QUANTIFYING THE EFFECTIVENESS OF PUBLIC MEETINGS TO GENERATE PUBLIC PARTICIPATION IN WATERSHED MANAGEMENT by Jennifer Kingsley A thesis submitted in partial fulfillment of the requirements of the degree MASTER OF SCIENCE IN NATURAL RESOURCES Waters Emphasis UNIVERSITY OF WISCONSIN Stevens Point, Wisconsin May 2008 ii ABSTRACT Public involvement has been identified as one of the key aspects of successful watershed management by professionals and researches in the field and is particularly important in the initial phases of management. In the Little Plover River Watershed, in central Wisconsin, stakeholders expressed a need to initiate watershed management. At this early stage in the process public involvement is seriously lacking. The goal of this study was to assess the effectiveness of public meetings to determine if public informational meetings increase a meeting attendee’s willingness to participate in future watershed management activities. A series of eight public informational meetings about the Little Plover River were hosted by several community organizations. A survey was developed to gauge respondent knowledge, behaviors, and demographics. At four of the meetings a survey was given to the respondent prior to the meeting. At four other meetings, the survey was given out after the meeting. A random sampling of the public not attending a meeting was used for a comparison. The study found that meeting attendees had a better understanding of watershed concepts then the public. Post-meeting respondents were better able to identify current issues within the Little Plover River Watershed. It was also found that pre-meeting respondents were more willing to participate in planning for future watershed management then post-meeting respondents were. Overall the public meetings served as a good source of information and education but were not effective at generating increased public participation in planning for watershed management. iii Understanding the effectiveness of public informational meetings is critical for planners and managers that must use public participation methods for management but have time and budget constraints that force them to choose only the public participation methods they feel will provide the biggest outcome. iv ACKNOWLEDGEMENTS This project would not have been possible without the assistance of many people. First and foremost I would like to thank my advisor, Dr. Katherine Clancy, for her support, contribution, and commitment to this project. Without her, this project would have only ever been a dream. I would also like to thank Dr. George Kraft and Dr. Anna Haines for their continued support and interest in this project. My husband, Matt, was with me from the beginning of this project always providing a helping hand and much needed support whenever it was needed. Thanks to his love and encouragement along the way. A big thank you also goes out to my entire family for their love, encouragement, support, and editing talents on this project. v TABLE OF CONTENTS ABSTRACT.....................................................................................................................III ACKNOWLEDGEMENTS ............................................................................................ V LIST OF TABLES AND FIGURES...........................................................................VIII INTRODUCTION............................................................................................................. 1 LITERATURE REVIEW ................................................................................................ 2 Watershed Management ..............................................................................................................................2 Watershed Management Strategies .............................................................................................................3 Public Participation .....................................................................................................................................5 Forms of Public Participation......................................................................................................................6 Evaluating Public Participation .................................................................................................................10 Use of Evaluation ......................................................................................................................................13 Public Participation in Wisconsin .............................................................................................................14 Conclusion.................................................................................................................................................15 METHODOLOGY ......................................................................................................... 16 Objectives..................................................................................................................................................16 Site Description .........................................................................................................................................16 Experimental Design .................................................................................................................................18 Meetings ................................................................................................................................................18 Surveys ..................................................................................................................................................20 Question Types .......................................................................................................................................21 Answer Types..........................................................................................................................................22 Survey Questions ....................................................................................................................................23 Pilot Testing ...........................................................................................................................................30 Sampling Methods.....................................................................................................................................30 ANALYSIS ...................................................................................................................... 33 Demographic Data.....................................................................................................................................33 Spearman Rank-Order Correlation.......................................................................................................34 Knowledge ................................................................................................................................................36 Chi-Square Test......................................................................................................................................37 Mann-Whitney U Test.............................................................................................................................39 Behaviors...................................................................................................................................................42 RESULTS ........................................................................................................................ 44 Section A – Background Knowledge ........................................................................................................44 Section B – Actions and Behaviors ...........................................................................................................51 Section C – Demographic Information......................................................................................................60 Survey Revisions and Results ...................................................................................................................67 vi DISCUSSION .................................................................................................................. 71 Objective 1 ................................................................................................................................................71 Objective 2 ................................................................................................................................................78 Objective 3 ................................................................................................................................................82 Additional Data .........................................................................................................................................87 Overall Findings........................................................................................................................................91 Improvements to Study .............................................................................................................................91 Impacts on Public Participation.................................................................................................................93 LITERATURE CITED .................................................................................................. 96 APPENDICES ............................................................................................................... 100 A. B. C. D. E. F. G. H. I. J. K. L. M. N. O. P. Q. Survey..............................................................................................................................................100 Chi-Square Test for question a-1 .....................................................................................................107 Mann-Whitney U Test for question A-2 ..........................................................................................110 Mann-Whitney U Test for question A-4..........................................................................................121 Respondent’s Rankings for question A-5........................................................................................124 Respondent’s rankings for question A-6 .........................................................................................129 Chi-Square Test for question B-3 ....................................................................................................131 Chi-Square Test for question B-4 ....................................................................................................133 Spearman Rank-Order Correlation Test for willingness to Donate and willingness to participate ..........................................................................................................136 Spearman Rank-Order Correlation Test for respondent income and WILLINGNESS TO PARTICipate...........................................................................................................139 Spearman Rank-Order Correlation Test for respondent income and willingness to participate..................................................................................................................142 Spearman Rank-Order Correlation Test for respondent age and willingness to participate..................................................................................................................145 Spearman Rank-Order Correlation Test for respondent residence and willingness to participate..................................................................................................................148 Spearman Rank-Order Correlation Test for respondent education and willingness to participate..................................................................................................................151 Spearman Rank-Order Correlation Test for respondent income and willingness to donate........................................................................................................................154 Chi-Square Test for revised question A-3 .......................................................................................157 Chi-Square Test for revised question B-3........................................................................................160 vii TABLES AND FIGURES FIGURE 1. Ladder of public participation ..............................................................................................................7 2. Gender demographics of survey respondents ....................................................................................61 3. Age demographics of survey respondents .........................................................................................62 TABLE 1. Watershed Management Unit Characteristics .....................................................................................4 2. Community organizations sampled and size of sample.....................................................................20 3. Example of survey codes used on each survey question ...................................................................31 4. Example of Spearman-Rank Correlation Data and calculation.........................................................35 5. Example of Chi-Square Test calculation...........................................................................................39 6. Example and rank of survey responses for question A-5 and A-6.....................................................41 7. Results of Chi-Square analysis for question A-1...............................................................................45 8. Results of Chi-Square analysis for question A-3...............................................................................49 9. Ranked responses of survey respondent groups for question A-5.....................................................50 10. Ranked responses of survey respondent groups for question A-6.....................................................51 11. Percentage of pre-meeting responses regarding how often respondents participated in the listed activities ..........................................................................................................................52 12. Percentage of post-meeting responses regarding how often respondents participated in the listed activities .............................................................................................................................53 13. Percentage of public responses regarding how often respondents participated in the listed activities...................................................................................................................................54 14. Percentage of pre-meeting respondent’s answers to question B-2 ....................................................55 15. Percentage of post-meeting respondent’s answers to question B-2 ..................................................55 16. Percentage of public respondent’s answers to question B-2 .............................................................56 17. Survey respondent’s willingness to participate .................................................................................56 18. Results of Chi-Square analysis for question B-3...............................................................................58 19. Survey respondent’s willingness to donate money towards watershed management........................58 20. Results of Chi-Square analysis for question B-4 ...............................................................................60 viii 21. Survey respondent’s employment status ...........................................................................................63 22. Survey respondent’s occupational status ...........................................................................................63 23. Survey respondent’s annual income ..................................................................................................64 24. Survey respondent’s home ownership...............................................................................................64 25. Survey respondent’s residence within the Little Plover River watershed .........................................64 26. Survey respondent’s distance of residence from the Little Plover River watershed..........................65 27. Spearman Rank-Order Correlation between survey respondent’s demographics and willingness to participate in future watershed management activities..................................................................66 28. Results of Chi-Square analysis for revised question A-3 ..................................................................68 29. Survey respondent’s willingness to participate with revised categories............................................69 30. Results of Chi-Square analysis for revised question B-3 ..................................................................69 31. Survey respondent’s willingness to participate in future watershed management ............................78 32. Survey respondent’s willingness to participate with revised categories............................................80 33. Age demographics of survey respondent’s and Portage County residents ........................................90 ix INTRODUCTION Watershed management is the management of natural resources based on naturally occurring, hydrologically defined boundaries. This type of management includes the consideration of a wide variety of physical and social variables, including the public who have a vested interest in the watershed (Sabatier et al, 1999). Past management efforts have illustrated the important role that the public plays. Without their acceptance and active participation, management efforts often fail (Nature, 2000). Public participation begins with knowledge and understanding of the watershed, the water resources, and the issues that the watershed faces. If the public has this knowledge it can in turn increases a watershed's value in the public eye (Council of State Governments, 1999). Without establishing a watershed's value we cannot expect voluntary cooperation from the public in management efforts. Public participation has been recognized as such an integral part of the success of watershed management that it is often required in order to receive funding. The Environmental Protection Agency, one of the top watershed funding sources, requires public participation components in both its Section 319 Grants and Targeted Watersheds Program. Hundreds of watersheds throughout the United States face an uncertain future due to the lack of public participation such as the Little Plover River, in central Wisconsin. Surface water discharges are diminishing and the public has expressed the need for watershed management but the process has stalled due to the lack of public involvement. 1 LITERATURE REVIEW Watershed Management Geographer and scientist John Wesley Powell defined a watershed as an “area of land, a bounded hydrologic system, within which all living things are inextricably linked by their common water course and where as humans settled, simple logic demanded they become a part of the community” (U.S. EPA, 2002). This definition not only serves as a definition of a watershed, but also highlights the principles of watershed management. Watersheds, also referred to as drainage basins, are simply an area of land that captures water in any form and drains it to a body of water (DeBarry, 2004). They are determined naturally by geology, soil type, and topography and therefore transcend political and regulatory boundaries. Watersheds acknowledge the connections between ground and surface water, upstream and downstream areas, and land and water interface. They provide us with a unique, comprehensive scale on which to manage our water resources. Watershed management is the integration, coordination, and management of human activities within the natural boundaries of a watershed to protect or improve water quality (Reimold, 1998). The National Research Council (1999) calls watershed management “an integrative way of thinking about all the various human activities that occur on a given area of land (the watershed) that have effects on, or are affected by, water.” 2 3 Managing water resources on a watershed scale is not a new concept globally. Indo-Europeans and ancient Egyptians developed complex plans for land management that included water management methods based on natural watershed boundaries. In ancient Himalaya, village boundaries were determined by natural hydrological boundaries (ICS, 1999). In the United States, the watershed concept was first recognized and became accepted between 1880-1924. It was during this time that John Wesley Powell urged congress to divide the west into districts that corresponded to natural drainage patterns (Sabatier, Weible, Flicker, 2005). During this time Theodore Roosevelt also observed that “every river system, from its headwaters in the forests to its mouth at the coasts, is a single unit and should be managed as such” (U.S. Inland Waterways Commission, 1908). Throughout history, American citizens have demanded economic development while seeking progress in environmental protection and restoration, something that can only be accomplished through the integration of ecological, economic, and social approaches. Watershed management has proven to be one method for addressing these needs. Watershed Management Strategies The process of watershed management includes three basic steps: watershed assessment, developing a management plan, and implementation of the plan. This process has been described as assembling a puzzle (DeBarry, 2004). Watershed assessment collects the biological, physiographic, hydrologic, hydraulic, political and social puzzle pieces. 