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Are we working to save the species our children want to protect? Evaluating species attribute preferences among children

Published online by Cambridge University Press:  04 May 2016

Kristin Frew ,
M. Nils Peterson  and
Kathryn Stevenson
Kristin Frew*
Affiliation:
Fisheries, Wildlife, and Conservation Biology Program, Department of Forestry and Environmental Resources, North Carolina State University, Box 8001, Raleigh, NC 27695, USA.
M. Nils Peterson
Affiliation:
Fisheries, Wildlife, and Conservation Biology Program, Department of Forestry and Environmental Resources, North Carolina State University, Box 8001, Raleigh, NC 27695, USA.
Kathryn Stevenson
Affiliation:
Fisheries, Wildlife, and Conservation Biology Program, Department of Forestry and Environmental Resources, North Carolina State University, Box 8001, Raleigh, NC 27695, USA.
*
(Corresponding author) E-mail knfrew@ncsu.edu
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Abstract

As conservation resources decline and numbers of threatened species increase, prioritizing species for conservation is increasingly important, and prioritizing based on attributes may be the most efficient approach. Despite the importance of biodiversity as a legacy to future generations, children's preferences for species attributes have never been considered. We surveyed 3rd and 5th grade students, typically 8–10 years old, in North Carolina, USA, to determine how children prioritize conservation of species based on attributes. We asked the students to rank five species attributes, allocate money to species with each attribute, and choose between each species attribute and endemism in terms of their importance for conservation. Children prioritized species that are important in nature and those whose numbers are declining over species with other attributes, whereas research suggests that adults prioritize endemic species over most other types. Our results suggest children prioritize biodiversity conservation differently from adults, and in ways that may be more conducive to biodiversity conservation in cases where endemism is not directly related to species endangerment, and we suggest the perspectives of children be considered more fully within biodiversity conservation.

Keywords

Childrenconservation prioritiesenvironmental educationspecies attributesvaluation
Type
Papers
Information
Oryx , Volume 51 , Issue 3 , July 2017 , pp. 455 - 463
Copyright
Copyright © Fauna & Flora International 2016 

Introduction

Prioritizing species for conservation is increasingly important as the resources available for biodiversity conservation are limited and often declining (Mace et al., Reference Mace, Possingham, Leader-Williams, Macdonald and Service2007; Butchart et al., Reference Butchart, Walpole, Collen, van Strien, Scharlemann and Almond2010) and conservation needs are increasing (Pereira et al., Reference Pereira, Leadley, Proença, Alkemade, Scharlemann and Fernandez-Manjarrés2010; Cardinale et al., Reference Cardinale, Duffy, Gonzalez, Hooper, Perrings and Venail2012; Hooper et al., Reference Hooper, Adair, Cardinale, Byrnes, Hungate and Matulich2012). Human actions have increased extinction rates by up to 1,000 times their background levels (Pimm et al., Reference Pimm, Russell, Gittleman and Brooks1995), and this catastrophe is projected to worsen as a result of rapid anthropogenic climate and land cover change (Foley et al., Reference Foley, DeFries, Asner, Barford, Bonan and Carpenter2005; Leadley et al., Reference Leadley, Pereira, Alkemade, Fernandez-Manjarres, Proença, Scharlemann and Walpole2010; Bellard et al., Reference Bellard, Bertelsmeier, Leadley, Thuiller and Courchamp2012). Fixed or declining conservation budgets (Iwamura et al., Reference Iwamura, Wilson, Venter and Possingham2010; Waldron et al., Reference Waldron, Mooers, Miller, Nibbelink, Redding and Kuhn2013) will necessitate trade-offs regarding which species are protected. Many government organizations and conservation NGOs prioritize species based on their risk of becoming extinct (e.g. the U.S. Endangered Species Act of 1973; the IUCN Red List, 2015); however, some scientists suggest that other attributes need to be considered when deciding conservation priorities. Experts have used criteria including endemism, economic value, ecological significance, charisma and evolutionary distinctiveness to prioritize species for conservation (Avise, Reference Avise, Purvis, Gittleman and Brooks2005; Isaac et al., Reference Isaac, Turvey, Collen, Waterman and Baillie2007; Sodhi et al., Reference Sodhi, Posa, Lee, Bickford, Koh and Brook2010; Curnick et al., Reference Curnick, Head, Huang, Crabbe, Gollock and Hoeksema2015). The importance of species that have significant impacts on ecological and evolutionary processes has also been highlighted (Possingham et al., Reference Possingham, Andelman, Burgman, Medellín, Master and Keith2002; Isaac et al., Reference Isaac, Turvey, Collen, Waterman and Baillie2007; Arponen, Reference Arponen2012).

