Risk management to prioritise the eradication of new and emerging invasive non-native species
Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has rece...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Booy, Olaf [verfasserIn] Mill, Aileen C. [verfasserIn] Roy, Helen E. [verfasserIn] Hiley, Alice [verfasserIn] Moore, Niall [verfasserIn] Robertson, Pete [verfasserIn] Baker, Simon [verfasserIn] Brazier, Matt [verfasserIn] Bue, Mathilde [verfasserIn] Bullock, Richard [verfasserIn] Campbell, Steve [verfasserIn] Eyre, Dominic [verfasserIn] Foster, Jim [verfasserIn] Hatton-Ellis, Maggie [verfasserIn] Long, Jo [verfasserIn] Macadam, Craig [verfasserIn] Morrison-Bell, Camilla [verfasserIn] Mumford, John [verfasserIn] Newman, Jonathan [verfasserIn] Parrott, David [verfasserIn] Payne, Robin [verfasserIn] Renals, Trevor [verfasserIn] Rodgers, Eoina [verfasserIn] Spencer, Mark [verfasserIn] Stebbing, Paul [verfasserIn] Sutton-Croft, Mike [verfasserIn] Walker, Kevin J. [verfasserIn] Ward, Alastair [verfasserIn] Whittaker, Stan [verfasserIn] Wyn, Gabe [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2017 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Biological invasions - Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999, 19(2017), 8 vom: 15. Mai, Seite 2401-2417 |
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| Übergeordnetes Werk: |
volume:19 ; year:2017 ; number:8 ; day:15 ; month:05 ; pages:2401-2417 |
| Links: |
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| DOI / URN: |
10.1007/s10530-017-1451-z |
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| Katalog-ID: |
SPR010897356 |
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| 245 | 1 | 0 | |a Risk management to prioritise the eradication of new and emerging invasive non-native species |
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| 520 | |a Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. | ||
| 650 | 4 | |a Risk analysis |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Resource management |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Feasibility of eradication |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Contingency planning |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Great Britain |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a NNRM |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Mill, Aileen C. |e verfasserin |4 aut | |
| 700 | 1 | |a Roy, Helen E. |e verfasserin |4 aut | |
| 700 | 1 | |a Hiley, Alice |e verfasserin |4 aut | |
| 700 | 1 | |a Moore, Niall |e verfasserin |4 aut | |
| 700 | 1 | |a Robertson, Pete |e verfasserin |4 aut | |
| 700 | 1 | |a Baker, Simon |e verfasserin |4 aut | |
| 700 | 1 | |a Brazier, Matt |e verfasserin |4 aut | |
| 700 | 1 | |a Bue, Mathilde |e verfasserin |4 aut | |
| 700 | 1 | |a Bullock, Richard |e verfasserin |4 aut | |
| 700 | 1 | |a Campbell, Steve |e verfasserin |4 aut | |
| 700 | 1 | |a Eyre, Dominic |e verfasserin |4 aut | |
| 700 | 1 | |a Foster, Jim |e verfasserin |4 aut | |
| 700 | 1 | |a Hatton-Ellis, Maggie |e verfasserin |4 aut | |
| 700 | 1 | |a Long, Jo |e verfasserin |4 aut | |
| 700 | 1 | |a Macadam, Craig |e verfasserin |4 aut | |
| 700 | 1 | |a Morrison-Bell, Camilla |e verfasserin |4 aut | |
| 700 | 1 | |a Mumford, John |e verfasserin |4 aut | |
| 700 | 1 | |a Newman, Jonathan |e verfasserin |4 aut | |
| 700 | 1 | |a Parrott, David |e verfasserin |4 aut | |
| 700 | 1 | |a Payne, Robin |e verfasserin |4 aut | |
| 700 | 1 | |a Renals, Trevor |e verfasserin |4 aut | |
| 700 | 1 | |a Rodgers, Eoina |e verfasserin |4 aut | |
| 700 | 1 | |a Spencer, Mark |e verfasserin |4 aut | |
| 700 | 1 | |a Stebbing, Paul |e verfasserin |4 aut | |
| 700 | 1 | |a Sutton-Croft, Mike |e verfasserin |4 aut | |
| 700 | 1 | |a Walker, Kevin J. |e verfasserin |4 aut | |
| 700 | 1 | |a Ward, Alastair |e verfasserin |4 aut | |
| 700 | 1 | |a Whittaker, Stan |e verfasserin |4 aut | |
| 700 | 1 | |a Wyn, Gabe |e verfasserin |4 aut | |
