Abstract
Despite biological invasions being a worldwide phenomenon causing significant ecological, economic, and human welfare impacts, there is limited understanding regarding how environmental managers perceive the problem and subsequently manage alien species. Spanish environmental managers were surveyed using questionnaires to (1) analyze the extent to which they perceive plant invasions as a problem; (2) identify the status, occurrence, and impacts of noxious alien plant species; (3) assess current effort and expenditure targeting alien plant management; and, finally, (4) identify the criteria they use to set priorities for management. In comparison to other environmental concerns, plant invasions are perceived as only moderately problematic and mechanical control is the most valued and frequently used strategy to cope with plant invasions in Spain. Based on 70 questionnaires received, 193 species are considered noxious, 109 of which have been the subject of management activities. More than 90% of species are found in at least one protected area. According to respondents, the most frequently managed species are the most widespread across administrative regions and the ones perceived as causing the highest impacts. The perception of impact seems to be independent of their invasion status, since only half of the species identified as noxious are believed to be invasive in Spain, while 43% of species thought to only be casual aliens are causing a high impact. Records of management costs are poor and the few data indicate that the total actual expenditure amounted to 50,492,437 € in the last decade. The majority of respondents stated that management measures are insufficient to control alien plants due to limited economic resources, lack of public awareness and support, and an absence of coordination among different public administrations. Managers also expressed their concern about the fact that much scientific research is concerned with the ecology of alien plants rather than with specific cost-efficient strategies to manage alien species.
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Acknowledgments
We thank all respondents to the inquiry (http://www.creaf.uab.es/propies/jara/Apendice artículo Ecosistemas.pdf), too many to name here, and three anonymous reviewers for helpful comments on a previous version of the manuscript. This study was partially funded by the projects ALARM (Assessing Large-Scale Environmental Risks for Biodiversity with Tested Methods; GOCE-CT-2003-506675; http://www.alarmproject.net, Settele and others 2005), DAISIE (Delivering Alien Invasive Species Inventories for Europe; SSPI-CT-2003-511202; http://www.europe-aliens.org), of the Sixth Framework Programme of the European Commission, RINVE (Determinantes Biológicos del Riesgo de Invasiones Vegetales), of the Spanish Ministerio de Educación y Ciencia and the CONSOLIDER-INGENIO 2010 project: Spanish woodlands and global change: threats and opportunities (MONTES-CSD2008-00040).
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Appendices
Appendix 1: Questionnaire on Alien Plants Sent to Environmental Managers
Part 1: General Questions on Perception and Identity of Alien Species of Concern
-
1.
Which priority would you assign to the problem of biological invasions in relation to the other environmental problems of your area of responsibility?
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i.
High priority
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ii.
Medium priority
-
iii.
Low priority
-
i.
-
2.
Could you assign a number from 1 to 5 to the following environmental problems according to their priority or importance? (1 = low importance, 2 = moderate importance, 3 = important, 4 = high importance, 5 = extremely important)?
Natural habitat loss
1
2
3
4
5
Habitat fragmentation
1
2
3
4
5
Wildfire
1
2
3
4
5
Biological invasions
1
2
3
4
5
Climate change
1
2
3
4
5
Pollution
1
2
3
4
5
Urbanization
1
2
3
4
5
Land use change
1
2
3
4
5
Other (specify which ones)
1
2
3
4
5
-
3.
Which priority would you assign to the following management strategies against invasions? (ranking from 1 to 4: 1 = low priority and 4 = maximum priority)
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i.
Legislation reinforcement
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ii.
Education and outreach
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iii.
Entry prevention
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iv.
Direct population control
-
i.
-
4.
Which are the main limitations or difficulties for an effective management of alien species in your area of responsibility?
-
5.
Which alien species are causing problems (i.e., noxious alien plants) in your area of responsibility?
Part 2: Questions for Each Alien Species of Concern
Species 1: Species Name
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1.
Which kind of impacts is it causing?
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i.
Ecological
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ii.