Understanding public perspectives on prioritizing species is critical because saving species often requires human intervention, and public preference should influence conservation in nominally democratic contexts (Czech et al., Reference Czech, Krausman and Borkhataria1998). Public preferences dictate where money is allocated, which species receive protection, and the overall success of conservation plans (Norton, Reference Norton1986; Martín-López et al., Reference Martín-López, Montes and Benayas2007, Reference Martín-lópez, Montes, Ramírez and Benayas2009). Efforts to evaluate public prioritization of biodiversity conservation have focused on willingness to pay for conserving a species or suite of species (e.g. Loomis & White, Reference Loomis and White1996; Martín-López et al., Reference Martín-López, Montes and Benayas2007). However, such studies tend to be species specific and do not provide general principles for prioritizing species. Eliciting public preference for species conservation can be problematic when using named species because public preference for iconic species tends to overestimate species’ value (Jacobsen et al., Reference Jacobsen, Boiesen, Thorsen and Strange2008). Furthermore, stakeholders may vary widely in their perceptions of specific species; for example, the tiger Panthera tigris is a popular flagship species in developed countries but those whose lives and livelihoods are threatened by tigers have a different view (Leader Williams & Dublin, Reference Leader Williams, Dublin, Entwistle and Dunstone2000). Researchers have responded to this need to elicit public preferences by developing and testing the importance of several relatively objective and general species attributes (e.g. Knegtering et al., Reference Knegtering, Hendrickx, Van Der Windt and Uiterkamp2002; Montgomery, Reference Montgomery2002; Meuser et al., Reference Meuser, Harshaw and Mooers2009). Being rare and endemic are often considered to be the most important species attributes (Veríssimo et al., Reference Veríssimo, Fraser, Groombridge, Bristol and MacMillan2009; Morse-Jones et al., Reference Morse-Jones, Bateman, Kontoleon, Ferrini, Burgess and Turner2012; Takahashi et al., Reference Takahashi, Veríssimo, MacMillan and Godbole2012). Body size and appearance are also relevant attributes for flagship species but their importance varies among studies (Takahashi et al., Reference Takahashi, Veríssimo, MacMillan and Godbole2012; Veríssimo et al., Reference Veríssimo, Fraser, Girão, Campos, Smith and Macmillan2014). One study ranked endemic species as the highest conservation priority, followed by species with declining numbers and species of economic importance (Meuser et al., Reference Meuser, Harshaw and Mooers2009).

This research trajectory focusing on multiple species attributes is important but conspicuously omits the perspectives of children. The idea that biodiversity conservation is in part about a bequest to our children and future generations is axiomatic to the field of conservation biology and has been voiced repeatedly (Weiss, Reference Weiss1990; Meine et al., Reference Meine, Soulé and Noss2006). Furthermore, the future success of conservation efforts depends on creating the next generation of conservationists. Experiences in childhood can set lasting trajectories in areas such as academic performance (Gelman & Brenneman, Reference Gelman and Brenneman2004), success (Gorey, Reference Gorey2001) and pro-environmental behaviour (Chawla, Reference Chawla1999), and understanding the opinions of children may elucidate how to foster lifelong stewardship of biodiversity. Children influence their parents in areas such as purchasing behaviour (e.g. convincing parents to buy particular breakfast cereals; Flurry & Burns, Reference Flurry and Burns2005), information technology (e.g. teaching parents computer skills; Hampshire, Reference Hampshire2000), and pro-environmental behaviour (e.g. encouraging parents to recycle; Legault & Pelletier, Reference Legault and Pelletier2000), which suggests that children's conservation priorities may influence those of their parents. For all these reasons the perspectives of children are fundamentally important in prioritizing biodiversity conservation.

We studied how children prioritized species attributes (cf. Meuser et al., Reference Meuser, Harshaw and Mooers2009), hypothesizing that they would rank species with declining numbers and ecologically important species highest. Although previous studies among adults found endemism to be an important, if not the most important, attribute (Meuser et al., Reference Meuser, Harshaw and Mooers2009; Veríssimo et al., Reference Veríssimo, Fraser, Groombridge, Bristol and MacMillan2009; Morse-Jones et al., Reference Morse-Jones, Bateman, Kontoleon, Ferrini, Burgess and Turner2012), this finding may be attributable to adults having a nativist response to animals, similar to xenophobia towards other people (Brown & Sax, Reference Brown and Sax2004), which may lead to favouritism for native animals, including endemic species. Although gender is a relatively strong and persistent driver of how adults prioritize and perceive wildlife (Kellert & Berry, Reference Kellert and Berry1987; Czech et al., Reference Czech, Devers and Krausman2001), we predicted the relationship would be weaker among children because gender identities are still forming (Serbin et al., Reference Serbin, Powlishta, Gulko, Martin and Lockheed1993; Martin & Ruble, Reference Martin and Ruble2004, Reference Martin and Ruble2009). We treated ethnicity, socio-economic status and education as exploratory variables because there was little or no theory suggesting potential relationships between these variables and how children prioritized species for conservation.

Methods

Sampling

We targeted 3rd and 5th grade students, typically 8–10 years old, in North Carolina, USA, because they represented the youngest age groups with cognitive abilities to think abstractly and form interests and concerns related to environmental issues (Gelman & Brenneman, Reference Gelman and Brenneman2004). We obtained a stratified random sample of children from elementary schools across North Carolina, selecting 60 schools from a list of all public middle and elementary schools in the state. From a list of all 3rd and 5th grade teachers in these 60 schools we randomly selected 118 teachers for participation in our study. Of the 118 teachers contacted, 36 responded (30.5% response rate) and 21 consented to participate (58.3% compliance rate). Data were collected via 440 surveys administered to students during 16 classroom visits in March 2014 (all students who attended class chose to participate). The decision to survey only 16 of the 21 classes that consented to participate was based on scheduling conflicts. Gender was balanced (53% female) and most students were in the 3rd grade (79%). The most prevalent ethnicity was white (46%), followed by African American (21%), Native American (11%), Hispanic (10%), other (10%) and Asian (2%). School-level data from the National Center for Education Statistics indicated that the mean percentage of students eligible for free or subsidized lunches at the schools in our sample was 66.4 ± SD 17.5% (U.S. Department of Education, 2012). The North Carolina State University institutional review board (IRB #3793) approved this study, and all participants gave their informed consent to participate.

