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LIBRARY 3; Michigan State ° 7 University This is to certify that the dissertation entitled Environmental Equity of Lansing’s Urban Park Policy presented by Sissi Patricia Bruch has been accepted towards fulfillment of the requirements for the Ph.D. degree in Geography fi/ZMM Major Professor’s Signature 6- l «9k. Date MSU is an Aflinnative Action/Equal Opportunity Institution » ..-—---o-.-.-----.-.--n--.--o--n-.-.-o-.-.-o—.-o-v-n-—a---.--.-.--o----.-----u----.-.— — PLACE IN RETURN BOX to remove this checkout from your record. TO AVOID FINES return on or before date due. MAY BE RECALLED with earlier due date if requested. DATE DUE DATE DUE DATE DUE f.- ‘3 73.79 .... 1 1 '7“. M'Yl‘ffitl u? L‘ ‘95? ‘1‘ 3 Nov 12 2001.5 2/05 p:/C|RC/Date0ue.indd-p.1 ENVIRONMENTAL EQUITY OF LANSING’S URBAN PARK POLICY By Sissi Patricia Bruch A DISSERTATION Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Department of Geography 2006 ABSTRACT Studies evaluating the quantity of social and economic benefits gained by the residents who live near urban parks find that a positive correlation exists between participation and residential proximity to parks (Page, Nielsen, & Goodenough, 1994). Because of the inherent uneven distribution of benefits experienced due to spatial distance, park master plan policies should be explored from an environmental justice perspective. This research looks at both the populations that are found in the surrounding area around neighborhood parks in the City of Lansing, Michigan and the asset expenditures for these parks. This study focused on the 5 minute walk area surrounding neighborhood parks (catchment areas). The populations that were found in these areas were analyzed and the assets in the parks were quantified. The population groups that were analyzed were Whites, Blacks, Hispanics, Above Poverty, and Below Poverty. The park assets were evaluated based on current replacement costs of only the man-made elements found in the parks. New methodology for environmental justice studies were used to get more accurate density calculations. These methods encompassed the subtraction of non-residential areas from the census data and the recalculation of densities based on the remaining acreage. The results showed a slight indication that Lansing’s neighborhood parks currently have fewer minority and the poverty populations within the study catchment areas as compared to the city wide population averages. Also, the parks that have a higher proportion of minority and poverty populations in their catchment areas show fewer dollars spent on assets. When evaluating the park master plan for Lansing, it was apparent that there were no specific procedures in place to address either of these groups (minority and poverty populations). The recommendations of this research were for both the State and the local government to require that both the minority and poverty population groups be included and planned for within the master planning process. Future studies looking at the relationships between people’s health and their life styles in comparison to where they choose to live would give greater knowledge to planners as they make decisions regarding these public resources. ACKNOWLEDGEMENTS I would like to extend my sincerest thanks to Dr. Rex LaMore for his guidance, continual support, patience, and advice, all crucial in the completion of this document. My gratitude also goes to my committee members, Dr. Eric Strauss, Dr. David Lusch, and Dr. Jay Harman, for all their time, advice, and effort on my behalf. Mr. J emerson from the Parks and Recreation Department and Dr. Sarah Nicholls from MSU were instrumental in supplying much of the data and information for this study. My colleagues and friends that helped me through the last two years deserve many thanks for all the help and support I needed with this document. Their continual encouragement and understanding was immeasurable for its completion. My final and most heartfelt acknowledgement goes to my whole family, my dear friend Carol Graysmith Laws, and my partner Robert Anthony Welch for supporting and encouraging me through out this long process. I would not have been able to do this without them and I owe them an irreplaceable debt. This dissertation is dedicated to my children Christopher and Hans who sacrificed much and helped me get through this degree. iv ENVIRONMENTAL EQUITY OF LANSING’S URBAN PARK POLICY TABLE OF CONTENTS List of Tables ............................................................................... vii List of Figures ............................................................................... ix CHAPTER 1 - INTRODUCTION Background ......................................................................... 1 Statement of Problem ............................................................. 3 Hypotheses ........................................................................ 4 Organization of Study ............................................................. 5 Summary ............................................................................ 6 CHAPTER 2 — PARKS Urban Parks ........................................................................ 8 Social Impacts of Parks .................................................. 9 Economic Impacts of Parks .............................................. 11 Health Impacts of Parks ................................................... 14 Environmental Impacts or Parks ....................................... 15 Summary ........................................................................... 16 CHAPTER 3 - URBAN PLANNING AND ENVIRONMENTAL JUSTICE REVIEW Introduction ........................................................................ 17 Urban Flaming .................................................................... 17 Goals and Objectives of Planning ..................................... 18 Urban Planning Theories ................................................ 22 Summary .................................................................. 34 Introduction to Equity and Environmental Justice ........................... 35 Equity .............................................................................. 36 Environmental Justice Studies .................................................. 38 Justice Theories .................................................................... 40 Summary ............................................................................ 48 Locational Theories ............................................................... 48 Conclusions ........................................................................ 50 CHAPTER 4 — LANSING’S DEMOGRAPHICS AND PARKS Introduction ........................................................................ 53 Demographics ...................................................................... 53 Introduction ............................................................... 53 Population Counts, Race, and Ethnicity .............................. 54 Poverty / Income .......................................................... 56 Demographic Summary ................................................. 60 Parks ................................................................................ 60 Introduction ............................................................. 60 History of Lansing Parks ................................................ 6O Lansing’s Parks and Recreation Master Plan ........................ 69 Conclusions ............................................................... 86 CHAPTER 5 - METHODS Introduction ........................................................................ 87 Neighborhood Parks and Study Variables ..................................... 88 Data Sources ....................................................................... 101 Park Data .................................................................. 101 City Data .................................................................. 101 Demographic Data ........................................... . ............ 102 Access Measures ......................................................... 103 Procedures ......................................................................... 104 Methodology Justification ........................................................ 110 Conclusions ........................................................................ 1 1 1 CHAPTER 6 — DATA ANALYSIS AND CONCLUSIONS Hypothesis #1 ..................................................................... 113 Hypothesis #1 — Conclusions ................................................... 124 Hypothesis #2 ..................................................................... 126 Hypothesis #2 — Conclusions ................................................... 134 Policy Implications ................................................................ 135 Conclusions ........................................................................ 141 CHAPTER 7 — POLICY RECOMMENDATIONS AND FUTURE STUDIES Limits of Study .................................................................... 144 Variables ............................................................................ 146 Policy Recommendations ........................................................ 147 Future Studies ...................................................................... 151 Conclusions ........................................................................ 153 REFERENCES ............................................................................. 154 APPENDIX Appendix A — City-Wide Baseline Statistics ................................. 158 Appendix B — Operating Budget for the Parks and Recreation Department ............................................................... 161 Appendix C Recreation Maps ................................................... 166 Appendix D — Michigan’s Recreation Opportunity Standards ............ 172 vi LIST OF TABLES Table l — 1992 Master Plan Recommendations ....................................... 62 Table 2 -— Park Density Table. Trust for Public Land ................................. 67 Table 3 — Committees and Focus Groups From Both the 1995-2000 and 2000- 2005 Master Plans .......................................................................... 78 Table 4 — Park Survey ..................................................................... 79 Table 5 —- Lansing Neighborhood Parks and Their Acreages ......................... 91 Table 6 — Number of Neighborhood Park Assets ...................................... 95 Table 7 - Asset Value Based on Estimates from Park Staff .......................... 97 Table 8 — Parks, Assets, and Total Asset Costs ........................................ 97-99 Table 9 — Number of Playgrounds in Neighborhood Parks and the Dates Installed ............................................................................. 100 Table 10 — Census Data Used in This Study ............................................ 103 Table 11 — Study Variables ............................................................... 104 Table 12 — Matrix for Hypothesis #1 .................................................... 109 Table 13 — Matrix for Hypothesis #2 .................................................... 110 Table 14 -— Matrix for Policy Implications .............................................. 110 Table 15 - Results of Population Percentages Within Catchment Areas .............................................................................. 114 Table 16 — Population Percent Difference and Index in Catchment Areas ................................................................................ 116 Table 17 — 1990 and 2000 Average Asset Value by Race and Ethnicity ........... 129 Table 18 —- 1990 Park Asset Information by Race and Ethnicity ..................... 130 Table 19 — 2000 Park Asset Information by Race and Ethnicity ..................... 131 vii Table 20 — 1990 Park Asset Information by Race, Ethnicity, and Poverty .............................................................................. 132 Table 21 — 2000 Park Asset Information by Race, Ethnicity, and Poverty .............................................................................. 133 Table 22 - 1990 and 2000 Information on Playgrounds .............................. 136- Table 23 -— 1990 and 2000 Information on Average Park Acres and Park 137 Size .................................................................................. 139 Table 24 — Matrix for Hypothesis 1 with Final Findings ............................. 141 Table 25 — Matrix for Hypothesis 2 with Final Findings ............................. 142 Table 26 — Matrix for Policy Implications with Final Findings ..................... 143 viii LIST OF FIGURES Figure l — Lansing Population .......................................................... Figure 2 — Lansing Demographic Profile .............................................. Figure 3 — Percent of Individuals by Poverty Status ................................. Figure 4 — Percent of Populations Below the Poverty Line based on 2000Census ....................................................................... Figure 5 — Percent of Household Income in Lansing 1999 .......................... Figure 6 — 1922 Neighborhood Park Districts ........................................ Figure 7 — 1922 Proposed Park System ................................................ Figure 8 — 1938 Existing and Proposed Neighborhood Parks ...................... Figure 9 — Lansing Parks ................................................................ Figure 10 — Rate of Park Acquisition .................................................. Figure 11 — Parks and Recreation Organizational Chart ............................. Figure 12 — Flowchart of the Planning Process to create the Parks and Recreation Master Plan ......................................................... Figure 13 — Lansing’s Neighborhood Parks .......................................... Figure 14 —- Lansing’s Neighborhood Parks by Size ................................. Figure 15 — 400 Meter Buffer Area .................................................... Figure 16 — 400 Meter Buffer Area Clipped by Barriers ............................ Figure 17 — 400 Meter Buffer Area Clipped by Barriers and Non- Residential Land Uses ............................................................ Figure 18 — Trends of Percent Change Between 1990 and 2000 in Proportional Representation in Catchment Areas ............................ Figure 19 — White Representation — 1990 .............................................. Figure 20 — White Representation— 2000 ............................................... ix 54 55 57 58 59 63 64 66 68 69 74 77 90 93 107 108 109 118 119 120 Figure 21 — Black Representation — 1990 .............................................. 120 Figure 22 — Black Representation - 2000 ............................................... 121 Figure 23 - Hispanic Representation - 1990 ........................................... 121 Figure 24 — Hispanic Representation - 2000 ........................................... 122 Figure 25 — Poverty Level in Park Catchment Areas — 1989 ........................ 122 Figure 26 — Poverty Level in Park Catchment Areas - 1999 .......................... 123 Figure 27 - City-Wide Percentages of Study Populations ........................... 125 Figure 28 - Chart Representation From Table 16. Percentage of Proportional Representation Within Catchment Areas of Neighborhood Parks .............................................................. 125 Figure 29 — Number of Parks with Catchment Areas That Have Greater Than City-Average Population Representation ............................... 127 Note: Images in this dissertation are presented in color. CHAPTER 1 - INTRODUCTION Background “A magical alchemy occurs in the best city parks: jangled nerves relax, breathing cases and a sense of delight awakens” (Mandel, 1998). These and many other benefits of urban parks have long been confirmed by a number of studies and surveys. Parks benefit individuals, neighborhoods, cities, and metropolitan regions in measurable areas such as health, economics, and social welfare (Ferris, Norman, & Sempik, 2001; Mandel, 1998; Young, 1995). Their impact is so intrinsic to urban existence that since their first appearance in the late 18005 they have been identified as one of the most valued elements critical to a satisfactory quality of life and rate second only to safety and security (Garvin & Berens, 1997). The quantity of benefits that the public gains through the use of urban parks has a direct positive correlation to the residential proximity (Page, Nielsen, & Goodenough, 1994) and to the assets found in that park (Hurnpel, Owen, & Leslie, 2002) such as aesthetics, facilities, and equipment. People living closer (i.e., having greater access to parks) benefit more from them than people living farther way. Parks with greater assets are associated with greater use. Recognizing that there is a spatial distribution of homes surrounding a park, some closer and some further away, there exists an inherent uneven gain in benefits to the surrounding populations due to park location. Because this resource’s benefits are gained by proximity, both the location of these parks and the resources spent on the assets allocated to each park have important implications for the populations surrounding these parks. This observable phenomenon (benefits gained by proximity) raises the critical questions of who currently has access to these parks, what assets do these parks have, and who benefits or is disadvantaged based on location and assets in these urban parks? Because the determination of where parks are located and what assets they have generally comes under the purview of urban planners, their actions have implications that may profoundly affect the urban population. Studies in environmental justice investigating impacts of land uses and services show that inequities do exist between population groups based on their spatial distribution in the urban landscape. They have generally confirmed that minorities and low-income populations bear an unfair and disproportionate burden of exposure to environmental harms and suffer from higher morbidity and mortality rates (Liu, 2001; Pastor & Sadd, 2002; Pastor, Sadd, & Hipp, 2001; Schulz, Williams, & Lempert, 2002). Some recent environmental justice studies have also investigated whether these populations (minorities and low-income) have a disproportionately lower gain from beneficial land uses (Liu, 2001). Because local governments’ master plans ofien guide the nature, location, and quality of urban parks and since these parks have been shown to affect the health and welfare of populations based on where they are sited, it is necessary to assess such park master plans and their outcomes to see what populations they are affecting. Planners, concerned with the allocation of public resources, master planning, and the subsequent social and economic outcomes of planning, are asked to distribute these resources in an equitable manner. According to the American Planning Association, planners strive “to expand choice and opportunity for all persons, recognizing a special responsibility to plan for the needs of disadvantaged groups and persons” (Planners, 1991). This professional responsibility to address the needs of the underserved in society is an ethical stand that urban planners have embraced. . Environmental justice studies have now begun to explore issues of equity based on a lack of a ‘benefit’ rather than a burden of an ‘ill’. Since urban planners’ land use decisions and master plans affect the quality of people’s lives (Beatley, 1994), urban parks and their master plans offer a unique phenomena that can be used to examine and determine whether this beneficial public resource is being distributed in a manner that reflects the ethical stance that urban planners have taken in their professional mission. Parks, and their accompanying assets, are generally considered a beneficial land use. If minorities and low-income populations have at least the same proportion of access to these parks and their benefits as the White majority population, then urban planners are following their professional mission of “recognizing a special responsibility to plan for the needs of disadvantaged groups and persons.” Statement of Problem The outcome of the City of Lansing’s park planning efforts that will be evaluated to see whether their efforts are truly meeting the planners’ professional goals and responsibilities. This study examines two of Lansing’s 5-year park and recreation master plans (1995-2000 and the 2000-2005) and determines whether there exists a measurable relationship between the distribution of parks, park assets, and the racial and economical characteristics of residents within an area representing a 5 minute walk (400 meters) to neighborhood parks. The City of Lansing’s park and recreation master plans are created and administered by the Lansing Parks and Recreation Department, whose mission is to “enhance the quality of life through the preservation and maintenance of park lands, the provision of quality leisure time activities and the provision of special facilities which would otherwise not be available to Lansing residents” (Lansing Parks and Recreation Department, 2000). In carrying out this mission, this agency influences both the creation and the spatial distribution of parks throughout the city, as well as the assets that are found in these parks through their budgetary expenditures. Understanding the implications of these master plans is essential in providing equitable services for the citizens of Lansing. This is the heart of this study and two hypotheses have been identified to accomplish this goal. Hypotheses The following two hypotheses are derived from two distinct research theories. The first hypothesis, following positivism, will be tested using quantitative evidence and looks at the spatial distribution of parks in relationship to race and income. HJDothesifs 1: Minority and poverty populations are under-represented in the area encompassing a 5 minute walk to neighborhood parks (400 meters). The second hypothesis belongs in the realm of ethical normative theory and requires analysis of the City of Lansing’s Park and Recreational master plans’ predicted outcomes and methodologies used in resource allocation to parks. This analysis will use both qualitative and quantitative methods to assess park assets in relationship to race and income. Use of both of these theories in public policy research is considered a better overall solution than either one alone (Liu, 2001). Hypothesis 2: Fewer resources have been allocated to parks located in the areas encompassing a 5 minute walk to neighborhood parks (400 meters) where greate_r than average minority and poverty populations live. Resources are defined as the current replacement costs of the assets found in neighborhood parks as of 2005. Organization of Study This study will be organized as follows: Chapter 2 reviews the current literature on the importance of parks and their impact on the populations that used them. Chapter 3 reviews the current theoretical literature and identifies the relevant theories applicable to this study in both areas of urban planning and environmental justice. A discussion on equity is included since this term has multiple definitions and interpretations throughout the literature. Chapter 4 goes into detail about the City of Lansing, its demographics, its parks and assets, and its history, specifically its park history. This information is necessary to understand the population settlement patterns and the current spatial distribution of parks. This chapter also includes the specifics of both the 1995-2000 and the 2000-2005 Lansing’s Park and Recreation master plans and their policies. Chapter 5 opens with a review of various relevant methods of environmental justice analyses and a justification of the methods used in this study. This chapter addresses the access to parks, the selection of the 5 minute walk or 400 meter area, and also covers data sources and specifies the method of analysis for each hypothesis. Chapter 6 presents the results of the study. Chapter 7 will discuss findings, the testing of both of the hypotheses, and the implications for planning and recommendations for future studies or future actions that could be developed from this research. Summary The broad purpose of this dissertation is to evaluate how well Lansing’s park master plans adhere to the more general urban planning values of ensuring that the needs of the underserved populations are being addressed. This type of evaluation is valuable to make sure that our current planning policies are equitable and that they follow the professional and ethical values held by the people who develop and enforce them. The planning profession and its body of literature must be aware of the implications of their actions. If this study finds that the underserved population is not being served equitably, changes may need to be made and inequities corrected, both in planning practice and in the training of professional planners. More specifically, this dissertation will describe the distribution of neighborhood parks in Lansing and its population, and will evaluate these distributions for equity of access and park assets for minority and poverty populations. The Lansing’s Park and Recreation master plans for 1995-2000 and 2000-2005 will be analyzed and their outcomes in terms of park asset allocation will be assessed against the equity definition used by today’s urban planners. CHAPTER 2 - PARKS This dissertation is designed to evaluate park planning efforts in terms of equity of park access and assets for disadvantaged populations. This involves the planning profession, the environmental justice movement, and the parks, which are being used as the test variable. The purpose of this chapter is to clarify the issues and implications of urban parks on the populations before they can be understood from a planning and environmental perspective. Chapter 3 will address both the urban planning and environmental theories that apply to this study. Urban Parks Parks have been studied widely since their inception in this country in the mid- 18003. The following literature review regarding parks is organized into four broad categories encompassing issues for both community and individuals in the areas of social, economic, health, and environmental impacts. This latter category focuses on more physical and biological aspects of parks such as pollution and storm water management. Before beginning to delve into the literature regarding parks, a very brief description follows describing what is considered a park through out this literature. Green spaces, urban forests, city squares, zoos, riverfront trails and many other terms fit under the broad umbrella of urban parks. Urban parks can contain market places, be inside or part of building plazas, and may even be part of the transportation systems as boulevards or streetscapes. Not only are park areas for outdoor recreation, but for shopping, strolling, exercising, driving, and many other activities. Since parks come in such various sizes and shapes, this literature review will only concentrate on the social, economic, health, and environmental impacts that parks, in general, have on cities and their residents. Social Impacts of Parks Historically, parks were first designed to improve the urban environment of cities by addressing both community and individual needs (Woudstra & Fieldhouse, 2000). In Britain, a report by the Select Committee on Public Walks was given to Parliament in 1833 that identified the benefits of parks. It stated that “parks would be the lungs for the city and would refresh the air; would improve people’s health and provide places for exercise; would be an alternative form of recreation to the tavern; and would provide beneficial contact with nature, so elevating the spirit. Furthermore, as all members of society would use parks, social tensions would be reduced and the classes would learn from each other” (Woudstra & Fieldhouse, 2000). Not only do they help people of all classes mix and enjoy each other, but with the no alcohol laws, it was historically thought that “drinking fountains provided ideal opportunity for promoting the values of temperance” (Woudstra & F ieldhouse, 2000). In this country, those same benefits were experienced and parks were built to help the industrialized, crowded, and polluted cities in the mid-nineteenth century (Sherer, 2003). Not only did American cities understand the benefits parks gave their citizens, they also realized the value in transforming polluted industrialized cities into beautiful, culturally uplifting centers (Harnik, 2003). Today, parks still offer places to socialize and recreate. Recreation has now been associated with lower crime rates, higher self-esteem, and increased community involvement (Land, 2001). In Stockholm, outdoor recreation is considered a fundamental and inalienable right, and no matter where you live, you are no more than half