Economic
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iii.
Social
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iv.
Human health
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i.
-
2.
Could you specify the impact type caused by this species?
-
3.
Could you specify the magnitude of the impact caused by this species?
-
i.
High
-
ii.
Intermediate
-
iii.
Low
-
i.
-
4.
Could you mention any direct impact of this plant, which associated costs are easily quantified? (i.e., infrastructure damage)?
-
5.
Is there any management strategy over this alien species in your area of responsibility? Yes/No
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6.
Which kinds of management activities do you carry out?
-
i.
Prevention–outreach
-
1.
Regional legislation
-
2.
Education and information activities
-
3.
other (specify)
-
1.
-
ii.
Eradication
-
iii.
Containment (i.e., population control)
-
iv.
Restoration (i.e., habitat improvement, reforestation with native species)
-
i.
-
7.
How long have the management strategies been functioning?
-
8.
Which method has been used to control or eradicate the alien species?
-
i.
Physical (mechanical, manual,…)
-
ii.
Chemical
-
iii.
Physical + chemical
-
iv.
Biological control
-
i.
-
9.
With which frequency have the treatments been carried out?
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10.
Are the treatments carried out by technicians or volunteers?
-
11.
Do you monitor the success of the management measures over the time?
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12.
How often do you monitor the state of the invasion?
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13.
Have you carried out a restoration of the locations previously invaded by the alien plant?
-
14.
Could you estimate the total economic cost of the management measures?
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i.
Prevention costs (three-page leaflets, workshops, conferences…) = €.
-
ii.
Eradication or control costs (herbicides, salary, material, machinery, etc.) = €.
-
iii.
Habitat restoration costs (native species plantation) = €.
-
i.
-
15.
Could you indicate which has been the result of the management measures?
-
i.
The species has been eliminated
-
ii.
The species has decreased considerably
-
iii.
The species has decreased very little
-
iv.
The species has not decreased
-
v.
The species continues to expand
-
i.
-
16.
Do you think that the management strategies have been successful?
-
i.
Very successful
-
ii.
Moderately successful
-
iii.
Not very successful
-
iv.
No successful at all
-
i.
Appendix 2
List and status of the most noxious species according to respondents and the number of autonomous communities (ACs) and protected areas where noxious and managed (status: I = invasive, N = naturalized, C = casual)
Species (family) | Status | No. of ACs where noxious | No. of ACs where managed | No. of ACs where presenta | No. of protected areas where noxious | No. of protected areas where managed |
---|---|---|---|---|---|---|
Carpobrotus spp. (Aizoaceae) | I | 11 | 8 | 10 | 21 | 13 |