Questionnaire design

To elicit children's species preferences we constructed a questionnaire asking them to rank species attributes, allocate money to species with each attribute, and choose between each species attribute and endemism in terms of importance for conservation. The questions were adapted for children from a similar survey by Meuser et al. (Reference Meuser, Harshaw and Mooers2009). We chose this approach both to facilitate comparisons and because other methods (e.g. choice experiments) were less suited to minimizing classroom time interrupted by the study and minimizing cognitive difficulty for the age group involved (Hanley et al., Reference Hanley, Mourato and Wright2001). Firstly, students were asked to rank the importance of five species attributes that could determine the allocation of resources for conservation: wild animals whose numbers are declining rapidly (species with declining numbers), wild animals that are important in nature (species important in nature), wild animals that live nowhere else but North Carolina (endemic species), wild animals that people like to watch (species people watch), and wild animals that people like to eat (species people eat). Secondly, students were asked to allocate a specific amount of money (USD 10) among the same species attributes. This constant-sum question provided a ranking of attributes and a measure of children's preferences for these attributes. Thirdly, students were asked to choose between endemic species and four other species attributes (species with declining numbers, species important in nature, species people watch, and species people eat). For each pair, the students identified the attribute they thought should be a higher priority for species protection. The final instrument was based on pre-testing the students. We administered the draft instrument to two classes of 5th grade students (n = 32). We asked them to circle questions that were difficult to understand, and make notes on how they could be improved. After adjusting the wording of several items we administered a second draft of the survey to two classes of 3rd grade students (n = 37) and asked for written feedback. Additionally, we conducted cognitive interviews (Desimone & Le Floch, Reference Desimone and Le Floch2004) with 12 students to gather general feedback and identify versions of questions that were easier to understand.

Analysis

For the first two questions (ranking species attributes and allocating money to species with each attribute) we compared students’ answers using Wilcoxon signed-rank tests (Meuser et al., Reference Meuser, Harshaw and Mooers2009). For the question asking students to choose between each species attribute and endemism we tested for differences in the pairwise comparisons using binomial tests. For each question we also explored whether students’ preferences differed by grade level, gender, ethnicity, locale and socio-economic status, using Mann–Whitney U tests. For socio-economic status we split the sample based on the median percentage of students eligible for free or subsidized lunches (65.6%). Students attending schools below the median were placed in the high socio-economic status group and students attending schools at or above the median were placed in the low socio-economic status group. We also used school-level locale data to split the sample into urban and rural students. Those attending schools in areas classified as rural or towns were placed in the rural group, and those in suburbs or cities were placed in the urban group. School-level socio-economic and locale data were obtained from the National Center for Education Statistics (U.S. Department of Education, 2012).

Results

When asked to rank species attributes, and allocate money to species with each attribute, children ranked species with declining numbers as most important (Table 1). Species with declining numbers were ranked higher and allocated more money than species with all other attributes except species important in nature. When asked to choose between each species attribute and endemism, children chose species important in nature over endemic species (Table 1), giving second preference to species with declining numbers.

Table 1 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks. All species attributes compared to endemism (i.e. wild animal species that live only in North Carolina) using the Wilcoxon signed-rank test.

1 Associated with comparison to endemic species (H0 = no difference in rank of species attributes; n = 296)

2 Associated with comparison to endemic species (H0 = no difference in rank of species attributes; n = 333)

3 Associated with comparison to endemic species (H0 = no difference in rank of species attributes; n = 424)

* Significant, with α < 0.0125 corrected for false discovery rate (Benjamini & Hochberg, Reference Benjamini and Hochberg1995)

We did not detect gender-based differences in ranking of species attributes, allocation of money to species with each attribute, or choices between each species attribute and endemism. Comparing education level we found children in the 3rd grade (n = 347) and 5th grade (n = 93) ranked species attributes in the same order but with different strengths of preference. The 5th grade students ranked species with declining numbers and species important in nature significantly higher than those in the 3rd grade (Table 2). The 3rd grade students ranked endemic species higher than those in the 5th grade. The 5th grade students allocated more money to species with declining numbers than those in the 3rd grade, and 3rd grade students allocated more money to endemic species than those in the 5th grade. When asked to choose between each species attribute and endemism 3rd grade students chose species people watch over endemic species more often than 5th grade students, and 5th grade students chose species people eat over endemic species more than 3rd grade students (Table 2). Third grade students demonstrated higher variance in their ranking of endemic species (SD = 1.46 vs 1.23), species people eat (SD = 1.51 vs 1.34) and species important in nature (SD = 1.41 vs 1.31).

Table 2 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks, with Mann–Whitney U tests (Z) comparing rankings of each species attribute between the two grades.

1 Associated with comparison of rankings based on grade level (H0 = no difference in rank of species attributes; n = 293)

2 Associated with comparison of rankings based on grade level (H0 = no difference in rank of species attributes; n = 333)

3 Associated with comparison of rankings based on grade level (H0 = no difference in rank of species attributes; n = 420)

* Significant, with α < 0.0125 corrected for false discovery rate (Benjamini & Hochberg, Reference Benjamini and Hochberg1995)

We did not detect a difference in the overall ranking of species attributes or the allocation of money to species with each attribute between white (n = 196) and non-white children (n = 229). However, examining individual attributes we found that white children ranked species with declining numbers higher than non-white children (Table 3). White children also allocated more money to species with declining numbers than non-white children. Non-white children allocated more money to conserving species people watch than white children. When asked to choose between each species attribute and endemism white children chose species with declining numbers over endemic species more often than non-white children (Table 3). Patterns in overall ranking and allocation of money between students attending schools in the low (n = 273) and high (n = 172) socio-economic status groups largely mirrored those evident when comparing white and non-white students (Table 3). This is reasonable as ethnicity was strongly related to socio-economic status in the study area (Macartney et al., Reference Macartney, Bishaw and Fontenot2013). Children from the high socio-economic status group placed more importance on species with declining numbers and less importance on species people watch than did the low socio-economic status group (Table 3). Children at high socio-economic status schools also allocated less money to species people watch, than children at low socio-economic status schools. When asked to compare each attribute to endemism, students in the high socio-economic status group chose species with declining numbers and species people eat more often, and species people watch less often, than the students at the low socio-economic status schools (Table 3).

Table 3 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks, by ethnicity and school socio-economic status (SES), with Mann–Whitney U tests (Z) comparing rankings of each species attribute between ethnicities and socio-economic status.

