversity conferred by polyandry in some species. These and other factors that may have influenced the successful establishment of invasive populations of
V. velutina
,
V. tropica
,
V. bicolor
,
V. orientalis
, and
V. crabro
are discussed. The highly publicized detections of
V. mandarinia
in North America and research into its status provide a real-time example of an unfolding hornet invasion. |
---|---|
AbstractList | Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies using local food and nest materials. Of the 22 species in the genus
, five species are now naturalized far from their endemic populations and another four have been detected either in nature or during inspections at borders of other countries. By far the most likely pathway of long-distance dispersal is the transport of gynes in transoceanic shipments of goods. Thereafter, natural dispersal of gynes in spring and accidental local transport by humans cause shorter-range expansions and contribute to the invasion process. Propagule pressure of hornets is unquantified, although it is likely low but unrelenting. The success of introduced populations is limited by low propagule size and the consequences of genetic founder effects, including the extinction vortex linked to single-locus, complementary sex determination of most hymenopterans. Invasion success is enhanced by climatic similarity between source locality and introduction site, as well as genetic diversity conferred by polyandry in some species. These and other factors that may have influenced the successful establishment of invasive populations of
,
,
,
, and
are discussed. The highly publicized detections of
in North America and research into its status provide a real-time example of an unfolding hornet invasion. Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies using local food and nest materials. Of the 22 species in the genus Vespa, five species are now naturalized far from their endemic populations and another four have been detected either in nature or during inspections at borders of other countries. By far the most likely pathway of long-distance dispersal is the transport of gynes in transoceanic shipments of goods. Thereafter, natural dispersal of gynes in spring and accidental local transport by humans cause shorter-range expansions and contribute to the invasion process. Propagule pressure of hornets is unquantified, although it is likely low but unrelenting. The success of introduced populations is limited by low propagule size and the consequences of genetic founder effects, including the extinction vortex linked to single-locus, complementary sex determination of most hymenopterans. Invasion success is enhanced by climatic similarity between source locality and introduction site, as well as genetic diversity conferred by polyandry in some species. These and other factors that may have influenced the successful establishment of invasive populations of V. velutina, V. tropica, V. bicolor, V. orientalis, and V. crabro are discussed. The highly publicized detections of V. mandarinia in North America and research into its status provide a real-time example of an unfolding hornet invasion.Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies using local food and nest materials. Of the 22 species in the genus Vespa, five species are now naturalized far from their endemic populations and another four have been detected either in nature or during inspections at borders of other countries. By far the most likely pathway of long-distance dispersal is the transport of gynes in transoceanic shipments of goods. Thereafter, natural dispersal of gynes in spring and accidental local transport by humans cause shorter-range expansions and contribute to the invasion process. Propagule pressure of hornets is unquantified, although it is likely low but unrelenting. The success of introduced populations is limited by low propagule size and the consequences of genetic founder effects, including the extinction vortex linked to single-locus, complementary sex determination of most hymenopterans. Invasion success is enhanced by climatic similarity between source locality and introduction