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首页> 外文期刊>Frontiers in Ecology and Evolution >Integrative Science to Achieve Long-Term Impact in Conservation: The Use of Participatory Mapping to Improve Trans-disciplinarity
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Integrative Science to Achieve Long-Term Impact in Conservation: The Use of Participatory Mapping to Improve Trans-disciplinarity

机译:整合科学在保护方面取得长远影响:使用参与式测绘改善跨学科性

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摘要

Biodiversity conservation is a major global issue (Sutherland et al., 2017). Conservation biology aims to identify and mitigate biodiversity loss through ecologically-centered planning (Salzer and Salafsky, 2006). Early conservation biology researchers recommended multi-disciplinary approaches to improve conservation (Soule, 1985), prompting inclusion of various disciplines to improve integrative approaches. A multitude of collaborations among social sciences and ecology resulted, combining theory and pragmatism in participatory approaches and action-research (Bennett et al., 2017).Environmental degradation is inherently about the way people value and act in an environment. While understanding and integrating social values (defined here as the values of a particular community or the cultural values and norms of society at large) is acknowledged as important in conservation (Norton, 2005; Jacobs et al., 2016), concepts are often poorly defined, operationalized or tested (Dennis et al., 2005; Liu et al., 2007). Poor assessment of social values limits achievements for effective conservation outcomes (Brennan, 2004). Recent re-conceptualizations of the relationships between social and ecological values have resulted in efforts to formalize and institutionalize integrated approaches (Chan et al., 2016; Teel et al., 2018). There is a need to better integrate local and indigenous knowledge with scientific knowledge in the value frameworks and to include multiple value sets including biodiversity and ecosystem services and functions (Díaz et al., 2015).The analysis of landscape values shows that people designate values through a range of frames (Plieninger et al., 2015; Luginbühl et al., 2016; Ernoul et al., 2018). The socio-political dimensions of management policy may be different from the ecological needs and management of species (Mathevet and Mauchamp, 2005). A science-engaged agenda that acknowledges social and cultural context of landscape management provides a scaffolding for effective planning (Turner et al., 2016). Conservation planning that integrates socio-cultural and ecological values identifies contingent social value-frameworks lighting pathways to potential solutions (Endter-Wada et al., 1998). Considering the way people value nature and their existing relationships with nature improves acceptance and implementation in conservation planning (Chan et al., 2016; Mathevet et al., 2018). Strategic sampling for participation that accounts for socio-geographic scale and value-frames within the social catchment (Wardell-Johnson, 2005) of the conservation plan identifies the range of voices and values upon which effective conservation depends (Ernoul and Wardell-Johnson, 2013). Thus effective conservation planning depends on a clear understanding of why, how, and when to elicit social value information in order to integrate socio-cultural values in the spatial dimensions at the landscape scale (Vimal and Mathevet, 2011).Participatory mapping of social values has been used in cultural geography (Ramirez-Gomez et al., 2016), conservation sciences (Ernoul et al., 