首页> 外文期刊>BioScience >Comparing Ecosystem Goods and Services Provided by Restored and Native Lands
【24h】

Comparing Ecosystem Goods and Services Provided by Restored and Native Lands

机译:恢复土地和原生土地提供的生态系统商品和服务比较

获取原文
获取原文并翻译 | 示例
           

摘要

We determined the relative benefits for eight categories of ecosystem goods and services associated with native and restored lands across the conterminous United States. Less than 10% of most native US ecosystems remain, and the proportion that is restored varies widely by biome. Restored lands offer 31% to 93% of native land benefits within a decade after restoration, with restored wetlands providing the most economic value and deserts providing the least. Restored ecosystems that recover rapidly and produce valuable commodities return a higher proportion of total value. The relative values of the benefits provided by restoration vary both by biome and by the ecosystem goods and services of interest. Our analysis confirms that conservation should be the first priority, but that restoration programs across broad geographic regions can have substantial value. “No net loss” policies should recognize that restored lands are not necessarily equivalent to native areas with regard to estimated ecosystem benefits.nnHumans influence every ecosystem on Earth, leading to impairment of natural ecosystem structure and function (MEA 2005). Converting native land to row-crop agriculture, suppressing fire, diverting water flow, increasing nutrient and toxic pollution, altering global precipitation patterns and gas concentrations, and homogenizing and lowering global biodiversity are a few of the ways humans have altered ecosystems. North American forests, savannas, and grasslands have experienced substantial losses, whereas woody savanna, shrubland, and desert areas have expanded because of desertification and woody expansion into grasslands (Wali et al. 2002), inevitably leading to changes in ecosystem function.nnConserving native land cover is an important component of maintaining ecosystem structure and function. Preservation is not always a viable management option, because many regions lack sufficiently large undisturbed areas to sustain biota and ecosystem function without improvement. Therefore, restoration is an essential activity for modern land management and conservation (Hobbs and Harris 2001). Setting achievable goals for restoration policies covering broad regions involves not only defining ecological potential in the region but coupling that potential with societal demands and economic feasibility. Valuation of ecosystem goods and services can help managers estimate long-term economic feasibility (Costanza et al. 1997). This coupling of the success of restoration with the value of ecosystem benefits leads to a definition of restoration as “the process of restoring one or more valued processes or attributes” of an ecosystem (Kahn 1995). The restoration of specific ecosystem goods and services, in addition to merely restoring the native complement of species in an area, has thus become the focus of many restoration ecologists.nnEstimating some of the benefits of lands used by humans can be fairly straightforward, particularly when the commodities produced have market value (e.g., the annual value of crops produced per hectare) and when externalities are ignored. Ascribing an economic value to some ecosystem goods and services, by contrast, can be difficult (Kahn 1995, Costanza et al. 1997), and sectors of the economic community have criticized such valuation (Bockstael et al. 2000, Spash and Vatn 2006). Nonetheless, ecosystems provide some recognized benefits, and the valuation of these benefits could become a major tool for directing