4 The watershed management plan takes all of the pieces and puts them together and implementation of the plan preserves the puzzle and keeps the puzzle from falling apart (DeBarry, 2004). Beyond this basic framework, there is no consensus on what the essential components of watershed management should be (Reimold, 1998). The strategies used in watershed management often vary from watershed to watershed. Each watershed is unique and must be explored so that specific strategies can be chosen to meet the management goals. Two of the most recognizable management strategies are watershed zoning and best management practices (Reimold, 1998). DeBarry (2004) adds source water identification and protection, minimizing discharges, managing stormwater, land use regulations, and growth management to the list of common strategies. Schueler (1995) goes even further to break a watershed into five units and outlines the management focus or strategy for each of them (Table 1). Table 1.Characteristics that define specific watershed management units (Schueler, 1995). Watershed Management Unit Catchment Typical area, mi2 Influence of impervious cover Primary planning authority Management Focus 0.05-.50 Very Strong Subwatershed 1-10 Strong Property Owner (local) Local government Watershed 10-100 Moderate Subbasin 100-1000 Weak BMP and site design Stream classification and management Watershed based zoning Basin Planning Basin 1000-10000 Very Weak Local or multilocal government Local, regional, or state State, multi-state, or federal Basin Planning 5 The U.S. Environmental Protection Agency developed a Watershed Approach Framework which was “a coordinating framework for environmental management that focuses public and private sector efforts to address the highest priority problems within hydrologically-defined geographic areas, taking into consideration both ground and surface water flow” (U.S. EPA, 1996) and has served as the guide for watershed approaches throughout the U.S. The EPA framework realizes that the individual watershed approach objectives, priorities, elements, and resources will all be different but they should be based on three guiding principles: 1) Strategies are conducted at a specific geographic focus; 2) Strategies utilize sound management techniques based on strong science and data; and, 3) Strategies involve those individuals who are most affected by management decisions. Public Participation Of the EPA principles, watershed managers often struggle with involving the public who will be affected by the management (Duram and Brown, 1999.) The basis for involving the public in the watershed management process is that it will help them understand the problems, identify and buy into goals, select priorities, and choose and implement the solutions (EPA, 1995; Reimold, 1998; DeBerry, 2004; Sabatier et al., 2005). In the past the government attempted to solve problems alone, through a topdown approach. 6 This was often met with resistance from those who lived, worked, or recreated within the area. Private individuals who embarked on management alone often did not have enough time or resources. It is with the combination of these parties that a successful collaborative effort can be achieved that meets the goals and objectives of all. Without support, trust, and participation from the public, management efforts will not be as effective (Nature, 2000; Kerr, 1999). It is widely accepted among professionals in the field that the public needs to be included in management efforts (Wondolleck and Yaffee, 2000; Nature, 2000; and Webler and Tuler, 2001). Glicken (1999) reasons that public participation enhances a decision making process because information from the public provides a holistic view of issues, public involvement creates legitimacy, and public involvement upholds democratic ideals. She stresses that the public is not the decision maker, but rather there to provide input which helps create a well-balanced, sound plan. Over the years there has been a greater understanding of the need for public involvement in management. Managers and planners have seen the increasing value of the information and perspectives that the public is able to bring to the management process. Forms of Public Participation Choosing exactly how to involve the public can be a difficult task. However, before any method of participation is chosen an understanding of how citizens become involved is necessary. There is a clear progression in the levels of participation that the public goes through. 7 Arnstein (1969) first described a “ladder of citizen participation”(Figure 1). The principle behind the participation ladder is that citizens start at the bottom of the ladder in levels of “shallow participation”. At this rung managers and planners are imparting information to the public, but there is no feedback or discussion. The second rung of participation is described as “degrees of tokenism”, in which managers and planners are still imparting education and information to the public, but the public is also providing feedback and discussion. Higher rungs move into increasing “degrees of citizen power”. This is the highest level of citizen participation. At this level information is not only being exchanged, as well as discussion and feedback, but citizens are also involved in the decision making process. The ladder describes a progression of citizen participation because participants start at the bottom and work their way through each level until they reach the top (Arnstein, 1969). Figure 1. The ladder of citizen participation (Arnstein, 1969). citizen control delegated power Degrees of Citizen Power partnership placation Degrees of Tokenism consultation informing therapy manipulation Shallow Participation 8 The International Association of Public Participation (IAP2) has a similar ladder of public participation, but it is instead called the “Spectrum of Public Participation”. IAP2’s spectrum is laid out horizontally, instead of vertically and citizens start at the inform level and move through consulting, involvement, collaborating, and finally into empowering. While the levels may be different, the principal behind each is the same (IAP2, 2007). While the ladder and spectrum of public participation are relatively well understood and accepted by professionals, it can be difficult to determine which specific methods of public participation should be used at various ladder rungs or fall within the spectrum. Methods of public participation are extremely varied in their approaches and results. In 1998, a mail survey of 126 federally funded watershed planning initiatives throughout the U.S. identified newsletters, public meetings, and informational programs were being used by 75% or more of the respondents. Pamphlets, door-to-door contact, surveys, and videos were also being widely used, but to a lesser degree. When respondents were asked what they felt was most effective, door-to-door contact and informational programs were identified (Duram and Brown, 1999). Griffin (1999) wrote a paper that outlined watershed councils as an emerging form of public participation in western states. These councils are composed of governmental and non-governmental stakeholders that come together to make management decisions. Mullen and Allison (1999) outlined several public participation efforts that were making a difference in Alabama, including the Alabama Water Watch Initiative. 9 The Alabama Water Initiative includes a volunteer education program in water resources management, locally led non-point source watershed re-assessments, and continuing public meetings. Konisky and Beierle (1999) identified three very unique public participation processes that were being used in the Great Lakes region. These included study circles, citizen juries or meetings that bring together a statistically representative sample of citizens to deliberate on technically complex issues, and round tables. In 2002, Pierce County Washington used a combination of focused discussion groups, committees, issue workshops, and public meetings to gain the needed public support and feedback for a watershed plan that was being developed (Smolko, Huberd, and Tam-Davis 2002). In the Illinois River Basin, a unique new tool was created to facilitate public participation in watershed management. A baseline impact study was conducted and findings were integrated into a computer-based decision support tool: an interactive, multimedia, impact visualization platform called the Watershed Management Decision Support System. Aerial and ground photography was obtained and combined with Geographic Information Systems base maps to create a background for the visualizations. These backgrounds were then overlaid with the assessments and animated to produce visual images that simulated impacts (Meo, et al. 2002). It was also during this time that sixteen planning regions in Texas had to develop a water plan for the needs of each individual region due to serious drought issues. 10 In the South Central region, a large focus was placed on developing public participation through public meetings, audience surveys, and multiple forms of communication including brochures, newspaper articles, presentations, fact sheets, and newsletters (Moorhouse and Elliff, 2002). Webler and Tuler (2001) choose to take a different route. Instead of identifying specific public participation methods they thought were effective, they instead highlighted key characteristics that make for a “good” public participation method. They explained that any public participation method that is credible, legitimate, competent, information driven, fosters fair democratic deliberation, and emphasizes constructive dialogue and education should be considered a good public participation method. Webler and Tuler developed this list after surveying watershed management planners and activists about what they believed constituted a good public participation method (Webler and Tuler 2001). Evaluating Public Participation It is important for people leading the management process to understand the “effectiveness”, merit or worth of different participation processes (Chess, 2000). Evaluation can help determine when and where to use public participation processes, address criticisms, and help to refine the process and theories for future use (Conley and Moote, 2003). However, determining what constitutes “effective” is difficult since there have been no definitive benchmarks to compare different public participation methods. Efforts to evaluate different methods of public participation can be divided into categories. 11 Outcome vs. Process There are those who evaluate public participation based on the outcome of the method and those who evaluate the process. Process goals are evaluated based on characteristics of the process (Chess and Purcell, 1999). Duram and Brown (1999) evaluated public participation based on process characteristics. They identified five factors that can influence the effectiveness of the public participation process. These include: • The approach to management: whether bureaucratic or grass-roots, • Fourteen different planning stages that can include public participation and whether they include participation throughout or selectively, • Methods to solicit participation; either one way communication or two-way communication, • The level of participation; whether participation is direct or indirect, and • The potential positive impacts of participation on watershed. They claim that a process and its success can be evaluated based on these criteria. Outcome evaluations are often done by comparing goals of a public participation method to the success of the result. What is considered successful varies. Some say that social outcomes such as increased understanding and improved relationships determine success (Buckle and Thomas-Buckle 1986). Others say that the ultimate measure of success is whether the effort leads to improved environmental conditions (Kenney, 1999). Still others stress that it is important to evaluate all of these outcomes (Innes, 1999). 12 The idea of evaluating based on outcomes can be problematic because there is no way to determine if the outcome was due specifically to public participation or other variables (Chess and Purcell 1999). For example, there may be simultaneous events taking place that can influence the process of public participation, the group of people involved or where the process is taking place may have an effect, or even the type of problem that is trying to be solved could have an effect. Theory vs. User Some feel that criteria for evaluating public participation methods should come from theories or from the users themselves. Webler (1995) developed a framework for public participation based on theory. In this framework he argues that evaluation should be based on “fairness” the ability for people to communicate, interact, dialogue, challenge and defend; “Competence” uses the best information available; and “right discourse” using multiple communication methods. These serve as normative criteria that can be applied universally to public participation processes. Others choose to evaluate based on participant’s goals and satisfaction. In this method the goals and satisfaction of the participants are what dictate the success of the process (Chess and Purcell 1999). Wondolleck and Yaffee (1994) used this process in the exploration of U.S. Forest Service efforts. They asked personnel to reflect on successful situations, decide what made them successful, and then construct a definition of success based on that. Blended Still others think that evaluating public participation should combine all of the above methods. 13 Chess and Purcell (1999) advocate for evaluation based on “methodological pluralism”. They suggest that researchers of public participation should solicit from participants their expectations and criteria for success, compare it to theory, and then synthesize the outcomes. In response to Chess and Purcell, Rowe and Frewer (2000) developed what they consider to be a comprehensive framework for evaluation. They evaluated multiple public participation methods based on two categories; acceptance criteria, which evaluates the construction and implementation of the process, and process criteria, which evaluates the public acceptance of the process. Acceptance Criteria includes representativeness of the public, independence of the process, early involvement of the public, influence of the procedure on policy, and transparency of the process to the public. Process Criteria includes resource availability to public participants, definition of tasks for public participants, structured decision-making, and cost-effectiveness. Use of Evaluation Interest in evaluating public participation methods is widespread among the different parties involved in management, but motivations for evaluation vary. Participants want to evaluate their efforts so they can make improvements and meet their goals. Managers and planners use evaluations as guidelines to determine which methods of public participation may be most appropriate for them. Policymakers want evaluations to help them formulate rules and regulations. 14 Advocates use evaluations to prove their success while critics use them to prove that their concerns are well-founded (Innes, 1999 and Coglianese, 1999). Ultimately, we look to evaluations to provide us with three things: 1.) The ability to determine when public participation works; 2.) The ability to address criticisms; and, 3.) The ability to refine methods. It is through evaluation of public participation efforts that evaluators are beginning to realize that public participation can, but does not always, work and when it fails it comes at a potentially heavy cost (Conley and Moote, 2003). Public Participation and Evaluation in Wisconsin It is widely accepted that public participation is critical to watershed management; however, the field is still extremely new. Many researchers identify additional research into the effectiveness of public participation as a great need (Margerum and Born 1999). This is especially true on the local and state scales where many of the theories have not yet been tested, including Wisconsin. Without knowing what methods are in use, it’s impossible to determine their effectiveness. Konisky and Beierle (2001) focused on the Great Lakes Region in their study of “innovative” participation processes. Duram and Brown (1999), in their survey of public participation methods in watershed planning initiatives, used a spatial distribution that focused primarily on the Midwest but no direct focus on Wisconsin. 15 Margerum and Born (1995) highlighted two planning processes in Wisconsin, but did not delve deeply into what public participation methods were being used. Conclusion Public participation has been shown to be an integral part of the watershed process. Not only is it desirable, but often mandated. Public participation processes often vary as do their effectiveness. Watershed managers in Wisconsin need to have a better understanding of how public participation processes are affecting the watershed management process within our own state. They need to identify what processes are being used and to what extent, as well as evaluating how effective they have been. There is a demonstrated need for this knowledge on state and local levels. Without this information, watershed managers within the state may struggle to form integrative public participation processes that represent all perspectives within a watershed. METHODOLOGY Objectives This study was designed to use the Little Plover River Watershed in Plover, Wisconsin as an example to assess the initial phase of public engagement, the public informational meeting, as a form of public participation in watershed management. The goal of this study was to determine if public informational meetings are an effective form of public participation. Three objectives were identified that would serve as a measure of the goal: 1) Determine if public informational meetings increase an attendee’s knowledge about the Little Plover River; 2) Determine if public informational meetings increase an attendee’s willingness to participate in future watershed management activities; and 3) Determine if there are significant differences in knowledge and actions between those who attend the public informational meetings and those who do not. Site Description The focus of the public informational meetings was on the Little Plover River Watershed. The Little Plover River runs southeast of the city of Stevens Point, in Portage County, Wisconsin. 16 17 Primary land uses within the watershed are irrigated vegetable farming, forested land, and residential areas. The Little Plover River is a groundwater fed stream with cold water that supports a Class 1 Trout fishery. The Little Plover River gained public notice when stretches of the river ran dry in the summers of 2005 and 2006, which is something that had never happened before, even in extreme drought situations according to historical and anecdotal evidence. The causes of the low-flow situations are still under investigation, but evidence strongly suggests that agricultural and municipal groundwater withdrawal has affected the flow regime. Due to the river drying up, the public urged for management of the river and the watershed. A workgroup of watershed stakeholders was assembled, which included members of state and local government, agriculture, environmental groups, and some concerned citizens. During the times when stretches of the river ran dry, articles providing information about the situation were published in the Stevens Point Journal and Portage County Gazette, two local newspapers. These articles were meant to make the public aware of what was happening with the Little Plover River, as well as provide basic information and invite them to become involved. Discussions of possible management options for the Little Plover River Watershed have just begun. Participation from the public in the stakeholder workgroup and management discussion has declined over the last year. 18 This river and its watershed will serve as a case study to assess the effectiveness of public informational meetings to generate additional public participation in planning for the management of the Little Plover River. Experimental Design A series of eight public informational meetings about the Little Plover River Watershed were held throughout the Stevens Point community and surrounding area. At four of these meetings attendees received a survey prior to the start of the meeting. At four other meetings attendees received a survey after the meeting was completed. The survey was also administered to a random sample of public who did not attend any of the meetings. Surveys conducted before and after the meeting, as well as the random sampling of the public were compared to determine if the public informational meeting had an effect on the knowledge, attitudes, values, and perceived future behaviors of the meeting attendees. Meetings Public informational meetings were chosen for evaluation because they are one of the most widely used forms of public participation (Duram & Brown, 1999) and because of where they fall on the scale of public participation. Public informational meetings fall in the category between information and education and higher levels of involvement in public participation, indicating that they may be one of the key methods of participation that is able to bring a participant from lower levels of participation into higher levels, something that watershed managers and planners strive for, but ultimately struggle with (IAP2, 2007). 19 The series of eight public informational meetings were offered in the fall and winter of 2007. Each meeting lasted approximately 45 minutes and covered the following information: - Introductory information about the water cycle, watersheds, and groundwater - Background information about the Little Plover River and its watershed; location, uses, historic and current flows - Current issues facing the Little Plover River - Current research on the Little Plover River and the findings - Possible future scenarios for the Little Plover River These meetings were presented to eight established community organizations instead of hosting open public meetings. Presenting to established community organizations guaranteed attendance at each of the eight meetings and ensured a large enough sample size for statistical analysis. The established community organizations also allowed control of a potential source of bias. People who attend open public meetings may already have a vested interest in the subject matter and usually have preconceived ideas and opinions when coming to the meeting. By using the community organizations, individuals attending may or may not have preconceived ideas and opinions. Each community organization that was chosen for a presentation had meetings that were open for the general public to attend. Each meeting was scheduled and advertised in advance to allow people with an interest in the subject matter to attend. 20 A variety of different organizations were chosen for the meetings so that a wide array of demographics, knowledge of the Little Plover River, and actions could be sampled. The eight community organizations that were given a presentation and sampled are found in Table 2. Table 2. Community Organizations Sampled and Size of Sample. Pre-Meeting Survey Post-Meeting Survey Random Survey Soil and Water Conservation Rotary Club of Stevens Amherst County Fair Society Point n=13 n=21 n=5 Members of the University of Stevens Point Kiwanis Stevens Point Harvest Wisconsin-Stevens Point Club Fest Library n=10 Public Meeting n=5 General Federation of Women’s Clubs Leadership Portage County n=15 n=4 n=20 Downtown Stevens Point n=6 n=17 Environmental Educations and Naturalists Association n=9 Survey Surveys were used as the method to gather information from respondents. Surveys were an appropriate method of gathering information because the information being collected regards a respondent’s personal knowledge, actions, behaviors, and demographics (Fink & Kosecoff, 1998). A written survey was given to each meeting attendee and they were asked to complete them on site to ensure high rates of return. At four of the meetings the survey was handed out and completed prior to the meeting starting. At four other meetings the survey was handed out and completed following the meeting. 