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Książki na temat „Habitat loss”

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Autor: Grafiati
Data publikacji: 4 czerwca 2021
Data aktualizacji: 4 marca 2023

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1

Loss of habitat. Lewiston: Mellen Poetry Press, 1993.

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2

Hanski, Ilkka. The shrinking world: Ecological consequences of habitat loss. Oldendorf/Luhe, Germany: International Ecology Institute, 2005.

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Hanski, Ilkka. The shrinking world: Ecological consequences of habitat loss. Oldendorf/Luhe, Germany: International Ecology Institute, 2005.

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4

Lanno, R. Protective modelling of fisheries habitat loss and replacement. Downsview, Ont: Research and Development Branch, Ontario Ministry of Transportation, 1992.

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5

Lynn, Brian. Nearshore habitat loss in Puget Sound: Recommendations for improved management. [Olympia?, Wash.]: Puget Sound/Georgia Basin International Task Force, [1998], 1998.

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6

Donatuto, Jamie. Fragmentation processes and subsequent loss of habitat in the Tijuana River Watershed. Bellingham, WA: Huxley College of Environmental Studies, Western Washington University, 2000.

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7

J, Pawlowski Robert, Ingham Merton C. 1930- i United States. National Marine Fisheries Service. Northeast Regional Operations Office, red. Quantifying resource loss through habitat degradation: Proceedings of the first NMFS Northeast Environmental Workshop, March 13-14, 1991, Gloucester, Massachusetts. Gloucester, Mass: U.S. Dept. of Commerce, National Oceanic and Atmospheric Administration, National Marine Fisheries Service, Northeast Region, Northeast Regional Operations Office, 1992.

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8

J, Kirali Sari, Cross Ford A, Buffington John D, United States. National Oceanic and Atmospheric Administration, United States. National Ocean Pollution Program Office i U.S. Fish and Wildlife Service, red. Federal coastal wetland mapping programs: A report by the National Ocean Pollution Policy Board's Habitat Loss and Modification Working Group. Washington, D.C: U.S. Dept. of the Interior, Fish and Wildlife Service, 1991.

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9

J, Kirali Sari, Cross Ford A, Buffington John D, United States. National Oceanic and Atmospheric Administration., United States. National Ocean Pollution Program Office. i U.S. Fish and Wildlife Service., red. Federal coastal wetland mapping programs: A report by the National Ocean Pollution Policy Board's Habitat Loss and Modification Working Group. Washington, D.C: U.S. Dept. of the Interior, Fish and Wildlife Service, 1991.

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10

John, Goss-Custard, Rufino Rui, Luis Martínez Moisés Armando, Wetlands International i Centre for Ecology and Hydrology (Great Britain), red. Effect of habitat loss and change on waterbirds: Proceedings of 10th International Waterfowl Ecology Symposium, held at the University of Aveiro, Portugal, 18-21 September 1995. London: Stationery Office, 1997.

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11

Rogers, Donald E. Impact of redd loss at Vernita Bar on Hanford Reach chinook salmon production: Final report 1988. Portland, OR: U.S. Dept. of Energy, Bonneville Power Administration, Division of Fish and Wildlife, 1988.

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12

Society, Ghana Wildlife, red. Replacing our lost habitat. Accra, Ghana: Ghana Wildlife Society, 2002.

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13

United States. Congress. House. Committee on Merchant Marine and Fisheries. Subcommittee on Fisheries and Wildlife Conservation and the Environment. Waterfowl decline in the Mississippi Flyway: Hearing before the Subcommittee on Fisheries and Wildlife Conservation and the Environment of the Committee on Merchant Marine and Fisheries, House of Representatives, One Hundredth Congress, second session, on the decline of waterfowl in the Mississippi Flyway and the loss of wintering habitat in the Mississippi Flood Plain, September 22, 1988. Washington: U.S. G.P.O., 1988.

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14

Dumbauld, Brett R. Mitigation for estimated juvenile Dungeness crab loss due to test of hopper dredging with sidecast disposal in Willapa Bay, Washington: Final report, June 10, 1998. Olympia, WA: Washington Dept. of Fish and Wildlife, Fish Program, Willapa Bay Field Station, 1999.

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15

Dumbauld, Brett R. Mitigation for estimated juvenile Dungeness crab loss due to test of hopper dredging with sidecast disposal in Willapa Bay, Washington: Final report, June 10, 1998. Olympia, WA: Washington Dept. of Fish and Wildlife, Fish Program, Willapa Bay Field Station, 1999.