1 Associated with comparison of rankings based on ethnicity (H0 = no difference in rank of species attributes; n = 288)

2 Associated with comparison of rankings based on socio-economic status (H0 = no difference in rank of species attributes; n = 296)

3 Associated with comparison of rankings based on ethnicity (H0 = no difference in rank of species attributes; n = 331)

4 Associated with comparison of rankings based on socio-economic status (H0 = no difference in rank of species attributes; n = 331)

5 Associated with comparison of rankings based on ethnicity (H0 = no difference in rank of species attributes; n = 293)

6 Associated with comparison of rankings based on socio-economic status (H0 = no difference in rank of species attributes; n = 419)

* Significant with α < 0.0125 corrected for false discovery rate (Benjamini & Hochberg, Reference Benjamini and Hochberg1995)

Discussion

In contrast with research involving adults (Meuser et al., Reference Meuser, Harshaw and Mooers2009), the children surveyed did not consider endemism to be the most important species attribute. They ranked endemic species as fourth most important, below species with declining numbers, species important in nature and species people eat. This outcome could be a result of children having less prejudice against alien species than adults. It has been theorized that implicit racial prejudice develops via exposure to detrimental socializing agents in early childhood (Devine, Reference Devine1989; Sinclair et al., Reference Sinclair, Dunn and Lowery2005). Adults may have a deep natural response, similar to xenophobia towards people, in how they perceive alien plants and animals (Brown & Sax, Reference Brown and Sax2004). Children may be less influenced by this nativist thinking because they have yet to develop prejudices against people, animals or plants that are seen as foreign (Brown & Sax, Reference Brown and Sax2004). Social desirability may have influenced our findings because endemism was the only variable used in multiple comparisons in the last question, perhaps suggesting that researchers cared more about it. However, this seems unlikely as we used three measures to test species attribute preferences and they yielded the same results despite the last question being the only one potentially vulnerable to social desirability bias.

The children prioritized species attributes in much the same way a conservation biologist would. Although conservation biologists have not reached consensus about which species attributes are most important (Wilson et al., Reference Wilson, Joseph, Moore and Possingham2011), species with declining or threatened populations and those with large ecological or evolutionary roles are typically given top priority (Carter et al., Reference Carter, Hunter, Pashley and Rosenberg2000; Forest et al., Reference Forest, Grenyer, Rouget, Davies, Cowling and Faith2007; Isaac et al., Reference Isaac, Turvey, Collen, Waterman and Baillie2007; Redding et al., Reference Redding, DeWolff and Mooers2010). These attributes are the ones the children valued above all others. Being endemic, fun to watch or edible may have some value but if species with these attributes face no threats to future population viability and do not play a critical role in ecosystem function, why dedicate resources to protecting them? As the perspectives of children often influence their parents, from purchasing (Flurry & Burns, Reference Flurry and Burns2005; Walia Sharma & Dasgupta, Reference Walia Sharma and Dasgupta2009) to pro-environmental behaviours (Easterling et al., Reference Easterling, Miller and Weinberger1995; Ballantyne et al., Reference Ballantyne, Connell and Fien1998, Reference Ballantyne, Fien and Packer2001; Duvall & Zint, Reference Duvall and Zint2007; Damerell et al., Reference Damerell, Howe and Milner-Gulland2013), the conservation perspectives of children may be leveraged to influence adults who may prioritize less critical species attributes. Conversely, some of the greatest wildlife conservation challenges require eradication of non-native species, such as feral cats (Ash & Adams, Reference Ash and Adams2003; Robertson Reference Robertson2008; Loss et al., Reference Loss, Will and Marra2013), and typical arguments justifying elimination of species on the basis of non-native or invasive status may not resonate as well among children as among adults.

Unlike studies that identified gender effects on species preferences among adults (Meuser et al., Reference Meuser, Harshaw and Mooers2009; Veríssimo et al., Reference Veríssimo, Fraser, Groombridge, Bristol and MacMillan2009), we did not find any correlations between gender and prioritization of any species attributes. Although there are many gender development theories rooted in diverse biological and social schema, it is widely accepted that the development of gender identity is a dynamic process that is far from complete among children of elementary school age (Bussey & Bandura, Reference Bussey and Bandura1999), and this may explain our lack of findings regarding gender differences in species attribute preferences among children. Social cognitive theory combines psychological and socio-structural determinants to explain gender development as a product of familial and social influences encountered regularly (Bussey & Bandura, Reference Bussey and Bandura1999). These relationships shape the development of gender identity from as early as 2 years old until a person is in their 20s; however, gender development is a dynamic process that can continue throughout life (Martin & Ruble, Reference Martin and Ruble2009; Leman & Tenenbaum, Reference Leman and Tenenbaum2011). Future research may therefore detect gender effects on species attribute preferences in young adults as they gain societal experience. Studies among older students (aged 10–20 years) have identified gender effects, with girls being more oriented towards pets (Bjerke et al., Reference Bjerke, Ødegårdstuen and Kaltenborn1998) and more fearful of animals, particularly threatening species (Prokop & Tunnicliffe, Reference Prokop and Tunnicliffe2010; Prokop & Fančovičová, Reference Prokop and Fančovičová2013). Future research should explore when gender identity begins to influence preferences for species and species attributes.

Differences in grade level, ethnicity and socio-economic status did not correspond to differences in species attribute rankings but were related to differences in mean ranking for some attributes. Our finding that 5th grade students prioritized species with declining numbers more than 3rd grade students indicates that 2 more years of schooling may result in increased knowledge regarding the environment and how organisms are interconnected (Kellert, Reference Kellert1984; Larson et al., Reference Larson, Castleberry and Green2010). This may correspond with species prioritization approaching a conservation biology ideal. Alternatively, 3rd grade students demonstrated more variance in their answers, which could be a result of not being able to read as well and having a less clear understanding of the questions. If this is the case, better reading comprehension could produce results similar to those for 5th grade students. A previous study among adults found that those with a higher level of education had a greater preference for endemic species (Meuser et al., Reference Meuser, Harshaw and Mooers2009); however, the contrast with our results may reflect a difference in the way education level was measured in the two studies.

