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Grand Experiments: A Review of Five Endangered Species Reintroductions in the US.

机译:大型实验:美国5种濒危物种再引进的回顾。

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摘要

Striking changes in American society resulted in the passage of the Endangered Species Act (ESA) in 1973, one of many laws passed during the environmental era of the 1960s and 70s. In just a few decades, we as a society moved from vilification and elimination of many species (or indifference to their decline) to protecting them legally under the ESA---a ground-breaking law based on the belief that all species have a fundamental right to exist.;The ESA calls for Recovery Plans to be written and implemented for species listed as in danger of extinction, plans that are to be implemented cooperatively by both federal and state agencies. When a species has been extirpated from a region or area, its recovery plan may include reintroducing that species within areas of its former range. Reintroduction of species is inherently difficu those working in the field face a number of challenges: high cost, behavioral issues in captive populations, genetic viability of often small founding populations, and habitat availability, among others. Reintroduction programs may face hostility from some sectors of the public---and even legal action.;Some reintroduction programs have been held up as successes; some species have been approved for delisting. When I began my study, I wanted to understand how and why the ESA and endangered species reintroductions have become so controversial. I wanted to understand how species reintroductions worked. Some reintroduction programs have been held up as successes; some species have been approved for delisting. What are the criteria for success? How has recovery been defined? My primary objective was to find out if several high-profile reintroduction programs had resulted in success on the ground---and what parameters might contribute to that success. To answer this question, I conducted comparative case studies of five well-known reintroductions. Four of the species were on that first list in 1967: Black-footed ferret (Mustela nigripes), reintroduced 1991; California condor (Gymnogyps californianus), reintroduced 1992; Gray wolf (Canis lupus ), reintroduced 1995; and Mexican wolf (Canis lupus baileyi ), reintroduced 1998. The fifth, listed as threatened in 2000, is the Canada lynx (Lynx canadensis.);Reintroduction success can be defined in a number of ways: numbers of animals in captivity or in the wild, genetic diversity preserved, public support, or efficient use of resources. I chose to define success by numbers---numbers of animals in captivity and in the wild, and reintroduced population demographics relative to principles of conservation biology as exemplified by resiliency, redundancy, and representation. I judged success by examining: 1) each species current status; 2) US Fish & Wildlife Recovery Plan goals for each species; 3) The ESA's Five Factor analysis [§4(a)1]; 4) Other government documents evaluating the status of each species; and 5) Books and peer-reviewed articles discussing the status of each species' recovery.;In addition, I present the species' natural history, historical conservation status, and policy background. Finally, I provide my findings. Of the species reintroductions I analyzed, all were somewhat successful in that each has a robust captive population, and at least one population has been established in the wild. Extinction has been averted for all species. However, with the exception of the Northern Rocky Mountain wolf population, all have been dependent on human intervention or assistance for survival in the wild. Only the Northern Rocky Mountain wolf population has achieved some degree of resiliency, redundancy, and representation, and exceeded initial recovery plan goals. The most successful reintroduction was the Northern Rocky Mountain wolf population, and the least successful was the Mexican wolf.;The most common reason for lack of success is that the reason(s) for initial extirpation have not been mitigated. The most common factors that led to success were a large initial release number and large recovery area. Overall, a successful reintroduction program encompasses the following: 1) a wild-born population, 2) a large initial release population, 3) a large release area, 4) connectivity among multiple populations, 5) adequate prey, 6) species characteristics that are more generalist than specialist, 7) a protected area, 8) public support.;Keywords: reintroduction, ESA, recovery
机译:美国社会发生了惊人的变化,1973年通过了《濒危物种法》(ESA),这是1960年代和70年代环境时代通过的众多法律之一。在短短的几十年中,我们作为一个社会,从文明的消灭和消灭许多物种(或漠不关心其灭绝)到根据ESA合法地保护它们-这是一项开创性的法律,其基础是相信所有物种都有基本的ESA要求为濒临灭绝的物种编写和实施恢复计划,这些计划应由联邦和州机构共同实施。当某个物种已从某个地区或地区被灭绝后,其恢复计划可能包括将该物种重新引入其先前范围内的区域。物种的固有引进是固有的困难;那些在该领域工作的人面临着许多挑战:高成本,圈养种群的行为问题,往往很小的基础种群的遗传生存力以及栖息地的可获得性等。重新引入计划可能会受到某些公共部门的敌视-甚至是法律诉讼。一些物种已获批准退市。当我开始研究时,我想了解ESA和濒危物种的重新引入如何以及为何引起如此大的争议。我想了解物种重新引入的工作方式。成功实施了一些重新引进计划;一些物种已获批准退市。成功的标准是什么?如何定义恢复?我的主要目标是找出几个引人注目的再引进计划是否在当地取得了成功-以及哪些参数可能有助于取得成功。为了回答这个问题,我对五个著名的重新介绍进行了比较案例研究。 1967年,该物种中有4个在该物种的第一名单上:1991年重新引入的黑脚雪貂(黑鼬)。加州秃鹰(Gymnogyps californianus),1992年重新引进;灰太狼(Canis lupus),1995年重新引进;和墨西哥狼(Canis lupus baileyi),于1998年重新引进。第五只,被列为受到威胁的2000年,是加拿大天猫座(Lynx canadensis。);成功引入的方式有多种:圈养或圈养动物的数量野生的,保留的遗传多样性,公众的支持或资源的有效利用。我选择用数字来定义成功-圈养和野外的动物数量,并根据保护生物学原理重新引入种群统计数据,例如弹性,冗余度和代表性。我通过检查以下内容来判断成功:1)每个物种的当前状态; 2)美国鱼类和野生动物恢复计划对每个物种的目标; 3)ESA的五因素分析[§4(a)1]; 4)其他评估每种物种状况的政府文件; 5)讨论每种物种恢复状况的书籍和同行评审文章。此外,我还介绍了该物种的自然历史,历史保护状况和政策背景。最后,我提供了我的发现。在我分析过的物种引进中,所有物种都取得了一定的成功,因为每个物种都有强大的圈养种群,并且至少有一个野生种群已经建立。避免了所有物种的灭绝。但是,除了北落基山狼种群以外,所有人都依靠人工干预或协助生存。仅北落基山狼种群已达到一定程度的复原力,冗余和代表性,并超出了最初的恢复计划目标。最成功的重新引入是北洛矶山脉狼种群,而最不成功的是墨西哥狼。缺乏成功的最常见原因是最初灭绝的原因没有得到缓解。导致成功的最常见因素是大量的初始发行版和较大的恢复区域。总的来说,一个成功的再引进计划包括以下内容:1)野生出生的种群; 2)大量的初始释放种群; 3)较大的释放区域; 4)多个种群之间的连通性; 5)足够的猎物; 6)具有以下特征的物种特征:比专家更通才; 7)保护区; 8)公众支持。关键字:再介绍,欧空局,恢复

著录项

  • 作者

    Nemeth, Lynne.;

  • 作者单位

    Prescott College.;

  • 授予单位 Prescott College.;
  • 学科 Agriculture Wildlife Conservation.;Environmental Studies.
  • 学位 M.A.
  • 年度 2012
  • 页码 280 p.
  • 总页数 280
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

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