a mile from a park that is at least 2 acres in size with convenient and safe access (Kollin, 2003). In urban spaces, researchers have recommended that restorative open spaces such as urban parks should be so accessible that they should be considered part of everyday life and therefore should be placed at a density of 5 per square kilometer or at about a 5 minute walk (approximately 400 meters) (Thwaites, 2005). Recommendations and policies like these underscore the importance given to parks by places like Stockholm and London. Research done by the Trust for Public Land also supports the community benefits received from parks. They state that “urban recreation and sport programs are a proven, common sense, cost effective means of preventing crime and delinquency” (Land, 1995). Another study regarding recreation and crime was done in Fort Worth, Texas, where the crime was found to drop 28 percent when midnight basketball was offered within a l-mile radius of the community center (Sherer, 2003). Findings from a workshop held in 2002 by the National Recreation and Parks Association (NRPA) state that people’s individual experiences in parks were very significant in developing self-confidence in children and in the value of public park departments. An individual responded that “this one department is the glue that held my community together” (Anonymous, 2002). Backing that statement, a study in Chicago found that when collective efficacy (“the cohesion among neighborhood residents combined with shared expectations for informal social control of public space”) was 10 high, as could be seen when community involvement occured in neighborhood parks, then rates of violence and social disorder were low (Sherer, 2003). Historical and current literatures agree. Parks do seem to have a beneficial impact on cities and residents. As stated before, the benefits of increased self-esteem, lower crime rates, and increased social cohesion can all be attributed to urban parks. Along with these social gains, parks have also benefited individuals and cities by the economic impact they have on them. Economic Impacts of Parks Alexander Garvin and Gayle Berens did a study for the Urban Land Institute regarding parks and they feel we have forgotten why the late nineteenth and early twentieth century cities spent public resources creating parks systems. They feel that today, as in the past, “public spending on park development stimulates widespread and sustained private investment, alters settlement patterns, encourages social interaction, and reshapes the very character of daily life” (Garvin & Berens, 1997). An excellent example of this can be seen in the economic implications experienced in Manhattan with the development of Central Park in 185 7. Fifteen years after the park was completed, the real estate values surrounding the park increased by 9 times compared to the doubling found in other parts of the city (Garvin & Berens, 1997). Other research also supports this claim. John Crompton reviewed 25 studies that assessed if parks and open spaces contributed to an increase in property values and 20 of these studies supported this claim (Sherer, 2003). 11 Increasing property value results in increased tax revenue for cities. A study in Colorado estimated that adding a greenbelt to a Boulder neighborhood would generate $500,000 per year in potential taxes. This same study measured the average home value near the greenbelt to be 32 percent higher than houses 3,200 feet away (Sherer, 2003). This seems also to hold true in neighborhoods with poor and immigrant residents. Pincetl et al., measured an approximate increase of 1.5 percent in the expected sales price of homes within a radius of 200 to 500 feet from green space in such neighborhoods (Pincetl, 2003). These studies, along with many others, support the notion that people are willing to pay more for homes near parks. In a nationwide survey of registered voters conducted by the National Association of Realtors in 2001, 50 percent responded that they would be willing to pay 10 percent more for a home located near a park or protected open space (Realtor, 2001). On the opposite side of the economic picture, two studies brought up interesting questions regarding equity and ethics of parks and their development. The first one asked, "Who were we fixing parks for?" The economic benefits gained from parks are not equally felt by all the members in a city. Property owners seem to benefit by such increases of home values, but lower income home renters may actually lose since property values, and therefore rents, may go up resulting in limited access to affordable housing (Harnik, 2000). Another study in 1996 looked at the expenditure of park development and recreational activities. Where the majority of park users (44 percent) are just people enjoying a walk, 50 percent of some park budgets are used for organized sports that take up 25 percent of the park space and are used by only 6 percent of the overall park users 12 (Woudstra & Fieldhouse, 2000). Research also has found that the tendency is to support male activities over the activities of females and children (Woudstra & F ieldhouse, 2000). The controversy of park fees is another equity issue being addressed currently by park departments especially in this tight budget era. Since parks are considered a community public service, how fair or equitable is it to charge for its use and maintenance (Harnik, 2000)? Although parks do seem to lead to some economic benefits, a study by John Crompton reports that an ill kept park may have the opposite effect (Sherer, 2003). Instead of assets, they become a neighborhood liability. Because a neglected environment has been shown to foster antisocial behavior (Woudstra & Fieldhouse, 2000), this means that a neglected park is prime real estate for vandalism. An example of this was Bryant Park in New York in the early 1980s, which became a haven for illicit drug use and crime. Much of the land surrounding this park was abandoned. After its renovation, the area surrounding this park had a 60 percent increase in lease activities and real estate brokers gave much of the credit to this “deal-clincher” park (Garvin & Berens, 1997). Neglect and underuse may also occur when design issues are not well addressed. Unimpeded automobile access hurts park usage. Banning or restricting cars can restore life to ailing parks (Harnik, 2000). Another study found that for some park users, the local parks failed to meet their needs. The lack of opportunity for children to encounter wild open spaces and the “institutional savanna” landscapes (lawns) and sport pitches provoked the strongest reaction to under use. Also in this study, the quality of maintenance seemed to be equated with the quality of the park (Burgess, Harrison, & Limb, 1988). Many examples of park redesigns and renovations are found in the 13 literature and they support the conclusion that well designed and maintained parks are economically beneficial, not only for residents and businesses, but also for cities which have used parks as a way to help attract and retain both tourism and commerce. Health Impacts of Parks Studies have shown that people who live closer to parks use them more often (Page et al., 1994). This access gives these citizens the opportunity to be more physically active and have greater contact with the natural environment than citizens living farther from parks. Health studies concur that increasing the physical activity of people generally lowers mortality rates and improves psychological well-being (Paffenbarger, 1996; Services, 1996), while the lack of physical activity is implicated in cardiovascular disease, cancer, chronic obstructive pulmonary disease and diabetes (Shephard, 1994). Physical inactivity was considered the third leading cause of death nationwide in 2000 (Mokdad, 2004). A study done on older adults found that “park-based leisure experiences can have a positive influence upon mood states, stress, and health of this population” (Orsega-Smith, 2004). Other studies have also suggested that health benefits may be derived directly from contact with natural elements, such as plants, animals, landscapes, and wilderness (Frumkin, 2001). In addition, qualitative studies have shown that park users place a high value on scenery and natural features (Woudstra & F ieldhouse, 2000). This scenic value has again been quantified in health studies done at hospitals. Patients with a view to green space were shown to heal faster than patients without such a view (Urlich, 1984). Thus, if people living near parks use them more (i.e., 14 greater physical activity) and are exposed to greater contact with the natural elements, they may be deriving greater health benefits than people living farther away. Although no current literature exists that has been able to determine specifically if people live longer or are healthier if they live closer to parks, there does seem to be a logical conclusion from these studies that the greater access to parks result in greater physical activity which should lead to greater health. Also missing in the literature is the correlation of naturally active people and their preference to live near parks. Environmental Impacts of Parks Environmentally, parks are usually considered an asset to the city. They are places to increase the biodiversity of plants and animals found in the city, improve water and air quality, have bioprocesses that improve the environment, and can be used to teach sustainable practices to park users. Also, park elements, such as trees, help to moderate the heat island effect that occurs in cities. In one study, trees were found to be able to filter up to 85 percent of the suspended particles in the air. One hectare of urban trees, shrubs, and grass can remove 600 kg. of carbon dioxide and return 600 kg. of oxygen in 12 hours (Woudstra & F ieldhouse, 2000). A study done by the US. Forest Service, quantified the environmental work done by urban trees. This study showed that one tree, in its 50 year lifetime, can provide the following economic services (Sherer, 2003): 0 $31,250.00 worth of oxygen 9 $62,000.00 worth of air pollution control 0 $37,500.00 worth of water recycling 15 0 $31,250.00 worth of soil erosion control By breaking up the impervious surfaces, parks and open spaces in cities also help with storm water runoff. Not only does infiltration of rainwater occur through the soil, but trees themselves manage the flow of storm water runoff more effectively and less expensively than do concrete sewers and drainage ditches. The study done by American Forests estimated that cities save approximately $400 billion in the construction cost of storm water retention facilities by their trees alone (Sherer, 2003). Summary Parks have long been recognized as an asset in urban spaces. They provide social and economic benefits to both individuals and communities. From an environmental perspective, they help communities with both human and ecological health and perform basic engineering functions of water management and pollution control that would otherwise be very costly to the public. With the proportion of benefits being distributed in a spatial pattern due to the location of the parks, and the distance fi'om the residents, this resource needs to be managed in such a way as to have its benefits distributed as widely and as equitably as possible. That is where urban planners and their master plans have the greatest impact. The following chapter looks at the theories that have guided urban planners in their planning decisions, as well as environmental justice studies that look at the equity of the various land uses and their distribution. 16 CHAPTER 3 -URBAN PLANNING AND ENVIRONMENTAL JUSTICE REVIEW Introduction With an understanding of the benefits associated with parks covered previously, this chapter seeks to place theory and research at the core of this study to help set the stage for the current debate of land use planning (i.e., distribution) and policy. Urban planners and their professional efforts, along with studies of environmental justice, seek to address the issue of equity in land planning. This chapter will first delve into urban planning, its goals, objectives, and theories. This section is followed by the various definitions of equity found in the literature, as well as the one being used in this study, and will conclude with a section covering theories and studies in environmental justice. The final section covers some historical background on the environmental justice movement and contains two subsections addressing justice and locational theories as they apply to the issues of land planning decisions and land use conflict resolution. Urban Planning The urban planning profession in the United States formally began in the early 19005 as a response to the industrialization and degradation of our cities. Defining and understanding this profession, its purpose, and its theories is the main goal of this section. This section is organized into two main parts: goals and objectives of planning, and 17 planning theories that relate to equity issues of land planning and distribution. The purpose of this first section is to show all the facets of planning and how the experience of the last century, with its benefits and constraints, has led to the current stand being taken by urban planners. This includes the various definitions of planning and what some believe is the purpose of planning. G_oali and Obiectives of Mg Today, the practice of urban planning is quite diverse with developers, designers, government officials, and residents of the city all participating in the planning and the development of our cities (Campbell and Fainstein, 1996). Likewise, professional planners can be found in myriad fields, such as social science, psychology, health, architecture, political science, and economics. The encompassing nature of this profession attracts people with different skills and focuses, thus allowing specialization in a variety of combined fields of study. This broad perspective begins to explain why the practice and theory of planning are so diverse. Planning has been defined by Michael Brooks as “the process by which we attempt to shape the future” (Brooks, 2002). Nigel Taylor describes planning in the post- war period and before to be “essentially an exercise in physical planning and design,” and believes that “planning exists to improve the world.” He continues by stating that “planning is a form of social action, or a social practice. It is about intervening in the world to protect or change it in some way — to make it other than