policy and making land-use decisions (Turner et al. 2007). Attempts to document the relationship between land restoration and the improvement of the supply rates of ecosystem goods and services have been made mainly in small-scale studies. We explore the hypothesis that the temporal trajectory of ecosystem goods and services supplied by restored lands varies across ecoregions and among the different goods and services. We test this hypothesis with respect to restoration across broad regions (i.e., continental), but some of the principles could be refined and applied also to specific restoration projects. We focus on the effects of restoration on ecologically based temporal trends in rates of benefit production from ecosystem goods and services, because that is an area where ecologists can provide useful information for use in future cost-benefit analyses.nnOur analysis involved four steps. First, we defined our ecosystem goods and services. Second, we defined restoration and created a “restoration index” to compare the value of native and restored lands. Third, we defined the ecoregions in our study and calculated the area of native and restored lands within each ecoregion. Last, we conducted a literature review to collect the data needed to parameterize our restoration index.
机译:我们确定了与整个美国本土和恢复土地相关的八类生态系统商品和服务的相对收益。在美国大多数本土生态系统中,只有不到10%的生态系统得以恢复,恢复的比例因生物群落而有很大差异。恢复后的十年内,恢复后的土地可提供31%至93%的本国土地收益,恢复后的湿地提供最大的经济价值,而沙漠提供的收益最少。快速恢复并生产有价值的商品的恢复的生态系统返回的总价值比例更高。恢复提供的利益的相对价值因生物群落和所关注的生态系统产品和服务而异。我们的分析证实,保护应该是第一要务,但是跨广泛地理区域的恢复计划可以具有重大价值。 “无净损失”政策应认识到,就估计的生态系统效益而言,恢复的土地不一定等同于本地。nn人类会影响地球上的每个生态系统,从而导致自然生态系统结构和功能受损(MEA 2005)。人类改变生态系统的几种方式包括将本国土地转为行作农业,抑制火灾,改变水流,增加养分和有毒污染,改变全球降水模式和气体浓度以及均质化和降低全球生物多样性。北美的森林,稀树草原和草原遭受了重大损失,而木质的稀树草原,灌木丛和沙漠地区由于荒漠化和木本植物的扩张而扩大(Wali等人2002),不可避免地导致了生态系统功能的变化。土地覆盖是维持生态系统结构和功能的重要组成部分。保护并非总是可行的管理选择,因为许多地区缺乏足够大的未扰动区域来维持生物群和生态系统功能,而无需改善。因此,恢复是现代土地管理和保护的一项必不可少的活动(Hobbs and Harris 2001)。为涵盖广泛地区的恢复政策设定可实现的目标,不仅涉及定义该地区的生态潜力,而且还需要将该潜力与社会需求和经济可行性相结合。对生态系统产品和服务的价值评估可以帮助管理人员估算长期经济可行性(Costanza等,1997)。恢复成功与生态系统效益的价值相结合,导致恢复被定义为生态系统的“恢复一个或多个有价值的过程或属性的过程”(Kahn 1995)。因此,恢复特定生态系统的商品和服务,不仅是恢复某个地区物种的原生补充,还成为许多恢复生态学家关注的焦点。nn估算人类使用土地的某些好处可能非常简单,尤其是当当忽略外部性时,所生产的商品具有市场价值(例如,每公顷农作物的年价值)。相比之下,将经济价值归因于某些生态系统产品和服务可能会很困难(Kahn 1995,Costanza等,1997),经济界的各个部门也批评这种估值(Bockstael等,2000; Spash和Vatn 2006)。 。然而,生态系统提供了一些公认的收益,这些收益的估值可能成为指导政策和做出土地使用决策的主要工具(Turner等人,2007)。主要在小规模研究中已尝试记录土地恢复与生态系统产品和服务的供应率提高之间的关系。我们探讨了以下假设:恢复土地提供的生态系统商品和服务的时间轨迹在整个生态区域以及不同商品和服务之间是不同的。我们针对广泛区域(即大陆)的恢复测试了该假设,但是可以对其中一些原则进行完善,并将其应用于特定的恢复项目。我们关注恢复对生态系统商品和服务的收益产生率的基于生态的时间趋势的影响,因为生态学家可以在该领域提供有用的信息,以供将来进行成本效益分析之用。我们的分析涉及四个步骤。首先,我们定义了生态系统的商品和服务。其次,我们定义了恢复并创建了一个“恢复指数”来比较原生和恢复土地的价值。第三,我们在研究中定义了生态区,并计算了每个生态区内的自然和恢复土地面积。最后,我们进行了文献综述,以收集参数化我们的恢复指数所需的数据。

著录项

  • 来源
    《BioScience》 |2008年第9期|p.837-845|共9页
  • 作者单位

    alter K. Dodds (e-mail: wkdodds@ksu.edu) is a professor in the Division of Biology at Kansas State University in Manhattan. Kymberly C. Wilson works for the Arizona Department of Water Resources in Phoenix. Ryan L. Rehmeier is an assistant professor of biology at Simpson College in Indianola, Iowa. G. Layne Knight works for the Kansas Department of Health and Environment in Topeka. Shelly Wiggam is a pollination ecologist who owns a prairie restoration consulting and implementation business in Manhattan, Kansas. Jeffrey A. Falke is a fish ecologist currently at Colorado State University in Fort Collins. Harmony J. Dalgleish is a postdoctoral researcher in the Department of Wildland Resources at Utah State University in Logan. Katie N. Bertrand is an assistant professor in the Department of Wildlife and Fisheries Sciences at South Dakota State University in Brookings;

  • 收录信息
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号