site, as well as genetic diversity conferred by polyandry in some species. These and other factors that may have influenced the successful establishment of invasive populations of V. velutina, V. tropica, V. bicolor, V. orientalis, and V. crabro are discussed. The highly publicized detections of V. mandarinia in North America and research into its status provide a real-time example of an unfolding hornet invasion. Hornets are large, predatory wasps that have the potential to alter biotic communities and harm honey bee colonies once established in non-native locations. Mated, diapausing females (gynes) can easily be transported to new habitats, where their behavioral flexibility allows them to found colonies using local food and nest materials. Of the 22 species in the genus Vespa , five species are now naturalized far from their endemic populations and another four have been detected either in nature or during inspections at borders of other countries. By far the most likely pathway of long-distance dispersal is the transport of gynes in transoceanic shipments of goods. Thereafter, natural dispersal of gynes in spring and accidental local transport by humans cause shorter-range expansions and contribute to the invasion process. Propagule pressure of hornets is unquantified, although it is likely low but unrelenting. The success of introduced populations is limited by low propagule size and the consequences of genetic founder effects, including the extinction vortex linked to single-locus, complementary sex determination of most hymenopterans. Invasion success is enhanced by climatic similarity between source locality and introduction site, as well as genetic diversity conferred by polyandry in some species. These and other factors that may have influenced the successful establishment of invasive populations of V. velutina , V. tropica , V. bicolor , V. orientalis , and V. crabro are discussed. The highly publicized detections of V. mandarinia in North America and research into its status provide a real-time example of an unfolding hornet invasion. |
Author | Mattila, Heather R. Otis, Gard W. Taylor, Benjamin A. |
AuthorAffiliation | 2 Institute of Bee Health, Vetsuisse Faculty, University of Bern and Agroscope , Bern , Switzerland 1 School of Environmental Sciences, University of Guelph , Guelph, ON , Canada 3 Department of Entomology, Purdue University , West Lafayette, IN , United States 4 Department of Biological Sciences, Wellesley College , Wellesley, MA , United States |
AuthorAffiliation_xml | – name: 2 Institute of Bee Health, Vetsuisse Faculty, University of Bern and Agroscope , Bern , Switzerland – name: 4 Department of Biological Sciences, Wellesley College , Wellesley, MA , United States – name: 1 School of Environmental Sciences, University of Guelph , Guelph, ON , Canada – name: 3 Department of Entomology, Purdue University , West Lafayette, IN , United States |
Author_xml | – sequence: 1 givenname: Gard W. surname: Otis fullname: Otis, Gard W. – sequence: 2 givenname: Benjamin A. surname: Taylor fullname: Taylor, Benjamin A. – sequence: 3 givenname: Heather R. surname: Mattila fullname: Mattila, Heather R. |
BackLink | https://www.ncbi.nlm.nih.gov/pubmed/38469472$$D View this record in MEDLINE/PubMed |
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CitedBy_id | crossref_primary_10_4081_bollettinosei_2024_111 crossref_primary_10_5141_jee_24_071 crossref_primary_10_3389_finsc_2024_1384598 crossref_primary_10_3390_insects15070546 crossref_primary_10_1002_ece3_11615 crossref_primary_10_3390_life14030283 crossref_primary_10_3389_finsc_2023_1136297 crossref_primary_10_3390_life14101293 crossref_primary_10_1111_1365_2656_14224 crossref_primary_10_1002_ece3_70502 crossref_primary_10_1111_1744_7917_13448 crossref_primary_10_1016_j_jip_2024_108215 crossref_primary_10_3389_frbee_2024_1374852 crossref_primary_10_3390_insects15080601 crossref_primary_10_70186_baeeRTCL6324 crossref_primary_10_1038_s41598_024_61534_0 crossref_primary_10_3390_app13137414 |
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Copyright | Copyright © 2023 Otis, Taylor and Mattila. Copyright © 2023 Otis, Taylor and Mattila 2023 Otis, Taylor and Mattila |