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10.1007/s10530-017-1451-z doi (DE-627)SPR010897356 (SPR)s10530-017-1451-z-e DE-627 ger DE-627 rakwb eng 570 ASE 42.00 bkl Booy, Olaf verfasserin aut Risk management to prioritise the eradication of new and emerging invasive non-native species 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. Risk analysis (dpeaa)DE-He213 Resource management (dpeaa)DE-He213 Feasibility of eradication (dpeaa)DE-He213 Contingency planning (dpeaa)DE-He213 Great Britain (dpeaa)DE-He213 NNRM (dpeaa)DE-He213 Mill, Aileen C. verfasserin aut Roy, Helen E. verfasserin aut Hiley, Alice verfasserin aut Moore, Niall verfasserin aut Robertson, Pete verfasserin aut Baker, Simon verfasserin aut Brazier, Matt verfasserin aut Bue, Mathilde verfasserin aut Bullock, Richard verfasserin aut Campbell, Steve verfasserin aut Eyre, Dominic verfasserin aut Foster, Jim verfasserin aut Hatton-Ellis, Maggie verfasserin aut Long, Jo verfasserin aut Macadam, Craig verfasserin aut Morrison-Bell, Camilla verfasserin aut Mumford, John verfasserin aut Newman, Jonathan verfasserin aut Parrott, David verfasserin aut Payne, Robin verfasserin aut Renals, Trevor verfasserin aut Rodgers, Eoina verfasserin aut Spencer, Mark verfasserin aut Stebbing, Paul verfasserin aut Sutton-Croft, Mike verfasserin aut Walker, Kevin J. verfasserin aut Ward, Alastair verfasserin aut Whittaker, Stan verfasserin aut Wyn, Gabe verfasserin aut Enthalten in Biological invasions Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999 19(2017), 8 vom: 15. Mai, Seite 2401-2417 (DE-627)320524477 (DE-600)2014991-8 1573-1464 nnns volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 https://dx.doi.org/10.1007/s10530-017-1451-z kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.00 ASE AR 19 2017 8 15 05 2401-2417 |
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10.1007/s10530-017-1451-z doi (DE-627)SPR010897356 (SPR)s10530-017-1451-z-e DE-627 ger DE-627 rakwb eng 570 ASE 42.00 bkl Booy, Olaf verfasserin aut Risk management to prioritise the eradication of new and emerging invasive non-native species 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. Risk analysis (dpeaa)DE-He213 Resource management (dpeaa)DE-He213 Feasibility of eradication (dpeaa)DE-He213 Contingency planning (dpeaa)DE-He213 Great Britain (dpeaa)DE-He213 NNRM (dpeaa)DE-He213 Mill, Aileen C. verfasserin aut Roy, Helen E. verfasserin aut Hiley, Alice verfasserin aut Moore, Niall verfasserin aut Robertson, Pete verfasserin aut Baker, Simon verfasserin aut Brazier, Matt verfasserin aut Bue, Mathilde verfasserin aut Bullock, Richard verfasserin aut Campbell, Steve verfasserin aut Eyre, Dominic verfasserin aut Foster, Jim verfasserin aut Hatton-Ellis, Maggie verfasserin aut Long, Jo verfasserin aut Macadam, Craig verfasserin aut Morrison-Bell, Camilla verfasserin aut Mumford, John verfasserin aut Newman, Jonathan verfasserin aut Parrott, David verfasserin aut Payne, Robin verfasserin aut Renals, Trevor verfasserin aut Rodgers, Eoina verfasserin aut Spencer, Mark verfasserin aut Stebbing, Paul verfasserin aut Sutton-Croft, Mike verfasserin aut Walker, Kevin J. verfasserin aut Ward, Alastair verfasserin aut Whittaker, Stan verfasserin aut Wyn, Gabe verfasserin aut Enthalten in Biological invasions Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999 19(2017), 8 vom: 15. Mai, Seite 2401-2417 (DE-627)320524477 (DE-600)2014991-8 1573-1464 nnns volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 https://dx.doi.org/10.1007/s10530-017-1451-z kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.00 ASE AR 19 2017 8 15 05 2401-2417 |
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10.1007/s10530-017-1451-z doi (DE-627)SPR010897356 (SPR)s10530-017-1451-z-e DE-627 ger DE-627 rakwb eng 570 ASE 42.00 bkl Booy, Olaf verfasserin aut Risk management to prioritise the eradication of new and emerging invasive non-native species 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. Risk analysis (dpeaa)DE-He213 Resource management (dpeaa)DE-He213 Feasibility of eradication (dpeaa)DE-He213 Contingency planning (dpeaa)DE-He213 Great Britain (dpeaa)DE-He213 NNRM (dpeaa)DE-He213 Mill, Aileen C. verfasserin aut Roy, Helen E. verfasserin aut Hiley, Alice verfasserin aut Moore, Niall verfasserin aut Robertson, Pete verfasserin aut Baker, Simon verfasserin aut Brazier, Matt verfasserin aut Bue, Mathilde verfasserin aut Bullock, Richard verfasserin aut Campbell, Steve verfasserin aut Eyre, Dominic verfasserin aut Foster, Jim verfasserin aut Hatton-Ellis, Maggie verfasserin aut Long, Jo verfasserin aut Macadam, Craig verfasserin aut Morrison-Bell, Camilla verfasserin aut Mumford, John verfasserin aut Newman, Jonathan verfasserin aut Parrott, David verfasserin aut Payne, Robin verfasserin aut Renals, Trevor verfasserin aut Rodgers, Eoina verfasserin aut Spencer, Mark verfasserin aut Stebbing, Paul verfasserin aut Sutton-Croft, Mike verfasserin aut Walker, Kevin J. verfasserin aut Ward, Alastair verfasserin aut Whittaker, Stan verfasserin aut Wyn, Gabe verfasserin aut Enthalten in Biological invasions Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999 19(2017), 8 vom: 15. Mai, Seite 2401-2417 (DE-627)320524477 (DE-600)2014991-8 1573-1464 nnns volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 https://dx.doi.org/10.1007/s10530-017-1451-z kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.00 ASE AR 19 2017 8 15 05 2401-2417 |