The relationships between ethnicity and species attribute preferences may be explained by previously established differences in attitudes towards wildlife among ethnic groups; for example, non-white children were found to be more utilitarian than white children (Kellert, Reference Kellert1984). Although recent research among children is limited, research suggests the same pattern has persisted over time among adults (Tarrant & Cordell, Reference Tarrant and Cordell2002; Brown, Reference Brown2003; Manfredo et al., Reference Manfredo, Teel and Bright2003; Teel et al., Reference Teel, Dayer, Manfredo and Bright2005). Because such utilitarian attitudes identified among non-white adults also exist among children, this could explain our finding that non-white children considered edibility and watchability to be more important species attributes than white children. These findings should be interpreted with caution, however, as ethnicity serves as a surrogate for other variables, such as income, education and the incidence of single-parent households (Collins, Reference Collins2004; Duncan & Magnuson, Reference Duncan and Magnuson2005). The fact that our results relating to socio-economic status mirrored those relating to ethnicity supports the assertion that ethnicity may serve as a surrogate for socio-economic status in this case. Research indicates that nature-based education may improve environmental literacy more among minority than non-minority students in the USA (Stevenson et al., Reference Stevenson, Peterson, Bondell, Mertig and Moore2013), and therefore exploring the degree to which similar experiences shape the balance between use-focused and conservation-focused attributes for species conservation would be valuable.

Differences in students’ preferences for species attributes depending on the socio-economic status of their schools may parallel studies linking affluence with pro-environmental attitudes and behaviours among adults (Van Liere & Dunlap, Reference Van Liere and Dunlap1980; Scott & Willits, Reference Scott and Willits1994; Chen et al., Reference Chen, Peterson, Hull, Lu, Hong and Liu2013). This line of research suggests that individuals become more concerned with the environment after their material needs have been met and they shift towards attending to aesthetic needs (Inglehart, Reference Inglehart1995). Our results suggest that children of low socio-economic backgrounds may have a more utilitarian interest in wildlife (e.g. having a stronger preference for species people watch) and those of higher socio-economic backgrounds may be interested in biodiversity conservation for its own sake (e.g. a stronger preference for species with declining numbers). Although our measure of socio-economic status was at the school level, these results warrant future research as this is the first study we are aware of that has investigated how socio-economic status influences children's wildlife conservation priorities.

Further research on how children prioritize species attributes would benefit from consideration of several variables, including geographical location of homes (Miller, Reference Miller2005), significant life experiences in nature (Stevenson et al., Reference Stevenson, Peterson, Carrier, Strnad, Bondell, Kirby-Hathaway and Moore2014), and adult role models (Monroe, Reference Monroe2003), which appear to shape the way children orient themselves towards nature and potentially biodiversity. Similarly, unique geographical contexts, such as islands, may elicit particular species attribute rankings among children (e.g. higher ranking for endemic species) and should be considered. Future research with older children may benefit from choice experiment methodology because it facilitates more realistic trade-offs between species attributes (Hanley et al., Reference Hanley, Mourato and Wright2001; Veríssimo et al., Reference Veríssimo, Fraser, Groombridge, Bristol and MacMillan2009; Di Minin et al., Reference Di Minin, Fraser, Slotow and Macmillan2013). Qualitative research would provide insight into why children think certain species attributes are more important than others. To combat declining global biodiversity, public awareness of the need to preserve biological diversity is crucial. Species attribute preferences among children may provide the foundation for a bridge between the preferences of the public and those of conservation biologists for prioritizing conservation efforts.

Acknowledgements

We thank R. Noss for giving us the idea for this research, E. Meuser, H. Harshaw and A. Mooers for explaining their work with Canadian adults, K. Gutierrez, L. Maynard and the 2014 Human Dimensions of Wildlife class at North Carolina State University for their help with data collection, and the teachers and students who participated in this study.

Biographical sketches

Kristin Frew is studying the valuation of wildlife species in North Carolina. Her interests include environmental education and human dimensions of wildlife science. Nils Peterson's research focuses on unravelling the drivers of environmental behaviour, particularly in contexts of environmental education, conservation development, and biodiversity conservation conflict. Kathryn Stevenson's interests focus on building environmental and climate literacy among elementary to high school students.

