The Dark Side of Birding: Perceptions of Bird Watching’s Negative Ecological Impacts Lisa Jeane Reznicek Co-advisors Dr.
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The Dark Side of Birding: Perceptions of Bird Watching’s Negative Ecological Impacts Lisa Jeane Reznicek Co-advisors Dr. W. vonZharen and Dr. F. Pearl Texas A&M University at Galveston. Masters in Marine Resources Management ABSTRACT METHODS Birding, the act of observing birds in the outdoors, is a form of nature recreation. The rapid growth and popularity of birding pushes people into remote habitats in search of these birds, creating closer and more extreme encounters that are altering bird physiology and behavior (Blumstein et al., 2005; Erwin, 1989; Koshak, 2007; Smith-Castro and Rodewald, 2009; Sekerciogul, 2002). Often, competition for space or resources can create conflict among recreational users and bird conservation initiatives. The geographic range of the data collection of the study included the upper portion of the Great Texas Birding Trail (GTCBT) and focused on sites and events with the highest number of birding stakeholders who could participate in the study. The GTCBT is one of five state-designated systems of trails, and it identifies sites and resources for birding. RESULTS Through an analysis of targeted data from interviews and surveys from different stakeholders and specialization levels, this study has resulted in both supported and unsupported hypotheses. Even though birders have traditionally been labeled as “nonconsumptive,” there were many interviews which reported perceptions of birders negatively impacting the environments in which they were pursuing their activity. A total of twenty-two negative ecological impacts were noted during the interviews, with calls and playbacks being noted most frequently (23% of all interview responses). There were 243 surveys returned from 443 surveys requested from all possible participants (or a survey response rate of 55%). As a result of surveyed perceptions, participants believe negative ecological impacts to be occurring “Rarely” to "Sometimes" on the five-point Likert scale used in the survey (or a perception score of 2.76). Hypothesis 1 testing results indicated that there was a relationship between the progressive nature of birder specialization and increasing frequency of perceived negative ecological impacts from birding. Therefore, Hypothesis 1 was not supported by the data. HYPOTHESIS 1 RESULTS Results showed a statistically significant difference between intensity levels of birders. Additionally, as birders progress in intensity, they also increase their perceptions of negative impacts from birding. All study participants were asked to voluntarily participate if they fit into the stakeholder criteria. Structured interviews (n= 18) in the spring and summer months of 2011 created a baseline of knowledge and confirmed stakeholder perceptions of impacts from birding. From the interviews, anonymous survey was developed for each stakeholder category. The surveys (n=243) were administered to stakeholders in December 2011 and January 2012, which targeted perceptions of birding’s negative ecological impact and strategies of conservation. A portion of this research examined differences in the various levels of involvement in birding. Birding participants vary in levels of experience, financial investment, and commitment to birding, but many follow a code of ethics to ensure the sustainability of their recreation and the resources needed. As a means to understand differences between birding management stakeholders and within-birder specialization, this study examined perceptions of unethical birding. Unethical birding was surveyed using questions based upon a standard birding code of ethics, previous research on birding impacts, and preliminary interviews. DATA ANALYSIS Through two separate independent T-tests, Hypotheses 2 & 3 were supported . Tests indicated statistically significant differences in perceptions between birders and the two other stakeholder groups. Further exploration of perceptional questions revealed that birders had more perceptional differences with bird managers than birding guides. To begin analyzing within- birder specialization perceptions, birder survey participants (n=213) were segmented into three levels of specialization by a K-means cluster analysis of the twenty questions regarding experience, economic investment, and lifestyle. To answer Hypothesis 1, an Analysis of Variance (ANOVA) test examined for statistical significance difference and a Least Significant Difference (LSD) test defined any differences between the negative ecological impact perceptions of the three levels of birder specialization. HYPOTHESIS 2 & 3 RESULTS Among stakeholders, tests indicated that there was a statistically significant difference between perceptions of birding’s negative ecological impact. 59% of the time, birders perceived the least amount of negative ecological impacts. Figure 3: This figure depicts the two major questions of focus for this study: do birders perceive their own negative ecological impacts differently as they change in level of specialization; and do other stakeholders – bird guides and bird managers - perceive birder impacts differently than birders? : HYPOTHESES 1. Birders’ perception of impact is not significantly (p < .05) related to their specialization level of birding. 3. There is a significant (p > .05) difference between birders’ and birding guides’ perceptions of impact from birding RESEARCH POSTER PRESENTATION DESIGN © 2012 www.PosterPresentations.com Blumstein, D.T., Fernandez-Juricic, E., Zolhner, P. A., and Garity, S.C. , D. F.