21 A random sampling of the public who had not attended a meeting was also required for comparison. Random surveys were administered at three different locations; the Amherst County Fair, downtown Stevens Point and the Stevens Point Harvest Fest. These sample sites allowed for a wide variety of survey respondents who were able to complete the survey at their leisure. Convenience samples were used as the sampling method for the surveys. Samples could only be obtained from those organizations that were willing to participate in the informational programs and the survey. The random sample of the public was also a convenience sample, only people who were willing to the complete the survey did. This type of survey samples has the potential to introduce sources of bias. Potential bias may include: public respondents who choose to fill out the survey are more interested in the topic than others, respondents at the already established meetings may have never chosen to attend an open public meeting on the subject, and still other respondents may feel the need to exaggerate in the survey. The survey design is a comparison group design. The control group is the random sample of the public that was surveyed and the two treatment groups are the pre-meeting and post-meeting survey respondents. This design is standard in the social science research when two groups must be compared before and after a treatment. Question Types A variety of different question types were used in the surveys. 22 Seventy-five of the seventy-seven questions asked were forced choice questions, meaning that survey respondents are presented with a statement, question, or situation followed by several alternative choices or solutions that they are able to choose from. This ensures ease of use for survey respondents as well as reliable uniform data for analysis. When using forced choice questions there are rules that must be followed. These include: 1) Each question should pertain to the respondent’s own personal experiences, knowledge, background etc 2) Questions were written using lay language and colloquial wording, for ease of understanding by respondents of all backgrounds 3) Questions should be concrete 4) Avoid biased words and phrases 5) Check your own bias 6) Use caution when asking about the personal (Fink & Kosecoff, 1998) The two questions that are not forced choice are open-ended questions. They both ask for a specific numeric amount that relates to them personally. These are not answers that would be possible to bin or separate into categories. Answer Types When using forced choice questions there are several different forms of answers. The first form of answer used was checklist answers. The respondent was provided with a checklist of answers from which they must choose one or more depending on the instructions. The other form of answer that was used was scale answers. 23 With scales, the respondent places their answer at some point along a continuum or in an ordered series of categories. There are four basic types of scales. These include: 1) Nominal. Nominal scales can also be referred to as categorical scales because respondents give answers based on a group to which they belong: gender, age, schooling, etc. 2) Ordinal. Ordinal scales require respondents to place answers in a rank order. A measure of how strongly a person felt about a statement from strongly agreeing to strongly disagreeing is an example of an ordinal scale. 3) Interval. In the interval scale the distance between numbers has meaning, such as the distance between the values of annual income levels. 4) Ratio. A ratio scale has adjoining units that are equidistant from each other, meaning that you are able to draw comparisons between two values. Surveys rarely utilize ratio scales. (Alreck, 1995) Survey Questions Survey questions were broken down into three different sections: 1) Knowledge 2) Behavior 3) Demographics Each of these sections provides valuable insight into aspects of a respondent’s lifestyle that may influence their willingness to participate in watershed management activities. 24 It also provides us with data to make comparisons and draw conclusions between preand post-meeting survey respondents as well as between meeting attendees and the public. From this data conclusions can be drawn about the effectiveness of public informational meetings. Background Knowledge – Section A The first section in the survey asks questions regarding the respondent’s background knowledge about general watershed concepts, watershed issues throughout the state, and specific knowledge about the Little Plover River. Questions related to background knowledge can be used to determine if public informational meetings had an effect on the level of knowledge of meeting participants. Question A-1 is designed to measure the respondent’s awareness of the watershed concept, the foundation of understanding watershed issues and watershed management. The question is a multiple-choice question with a single response answer. • A-1.) Please put an “X” in front of the statement that best fits your definition of a watershed. Question A-2 measures the respondent’s familiarity and awareness of issues within the Little Plover River Watershed. It uses a Linear-Numeric Scale for the answers. Respondents must choose an answer from the scale of one to four, one being “Not a Problem” to four being a “Serious Problem”. Respondents are also offered a neutral choice of zero, which is “Don’t Know”. 25 • A-2.) Please circle an estimate of how much of a problem you think each of the following issues currently is in the Little Plover River Watershed. Questions A-3 through A-5 are indicative of how an individual feels about the Little Plover River. It is important to determine if the respondent has positive or negative feeling towards the Little Plover River. The intensity of those feelings must also be determined. Question A-3 rates the respondent’s opinion on the perceived condition of the Little Plover River Watershed. This question will use a multiple-choice format with a single response from the respondent. • A-3.) Please put an “X” in front of the statement that best expresses your opinion on current conditions in the Little Plover River Watershed Question A-4 utilizes the Likert Scale to obtain the respondent’s degree of agreement or disagreement with statements regarding the importance of the Little Plover River. The question uses a scale of one to five, with one indicating strong agreement, five indicating strong disagreement, and three indicating a neutral opinion. The respondent will choose a number of one through five for each of the statements. If the respondent is in strong agreement with the statements, they will generally place a high value on the Little Plover River Watershed. If a respondent places a high value on the resource, he or she is more likely to take action to protect or conserve it. 26 • A-4.) Please pick a number from the scale to show how strongly you agree or disagree with each statement and circle the number to the right of the item. Questions A-5 and A-6 indicate which groups the respondent perceives as accountable for issues and management of the rivers and streams in the state of Wisconsin and specifically for the Little Plover River. Questions A-5 and A-6 both utilize a rank order scale in which the respondent must rank the listed options from one through ten, with one being the most responsible and ten being the least responsible. If respondents list local sources or groups that they are involved in as responsible, they may be more inclined to take action than if they listed distant groups or organizations with no relation to themselves. • A-5.) Please rank the following in the order of who you think should be most responsible for protecting Wisconsin’s stream and rivers. 1 is the most responsible, 10 is the least responsible. • A-6.) Please rank the following in the order of who you think should be most responsible for protecting the Little Plover River. 1 is the most responsible, 10 is the least responsible. Behavior - Section B Section B in the surveys addresses past, present, and future behaviors of the survey respondent. 27 A respondent’s behaviors may indicate a predisposition to certain types of involvement or participation in activities related to environmental or watershed activities. Involvement in these activities may also influence a respondent’s knowledge and/or attitudes toward the subject. Questions B-1 and B-2 ask about the type, timing, and frequency of the respondent’s behaviors and activities. Question B-1 asks about respondent’s participation in outdoor recreational activities within the Little Plover River Watershed. Participation in recreational activities within the Little Plover River may indicate a greater familiarity and background knowledge of the watershed and its issues. Question B-2 pertains to the respondent’s participation in activities similar to participating in watershed management. Past behavior can serve as a potential indicator of future behavior. Questions B-1 and B-2 use a verbal frequency scale. Respondents were asked to answer question B-1 using a scale of one through three, one indicating one to two times a year, two indicating one to two times a month, and three indicating one to two times a week. A score of zero was also offered, indicating that they don’t participate in the activity at all. Question B-2 uses a scale of zero, one to four, and five or more indicating the number of times that respondents have participated in the activity. • B-1.) Please indicate how often you partake in each of the following outdoor leisure and recreational activities in or around the Little Plover River. 28 • B-2.) Please circle your rate of involvement for each of the following activities. Questions B-3 and B-4 are questions designed to gauge the respondent’s willingness to participate. Question B-3 asks the respondents about future participation in planning for watershed management. It goes on to ask the respondent to estimate how many hours per month they would be willing to participate. Question B-4 asks respondents if they would be willing to donate money towards management and if so, how much. A measure of a respondent’s willingness to participate is important because it provides a gauge of change between pre- and post-meeting respondents. A higher rate of willingness in post-meeting respondents indicates that the informational meetings may have helped to move citizens into higher rates of participation. A respondent’s willingness to pay may help to explain a respondent’s unwillingness to participate in watershed management. • B-3.) How many hours per month would you be willing to participate in planning for the Little Plover River watershed management? • B-4.) How much money per year would you be willing to donate towards the management of the Little Plover River? Demographics – Section C The questions in the demographics section were used to identify groups of respondents who are distinct or who might behave in similar ways. 29 This section of the survey was used to determine if all demographic groups from within the watershed were represented at the public meetings. Demographic data is the most sensitive data to obtain from a respondent. It is placed at the end of the survey to allow the respondent to become familiar with the survey format and to feel comfortable answering questions, before they are asked to fill out personal information. • C-1.) I am Male or Female • C-2.) Age • C-3.) Formal education.______ years (For example, High school graduate=12 years) • C-4.) Employment Status: • C-5.) Occupational Status: • C-6.) Annual Income: • C-7.) Do you currently own the home you live in? Yes No • C-8.) If yes, how long have you lived there? _________________________ • C-9.) Is your residence in the Little Plover River Watershed? Yes No • C-10.) Please mark the approximate location of your current residence on the map below 30 Pilot Testing Survey questions were pilot tested for clarity of the questions, reliability of the answers, ease of use, and ability to code and analyze. Surveys were first sent through two reviews to edit questions and answers. Surveys were then randomly provided to fifteen people to complete and test. Comments about questions or answers were encouraged. These surveys were then coded and entered into an Excel spreadsheet to test for any errors in the process. Survey questions were further refined to meet the needs of the audience to be sampled and analyzed. Sampling Methods The sample population of the survey was all attendees of the informational meetings on the Little Plover River and the random sampling of the public. The sample unit of the survey was the individual respondents to the survey. Survey questions were pre-coded with response and format codes. Response codes have a number for each alternative response to each structured question. Questions that did not have listed responses were post-coded, or responses were given a number after the surveys were returned. Format codes indicate the position in the spreadsheet where data for each item was entered. The question number corresponds to the section of the survey where the question is found followed by the question number (Table 3). 31 Table 3. Example of survey codes used on each survey question. Question Number Format Code A-1.) Please put an “X” in front of the statement that best fits your definition of a 1 watershed. 1.) ____ Low area that retains water 2.) ____ An area of land that drains water to a specific river or lake 3.) ____ A reservoir that serves a municipal water source 4.) ____ Don’t know Response Codes Surveys were distributed and collected at each of the eight informational meetings. Surveys were handed out prior to four of the meetings and after four other meetings. In addition, a random sample of people who did not attend a meeting were asked to complete a survey. Each survey was given a unique identification number in the corner. All surveys were counted and placed in an envelope with the time, date, and location of where they were administered recorded on the outside. If the surveys were administered at a meeting, the number of meeting participants and the number of surveys collected from the meeting were also recorded. Each survey was evaluated for completeness. If only two to four questions were left unanswered, the survey was still counted as complete. If entire sections were left unanswered the survey was not counted. Superfluous or extra data in the survey was marked out and the survey was still counted. 32 Results from each survey were entered into an Excel spreadsheet. Each sampling location had a separate worksheet within the spreadsheet where data was compiled. Data was then condensed into responses from pre-meeting surveys, postmeeting surveys, all surveys from people who went to meetings (pre- and postmeeting surveys combined), and random samples of people who did not attend meetings, for further analysis. ANALYSIS Surveys given before the meeting, given after the meeting, and given to the public were all independently analyzed for statistically significant relationships of responses between those factors. All surveys were then compared to one another to find statistically significant relationships throughout. Demographic Data Demographic data (Section C) was the first section of data to be analyzed in all of the surveys. Demographic data was condensed into three groups, pre-meeting surveys, post-meeting surveys, and random sampling surveys (the public). Percent of survey respondents in each gender, age, and income category were compared between the groups and then compared to Portage County to ensure that each group of surveys was representative of basic local demographics. Demographic data was also analyzed to see if it could be used as a predictor for a survey respondent’s willingness to participate in future watershed management. A respondent’s willingness to participate was correlated to 4 different factors: 1) Age 2) Education 3) Distance of Residence from Little Plover River Watershed 4) Income All survey respondents that attended a meeting (both pre and post) were analyzed to determine if there were significant correlations between the factors and the willingness to participate, using a Spearman-Rank Correlation Test. 33 34 Spearman Rank-Order Correlation Spearman Rank-Order Correlations are used with categorical data, those that come from nominal or ordinal scales, because it is a non-parametric test. It provides a measure of the degree of association between two sets of ranks (Hollander and Wolfe, 1999). The assumptions associated with this test are as follows: • The two variables are ordinal or metric variables that have been reduced to an ordinal scale of measurement, • The correlation between the variables is linear, and • If a test of significance is applied, the sample has been selected randomly from the population. (Hollander and Wolfe, 1999) D = Difference between X rank and Y Rank N = Number of data points X and Y variables are first ranked. The differences between the X and Y ranks are calculated for each data point. The difference for each point is squared and all are summed. The data is then entered into the Spearman Rank-Order Correlation Equation, which calculates an r-value (Table 4). 35 Table 4. Example of Spearman Rank-Order Correlation Data and Calculation used in the survey. X (Years of Education) X rank 18 14 18 18 12 17 14 18 17 18 16 18 18 17 26 14 9 2 9 9 1 6 2 9 6 9 5 9 9 6 16 2 Y (Willingness to participate) 1 1 1 1 1 1 1 2 1 1 1 1 1 3 1 2 rs = 1- 6*(946) 16 (162-1) x rank-y rank y rank rs = 1- 5676 4080 1 1 1 1 1 1 1 14 1 1 1 1 1 16 1 14 rs = 1-1.39 8 1 8 8 0 5 1 -5 5 8 4 8 8 -10 15 -12 Sum Difference of ranks^2 64 1 64 64 0 25 1 25 25 64 16 64 64 100 225 144 946 rs = 1-1.39 = -.39 An r-value of 1 is a perfect positive correlation (as one variable increases so does the other) and an r-value of -1 is a perfect negative correlation (as one variable increases the other decreases). A correlation of 0.5 or -0.5 or higher is considered to be a significant correlation between a factor and the level of willingness to participate in future watershed management activities. It is important to note that while the Spearman Rank-Order Correlation provides us with a degree of correlation between two variables, it in no way indicates cause and effect relationships between the variables. 36 Questions C-7 through C-10 in the demographics section asked about the survey respondent’s general location of residence compared to the Little Plover River Watershed. Survey respondents were asked to mark the approximate location of their residence on a county map. Responses were binned into categories of distance from the Little Plover River Watershed. All questions in the demographic section were also analyzed using counts and proportions of responses in the categories of pre-meeting attendees, post-meeting attendees, meeting attendees, and random survey samples. Knowledge Questions in Section A evaluated a respondent’s background knowledge of watershed concepts, awareness, and opinions about local and state watershed issues. Questions in Section A were analyzed using tallies and frequencies of responses as well as some specialized tests for comparison. In question A-1 survey respondents were asked to choose the correct definition of a watershed from three possible choices. A neutral option of “I don’t know” was also offered but was discounted from the statistical analysis. The responses to the question were compared between meeting attendees and the public as well as pre-meeting survey respondents and post-meeting survey respondents using a Chi-Square Analysis. 37 Chi-Square Test Chi-Square analysis is a non-parametric test used to determine the probability that an observed distribution of categorical qualitative data, based on rankings or distribution is due to chance alone (Levine, 2005). The Chi-Square statistic used was for two-way tables. A significance value of .05 was used because it is the standard for social science research. The assumptions for the Chi-Square Test are: • Data are random • A sufficiently large sample size (There is no accepted cutoff. Some set the minimum sample size at 50, while others would allow as few as 20) • There must be adequate cell sizes (A common rule is 5 or more in each cell of a 2-by-2 table, and 5 or more in 80% of cells in larger tables, but no cells with zero count) • Observations are independent • Observations must have the same distribution • Hypotheses are non-directional • Observations have finite values • Deviations (observed minus expected values) have a normal distribution (Chekravert, 1967) χ2= Σ (ƒ0-ƒe)2 ƒe ƒ0 = Observed cell frequencies ƒe = Expected cell frequencies The level of significance α= 0.05 38 Hypotheses are as follows: H0: There is no relationship between the row variable and the column variable. Ha: There is a relationship between the row variable and the column variable. Observed data frequencies are entered into a spreadsheet. Expected frequencies for each row and column variable are calculated using (row total)*(column total Sample Size The difference between the observed frequencies and expected frequencies is calculated for each row and column variable. The difference is then squared and divided by the expected frequency. These are all summed to find the Chi-Test statistic. The degrees of freedom for the Chi-Square Test is determined by taking the number of rows minus one and multiplying it by the number of columns minus one ((# of rows-1)*(#of columns-1)). The critical value for the Chi-Square Test is obtained from a Critical Value Table for x2 using the calculated degrees of freedom and level of significance. If the Chi-Test statistic is greater then the critical value you can reject the null hypothesis (Table 5). 39 Table 5. Example of Chi-Square Test Calculation used to compare survey data. Row variable Attend Non Total Observed Frequencies Column variable 1 2 3 2 52 6 17 8 69 2 5 7 Total 56 28 84 Row variable Attend Non Total Expected Frequencies Column variable 3 1 2 5.333333 46 4.666667 2.666667 23 2.333333 8 69 7 Total 56 28 84 Calculations fo-fe -3.33333 3.333333 6 -6 -2.66667 2.666667 (fo-fe)^2/fe 2.083333 0.782609 1.52381 4.166667 1.565217 3.047619 The second question in the knowledge section asked a person to rate their perceived seriousness of each of the listed watershed issues. Respondents were able to respond on a scale of one to four, one being not a problem and four being a serious problem. A neutral option of zero, don’t know, was also offered. A Mann-Whitney U Test was used to determine if there was a difference between pre-meeting responses and post-meeting responses and between meeting attendees and the public who didn’t attend a meeting. Mann-Whitney U Test A Mann-Whitney U test is a non-parametric test used to assess the equality of two population medians (Helsel, 2002). The responses of the pre-meeting survey respondents and post-meeting survey respondents were compared as well as meeting attendee survey respondents and the random survey sample. 