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10.1007/s10530-017-1451-z doi (DE-627)SPR010897356 (SPR)s10530-017-1451-z-e DE-627 ger DE-627 rakwb eng 570 ASE 42.00 bkl Booy, Olaf verfasserin aut Risk management to prioritise the eradication of new and emerging invasive non-native species 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. Risk analysis (dpeaa)DE-He213 Resource management (dpeaa)DE-He213 Feasibility of eradication (dpeaa)DE-He213 Contingency planning (dpeaa)DE-He213 Great Britain (dpeaa)DE-He213 NNRM (dpeaa)DE-He213 Mill, Aileen C. verfasserin aut Roy, Helen E. verfasserin aut Hiley, Alice verfasserin aut Moore, Niall verfasserin aut Robertson, Pete verfasserin aut Baker, Simon verfasserin aut Brazier, Matt verfasserin aut Bue, Mathilde verfasserin aut Bullock, Richard verfasserin aut Campbell, Steve verfasserin aut Eyre, Dominic verfasserin aut Foster, Jim verfasserin aut Hatton-Ellis, Maggie verfasserin aut Long, Jo verfasserin aut Macadam, Craig verfasserin aut Morrison-Bell, Camilla verfasserin aut Mumford, John verfasserin aut Newman, Jonathan verfasserin aut Parrott, David verfasserin aut Payne, Robin verfasserin aut Renals, Trevor verfasserin aut Rodgers, Eoina verfasserin aut Spencer, Mark verfasserin aut Stebbing, Paul verfasserin aut Sutton-Croft, Mike verfasserin aut Walker, Kevin J. verfasserin aut Ward, Alastair verfasserin aut Whittaker, Stan verfasserin aut Wyn, Gabe verfasserin aut Enthalten in Biological invasions Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999 19(2017), 8 vom: 15. Mai, Seite 2401-2417 (DE-627)320524477 (DE-600)2014991-8 1573-1464 nnns volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 https://dx.doi.org/10.1007/s10530-017-1451-z kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.00 ASE AR 19 2017 8 15 05 2401-2417 |
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10.1007/s10530-017-1451-z doi (DE-627)SPR010897356 (SPR)s10530-017-1451-z-e DE-627 ger DE-627 rakwb eng 570 ASE 42.00 bkl Booy, Olaf verfasserin aut Risk management to prioritise the eradication of new and emerging invasive non-native species 2017 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. Risk analysis (dpeaa)DE-He213 Resource management (dpeaa)DE-He213 Feasibility of eradication (dpeaa)DE-He213 Contingency planning (dpeaa)DE-He213 Great Britain (dpeaa)DE-He213 NNRM (dpeaa)DE-He213 Mill, Aileen C. verfasserin aut Roy, Helen E. verfasserin aut Hiley, Alice verfasserin aut Moore, Niall verfasserin aut Robertson, Pete verfasserin aut Baker, Simon verfasserin aut Brazier, Matt verfasserin aut Bue, Mathilde verfasserin aut Bullock, Richard verfasserin aut Campbell, Steve verfasserin aut Eyre, Dominic verfasserin aut Foster, Jim verfasserin aut Hatton-Ellis, Maggie verfasserin aut Long, Jo verfasserin aut Macadam, Craig verfasserin aut Morrison-Bell, Camilla verfasserin aut Mumford, John verfasserin aut Newman, Jonathan verfasserin aut Parrott, David verfasserin aut Payne, Robin verfasserin aut Renals, Trevor verfasserin aut Rodgers, Eoina verfasserin aut Spencer, Mark verfasserin aut Stebbing, Paul verfasserin aut Sutton-Croft, Mike verfasserin aut Walker, Kevin J. verfasserin aut Ward, Alastair verfasserin aut Whittaker, Stan verfasserin aut Wyn, Gabe verfasserin aut Enthalten in Biological invasions Dordrecht [u.a.] : Springer Science + Business Media B.V., 1999 19(2017), 8 vom: 15. Mai, Seite 2401-2417 (DE-627)320524477 (DE-600)2014991-8 1573-1464 nnns volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 https://dx.doi.org/10.1007/s10530-017-1451-z kostenfrei Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 42.00 ASE AR 19 2017 8 15 05 2401-2417 |
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Enthalten in Biological invasions 19(2017), 8 vom: 15. Mai, Seite 2401-2417 volume:19 year:2017 number:8 day:15 month:05 pages:2401-2417 |