it would otherwise be without planning” (Taylor, 1998). Scott Campbell and Susan Fainstein state that planning “claims to be able to predict the consequences of its actions” and that it “is 18 intervention with an intention to alter the existing course of events” (Campbell and Fainstein, 1996). Perhaps the most insightful definition of planning is Charles Hoch’s in which he states that planning seeks “to change the physical, social, and economic patterns of settlements, especially in the rapidly growing cities, to reduce social disorder and injustice, while enhancing the efficiency and beauty of daily life” (I-Ioch, 1994). Planners attempt to address urban issues, whether the issues are social, environmental or economic in nature. The need and the uses for planning often become evident when society faces some sort of crisis in one or more of these areas. In the U.S., the urban planning profession grew as a necessary response to the difficult conditions found in the late nineteenth century (Hall, 1989). The rapid growth of cities at the turn of the century was so dramatic that “in 1905, New York’s lower Manhattan district housed 742,135 people on 2,415 acres, or 195,000 people per square mile” (Marshall, 2000). Such hyperdensity has not been seen here in the U.S. before this time or since. As cities industrialized and became more crowded, poverty and crime rose, while general health deteriorated. Housing conditions and poor social services, along with the flight of the rich from our urban centers, left cities in need of planning and reform. From an environmental point of view, the industrialization of our cities polluted our air and water, causing health, safety and welfare problems for society. Land degradation, the creation of brownfields, and the reduction of green, healthy spaces in cities also called for regulation. According to Brooks, planning considers the distributional effects of public and private action, and attempts to resolve inequities in the distribution of basic goods and services. It promotes the common or collective interests 19 of the community, particularly with respect to the provision of public goods, such as developing parks and ensuring clean air and water for all (Brooks, 2002). Today our cities are still experiencing social, environmental, and economic problems. As society becomes more polarized economically and socially, planning is needed to protect the interest and quality of life of all its citizens, to protect and guide in the use of its limited and dwindling resources, and to set a course guiding the future development and growth. Hoch’s explanation of why we need planning shows the comprehensiveness of the problem. “Professional planners in the United States take on the problems that private organizations not only avoid, but tend to aggravate or cause. These collective problems, such as congestion, pollution, land use conflict, residential displacement, and flooding, defy simple and unilateral treatment by a single agency. They are problems that the markets often create and cannot solve. The complexity and interdependence of these problems’ causes and effects make even identifying them a difficult and contested task. [P]rofessiona1 planners try to classify and analyze these messy problems and propose solutions” (Hoch, 1994). The question of who benefits from planning efforts has led many to oppose planning on the grounds that it is unfair. Questions as to who should decide what is good for the community and the knowledge that it is only the powerful and wealthy who are imposing their views on the city and deciding how it is to function and be developed, has fueled this opposition. Not only has planning been accused of being unfair in its practices, critics such as Oren Yaiftachel contend that planning actually advances “regressive goals such as social oppression, economic inefficiency, male dominance, [and] ethnic marginalization.” He adds that “planning facilitates elite domination and control of four key societal resources: space, power, wealth, and identity” (Brooks, 2002). The systematic exclusion of minority, low-income groups, women, and the 20 underprivileged and under-represented populations from the planning process reinforces these views. Aaron Wildavsky’s 1973 article attacked planning by questioning its effectiveness. “To be valid, planning must guide governmental decisions - that is, it must govern; otherwise there is no reason to do it. In reality, however, planning never governs, and thus is rarely successful or even accurate in its projections for the future. Instead of shaping reality, plans are consistently adjusted to reflect the reality that has occurred despite the plans. Planning fails, then, to carry out its basic purpose. The favorite concepts of planners — such as rationality, coordination, and efficiency - are all platitudes; none of them truly fall within the planners’ range of control” (Brooks, 2002). Overall, planners never seem to get things right, in large part because their professed role is simply impossible. Ultimately, those who continue to support planning do so as an expression of faith, not reason; accordingly, planning “is not so much a subject for the social scientist as for the theologian” (Brooks, 2002). Most of this negative criticism of planning is based on the fact that cities are made up of a variety of individuals with distinctive needs and planning has affected all of these individuals at some point. Whether they have been hurt or helped by planning will likely determine on which side of the fence they sit regarding the usefulness and necessity of planning. Of concern then is the question of when planning should be done. How many people need to be helped by our actions before we deem that their needs should be considered in the overall city plans? By helping these people, how many others will be hampered by this new plan? Who should decide at what point we help more people than we hamper? Other issues, regarding whether to plan or not, deal with who will benefit and who decides who will benefit? Planners must use their professional expertise and 21 balance the benefits of planning along with the constraints that planning causes. Campbell and Fainstein point out that in making these types of decisions, planners end up placing a monetary value on the quality of human life; a value-laden task and one that diverse individuals may never agree on. They state that: “belief in the public interest is the foundation for a set of values that planners hold dear: equity protection and equal opportunity, public space and a sense of civic community and social responsibility. The challenge is to reconcile these benefits of a common public interest with the diversity that comes from many communities living side by side” (Campbell and Fainstein, 1996). That task requires knowledge of each community’s interests, the ability to define equity in terms that all will agree on, and the ability to define and develop civic community and social responsibility. Speaking directly to this concern, the planning profession has set guidelines for its practice in their code of ethics. As stated in the beginning of this document, planners strive “to expand choice and opportunity for all persons, recognizing a special responsibility to plan for the needs of disadvantaged groups and persons” (Planners, 1991). This professional responsibility to address the needs of the underserved in society is an ethical and value stand that urban planners have embraced. This stance emerged from the problems and issues stated above and the theories that have evolved during the evolution of the urban planning profession. The following section will review only the relevant theories that helped this profession arrive at this code of ethics. Urban Planning Theories Since urban planning is concerned with the health, safety, and welfare of city dwellers, many theories that guide this practice abound. Earlier theories concentrated on 22 the physical layout of cities, while more contemporary theories took on a more ethical stand regarding urban dwellers. These contemporary theories are important to understand as they guide the current stance that urban planners are taking in planning and designing our cities, which in turn guides policies that aid or discourage unfair land use practices. Of the many theories that exist, only the following theories and practices are covered in this section since they are most related to the ethical stand currently taken by planners or are highly significant in current urban planning practice: (1) the comprehensive rational theory, (2) critical planning theory, (3) advocacy planning theory, (4) feminist planning theory, (5) postmodern planning theory, (6) citizen and the communicative model, and (7) just city theory. 1. The Comprehensive Rational Theory In an attempt to address all the needs of its citizens and avoid fixing one problem and causing another, planners came up with the ‘comprehensive rational theory.’ This theory combines two other theories, systems theory and the rational process. Systems theory is based on the assumptions that the city is made up of various sets of interconnected systems and that these systems can be defined and understood and thus would lead to a solution to urban problems (Taylor, 1998). The rational process is based on the assumptions that urban problems are solvable and that they can be analyzed in a logical and rational manner. This process allowed for the quantification of solutions being applied to social problems with the belief that plans and policies could be studied and analyzed for their merits, equities, or shortcomings. The combination of both of these theories allowed for an overall comprehensive look at the city. No longer would 23 one solution be proposed without an attempt at understanding the effect it would have on the whole system. The assumptions of this theory are that by analyzing all the elements and interactions of a system, and by using the rational process, one can resolve all the problems found in all parts of the cities. In other words, a whole system approach of addressing urban problems is better than a piece-meal one. Problems can be studied and resolved in the context of the whole city. Many criticisms are levied on this theory. Critics take issue with the assumption that we can ever come close to defining and understanding the complexity of urban systems. The definition of systems becomes problematic because not everyone would define them the same way. Also, which systems are defined and who defines them become points of contention. Understanding the interactions between systems that we have defined may also not lead to a true understanding of these interactions as we might have misidentified a system or overlooked a critical one in our identification of the systems that were analyzed. Further, the assumption that urban problems are solvable and that they can be analyzed in a logical and rational manner is questionable. Since human behavior is not always rational or logical, this process ignores basic human nature. In addition to the whims of humans is the problem of their various and greatly varying views. What seems to be a logical and rational process for one person may be considered the opposite by others. If systems theory is correct that all parts of the city are connected and interrelated, then a solution suggested through use of the rational process for one part of the city, may in fact, cause problems for other parts. Also, what may solve the problem for a specific population group may actually cause problems for another population group. This brings 24 into question the validity of one of this theory’s assumptions. Are all urban problems solvable? An additional criticism is that a plan can never be comprehensive because reality is always more complex (Benveniste, 1989). Since we can’t know it all, our analysis will never really be truly comprehensive. For instance, a solution that took place in New Jersey that seemed to correct problems of congestion and slum housing turned out not to take social needs into sufficient account and was considered by some to be unethical or inequitable. The construction of the highway and the removal of slum housing resulted in peoples’ social fabric being torn apart and resulted in a much lower quality of life for some urban residents. What was thought to be a poor, degenerated housing area, actually had a well-integrated and healthy social system (Marshall, 2000). Our inability to know and incorporate all issues in our analysis and solutions has created much opposition and criticism of planning. This theory attempts to get to the issue of equity by trying to view the city in a systematic and comprehensive manner. Because it attempts to understand the connection between parts, the equity issue comes into play in the definition of the problem and the weight being placed on the various parts and sections of the equation. The ethics of equity are not well developed in this theory, but this theory is important because it forces the understanding of all the parts and their interactions. It is the comprehensive ideal that has made many cities attempt to create master plans to guide development. The park master plans that will be reviewed in the next chapter owe their existence to this ideal that a comprehensive view can make for good planning. 25 2. Critical Planning Theory “Critical planning theory is concerned with the distribution of power in society and the extent to which planning reflects this distribution of power” (Benveniste, 1989). Unlike strategic planning that identifies critical trends, critical planning theory is not about critical issues, but more about criticizing current planning efforts. The philosophy that guides this theory is that planning should benefit all of society equally, not just the powerful. The assumptions that this is based on are that the powerfirl currently benefit more fiom planning than the general public, and that the planners have the power to change this status quo. A second philosophical point of this theory is that if planners had a greater understanding of the current differences and needs found in society today, their planning would result in an improvement of quality of life for the majority of the population. The assumptions of this philosophical point are that planners have the capacity to understand differing cultures and needs, and that planners can adjust the way they currently plan in response to this understanding. This includes underprivileged populations and attempts to correct inequalities of the current plan. Critical planning theory is important in its critical examination of the profession and its goals. It forces the comparison of actual planning with the general planning philosophy of protecting the interests and quality of life of all citizens with the added emphasis on the underserved populations. Although this theory has been criticized for pushing Marxist and Communist ideals, critical planning theory’s contribution of forcing introspection and reevaluation of planning goals by the profession is invaluable. 