40 Where samples of size n1 and n2 are pooled and Ri are ranks. Assumptions for the Mann-Whitney U test are; • Random samples from populations • Independence within samples and mutual independence between samples • Measurement scale is at least ordinal (Helsel, 2002) A significance level of .05 or 95% was used for each comparison. Hypotheses for this test are as follows: H0: There is no difference between the medians of the populations being compared. Ha: There is a difference between the medians of the populations being compared. Question A-3 in the background knowledge section asks respondents to mark which statement they feel best describes the current condition of the Little Plover River Watershed. One is excellent, two is good, three is fair, and four is poor. Statements from pre-meeting survey respondents and post-survey respondents were compared as well as meeting attendee survey respondents and the random survey sample using the Chi-Square Test (See Chi-Square Test for calculation). Question A-4 asked survey respondents how strongly they agreed or disagreed with each statement about the Little Plover River. Survey respondents were asked to provide answers on a scale of one to five, with one being strongly agreed, three was neutral, and five was strongly disagreed. Responses from pre-meeting survey respondents and post-meeting survey respondents were compared, as well as responses from meeting attendee survey respondents and the random survey sample using the Mann-Whitney U test (See Mann-Whitney U Test for Calculations). 41 Questions A-5 and A-6 asked a survey respondent to order the listed parties in order of responsibility for watersheds in the state of Wisconsin and the Little Plover River Watershed itself specifically; one is the most responsible and nine is the least responsible. Data were condensed into answers for pre-meeting survey respondents, post-meeting survey respondents, meeting attendee survey respondents and random survey sample respondents. The total number of responses for each rank of every listed party was calculated. The listed party that received the highest number of responses for a rank received that rank (Table 6). Table 6. Example of Ranked Survey Responses for Questions A-5 and A-6. Highlighted box corresponds to the rank listed for that row. Rank 1 2 3 4 5 6 7 8 9 Fed. Gov. 0 5 2 6 2 3 0 3 5 State Gov. County Gov. Local Munici. Local Landowners Industry/ Business Enviro Groups Farm Groups Educators 13 4 2 3 2 0 0 1 1 4 10 7 2 1 1 1 1 0 5 4 8 4 2 1 4 0 0 4 1 2 6 4 3 5 2 0 1 3 1 4 3 5 3 1 5 1 0 3 1 8 7 4 3 0 1 1 1 3 3 2 9 5 1 1 2 1 1 2 3 0 7 10 Ranking of Parties 1 (most responsible) – State Government 6 – Environmental Groups 2 – County Government 7 – Farm Groups 3 – Local Municipalities 8 - Educators 4 – Local Landowners and Federal Government 9 (least responsible) - Educators 5 – Environmental Groups 42 Behaviors Section B of the survey asked respondents about past, present, and future behaviors that may indicate their predisposition towards participating in watershed management, as well as past experiences with or knowledge of the Little Plover River. All questions in Section B were analyzed using tallies and frequencies of responses. Question B-1 asked respondents how often they participated in each of the listed activities within the Little Plover River Watershed. Responses were binned into categories of one to two times per year, one to two times per month, one to two times per week, or not at all. This question was analyzed using only tallies and frequencies of responses. The question was not analyzed further due to the fact that it was found not to relate to the data that was needed for the study. Question B-2 asked respondents how often they participated in each of the listed activities. Responses were binned into categories of zero, one to four times, or five or more times. The time period for the responses was indicated in each question (ex. Over the past month or in the last five years). Responses for these questions were condensed into pre-meeting responses, post-meeting responses, meeting attendee responses, and random survey sample responses. Pre-meeting and postmeeting responses were compared, as well as the meeting attendee responses and random survey sample responses using the Mann-Whitney U Test (see MannWhitney U Test for calculations). Question B-3, which asked respondents how many hours per month they would be willing to participate in future watershed management activities, was analyzed using the Chi-Square Test (See Chi-Square Test for calculations). 43 Responses from pre-meeting survey respondents were compared to answers from post-meeting survey respondents and responses from meeting attendees were compared to the survey of the public. Question B-4 asked respondents how much money they were willing to donate towards the management of the Little Plover River Watershed. Responses for each category were counted. Pre-meeting survey responses were compared to post-meeting survey responses using the Chi-Square Test (See ChiSquare Test for calculations). A Spearman Rank-Order Correlation test was used to determine if there was a correlation between a respondent’s willingness to participate in watershed management and a respondent’s willingness to donate money towards watershed management. RESULTS Section A – Background Knowledge Question A-1 asked respondents to choose the correct definition of the term “watershed”. Ninety five percent of post-meeting survey respondents were able to correctly identify the definition of a watershed compared to 85% of pre-meeting survey respondents and just 59% of the public. Answers were compared between pre-meeting survey respondents and postmeeting survey respondents, as well as the meeting attendees and the public. The Chi-Square Test was used to determine if there were significant relationships between when a meeting attendee filled out a survey and the definition of watershed chosen, as well as whether a survey respondent attended a meeting or not and the definition of watershed chosen. Hypotheses for these tests are: Pre-meeting respondents vs. Post-meeting respondents Ho: There is no significant relationship between the definition of watershed chosen and when the meeting attendee filled out the survey (pre-meeting or post-meeting). Ha: There is a significant relationship between the definition of watershed chosen and when the meeting attendee filled out the survey (pre-meeting or post-meeting). Meeting attendees vs. the Public Ho: There is no significant relationship between the definition of watershed chosen and whether a respondent attended a meeting or not. 44 45 Ha: There is a significant relationship between the definition of watershed chosen and whether a respondent attended a meeting or not. At a 0.05 level of significance, the meeting attendees vs. the public had a pvalue of 0.001. Results show that there is a significant relationship between the definition of watershed chosen and whether the respondent attended a meeting or not (Appendix B). At the same 0.05 level of significance the comparison between the pre-meeting and survey respondents and post-meeting survey respondents returned a p-value of 0.561. This indicates that there is not a significant relationship between the definition of watershed chosen and whether the respondent filled out the survey prior to the meeting or after the meeting (Table 7 and Appendix B). Table 7. Results of the Chi-Square analysis for question A-1 Variable 1 Variable 2 Critical Value P-Value Pre and Post Definition of watershed chosen Definition of watershed chosen 0.05 0.561 0.05 .0001 Public and Meeting Attendee Question A-2 asked survey respondents how they perceived water related issues in the Little Plover River Watershed. Survey respondent’s answers were given on a Likert Scale of one to four. One indicated that the situation was not a problem and four indicated that the situation was a serious problem. A neutral choice of zero was also offered. 46 Respondents were asked to provide an opinion about 18 different situations which included: nitrate levels in streams, rivers and lakes; nitrate levels in groundwater; pesticide levels in streams, rivers and lakes; pesticide levels in groundwater; soil deposition in streams, rivers and lakes; drinking water quality; soil loss from agricultural fields; rivers and streams with eroding banks; invasive weed growth; loss of water flows; loss of wetlands; loss of forested or wooded areas; loss of wildlife; loss of family farms; loss of agricultural land to development; loss of agricultural land to natural land; loss of natural land to development; and loss of natural land to agricultural production. Of the watershed issues listed, the loss of water flows in the Little Plover River is arguably the largest issue that the watershed faces. Sixty two percent of postmeeting respondents felt that the loss of water flows was a serious issue compared to 50% of the pre-meeting respondents and 37% of the random public. The Mann-Whitney U Test was used to compare all 18 proposed situations between pre-meeting survey respondents and post-meeting survey respondents as well as meeting attendees and the public. The hypotheses for these tests are: Pre-Meeting Respondents vs. Post-Meeting Respondents Ho: There is no statistically significant difference in the responses between premeeting survey respondents and post-meeting survey respondents. Ha: There is a statistically significant difference in responses between pre-meeting survey respondents and post-meeting survey respondents. 47 Meeting Attendees vs. the Public Ho: There is no statistically significant difference in responses between meeting attendees and the public. Ha: There is a statistically significant difference in responses between meeting attendees and the public. At a significance level of 0.05. all of the comparisons between pre-meeting respondents and post-meeting respondents, as well as the comparisons between the meeting attendees and the public all returned p-values higher than 0.05. I was able to conclude from these results that there is not a statistically significant difference between the population’s responses for any of the 18 listed watershed issues (Appendix C). Question A-3 asked respondents to choose a statement that best expressed their opinions about the current condition of the Little Plover River Watershed. Thirty five percent of pre-meeting respondents felt that the Little Plover River Watershed was in poor condition versus 48% of the post-meeting respondents and 38% of the public. Conversely, 65% of the pre-meeting respondents, 52% of the post-meeting respondents, and 62% of the public felt that the watershed was in good or fair condition. The Chi-Square Test was used to determine if there were significant relationships between when a meeting attendee filled out a survey and the perceived condition of the watershed as well as whether a respondent attended a meeting or not and their perceived condition of the watershed. 48 Hypotheses for these tests are: Pre-Meeting Respondents vs. Post Meeting Respondents Ho: There is no significant relationship between the perceived condition of the watershed and when the meeting attendee filled out the survey (pre-meeting or postmeeting). Ha: There is a significant relationship between the perceived condition of the watershed and when the meeting attendee filled out the survey (pre-meeting or postmeeting). Meeting Attendees vs. the Public Ho: There is no significant relationship between the perceived condition of the watershed and whether a respondent attended a meeting or not. Ha: There is a significant relationship between the perceived condition of the watershed and whether a respondent attended a meeting or not. At a 0.05 level of significance the comparison of the pre-meeting respondents versus the post-meeting respondents had a p-value of 0.06. We can conclude that there is not a significant relationship between the perceived condition of the watershed and whether a meeting attendee filled out the survey prior to the meeting or after the meeting (Appendix D). At the same level of significance, the comparison of meeting attendees versus the public had a p-value of 0.8. We can conclude that there is no significant relationship between the perceived condition of the watershed and whether a respondent attended a meeting or not (Table 8 and Appendix D). 49 Table 8. Results of the Chi-Square analysis for question A-3. Variable 1 Variable 2 Critical Value P-Value Pre and Post Perceived condition of the watershed Perceived condition of the watershed 0.05 0.06 0.05 0.8 Public and Meeting Attendee Question A-4 asked respondents how strongly they agreed or disagreed with a statement regarding the Little Plover River and its watershed. Respondents chose their answers based on a Likert scale; one indicating that they strongly agreed with the statement, three was neutral and five indicated they strongly disagreed with the statement. The Mann-Whitney U-Test was used to compare the seven statements between pre-meeting survey respondents and post-meeting survey respondents as well as meeting attendees and the public. The hypotheses for these tests are: Pre-Meeting Respondents vs. Post-Meeting Respondents Ho: There is no statistically significant difference in responses between the premeeting survey respondents and the post-meeting survey respondents. Ha: There is a statistically significant difference in responses between the pre-meeting survey respondents and the post-meeting survey respondents. Meeting Attendees vs. the Public Ho: There is no statistically significant difference in responses between the meeting attendees and the public. Ha: There is a statistically significant difference in responses between the meeting attendees and the public. 50 At a 0.05 level of significance the comparison of the statement responses of the pre-meeting survey respondents and post-meeting survey respondents and the statement responses of the meeting attendees and the public all returned p-values higher then 0.05 indicating that there is no statistically significant difference between the responses of the populations (Appendix E). Question A-5 asks survey respondents to rank nine groups in order of who they felt should be most responsible for protecting Wisconsin’s streams and rivers, with one being the most responsible and ten being the least responsible. Responses were compiled into pre-meeting survey respondents, post-meeting survey respondents, and the public. Each group received the rank that had the highest percentage of responses (Table 9 and Appendix F). Table 9. Ranked Responses of all survey respondent groups for question A-5. Pre-meeting Rank Post-Meeting Rank Public Rank Group 1 1 1 State Government 2 2 4 County Government 3 3&4 1 Local Municipality 4 8 3 Federal Government 2 Local Landowner 5 6 5 Environmental Groups 6 5 7&8 Industry/Business 7 7 6 Farm Groups 8&9 9 9 Educators 51 Question A-6 asks survey respondents to rank the nine groups in order of who they thought they should be most responsible for protecting the Little Plover River, with one was the most responsible and ten being the least responsible. Responses were compiled into pre-meeting survey respondents, post-meeting survey respondents, and the public. Each group received the rank that had the highest percentage of responses (Table 10 and Appendix G). Table 10. Ranked responses of all survey respondent groups for question A-6. Pre-meeting rank Post-meeting rank 1 3 2 2 2 County Government 3 1 1 Local Municipality 4 4&7 5 Federal Government 5 8 4 Environmental Groups 6 5 8 Industry/Business 7 6 6&7 Farm Groups 3 Local landowner 9 Educators Identified as an Self 8 9 9 Identified as an extra Public rank Group State Government extra Section B – Actions & Behaviors Question B-1 asked survey respondents to indicate how often they participated in eleven different activities within the Little Plover River Watershed (Table 11, 12, 13) 52 Table 11. Percentage of pre-meeting responses regarding how often respondents participated in listed activities within the Little Plover River Watershed. 1-2 times per 1-2 times per 1-2 times per Not at all year month week Walking/running 37% 18% 15% 30% Nature 41% 22% 0% 37% Picnicking 37% 4% 0% 59% Biking 26% 15% 11% 48% Hiking 40% 12% 8% 40% Hunting 7% 22% 4% 67% Fishing 8% 19% 4% 69% Boating 19% 7% 0% 74% Camping 19% 7% 0% 74% Cross-Country 19% 0% 0% 81% 9% 5% 5% 81% Observation Skiing Swimming 53 Table 12. Percentage of post-meeting responses regarding how often respondents participated in listed activities within the Little Plover River Watershed. 1-2 times per 1-2 times per 1-2 times per Not at all year month week Walking/running 18% 18% 16% 47% Nature 11% 34% 0% 55% Picnicking 21% 5% 0% 74% Biking 18% 16% 11% 55% Hiking 24% 16% 5% 55% Hunting 3% 3% 3% 92% Fishing 8% 8% 3% 82% Boating 5% 3% 5% 87% Camping 8% 5% 3% 84% Cross-Country 3% 5% 0% 92% 16% 5% 0% 79% Observation Skiing Swimming 54 Table 13. Percentage of public responses regarding how often respondents participated in listed activities within the Little Plover River Watershed. 1-2 times per 1-2 times per 1-2 times per Not at all year month week Walking/running 27% 17% 23% 33% Nature 27% 23% 17% 33% Picnicking 27% 7% 10% 56% Biking 27% 13% 30% 30% Hiking 23% 13% 20% 43% Hunting 7% 3% 7% 83% Fishing 3% 3% 17% 77% Boating 10% 17% 7% 66% Camping 13% 7% 10% 70% Cross-Country 3% 13% 7% 77% 13% 20% 7% 60% Observation Skiing Swimming Question B-2 asked survey respondents to indicate their rate of involvement for eight activities that related to public participation, community involvement, or environmentally related activities. Answers were grouped in categories of zero, one to four, and five or more. The time period for involvement for each activity was specified in the question (Table 14, 15, 16). 55 Table 14. Percentage of pre-meeting respondent’s answers to question B-2. 0 1-4 5 or more 23% 52% 25% How many governmental meetings attended in the past year 54% 32% 14% How many times worked to address a community problem in the 30% 63% 7% 36% 52% 11% 27% 52% 21% 50% 34% 16% 9% 61% 30% 18% 75% 7% Hours per month participated in civic or community organizations last 5 years. How many times worked with a neighbor to solve a problem in the last 5 years. How many conservation programs have participated in, in the last 5 years. How many times talked with public officials about natural resource concerns in last 5 years. Next year how many hours per month participating in civic or community organizations Next year how many conservation programs will participate in Table 15. Percentage of post-meeting respondent’s answers to question B-2. 0 1-4 5 or more 5% 53% 42% How many governmental meetings attended in the past year 60% 35% 5% How many times worked to address a community problem in the 21% 57% 21% 20% 67% 13% 35% 54% 11% 73% 22% 5% 0% 46% 54% 31% 58% 11% Hours per month participated in civic or community organizations last 5 years. How many times worked with a neighbor to solve a problem in the last 5 years. How many conservation programs have participated in, in the last 5 years. How many times talked with public officials about natural resource concerns in last 5 years. Next year how many hours per month participating in civic or community organizations Next year how many conservation programs will participate in 56 Table 16. Percentage of the public’s answers to question B-2. 0 1-4 5 or more 33% 53% 13% How many governmental meetings attended in the past year 65% 33% 2% How many times worked to address a community problem in the 43% 46% 11% 41% 50% 9% 39% 52% 9% 62% 36% 2% 29% 53% 18% 27% 69% 4% Hours per month participated in civic or community organizations last 5 years. How many times worked with a neighbor to solve a problem in the last 5 years. How many conservation programs have participated in, in the last 5 years. How many times talked with public officials about natural resource concerns in last 5 years. Next year how many hours per month participating in civic or community organizations Next year how many conservation programs will participate in Question B-3 asked survey respondents how many hours per month they would be willing to participate in planning for future watershed management activities. Answers were binned into six different categories (Table 17). Table 17. Survey respondent’s willingness to participate in planning for future watershed management activities. Pre-meeting 0-5 5-10 10-15 15-20 20-25 More then hours hours hours hours hours 25 hours 61% 25% 11% 3% 0% 0% 85% 14% 0% 0% 0% 0% 86% 14% 0% 0% 0% 0% respondents Post-meeting respondent Public respondents 57 A Chi-Square Test was used to determine if there was a relationship between a respondent’s willingness to participate and whether they attended a meeting or if they did attend a meeting, whether they filled out a survey prior to the meeting or after the meeting. Hypotheses for these tests are: Pre-Meeting Respondents vs. Post-Meeting Respondents Ho: There is no significant relationship between a respondent’s willingness to participate and whether they filled out a survey prior to or after the meeting. Ha: There is a significant relationship between a respondent’s willingness to participate and whether they filled out the survey prior to or after the meeting. Meeting attendees vs. the Public Ho: There is no significant relationship between a respondent’s willingness to participate and whether they attended a meeting or not. Ha: There is a significant relationship between a respondent’s willingness to participate and whether they attended a meeting or not. At a 0.05 level of significance the comparison of the pre-meeting respondents versus the post-meeting survey respondents had a p-value of 0.04 indicating that there is a significant relationship between a respondent’s willingness to participate and whether they filled out the survey prior to or after the meeting (Appendix H). At the same level of significance the comparison of the meeting attendees and the public had a p-value of 0.37 indicating that there is not a significant relationship between a respondent’s willingness to participate and whether they attended a meeting or not (Table 18 and Appendix H). 