This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Economic Benefits of Preserving Natural Areas Bonnie G. Colby1 ABSTRACT The focus of this paper is on values that can be quantified in dollar terms. It is important to acknowledge that natural preserves-such as grasslands and riparian areas-have psychological, cultural, and spiritual values that may be just as, or more, important than the values which economists are able to quantify. While economists have developed methods to quantify natural resource values beyond the direct use of resources for commercial purposes and recreation, even these modern economic methods cannot capture the full range of benefits that natural areas provide. QUANTIFYING THE ECONOMIC VALUE OF NATURAL AREAS The notion of measuring the value of nature in dollar terms may seem distasteful. Money is a cold unit by which to characterize grasslands, clean air, scenic views, open space, endangered species and other amenities which are important to our quality of life. Nevertheless, there are some valid reasons to cast the value of nature in monetary terms. In times of tight government budgets, public policies require closer scrutiny of how taxpayers dollars are spent. Consequently, when an agency is considering spending money to acquire or to manage land for a natural preserve it typically must document the benefits anticipated from the preserve, as well as the costs of leaving the land in a natural state (including the foregone benefits of more intensive land uses). Over the last five years, popular concern regarding the potential impact of government activities on private property values has swelled. This has led to more use of economic analysis by public agencies because they are subject to added scrutiny of the impact of their proposed regulations, land acquisitions, and land management plans on private property. For instance, Arizona statutes now require review of proposed state agency rules by the Governor's Regulatory Review Council and the agency must submit an economic impact statement on the proposed action to the Council for their consideration. Other states have passed stronger measures to prevent takings (the diminishment of private property values caused by government action). Congress has considered such legislation as well. These policies, which seek to protect private property, have the effect of increasing the pressure on agencies to document the costs and benefits of their activities, including acquisition and management of lands as nature preserves. Private firms and environmental organizations also must weigh economic costs and benefits associated with natural areas. For instance, to obtain a final certificate of a water right for instream flow purposes in Arizona, the holder of the right (a federal agency or the Nature Conservancy, for example) must document the benefits of preserving streamflows. Even in instances where examination of economic values is not required, it still is a useful exercise for an environmental 1 Agricultural and Resource Economics, University of Arizona, Tucson AZ. 337 organization or a public agency to weigh the economic costs and benefits of setting aside a natural area for wildlife and recreation. This paper briefly reviews the different types of economic values associated with natural preserves. Strong economic arguments can be made for preserving natural areas for recreation and wildlife habitat and for maintaining the aesthetic appeal that wide open spaces have in the American West. TYPES OF ECONOMIC VALUES GENERATED BY NATURAL AREAS Direct Benefits to Recreationists Many natural areas in the West are heavily used for recreation and generate increased economic benefits as population and demand for outdoor recreation grows. Urban westerners demand outdoor recreation opportunities and place a high value on them. A comprehensive survey of economic benefits to recreationists at outdoor recreation sites in the western United States indicates recreation benefits of $18 to $27 per visitor day for general hiking and wildlife viewing (Walsh et al, 1992). Data collected for southern and central Arizona riparian areas indicates values per visitor (in a one-time contribution) of $65 to $102 to maintain the quality of the Hassayampa River Preserve, and $65 to $97 to protect the riparian ecosystems of the San Pedro Riparian National Conservation Area and the Nature Conservancy's Ramsey Canyon Preserve (Kirchoff, 1994, Crandall, Colby and Rait, 1992). These values lie far above the nominal fees charged to enter federal and state parks and recreation areas. ContributiQn to Local Economies In addition to economic benefits to the recreationists themselves, small businesses and outlying communities depend on spending by outdoor recreationists. Outdoor recreation brings millions of dollars each year into the Arizona economy. Restaurants, retail stores, motels, bed and breakfasts, gas stations and other businesses benefit from preservation of attractive outdoor recreation sites. Tourism linked to outdoor recreation is a particularly important component of the economy of rural Arizona, including Arizona's tribes and their reservation economies, many of which contain Arizona's last unspoiled natural areas. Bird-watching opportunities in Cave Creek, Madera Canyon, Ramsey Canyon, and other sites are known worldwide and bring relatively high-income visitors to these parts of Arizona. In the Sierra Vista area alone, expenditures by visitors to prime bird-watching areas stimulate $3 million per year in local economic activity (Crandall, Leones and Colby, 1992). The San Pedro Riparian National Conservation Area and the Nature Conservancy's Ramsey Canyon have annual visitation of approximately 12,000 and 26,000 visitor days, respectively. Several factors affect the extent to which natural areas contribute to the economy of nearby communities. Local economic stimulation is increased as the percentage of nature preserve visitors that are non-local increases and as visitors stay overnight in the area (instead of just making a day visit) and thus spend more on lodging and meals. As the local economy diversifies, dollars spent by tourists circulate more times within the local area and further stimulate local business activity, before "leaking" out of the local economy as payments for goods and services produced elsewhere (Crandall, Leones, and Colby, 1992). 