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Evaluation of bison (Bison bison) ecology at the Olson's Bison Conservation Ranches, Pine River Ranch, Manitoba, Canada

机译:在加拿大曼尼托巴省松河牧场的奥尔森野牛保护牧场评估野牛(野牛野牛)生态

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摘要

Bison (Bison bison), the largest mammalian species in North America, historically numbering in the tens of millions (Roe 1970, McHugh 1972, Dary 1989, Shaw 1995), was nearly extirpated at the turn of the 19 th century (Knapp et al. 1999; Gates et al. 2010). At the time, estimates of less than 1,000 bison remaining in North America are widely accepted (Hornaday 1889; Seton 1927; Gates et al. 2010). The decline of bison includes factors such as disease (Flores 1991; Isenberg 2000), sport hunting (Danz 1997; Dary 1989; Hewitt 1919; Isenberg 2000; McHugh 1972), and unofficially funded commercial hunting by the U.S. government (Hornaday 1889; Mayer and Roth 1958; Isenberg 2000).;As bison populations started to decrease, private citizens were the catalysts in conserving bison in the early 1900's (Gates et al. 2010); since, at the time, laws protecting bison were minimal (Danz 1997). Protection for bison was first implemented in 1877 in Canada (Gates et al. 2001). The U.S. followed shortly thereafter, in 1894, when President Cleveland signed the National Park Protective Act (Lacey Act). The Lacey Act protected bison and imposed jail sentences or fines on anyone found guilty of killing bison in Yellowstone National Park, where the last free ranging bison were located (Boyd and Gates 2006). Furthermore, conservation efforts by state, federal, non-government organization (NGO), and private herdsmen have reestablished populations across North America. As a result, the United States Department of Agriculture's Census of Agriculture recently reported 162,110 bison on 2,584 farms (USDA 2012), whereas, Canada reported 125,142 bison on 1,211 farms (Statistics Canada 2011). Of those, about 31,000 individuals (7.4%) are part of conservation herds, operated by state, federal, or an NGO agency (Gates et al. 2010).;Today, private stakeholders manage approximately 92% of the bison, with a common belief that management is primarily economically driven for profit, in contrast to the conservation focus of state, federal, and NGO managed herds (Hudson and Frank 1987). Therefore, private organizations are not considered conservation herds, even if the primary management goal is conservation oriented (Gates et al. 2010). Contrary to this misconception, the Olson's Conservation Bison Ranches manages for conservation by following the "Bison Conservation Management: Guidelines for Herd Managers" (Lammers et al. 2013). The basis of our research was to evaluate the efficacy of this manual for managing bison in private herds from a conservation standpoint. The projects main objectives were to 1) calculate forage availability and determine bison diet composition to understand forage selection (Chapter 1), 2) calculate biomass production and estimate carrying capacity of bison (Chapter 1), 3) calculate bison neonatal survival and determine cause-specific mortality (Chapter 2), and 4) examine corridor movements of bison in aspen-dominated forests (Chapter 3).
机译:北美最大的哺乳动物北美野牛(Bison bison)的历史数量达数千万种(Roe 1970,McHugh 1972,Dary 1989,Shaw 1995),在19世纪初几乎被灭绝(Knapp等人) (1999;盖茨等,2010)。当时,人们普遍接受的估计是北美剩余的不到1000只野牛(Hornaday 1889; Seton 1927; Gates等2010)。野牛的衰落包括多种因素,例如疾病(Flores 1991; Isenberg 2000),运动狩猎(Danz 1997; Dary 1989; Hewitt 1919; Isenberg 2000; McHugh 1972)以及美国政府提供的非官方资助的商业狩猎(Hornaday 1889; Mayer)和Roth 1958; Isenberg 2000);随着野牛数量的减少,在1900年代初期,私人公民是保护野牛的催化剂(Gates等,2010)。因为在当时,保护野牛的法律极少(Danz 1997)。保护野牛于1877年在加拿大首次实施(Gates等,2001)。此后不久,即1894年,美国总统克利夫兰签署了《国家公园保护法》(《莱西法》)。 《雷斯法案》保护了野牛,并对在黄石国家公园杀害野牛的任何人判处有期徒刑或罚款,黄石国家公园是最后一个放养野牛的地方(Boyd and Gates 2006)。此外,各州,联邦,非政府组织(NGO)和私人牧民的保护努力在北美重新建立了种群。结果,美国农业部农业普查最近报告了2,584个农场的野牛为162,110野牛(USDA 2012),而加拿大报告了1,211个农场的野牛为125,142野牛(加拿大统计局,2011)。其中,大约31,000人(7.4%)是保护畜群的一部分,由州,联邦或非政府组织负责运营(Gates等,2010)。如今,私人利益相关者管理着约92%的野牛,与州,联邦和非政府组织管理的畜群的保护重点不同(Hudson和Frank,1987),人们认为管理主要是从经济上为牟利而进行的。因此,即使主要的管理目标是以保护为导向,私人组织也不被视为保护群体(Gates等,2010)。与这种误解相反,奥尔森保护区野牛牧场按照“野牛保护管理:牧民管理者指南”进行管理(Lammers等,2013)。我们研究的基础是从保护的角度评估本手册对管理野牛野牛的功效。该项目的主要目标是:1)计算草料的利用率并确定野牛的饮食组成以了解草料的选择(第1章),2)计算生物量并估算野牛的承载能力(第1章),3)计算野牛的新生儿存活率并确定原因特定死亡率(第2章)和第4章)研究了在白杨为主的森林中野牛的走廊运动(第3章)。

著录项

  • 作者

    Leonard, Joshua L.;

  • 作者单位

    South Dakota State University.;

  • 授予单位 South Dakota State University.;
  • 学科 Ecology.;Wildlife conservation.;Wildlife management.
  • 学位 M.S.
  • 年度 2016
  • 页码 91 p.
  • 总页数 91
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

  • 入库时间 2022-08-17 11:46:36

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