58 Table 18. Results of Chi-Square Analysis for question B-3. Variable 1 Variable 2 Critical Value P-Value Pre and Post Willingness to participate in watershed management Willingness to participate in watershed management 0.05 0.04 0.05 0.37 Public and Meeting Attendee Question B-4 asked survey respondents how much money per year they would be willing to donate towards management of the Little Plover River. Answers were divided into categories of zero dollars, one to twenty dollars, twenty to forty dollars, forty to sixty dollars, sixty to eighty dollars, eighty to one hundred dollars, and more then one hundred dollars (Table 19). Table 19. Survey respondent’s willingness to donate money towards watershed management. $0 $1-$20 $20-$40 $40-$60 $60-$80 $80-$100 More then $100 Pre- 28% 40% 20% 0% 3% 6% 3% 19% 39% 19% 3% 8% 8% 3% 33% 46% 14% 5% 0% 2% 0% meeting Postmeeting Public A Chi-Square Test was used to determine if there was a significant relationship between a respondent’s willingness to donate money and when a respondent completed a survey or if a respondent even attended a meeting. 59 Hypotheses for these tests are: Pre-Meeting Respondents vs. Post-Meeting Respondents Ho: There is no significant relationship between a respondent’s willingness to pay and whether they filled out the survey prior to or after the meeting. Ha: There is a significant relationship between a respondent’s willingness to pay and whether they filled out the survey prior to or after the meeting.. Meeting Attendees vs. the Public Ho: There is no significant relationship between a respondent’s willingness to pay and whether they attended a meeting or not. Ha: There is a significant relationship between a respondent’s willingness to pay and whether they attended a meeting or not. At a 0.05 level of significance the comparison of the pre-meeting respondents versus the post-meeting survey respondents had a p-value of 0.98 (Appendix I). This indicates that there is not a significant relationship between a respondent’s willingness to pay and whether they filled out the survey prior to or after the meeting. At the same level of significance the comparison of the meeting attendees and the public had a p-value of 0.30. This also indicates that there is not a significant relationship between a respondent’s willingness to pay and whether they attended a meeting or not (Table 20 and Appendix I). 60 Table 20. Results of Chi-square analysis for question B-4. Variable 1 Variable 2 Pre and Post Willingness to donate 0.05 money towards watershed managment Willingness to donate 0.05 money towards watershed management Public and Meeting Attendee Critical Value P-Value 0.98 0.30 A Spearman Rank-Order Correlation Test was conducted to determine if there was a correlation between the amount of money a respondent was willing to donate and the amount of a time a respondent was willing to participate in watershed management. The Spearman Rank-Order Correlation test returned an r-value of – 0.05 indicating that there is no significant correlation between the two variables or that a respondent’s willingness to participate is not correlated to a respondent’s willingness to donate money towards management (Appendix J). Section C – Demographic Information Question C-1 asked survey respondents if they were male and female (Figure 2). 61 Figure 2. Gender demographics of survey respondents. Gender Demographics of Pre Survey Respondents Gender Demographics of Post Survey Respondents Male Female Male Female Female 50% Male 50% Male 47% Female 53% Gender Demographics for Random Survey Respondents Male Female Female 47% Male 53% Question C-2 asked respondents to choose the category where their age fell. Categories were under eighteen, eighteen to twenty five, twenty six to forty, forty one to sixty, and older than sixty (Figure 3). 62 Figure 3. Age demographics of survey respondents. Age Demographics of Pre Survey Respondents Older then 60 Under 18 0% 2% 41-60 25% Age Demographics of Random Survey Respondents Older then 60 15% 18-25 46% Under 18 17% Under 18 Under 18 18-25 18-25 18-25 19% 26-40 41-60 Older then 60 41-60 30% 26-40 27% 26-40 41-60 Older then 60 26-40 19% Age Demographics of Post Survey Respondents Older then 60 26% Under 18 0% 18-25 23% Under 18 18-25 26-40 26-40 10% 41-60 Older then 60 41-60 41% Question C-3 asked survey respondents their formal education in years. Twelve years is equivalent to a high school graduate. Pre-meeting survey respondents had an average of 16.24 years of education, post-meeting survey respondents had an average of 16.73 years of education, and public survey respondents had an average of 17.42 years of education. 63 Question C-4 asked survey respondents to choose a response that represented their employment status or where the majority of their work hours went (Table 21). Table 21. Survey respondent’s employment status or where the majority of their work hours went. Premeeting respondents Postmeeting respondents Public respondents Company Employed Government Employed SelfEmployed Seeking Employment Military Retired Student 43% 26% 0% 0% 0% 2% 29% 34% 11% 11% 2% 2% 11% 28% 38% 9% 13% 0% 2% 17% 21% Question C-5 asked respondents to choose the option that best described their occupational status (Table 22). Table 22. Survey respondent’s occupational status. Premeeting respondent Postmeeting respondent Public respondent Premeeting respondent Postmeeting respondent Public respondent Professional Managerial Administrative Engineering Marketing 7% 18% 13% 5% 7% 13% 26% 11% 3% 13% 14% 5% 2% 2% 2% Education Agriculture Skilled craft Semiskilled Craft Student 9% 4% 0% 0% 36% 13% 0% 0% 0% 21% 14% 0% 19% 16% 26% Question C-6 asked respondents about their annual income (Table 23). 64 Table 23. Survey respondent’s annual income. $0-$10,000 Pre-meeting 39% respondents 15% Postmeeting respondents 41% Public respondents $10,000$30,000 12% $30,000$60,000 29% $60,000$90,000 15% More then $90,000 5% 6% 26% 21% 32% 11% 33% 6% 9% Question C-7 asked survey respondents if they lived in their own home (Table 24). Table 24. Survey respondent’s home ownership. Yes Pre-meeting respondents 55% Post-meeting respondents 71% 53% Public respondents No 45% 29% 47% Question C-8 asked survey respondents on average how long they had lived in the residence that they owned. Pre-meeting respondents indicated they lived in their home an average of 10.14 years, post-meeting respondents lived in their homes an average of 16.73 years, and public respondents lived in their home an average of 13.62 years. Question C-9 asked survey respondents if their residence was within the Little Plover River Watershed (Table 25). Table 25. Survey respondent’s residence within the Little Plover River Watershed. Yes Pre-meeting respondents 12% Post-meeting respondents 15% 6% Public respondents No 88% 85% 94% 65 Question C-10 asked survey respondents to indicate the approximate location of their current residence. The first category of residences identified were those that lived within the Little Plover River Watershed. Subsequent categories were broken down into those who lived one mile outside of the watershed, 5 miles outside of the watershed, ten miles outside of the watershed, fifteen miles outside of the watershed, or greater then fifteen miles outside of the watershed. A visual map was provided so survey respondents could either mark their residence on the map or in the box indicating the distance from the watershed (Table 26). Table 26. Survey Respondent’s distance of current residence from Little Plover River Watershed. Pre-Meeting PostMeeting Public Within Watershed 1 mile outside 1-5 miles outside 5-10 miles outside 10-15 miles outside 9% 16% 6% 9% 76% 50% 6% 22% 3% 3% 2% 14% 46% 11% 16% More then 15 miles outside 11% The Spearman Rank-Order Correlation was used to determine if certain demographic variables; age, education, income, and the distance of a respondent’s residence from the Little Plover River Watershed, were correlated to a respondent’s willingness to participate in future watershed management activities (Table 27 and Appendices K, L, M, and N). Respondent’s income and willingness to participate had a strongest correlation with an r-value of -0.93. 66 Table 27. Spearman Rank-Order Correlation of survey respondent’s demographic variables and willingness to participate in planning for future watershed management activities. Variable 1 Age Education Income Distance of Residence Variable 2 Willingness to Participate Willingness to Participate Willingness to Participate Willingness to Participate R-value -0.74 -0.77 -0.93 -0.67 67 Survey Revisions and Results After the original data was compiled and analyzed there was a need for some revisions and additional analysis for certain questions. The revisions were made and the analysis was completed. In Question A-3 respondents were asked to mark the response that best expresses their opinion about the current condition of the Little Plover River Watershed. Responses included the options of; Excellent, need no change in management; Good, but could use some improved management; Fair, in need of more management; and Poor, in need of urgent management. When the original Chi-Square Test was conducted, the comparison between the pre-meeting respondents and the post-meeting respondents returned a p-value of 0.06, which is very close to the 0.05 level of significance. Upon further consideration of the question and responses, it was felt that the good and fair categories were very similar and that the test may not have detected the small differences between the two categories. These two categories were combined and the question was again analyzed using the Chi-square test. The pre- and post-meeting responses as well as the meeting attendees and the public were compared again using the same hypotheses as the original test. At a 0.05 level of significance the comparison of pre-meeting respondents and post-meeting respondents, using the newly combined categories of excellent, good/fair and poor, returned a p-value of 0.054, and we were able to conclude that by combining the categories there was still not a relationship between the perceived condition of the watershed and whether the meeting attendee had filled out the survey prior to the meeting or after the meeting (Appendix P). 68 The comparison of the meeting attendees and the public returned a p-value of 0.25, which was p-value lower then the original test but still did not indicate a significant relationship between the variables (Table 28 and Appendix P). Table 28. Results of Chi-Square analysis for revised question A-3. Variable 1 Variable 2 Critical Value P-Value Pre and Post Public and Meeting Attendee Perceived condition of the watershed with revised categories Perceived condition of the watershed with revised categories 0.05 0.054 0.05 0.25 In Question B-3 the Chi-Square Test returned a p-value that was statistically significant, indicating that there was a relationship between a respondent’s willingness to participate in watershed management and whether the respondent filled out the survey prior to the meeting or after the meeting. In the analysis of the results it was discovered that there was difficulty differentiating between the levels of participation in pre-meeting survey respondents versus post-meeting survey respondents due to the way the responses were binned. Responses were binned in categories of zero to five hours, five to ten hours, ten to fifteen hours, fifteen to twenty hours, twenty to twenty five hours, and more then twenty five hours. Because zero was included in the zero to five bin it is difficult to distinguish between people who moved from no willingness to participate to some level of willingness to participate. For that reason, question B-3 was revised and new bins of zero and one were created and the zero to five bin was revised to two to five. 69 The revised survey was given to a sample of the public and a sample of pre-meeting respondents (Table 29). Table 29. Survey respondent’s willingness to participate in future planning for watershed management with revised categories. 0 hours 1 hour 2-5 5-10 10-15 15-20 20-25 More hours hours hours hours hours then 25 hours Pre-meeting 6% 20% 60% 7% 7% 0% 0% 0% 13% 40% 27% 13% 0% 0% 0% 7% survey respondents Public Survey Respondents Results from the new sample of pre-meeting respondents and public were compared using the Chi-Square Test to determine if there was a statistically significant relationship between the respondent’s willingness to participate (with the new categories) and whether a respondent attended a meeting or not. The hypotheses for this test were the same as the original test. At a 0.05 level of significance the comparison of the meeting attendees and the public had a p-value of 0.77. This indicates that there is not a relationship between a respondent’s willingness to pay and whether they attended a meeting or not (Table 30 and Appendix Q). Table 30. Results of Chi-Square analysis for revised question B-3. Variable 1 Variable 2 Critical Value P-Value Pre and Public Willingness to participate in future watershed management with revised categories 0.05 0.77 70 In section C of the survey, demographic variables were correlated with a respondent’s willingness to participate. A question arose as to whether a respondent’s income was correlated to the amount of money that they were willing to donate towards watershed management. A Spearman Rank-Order Test was run to determine if there was a correlation between the two variables. The test returned an rvalue of –0.059, which indicates that there is no correlation between respondent’s income and their willingness to donate money towards watershed management (Appendix O). DISCUSSION The goal of this study was to determine if public informational meetings were an effective method to generate public participation in watershed management activities. This was to be accomplished through three objectives; 1) To determine whether public informational meetings increase an attendee’s knowledge about the Little Plover River; 2) To determine whether public informational meetings increase an attendee’s willingness to participate in future watershed management activities; and 3) To determine whether there are significant differences in knowledge and actions between those who attend the public informational meetings and those who do not Objective 1 The first objective was to determine whether informational meetings increase an attendee’s knowledge about the Little Plover River. A survey respondent’s background knowledge about a subject may be indicative of how familiar he or she is with the watershed and its associated issues such as water quality, water use, and current water levels. It can also indicate a level of advanced understanding about watersheds in general. Often, when an individual understands an issue or subject they are able to make informed decisions and may be inclined to take action. 71 72 The survey asked questions regarding the definition of watershed, the seriousness of issues involving the Little Plover River, and the perceived condition of the watershed. Responses to question A-1, asking the correct definition of a watershed, were first to be analyzed for this objective. The results of this question indicated that 84% of the pre-meeting respondents correctly chose the definition of a watershed compared to 95% of post-meeting respondents. A chi-square test with a significance level of 0.05 determined that there was no relationship between the definition of watershed chosen and whether the meeting attendee filled out the survey prior to the meeting or after the meeting. However, the sample sizes were so small that even the smallest change in the number of responses in each category significantly impacts the p-value of the test. While there was not a relationship between pre and post survey respondents who chose the correct definition of a watershed, there was a decline from pre-meeting attendees to post-meeting attendees who did not select a definition. Seven percent of the pre-meeting respondents did not select a definition compared to zero in postmeeting respondents. This perhaps suggests that pre-meeting respondents were uncomfortable choosing a definition of the concept prior to the meeting. Results of analysis of the responses to this question indicate that all meeting attendees, whether pre or post, are relatively familiar with the watershed concept. The meeting itself is not making a notable difference in the understanding of the watershed concept. 73 The change in percentage of respondents not choosing a definition of watershed is significant to note because it may indicate that post-respondents were more familiar or comfortable with the subject matter to try and choose a definition rather then premeeting respondents. The second set of responses that were analyzed to address the first objective were from question A-2. This question asked respondents to rate the seriousness of 18 different watershed issues in the Little Plover River watershed. Watershed issues included nitrate levels in surface water and groundwater, pesticide levels in surface water and groundwater, soil deposition in surface water, drinking water quality, soil loss from agricultural fields, eroding banks on rivers and streams, invasive weed growth, loss of water flows, loss of wetlands, loss of forested or wooded areas, loss of wildlife, loss of family farms, loss of agricultural land to development, loss of agricultural land to natural land, loss of natural land to development, and loss of natural land to agricultural production. Although these issues are common throughout Wisconsin, not all apply to the Little Plover River Watershed. The responses to this question allowed analysis of a respondent’s familiarity with the particular issues that face the Little Plover River. The familiarity with issues gives insight into how the informational meeting may change the respondent’s understanding of the issue. It also denotes a sense of understanding and knowledge of the watershed that may influence a respondent’s decisions and actions in the future. Of the 18 issues listed, the loss of water flows is arguably the most serious and pressing issue facing the Little Plover River. 74 Fifty two percent of pre-meeting respondents identified the loss of water flows as serious compared to 62% of the post-meeting respondents. A Mann Whitney U-Test was used to determine if the difference in responses between the populations was statistically significant. At a significance level of 0.05 the test returned a p-value of 0.67, therefore it was concluded that there was not a statistically significant difference between the responses of the two populations. In fact, there was not a statistically significant difference in responses of pre-meeting respondents and post-meeting respondents for any of the 18 issues. Results of the Mann-Whitney U-Test indicates that there is not a statistically significant difference in responses to the question that asked respondents to rate the seriousness of the loss of water flows within the Little Plover River watershed. This is an indication that the meeting did not increase a respondent’s awareness about the loss of water flows. The fact that there was a not a statistically significant difference between pre-meeting and post-meeting respondents for any of the 18 issues indicates that the meeting did not increase awareness on any of the issues. It also serves as an indicator that there may be potential bias among the respondents. This is contradictory to expectations that the meetings would increase the awareness of watershed issues from pre-meeting respondents to post-meeting respondents. One explanation was that media exposure about Little Plover River issues may have increased public awareness prior to the meetings. Local newspapers and other media had covered the loss of water flows in the Little Plover River, including memorable photos of fish kills and dry ups when they occurred the two previous summers. 75 If a respondent had been exposed to these media sources, they may have already been familiar with the water loss issues. However, this would not explain the differences between the 17 other issues that were listed. Respondents may have guessed at the answers and assumed that all of the listed issues were applicable to the Little Plover River watershed. Some respondents also may have thought that the question applied to watersheds throughout the entire state, not just the Little Plover River watershed. The responses to question A-3 were also analyzed for this section. This question asked respondents to express their opinion about the current condition of the watershed. Respondents were able to choose from categories that included; Excellent, needs no change in management; Good, but could use some improved management; Fair, in need of more management; and Poor, in need of urgent management. Twenty seven percent of the pre-meeting respondents felt that the watershed was in poor condition and needed urgent management compared to 48% of the post-meeting respondents. Fifty one percent of pre-meeting respondents felt that the watershed was in fair condition and 22% felt that it was in good condition. Forty five percent of post-meeting felt that the watershed was in fair condition and eight percent felt that it was in good condition. A Chi-square test was used to determine if there was a significant relationship between the perceived condition of the watershed and whether the respondent filled out the survey prior to the meeting or after the meeting. The Chi-square test returned a pvalue of 0.06 which indicates there is no significant relationship between the perceived condition of the watershed and when the survey was filled out. However, 0.06 is relatively close to the 0.05 level of significance. 76 Upon closer examination of the question, the categories of good and fair were determined to be very similar to each other in meaning. It was felt that the important difference between categories was not between good and fair but rather between those two categories and excellent or poor. The categories of good and fair were grouped together. The resulting responses were that 73% of premeeting respondents felt that the watershed was in good or fair condition compared to 53% of post-meeting respondents. Twenty seven percent of pre-meeting respondents felt that the watershed was in poor condition while 47% of post-meeting respondents felt it was in poor condition. The Chi-Square Test was re-run with the revised categories of good/fair and poor. The test returned a p-value of 0.054, just over the level of significance set at 0.05. This indicates that there is a relationship even closer then the original test to being significant between the pre-meeting respondents and postmeeting respondents and the perceived condition of the watershed. While the relationship is technically not statistically significant, it is still important to note. The p-value as well as the percentage of respondents in each category suggests that post-meeting respondents are more in tune with what is happening within the watershed. A greater percentage of respondents also indicated that there is an urgent need for management within the Little Plover River. If the need for management is recognized, respondents may be more inclined to participate in the management effort. The reason that the Chi-Square test may not have found the relationship significant is simply due to the size of samples. Larger sample sizes may have made the distinction between the categories more dramatic. 