A. Gunn, D. Russell, C. Daniel, R. White, G. Kofinas
{"title":"CARMA对累积效应的协作和跨学科评估方法","authors":"A. Gunn, D. Russell, C. Daniel, R. White, G. Kofinas","doi":"10.7557/2.33.2.2540","DOIUrl":null,"url":null,"abstract":"32 (1), 2012 This journal is published under the terms of the Creative Commons Attribution 3.0 Unported License Editor in Chief: Birgitta Ahman, Technical Editor Eva Wiklund and Graphic Design: Bertil Larsson, www.rangifer.no Introduction One of the most frequent concerns about the future of migratory tundra caribou, Rangifer tarandus groenlandicus or granti, are the impacts of the cumulative e\"ects of changing climate and land-use activities across herd’s ranges. Assessing cumulative e\"ects is typically a requirement in environmental assessment of industrial developments but policy and technical limitations have hindered development of assessment methods (Duinker & Greig, 2006). Johnson & St.-Laurent (2011) commented on the lack of a methodological framework as one of the reasons for slow progress on cumulative e\"ects. #ey suggested a framework based on the scaling from individual to population, the relative frequency, and magnitudes of e\"ects and their regulation. We know quite a bit about individual caribou responses to human activities – interruptions to foraging and displacement of individuals at various distances from the disturbance (Aastrup, 2000; Cameron et al., 2005; Boulanger et al., 2012). However, to scale up from the behavioral responses of individual caribou to the population scale (Johnson & St.-Laurent, 2011) requires baseline information on the ‘state’ of the individual and population giving consideration to, for example, climate, population density, and genetic structure. At both the individual and population scale, we also have to consider environmental in$uences, especially weather and climate, which will be additive or compensatory to impacts imposed by human activities. To scale up the individual’s behavioral responses to the population requires being able to estimate the costs to the individual and whether those costs will a\"ect its reproduction and survival. Estimating the costs of a behavioral response is not straight forward; as well as the energy costs of movement and interruption in foraging time, there may also be an e\"ect on diet (energy protein intake) if a displacement puts the individual in a di\"erent habitat. 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Johnson & St.-Laurent (2011) commented on the lack of a methodological framework as one of the reasons for slow progress on cumulative e\\\"ects. #ey suggested a framework based on the scaling from individual to population, the relative frequency, and magnitudes of e\\\"ects and their regulation. We know quite a bit about individual caribou responses to human activities – interruptions to foraging and displacement of individuals at various distances from the disturbance (Aastrup, 2000; Cameron et al., 2005; Boulanger et al., 2012). However, to scale up from the behavioral responses of individual caribou to the population scale (Johnson & St.-Laurent, 2011) requires baseline information on the ‘state’ of the individual and population giving consideration to, for example, climate, population density, and genetic structure. At both the individual and population scale, we also have to consider environmental in$uences, especially weather and climate, which will be additive or compensatory to impacts imposed by human activities. To scale up the individual’s behavioral responses to the population requires being able to estimate the costs to the individual and whether those costs will a\\\"ect its reproduction and survival. Estimating the costs of a behavioral response is not straight forward; as well as the energy costs of movement and interruption in foraging time, there may also be an e\\\"ect on diet (energy protein intake) if a displacement puts the individual in a di\\\"erent habitat. 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引用次数: 5
摘要
主编:Birgitta Ahman,技术编辑Eva Wiklund,平面设计:Bertil Larsson, www.rangifer.no简介关于迁徙的苔原驯鹿(Rangifer tarandus groenlandicus或granti)的未来,最常见的担忧之一是气候变化和土地利用活动对牧群范围的累积影响。评估累积影响通常是工业发展环境评估的一项要求,但政策和技术限制阻碍了评估方法的发展(Duinker & Greig, 2006)。Johnson & st . laurent(2011)评论说,缺乏方法框架是累积效应进展缓慢的原因之一。他们提出了一个基于个体到群体的尺度、影响的相对频率和程度及其调控的框架。我们对驯鹿个体对人类活动的反应有相当多的了解——觅食的中断和个体在远离干扰的不同距离上的迁移(Aastrup, 2000;Cameron et al., 2005;Boulanger et al., 2012)。然而,要将单个驯鹿的行为反应扩大到种群规模(Johnson & st . laurent, 2011),需要考虑到气候、种群密度和遗传结构等因素的个体和种群“状态”的基线信息。在个人和人口规模上,我们还必须考虑环境影响,特别是天气和气候,它们将对人类活动造成的影响起到附加或补偿作用。为了扩大个体对群体的行为反应,需要能够估计个体的成本,以及这些成本是否会影响其繁殖和生存。估计一种行为反应的成本并不是直截了当的;除了迁徙的能量消耗和觅食时间的中断,如果迁徙将个体置于不同的栖息地,也可能对饮食(能量蛋白质摄入)产生影响。生态学报,2013,第21期,第161-166页。2011年8月22-26日,中国科学院学报
CARMA’s approach for the collaborative and inter-disciplinary assessment of cumulative effects
32 (1), 2012 This journal is published under the terms of the Creative Commons Attribution 3.0 Unported License Editor in Chief: Birgitta Ahman, Technical Editor Eva Wiklund and Graphic Design: Bertil Larsson, www.rangifer.no Introduction One of the most frequent concerns about the future of migratory tundra caribou, Rangifer tarandus groenlandicus or granti, are the impacts of the cumulative e"ects of changing climate and land-use activities across herd’s ranges. Assessing cumulative e"ects is typically a requirement in environmental assessment of industrial developments but policy and technical limitations have hindered development of assessment methods (Duinker & Greig, 2006). Johnson & St.-Laurent (2011) commented on the lack of a methodological framework as one of the reasons for slow progress on cumulative e"ects. #ey suggested a framework based on the scaling from individual to population, the relative frequency, and magnitudes of e"ects and their regulation. We know quite a bit about individual caribou responses to human activities – interruptions to foraging and displacement of individuals at various distances from the disturbance (Aastrup, 2000; Cameron et al., 2005; Boulanger et al., 2012). However, to scale up from the behavioral responses of individual caribou to the population scale (Johnson & St.-Laurent, 2011) requires baseline information on the ‘state’ of the individual and population giving consideration to, for example, climate, population density, and genetic structure. At both the individual and population scale, we also have to consider environmental in$uences, especially weather and climate, which will be additive or compensatory to impacts imposed by human activities. To scale up the individual’s behavioral responses to the population requires being able to estimate the costs to the individual and whether those costs will a"ect its reproduction and survival. Estimating the costs of a behavioral response is not straight forward; as well as the energy costs of movement and interruption in foraging time, there may also be an e"ect on diet (energy protein intake) if a displacement puts the individual in a di"erent habitat. Understanding and integrating those relationships between behavior, habitat selection, energy and protein intake relative to reproduction and surRangifer, 33, Special Issue No. 21, 2013: 161–166 13 Arctic Ungulate Conference Yellowknife, Canada 22-26 August, 2011