26 3. Advocacy Planning Theory Like critical planning theory, advocacy planning theory states that there is a definite difference in the way that the powerful and the underprivileged have been served by planning. While critical planning is more general in its equity goal, advocacy planners concentrate mainly on the underprivileged. The powerful and wealthy have no problem in making their concerns heard and addressed by current planning practices. The system works for them. It is the poor, minority, and uneducated public that spend their time concentrating on survival and find themselves facing bureaucracy and regulations that hamper their efforts to improve their situation. Banking policies and district red-lining were just two practices that aimed at protecting the privileged and kept many minorities and poor from owning their own home. Examples like these forced planners to reevaluate their practice, explore their own assumptions, and redefine their goals. Advocacy theory is based on the assumptions that the underprivileged have no voice in the current planning process and that planners can truly make a change in their quality of life. Advocacy philosophy is centered on the belief that because this population has generally been ignored by planners, planners have a responsibility to represent and advocate for a change in the quality of life of this population. Although a noble and worthy cause, advocacy planning doesn’t usually generate the attention it requires. These planners generally have little influence and power over the system, and their clients have little in the way of resources (Benveniste, 1989). Since the planners want to change the quality of life of the underprivileged, they must gain the required knowledge of the existing social and economic systems. Manipulation of these systems 27 places planners directly into the political dimensions of planning and provides them the opportunity to participate in shaping the political climate that can influence their goals. It is this theory that currently guides the stance that the American Planning Association takes regarding the professional attitudes and values held by planners. This theory, based on egalitarianism, seeks to eliminate inequalities. 4. Feminist Theory of Planning The feminist movement is rooted in the following three general assumptions: “(1) the position that women are exploited, oppressed or devalued by society; (2) an interest on the part of the feminist thinker in changing the condition of women’s lives; and (3) the assertion that traditional, still dominant theory, research, and practice ignore or justify inappropriate and/or exploitative treatment of women” (Campbell and F ainstein, 1996). In planning, feminists assert that women’s issues have been ignored and are sometimes not even acknowledged. Women and men use space differently, yet women’s needs are not being addressed. While the central business district meets men’s needs, the residential district, which is generally associated with women, lacks daycare facilities and convenient public transportation to work, schools, and shopping. Zoning has effectively separated these uses and created a hardship for women. Changes need to reflect that although women and men are different, they must be treated equally. This poses the problem of determining how the equality is to be defined when real differences exist. Take for instance the idea of justice. Feminists would like to mete out justice based on contextual understanding and use the ethics of caring vs. the 28 current ethics of judgment in which individuals’ actions are determined to be either right or wrong. The issue of equality for feminists revolves around the idea that women are not just counterparts to men, but they themselves are a whole entity. Feminist planners are really advocacy planners for women since, in the current system, women find themselves outside of the decision-making process. Where feminists and advocacy planners diverge is in the wholesale changes that feminists want to create. They would like to see a world where there are more “alternative images of the good life,” and where instead of competition with winners and losers, there could be more team-building and communal fostering (Campbell and Fainstein, 1989). Knowledge could come not just fiom rigorous scientific methodologies, but also fi'om intuitive approaches, oral traditions, and symbolic representations. Logic could sometimes give way to non-rational solutions and sentiment would be valued. Planning in this new way of thinking would make adjustments for multiple cultures and help acknowledge and celebrate these differences (Campbell and Fainstein, 1989). No theory is without its critics, and feminism is no different in this regard. The two main criticisms of this theory are that feminism excludes men or doesn’t embrace them fully, and secondly, that women have many voices, not just the one heard from the feminists. Another criticism of feminism concerns its definition of knowledge to include unscientific and intuitive information. This theory is valuable in that here is a group defining themselves as underserved and thus, with the current planning stance of addressing the needs of the underserved, requiring a complete change in planning and policy. This theory, and its implications, illustrates the complex nature of trying to meet 29 the needs of the underserved and the difficulty in mixing the needs of various groups at once. 5. Postmodern Planning Theory Postmodernism at its core is the rejection of all that is modern (Knox, 1991). Paul Delany has defined it as “everything that [other] systems [have] devalued: the aleatory and the unmotivated, representation in the visual arts, surface decoration in architecture, small-scale innovation, the superstructure, market forces, popular culture. Everyone can make their own list.” His last statement captures the essence of postmodernism. Everybody’s interpretation is equally valid. This also means that since everyone’s views are equal, then contradictions and inconsistencies are valid and can stand simultaneously (Delany, 1994). Postmodern planning theory can therefore be extrapolated fiorn the definition of postmodernism, and at its basic philosophical core, this theory maintains that everything in urban environments is equally valid while all modern theories are rejected. In other words, since modernity has failed, therefore, all the other voices are right. The basic assumptions for this theory are that modernity has failed, all have a right to a voice, and all voices are equal. Rosenau’s description of postmodern urban planning states that “[t]he city is a text, constituted of different interpretations by various readers. Postmodern planning dissolves space as a knowable, manageable constraint and replaces it with hyper—space, which conceives of space as fragmented and disorganized, as manifesting gaps of undecidability” (Rosenau, 1992). Ted Relph states that “postmodern is not a style, but a 30 frame of mind — [a] confluence of many trends” (Dear & Flusty, 1998). Michael Dear, a postmodern urbanist and professor of urban planning, describes postmodern planning as “a pastiche, a hodgepodge, crazy-quilt composition” (Dear, 1986). No longer is the generally accepted Chicago school’s view of an orderly centric city with segregated land uses and ring-like growth patterns valid (Dear & F lusty, 1998). A new school of thought, the Los Angeles school, begins to emerge out of postmodern thinking. Los Angeles is seen as the epitome of postmodern urban planning. This is because it was not planned and it has sprawled out of control. Precisely because one would not plan a city like Los Angeles is why it is postmodern in nature. Criticisms of postmodernism are many, but since all voices are considered valid under this theory each criticism is just another voice expressing its (valid) view. This theory is difficult to assimulate with the current planning stance, yet it seems to present a solution to the issues raised by the feminists and attempts to mix all needs into one. All solutions work as long as it doesn’t negate anyones voice. What is interesting in this theory is the removing of rules and guidelines to try to accommodate all, yet that is also its weakest point. The underserved may have an equal voice, yet they are still powerless to make a change. 6. Citizen Participation and the Communicative Model Citizen participation theory addresses the need for the public to be involved in planning decision making. This simple theory’s philosophy is that the more people who participate in the planning process, the better the solution. This is based on the assumptions that the general public knows the issues that affect it better than the planners, that each person holds different views, and that people want to participate in 31 planning decisions. The communicative model’s philosophy is very similar and states that “public policy needs to draw upon and make widely available a broad range of knowledge and reasoning drawn from different sources” (F ainstein, 2000). Its assumptions are: “(1) all forms of knowledge are socially constructed; (2) knowledge and reasoning may take many different forms, including storytelling and subjective statements; (3) individuals develop their views through social interaction; (4) people have diverse interests and expectations and these are social and symbolic as well as material” (Fainstein, 2000). Planners have often been criticized for making decisions that will affect many people without consulting them about the problem or the solution. The justification for this has been the belief that “the layman simply cannot understand and responsibly judge complex technological issues” (Campbell and F ainstein, 1989). Although there is some truth to this statement, planning issues need not be ensconced in technical language. People can react to plans or ideas that may make a real change in their environment and evaluate them according to how useful they find them. Fainstein adds that “within communicative theory, the planner’s primary function is to listen to people’s stories and assist in forging a consensus among differing viewpoints. Rather than providing technocratic leadership, the planner is an experiential learner, at most providing information to participants but primarily being sensitive to points of convergence. Leadership consists not in bringing stakeholders around to a particular planning content but in getting people to agree and in ensuring that whatever the position of participants within the socioeconomic hierarchy, no group’s interest will dominate” (Fainstein, 2000). 32 The use of this technique has given planners two major benefits. First, citizen participation in the planning process has helped identify problems or conflicts that may have been missed by the planners, and secondly, having the public participate in the decision process helps to build both credibility and acceptance for the decision (Campbell and Fainstein, 1989). Reaching an acceptable decision can be a problem, especially since the population holds a variety of values and beliefs. Politics and diplomacy are involved in this process, as different groups may require different solutions to a single problem. Educating the public about all views and coming to a consensus can result in greater tolerance and understanding between peoples. The opposite can lead to the “assumptions that if only people were reasonable, deep structural conflict would melt away” (Fainstein, 2000). A planner is put in the position of being neutral, a position he/she might not hold, and also of finding a common solution, which may or may not be possible. Other problems with these theories are the length of time they add to the planning process, and the gap that exists between the theory and the practice of using the communication model and/or citizen participation in actual practice. The diversity and selection of the participating population may also be a problem, especially if the issue involves diversity and the population is not diverse in its makeup. 