77 These three questions indicate that there were some shifts in levels of knowledge and awareness between pre- and post-meeting respondents. Question one showed an increase in knowledge and understanding in the watershed concept between pre- and post-meeting respondents, with a greater percentage of the sample choosing the correct definition of a watershed in post-meeting respondents. A drop in the percentage of pre-meeting respondents to post-meeting respondents who could not choose a definition was also noted. Question two indicated that both pre- and post-meeting respondents were familiar with issues facing the Little Plover River watershed. Question three indicated that there was a shift in the perceived condition of the Little Plover River Watershed. Pre-meeting respondents felt that the Little Plover River watershed was in good or fair condition. The majority of the post-meeting respondents felt that the Little Plover River watershed was in poor condition. This shift in perceived condition also noted a change in the amount of management that respondents felt was necessary within the watershed. Pre-meeting respondents felt that the Little Plover Watershed was in need of some more or improved management. Post-meeting respondents felt that the watershed was in need of urgent management. While some of these relationships may not have been as statistically significant it is still important that shifts were noticed and it suggests that follow up meetings may be useful in getting the message across. 78 Objective 2 The second objective was to determine if public informational meetings increased an attendee’s willingness to participate in future watershed management activities. An attendee’s willingness to participate is important because it is an indication whether the informational meetings were merely educational and informational or whether they began to shift participants into higher levels of involvement, including participating in management. The first responses that were analyzed for this objective came from question B3, which asked a respondent how many hours per month they would be willing to participate in watershed management activities. Respondents were able to choose from six different categories of time (Table 27). Table 31. Survey respondent’s willingness to participate in planning for future watershed management. Pre-meeting 0-5 5-10 10-15 15-20 20-25 More then hours hours hours hours hours 25 hours 61% 25% 11% 3% 0% 0% 85% 14% 0% 0% 0% 0% respondents Post-meeting respondent A chi-square test was used to determine if there was a relationship between a survey respondent’s willingness to participate and whether they filled out the survey prior to or after the meeting. 79 The chi-square test returned a p-value of .044 indicating that there was a significant relationship between a respondent’s willingness to participate and when they filled out the survey. The respondent’s willingness to donate time shows an unexpected and different result. A greater percentage of pre-meeting respondents were willing to volunteer more hours then post-meeting respondents. This is opposite of what was expected. The difference between pre-meeting respondents and post-meeting respondents may have been due to a number of different things. As explained in the meetings, the Little Plover River’s water quantity issues are directly related to municipal and agricultural pumping. As people sat through the informational meeting they may have begun to feel that this problem was not within their control or that they would not be able to do anything to help with the issue. While it cannot definitively determined what might have caused this difference from the information gathered in this survey, evidence to support this theory comes from question A-6 which asks respondents to rank listed groups in the order of who they think should be most responsible for management on the Little Plover River. Premeeting respondents identified self as one of the groups that should be responsible while post-meeting respondents did not. During the analysis of the responses to question B-3 it was noted that there was no way to determine if respondents had moved from not willing to participate at all to willing to participate some. This was because the level of no participation or zero was combined in the zero to five hours per month category. Using this category, there is no way to differentiate if a respondent is choosing zero or five hours per month. 80 In order to determine if there would be a difference with the zero category separate from the rest the question had to be re-written. The new categories for the question were divided into categories of zero hours, one hour, two to five hours, five to ten hours, ten to fifteen hours, fifteen to twenty hours, and more than twenty five hours. A new survey with the revised categories for question B-3 was given to a sample of the public and pre-meeting (Table 28). Table 32. Survey respondent’s willingness to participate in planning for future watershed management with revised categories. 0 hours 1 hour 2-5 5-10 10-15 15-20 20-25 More hours hours hours hours hours then 25 hours Pre-meeting 6% 20% 60% 7% 7% 0% 0% 0% 13% 40% 27% 13% 0% 0% 0% 7% survey respondents Public Survey Respondents The results indicate that even with the new categories of zero and one hour, over half of the pre-meeting respondents still chose between two and five hours, which reflects the results of the original survey. This demonstrates that the revised categories would not have made a significant difference in the results. It was also important to determine if any of the demographics could serve as a predictor of a respondent’s willingness to participate. This would allow a planner or manager to approach specific demographic groups that might be more inclined to participate in management in the future. 81 The demographic variables that were examined included: age, education, income, and the distance of residence from the Little Plover River Watershed. The Spearman RankOrder Test was used to determine the strength of the correlation between the demographic variable and the respondent’s willingness to participate. The distance of residence from the watershed had the weakest correlation with willingness to participate, which had an r-value of -0.67. This was expected to be one of the demographic variables with the highest correlation. However, survey respondents were asked to mark the approximate location of their current residence. From this information it is clear that more then 53% of all survey respondents live between five and ten miles outside of the Little Plover River Watershed, where both the city of Stevens Point and the village of Plover lie. Very few of the survey respondents actually resided within one mile of, or within, the Little Plover River Watershed. The demographic variable with the highest correlation was income and willingness to participate, with an r-value of -0.93. This indicates a strong negative correlation between the two variables. As a respondent’s income increases, the willingness to participate decreases, which may suggest that respondents are already occupied with things such as work or other volunteer activities and don’t have time to participate in management. The relationship between income and willingness to participate was expected to follow a similar trend as income and participation. The Spearman Rank-Order test was used to determine the correlation between a respondent’s income and their willingness to donate money towards management. The test returned an r-value of –0.059 indicating that there is not a correlation between the variables. 82 This result could be related to the specific nature of the Little Plover River’s problem of water quantity, which may be viewed as a problem government should be required to deal with directly without financial aid. When analyzing the responses for objective two, the results were surprising. It was found that pre-meeting respondents were more willing to participate in watershed management activities then post-meeting participants, suggesting that the meeting was no help in generating participation in activities and may have even been detrimental in this effort. It was also found that income had a strong negative correlation with a respondent’s willingness to participate. While these outcomes were not what were originally expected, they helped show that a respondent’s willingness to participate is extremely variable and can be difficult to predict or even associate with other variables. Objective 3 The purpose of objective three was to determine if there were significant differences in meeting attendee’s knowledge and actions compared to the general public. In this study, the public had the same opportunities for exposure and education prior to the meetings as those who attended the meetings. The public also served as a control group in the study, allowing us to see how people felt and acted towards the Little Plover River and its associated issues without the information and education provided in a meeting. 83 Question A-1, from the previous section, asked respondents for the correct definition of a watershed. However, in this analysis comparisons were made between meeting attendees and the public. Eighty eight percent of the meeting attendees were able to correctly identify the definition of a watershed compared to fifty one percent of the public. A Chi-Square Test was used to determine if there was a statistically significant relationship between the definition of watershed chosen and whether a respondent had attended a meeting. The test returned a p-value of .0001 at a significance level of 0.05, which indicated that there is a strong relationship between the definition chosen and meeting attendance. It was expected that meeting attendees would have a better understanding of the watershed concept because it was a concept that was explained in the meetings. The second set of responses that were analyzed for this objective came from question A-2, which asked survey respondents to rate the seriousness of 18 watershed issues. The loss of water flows was the watershed issue that was focused on for analysis because it is arguably the largest issue facing the Little Plover River. Thirty one percent of the public felt that the loss of water flows was a serious issue compared to fifty seven percent of the meeting attendees. A Mann Whitney U-Test was used to determine if the differences between answers was statistically significant. At a 0.05 level of significance the test returned a p-value of 0.4, which indicates that the difference between the two groups is not statistically significant. While the difference is not statistically significant it is still important to note the difference between 31% of the public and the 57% of the meeting attendees that felt that the loss of water flows was serious. 84 The higher percentage of meeting attendees who felt the issues was serious indicates that meeting respondents may have had a better idea of what was happening in the Little Plover River Watershed. When the responses to the other 17 watershed issues were compared between meeting attendees and the public, it was found that none of the comparisons were statistically significant. The lack of significant difference in responses regarding the loss of water flows could be due to exposure on the issues of the Little Plover River, the same reason for the non-significant difference found between pre-meeting respondents and post-meeting respondents in objective one. Local newspapers and other sources of media had covered the loss of water flows in Little Plover River both summers that it took place. If a respondent had been exposed to these media sources they may have already been familiar with the issue of water loss. For the other 17 issues that were analyzed, respondents may have guessed at the answers and assumed that all of the listed issues were applicable to the Little Plover River watershed. Some respondents may have also thought that the question applied to watersheds throughout the entire state, not just the Little Plover River watershed. The third set of responses that were analyzed for objective three were from question A-3 regarding the perceived condition of the watershed between meeting attendees and the public. Survey respondents were asked to indicate what condition they felt the Little Plover River Watershed was currently in. Respondents were able to choose excellent, good, fair or poor for their responses. The data indicated that 31% of the public felt that the watershed was in poor condition compared to 37% of the meeting attendees. 85 Sixty nine percent of the public felt the watershed was in good or fair condition compared to 63% of the meeting attendees. A Chi-Square Test was used to determine if there was a significant relationship between the perceived condition of the watershed and whether a respondent attended a meeting. At a significance level of 0.05 the test returned a p-value of 0.8 indicating that there is no significant relationship between the perceived condition of the watershed and whether a meeting was attended or not. While there was not a large difference between the percentages of respondents who ranked the watershed in poor condition, meeting attendees still had a slightly higher percentage of respondents who ranked the watershed in poor condition. The fourth set of responses that were analyzed for this objective were from question B-3, which asked survey respondents how many hours per month they would be willing to participate in planning for future watershed management. Respondents were able to choose from six different categories. Eighty six percent of the public were willing to donate between zero and five hours and fourteen percent were willing to donate between five and ten hours. Seventy five percent of meeting respondents were willing to donate between zero and five hours, nineteen percent were willing to donate between five and ten hours, four percent were willing to donate between ten and fifteen hours, two percent were willing to donate between fifteen and twenty hours. A chi-square test was conducted to determine if there was a significant relationship between a respondent’s willingness to participate and whether a respondent attended a meeting or not. The chi-square test returned a p-value of 0.37, indicating that there was no significant relationship between meeting attendance and willingness to participate. 86 While there was not a significant relationship between the two variables, meeting attendees were overall willing to volunteer more time towards watershed management than the public. During the analysis of question B-3 it was noted that there was no way to determine whether respondents were not willing to participate at all or were willing to participate at some level, because the level of not participation or aero was included in the zero to five hours per month category. Using that category there is no way to differentiate whether a respondent chose zero or up to five hours per month. The question had to be re-written to determine whether thee would be a difference with zero separate from the rest of the category. The revised categories of responses for the question were zero hours, one hour, two to five hours, five to ten hours, ten to fifteen hours, fifteen to twenty hours, twenty to twenty five hours, and more then twenty five hours a month. The percentage of survey respondents in each revised category is found in Table 28. The new data indicates that the majority of public respondents chose one hour per month, indicating that the public may be less willing to participate in management activities. The Chi-Square Test was run again using the new data from the pre-survey respondents and the public. This time at a 0.05 level of significance the test returned a p-value of 0.77 indicating that there is still no statistically significant relationship between a survey respondent’s willingness to participate and whether they attended a meeting or not. The seven percent of the public that was willing to participate more then 25 hours per month was a response from one respondent. This is a highly unlikely response that is not typical of the data collected. 87 The responses that were used to evaluate objective three indicate that there were some differences in levels of knowledge, awareness, and actions between meeting attendees and the general public. Responses to question A-1 indicated a higher level of knowledge and understanding about the watershed concept between meeting attendees and the public, with a greater percentage of meeting attendees choosing the correct definition of a watershed. Responses to question A-2 indicated that both meeting attendees and the public were familiar with issues facing the Little Plover River watershed. Responses to question A-3 indicated that there was not a significant relationship between the perceived condition of the watershed and meeting attendance. The original survey data for question B-3 indicated that there were no differences in willingness to participate between meeting attendees and the public. When the survey was revised and the new categories of zero and one hour per month were added, the majority of the public chose the one hour category, indicating that there might be some difference between the revised and original categories. However, the Chi-Square Test still indicated that there was no relationship between the variables. Additional Data Additional data was collected from survey respondents, but was not used to analyze any of the objectives. The additional data can be shared with organizations that are interested in the available information. Question A-2 asked respondents to rate the seriousness of 18 watershed issues. Issue 10, the loss of water flows, was used to help determine the background knowledge of survey respondents. 88 The other 17 issues can be used to help managers and planners determine what were perceived as serious issues within the watershed. The issues perceived as serious by the survey respondents had high percentages of responses that rated it as a serious problem. Sixty three percent of post-meeting respondents identified loss of water flows and invasive weed growth as serious problems. Fifty five percent of pre-meeting respondents identified loss of natural land to development as one of the most serious issues. Fifty four percent of the public identified loss of agricultural land to development as one of the most serious problems. These issues can then be addressed as real concerns within the watershed or something that may be perceived as a concern, but may not be entirely founded in truth. It may also alert planners and managers to issues within the watershed that they may not have been aware of. Question A-4 asked respondents how strongly they agreed or disagreed with statements regarding the Little Plover River watershed. These statements determine how valued the Little Plover River is as a natural resource, source of economics, and recreational opportunity. If a survey respondent values the Little Plover River then he or she may be more inclined to take action towards it. Question A-5 and A-6 ask respondents to rank who is the most to least responsible for management of waters in Wisconsin and the Little Plover River. This determines who respondents think should be in charge of resolving the issue. If respondents feel local organizations or groups and individuals should be in charge they may be more likely to participate in management then if they identify the federal government as the responsible party. Data from question A-6 was also used in the evaluating question B-3 for objective two. 89 Question B-1 asked respondents about their outdoor leisure and recreational activities they participated in while on the Little Plover River. This question simply identifies what activities the Little Plover River is being used for. This question turned out not to be very influential in the survey and thus was not used in any of the analysis. The Little Plover River is a relatively small river and is not extensively used by any of the respondents. That’s not to say it doesn’t have other, more intrinsic values (see question A-4). Paul Radomski, a local citizen, fondly recalls growing up in the area and spending time during his childhood playing and exploring along the river. Question B-2 asked respondents about their involvement in local government, community organizations, and conservation programs. The question was used to try to determine if there were any significant relationships between their past activities and their willingness to participate in future activities. No relationships could be found with the data gathered. Question B-4 asked respondents how much money they would be willing to donate towards management of the Little Plover River. There were no significant differences in the amount of money that respondents were willing to donate towards management. A Chi-Square Test was used to determine whether was a significant relationship between a respondent’s willingness to donate and their meeting attendance, or when meeting attendees completed the survey before or after the meeting. No relationship was found. The majority of all respondents were willing to donate between one and twenty dollars a year. The Chi-Square analysis of this question was not used to meet any of the objectives of this study. However, a correlation of a respondent’s income and their willingness to donate was used in objective two. 90 Section C asked questions regarding basic demographics of the survey respondents. The demographics were not only used as variables to predict a respondent’s willingness to participate or donate, but were also used to determine whether the samples were representative of the population. The basic demographics of gender and age of survey respondents were compared to those of Portage County. Portage County demographics were obtained from the U.S. Census Bureau 2000 Census Survey. Portage County gender demographics are split 50% male and 50% female. The survey age demographics were also split 50/50 between male and female. Age demographics for both the survey respondents and Portage County residents can be found in Table 29. Table 33. Age Demographics of Survey Respondents and Portage County Residents. Survey Under 18 18-25 26-40 41-60 Older then 60 6% 29% 19% 32% 14% 29% 11% 28% 18% 14% Respondents Portage County Residents Differences between the ages of survey respondents and residents of Portage County can be explained by audiences that were targeted for the surveys. Surveys were not targeted at youth or students under the age of 18. This age group is not likely to become involved in watershed management activities. Stevens Point is also a college town. The majority of surveys were conducted while college was in session when there is a significant increase in college age students (ages 18-25) within the community. We expected to see a larger number of students in this age group in the survey samples. 