Research Article |
Corresponding author: Petra Lindemann-Matthies ( petra.lindemann-matthies@ph-karlsruhe.de ) Academic editor: Uwe Starfinger
© 2016 Petra Lindemann-Matthies.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Lindemann-Matthies P (2016) Beasts or beauties? Laypersons’ perception of invasive alien plant species in Switzerland and attitudes towards their management. NeoBiota 29: 15-33. doi: 10.3897/neobiota.29.5786
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This study investigated laypersons’ perception of invasive alien plant species (IAPS) and attitudes towards their management with the help of a written questionnaire in the cities of Zurich, Geneva, and Lugano, Switzerland. Survey participants (n = 720) judged attractiveness from certain species on visual contact (eight IAPS were shown as photographs). Trachycarpus fortunei and Ludwigia grandiflora were liked most, while Ambrosia artemisiifolia was clearly disliked most. With the exception of Trachycarpus fortunei, all plant species were perceived as rather ordinary, familiar and native to Switzerland, and feelings of ordinariness, familiarity and nativeness were positively correlated. Few participants could correctly identify the species depicted. Knowledge of an IAPS (ability to identify it) and desire to have it around were negatively correlated. Participants agreed most with the eradication of IAPS that cause serious costs and problems. However, people were rather unwilling to remove Buddleja davidii, Solidago canadensis, and Trachycarpus fortunei which are already widely established ornamentals in settlement areas or gardens. Overall, willingness to remove an IAPS and to report it to the authorities decreased with increasing desirability (and thus beauty) of a species.
Invasive alien plant species, Switzerland, public perception, public attitudes, management
Invasive alien species (IAS) are often considered a major threat to the world’s biodiversity (
Designing policies which prevent the introduction and release of IAS, and the management of species already established have become priority goals in many European countries (
The general public’s support and participation can be a key to success or failure of prevention, control, and eradication measures regarding IAS (
This study investigated the perception of IAPS by more than 700 laypersons in Switzerland and their attitudes towards species management. The study contributes to international research on public perception of IAS and attitudes towards management strategies (e.g.,
Main objectives were to investigate laypersons’ (1) characterization of eight IAPS shown on paper, (2) ability to identify them, and (3) attitudes towards certain types of management. It was also investigated whether laypersons’ perception of IAPS and attitudes towards certain types of management were influenced by socio-demographic variables and study location.
The study was carried out in three cities Zurich, Geneva, and Lugano, which are situated in three different regions and cantons (= administrative divisions) of Switzerland. Zurich in the north of the country belongs to the canton of Zurich (German-speaking part of Switzerland), Geneva in the southwest to the canton of Geneva (French-speaking part), and Lugano in the very south to the canton of Ticino (Italian-speaking part). Data were collected at the lake-sides of the three cities, as people are likely to be there during leisure time, and willing to take their time to answer the questions. Randomly selected passers-by (18 years and older) were asked, always in a similar way, to participate in a study about plants. In summer 2009, 720 persons filled out the questionnaire (240 in each city) in the local language. Data collection exercises required approximately 15 minutes time, and anonymity was guaranteed to the participants.
The questionnaire consisted of two parts, which were printed on two separate sheets of paper to avoid influences of the second part, in which information about IAPS was provided, on the first part (Suppl. material
All plants were presented as photographs and their invasive status was not revealed. Each species had to be characterized by five opposing attributes (ugly-beautiful, extraordinary-ordinary, exotic-indigenous, unfamiliar-familiar, unwanted-wanted) on 7-step scales (e.g., very ugly, ugly, rather ugly, neither/nor, rather beautiful, beautiful, very beautiful). After the characterization exercise, participants had to identify as many species as they could and write down their common names. A plant was regarded as correctly identified if its common name was provided at the genus or species level.
The second part investigated laypersons’ attitudes towards different types of management (objective 3). A short introduction provided information about IAPS and also clarified that all species shown in the first part were invasive. Participants had to choose among four different types of management (no intervention, no removal of aesthetically pleasing plants, but removal of less appealing ones, removal of only those invasive plants that provoke serious problems and costs, removal of all invasive plants in order to conserve unique habitats and species) to find the one type of management they considered most suitable. To investigate whether the choice of a certain management type depends on the species involved, a brief portrait of one of the IAPS used in the picture test was included in each questionnaire. Eight different versions of the second questionnaire part were thus prepared (varying in portraits, but being otherwise identical). The questionnaires were handed out to the 240 participants (30 persons per version) in each city which overall amounted to 720 questionnaires being filled out. Participants had to select among three types of management (no intervention, surveillance without taking immediate action, removal), and choose the one they considered to be most fitting for the IAPS presented. In case they had chosen the latter type, they were asked where the species should be removed (from nature reserves, natural areas, forests or farmland, settlement areas, cities, and gardens). Moreover, they were asked whether they would report the species if they detected it, and whether they would remove it from their own garden.