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Keywords | extinction vortex giant hornet propagule pressure Asian hornet invasion potential Vespa invasive species |
Language | English |
License | Copyright © 2023 Otis, Taylor and Mattila. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms. |
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Notes | ObjectType-Article-1 SourceType-Scholarly Journals-1 ObjectType-Feature-2 ObjectType-Review-3 content type line 23 Edited by: Xesús Feás, Academy of Veterinary Sciences of Galicia, Spain ORCID: Gard W. Otis, orcid.org/0000-0001-9826-9013; Benjamin A. Taylor, orcid.org/0000-0001-8634-0484; Heather R. Mattila, orcid.org/0000-0001-5172-1688 Reviewed by: Simone Lioy, Independent researcher, Turin, Italy; Hannah J. Penn, Agricultural Research Service (USDA), United States; Laura Bortolotti, Council for Agricultural and Economics Research (CREA), Italy |
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32 B269 Delaplane (B142) 2021; 75 Colautti (B107) 2006; 8 Graziani (B40) 2021; 12 Moller (B3) 1996; 78 Lester (B196) 2020; 10 B260 Looney (B33) 2023; 96 Matsuura (B18) 1988; 23 Quaresma (B125) 2022; 24 Zayed (B158) 2005; 102 Cappa (B275) 2021; 12 Cook (B154) 1995; 10 Villemant (B78) 2011; 144 Bradshaw (B206) 2016; 7 B276 Hijmans (B214) 2006; 12 Poidatz (B247) 2018; 109 Toft (B177) 2004; 28 Crowder (B5) 2010; 12 Dvořák (B42) 2006; 36 Tan (B253) 2007; 94 Buysson (B34) 1905; 73 Ekroth (B165) 2019; 286 Ríos (B35) 2020; 46 Park (B232) 2016; 31 Abe (B91) 1991 Garnas (B122) 2016; 18 Milanesio (B191) 2017; 7 Meiborg (B197) 2023; 13 Goodisman (B143) 2007; 61 Strauss (B167) 2012; 26 Dong (B186) 2022; 32 Essl (B111) 2015; 65 Franklin (B212) 2010 van Wilgenburg (B153) 2006; 3 Leza (B189) 2021; 77 Lioy (B179) 2020; 11 Cohen (B76) 2022; 47 Martin (B96) 2017 Harpur (B157) 2013; 146 Lioy (B190) 2021; 11 van Itterbeeck (B183) 2021; 24 Power (B172) 2022; 12 Turchi (B169) 2018; 142 Cappa (B248) 2022; 42 Hanna (B8) 2014; 16 Archer (B77) 1991; 6 Matsuura (B72) 1966; 34 Lockwood (B106) 2005; 20 Thomas (B176) 1960 Harris (B101) 1995; 22 Park (B201) 2004; 9 Courchamp (B159) 2008 Kiewhuo (B95) 2022; 8 Verdasca (B63) 2021; 69 Takahashi (B129) 2006; 41 Simberloff (B198) 2003; 51 B185 Landolt (B30) 2010; 2629 Takahashi (B68) 2018; 30 Bock (B209) 2015; 24 Choi (B12) 2012; 15 Oldroyd (B148) 2007; 22 Work (B112) 2005; 7 Foster (B132) 1999; 46 Mattila (B144) 2007; 317 Demichelis (B182) 2014; 67 Martin (B75) 1995; 49 Lioy (B88) 2019; 46 Dlugosch (B121) 2015; 24 Rome (B251) 2021; 57 Granato (B239) 2019; 21 Taylor (B123) 2005; 8 Dillane (B204) 2022; 93 Beggs (B9) 2011; 56 Mattila (B271) 2021; 8 Matsuura (B2) 1991 Kim (B218) 2021; 193 B199 Fujiwara (B270) 2018; 21 Norderud (B281) 2021; 21 Frankham (B126) 2005; 126 B195 Elton (B261) 1958 Matsuura (B74) 1990 Takahashi (B136) 2002; 37 Takeuchi (B64) 2017; 64 Hanna (B10) 2014; 95 Archer (B23) 2012 Simberloff (B105) 2009; 40 Archer (B226) 1994; 130 Zhu (B223) 2020; 117 Levine (B81) 2003; 17 Yang (B174) 2020; 12 Matsuura (B21) 1990 Gereys (B37) 2021; 9 Verdasca (B234) 2022; 10 De Jong (B15) 1990 Mortier (B120) 2021; 102 Sandeman (B73) 1936; 11 Marzoli (B171) 2020; 68 Carpenter (B46) 1997; 1 Monceau (B117) 2013; 8 Jeong (B164) 2021; 24 Smith-Pardo (B65) 2020; 4 Lande (B118) 2015; 24 Archer (B268) 1995; 131 Anderson (B216) 2012; 1260 Choi (B238) 2013; 43 Lockwood (B104) 2009; 15 Mattila (B138); 3 Werenkraut (B259) 2022; 51 Hagan (B160) 2021; 46 Matsuura (B280) 2002; 53 Mattila (B272) 2020; 15 Dlugosch (B151) 2008; 17 Owens (B217) 2013; 263 Fajardo (B51) 2020; 52 Snyder (B6) 2006; 37 Bessa (B215) 2016; 9 Loope (B140) 2014; 14 Ying (B98) 2008 Abou-Shaara (B235) 2022; 24 Ono (B273) 1995; 377 Darrouzet (B155) 2015; 10 Leung (B150) 2022; 170 Kissling (B194) 2013; 89 Takahashi (B134) 2004; 22 Azmy (B277) 2016; 18 Perrard (B250) 2009; 45 Takahashi (B130) 2007; 10 Turner (B85) 2021; 30 Jones (B139) 2020; 10 Barbet-Massin (B86) 2020; 55 |
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Title | Invasion potential of hornets (Hymenoptera: Vespidae: Vespa spp.) |
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