Eucalyptus spp. (Myrtaceae) | I | 11 | 8 | 13 | 14 | 13 |
Ailanthus altissima (Simaroubaceae) | I | 11 | 6 | 12 | 10 | 4 |
Robinia pseudoacacia (Fabaceae) | I | 11 | 3 | 17 | 2 | 1 |
Acacia spp. (Fabaceae) | I | 9 | 7 | 12 | 9 | 8 |
Cortaderia selloana (Poaceae) | I | 8 | 7 | 11 | 2 | 2 |
Agave americana (Agavaceae) | I | 7 | 3 | 12 | 14 | 2 |
Arundo donax (Poaceae) | I | 7 | 1 | 15 | 1 | 0 |
Opuntia spp. (Cactaceae) | I | 7 | 4 | 13 | 9 | 3 |
Oxalis pes-caprae (Oxalidaceae) | I | 7 | 2 | 11 | 4 | 2 |
Senecio spp. (Asteraceae) | I | 6 | 3 | 11 | 4 | 2 |
Arctotheca calendula (Asteraceae) | I | 5 | 3 | 10 | 2 | 2 |
Ipomoea spp. (Convolvulaceae) | I | 5 | 3 | 14 | 1 | 1 |
Myoporum spp. (Myoporaceae) | N | 5 | 4 | 3 | 1 | 1 |
Nicotiana glauca (Solanaceae) | I | 5 | 2 | 8 | 5 | 2 |
Oenothera glazioviana (Onagraceae) | I | 5 | 3 | 14 | 0 | 0 |
Paspalum spp. (Poaceae) | I | 5 | 0 | 17 | 1 | 0 |
Ricinus communis (Euphorbiaceae) | I | 5 | 1 | 8 | 2 | 2 |
Tradescantia fluminensis (Commelinaceae) | I | 5 | 3 | 8 | 2 | 2 |
Aptenia cordifolia (Aizoaceae) | N | 4 | 1 | 7 | 2 | 0 |
Aster squamatus (Asteraceae) | I | 4 | 0 | 16 | 1 | 1 |
Baccharis halimifolia (Asteraceae) | I | 4 | 4 | 3 | 0 | 0 |
Conyza spp. (Asteraceae) | I | 4 | 0 | 17 | 0 | 0 |
Eichhornia crassipes (Pontederiaceae) | I | 4 | 4 | 3 | 1 | 1 |
Xanthium strumarium (Asteraceae) | I | 4 | 2 | 13 | 1 | 1 |
Aloe spp. (Liliaceae) | C | 3 | 1 | 4 | 1 | 0 |
Amaranthus spp. (Amaranthaceae) | I | 3 | 0 | 17 | 0 | 0 |
Azolla filiculoides (Azollaceae) | I | 3 | 2 | 8 | 2 | 1 |
Buddleja davidii (Buddlejaceae) | I | 3 | 2 | 7 | 1 | 1 |
Fallopia japonica (Polygonaceae) | I | 3 | 2 | 6 | 0 | 0 |
Lantana spp. (Verbenaceae) | I | 3 | 0 | 5 | 0 | 0 |
Oenothera biennis (Onagraceae) | I | 3 | 2 | 14 | 0 | 0 |
Pennisetum setaceum (Poaceae) | I | 3 | 1 | 3 | 2 | 2 |
Tropaeolum majus (Tropaeolaceae) | I | 3 | 1 | 10 | 0 | 0 |
Yucca spp. (Agavaceae) | C | 3 | 3 | – | 3 | 2 |
Araujia sericifera (Asclepiadaceae) | I | 2 | 0 | 8 | 0 | 0 |
Artemisia spp. (Asteraceae) | I | 2 | 0 | 13 | 1 | 0 |
Datura stramonium (Solanaceae) | I | 2 | 2 | 16 | 3 | 2 |
Disphyma crassifolium (Aizoaceae) | N | 2 | 0 | 4 | 1 | 0 |
Egeria densa (Hydrocharitaceae) | N | 2 | 1 | 2 | 1 | 0 |
Kalanchoe spp. (Crassulaceae) | C | 2 | 1 | – | 0 | 0 |
Ludwigia spp. (Onagraceae) | N | 2 | 2 | 2 | 2 | 0 |
Oenothera drummondii (Onagraceae) | N | 2 | 1 | 2 | 1 | 1 |
Pittosporum tobira (Pittosporaceae) | C | 2 | 1 | 1 | 0 | 0 |
Platanus hybrida (Platanaceae) | N | 2 | 2 | 8 | 0 | 0 |
Solanum bonariense (Solanaceae) | I | 2 | 0 | 9 | 0 | 0 |
Sorghum halepense (Poaceae) | I | 2 | 0 | 15 | 0 | 0 |
Spartina patens (Poaceae) | I | 2 | 0 | 9 | 0 | 0 |
Xanthium spinosum (Asteraceae) | N | 2 | 0 | 16 | 0 | 0 |
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Andreu, J., Vilà, M. & Hulme, P.E. An Assessment of Stakeholder Perceptions and Management of Noxious Alien Plants in Spain. Environmental Management 43, 1244–1255 (2009). https://doi.org/10.1007/s00267-009-9280-1
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DOI: https://doi.org/10.1007/s00267-009-9280-1