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首页> 外文期刊>Journal of Contemporary Water Research and Education >Institutional Constraints to Collaborative Ecosystem Management within a Wetlands Conservation Partnership
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Institutional Constraints to Collaborative Ecosystem Management within a Wetlands Conservation Partnership

机译:湿地保护合作伙伴关系中协同生态系统管理的制度制约

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The resource management paradigm is in a state of transition from the conventional sustained yield and multiple use management paradigm toward ecosystem management (Cortner and Moote 1999; Yaffee 1999; Chapin et al. 2010; Folke et al. 2011). The sustained yield and multiple use management paradigm was based on the view of humans as separate from nature and a belief in human mastery over nature (Cortner et al. 1998). This paradigm also relied on expert science and centralized institutions with the aim of enhancing efficiency and output maximization of economically valuable resources, including timber and water resources (Daniels and Walker 1996; Yaffee 1999). This over-emphasis on the predictable supply of commodity outputs has resulted in biodiversity crisis (Grumbine 1994; Chapin et al. 2010). Since the concept of sustainable development emerged in the 1980s, the paradigm of the ecosystem management has been gaining recognition as an alternative to the conventional paradigm (Cortner and Moote 1999). The turn toward ecosystem management in recent decades is a response to the biodiversity crises created by the narrow focus of conventional management approaches, as well as changing societal values, and new scientific insights from recent disciplines such as conservation biology and landscape ecology (Grumbine 1994; Cortner and Moote 1999).Ecosystem management is a holistic approach to resource management that addresses the sustainability of human and ecological communities (Endter-Wada et al. 1998). In this regard, ecosystem management departs from the narrow focus of the conventional paradigm by emphasizing the pursuit of integrated management goals that cover social, ecological, and economic dimensions (Keogh and Blahna 2005). As Stein and Gelburd (1998, 74) have succinctly stated, “The goal of the ecosystem approach is to restore and sustain the health, productivity, and biological diversity of ecosystems and the overall quality of life through a natural resource management approach that is fully integrated with social and economic goals.” The ecosystem management paradigm considers humans an integral part of nature (Folke et al. 2011), and it recognizes the uncertainties that characterize the dynamic interaction between social and ecological systems (Yaffee 1996). In view of these uncertainties, ecosystem management highlights the need for interdisciplinary science and adaptive management processes (Cortner et al. 1998; Butler and Koontz 2005). Ecosystem management also emphasizes a bioregional approach that considers resource management issues across multiple political and administrative boundaries (Lee 1999). Examination of resource management goals across multiple spatial and temporal scales reveals significant conflicts and other organizational challenges that cannot be managed through conventional top-down institutional mechanisms (Daniels and Walker 1996; Bonnell and Koontz 2007). In this regard, collaborative decision-making is increasingly relied upon as a means of dealing with conflicts among the multiple stakeholders in ecosystem management (Imperial 1999; Wondolleck and Yaffee 2000; Keogh and Blahna 2005).Besides the influence of the ecosystem management paradigm, the turn toward collaborative resource management is also fueled by the increasing devolution of decision-making authority and implementation responsibilities to state and non-state actors at lower administrative levels (Steel and Weber 2001). In this regard, co-management or collaboration can be seen as a form of governance (Carlsson and Berkes 2005), defined as “the whole of public as well as private interactions to solve societal problems and create societal opportunities” (Berkes 2010, 491). Collaborative decision-making entails the use of multiparty and multidisciplinary approaches to problem-solving (Yaffee 1996). Keogh and Blahna (2005) contend that collaboration goes beyond public involvement. Collaborative processes are characterized by inclusiv
机译:资源管理范例是从传统的持续产量和多次使用管理范例转向生态系统管理的状态(Cortner和Moote 1999; Yaffee 1999; Chapin等,2010; Folke等,2011)。持续收益率和多次使用管理范式是基于人类与自然分开的观点,以及对人类掌握的信念(Cortner等人1998)。该范式还依赖于专家科学和集中机构,旨在提高经济上有价值的资源的效率和产出最大化,包括木材和水资源(Daniels和Walker 1996; Yaffee 1999)。这种过度强调可预测的商品产出供应导致生物多样性危机(Grumbine 1994; Chapin等,2010)。自20世纪80年代可持续发展的概念以来,生态系统管理的范例一直在获得传统范式的替代方案(Cortner和Moote 1999)。近几十年来转向生态系统管理是对传统管理方法的狭隘焦点,以及改变社会价值观的狭隘焦点,以及近期学科的新科学见解(Grumbine 1994; Cortner和Moote 1999).Ecosystem管理是资源管理的整体方法,解决了人类和生态社区的可持续性(Endter-Wada等,1998)。在这方面,生态系统管理通过强调追求涵盖社会,生态和经济方面的综合管理目标(Keogh和Blahna 2005),从传统范式的狭隘焦点离开。作为斯坦因和戈尔伯德(1998,74)简明扼要地说:“生态系统方法的目标是通过完全的自然资源管理方法恢复和维持生态系统的健康,生产力和生物学质量。与社会和经济目标融为一体。“生态系统管理范式认为人类是自然的一个组成部分(Folke等人2011),它认识到了对社会和生态系统(Yaffee 1996)之间的动态互动的不确定性。鉴于这些不确定性,生态系统管理突出了对跨学科科学和自适应管理进程的需求(Cortner等,1998; Butler和Koontz 2005)。生态系统管理还强调了一项生物协调方法,以跨多个政治和行政校长(LEE 1999)考虑资源管理问题。在多个空间和时间尺度审查资源管理目标揭示了无法通过传统的自上而下的制度机制管理的重大冲突和其他组织挑战(Daniels和Walker 1996; Bonnell和Koontz 2007)。在这方面,合作决策越来越依赖于处理生态系统管理中多利益攸关方(1999年帝国帝国帝国帝国; Wondolleck和Yaffee 2000; Keogh和Blahna 2005)的一种手段。在生态系统管理范式的影响下,还通过在较低的行政一级(钢铁和韦伯2001)下,决策权限和执行责任的日益发展促进了协作资源管理的转向。在这方面,共同管理或合作可以被视为治理(Carlsson和Berkes 2005)的形式,被定义为“全部公共和私人互动,以解决社会问题并创造社会机会”(Berkes 2010,491 )。协作决策需要使用多党和多学科方法来解决问题(Yaffee 1996)。 Keogh和Blahna(2005)争辩说,合作超出公众参与。协作过程的特点是包含的特征

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