7. Just City Theory Similar to the feminists and the postrnodemists, just city theorists call for a dramatic change in the status quo. They, like the communicative planning theorist, believe that the public should participate, not just in planning decisions, but in all aspects 33 of local government. Their philosophy is based on the belief that “progressive social change results only from the exercise of power by those who previously have been excluded from power” (Fainstein, 2000). This assumes that governments are not neutral or benevolent, that planners have protected the interests of businesses, that there are conflicting views of society, and that the public has been excluded from the planning process. Just theorists have two expressions, the radical democrat and the political economist. The radical democrat would like to see governance being turned over to the people. They understand that there will always be conflicting views and that it is in the participation of the public that power is exerted. Political economists are concerned mainly with the distribution of social benefits and the unfairness related to this distribution. Although both types of theorists have different viewpoints, their main purpose is to mobilize the public to bring about change. Prescribing what those changes will be is not their concern so much as having the public (especially the relatively powerless groups) participate in governance and in coming up with equitable solutions. The just city theory is much like socialized democracy and thus shares the criticisms of both. Socialist criticism related to economic vitality and democratic problems related to the deprivation of minority needs are both levied at just city theory. Summm Although no one theory or method has been developed that addresses all the issues that planners deal with, an overall ethical stance has been agreed to by the American Planning Association. This stance, to be responsible for planning specifically 34 for the needs of the underserved populations, can be seen through different iterations in the previous theories. While some theories will question who are the underserved in society, planners do have an ethical stance that guides them in their professional work. Ensuring that current planning efforts continue to address the needs of the underserved populations is the focus of this dissertation. When planning efforts fail, or population shifts occur, the result may be that an excess burden ends up being carried by one population group over another. It is this issue of equity and imbalance that are addressed in environmental justice studies. From all the different theories reviewed, this dissertation will use the advocacy theory because it is most closely aligned to the ethical stance taken by the planning profession. This theory supports the idea that the underserved population needs to be aided in having their voice heard regarding planning issues since their position in society is such that without this intervention, their needs would not be heard. This theory is also at the heart of the environmental justice movement that tries to advocate for the populations least likely to defend themselves from unfair development and planning practices. Introduction to Equity and Environmental Justice Since the appearance of the first case in the early 1980s, environmental justice studies and the issues surrounding these cases have been the subject of much debate. Specifically, what theory or principles should guide the equitable planning and distribution of various land uses in relationship to the urban population? This section covers various studies and theories that have a direct focus on environmental equity 35 issues and begins by first clarifying the meaning of equity used in the literature and in this study. Emmy Equity, fairness, and justice are terms used interchangeably to mean the impartial, evenhanded treatment of others (Garner, 2001 ). This study uses the term equity. The use of this term in relationship to land use distribution usually means that one measures the disproportionate level or inequitable distribution of impacts caused by a noxious land use on individual populations. Policy makers, minority advocates, and the various population groups do not always interpret equity in the same manner. The term “evenhanded treatment” especially in the distribution of land uses, has many interpretations depending on which distribution theory you hold. There are three general distribution theories that, if applied, may have completely different policy outcomes (Liu, 2001). They are egalitarian distribution, input-based distribution, and need-based distribution. Egalitarian distribution is based on the theory that fair distribution of an item means that the item is divided into equal proportions and everyone in the group receives an equal number or portion. In terms of land use distribution, all population groups would be equally affected, both in a positive or negative manner, by the various land uses (noxious or beneficial). This is the definition of fair treatment used by the Environmental Protection Agency (EPA) that states that no group of people, including racial, ethnic, or socioeconomic, should bear a disproportionate share of the negative environmental consequences resulting from industrial, municipal, and commercial operations or the execution of federal, state, local, and tribal programs and policies (Liu, 2001). 36 The second distribution theory is based on input. This theory states that the distribution of an item depends on the amount of input that each population puts into the specific item. In terms of land use, those p0pulations that pay higher taxes, could earn a great portion of the public land use or a greater benefit fi'om public policy outcome, such as the reduction of exposure to noxious land uses and/or the increased exposure to beneficial land uses such as parks. This distribution theory has been the basis for most of city planning in that each city collects its own taxes and uses them to help its citizens. A city with higher tax revenues would not share with other cities with lower revenues. This can also be seen in specific neighborhoods. School districts with higher tax revenues have greater budgets for their students than lower tax generating school districts. The third type of distribution is based on need. This theory states that those individuals or groups that have a greater need of an item get a larger proportion of that item. In terms of land use distribution, this can be interpreted by stating that populations having greater needs of benefits gained from a land use, or greater need to reduce an impact from a noxious land use, will be given priority over other population groups. Therefore, groups such as minorities, which the research shows as having a decreased quality of life and health status, should have greater access to beneficial land uses such as parks, and have a reduction in their exposure to noxious land uses. This is precisely the distribution theory that is suggested by the Urban Planners code of ethics. By stating that they recognize a special responsibility to plan for the needs of disadvantaged groups and persons, they are supporting the distribution of land use based on need. It is this type of distribution that this study uses to measure the equitable distribution of park access and 37 assets. With these definitions of equity explained, the following sections use these definitions through out the description of the environmental justice literature. Environmental Justice Studies Environmental justice studies concern themselves with the equitable distribution of burdens created as an outcome of human activity, on all populations (Liu, 2001). These studies, which generally use proportional distribution as an equity definition, have generally confirmed that minorities and low-income populations bear a disproportionate burden of exposure to environmental toxins, and that they suffer from higher morbidity and mortality rates (Liu, 2001; Pastor & Sadd, 2002; Pastor et al., 2001; Schulz et al., 2002). The federal govemment’s response to these recognized injustices is found in President Clinton’s 1994 Executive Order 12898 directing all federal agencies to identify and address any effects caused by their policies that would result in highly disproportionate and adverse conditions specifically affecting these vulnerable populations (Maantay, 2002). EPA’s definition of environmental justice is in line with Executive Order 12898, and both emphasize that resulting actions of policies must be viewed fiom their impact on all populations. Concerning the impact of various land uses on all populations, the laws that were put into effect in 1994 attempt to mitigate some of the hazardous and noxious land uses. Sadly enough, they only concentrate on the noxious exposure, rather than also balancing the beneficial effects of some land uses through the use of federal policy. Advocacy planning, which has its roots in need-based distribution, attempts to move the debate further along the continuum and give disadvantaged populations a say and a chance to 38 address their needs. The failure of planning was the impetus for the grass roots movement by minorities to address the inequities that they found in the land use distribution of noxious land uses. Case after case have been documented that highlight the struggles by these groups in fighting inequitable land use distributions. The first case in East Los Angeles in the late 1980s dealt with a hazardous-waste incinerator that was to be located in a predominantly Hispanic neighborhood. The grassroots movement succeeded in defeating the state’s plan to locate the first hazardous-waste incinerator in this neighborhood. This case was followed by one in south-central Los Angeles that dealt with a garbage incinerator that was to be sited in a predominantly Afi'ican American neighborhood. Since then, many cases, usually emerging from grassroots activism, have pointed out the continuing inequities in land use distribution. The one believed to be “the seminal event” for environmental justice was done in 1987 by the United Church of Christ Commission for Racial Justice. This report found that race was the most significant variable associated with the location of hazardous waste facilities and that the poor and minorities do bear a disproportionate burden of these waste facilities (Liu, 2001). That all these cases exist and continue to be brought up, points to a number of complex issues. These are some of the problems with planning as they were discussed in the previous sections: the diversity in the definition of equity, politics and policies, and land values, just to name a few. In addition, population shifts and economic downturns can also affect land patterns and land use distributions. Due to the complexity of existing inequalities in land use distribution, environmental justice studies measure these inequalities to help point out the problems in our planning and policies. 39 Equity and justice of land use distributions are at the heart of these cases. In the following sections, justice theories, economic theories, and locational theories will be discussed to give a broad view of the impact of various points of view, and how they can affect land use distribution. Justice Theories This section looks at theories regarding broad issues related to justice. In our current capitalist society and our efforts to plan our cities, not one specific theory dominates. Instead, current land planning and environmental justice studies use a variety of theories to best describe the needs and views of the current time and political view- point. Although many more theories exist, the following are highlighted because of their diversity in value systems and wide variation of results that can occur from their application. In addition, where applicable, the economic implications related to people and land uses will be discussed. These theories are (1) consequentialism or teleological vs. deontological, (2) utilitarianism, (3) pareto optimality and efficiency of the market economy, (4) contractarian, (5) egalitarian, and (6) libertarianism (including the free market and extemalities/spill over effects). 1. Consequentialism or teleological vs. deontological Consequentialism or teleological theory states that the “correct land-use policy or action is the one that generates the greatest quantity of value” (Beatley, 1994). In other words, the correct action is the one that maximizes what is good. In contrast, the 40 deontological theory focuses on what is morally right. It argues that what may maximize the greatest good, may not be the morally correct action. These two philosophical points of view are at the heart of the environmental justice debate. If building a nuclear plant in a poor neighborhood will maximize the land values in other neighborhoods, and if this nuclear plant results in the greatest good for the community, should this be done when some find this morally reprehensible? Planners with their master plans attempt to bring about the greatest benefits to a city and its citizens, but these decisions are sometimes based on the greatest good even when some find the results morally suspect. The example covered under the planning section illustrates this well. The tearing down of neighborhoods to build a highway, though good for the overall city, completely tore a neighborhood apart (Marshall, 2000). In this example it was debated that relocating these poor populations would be best for them, yet in retrospect, that was not the case. The idea of who defines what is good for a population, how is “maximum good” defined, for whom, and whose moral values will be addressed, complicates the issue even further. Because of the wide variations of answers to the previous questions, the debate rages on. From an economic and spatial perspective, the maximum good for an individual vs. the maximum good for a community may result in two completely different outcomes. Sprawl, the current result of many policies, has been blamed for wasting land resources, yet because it maximizes the profits of businesses and corporations, instead of communities, it has been dominating the current land use pattern. The same can be said of big box developments like Wal-Mart that maximize profit at the expense of social services and employees. 41 For urban planners, doing the morally correct action of addressing the issues of the underserved population may come under attack from businesses, individuals and communities that are trying to maximize the greatest good. 2. Utilitarianism This teleologically based theory has been the driving force of most contemporary land use policies (Beatley, 1994). It states that “goods and services should be produced and distributed so as to maximize the total welfare or aggregate social utility. The goal is to achieve the greatest possible balance of good over bad for society as a whole” (Liu, 2001). Although very similar to consequentialism, this theory addresses not just the good, but it mixes the bad with the good to look at the net effect. Using the previous example, the nuclear plant siting would have to be balanced with, for example, the health costs incurred by the neighborhood and the loss of productivity due to health reasons from this neighborhood. Although this theory doesn’t totally disregard harms done since this is weighed in the equation, if the net gain is positive, then harms done are acceptable, no matter how this harm is distributed. This means that benefit-cost analysis is done and human lives, health, and happiness are given a monetary value and treated as just another factor. Land is treated as a means to an end (Beatley, 1994) and current inequities may be exacerbated if a greater good is achieved at the expense of a few. Questions of value and how much factors like health and clean air are worth, keep the debate going. 