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16

Dumbauld, Brett R. Mitigation for estimated juvenile Dungeness crab loss due to test of hopper dredging with sidecast disposal in Willapa Bay, Washington: Final report, June 10, 1998. Olympia, WA: Washington Dept. of Fish and Wildlife, Fish Program, Willapa Bay Field Station, 1999.

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17

Kolankiewicz, Leon J. Weighing sprawl factors in large U.S. cities: A report on the nearly equal roles played by population growth and land use choices in the loss of farmland and natural habitat to urbanization. Arlington, VA: NumbersUSA, 2001.

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18

Eve, Adamson, i Zhang Siting, red. Zi ran shou: Jiao ni yong yuan bai tuo jian fei fan nao de shi da fa ze. Taibei Xian Xindian Shi: Mu ma wen hua shi ye gu fen you xian gong si, 2010.

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19

United States. Department of Veterans Affairs. 9 steps to a healthy weight. Washington, D.C.?]: Department of Veterans Affairs, 1992.

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20

Hobbs, Chantel. Love food and live well: Lose weight, get fit, and taste life at its very best. Colorado Springs, Colo: WaterBrook Press, 2010.

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21

Sander, Jennifer Basye. The martini diet: The self-indulgent way to a thinner, more fabulous you! Gloucester, MA: Fairwinds Press, 2004.

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22

Your weight is over: A personal trainer for emotional eaters. Pittsburgh, Pa: Rosedog Books, 2009.

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23

Simmons, Jaime. Deforestation and Habitat Loss. Rosen Publishing Group, 2017.

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Simmons, Jaime. Deforestation and Habitat Loss. Rosen Publishing Group, 2017.

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25

Simmons, Jaime. Deforestation and Habitat Loss. Rosen Publishing Group, 2017.

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26

Korsgaard, Christine M. Species, Communities, and Habitat Loss. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198753858.003.0011.

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This chapter examines the question what is bad about the extinction of a species, and whether the extinction of a species is bad for its members. It asks what a species is, whether it is a population rather than a type, whether it has a good, and whether it can act, and argues that we cannot straightforwardly say yes to any of those questions. It argues that our tendency to speak and think of species as if they were generic organisms makes us overlook the value of individual animals. In place of thinking about the wrong we are doing to a species, we should think about the wrong we are doing to communities of animals when we destroy the possibility of their carrying on shared lives in shared habitats. The chapter ends by asking whether given our terrible effects on other species, the human species ought voluntarily to go extinct.
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27

Habitat Loss: Causes, Impacts on Biodiversity and Reduction Strategies. Nova Science Pub Inc, 2014.

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28

Cushman, Samuel A., i Tzeidle N. Wasserman. Quantifying loss and degradation of former American marten habitat due to the impacts of forestry operations and associated road networks in northern Idaho, USA. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198759805.003.0012.

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American marten are associated with extensive and unfragmented late seral forest habitats, and are often considered to be particularly vulnerable to habitat loss and fragmentation. This chapter evaluates the impact of road building and timber harvest on habitat suitability for marten in northern Idaho, USA, using an empirically derived, multi-scale habitat suitability model, reconstructing key predictor variables (elevation, forest type, road density, canopy cover, landscape fragmentation and the extensiveness of late seral forest in the landscape) as they appear to have existed prior to harvest, and applying the model to both current and pre-harvest conditions. Calculating changes in the extent and pattern of habitat in the landscape indicate that timber harvest and road construction together reduced marten habitat quality considerably across the study area, which is likely responsible for current patterns of reduced detection rates and lower genetic diversity in areas that have experienced the largest amounts of habitat loss.
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29

Fahrig, Lenore. Forty years of bias in habitat fragmentation research. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780198808978.003.0005.

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This chapter evaluates biases that contribute to the common misrepresentation of fragmentation as a major threat to biodiversity. The idea that habitat fragmentation seriously threatens biodiversity is so widespread that it might be considered a “conservation biology principle.” However, effects attributed to habitat fragmentation are usually confounded with effects of habitat loss. A recent review of the effects of habitat fragmentation per se (effects independent of habitat loss) indicated that 76% of significant effects of fragmentation were positive, and in no situation were most effects negative. Comparing the abstracts of papers with the actual results reported in the body of each paper revealed that fewer than half of the authors who found only positive fragmentation effects actually discuss these positive effects in their abstracts. Thus, authors themselves reinforce the misrepresentation of the fragmentation literature, potentially because authors fear that their results could be incorrectly used to justify habitat destruction.
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30

Global emergence of infectious diseases: links with wild meat consumption, ecosystem disruption, habitat degradation and biodiversity loss. FAO, 2020. http://dx.doi.org/10.4060/ca9456en.