References

Arponen, A. (2012) Prioritizing species for conservation planning. Biodiversity and Conservation, 21, 875–893.Google Scholar
Ash, S.J. & Adams, C.E. (2003) Public preferences for free-ranging domestic cat (Felis catus) management options. Wildlife Society Bulletin, 31, 334–339.Google Scholar
Avise, J.C. (2005) Phylogenetic units and currencies above and below the species level. In Phylogeny and Conservation (eds Purvis, A., Gittleman, J.L. & Brooks, T.), 76–100. Cambridge University Press. Cambridge, UK.Google Scholar
Ballantyne, R., Connell, S. & Fien, J. (1998) Students as catalysts of environmental change: a framework for researching intergenerational influence through environmental education. Environmental Education Research, 4, 285–298.Google Scholar
Ballantyne, R., Fien, J. & Packer, J. (2001) Program effectiveness in facilitating intergenerational influence in environmental education: lessons from the field. The Journal of Environmental Education, 32, 8–15.Google Scholar
Bellard, C., Bertelsmeier, C., Leadley, P., Thuiller, W. & Courchamp, F. (2012) Impacts of climate change on the future of biodiversity. Ecology Letters, 15, 365–377.Google Scholar
Benjamini, Y. & Hochberg, Y. (1995) Controlling the false discovery rate: a practical and powerful approach to multiple testing. Journal of the Royal Statistical Society, 57, 289–300.Google Scholar
Bjerke, T., Ødegårdstuen, T.S. & Kaltenborn, B.P. (1998) Attitudes toward animals among Norwegian children and adolescents: species preferences. Anthrozoos, 11, 227–235.Google Scholar
Brown, J.H. & Sax, D.F. (2004) An essay on some topics concerning invasive species. Austral Ecology, 29, 530–536.Google Scholar
Brown, S.E. (2003) Ethnic variations in pet attachment among students at an American school of veterinary medicine. Society & Animals, 11, 101–102.CrossRefGoogle Scholar
Bussey, K. & Bandura, A. (1999) Social cognitive theory of gender development and differentiation. Psychological Review, 106, 676–713.Google Scholar
Butchart, S.H.M., Walpole, M., Collen, B., van Strien, A., Scharlemann, J.P.W., Almond, R.E.A. et al. (2010) Global biodiversity: indicators of recent declines. Science, 328, 1164–1168.Google Scholar
Cardinale, B.J., Duffy, J.E., Gonzalez, A., Hooper, D.U., Perrings, C., Venail, P. et al. (2012) Biodiversity loss and its impact on humanity. Nature, 486, 59–67.CrossRefGoogle ScholarPubMed
Carter, M.F., Hunter, W.C., Pashley, D.N. & Rosenberg, K.V. (2000) Setting conservation priorities for landbirds in the United States: the partners in flight approach. The Auk, 117, 541–548.Google Scholar
Chawla, L. (1999) Life paths into effective environmental action. The Journal of Environmental Education, 31, 15–26.Google Scholar
Chen, X., Peterson, M.N., Hull, V., Lu, C., Hong, D. & Liu, J. (2013) How perceived exposure to environmental harm influences environmental behavior in urban China. Ambio, 42, 52–60.Google Scholar
Collins, F.S. (2004) What we do and don't know about ‘race’, ‘ethnicity’, genetics and health at the dawn of the genome era. Nature Genetics, 36, S13–S15.CrossRefGoogle Scholar
Curnick, D.J., Head, C.E.I., Huang, D., Crabbe, M.J.C., Gollock, M., Hoeksema, B.W. et al. (2015) Setting evolutionary-based conservation priorities for a phylogenetically data-poor taxonomic group (Scleractinia). Animal Conservation, 18, 303–312.Google Scholar
Czech, B., Devers, P.K. & Krausman, P.R. (2001) The relationship of gender to species conservation attitudes. Wildlife Society Bulletin, 29, 187–194.Google Scholar
Czech, B., Krausman, P.R. & Borkhataria, R. (1998) Social construction, political power, and the allocation of benefits to endangered species. Conservation Biology, 12, 1103–1112.Google Scholar
Damerell, P., Howe, C. & Milner-Gulland, E.J. (2013) Child-orientated environmental education influences adult knowledge and household behaviour. Environmental Research Letters, 8, 015016.Google Scholar
Desimone, L.M. & Le Floch, K.C. (2004) Are we asking the right questions? Using cognitive interviews to improve surveys in education research. Educational Evaluation and Policy Analysis, 26, 1–22.Google Scholar
Devine, P.G. (1989) Stereotypes and prejudice: their automatic and controlled components. Journal of Personality and Social Psychology, 56, 5–18.Google Scholar
Di Minin, E., Fraser, I., Slotow, R. & Macmillan, D.C. (2013) Understanding heterogeneous preference of tourists for big game species: implications for conservation and management. Animal Conservation, 16, 249–258.Google Scholar
Duncan, G.J. & Magnuson, K.A. (2005) Can family socioeconomic resources account for racial and ethnic test score gaps? The Future of Children, 15, 15–34.Google Scholar
Duvall, J. & Zint, M. (2007) A review of research on the effectiveness of environmental education in promoting intergenerational learning. The Journal of Environmental Education, 38, 14–24.Google Scholar
Easterling, D., Miller, S. & Weinberger, N. (1995) Environmental consumerism: a process of children's socialization and families’ resocialization. Psychology & Marketing, 12, 531–550.Google Scholar
Flurry, L.A. & Burns, A.C. (2005) Children's influence in purchase decisions: a social power theory approach. Journal of Business Research, 58, 593–601.Google Scholar
Foley, J.A., DeFries, R., Asner, G.P., Barford, C., Bonan, G., Carpenter, S.R. et al. (2005) Global consequences of land use. Science, 309, 570–574.Google Scholar
Forest, F., Grenyer, R., Rouget, M., Davies, T.J., Cowling, R.M., Faith, D.P. et al. (2007) Preserving the evolutionary potential of floras in biodiversity hotspots. Nature, 445, 757–760.Google Scholar
Gelman, R. & Brenneman, K. (2004) Science learning pathways for young children. Early Childhood Research Quarterly, 19, 150–158.Google Scholar