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Booy, Olaf @@aut@@ Mill, Aileen C. @@aut@@ Roy, Helen E. @@aut@@ Hiley, Alice @@aut@@ Moore, Niall @@aut@@ Robertson, Pete @@aut@@ Baker, Simon @@aut@@ Brazier, Matt @@aut@@ Bue, Mathilde @@aut@@ Bullock, Richard @@aut@@ Campbell, Steve @@aut@@ Eyre, Dominic @@aut@@ Foster, Jim @@aut@@ Hatton-Ellis, Maggie @@aut@@ Long, Jo @@aut@@ Macadam, Craig @@aut@@ Morrison-Bell, Camilla @@aut@@ Mumford, John @@aut@@ Newman, Jonathan @@aut@@ Parrott, David @@aut@@ Payne, Robin @@aut@@ Renals, Trevor @@aut@@ Rodgers, Eoina @@aut@@ Spencer, Mark @@aut@@ Stebbing, Paul @@aut@@ Sutton-Croft, Mike @@aut@@ Walker, Kevin J. @@aut@@ Ward, Alastair @@aut@@ Whittaker, Stan @@aut@@ Wyn, Gabe @@aut@@ |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR010897356</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230519190700.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201005s2017 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s10530-017-1451-z</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR010897356</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s10530-017-1451-z-e</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="082" ind1="0" ind2="4"><subfield code="a">570</subfield><subfield code="q">ASE</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">42.00</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Booy, Olaf</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Risk management to prioritise the eradication of new and emerging invasive non-native species</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2017</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Risk analysis</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Resource management</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Feasibility of eradication</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Contingency planning</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Great Britain</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">NNRM</subfield><subfield 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Risk management to prioritise the eradication of new and emerging invasive non-native species |
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Booy, Olaf Mill, Aileen C. Roy, Helen E. Hiley, Alice Moore, Niall Robertson, Pete Baker, Simon Brazier, Matt Bue, Mathilde Bullock, Richard Campbell, Steve Eyre, Dominic Foster, Jim Hatton-Ellis, Maggie Long, Jo Macadam, Craig Morrison-Bell, Camilla Mumford, John Newman, Jonathan Parrott, David Payne, Robin Renals, Trevor Rodgers, Eoina Spencer, Mark Stebbing, Paul Sutton-Croft, Mike Walker, Kevin J. Ward, Alastair Whittaker, Stan Wyn, Gabe |
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risk management to prioritise the eradication of new and emerging invasive non-native species |
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Risk management to prioritise the eradication of new and emerging invasive non-native species |
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Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. |
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Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. |
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Abstract Robust tools are needed to prioritise the management of invasive non-native species (INNS). Risk assessment is commonly used to prioritise INNS, but fails to take into account the feasibility of management. Risk management provides a structured evaluation of management options, but has received little attention to date. We present a risk management scheme to assess the feasibility of eradicating INNS that can be used, in conjunction with existing risk assessment schemes, to support prioritisation. The Non-Native Risk Management scheme (NNRM) can be applied to any predefined area and any taxa. It uses semi-quantitative response and confidence scores to assess seven key criteria: Effectiveness, Practicality, Cost, Impact, Acceptability, Window of opportunity and Likelihood of re-invasion. Scores are elicited using expert judgement, supported by available evidence, and consensus-building methods. We applied the NNRM to forty-one INNS that threaten Great Britain (GB). Thirty-three experts provided scores, with overall feasibility of eradication assessed as ‘very high’ (8 species), ‘high’ (6), ‘medium’ (8), ‘low’ (10) and ‘very low’ (9). The feasibility of eradicating terrestrial species was higher than aquatic species. Lotic freshwater and marine species scored particularly low. Combining risk management and existing risk assessment scores identified six established species as priorities for eradication. A further six species that are not yet established were identified as priorities for eradication on arrival as part of contingency planning. The NNRM is one of the first INNS risk management schemes that can be used with existing risk assessments to prioritise INNS eradication in any area. |
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Risk management to prioritise the eradication of new and emerging invasive non-native species |
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