338 Habitat Preservation Natural areas preserve wildlife habitat and can help avert a species becoming listed as threatened or endangered, thus averting the complex and costly formal Endangered Species Act processes for designating critical habitat and developing species recovery plans. These averted costs and conflicts are a notable benefit of nature preserves, a benefit that can be appreciated by examining the enormous costs incurred in the Pacific Northwest over salmon and spotted owl issues. Indeed, the threat of a species becoming listed as threatened or endangered and of triggering the formal Endangered Species Act (ESA) process has proved a powerful incentive for setting aside habitat for species. ···.··· Water Protection Natural preserves that maintain the ecological integrity of watersheds can protect water quality and stream flow levels. Preserving the quality and volumes of flows reduces the costs of complying with surface water quality standards for downstream towns and industries which discharge into rivers. High quality stream flows from protected natural areas provide economic benefits to these dischargers by averting or postponing the costs of providing more sophisticated sewage treatment (and the huge capital costs of upgrading treatment facilities) to remain in compliance with surface water standards. If streams become degraded, downstream pollutant loads become more concentrated and the probability of surface water quality standard violations increases, as do costs and fines for non-compliance (Colby, 1994). Private Property Values The value of private property located adjacent to or near natural open space preserves is enhanced when water quality, open space and wildlife habitat are protected. Studies elsewhere in the U.S. indicate a twenty percent increase in private property values due to water quality protection in nearby water bodies (Young, 1984). In the Tucson area, economic studies document an increase in property values associated with proximity to wildlife habitat, such as washes and riparian areas (King, White and Shaw, 1991). Southern Arizona homes and resorts that are located adjacent to open spaces (such as national forests and monuments) enjoy a property value premium associated with the natural areas. The growth of residential construction in the Sonoita/Patagonia area, and the accompanying rise in property values, is an example of the positive influence of attractive open space on private property values. Values Unrelated to Direct Use People who don't actually visit natural areas still benefit from them and are willing to contribute to their preservation. Economists divide these nonuse values into three categories, based on the underlying motivations. Existence value stems from knowing a particular species will continue to exist in a natural state. Option value is based on a collective desire to keep options open for the future. Option value emerges when faced with an irreversible decision-do we develop a natural area for agricultural or urban use-altering the area forever, or do we leave it as it is for now, knowing it can always be developed in the future? Policy choices to preserve a species rather than let it become extinct (irreversibly lost), also exemplify the option value concept. Bequest value stems from wanting to preserve natural areas and wildlife for the future, for our own heirs or for future generations in general. These nonuse values represent substantial economic benefits associated with preserving endangered species, wildlife habitat, and unique natural sites. These preservation values (also termed "nonuse or passive use" values) have been affirmed by the courts as a valid component of economic costs and benefits (State of Ohio v U.S. Department of Interior, 880 F.2d 432 (D.C. Circ. 1989)), and are incorporated into assessments of proposed federal regulatory actions as well as in 339 assessing liability for environmental damages under CERCLA. These values are expressed through donations of time and money to wildlife and environmental organizations, and through political support for species recovery programs and for laws and policies that preserve habitat and prevent environmental degradation. Examples of the application of nonuse values to examine environmental policies in Arizona include the Federal Bureau of Reclamation's Environmental Impact Statement for Operations of Glen Canyon Dam (1995) and an earlier federal study on changes in air quality and visibility in the Four Corners region. Recent studies of preservation values associated with nature preserves in the western United States indicate economic benefits of $15 to $80 annually per household located in the general region of the site (Sanders, Walsh and Loomis, 1990 and Brown, 1991). Studies in Colorado, Canada, Wyoming and Alaska indicate $40 to $80 per non-user household in cities located within a few hours of nature preserves. These nonuse values may seem esoteric (less tangible than spending by recreationists, for instance), but they are real values and economic studies on natural areas around the West suggest these values are even larger than the direct values people place on their recreational use of such areas. IF NATURAL AREAS ARE SO VALUABLE, WHY DON'T THEY RECEIVE MORE PROTECTION? Despite the numerous economic benefits provided by natural areas, they are not .. supplied" by market forces to an extent commensurate with the benefits they provide. This .. market failure" occurs for several reasons. First, benefits provided are real, but often not readily "collectible." There is no easy voluntary way to collect money for acquiring open space and wildlife habitat. Only nominal fees are charged to