Gorey, K.M. (2001) Early childhood education: a meta-analytic affirmation of the short- and long-term benefits of educational opportunity. School Psychology Quarterly, 16, 9–30.CrossRefGoogle Scholar
Hampshire, M. (2000) Lost in cyberspace. The Times Educational Supplement, 4381, 30–31.Google Scholar
Hanley, N., Mourato, S. & Wright, R.E. (2001) Choice modelling approaches: a superior alternative for environmental valuation? Journal of Economic Surveys, 15, 435–462.Google Scholar
Hooper, D.U., Adair, E.C., Cardinale, B.J., Byrnes, J.E.K., Hungate, B.A., Matulich, K.L. et al. (2012) A global synthesis reveals biodiversity loss as a major driver of ecosystem change. Nature, 486, 105–108.Google Scholar
Inglehart, R. (1995) Public support for environmental protection: objective problems and subjective values in 43 societies. PS: Political Science and Politics, 28, 57–72.Google Scholar
Isaac, N.J.B., Turvey, S.T., Collen, B., Waterman, C. & Baillie, J.E.M. (2007) Mammals on the EDGE: conservation priorities based on threat and phylogeny. PLoS ONE, 2(3), e296.Google Scholar
Iwamura, T., Wilson, K.A., Venter, O. & Possingham, H.P. (2010) A climatic stability approach to prioritizing global conservation investments. PLoS ONE, 5(11), e15103.Google Scholar
Jacobsen, J.B., Boiesen, J.H., Thorsen, B.J. & Strange, N. (2008) What's in a name? The use of quantitative measures versus ‘Iconised’ species when valuing biodiversity. Environmental and Resource Economics, 39, 247–263.CrossRefGoogle Scholar
Kellert, S.R. (1984) Attitudes toward animals: age-related development among children. Advances in Animal Welfare Science, 1, 43–60.Google Scholar
Kellert, S.R. & Berry, J.K. (1987) Attitudes, knowledge, and behaviors toward wildlife as affected by gender. Wildlife Society Bulletin, 15, 363–371.Google Scholar
Knegtering, E., Hendrickx, L., Van Der Windt, H.J. & Uiterkamp, A.J.M.S. (2002) Effects of species’ characteristics on nongovernmental organizations’ attitudes toward species conservation policy. Environment and Behavior, 34, 378–400.Google Scholar
Larson, L.R., Castleberry, S.B. & Green, G.T. (2010) Effects of an environmental education program on the environmental orientations of children from different gender, age, and ethnic groups. Journal of Park & Recreation Administration, 28, 95–113.Google Scholar
Leader Williams, N. & Dublin, H.T. (2000) Charismatic megafauna as ‘flagship species’. In Priorities for the Conservation of Mammalian Diversity: Has the Panda had its Day? (eds Entwistle, A. & Dunstone, N.), pp. 53–81. Cambridge University Press, Cambridge, UK.Google Scholar
Leadley, P., Pereira, H.M., Alkemade, R., Fernandez-Manjarres, J.F., Proença, V., Scharlemann, J.P.W. & Walpole, M.J. (2010) Biodiversity Scenarios: Projections of 21st Century Change in Biodiversity and Associated Ecosystem Services. Secretariat of the Convention on Biological Diversity, Montreal, Canada, CBD Technical Series no. 50, 132 pp.Google Scholar
Legault, L. & Pelletier, L.G. (2000) Impact of an environmental education program on students’ and parents’ attitudes, motivation, and behaviours. Canadian Journal of Behavioural Science, 32, 243–250.Google Scholar
Leman, P.J. & Tenenbaum, H.R. (2011) Practising gender: children's relationships and the development of gendered behaviour and beliefs. British Journal of Developmental Psychology, 29, 153–157.CrossRefGoogle ScholarPubMed
Loomis, J.B. & White, D.S. (1996) Economic benefits of rare and endangered species: summary and meta-analysis. Ecological Economics, 18, 197–206.Google Scholar
Loss, S.R., Will, T. & Marra, P.P. (2013) The impact of free-ranging domestic cats on wildlife of the United States. Nature Communications, 4, 1396.CrossRefGoogle ScholarPubMed
Macartney, S., Bishaw, A. & Fontenot, K. (2013) Poverty rates for selected detailed race and Hispanic groups by state and place: 2007–2011. Https://www.census.gov/prod/2013pubs/acsbr11-17.pdf [accessed 25 February 2016].Google Scholar
Mace, G.M., Possingham, H.P. & Leader-Williams, N. (2007) Prioritizing choices in conservation. In Key Topics in Conservation Biology (eds Macdonald, D. & Service, K.), pp. 17–34. Blackwell Publishing, Oxford, UK.Google Scholar
Manfredo, M.J., Teel, T.L. & Bright, A.D. (2003) Why are public values toward wildlife changing? Human Dimensions of Wildlife, 8, 287–306.Google Scholar
Martin, C.L. & Ruble, D. (2004) Children's search for gender cues: cognitive perspectives on gender development. Current Directions in Psychological Science, 13, 67–70.Google Scholar
Martin, C.L. & Ruble, D.N. (2009) Patterns of gender development. Annual Review of Psychology, 61, 353–381.Google Scholar
Martín-López, B., Montes, C. & Benayas, J. (2007) The non-economic motives behind the willingness to pay for biodiversity conservation. Biological Conservation, 139, 67–82.Google Scholar
Martín-lópez, B., Montes, C., Ramírez, L. & Benayas, J. (2009) What drives policy decision-making related to species conservation? Biological Conservation, 142, 1370–1380.Google Scholar
Meine, C., Soulé, M. & Noss, R.F. (2006) ‘A mission-driven discipline’: the growth of conservation biology. Conservation Biology, 20, 631–651.Google Scholar
Meuser, E., Harshaw, H.W. & Mooers, A.Ø. (2009) Public preference for endemism over other conservation-related species attributes. Conservation Biology, 23, 1041–1046.Google Scholar
Miller, J.R. (2005) Biodiversity conservation and the extinction of experience. Trends in Ecology & Evolution, 20, 430–434.Google Scholar
Monroe, M.C. (2003) Two avenues for encouraging conservation behaviors. Human Ecology Review, 10, 113–125.Google Scholar
Montgomery, C.A. (2002) Ranking the benefits of biodiversity: an exploration of relative values. Journal of Environmental Management, 65, 313–326.Google Scholar