-J. (2005). Interspecific variation in avian responses to human disturbances. . Journal of Applied Ecology, 42 (5), 943-953. Burger, J., Gochfeld, M., Niles, L. (1995). Ecotourism and birds in coastal New Jersey: Contrasting responses of birds, tourists, and managers. Environmental Conservation 22(1), 5665. Decker, D.J., and Chase, L.C. (1997). Human Dimensions of Living with Wildlife: A Management Challenge for the 21st Century. Wildlife Society Bulletin 25 (4), 788-795. Erwin, R. (1989). Responses to human intruders by birds nesting in colonies: experimental results and management guidelines. Colonial Waterbirds 12 (1), 104-108. Jacobson, S.K., and Duffer, M.D. (1998). Training Idiot Savants: The Lack of Human Dimensions in Conservation Biology. Conservation Biology 12 (2), p 263-267. Johnson, R.B., and Onwuegbuzie, A.J. (2004). Mixed methods research: a research paradigm whose time has come. Educational Researcher 33 (7), 14-26. Kazmierow, B., Hickling, G., and Booth, K. (2000). Ecological and human dimensions of tourism-related wildlife disturbance: White herons at waitangiroto, New Zealand. Human Dimensions of Wildlife 5 (2), 1-14. Koshak, D. C. (2007). The impacts of wildlife viewing and related non-consumptive outdoor recreation activities on avian populations: An annotated bibliography. Denver, CO: Colorado Division of Wildlife. North American Bird Conservation Initiative, U. C. (2011). The State of the Birds 2011 Report on Public Lands and Waters. Washington, D.C.: U.S. Department of Interior. Riley, S. S. (2003). Adaptive impact management: An integrative approach to wildlife management. Human Dimensions of Wildlife 8 (2), 81-95. Sekerciogul, C. H. (2002). Impacts of birdwatching on human and avian communities. Environmental Conservation 29 (3), 282-289. Smith-Castro, Jennifer R. and Rodewald, Amanda D. (2009). Behavioral responses of nesting birds to human. Journal of Field Ornithology 81 (2), 130-138. Wellman, J.D., Roggenbuck, J.W., and Smith, C.A. (1982). Recreation specialization and norms of depreciative behavior among canoeists. Journal of Leisure Research 14 (4), 323-340. ACKNOWLEDGEMENTS By completing a comparative study on perceptions of these impacts from birding along the upper portion of the Great Texas Coastal Birding Trail (GTCBT), professional bird managers and guides will be provided an additional tool for effectively managing people whom they serve. 2. There is a significant (p > .05) difference between birders’ and bird managers’ perceptions of impact from birders. For those who manage and monitor impacts from recreation, understanding human dimensions are critical to the success of wildlife management, facilitating an understanding of resource importance and cooperation amongst those who use public lands. Perceptions form the basis for actions. There must be a consideration of the potential impacts to promote and retain the benefits of wildlife-viewing recreation: benefits to individuals, to communities, and to wildlife (Riley, 2003; Koshak, 2007). Although Hypothesis 1 was not supported by the study results, a surprising relationship between the progressive nature of birder specialization and the increasing frequency of perceived negative ecological impacts from birding was observed. Hypothesis 2 & 3 were supported by the testing results which indicated that birders are the least perceptive to negative ecological impacts from birding among the three stakeholders in this study. Taken together, the results validate the theory that those who have experience at a location or with birding activities may become more sensitive to impacting behaviors. This study has provided scientific data analysis of birding’s perceived negative impacts, as well as strategies for bird conservation. This work provides needed data on the human dimension of natural resource use conflicts for natural resource managers, who require better understanding of their constituents to accomplish recreational and conservation conflict management. From these results, birding managers can begin to identify ways stakeholders and levels of specialization differ in their assessments and evaluation of negative ecological impacts. REFERENCES This study approach to designing and conducting research is important because it reflects the mixed methodology of social and biological science emphasized in natural resource management (Johnson and Onwuegbuzie, 2004; Burger and Gochfeld, 1995; Decker and Chase, 1997; Jacobson and Duffer, 1998; Kazmierow et al., 2000; Wellman et al., 1982). To gauge frequency of perceived negative ecological impacts, a five-point Likert scale was used and then numerically coded for analysis. Comparisons of negative impact perceptions were investigated among birder specialization categories, and between birders and other stakeholders. The qualitative data were open-ended answers evaluated for frequency patterns, and were specifically used with interviews and with conservation strategies from the survey. The second quantitative data set, from the survey questions on specialization and negative ecological impacts, was coded numerically. Quantitative data entry and analysis were performed using the Statistical Package for the Social Sciences (SPSS) version 19. All statistics were evaluated at a 0.05 significance level. CONCLUSIONS Hypotheses2 & 3 compares the average scores from survey questions regarding perceptions of negative ecological impacts. Through two independent T-tests, birders’ impact scores were tested against those of birding guides and bird managers separately. Figure 9: Survey questions regarding perceptions of negative ecological impact from birding were compared between stakeholders to identify specific points of difference. Stakeholder answers to questions are coded according to the five-point Likert scale. There is a big note of gratitude to all the birding stakeholders who were willing to participate in the study and teach me about the world of birding. Although many people helped with the data collection, the faculty at Texas A&M at Galveston provided the academic support needed to develop, advance, and analyze the project. I would like to thank my committee co-chairs, Dr. vonZharen and Dr. Pearl, also my committee members, Dr. Knock and Prof. Bodson, for their guidance and support throughout the course of this research. Thanks also go to my friends and colleagues and the department faculty and staff for making my time at Texas A&M University at Galveston a great experience. Thanks to my ma and pa for their encouragement as well as to my special man-friend for his patience and love. Lastly, the project is a reflection of people who’ve led the way and given me examples to follow. They should be acknowledged for their contributions.