42 3. Pareto Optimality and Efficiency of Markets Trying to address the harms done, pareto optimality is the “condition in which, through mutually agreeable economic transactions, a point is reached at which no firrther transactions can be undertaken that would make at least one person better off without making anyone else worse off” (Beatley, 1994). Thus, in equity terms, no one would lose, and at least one person would gain. Theoretically, this prevents greater harm, yet inequities may still be exacerbated. In reality, this concept is nearly impossible to practice so the modification of potential compensation of harms (Kaldor-Hicks optimality) adds practicality to this theory. Thus, Pareto efficiency states that those that gain will reimburse those that lose, yet still come out ahead. With an economic focus, this theory encompasses the idea that all those who may lose can get together and compensate the potential winner so that the action can be avoided. From the nuclear plant example, the poor neighborhood could potentially buy the land from the city to compensate for the relocation of the power plant and its output and thus compensating the rest of the city for the loss of energy. Or, the rest of the city would compensate the poor neighborhood for putting up with the nuclear plant and all the health issues that arise from it. In land use and economic terms, an economy is pareto efficient if there are “no unexploited gains to trade, no unexploited ways of increasing output with the same level of inputs, and no mix of products that do not reflect the preferences of consumers” (Liu, 2001). This assumes that the participants are rational, that there is perfect information, that one knows what and how the maximization of profit or utility is, and that no market failure conditions exist (Liu, 2001). Criticisms to this arise in the assessment and 43 evaluation of the worth of the land, the harms being done, and the impact on public health, safety, and welfare. In addition, the assumption that people are the best judges of what they want, can do something about it, and thus are able to guide the allocation of resources, is a flawed concept. As markets do not exist in a failure-free condition, this also invalidates this theory. Again, this principle does not address equity issues and does not improve the economic position of underprivileged groups. This theory is important as a guiding principle in the part of planning that helps with land use distribution issues and decision making. It is incorporated in various planning theories such as community input and just city where citizens are asked to participate with the assumption that the solution will reflect the preferences of the people. What would be a fair exchange for placing the beneficial or the noxious land use in a neighborhood? If a neighborhood already has low housing values, can the neighborhood be compensated with a park in exchange for having a nuclear plant located near by? Would health and land values be held at the same level as before? Since all issues cannot be weighed, one will not reach pareto efficiency, but compensating for the harms done attempts to make things more equitable. 4. Contractarianism This theory belongs under the deontological philosophy. It is morally based and provides guidance pertaining to the dignity and autonomy of human beings (Liu, 2001). At it’s core, contractarianism states that “each person is to have an equal right to the most extensive basic liberty compatible with a similar liberty for others [and that] social and economic inequalities are to be arranged so that they are both to the greatest benefit of the least advantaged [and that] offices and positions [be] opened to all under conditions of fair equality of opportunity” (Liu, 2001). Rawls, who developed this theory, felt that if everyone was involved in reaching a consensus without knowing theirs’ and other’s economic and social positions, they would pick what was best for the poor and thus minimize pain. Although this does not increase harm done to the disadvantaged, and they may get the greatest gain, it also does not necessarily reduce inequalities or work towards the elimination of these inequalities (Liu, 2001). Contractarianism can be found in a combination of planning theories. Post modernism and advocacy theories can be matched up to illustrate the equal voice and the addressing of the least advantaged. As a decision tool, it seems very hard to apply since one does know one’s social and economic position, but from a planning perspective, it does address the underserved population’s need, but it doesn’t necessarily address the core issues that allowed an underserved population to exisit. 5. Egalitarianism Similar to contractarianism, egalitarianism does work towards the elimination of inequalities. This theory holds that: a “All social inequalities are unnecessary and unjustifiable, and ought to be eliminated o “All men are equal — now and forever — in intrinsic value, inherent worth, and essential nature 0 “The concept of justice involves that of equality 45 0 “Social equalities need no special justification, whereas social inequalities always do 0 “All persons are to be treated alike, except where circumstances require different treatment” (Liu, 2001). Planning theories such as advocacy and just city are based on the principles of egalitarianism. Criticisms to this theory are usually levied based on efficiency. The greatest gain may not be achieved by the disadvantaged, yet inequity would be reduced. The moral stance of this theory has been embraced by many environmental movements. Not only do they want to prevent injustices by addressing “not in my back yar ” issues, but they go farther and push for the idea of “not in anyone’s back yar ” (Liu, 2001). 6. Libertarianism Similar to the two previous theories, libertarianism, based on Kant’s humanity principle that you treat others as an end, not as a means, states that everyone is equal, yet it emphasizes the freedom of action. This means that people may do as they wish, just as long as they respect the rights of others to do as they wish. Harm occurs if your freedoms are curtailed by others. The government would then take action in case of aggression or mm. In terms of land use harms, this philosophy, of minimizing harms is really the basis for the practice of zoning and other land use controls (Beatley, 1994). Since disputes will occur as to what a harm is and what restrains freedom, nuisance laws and land use ordinances establish the criteria for defining a harm. This raises conflicts when issues, such as environmental pollution, are difficult to assess in terms of value lost, affected health, or harm done. According to Beatley, many philosophers view that the 46 existence of public harm by private actions is the reason for government; the intervention and social constraints on private actions. Libertarianism is also the foundation for free markets and the conflicts of externalities. Free markets are based on the hypothetical ideology listed below and thus do not really exist. They are supposed to bring about efficient allocation of resources and assume the following (Beatley, 1994): o No one can increase or decrease the price of a good due to their control of the available share by restricting supply or demand. 0 All have firll information regarding quality of goods and value worth of the exchanges. o All are self interested actors that are assumed to be rational wealth- maximizers. o All goods and services have no externalities or spill over effects on others. 0 The costs of the transactions are all either equal or cost free. Critics of free markets point to the externalities ignored, the unaddressed equity issues, and the impossible valuation of resources such as clean air. Adam Smith’s invisible hand explaining fiee markets is refuted by Alex Marshall, who contends that for this to happen, there is an invisible arm of government that has set all the infrastructures such as roads, in place (Marshall, 2000). The issue of externalities and spill over effects can occur when free market costs don’t take into account public expenditures such as health costs due to industrial pollution, water filtration systems to clean up industrial residue, acid rain effects, etc. 47 These unintentional impacts are not taken into account into the original cost of the free market goods and thus the public ends up picking up the tab. Summgy These 6 philosophical theories show the various points of view regarding justice and equity and how they can affect the decisions to be made regarding land use. Depending on the one used, the results can vary significantly and yet be considered equitable by some portion of the population. Since decisions regarding land use generally result in the building of permanent structures and uses in specific locations in the urban landscape, it is important to understand how p0pulations are affected. Since populations have greater mobility than the land use, how does that affect their final relationship to the land use in the urban environment? In other words, who can or cannot move away from the noxious land use, and is it an issue of population shifting due to land use development, or is it land use development that determines what populations live there? The following section covers briefly theories and literature on the spatial distribution of land uses and population. Locational Theories (Also known as spatial economics, regional science, urban and regional studies, urban economic theory, location theory and economic geography.) This section looks at the spatial distribution of land uses and population and how they anived at the place they are today. These theories and effects try to explain past and current land use patterns. They are (1) Von Thunen’s theory, (2) externalities, and (3) population location. 48 1. Von Thunen — theory of agricultural land use. Although this theory was originally used to explain agricultural land uses, it is applicable to current urban land uses. It states that land within an urban area is allocated according to the rent that the competing users are able and willing to pay (Liu, 2001). This theory explains why the monocentric theory of city growth shows spatial patterns with class divisions. It is the competing users who are unwilling to pay the same amount for neighborhoods with higher minority and poor populations, thus the segregated neighborhoods emerge. 2. Extemalities — both in land use and social a. Land use — if industry increases pollution, this can drive the population away from that site. This effect can occur over time, and although it can be changed or reversed due to a cleanup effort or new technology, this increases social cost. b. Social — if racial discrimination exists, once there is a predominant race that has moved into a neighborhood, it can quickly change the entire neighborhood. This is known as neighborhood tipping. 3. Population location Population location or distribution has been described by the Tiebout model. This model predicts that people choose a place to live based on it satisfying his/her preference pattern for public goods. This means that individuals have freedom to live where they want to and thus choose their living environments. This assumes that an individual has perfect knowledge of the community, free mobility, no restrictions, and no externalities exist. This model was supported by 49 empirical data and the study showed that a better package of goods (i.e., neighborhoods with parks rather than industry) increases housing costs even if race is taken into account (Liu, 2001). Another study that looked specifically at population settlement patterns in response to toxic facilities, found that the disproportionate siting of toxic facilities mattered more than minority move-in (Pastor et al., 2001). This brings back the question raised earlier regarding parks and population shift. Although no studies substantiated this, the question was made, “who are we fixing our parks for” (Harnik, 2000). Since a better package increases housing costs, does this force a minority move-out? Conclusion As Liu and other authors have stated, there does not seem to be a consensus on a single specific theory, but many of the theories reviewed, can offer some explanations for the current state of our land use patterns and for the continual controversies raised by environmental justice cases (Liu, 2001). Depending on which theories of planning one picks, what decision-making philosophies and definitions of equity and justice one holds, and which locational theories apply to the current urban environment, these combinations will result in different policies and have widely varying consequences for each population. In relation to park and park policies, the theories reviewed attempt to establish guidelines for planners to arrive at the most equitable and best solution. In the realm of 50 positivism, the comprehensive rational theory and the critical planning theory try to use scientific orderly thinking to guide the solution. To challenge this century-dominating paradigm (positivism), phenomenological perspectives can be seen in the theories of advocacy, feminism, postmodernism, communicative, and the just city and try to bring the individual perspective into the park planning solutions. In addition, the question of what or how one defines equity is complicated with how one goes about bringing an equitable solution for all. The review of the justice theories gets specifically into this debate. Consequentialism, utilitarianism, and pareto optimality go for the greatest good while minimizing the harms done. Minorities and the disadvantaged are not well represented in these theories. Contractarianism, egalitarianism, and libertarianism take into account the issue of equity and begin to question actions that harm anyone, regardless of gain. With the diversity of theories that contain differing concepts of justice that are in conflict with one another, someone will always feel that there has been an injustice being made. Because of this disparity in views and guiding principles, today’s planners need to rely on their professional’s ethical stance, though there are still many unspecified values and undefined terms that result in differing outcomes. Studies like this dissertation attempt to understand if injustices exist, what type of injustice exists, and why it might exist. The theories and principles reviewed are valuable in shedding light on a very complex and value laden issue. The review of these theories was instrumental in selecting and shaping this study. The hypotheses evolved from a desire to understand how current planning documents such as the park master plans influence the community that they serve. Understanding 51 the various definitions and views of equity helped shape the data collection so that it would follow the needs-based definition that aligns itself well with the advocacy theory. The values implied by the Planners’ ethical stance were substantiated by the deontological justice theories, and in lieu of the population location theories, force the review of current planning practices to insure the desired outcomes. Although this study will only look at a specific outcome of the park planning policy, it is hoped that through the understanding of resource expenditure, awareness of the inequities that may exist can be corrected. 