Morse-Jones, S., Bateman, I.J., Kontoleon, A., Ferrini, S., Burgess, N.D. & Turner, R.K. (2012) Stated preferences for tropical wildlife conservation amongst distant beneficiaries: charisma, endemism, scope and substitution effects. Ecological Economics, 78, 9–18.Google Scholar
Norton, B.G. (1986) The Preservation of Species: The Value of Biological Diversity. Princeton University Press, Princeton, USA.Google Scholar
Pereira, H.M., Leadley, P.W., Proença, V., Alkemade, R., Scharlemann, J.P.W., Fernandez-Manjarrés, J.F. et al. (2010) Scenarios for global biodiversity in the 21st century. Science, 330, 1496–1501.Google Scholar
Pimm, S.L., Russell, G.J., Gittleman, J.L. & Brooks, T.M. (1995) The future of biodiversity. Science, 269, 347–350.Google Scholar
Possingham, H.P., Andelman, S.J., Burgman, M.A., Medellín, R.A., Master, L.L. & Keith, D.A. (2002) Limits to the use of threatened species lists. Trends in Ecology & Evolution, 17, 503–507.Google Scholar
Prokop, P. & Fančovičová, J. (2013) Does colour matter? The influence of animal warning coloration on human emotions and willingness to protect them. Animal Conservation, 16, 458–466.Google Scholar
Prokop, P. & Tunnicliffe, S.D. (2010) Effects of having pets at home on children's attitudes toward popular and unpopular animals. Anthrozoos, 23, 21–35.Google Scholar
Redding, D.W., DeWolff, C.V. & Mooers, A.Ø. (2010) Evolutionary distinctiveness, threat status, and ecological oddity in primates. Conservation Biology, 24, 1052–1058.CrossRefGoogle ScholarPubMed
Robertson, S.A. (2008) A review of feral cat control. Journal of Feline Medicine & Surgery, 10, 366–375.Google Scholar
Scott, D. & Willits, F.K. (1994) Environmental attitudes and behavior: a Pennsylvania survey. Environment and Behavior, 26, 239–260.Google Scholar
Serbin, L.A., Powlishta, K.K., Gulko, J., Martin, C.L. & Lockheed, M.E. (1993) The development of sex typing in middle childhood. Monographs of the Society for Research in Child Development, 58, 1–95.Google Scholar
Sinclair, S., Dunn, E. & Lowery, B. (2005) The relationship between parental racial attitudes and children's implicit prejudice. Journal of Experimental Social Psychology, 41, 283–289.Google Scholar
Sodhi, N.S., Posa, M.R.C., Lee, T.M., Bickford, D., Koh, L.P. & Brook, B.W. (2010) The state and conservation of Southeast Asian biodiversity. Biodiversity and Conservation, 19, 317–328.Google Scholar
Stevenson, K.T., Peterson, M.N., Bondell, H.D., Mertig, A.G. & Moore, S.E. (2013) Environmental, institutional, and demographic predictors of environmental literacy among middle school children. PLoS ONE, 8(3), e59519.Google Scholar
Stevenson, K.T., Peterson, M.N., Carrier, S.J., Strnad, R.L., Bondell, H.D., Kirby-Hathaway, T. & Moore, S.E. (2014) Role of significant life experiences in building environmental knowledge and behavior among middle school students. The Journal of Environmental Education, 45, 163–177.Google Scholar
Takahashi, Y., Veríssimo, D., MacMillan, D.C. & Godbole, A. (2012) Stakeholder perceptions of potential flagship species for the sacred groves of the North Western Ghats, India. Human Dimensions of Wildlife, 17, 257–269.Google Scholar
Tarrant, M.A. & Cordell, H.K. (2002) Amenity values of public and private forests: examining the value–attitude relationship. Environmental Management, 30, 692–703.Google Scholar
Teel, T.L., Dayer, A.A., Manfredo, M.J. & Bright, A.D. (2005) Regional Results from the Research Project Entitled ‘Wildlife Values in the West’. Project report for the Western Association of Fish and Wildlife Agencies, Fort Collins, USA.Google Scholar
U.S. Department of Education (2012) National Center for Education Statistics. Https://nces.ed.gov/ [accessed 11 November 2015].Google Scholar
Van Liere, K.D. & Dunlap, R.E. (1980) The social bases of environmental concern: a review of hypotheses, explanations and empirical evidence. The Public Opinion Quarterly, 44, 181–197.CrossRefGoogle Scholar
Veríssimo, D., Fraser, I., Girão, W., Campos, A.A., Smith, R.J. & Macmillan, D.C. (2014) Evaluating conservation flagships and flagship fleets. Conservation Letters, 7, 263–270.CrossRefGoogle Scholar
Veríssimo, D., Fraser, I., Groombridge, J., Bristol, R. & MacMillan, D.C. (2009) Birds as tourism flagship species: a case study of tropical islands. Animal Conservation, 12, 549–558.Google Scholar
Waldron, A., Mooers, A.O., Miller, D.C., Nibbelink, N., Redding, D., Kuhn, T.S. et al. (2013) Targeting global conservation funding to limit immediate biodiversity declines. Proceedings of the National Academy of Sciences of the United States of America, 110, 12144–12148.Google Scholar
Walia Sharma, R. & Dasgupta, P. (2009) Marketing to children: a planning framework. Young Consumers, 10, 180–187.Google Scholar
Weiss, E.B. (1990) Our rights and obligations to future generations for the environment. The American Journal of International Law, 84, 198–207.Google Scholar
Wilson, H.B., Joseph, L.N., Moore, A.L. & Possingham, H.P. (2011) When should we save the most endangered species? Ecology Letters, 14, 886–890.Google Scholar
Figure 0

Table 1 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks. All species attributes compared to endemism (i.e. wild animal species that live only in North Carolina) using the Wilcoxon signed-rank test.

Figure 1

Table 2 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks, with Mann–Whitney U tests (Z) comparing rankings of each species attribute between the two grades.

Figure 2

Table 3 Responses of 3rd and 5th grade students in North Carolina, USA, to three species attribute preference tasks, by ethnicity and school socio-economic status (SES), with Mann–Whitney U tests (Z) comparing rankings of each species attribute between ethnicities and socio-economic status.