Ĭhapin FS, Carpenter SR, Kofinas GP, Folke C, Abel N, Clark WC et al (2010) Ecosystem stewardship: sustainability strategies for a rapidly changing planet. Ĭhan KM, Balvanera P, Benessaiah K, Chapman M, Díaz S, Gómez-Baggethun E et al (2016) Opinion: Why protect nature? Rethinking values and the environment. Wilson Bull 101:11–25Ĭamacho M, Hernández JM, Lima-Barbero JF, Höfle U (2016) Use of wildlife rehabilitation centres in pathogen surveillance: A case study in white storks ( Ciconia ciconia). īlockstein DE (1989) Crop Milk and Clutch Size in Mourning Doves. Ann Stat 29:1165–1188īennett NJ, Whitty TS, Finkbeiner E, Pittman J, Bassett H, Gelcich S, Allison EH (2018) Environmental stewardship: a conceptual review and analytical framework. īenjamini Y, Yekutieli D (2001) The control of the false discovery rate in multiple testing under dependency. īelaire JA, Westphal LM, Minor ES (2016) Different social drivers, including perceptions of urban wildlife, explain the ecological resources in residential landscapes. īateman H, Childers D, Warren P (2018) Data from: Point-count bird censusing: long-term monitoring of bird abundance and diversity along the Salt River in the greater Phoenix metropolitan area, ongoing since 2013 (Reformatted to ecocomDP Design Pattern). īateman HL, Brown JA, Larson KL, Andrade R, Hughes B (2021) Unwanted residential wildlife: Evaluating social-ecological patterns for snake removals. īallantyne R, Packer J, Falk J (2011) Visitors’ learning for environmental sustainability: Testing short- and long-term impacts of wildlife tourism experiences using structural equation modelling. īaicich PJ, Harrison CJ (1997) A guide to the nests, eggs, and nestlings of North American birdsīallantyne R, Packer J (2011) Using tourism free-choice learning experiences to promote environmentally sustainable behaviour: the role of post-visit ‘action resources.’ Environ Educ Res 17:201–215. Īrcher J, Monton S (2011) Preferences for infant facial features in pet dogs and cats. WileyĪllen DC, Bateman HL, Warren PS, de Albuquerque FS, Arnett-Romero S, Harding B (2019) Long-term effects of land-use change on bird communities depend on spatial scale and land-use type. Our findings are relevant to understanding drivers of wildlife stewardship actions and for intake centers who wish to reduce the occurrence of people bringing in wildlife that do not need to be rescued.Īgresti A (2018) An introduction to categorical data analysis. Neighborhoods with greater numbers of rescues were more likely to have residents participating in yard stewardship activities as compared to neighborhoods with fewer rescues. Conversely, few rescues came from neighborhoods with a high percentage of Hispanic/Latinx residents, who often feel more interdependent with nature. We found rescues came from neighborhoods with higher incomes and residents with pro-ecological worldviews, perhaps reflecting a perceived responsibility for wildlife. Altricial species (helpless at hatching) and young birds were more likely to be brought to the center, perhaps due to perceptions of young animals as vulnerable. In Phoenix metropolitan area, Arizona, USA in 2017–2018, we found doves and common species were sent to the center most often. Our study is the first to investigate both the social and ecological drivers of bird rescues using census, household survey, and intake data. Literature has primarily focused on understanding the ecological drivers and implications of wildlife rescues. Some animals are more likely to be brought into a rescue center than others, suggesting that human drivers underlying wildlife rehabilitation efforts are important to understand for urban conservation efforts. Although rescues may be considered a wildlife stewardship behavior, not all ‘rescues’ may be warranted. Animals from urban areas are regularly brought into wildlife rehabilitation centers, providing untapped potential data records to inform management of wildlife species.
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