Finally, participants were asked about their age, sex, level of formal education, professional expertise (profession related to biology, ecology or landscape topics), and environmental commitment (membership in an environmental organization). These variables were found influential in studies on biodiversity perception (e.g.,
Participants (52% women) were between 18 and 79 years old (mean age = 32 years). About 68% of participants had a high school degree, 9% a profession related to biology, ecology, or landscape topics, and 22% were members in an environmental organization. Similar numbers were found in a large representative Swiss study on landscape perception (
Linear regressions were used to test for influences of socio-demographic variables and study location on participants’ characterizations of eight IAPS and number of IAPS correctly identified. The final minimum adequate models were obtained by backward elimination of non-significant (p > 0.05) variables. As this type of analysis does not allow strong correlations between explanatory variables (r > 0.35), Pearson correlations between binomial and metric explanatory variables were tested first (
Ordinal regression was used to test for influences on participants’ attitudes towards certain types of management (as outlined in Figure
Almost all plants were perceived as beautiful and wanted. On average, Ludwigia grandiflora was considered most beautiful, Trachycarpus fortunei most extraordinary, exotic and wanted, Senecio inaequidens most ordinary, indigenous and familiar, Solidago canadensis most unfamiliar, and Ambrosia artemisiifolia most ugly and unwanted (Figure
Characterization of eight invasive alien plant species in Zurich, Geneva and Lugano. Participants (n = 720) had to characterize each species by five opposing attributes (ugly-beautiful, extraordinary-ordinary, exotic-indigenous, unfamiliar-familiar, unwanted-wanted) on 7-step scales (e.g., very ugly, ugly, rather ugly, neither/nor, rather beautiful, beautiful, very beautiful). Mean rating scores and standard errors of means are shown.
Study location influenced characterizations (Table
Influence of socio-demographic variables and study location on laypersons’ (n = 720) characterization of eight invasive alien plant species of Switzerland that were shown to them on photos. All characterizations were done with the help of 7-step rating scales, anchored on both sites with five dichotomous attributes (e.g., very ugly-very beautiful; see Figure
Attributes and species | Age | Women vs. men | Prof. related to ecology | NGO member | Geneva vs. Zurich | Lugano vs. Zurich |
---|---|---|---|---|---|---|
Beautiful | ||||||
S. canadensis | 6.11*** | |||||
B. davidii | 3.09* | 4.56*** | 3.01* | |||
A. artemisiifolia | 6.53*** | 3.27* | ||||
S. inaequidens | 2.87* | 2.97* | -5.95*** | |||
H. mantegazzianum | 4.45*** | 3.19** | ||||
I. glandulifera | 3.25** | |||||
L. grandiflora | 3.31** | |||||
Ordinary | ||||||
B. davidii | 2.97* | |||||
S. inaequidens | -4.38*** | |||||
T. fortunei | -2.78* | 17.88*** | ||||
H. mantegazzianum | -2.84* | |||||
I. glandulifera | -2.99* | 4.14*** | ||||
L. grandiflora | -3.09* | 5.06*** | ||||
Indigenous | ||||||
B. davidii | 3.84*** | |||||
S. inaequidens | -5.51*** | |||||
H. mantegazzianum | 3.42* | -3.63*** | ||||
I. glandulifera | 3.33** | -3.87*** | ||||
L. grandiflora | -3.51*** | |||||
Familiar | ||||||
S. canadensis | 3.98*** | -3.77*** | ||||
B. davidii | 4.52*** | 5.54*** | ||||
A. artemisiifolia | 4.38*** | 3.07* | ||||
T. fortunei | 3.20* | 2.83* | 9.12*** | |||
H. mantegazzianum | 3.59*** | 3.38** | -3.81*** | |||
I. glandulifera | 4.53*** | |||||
L. grandiflora | 3.03* | |||||
Wanted | ||||||
S. canadensis | 3.30** | -2.76* | ||||
B. davidii | 3.56*** | -2.90* | -5.06*** | |||
S. inaequidens | 3.66*** | -4.50*** | ||||
T. fortunei | -4.07*** | |||||
I. glandulifera | 3.80*** | -3.00* | -7.08*** | |||
L. grandiflora | -4.68*** |
Only 75 participants could correctly identify at least one of the plant species presented (1 species: 41 persons, 2–3 species: 27 persons, 4–7 species: 7 persons, 8 species: nobody). B. davidii and H. mantegazzianum were most often and S. inaequidens and L. grandiflora least often correctly identified (see numbers in brackets in Table
Relationship between knowledge of IAPS (measured as the ability to identify them) and degree of their desirability (measured on a 7-step scale with 1: very unwanted, 2: unwanted; 3: rather unwanted; 4: neither unwanted nor wanted; 5: rather wanted, 6: wanted, 7: very wanted). The number of participants (overall 720 persons) who could correctly identify the species is shown in brackets. Data were analyzed only when more than ten participants could identify the species. *: p < 0.05; **: p <0.01; ***: p < 0.001.