52 CHAPTER 4 — LAN SING’S DEMOGRAPHICS AND PARKS Introduction The purpose of this chapter is to better understand the current state of Lansing’s demographics and its park system. This is critical since this dissertation will use specific population groups in the city of Lansing and selected parks fiom the overall park system as a case study. In addition, two parks master plans (1995-2000 and the 2000-2005) are being reviewed and analyzed in this study. This chapter is divided into two main sections, the first one being the description of Lansing’s demographics and the second one concentrates on its parks. While the demographic section generally illustrates population trends, the park section will review the park history and the Department of Parks and Recreation’s master plans that have helped to shape the park system that is in place today. Throughout these sections, the variables used in this study are defined. These include race, ethnicity, income, neighborhood parks, park assets, and catchment area of these parks. Demographics Introduction This section shows the overall population trends that are taking place specifically in the City of Lansing with selected comparisons to Michigan and the nation. Overall population counts, racial and ethnic profiles, and poverty levels are explained. This 53 section also defines the following population variables used in this study: race, ethnicity, and income. Population Counts. Race. and Ethnicity Figure 1 shows that Lansing experienced a sustained population growth between the early I900S and thel 9705. Since then, the population has been slowly declining and has dropped from an all time high of 131,506 people in 1970 to an estimated 116,941 persons in 2004. Lansing Population Populatio 9.93.33- §§§§§ 1880 1890 1900 1910 1920 1930 1940 1950 1960 1970 1980 1990 2000 2004 Year Figure 1 — Lansing Population (Commission, 1954), (Development, 2000), (Bureau, 2005) This decline in population is not unique to Lansing. Between 1990 and 2000 only three cities in the state of Michigan with populations over 100,000 saw an increase (Grand Rapids, Sterling Heights, and Ann Arbor) (Bureau, 2006). The remaining five cities with populations over 100,000 (Detroit, Lansing, Flint, Warren, and Livonia) experienced an average decline in population of 6 percent. During this period, the overall state 54 population increase was only 7 percent (Thornton & Weissert, 2002) compared to the nationwide growth of 13.1 percent (http://quickfacts.census.gov/qfd/index.htrnl). Although the overall population in Lansing is decreasing, its diversity is increasing. Figure 2 shows the steady growth of the Black and Hispanic populations (as a percentage) since the 1970s. Information on the Hispanic population collected by the census bureau was not available in a separate format before this date. Lanelng'e Racial and Ethnic Profile Percent of Population 1950 1960 1970 1980 1990 2000 Yeere [- White I Black a Hispanic 3 American Indian ] Figure 2 — Lansing Demographic Profile (Bureau, 2005). Lansing experienced a 28 percent growth of Hispanics between 1990 and 2000, but in the mid-Michigan area (includes the metropolitan areas of Ann Arbor, Benton Harbor, Detroit, Flint, Grand Rapids-Muskegon-Holland, Jackson, Kalamazoo-Battle Creek, Lansing-East Lansing, and Saginaw-Bay City-Midland), the growth of this group varied fi'om 18 percent to 153 percent. Grand Rapids (153 percent) and Benton Harbor (113 55 percent) have seen the overall greatest grth in this population group, with Saginaw only showing a grth of 18 percent (Thornton & Weissert, 2002). The Black population is also experiencing growth in Lansing. Between 1970 and 1990, the Black population doubled in size (from 9.3 percent to 18.6). In the 2000 census, the Lansing Black population grew to 21.9 percent. Because of the significant changes in both of these two dominant minority populations, this study will use Whites, Blacks, and Hispanics as population variables. The Asian and the American Indian minorities comprise less than 3 percent of the population. Blacks and Hispanics experience discrimination differently and, therefore, these two populations will be analyzed separately. Blacks, which may contain Hispanic Blacks in the overall count, usually experience greater discrimination, as an overall group, compared to Hispanics. Hispanics, although they may also contain Blacks in the overall count, also have very light skinned members and thus seem to assimilate better in the White majority. “Usually, the lighter-skinned people, such as those whose features most like whites, are treated less harshly and receive less discrimination” (Thornton & Weissert, 2002). Poverty/ Income Although Lansing’s population is experiencing an increase in racial and ethnic diversity, the percentage of individuals who are living below the poverty line is on the decline (see Figure 3). 56 Percent of Individuals In Poverty I Lansing Total I: MchiganTotal I US Total 1989 1979 1989 1999 Years Figure 3 - Percent of Individuals in Poverty (Bureau, 2005; Wikipedia) (Lansing data came from the Census Bureau 1990 and 2000 SF3 Poverty tables). While this decline in poverty is a positive trend, the fact that almost 17 percent of the population is living below the poverty level makes for a large percentage of the population that is in need of public services. According to the 2000 census (see Figure 4), families in Lansing falling below the poverty line encompass 13.2 percent of all families, compared to 16.9 percent of individuals. Individuals under the age of 18 and living in poverty make up 23.2 percent of that population group, while 9.0 percent of the people who are 65 and older are living below the poverty line. 57 Percent of Popuiatione below the Poverty Line - 2000 Census .lLansing‘iii iDMchigan‘Xi IUS% Families hdivlduals Lhdef 18 Over 65 Figure 4 — Percent of Populations below the Poverty Line based on 2000 Census. This poverty information is based on the poverty levels set by the national Office of Management and Budget, which in turn, is based on complicated formulas that take into consideration, income, individuals, families, the Consumer Price Index, sex, food prices, and nutritional diet recommendations. With these guidelines, the census bureau uses the population information and 48 poverty thresholds to determine the number of individuals and families in poverty (Bureau, 2006). This leads to multiple income numbers representing poverty. Poverty varies by population type (age, household, individual, etc.) and it is not defined specifically by household income. Figure 5 shows the overall household income for both Lansing and Michigan. 58 Percent of Household Income in Lansing and Michigan in 1999 $200,000 or more J . $150,000 to $199,999 4' $100,000 to $149999 — ML afiR';ZJ‘t-¥‘Jki II . $75,000 to $99,999 ‘ 550.000 to 574.999 _- gum ”a“, H naming $35,00010$49,999 _ ‘ , _ 7‘ - .. lMichigan Household income $25,000to$34,999 Jan -_ o , ‘ $15,000 10324.999 ‘ - A ' . - - new $10,000 to $14,999 Less than $10,000 15 20 25 Percent Figure 5 — Percent of Household Income in Lansing 1999. Data source: Census Bureau 2000 census, SF3 — DP3 Profile of Selected Economic Characteristics. Overall, Lansing has a higher percentage of its population earning under $50,000 and a lower percentage of its population earning over $50,000 than the state percentages. Of the households in Lansing, 19.1 percent earn less than $15,000. This economic picture of Lansing shows a city with a significantly lower median household income than the rest of the state. The median household income in Michigan is $44,667, while the median income in Lansing is $34,833. Recognizing that populations of lower socioeconomic status need and use more social services, and that people in poverty are considered underserved populations, this study will use poverty levels as a determinant to place people into the underserved population category. The two population groups will be Above Poverty level and Below Poverty level. 59 Demogr_aphic Summary This section established the race and ethnicity variables in this study as Whites, Blacks, and Hispanics and the income variables were set at Above Poverty level and Below Poverty levels. The population of Lansing was very homogeneous before the 1970s. Today, there is a greater disparity in incomes and a greater diversity in race and ethnicity. This population shift creates different needs and expectations due to the nature of the emerging population groups. With this information, the following review of the park system and its policies will help to give a good, broad understanding of the issues facing the Park Department in their efforts to address the needs of the current shifting population. Parks Introduction This section covers issues that concern the City of Lansing’s park system. It encompasses the history of Lansing parks, the parks master plans, and then it focuses directly on the neighborhood parks. Under the neighborhood park section, discussions of assets and catchment area are undertaken and all park related study variables are defined. History of Lansing Parks Lansing was first settled in 1837 and became incorporated in 1859. By 1889, only two parks existed and one of them was formed from an abandoned cemetery. Only one additional park would be added by the time the first master plan for the City of Lansing was created in 1922. Previous to that, home-rule was established in Lansing in 60 1912 and a City Planning Commission was formed in 1920 with one of its active members being both the Superintendent of Parks and the City Forester. This commission requested a comprehensive city plan to be done that year by Harland Bartholomew, a city planning engineer from St. Louis, Missouri, and by 1922, the final report was completed. This report was very critical to the existing conditions of Lansing in the 19205 (Bartholomew, 1922). The report stated that the planning of the city was deficient in the reservation of space for a central square that contained the capitol. “There was not generous provision of open spaces for state buildings, no placing of streets for impressiveness, no reservations of native woodland, and no appreciation whatever of the value of the river and riversides as public property. As a consequence of this unfortunate lack of vision Lansing is now a most ordinary city (Bartholomew, 1922).” Although Bartholomew was highly critical of the development of Lansing, he felt that the park system at the time was “of more than ordinary distinction.” This was due to the amount of lands donated toward the park system, although not yet developed. The recommendations of the 1922 master plan related specifically to parks were as follows: 61 Table l - 1922 Master Plan Recommendations 1. Develop facilities for organized play. This included maintaining and adding playgrounds, community centers, and playfields. 2. Extend the park system to serve more people. High-use neighborhood parks of about 20 acres in size need to be acquired within the city. Extended outlying parks of a more naturalistic nature should be reserved along the riverfront. Riverfront property also needs to be added in as large a quantity as possible in the center of town and kept for scenic purposes. 3. Connect all parks with scenic drives. This was expected to occur specifically along the river edges, but existing streets were to be updated that connected interior neighborhood parks. 4. Develop small parcels throughout the city to add dignity and character to the capitol city. 5. Create cooperation between social agencies to help in the location of corrnnunity activities. Figure 6 shows a plan of the proposed neighborhood districts that Bartholomew felt needed additional park lands. Figure 7 shows the proposed parks and the connecting “pleasure driveways” that were envisioned for the Lansing park system in 1922. 62 OF I G- IGAN SHOW met-mp PARK. pm Mo;- 1'»:- N C I C. ‘ILA. M ./ CITY PIAN WI”: SAD" 1.01.118 1971. “LELAND IAITHOLOMIW DISTRIBUTION 01’ POPULATION m District in which neighborhood park may be developed I “ District needing neighborhood park 4’ 13 3 A a. / / g e E a. .8 g - ”g 3°51) .5 _ “E g 3 3 3‘ in I: ‘e’ '8 8 m '9; g g 2 '5 e P- .22 'E c .- W E o :3 TIEU i t .51" 5:: ram “D II IIIEBDIBDGDBDDDB .- 'EEEfiamggfiaa-i mwhmna .. m9 IIIG ”.5 lellEillllEElEii 811g; ' Mim~mm " NJ i'.l iii 51E .. , 5:1" i . ‘1 _""'m-¢ Fm— "In-run— L?" A r Him ”I \\§1 Figure 6 - 1922 Neighborhood Park Districts — Bartholomew 63 was; 2:32.— vomoaok— I Engages I .8885 cram e 29:92 Ease EU a 95m 3.3m 5m— m5Q. .52” 3.32.05 25.. E0 Zuionorhdtd 024.32: 96523 “85 b I U— 3% K iHIH I .012 _ 4 ho 2. <1:- 0 Figure 7 - 1922 Proposed Park System — Bartholomew In 1938, based on a request from City Council, Bartholomew was asked to do an updated Comprehensive City Plan for Lansing (see Figure 8). In this report, Bartholomew reports that the city has made most of its improvements following the master plan, and that most of the park development recommendations listed in the 1922 report are now a reality (Bartholomew, 1938). This early city planning effort and the subsequent master plans that have followed, have left Lansing with the distinction of having “more parks per capita than any other city of its size” according to Eric Reickel, Lansing’s past director of Parks and Recreation (Andrejevic, 1995). In 1944, the Park Board, a citizen-based advisory board that assists the Parks and Recreation Department, was officially established. Its members serve a four-year term and are appointed by the Mayor and approved by City Council. There are many boards and clubs today that also advise, support, and participate in various ways within the Parks Department. Some of them are: baseball advisory board, fiiends of Cooley gardens, Gier center advisory board, and the river and waterfront development boards. Input fi'orn all of these boards is gathered by the Parks and Recreation Department in its effort to continue to maintain and develop the Lansing’s park system. Lansing currently has a park system containing cemeteries, golf courses, and three different types of parks. There are 106 parks in the system and 60 of them are classified as neighborhood parks. In 2000 the total park acreage in Lansing was 1,765.19 acres with an average park size of 16.3 acres (Lansing Parks and Recreation Department, 2000). This gives Lansing a park density of 14.8 acres per 1,000 residents (using the 2000 population count of 119,128). In a study done by the Trust for Public Land, park 65 densities were determined for the 50 largest cities in the country using 2002 data. 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