91 Overall, the demographics of the survey respondents do not significantly differ from the population of Portage County. Overall Findings The findings of the surveys indicate that the informational public meetings are a good source of information and education to participants. Survey respondents were more aware of issues within the watershed and better understood the concepts related to watershed management after the meetings. However, participants were not more inclined to participate in future watershed management activities after attending the meetings. Referring back to the spectrum of public participation, informational public meetings fell in the second category of participation, degrees of tokenism or consulting. It was at a level where the proposed method of public participation could possibly move participants into higher levels of participation such as degrees of citizen power or involvement. This study was unable to determine that the informational meetings had that impact. The surveys indicated that public meetings would be a better method of distributing information and education, placing it in the first category of shallow participation or informing the public. Improvements to Study There are some changes that should be made if this study were repeated. An obvious change would be the revisions to the willingness to participate question. 92 Breaking out the zero category would have provided more definitive results as well as a stronger analysis of the question. The second improvement would have been sample sizes. While it was a struggle to obtain the current survey samples, additional samples would have provided an even better idea of the differences between the public, pre-meeting attendees, and post-meeting attendees. Larger samples may have also provided more definitive answers on some of the questions that were very close. Another change to the study would have been a follow-up survey to meeting attendees. The follow-up survey could have asked questions about their current involvement in watershed management activities, how the information from the meeting has been put to use in their lives, whether they have shared the information from the meeting, and their current knowledge about watershed issues. The follow-up survey could have been sent out approximately six months after the initial survey was given. The additional follow-up survey would not have only provided additional data that better indicates the impact of the meeting, but it would have also eliminated another potential source of bias between pre and post meeting respondents. While analyzing this survey, additional questions about survey respondents were raised and could have been included in the survey. Identifying a survey respondent’s level of previous exposure to general watershed issues, as well as specific issues within the Little Plover River would have been extremely helpful. This information would have helped to eliminate some speculation surrounding the non-significant differences in responses about watershed issues. It also would have been helpful to determine what sources of information survey respondents had utilized. 93 This could have helped determine if respondents were using reliable sources of information. It also would provide managers and planners with some idea of what information sources the public uses so that they could make use of those for future management and public participation efforts. Impacts on Public Participation There are a number of characteristics about the watershed that could have potentially impacted public participation efforts in this study. The Little Plover River is a small body of water with a small watershed. People may not see a strong value associated with such a small body of water. There is also not a very clear idea of the economic impact of this river. Both of these factors create a sense that the river may be somewhat disposable. In this case the issue becomes one of economic value. The Little Plover River does not have a clear economic value associated with its dry-up. In the case of the Little Plover River, the way people view the “worth” or the economic impact of the river varies greatly, due in large part to a relatively distinct generation gap. Older individuals remember and relate to the river when it had higher water levels, more significant flow, hosted a well-known trout fishery, and was in a more rural area. Younger individual’s have only known the river in an urban setting and at much lower water flows that limit some uses of the river. The differences in the perceptions of the river between the two generations impact the individual’s value of the river and thus might impact their efforts to protect the river. 94 One of the other factors that should be considered is that the loss of water flows on the Little Plover River is largely an intangible issue. While the diminished flows themselves are extremely tangible, the underlying cause is not. The Little Plover River is largely groundwater fed making it a groundwater issue. Getting the public to connect groundwater pumping to surface water levels is a well-known difficulty. Perhaps it is difficult for the public to become involved with something that they cannot directly see or deal with. Even considering the effect that these factors could have on the study, there still remains one large issue. The informational meeting was a single event that introduced most of the participants to the in-depth issues of the Little Plover River Watershed. Research has shown that while a single event, like a public meeting, may be successful at increasing short term knowledge, in order to be truly successful they should be linked with a broader communication strategy. By becoming a part of a continuous series of events, the same messages can be repeated multiple times (Seevers et al, 1997). Research has also shown that the more people are familiar with a topic the more likely they are to become involved. However, in order to become involved the knowledge needs constant updating and reminders (Coyle, 2004). This research helps to identify that the true threshold for moving individuals into higher levels of participation may not lie exclusively in the method of public participation itself but perhaps in a combination of the method or methods and the number of times an individual hears the same message. 95 It also shows that these meetings serve as an opportunity to disseminate accurate information and education to the public in an informal manner as well as allowing meeting attendees to participate in a dialogue. While public meetings may not be the key to solving watershed management issues nor the ideal public participation method, it is certainly a powerful tool that managers and planners should continue to use. LITERATURE CITED Alreck, Pamela L. and Robert B. Settle. 1995. The Survey Research Handbook. Boston: Irwin/McGraw Hill. Arnstein, Sherry R. 1969. A Ladder of Citizen Participation. American Institute of Planners Journal. 35(4): 216-224. Chakravart, I.M., R.G. Laha and J. Roy. 1967. Handbook of Methods of Applied Statistics Volume 1. New York, Wiley Chess, C. 2000. Evaluating Environmental Public Participation: Methodological Questions. Journal of Environmental Planning and Management. 43(6):769784 Chess, C. and K. Purcell. 1999. Public Participation and the Environment: Do We Know What Works? Environmental Science and Technology. 38(16):26852692 Conglianese, C. 1999. The Limits of Consensus. Environment. 41(3): 28-33 Conley, A. and M.A. Moote. 2003. Evaluating Collaborative Natural Resource Management. Society and Natural Resources. 16:371-386 Council of State Governments.1999. Getting in Step: Guide to Effective Outreach in Your Watershed. Environmental Protection Agency. Coyle, Kevin. 2004. Education – An Essential Ingredient for Successful Water Management: Opening Keynote Address. Best Education Practices (BEPs for Water Outreach Professionals: Defining BEPs, Refining New Resources and Recommending Future Actions. June 2004 Symposium Proceedings. DeBarry, P. 2004. Watersheds: Processes, Assessment and Management. Hoboken, New Jersey: John Wiley & Sons Dillman, P.A. 1978. Mail & Telephone Surveys: The total design method. New York: John Wiley & Sons, Inc. Duram, L.A. and K.G. Brown. 1999. Assessing Public Participation in U.S. Watershed Planning Initiatives. Society & Natural Resources. 12:455-467 Fiorino, D.J. 1990. Citizen Participation and Environmental Risk: A Survey of Institutional Mechanisms. Science, Technology, & Human Values. 15(2):226243 96 97 Frewer, L.J. and R. Shepard. 1998. Consumer Perceptions of Modern Food Biotechnology. Genetic Engineering for the Food Industry: A Strategy for Food Quality Improvement. New York: Blackie Academic. 27-46 Glicken, J. 1999. Effective Public Involvement in Public Decisions. Science Communication. 20(3):298-327 Griffin, C.B. 1999. Watershed Councils: An Emerging Form of Public Participation in Natural Resource Management. Journal of the American Water Resources Association. 35(3): 505-516 Helsel, D.R and R.M. Hirsch. 1993. Statistical Methods in Water Resources. Amesterdam, Elsevier Press. Hollander, M. and D. A. Wolfe. 1999. Nonparametric Statistical Methods (2nd ed.) NewYork: Wiley Innes, J.E. 1999. Evaluating Consensus Building. The Consensus Building Handbook: A Comprehensive Guide to Reaching Agreement. Thousand Oaks, CA: Sage International Association for Public Participation. 2007. IAP2 Spectrum of Public Participation. http://www.iap2.org/associations/4748/files/IAP2%20Spectrum_vertical.pdf International Center for Integrated Studies (ICS). 1999. Integrated Assessment, A Bird's-eye View. Introductory Guide for European Summer school Puzzle Solving for policy: tools and methods for integrated assessment. The Netherlands: 30 Masstrcht Kerr, M. 1999. Creating Community Support for Watershed Management. Maritimes. 41(3) Konisky, D.M. and T.C. Beierle. 2001. Innovations in Public Participation and Environmental Decision Making: Examples from the Great Lakes Region. Society and Natural Resources. 14:815-826 Levine, David M. and David F. Stephan. 2005. Even You Can Learn Statistics. Upper Saddle River, New Jersey: Pearson Prentice Hall 98 Margerum, R.D. and S.M. Born. 1995. Integrated Environmental Management: Moving From Theory to Practice. Journal of Environmental Planning & Management. 38(3):271-392 Meo, M., W. Focht, L. Caneday, R. Lynch, F. Moreda, B. Pettus, E. Sankowski, Z. Trachtenberg, B. Vieux, and K. Willett. 2002. Negotiating Science and Values With Stakeholders in the Illinois River Basin. Journal of the American Water Resources Association. 35(2): 541-554 Moorhouse, M. and S. Elliff. 2002. Planning Process for Public Participation in Regional Water Resources Planning. Journal of the American Water Resources Association. 38(2):531-540 Mullen, M.W. and B.E. Allison. 1999. Stakeholder Involvement and Social Capital: Keys to Watershed Management Success in Alabama. Journal of the American Water Resources Association. 35(3):655-662 National Research Council. 1999. New Strategies for America’s Watersheds. Washington, D.C.: National Academy Press Nature. 2000. Benefits of Increased Public Participation. Nature. 45:259 Reimold, R.J. 1998. Watershed Management Practice, Policies, and Coordination. New York: McGraw-Hill Rowe, G. and L.J. Frewer. 2000. Public Participation Methods: A Framework for Evaluation. Science, Technology, & Human Values. 25(1):3-29 Sabatier, P., C. Weible, and J. Flicker. 2005. Eras of Water Management in the United States: Implications for Collaborative Watershed Approaches. Swimming Upstream Collaborative Approaches to Watershed Management. London: MIT Press. Schueler, T. 1995. Site Planning for Urban Stream Protection. Washington: Metropolitan Washington Council of Governments. Seevers, B., D. Graham J. Gamon and N. Conklin. 1997. Education Through Cooperative Extension. Albany, New York: Delmar Publishers. Smith, L.G. 1983. Impact Assessment and Sustainable Resource Management. Harlow, UK: Longman. Smith, L.G., C.Y. Nell, and M.V. Prystupa. 1997. The Converging Dynamic of 99 Interest Representation in Resources Management. Environmental Management. 21(2):139-146 Smolko, B.A., R.R. Huberd, and N. Tam-Davis. 2002. Creating Meaningful Stakeholder Involvement in Watershed Planning in Pierce County, Washington. Journal of the American Water Resources Association. 38(4):981-994 U.S. Environmental Protection Agency. 2002. What is a Watershed? http://www.epa.gov/owow/watershed/whatis.html U.S. Inland Waterways Commission. 1908. Report to Congress of the Inland Waterways Commission. Washington, D.C.: U.S. Inland Waterways Commission. Webler, T. 1995. “Right” Discourse in Citizen Participation: An Evaluative Yardstick. In Fairness and Competence in Citizen Participation: Evaluating Models for Environmental Discourse. Dordecht, the Netherlands: Kluwer Academic. 3586 Webler, T and S. Tuler. 2001. Public Participation in Watershed management Planning: Views on Process from People in the Field. Human Ecology Review. 8(2):29-38 Wondolleck, J. and S. Yafee. 2000. Making Collaboration Work: Lessons from Innovation in Natural Resource Management. Washington, D.C.: Island Press. Appendix A Survey 100 101 102 103 104 105 106 Appendix B Chi-Square Test for question A-1 107 108 Chi-Square for question A-1 Meeting Attendees vs. Public Observed Frequencies Column variable Row variable 1 2 Attend 4 65 Non 11 24 Total 15 89 Row variable Attend Non Total Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 3 2 7 9 Total 71 42 113 Expected Frequencies Column variable 1 2 3 9.424779 55.92035 5.654867 5.575221 33.07965 3.345133 15 89 9 Total 71 42 113 Calculations 0.05 2 3 2 Results Critical Value 5.9915 Chi-Square Test Statistic 18.7227 p-Value 0.0001 Reject the null hypothesis Expected frequency assumption is met. fo-fe -5.42478 5.424779 9.079646 -9.07965 -3.65487 3.654867 (fofe)^2/fe 3.122431 5.278396 1.474239 2.492166 2.362222 3.993281 109 Chi-Square for 2question A-1 Pre-meeting respondents vs. Postmeeting respondents Observed Frequencies Column variable Row variable 1 2 3 Pre 3 37 Post 1 38 Total 4 75 Row variable 1 2 3 Expected Frequencies Column variable 1 2 3 Pre 2 37.5 1.5 Post 2 37.5 1.5 Total 4 75 3 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom Total 41 41 82 Calculations 0.05 2 3 2 Results Critical Value 5.9915 Chi-Square Test Statistic 1.3467 p-Value 0.5100 Do not reject the null hypothesis Expected frequency assumption is met. Total 41 41 82 1 -1 0.5 0.5 fo-fe -0.5 0.5 -0.5 0.5 (fo-fe)^2/fe 0.006667 0.166667 0.006667 0.166667 Appendix C Mann-Whitney U Test for question A-2 110 111 Results for: Question A-2 Meeting Attendees vs. the Public Issue A Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 8.00 3.00 Point estimate for ETA1-ETA2 is 5.00 96.3 Percent CI for ETA1-ETA2 is (-7.99,24.00) W = 32.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4034 The test is significant at 0.4020 (adjusted for ties) Issue B Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 6.00 6.00 Point estimate for ETA1-ETA2 is 3.00 96.3 Percent CI for ETA1-ETA2 is (-6.00,28.01) W = 30.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6742 (adjusted for ties) Issue C Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 12.00 2.00 Point estimate for ETA1-ETA2 is 5.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,29.00) W = 31.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4647 The test is significant at 0.4578 (adjusted for ties) Issue D Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 11.00 5.00 Point estimate for ETA1-ETA2 is 6.00 96.3 Percent CI for ETA1-ETA2 is (-8.01,22.99) W = 31.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4647 The test is significant at 0.4633 (adjusted for ties) 112 Issue E Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 12.00 4.00 Point estimate for ETA1-ETA2 is 8.00 96.3 Percent CI for ETA1-ETA2 is (-7.00,22.99) W = 32.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.3472 The test is significant at 0.3457 (adjusted for ties) Issue F Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 18.00 4.00 Point estimate for ETA1-ETA2 is 7.00 96.3 Percent CI for ETA1-ETA2 is (-2.99,19.00) W = 34.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2101 The test is significant at 0.2059 (adjusted for ties) Issue G Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 13.00 6.00 Point estimate for ETA1-ETA2 is 7.00 96.3 Percent CI for ETA1-ETA2 is (-8.00,20.99) W = 34.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2101 The test is significant at 0.2073 (adjusted for ties) Issue H Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 17.00 5.00 Point estimate for ETA1-ETA2 is 8.00 96.3 Percent CI for ETA1-ETA2 is (-7.01,20.00) W = 34.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2101 The test is significant at 0.2073 (adjusted for ties) 113 Issue I Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 11.00 3.00 Point estimate for ETA1-ETA2 is 2.00 96.3 Percent CI for ETA1-ETA2 is (-7.01,33.01) W = 32.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4034 The test is significant at 0.4020 (adjusted for ties) Issue J Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 7.00 6.00 Point estimate for ETA1-ETA2 is 4.00 96.3 Percent CI for ETA1-ETA2 is (-6.00,32.00) W = 30.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6742 (adjusted for ties) Issue K Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 9.00 3.00 Point estimate for ETA1-ETA2 is 6.00 96.3 Percent CI for ETA1-ETA2 is (-9.01,28.00) W = 30.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6015 The test is significant at 0.6004 (adjusted for ties) Issue L Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 10.00 8.00 Point estimate for ETA1-ETA2 is 3.00 96.3 Percent CI for ETA1-ETA2 is (-6.00,23.01) W = 33.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2506 The test is significant at 0.2477 (adjusted for ties) 114 Issue M Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 8.00 7.00 Point estimate for ETA1-ETA2 is 5.00 96.3 Percent CI for ETA1-ETA2 is (-4.01,23.00) W = 33.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2963 The test is significant at 0.2918 (adjusted for ties) Issue N Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 12.00 5.00 Point estimate for ETA1-ETA2 is 7.00 96.3 Percent CI for ETA1-ETA2 is (-4.00,19.99) W = 34.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.1745 The test is significant at 0.1732 (adjusted for ties) Issue O Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 10.00 2.00 Point estimate for ETA1-ETA2 is 4.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,25.00) W = 35.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.1437 Issue P Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 10.00 7.00 Point estimate for ETA1-ETA2 is 4.00 96.3 Percent CI for ETA1-ETA2 is (-2.00,17.00) W = 34.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.1745 The test is significant at 0.1666 (adjusted for ties) 115 Issue Q Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 7.00 3.00 Point estimate for ETA1-ETA2 is 4.00 96.3 Percent CI for ETA1-ETA2 is (-11.00,30.99) W = 30.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6742 (adjusted for ties) Issue R Mann-Whitney Test and CI: Meeting Attendees, Public Meeting Attendee Public N 5 5 Median 11.00 7.00 Point estimate for ETA1-ETA2 is 4.00 96.3 Percent CI for ETA1-ETA2 is (-2.00,21.00) W = 33.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2963 The test is significant at 0.2843 (adjusted for ties) 116 Results for: Question A-2 Pre-Meeting Respondents vs. Post-Meeting Respondents Issue A Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 3.00 5.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,9.00) W = 25.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6752 (adjusted for ties) Issue B Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 4.00 Point estimate for ETA1-ETA2 is 0.00 96.3 Percent CI for ETA1-ETA2 is (-16.00,10.01) W = 27.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 1.0000 The test is significant at 1.0000 (adjusted for ties) Issue C Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 3.00 9.00 Point estimate for ETA1-ETA2 is -0.00 96.3 Percent CI for ETA1-ETA2 is (-13.99,9.00) W = 26.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.9168 The test is significant at 0.9155 (adjusted for ties) Issue D Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 3.00 8.00 117 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,10.00) W = 25.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.7540 The test is significant at 0.7533 (adjusted for ties) Issue E Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 7.00 5.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-12.99,8.00) W = 26.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.8345 Issue F Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 6.00 7.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,6.00) W = 25.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.7540 The test is significant at 0.7503 (adjusted for ties) Issue G Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 5.00 8.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-12.00,7.00) W = 25.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.7540 The test is significant at 0.7503 (adjusted for ties) 118 Issue H Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 8.00 9.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,8.00) W = 24.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.5309 The test is significant at 0.5258 (adjusted for ties) Issue I Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 6.00 5.00 Point estimate for ETA1-ETA2 is 1.00 96.3 Percent CI for ETA1-ETA2 is (-18.00,7.00) W = 29.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.8345 The test is significant at 0.8330 (adjusted for ties) Issue J Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 4.00 Point estimate for ETA1-ETA2 is -0.00 96.3 Percent CI for ETA1-ETA2 is (-20.00,10.00) W = 27.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 1.0000 The test is significant at 1.0000 (adjusted for ties) Issue K Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 5.00 4.00 Point estimate for ETA1-ETA2 is 1.00 96.3 Percent CI for ETA1-ETA2 is (-15.00,10.00) W = 28.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 1.0000 The test is significant at 1.0000 (adjusted for ties) 119 Issue L Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 6.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-16.00,7.00) W = 27.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 1.0000 The test is significant at 1.0000 (adjusted for ties) Issue M Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 6.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,6.00) W = 25.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6723 (adjusted for ties) Issue N Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 3.00 9.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,6.00) W = 23.