Species | Desirability (mean rating scores) | Test statistics | ||
---|---|---|---|---|
Unable to identify | Able to identify | F-value | P-value | |
Solidago canadensis | 4.7 ± 0.05 | 4.0 ± 0.27 (25) | 6.76 | 0.009 |
Buddleja davidii | 5.2 ± 0.06 | 5.1 ± 0.20 (51) | 0.08 | 0.781 |
Ambrosia artemisiifolia | 4.0 ± 0.06 | 2.1 ± 0.33 (19) | 31.45 | <0.001 |
Senecio inaequidens | 5.3 ± 0.06 | 2.0 (1) | - | - |
Trachycarpus fortunei | 5.5 ± 0.06 | 3.2 ± 0.60 (6) | - | - |
Heracleum mantegazzianum | 4.4 ± 0.07 | 3.6 ± 0.32 (28) | 5.38 | 0.021 |
Impatiens glandulifera | 5.2 ± 0.05 | 3.2 ± 0.45 (9) | - | - |
Ludwigia grandiflora | 5.4 ± 0.05 | 2.5 ± 0.91 (2) | - | - |
In the model (r2 = 0.16), age, professional experience, membership in an environmental organization and study location influenced participants’ “taxonomic” knowledge. With increasing age, individuals were more able to identify species correctly (b = 0.01, t = 6.29, p < 0.001), as were participants with professional expertise (b = 0.39, t = 4.54, p < 0.001) and environmental organization members (b = 0.23, t = 3.74, p < 0.001). Participants in Lugano were less able than the others to identify species correctly (b = -0.16, t = -3.08, p = 0.002).
Knowledge of an IAPS (ability to identify it on paper) and desire to have it around (attributed score on the “unwanted-wanted” scale) were negatively correlated. An IAPS was considered (rather) unwanted by those participants who knew it, and (rather) wanted by those who did not. Only with B. davidii was this not the case (see Table
In view of participants, for IAPS that cause serious costs and problems, removal was clearly the best type of management and thus most often chosen (Figure
Preference for certain types of management in Zurich, Geneva and Lugano. Participants (n = 720) had to choose among four management types the one they considered most suitable.
When asked how to proceed with the individual species presented in the second questionnaire sheet, participants more often opted for removal than surveillance, only with T. fortunei and B. davidii was this not the case (Figure
Proportion of people choosing various types of management for eight invasive alien plant species. Each species was introduced to 90 participants who then had to select the one type they considered most suitable for the species presented.
Participants who had opted for the removal of a species were asked where they wanted a species to be removed. Especially in case of S. canadensis, B. davidii, T. fortunei and I. glandulifera, a removal from nature reserves, natural areas and forests or farmland received more support than one from settlement areas, cities, and gardens (Table
Willingness of participants to remove IAPS in certain locations and to report these species to the authorities. Only participants who had previously opted for a removal of these species in Switzerland (numbers provided in brackets) were included.