enter parks and recreation areas. Recreationists' "true" values, their willingness to pay, are not collected by anyone. Of all the types of economic benefits described, the only money actually going into someone's pockets is dollars spent by recreationists. However, these expenditures are not a complete measure of the value of a natural area. Part of the .. collectibility" problem is the absence of a clear, well-defined constituency to collect money from. It requires a tremendous effort to raise money from a dispersed constituency through voluntary donations, as environmental groups do. Recreationists and environmental advocates are dispersed among the general population. They do not tend to be as identifiable and tightly organized as commercial users of land and water. Developers, farmers, ranchers, loggers, and mining interests have effective lobbies to promote their access to land and water. Another reason for the "collectibility" problem is free-rider tendencies. Once a preserve is established, many can benefit from its existence even though they made no donations to help establish the preserve. There also is a lack of information that handicaps protection of natural areas. In contrast to the benefits provided by nature preserves, the values of other land uses (industry, agriculture, subdivisions) are easier to measure, "collect," and recognize as an economic investment. There is plenty of information from the real estate market on the value of land in growing crops, houses, and golf courses, but very little documentation on the value of wildlife habitat and recreation areas. In response to the inability of the free market to supply nature areas to the degree justified by the benefits provided, two broad approaches are taken to acquiring land for recreational and environmental needs. First, private organizations such as the Nature Conservancy and Trout Unlimited buy land and water, using money they have raised from donors and investments. Second, public agencies acquire land and water. However, new public agency acquisitions have become difficult in times of tight budgets. Funds are tight for managing natural areas already held by federal, state, and local governments. A two-pronged approach involving both the private and public sector is necessary for improved 340 protection of natural areas. Private groups, such as the Nature Conservancy, can't do it all on their own due to the "collectibility" problem. State, local and federal agencies use tax dollars and need not rely on voluntary donations alone. Private-sector participation can be facilitated through favorable tax policies that encourage contributions of money, water rights, and land to non-profit wildlife and environmental organizations. Enhanced public-sector participation requires continued authorization and funding for federal, state and local agencies to acquire and manage natural areas. Cooperative strategies involving public-private partnerships are a hopeful approach that combines the strengths offered by public agencies with those of the non-profit sector. Examples include the Nature Conservancy's acquisition of land when it becomes available at the right price, at times when a public agency is not able to secure funds quickly enough to make a timely purchase. In many cases, the Nature Conservancy later turns the land over to a public agency, such as the BLM, for long term management, with the Conservancy eventually reimbursed for some or all of their acquisition expenses. SUMMARY To summarize, many (though not all) of the benefits provided by natural areas can be quantified in dollar terms. It is increasingly necessary to quantify these values in order to respond to increased scrutiny of public agency spending in times of tight budgets and to concerns over takings. The market forces of supply and demand do not provide adequate protection of natural areas, so continued involvement by public agencies and the non-profit sector is essential. REFERENCES Brown, T., "Water For Wilderness Areas," Rivers 2:311-325, 1991. Checchio, Elizabeth and Bonnie Colby. Indian Water Rights: Negotiating The Future. Water Resources Research Center, The University of Arizona, Tucson, 1993 (103 pp.) Colby, Bonnie G. "Benefits, Costs and Water Acquisition Strategies: Economic Considerations in lnstream Flow Protection," chapter in L. MacDonnell, editor, lnstream Flow Law and Policy, Natural Resources Law Center, University of Colorado, 1994. Colby, Bonnie G. "Applying Fair Market Value Concepts to Water Rights," Real Estate Issues 18:8-14, 1993. Crandall, K., Bonnie Colby and K. A. Rait. "Valuing Riparian Preserves: A Southwestern Case Study," Rivers 3: 88-98, 1992. Colby, Bonnie G. "Southwestern Water Values and Market Activity," Appraisal Journal 59:488-500, 1991. Colby, Bonnie G. ''Alternative Approaches to Valuing Water Rights," Appraisal Journal 57: 180-196, 1989. Crandall. K., J.. Leones, and B. Colby, "Nature Based Tourism and the Economy of Southern Arizona,"University of Arizona, Dept. of Agricultural Economics, 1992. King, D., J. White and W. Shaw, "Influence of Wildlife Habitat on the Value of Residential Properties," in: Wildlife Conservation in Metropolitan Environments, Columbia, Maryland: National Institute for Urban Wildlife, 1991. Kirchoff, S. "Estimating the Benefits of lnstream Flows: Case Studies in Arizona and New Mexico," Master's Thesis, University of Arizona, 1994. Moore, S, M. Wilkosz and S. Brickler, 'The Recreational Impact of Reducing the Flows of Aravaipa Creek," Rivers 1: 43-50, 1990. Sanders, L., R. Walsh and J. Loomis, "Toward Empirical Estimation of The Total Value of Protecting 341 Rivers," Water Res. Research 26:1345-1357, 1990. Walsh, R., D. Johnson, and J. McKean, "Benefit Transfer of Outdoor Recreation Demand Studies, 1968-1988," Water Res. Research 28:707-716, 1992 (no. 3). Water Intelligence Monthly and Water Strategist, published by Strat Econ Inc., Claremont, California. Young, E. "Perceived Water Quality and The Value of Seasonal Homes," Water Res. Bull., April, 1984. 342