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4647 The test is significant at 0.4578 (adjusted for ties) Issue O Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 9.00 Point estimate for ETA1-ETA2 is -0.00 96.3 Percent CI for ETA1-ETA2 is (-11.01,9.00) W = 27.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 1.0000 The test is significant at 1.0000 (adjusted for ties) 120 Issue P Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 4.00 9.00 Point estimate for ETA1-ETA2 is -3.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,7.00) W = 24.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6015 The test is significant at 0.6004 (adjusted for ties) Issue Q Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 2.00 5.00 Point estimate for ETA1-ETA2 is -0.00 96.3 Percent CI for ETA1-ETA2 is (-17.01,10.00) W = 26.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.9168 The test is significant at 0.9153 (adjusted for ties) Issue R Mann-Whitney Test and CI: Pre-Meeting Respondent, Post-Meeting Respondent Pre-Meeting Post-Meeting N 5 5 Median 6.00 5.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-10.00,7.00) W = 25.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6733 (adjusted for ties) Appendix D Chi-Square Test for question A-3 121 122 Chi-Square for Question A-3 Meeting Attendees vs. Public Row variable Attend Non Total Observed Frequencies Column variable Good Fair Poor 12 39 30 8 22 14 20 61 44 Total 81 44 125 Row variable Attend Non Total Expected Frequencies Column variable Good Fair Poor 12.96 39.528 28.512 7.04 21.472 15.488 20 61 44 Total 81 44 125 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 2 Calculations fo-fe 3 -0.96 -0.528 1.488 2 0.96 0.528 -1.488 0.007053 0.012984 0.077657 0.142959 Results Critical Value 5.9915 Chi-Square Test Statistic 0.4427 p-Value 0.8014 Do not reject the null hypothesis Expected frequency assumption is met. (fo-fe)^2/fe 0.071111 0.130909 123 Chi-Square for Question A-3 Pre-Meeting Respondents vs. Post-Meeting Respondents Row variable Observed Frequencies Column variable Good Fair Poor Pre 9 21 11 Post 3 18 19 Total 12 39 30 Total 41 40 81 Expected Frequencies Column variable Good Fair Poor Pre 6.074074 19.74074 15.18519 Post 5.925926 19.25926 14.81481 Total 12 39 30 Total 41 40 81 Calculations fo-fe 2.925926 -2.92593 1.259259 -1.25926 -4.18519 4.185185 (fo-fe)^2/fe 1.40944 1.444676 0.080328 0.082336 1.153478 1.182315 Row variable Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 2 3 2 Results Critical Value 5.9915 Chi-Square Test Statistic 5.3526 p-Value 0.0688 Do not reject the null hypothesis Expected frequency assumption is met. Appendix E Mann-Whitney U Test for question A-4 124 125 Results for: Question A-4 Meeting Attendees vs. the Public 1.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 5.00 2.00 Point estimate for ETA1-ETA2 is 2.00 96.3 Percent CI for ETA1-ETA2 is (-15.99,36.01) W = 30.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6015 The test is significant at 0.5888 (adjusted for ties) 2.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 7.00 2.00 Point estimate for ETA1-ETA2 is 5.00 96.3 Percent CI for ETA1-ETA2 is (-9.99,31.00) W = 29.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.8345 The test is significant at 0.8325 (adjusted for ties) 3.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 20.00 8.00 Point estimate for ETA1-ETA2 is 11.00 96.3 Percent CI for ETA1-ETA2 is (-8.00,20.01) W = 32.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.3472 The test is significant at 0.3443 (adjusted for ties) 4.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 16.00 4.00 Point estimate for ETA1-ETA2 is 8.00 96.3 Percent CI for ETA1-ETA2 is (-6.00,27.00) W = 33.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.2506 The test is significant at 0.2492 (adjusted for ties) 126 5.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 4.00 8.00 Point estimate for ETA1-ETA2 is -4.00 96.3 Percent CI for ETA1-ETA2 is (-27.00,7.00) W = 22.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.3472 The test is significant at 0.3443 (adjusted for ties) 6.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 8.00 5.00 Point estimate for ETA1-ETA2 is 3.00 96.3 Percent CI for ETA1-ETA2 is (-7.00,32.00) W = 30.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6015 The test is significant at 0.5982 (adjusted for ties) 7.) Mann-Whitney Test and CI: Meeting Attendee, Public Meeting Attendee Public N 5 5 Median 15.00 2.00 Point estimate for ETA1-ETA2 is 8.00 96.3 Percent CI for ETA1-ETA2 is (-11.01,27.00) W = 31.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4647 The test is significant at 0.4506 (adjusted for ties) 127 Results for: Question A-4 Pre-Meeting Respondent vs. Post-Meeting Respondents 1.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 2.00 3.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-19.00,13.99) W = 24.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.5309 The test is significant at 0.5284 (adjusted for ties) 2.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 3.00 4.00 Point estimate for ETA1-ETA2 is -1.00 96.3 Percent CI for ETA1-ETA2 is (-16.00,11.01) W = 24.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.5309 The test is significant at 0.5258 (adjusted for ties) 3.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 8.00 10.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-12.00,8.00) W = 23.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.4034 The test is significant at 0.3917 (adjusted for ties) 4.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 5.00 11.00 Point estimate for ETA1-ETA2 is -6.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,6.01) W = 22.5 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.3472 The test is significant at 0.3428 (adjusted for ties) 128 5.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 2.00 6.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,11.00) W = 25.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.6761 The test is significant at 0.6723 (adjusted for ties) 6.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 3.00 5.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-16.00,16.00) W = 24.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.5309 The test is significant at 0.5284 (adjusted for ties) 7.) Mann-Whitney Test and CI: Pre-Meeting, Post-Meeting Pre-Meeting Post-Meeting N 5 5 Median 5.00 8.00 Point estimate for ETA1-ETA2 is -2.00 96.3 Percent CI for ETA1-ETA2 is (-14.00,6.99) W = 24.0 Test of ETA1 = ETA2 vs ETA1 not = ETA2 is significant at 0.5309 The test is significant at 0.5258 (adjusted for ties) Appendix F Respondent’s rankings for question A-5 129 130 Question A-5 Pre-Meeting Respondents Rank Federal Gov. State Gov. County Gov. Local Munic Local Landownders Industry/ Business Enviro Groups Farm Groups Educators 1 0.0 46.4 14.3 17.9 14.3 3.8 3.6 3.8 3.6 2 17.9 14.3 35.7 14.3 3.6 11.5 0.0 3.8 7.1 3 7.1 7.1 25.0 28.6 7.1 3.8 10.7 3.8 3.6 4 21.4 10.7 7.1 14.3 21.4 15.4 3.6 11.5 3.6 5 7.1 7.1 3.6 7.1 14.3 11.5 28.6 11.5 7.1 6 10.7 0.0 3.6 3.6 10.7 19.2 25.0 7.7 10.7 7 0.0 0.0 3.6 14.3 17.9 11.5 14.3 34.6 0.0 8 10.7 3.6 3.6 0.0 7.1 3.8 10.7 19.2 25.0 9 17.9 3.6 0.0 0.0 0.0 19.2 0.0 3.8 35.7 Farm Groups 6.1 3.0 15.2 3.0 12.1 12.1 27.3 21.2 0.0 Educators 3.0 0.0 6.1 6.1 3.0 9.1 12.1 9.1 45.5 Farm Groups 14.3 10.7 7.1 7.1 7.1 17.9 17.9 14.3 0.0 Educators 3.7 3.7 11.1 0.0 0.0 3.7 3.7 25.9 40.7 * Highlighted Box is the highest percentage of respondents for the corresponding rank Question A-5 Post-Meeting Respondents Rank 1 2 3 4 5 6 7 8 9 Federal Gov. 14.3 0.0 2.9 20.0 0.0 11.4 5.7 14.3 28.6 State Gov. 37.8 13.5 8.1 0.0 10.8 13.5 2.7 13.5 0.0 County Gov. 15.8 36.8 21.1 2.6 10.5 2.6 7.9 0.0 2.6 Local Munic. 16.2 18.9 29.7 27.0 0.0 5.4 0.0 0.0 0.0 Local Landownders 21.2 12.1 12.1 12.1 12.1 12.1 6.1 9.1 3.0 Industry/ Business 2.9 11.4 8.6 17.1 25.7 11.4 14.3 5.7 0.0 Enviro Groups 8.8 0.0 5.9 8.8 14.7 17.6 14.7 14.7 11.8 * Highlighted Box is the highest percentage of respondents for the corresponding rank Question A-5 Public Respondents Rank 1 2 3 4 5 6 7 8 9 Federal Gov. 11.1 7.4 18.5 3.7 3.7 14.8 11.1 3.7 18.5 State Gov. 30.8 7.7 15.4 7.7 19.2 7.7 3.8 3.8 3.8 County Gov. 10.7 17.9 14.3 25.0 14.3 7.1 3.6 7.1 0.0 Local Munic. 31.0 6.9 13.8 10.3 10.3 6.9 17.2 0.0 3.4 Local Landownders 17.2 31.0 13.8 13.8 10.3 10.3 0.0 3.4 0.0 Industry/ Business 6.9 10.3 3.4 17.2 6.9 13.8 17.2 20.7 3.4 Enviro Groups 0.0 17.9 10.7 0.0 21.4 7.1 14.3 14.3 3.6 * Highlighted Box is the highest percentage of respondents for the corresponding rank Appendix G Respondent’s rankings for question A-6 131 132 Question A-6 Pre-Meeting Respondents Rank Federal Gov. State Gov. County Gov. Local Munic Local Landownders Industry/ Business Enviro Groups Farm Groups Educators 1 0.0 37.5 21.7 34.8 13.6 4.3 4.3 4.3 4.2 2 8.7 8.3 47.8 13.0 0.0 8.7 0.0 4.3 4.2 3 4.3 29.2 13.0 30.4 13.6 0.0 0.0 4.3 0.0 4 39.1 8.3 8.7 4.3 13.6 4.3 8.7 8.7 0.0 5 8.7 8.3 4.3 8.7 18.2 21.7 34.8 0.0 0.0 6 8.7 0.0 4.3 4.3 13.6 21.7 17.4 8.7 16.7 7 0.0 4.2 0.0 4.3 18.2 13.0 21.7 30.4 4.2 8 8.7 4.2 0.0 0.0 4.5 17.4 13.0 30.4 16.7 9 21.7 0.0 0.0 0.0 4.5 8.7 0.0 8.7 50.0 Farm Group s 6.5 6.5 16.1 9.7 12.9 19.4 12.9 12.9 3.2 Educators 3.1 0.0 3.1 6.3 3.1 15.6 6.3 15.6 43.8 * Highlighted Box is the highest percentage of respondents for the corresponding rank Question A-6 Post-Meeting Respondents Rank 1 2 3 4 5 6 7 8 9 Federal Gov. 3.2 0.0 3.2 22.6 0.0 9.7 16.1 16.1 25.8 State Gov. 20.0 11.4 17.1 0.0 17.1 8.6 11.4 14.3 0.0 County Gov. 25.7 31.4 11.4 2.9 5.7 8.6 8.6 0.0 2.9 Local Munic 33.3 19.4 22.2 13.9 2.8 2.8 2.8 0.0 0.0 Local Landownders 20.6 17.6 14.7 11.8 5.9 14.7 11.8 2.9 0.0 Industry/ Business 6.1 12.1 18.2 18.2 24.2 6.1 9.1 6.1 0.0 Enviro Groups 9.1 0.0 6.1 6.1 18.2 9.1 12.1 24.2 12.1 * Highlighted Box is the highest percentage of respondents for the corresponding rank Question A-6 Public Respondents Rank 1 2 3 4 5 6 7 8 9 Federal Gov. 7.4 7.4 7.4 7.4 18.5 7.4 14.8 0.0 14.8 State Gov. 25.0 7.1 14.3 10.7 14.3 7.1 0.0 10.7 10.7 County Gov. 14.3 28.6 21.4 7.1 3.6 7.1 7.1 10.7 0.0 Local Munic 28.6 14.3 7.1 10.7 14.3 10.7 7.1 0.0 7.1 Local Landownders 24.1 17.2 24.1 3.4 13.8 3.4 6.9 3.4 3.4 Industry/ Business 6.9 13.8 10.3 6.9 10.3 17.2 6.9 27.6 0.0 Enviro Groups 3.4 10.3 0.0 27.6 10.3 6.9 13.8 17.2 10.3 Farm Group s 11.1 11.1 7.4 7.4 3.7 22.2 18.5 11.1 3.7 * Highlighted Box is the highest percentage of respondents for the corresponding rank Educators 0.0 0.0 7.4 11.1 3.7 11.1 7.4 18.5 37.0 Appendix H Chi-Square Test for question B-3 133 134 Chi-Square for Question B-3 Meeting Attendee vs. Public Observed Frequencies Column variable Row variable 0-5 5-10 10-15 Meeting Attendee 48 12 3 Public 25 4 0 Total 73 16 3 Total 63 29 92 Expected Frequencies Column variable Row variable 0-5 5-10 10-15 Meeting Attendee 49.98913 10.95652 2.054348 Public 23.01087 5.043478 0.945652 Total 73 16 3 Total 63 29 92 Calculations fo-fe -1.98913 1.98913 1.043478 -1.04348 0.945652 -0.94565 (fo-fe)^2/fe 0.07915 0.171947 0.099379 0.215892 0.4353 0.945652 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 2 3 2 Results Critical Value 5.9915 Chi-Square Test Statistic 1.9473 p-Value 0.3777 Do not reject the null hypothesis 135 Chi-Square for Question B-3 Pre-Meeting Respondents vs. Post-Meeting Respondents Row variable Observed Frequencies Column variable 0-5 5-10 10-15 Pre 17 7 post 31 5 Total 48 12 Row variable Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 3 0 3 Total 27 36 63 Expected Frequencies Column variable 0-5 5-10 10-15 Pre 20.57143 5.142857 1.285714 post 27.42857 6.857143 1.714286 Total 48 12 3 Total 27 36 63 0.05 2 3 2 Calculations fo-fe -3.57143 3.571429 1.857143 -1.85714 1.714286 -1.71429 (fo-fe)^2/fe 0.62004 0.46503 0.670635 0.502976 2.285714 1.714286 Results Critical Value 5.9915 Chi-Square Test Statistic 6.2587 p-Value 0.0437 Reject the null hypothesis Appendix I Chi-Square Test for question B-4 136 137 Chi-Square for Question B-4 Meeting Attendee vs. Public Row variable attend Non Total Observed Frequencies Column variable 1 2 3 4 15 24 10 0 14 20 6 2 29 44 16 2 Row variable attend Non Total Expected Frequencies Column variable 1 2 3 4 16.27551 24.69388 8.979592 1.122449 12.72449 19.30612 7.020408 0.877551 29 44 16 2 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 3 0 3 6 3 1 4 Total 55 43 98 5 1.683673 1.316327 3 6 2.244898 1.755102 4 Total 55 43 98 Calculations fo-fe 0.05 fo-fe 2 -1.27551 -0.69388 1.020408 -1.12245 1.316327 0.755102 6 1.27551 0.693878 -1.02041 1.122449 -1.31633 -0.7551 (fo-fe)^2/fe 0.019497 0.115955 1.122449 1.029128 0.253989 1.435691 1.316327 0.324869 5 Results Critical Value 11.0705 Chi-Square Test Statistic 6.0190 p-Value 0.3044 Do not reject the null hypothesis Expected frequency assumption is met. 5 0.099962 0.127858 0.024939 0.148315 138 Chi-Square for Question B-4 Pre-Meeting Respondent vs. Post-Meeting Respondent Row variable Pre Post Total Row variable Pre Post Total Data Level of Significance Number of Rows Number of Columns Degrees of Freedom Observed Frequencies Column variable 1 2 3 7 14 7 10 14 7 17 28 14 5 1 1 2 6 3 2 5 Total 32 34 66 Expected Frequencies Column variable 1 2 3 5 8.242424 13.57576 6.787879 0.969697 8.757576 14.42424 7.212121 1.030303 17 28 14 2 6 2.424242 2.575758 5 Total 32 34 66 Calculations 0.05 2 fo-fe -1.24242 0.424242 0.212121 0.030303 0.575758 6 1.242424 -0.42424 -0.21212 -0.0303 -0.57576 (fofe)^2/fe 0.187277 0.013258 0.006629 0.000947 0.136742 0.176261 0.012478 0.006239 0.000891 0.128699 5 Results Critical Value 11.0705 Chi-Square Test Statistic 0.6694 p-Value 0.9846 Do not reject the null hypothesis Appendix J Spearman-Rank Correlation Test for willingness to donate and willingness to participate 139 140 X (Willingness to Donate) Y (Willingness to Participate) X rank y rank x rank-y rank Dif of ranks^2 3 50 2 48 2 4 1 1 3 60 -59 3481 1 1 1 1 0 0 2 22 2 48 -26 676 2 22 2 48 -26 676 3 50 2 48 2 4 2 22 4 63 -41 1681 3 50 1 1 49 2401 2 22 2 48 -26 676 2 22 1 1 21 441 1 1 1 1 0 0 1 1 1 1 0 0 0 1 1 1 1 0 5 58 3 60 -2 4 2 22 1 1 21 441 2 22 2 48 -26 676 2 22 1 1 21 441 2 22 1 1 21 441 1 1 1 1 0 0 2 22 1 1 21 441 1 1 1 1 0 0 1 1 1 1 0 0 1 1 1 1 0 0 1 1 1 1 0 0 6 60 1 1 59 3481 1 1 1 1 0 0 1 1 1 1 0 0 1 1 1 1 0 0 1 1 1 1 0 0 2 22 2 48 -26 676 2 22 1 1 21 441 2 22 1 1 21 441 2 22 1 1 21 441 5 58 1 1 57 3249 3 50 1 1 49 2401 2 22 1 1 21 441 6 60 2 48 12 144 1 1 1 1 0 0 2 22 1 1 21 441 2 22 2 48 -26 676 1 1 2 48 -47 2209 1 1 1 1 0 0 2 22 1 1 21 441 2 22 2 48 -26 676 2 22 1 1 21 441 141 2 22 1 1 21 441 1 1 1 1 0 0 3 50 2 48 2 4 2 22 1 1 21 441 3 50 1 1 49 2401 2 22 1 1 21 441 2 22 1 1 21 441 2 22 1 1 21 441 6 60 3 60 0 0 4 57 1 1 56 3136 2 22 1 1 21 441 6 60 1 1 59 3481 2 22 1 1 21 441 1 1 1 1 0 0 2 22 1 1 21 441 1 1 1 1 0 0 1 1 1 1 0 0 3 50 1 1 49 2401 Sum 44034 r= -0.056883641 Appendix K Spearman-Rank Correlation Test for respondent income and willingness to participate 142 143 X (Income) Y (Willingness to participate) X rank 1 1 1 1 1 2 1 1 1 2 1 1 1 4 1 1 1 1 0 5 4 5 5 4 5 4 5 4 3 4 5 3 3 5 5 3 2 2 1 1 1 1 1 1 3 2 2 2 2 2 23 2 2 2 23 2 2 2 42 2 2 2 2 1 51 42 51 51 42 51 42 51 42 28 42 51 28 28 51 51 28 23 23 2 2 2 2 2 2 28 x rank-y rank y rank 2 3 1 2 2 2 4 1 2 1 1 1 1 3 1 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 1 1 1 2 1 2 2 1 2 1 1 1 44 56 1 44 44 44 59 1 44 1 1 1 1 56 1 44 1 1 1 1 1 1 1 1 1 1 1 1 1 1 44 1 1 1 1 1 44 1 44 44 1 44 1 1 1 -42 -54 1 -42 -42 -21 -57 1 -42 22 1 1 1 -14 1 -42 1 1 0 50 41 50 50 41 50 41 50 41 27 41 7 27 27 50 50 27 -21 22 -42 -42 1 -42 1 1 27 Dif of ranks^2 1764 2916 1 1764 1764 441 3249 1 1764 484 1 1 1 196 1 1764 1 1 0 2500 1681 2500 2500 1681 2500 1681 2500 1681 729 1681 49 729 729 2500 2500 729 441 484 1764 1764 1 1764 1 1 729 144 3 2 3 3 4 3 3 3 4 3 3 4 3 5 28 23 28 28 42 28 28 28 42 28 28 42 28 51 2 1 1 1 1 1 3 1 1 1 1 1 1 1 44 1 1 1 1 1 56 1 1 1 1 1 1 1 r= -16 22 27 27 41 27 -28 27 41 27 27 41 27 50 Sum 256 484 729 729 1681 729 784 729 1681 729 729 1681 729 2500 66103 0.931706604 (Excel Equation) Appendix L Spearman-Rank Correlation Test for respondent age and willingness to participate 145 146 X (Age) X rank 2 2 2 2 2 2 2 2 2 2 2 2 2 5 2 2 2 2 5 4 3 4 2 4 5 4 4 2 4 4 5 3 4 5 5 5 4 2 2 4 2 3 2 2 2 1 1 1 1 1 1 1 1 1 1 1 1 1 56 1 1 1 1 56 34 29 34 1 34 56 34 34 1 34 34 56 29 34 56 56 56 34 1 1 34 1 29 1 1 1 Y (Willingness to participate) 2 3 1 2 2 2 4 1 2 1 1 1 1 3 1 2 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 1 1 1 1 2 1 1 2 2 1 1 2 y rank 49 61 1 49 49 49 64 1 49 1 1 1 1 61 1 49 1 1 1 1 1 1 1 1 1 1 1 1 1 1 49 1 1 1 1 1 1 49 1 1 49 49 1 1 49 x rank-y rank -48 -60 0 -48 -48 -48 -63 0 -48 0 0 0 0 -5 0 -48 0 0 55 33 28 33 0 33 55 33 33 0 33 33 7 28 33 55 55 55 33 -48 0 33 -48 -20 0 0 -48 Dif of ranks^2 2304 3600 0 2304 2304 2304 3969 0 2304 0 0 0 0 25 0 2304 0 0 3025 1089 784 1089 0 1089 3025 1089 1089 0 1089 1089 49 784 1089 3025 3025 3025 1089 2304 0 1089 2304 400 0 0 2304 147 2 2 4 4 4 3 2 4 3 4 4 4 4 4 4 4 5 4 5 1 1 34 34 34 29 1 34 29 34 34 34 34 34 34 34 56 34 56 1 1 1 2 1 1 1 1 1 3 1 1 1 1 1 1 1 1 1 1 1 1 49 1 1 1 1 1 61 1 1 1 1 1 1 1 1 1 0 0 33 -15 33 28 0 33 28 -27 33 33 33 33 33 33 55 33 55 Sum r= 0 0 1089 225 1089 784 0 1089 784 729 1089 1089 1089 1089 1089 1089 3025 1089 3025 75824 -0.735897436 Appendix M Spearman-Rank Correlation Test for respondent residence and willingness to participate 148 149 X (Residence) 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 3 1 3 3 4 3 4 6 4 3 1 6 1 3 4 2 3 4 3 3 1 5 3 1 3 5 3 3 1 X rank 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 10 1 10 10 42 10 42 53 42 10 1 53 1 10 42 7 10 42 10 10 1 51 10 1 10 51 10 10 1 Y (Willingness to participate) 2 3 1 2 2 1 1 1 1 1 3 1 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 1 1 1 2 1 1 2 2 1 2 1 1 1 2 1 1 y rank 43 52 1 43 43 1 1 1 1 1 52 1 1 1 1 1 1 1 1 1 1 1 1 1 1 43 1 1 1 1 1 43 1 1 43 43 1 43 1 1 1 43 1 1 x rank-y rank -33 -42 9 -33 -33 9 9 9 9 9 -42 9 9 9 9 9 0 9 9 41 9 41 52 41 9 -42 52 0 9 41 6 -33 41 9 -33 -42 50 -33 0 9 50 -33 9 0 Dif of ranks^2 1089 1764 81 1089 1089 81 81 81 81 81 1764 81 81 81 81 81 0 81 81 1681 81 1681 2704 1681 81 1764 2704 0 81 1681 36 1089 1681 81 1089 1764 2500 1089 0 81 2500 1089 81 0 150 4 3 4 3 3 2 4 3 4 2 42 10 42 10 10 7 42 10 42 7 1 3 1 1 1 1 1 1 1 1 1 52 1 1 1 1 1 1 1 1 41 -42 41 9 9 6 41 9 41 6 Sum 1681 1764 1681 81 81 36 1681 81 1681 36 43870 r= -0.672193634 Appendix N Spearman-Rank Correlation Test for respondent education and willingness to participate 151 152 X (Education) 18 14 18 18 12 17 14 18 17 18 16 18 18 17 26 14 15 15 16 16 16 15 16 16 19 20 16 18 21 12 19 16 16 16 17 16 20 17 16 18 20 16 16 X rank 45 8 45 45 1 40 8 45 40 45 21 45 45 40 61 8 13 13 21 21 21 13 21 21 55 57 21 45 60 1 55 21 21 21 40 21 57 40 21 45 57 21 21 Y (Willingness to participate) y rank 1 1 1 1 1 1 1 2 1 1 1 1 1 3 1 2 1 1 2 2 1 1 2 1 1 1 1 1 1 1 1 1 1 1 1 1 2 1 1 1 1 1 1 1 1 1 1 1 1 1 46 1 1 1 1 1 58 1 46 1 1 46 46 1 1 46 1 1 1 1 1 1 1 1 1 1 1 1 1 46 1 1 1 1 1 1 x rank-y rank 44 7 44 44 0 39 7 -1 39 44 20 44 44 -18 60 -38 12 12 -25 -25 20 12 -25 20 54 56 20 44 59 0 54 20 20 20 39 20 11 39 20 44 56 20 20 Dif of ranks^2 1936 49 1936 1936 0 1521 49 1 1521 1936 400 1936 1936 324 3600 1444 144 144 625 625 400 144 625 400 2916 3136 400 1936 3481 0 2916 400 400 400 1521 400 121 1521 400 1936 3136 400 400 153 18 13.5 12 15 16 15 13 15 12 14 16 12 15.5 14 16 15 16 16 45 7 1 13 21 13 6 13 1 8 21 1 20 8 21 13 21 21 3 1 2 1 1 2 3 1 2 2 2 4 1 2 1 1 1 1 58 1 46 1 1 46 58 1 46 46 46 61 1 46 1 1 1 1 -13 6 -45 12 20 -33 -52 12 -45 -38 -25 -60 19 -38 20 12 20 20 Sum r= 169 36 2025 144 400 1089 2704 144 2025 1444 625 3600 361 1444 400 144 400 400 67006 -0.771708091 Appendix O Spearman-Rank Correlation Test for respondent income and willingness to donate 154 155 X (Income) 4 3 1 3 1 1 1 1 1 2 1 1 1 2 1 1 1 4 1 1 1 1 5 4 5 4 5 4 5 4 3 4 5 3 3 5 5 3 2 2 1 1 1 1 1 X rank 64 41 1 41 1 1 1 1 1 34 1 1 1 34 1 1 1 64 1 1 1 1 76 64 76 64 76 64 76 64 41 64 76 41 41 76 76 41 34 34 1 1 1 1 1 Y (Willingness to donate) 2 2 1 2 3 1 1 2 2 3 2 3 2 2 1 1 1 5 2 2 2 2 2 1 1 1 1 6 1 1 1 1 2 2 2 2 5 3 6 1 2 1 1 2 2 y rank 36 36 1 36 73 1 1 36 36 73 36 73 36 36 1 1 1 79 36 36 36 36 36 1 1 1 1 81 1 1 1 1 36 36 36 36 79 73 81 1 36 1 1 36 36 x rank-y rank Dif of ranks^2 28 5 0 5 -72 0 0 -35 -35 -39 -35 -72 -35 -2 0 0 0 -15 -35 -35 -35 -35 40 63 75 63 75 -17 75 63 40 63 40 5 5 40 -3 -32 -47 33 -35 0 0 -35 -35 784 25 0 25 5184 0 0 1225 1225 1521 1225 5184 1225 4 0 0 0 225 1225 1225 1225 1225 1600 3969 5625 3969 5625 289 5625 3969 1600 3969 1600 25 25 1600 9 1024 2209 1089 1225 0 0 1225 1225 156 1 3 3 2 3 3 4 3 3 3 4 3 3 4 5 5 4 1 1 2 1 1 1 1 1 2 3 1 3 3 3 1 3 3 4 3 1 1 3 1 41 41 34 41 41 64 41 41 41 64 41 41 64 76 76 64 1 1 34 1 1 1 1 1 34 41 1 41 41 41 1 41 41 64 41 1 1 41 2 1 3 2 3 2 2 2 6 2 6 2 1 2 2 1 2 1 1 1 2 2 1 1 2 1 1 1 2 2 1 1 1 2 1 2 1 1 1 36 1 73 36 73 36 36 36 81 36 81 36 1 36 36 1 36 1 1 1 36 36 1 1 36 1 1 1 36 36 1 1 1 36 1 36 1 1 1 -35 40 -32 -2 -32 5 28 5 -40 5 -17 5 40 28 40 75 28 0 0 33 -35 -35 0 0 -35 33 40 0 5 5 40 0 40 5 63 5 0 0 40 Sum 1225 1600 1024 4 1024 25 784 25 1600 25 289 25 1600 784 1600 5625 784 0 0 1089 1225 1225 0 0 1225 1089 1600 0 25 25 1600 0 1600 25 3969 25 0 0 1600 104613 r 0.059157639 Appendix P Chi-Square Test for revised question A-3 157 158 Chi-Square for Revised Question A-3 Pre-Meeting Respondents vs. Post-Meeting Respondents Observed Frequencies Column variable Row variable Good Poor Pre 30 11 Post 21 19 Total 51 30 Total 41 40 81 Expected Frequencies Column variable Row variable Good Poor Pre 25.81481 15.18519 Post 25.18519 14.81481 Total 51 30 Total 41 40 81 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 2 2 1 Results Critical Value 3.8415 Chi-Square Test Statistic 3.7098 p-Value 0.0541 Do not reject the null hypothesis Expected frequency assumption is met. Calculations fo-fe 4.185185 -4.18519 -4.18519 4.185185 (fo-fe)^2/fe 0.678516 1.153478 0.695479 1.182315 159 Chi-Square for Revised Question A-3 Meeting Attendee vs. Public Observed Frequencies Calculations Column variable fo-fe Row variable Good Poor Total Attend 51 30 81 -2.77869 2.778689 Non 30 11 41 2.778689 -2.77869 Total 81 41 122 Expected Frequencies Column variable Row variable Good Poor Total Attend 53.77869 27.22131 81 Non 27.22131 13.77869 41 Total 81 41 122 Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 2 2 1 Results Critical Value 3.8415 Chi-Square Test Statistic 1.2712 p-Value 0.2595 Do not reject the null hypothesis Expected frequency assumption is met. (fo-fe)^2/fe 0.143572 0.283642 0.283642 0.560366 Appendix Q Chi-Square Test for revised question B-3 160 161 Chi-Square for Revised Question B-3 Pre-Meeting Respondents vs. The Public Observed Frequencies Column variable Row variable 0 1 5-Feb Random 2 6 4 Pre 1 3 9 Total 3 9 13 10-May 2 1 3 Total 14 14 28 Expected Frequencies Column variable 0 1 39483 1.5 4.5 6.5 1.5 4.5 6.5 3 9 13 39578 1.5 1.5 3 Total 14 14 28 1.5 -1.5 -2.5 2.5 0.5 -0.5 0.5 0.5 0.961538 0.961538 0.166667 0.166667 Row variable Random Pre Total Data Level of Significance Number of Rows Number of Columns Degrees of Freedom 0.05 3 4 6 Calculations fo-fe 0.5 -0.5 Results Critical Value 12.5916 Chi-Square Test Statistic 3.2564 p-Value 0.7760 Do not reject the null hypothesis Expected frequency assumption is met. (fofe)^2/fe 0 0