Species | Removal of species (agreement in %) | Reporting of species (%) | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
Nature reserves | Natural areas | Forests or farmland | Settlement areas | Cities | Gardens | Own garden | Overall mean | Yes | No | Not sure to recognize it | |
Solidago canadensis (n = 45) | 75.6 | 66.7 | 60.0 | 24.4 | 20.0 | 24.4 | 64.4 | 47,9 | 22.2 | 31.1 | 46.7 |
Buddleja davidii (n = 33) | 69.7 | 60.6 | 39.4 | 24.2 | 27.3 | 27.3 | 45.5 | 42,0 | 15.2 | 54.5 | 30.3 |
Ambrosia artemisiifolia (n = 55) | 52.7 | 45.5 | 58.2 | 76.4 | 69.1 | 63.6 | 85.5 | 64,4 | 25.5 | 25.5 | 49.0 |
Senecio inaequidens (n = 50) | 54.0 | 58.0 | 66.0 | 36.0 | 30.0 | 46.0 | 78.0 | 52,6 | 14.0 | 30.0 | 56.0 |
Trachycarpus fortunei (n = 27) | 59.3 | 70.4 | 55.6 | 11.1 | 14.8 | 18.5 | 33.3 | 37,6 | 18.5 | 48.1 | 33.4 |
Heracleum mantegazzianum (n = 54) | 66.7 | 63.0 | 46.3 | 53.7 | 37.0 | 55.6 | 87.0 | 58,5 | 31.5 | 20.4 | 48.1 |
Impatiens glandulifera (n = 63) | 68.3 | 68.3 | 55.6 | 19.0 | 14.3 | 17.5 | 54.0 | 42,4 | 17.5 | 36.5 | 46.0 |
Ludwigia grandiflora (n = 53) | 77.4 | 67.9 | 64.2 | 39.6 | 35.8 | 37.7 | 60.4 | 54,7 | 20.8 | 34.0 | 45.2 |
The overall determination to remove an IAPS from the environment (mean proportion of agreement to removal of species in the seven locations, see Table
Almost all plants were perceived as beautiful and wanted (first part of the questionnaire). Moreover, perceived beauty and desirability (high scores on the “beautiful” and “wanted” side of the rating scales) were positively correlated. It should be noted that participants’ characterizations were unaffected by information about the invasive status of these species, this information was provided only in the second part of the questionnaire. As most participants did not recognize the species presented anyway, the results reflect unbiased feelings and preferences. Encounters with IAPS might thus evoke pleasurable (aesthetic) feelings, at least in laypersons, and a desire to keep them where they are. Participants’ aesthetic feelings were hardly influenced by education or expertise, but were more prominent in women and increased with age. Women are generally more in favor than men of visually appealing plants (
Plants with bright flower colors, large sizes, and fragrance were found to be highly attractive to humans (
With exception of the Chinese windmill palm (Trachycarpus fortunei), all species were perceived as rather ordinary, familiar and indigenous. Feelings of familiarity, ordinariness and nativeness were positively correlated. Such feelings paired with a lack in “taxonomic” knowledge might severely bias laypersons’ perception of IAPS. Perceived familiarity with an IAPS has been found to have a mitigating effect on risk perception, and perceptions of risk increased if a species was perceived to be non-native (
Level of formal education did not influence participants’ attitudes towards certain management types (but see
Participants agreed most with the proposal to eradicate only IAPS that cause serious problems and costs. A preference for the eradication of only economically damaging species instead of eradication of all IAS was also found in other studies (
As seen in this study, invasive species management might get in conflict with a public unwilling to support eradication of appealing plants. Ludwigia grandiflora and Trachycarpus fortunei (both with strong invasive potential in Switzerland, e.g.,
There are certain limitations to the present study. Younger people were over-represented as they were much more willing to participate than older ones. Moreover, higher qualified and environmentally engaged individuals were also overrepresented. Similar results were found in other comparable studies (e.g.,
Public support is seen as crucial for the prevention and successful management of IAS in Switzerland (
The present results also highlight that public information should focus more on impact-related criteria of IAPS than on species’ origin (see also
In general, participants were rather supportive of a removal of IAPS. However, information about negative effects does not change beauties into beasts. The present results highlight that laypersons may ignore the damage attractive IAPS can cause, and thus not support their removal in settlement areas and gardens, especially when these species do not affect human health. Information on IAPS should thus not only focus on their general impact, but rather on reasons for the eradication and control in particular locations. First attempts in this direction have already been made in Switzerland. Cantonal authorities and NGOs have published a number of information sheets about IAPS for garden owners, and flyers about, e.g., Solidago canadensis have been distributed to garden owners who live close to conservation areas (for an example see
The present results highlight also the importance of taxonomic knowledge. Although taxonomic knowledge of laypersons may be irrelevant for the effective management of IAPS, it is still an important proxy for people’s reaction to IAPS. Six out of the eight IAPS in the present study are included in the “Swiss Ordonnance on Organism Dissemination in the Environment 814.911” and may therefore not be introduced in the environment in Switzerland. However, a lack of knowledge of these species is likely to limit the efficiency of this legal obligation. If laypersons are unable to identify these IAPS, they are also unable to detect them and report them to the authorities. One way to counteract this lack of “taxonomic” knowledge could be to directly engage the public in eradication projects. Nationwide “root-out-days” are yearly events in Switzerland where the public receives information about the IAPS in focus (in 2015 Solidago canadensis, http://www.arten-ohne-grenzen.ch/). Personal experience and direct involvement in the root-out-event might foster the understanding of the public of the damage caused by IASP and the necessity of measures to control even beautiful invasive plants.
I would like to thank Barbara Roth and Maja Ravaioli for their help in acquiring the data, Diethart Matthies for valuable comments on an earlier version of this article, and Chris Auber for checking the English.
The “Black List” includes invasive alien plants of Switzerland that cause damage in the areas of biodiversity, health, and/or economy. The establishment and the spread of these species must be prevented (