2018), and landscape ecology (Brown, 2013) to incorporate human dimensions in landscape planning, modeling, and decision-support systems (Le Page et al., 2013). Participatory mapping provides a spatial platform to integrate knowledge about complex landscape situations (e.g., climate change, urban sprawl, tourism development, regional planning, landscape management etc.) (Alhamwi et al., 2017), thus identifying a range of values within a landscape and revealing context in representations. This platform integrating socio-ecological values is highly sensitive to norms and values of the people involved, potentially representing specific interests in the political and social descriptions of environmental issues and actions. The map is not a basic tool, but rather defines boundaries presenting different ideals, ideologies, and practices within a landscape (Wardell-Johnson, 2005). Mapping includes a diversity of technical artifacts, processes, interfaces, and interpretations. The map as a boundary-object is central in the role of elicitation, collection, representation, management, and coordination of distributed knowledge (Star and Griesemer, 1989). Maps serve as intermediate-objects in the material sense (in the sense of Vinck, 1999) mediating between different visions and knowledge contributing to normative representation of positions about the environment. Maps play a part in contextualizing knowledge in the representation of “truth” and “facts.”A key challenge is to integrate the plurality of value-frames using social science techniques in order to re-frame decision-making processes and institutional structures (Ernoul and Wardell-Johnson, 2015; Estévez et al., 2015). This article proposes 3 basic principles derived from Mathevet and Marty (2015) that can be used to create a deliberative and procedural consultative processes coupling democracy with sc
机译:生物多样性保护是全球主要问题(Sutherland等,2017)。保护生物学旨在通过以生态为中心的规划来识别和减轻生物多样性的丧失(Salzer and Salafsky,2006)。早期的保护生物学研究人员推荐了多学科的方法来改善保护(Soule,1985),促使包括各种学科在内的人们来改进综合方法。社会科学与生态学之间进行了许多合作,在参与性方法和行动研究中将理论和实用主义相结合(Bennett等人,2017)。环境退化本质上是关于人们在环境中的价值和行为方式。尽管人们认识并理解社会价值(在这里定义为特定社区的价值或整个社会的文化价值和规范)在保护方面很重要(Norton,2005; Jacobs等,2016),但概念通常很差定义,操作或测试(Dennis等,2005; Liu等,2007)。对社会价值的评估不力限制了取得有效保护成果的成就(Brennan,2004)。最近对社会和生态价值之间关系的重新概念化导致人们努力使综合方法正规化和制度化(Chan等,2016; Teel等,2018)。需要在价值框架中更好地整合当地和土著知识与科学知识,并纳入包括生物多样性,生态系统服务和功能在内的多个价值集(Díazet al。,2015)。景观价值分析表明,人们指定了价值通过一系列框架(Plieninger等,2015;Luginbühl等,2016; Ernoul等,2018)。管理政策的社会政治层面可能不同于生态需求和物种管理(Mathevet和Mauchamp,2005年)。重视景观管理的社会和文化背景的科学活动议程为有效规划提供了基础(Turner等,2016)。整合了社会文化和生态价值的保护规划确定了潜在的社会价值框架照明途径,以寻求潜在的解决方案(Endter-Wada等,1998)。考虑人们看重自然的方式及其与自然的现有关系,可以提高人们在保护规划中的接受度和实施度(Chan等,2016; Mathevet等,2018)。参与计划的战略抽样考虑了保护计划的社会流域内的社会地理规模和价值框架(Wardell-Johnson,2005年),确定了有效保护所依赖的声音和价值范围(Ernoul和Wardell-Johnson,2013年) )。因此,有效的保护规划取决于对为什么,如何以及何时获取社会价值信息的清晰理解,以便在景观尺度上将社会文化价值整合到空间维度中(Vimal and Mathevet,2011)。已被用于文化地理学(Ramirez-Gomez等人,2016),保护科学(Ernoul等人,2018)和景观生态学(Brown,2013)中,以将人为因素纳入景观规划,建模和决策支持中系统(Le Page et al。,2013)。参与式测绘提供了一个空间平台,用于整合有关复杂景观情况的知识(例如,气候变化,城市蔓延,旅游业发展,区域规划,景观管理等)(Alhamwi等人,2017),从而在一个区域内确定一系列价值。表现形式中的风景和揭示上下文。这个整合社会生态价值的平台对相关人员的规范和价值高度敏感,有可能代表对环境问题和行动的政治和社会描述中的特定利益。地图不是基本工具,而是定义了代表景观中不同理想,意识形态和实践的边界(Wardell-Johnson,2005年)。映射包括各种技术工件,过程,接口和解释。作为边界对象的地图在分布式知识的启发,收集,表示,管理和协调中起着中心作用(Star and Griesemer,1989)。地图是物质意义上的中间对象(在Vinck,1999年意义上),在不同的视觉和知识之间进行调解,有助于规范表示环境位置。地图在“真相”和“事实”表示的语境化知识中发挥着作用。关键的挑战是使用社会科学技术整合多个价值框架,以重新制定决策过程和制度结构(Ernoul和Wardell-Johnson,2015年;Estévez等人,2015年)。本文提出了源自Mathevet和Marty(2015)的3条基本原则,这些原则可用于建立将民主与政治联系起来的审议性和程序性协商程序

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