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31

Thompson, Douglas M. Quest for the Golden Trout: Environmental Loss and America's Iconic Fish. University Press of New England, 2013.

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32

Thompson, Douglas M. Quest for the Golden Trout: Environmental Loss and America's Iconic Fish. University Press of New England, 2013.

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33

Quest for the Golden Trout: Environmental Loss and America's Iconic Fish. University Press of New England, 2013.

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34

Federal coastal wetland mapping programs: A report by the National Ocean Pollution Policy Board's Habitat Loss and Modification Working Group. Washington, D.C: U.S. Dept. of the Interior, Fish and Wildlife Service, 1990.

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35

Edwards, Martin. Plankton and Global Change. Oxford University Press, 2017. http://dx.doi.org/10.1093/oso/9780199233267.003.0007.

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Global change caused by human activities has had large consequences for the Earth's biosphere through such effects as climate warming, pollution, loss of biodiversity, unsustainable exploitation of resources, loss of habitats, and alterations to nutrient cycles. These changes have accelerated over the last 50 years as human populations have sharply grown, coupled with unsustainable economic practices. The marine pelagic realm, the habitat for planktonic organisms, is the largest ecological habitat on the planet, occupying 71% of the planetary surface. This chapter focuses on the effects of global changes caused by human activities on marine plankton. It introduces some key concepts of plankton ecology such as the ecological niche concept, plankton succession, and the use of planktonic indicators to monitor these changes.
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36

Habitat Lost. Cave Moon Press, 2017.

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37

Goss-Custard, John. Effect of Habitat Loss and Change on Waterbirds: Proceedings of 10th International Waterfowl Ecology Symposium, Held at the University of Aveiro, Port (Ite Symposium). Stationery Office Books (TSO), 1997.

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38

Gallaghar, Carol Lee. No net loss of what, when, where & how: An analysis of aquatic habitat policy implementation through the Clean Water Act section 404 permit process. 1993.

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39

Goss-Custard, John. Effect of Habitat Loss and Change on Waterbirds: Proceedings of 10th International Waterfowl Ecology Symposium, Held at the University of Aveiro, Port (Ite Symposium). Stationery Office Books (TSO), 1997.

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40

Powell, Roger A., Aaron N. Facka, Mourad W. Gabriel, Jonathan H. Gilbert, J. Mark Higley, Scott D. LaPoint, Nicholas P. McCann, Wayne Spencer i Craig M. Thompson. The fisher as a model organism. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198759805.003.0011.

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The literature on fishers - medium-sized, North American carnivores - is broad, despite being limited, and traditional ecological knowledge of Native Americans contributes to our understanding of fishers. Fishers are generalist predators but also specialized predators of North American porcupines. Over trapping, habitat loss and climate change reduced fisher populations after European colonization of North America. Protection and reintroductions led to general but not to universal population recovery, contributing to the understanding of reintroduction science, including population genetics of both rare and expanding populations. Although adapted to live in old forests with complex structure, some fishers have colonized fragmented habitats, including suburbs. Models of fisher habitat, energetics, sexual dimorphism, genetics, and use of space illustrate the diversity of approaches possible for carnivore studies. Thus, the fisher has become a model organism for ecological and conservation research on mammalian carnivores.
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41

Daniel C,; Schroeter, Stephen C.; Huang, David Reed. Experimental Investigation of the Use of Artificial Reefs to Mitigate the Loss of Giant Kelp Habitat: A Case Study of the San Onofre Nuclear Generating Station's Artificial Reef Project. Univeristy of California Santa Barbara, 2006.

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42

Esler, Karen J., Anna L. Jacobsen i R. Brandon Pratt. Transformation. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198739135.003.0008.

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Extensive habitat loss and habitat conversion has occurred across all mediterranean-type climate (MTC) regions, driven by increasing human populations who have converted large tracts of land to production, transport, and residential use (land-use, land-cover change) while simultaneously introducing novel forms of disturbance to natural landscapes. Remaining habitat, often fragmented and in isolated or remote (mountainous) areas, is threatened and degraded by altered fire regimes, introduction of invasive species, nutrient enrichment, and climate change. The types and impacts of these threats vary across MTC regions, but overall these drivers of change show little signs of abatement and many have the potential to interact with MTC region natural systems in complex ways.
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43

Carp, Howard J. A. Recurrent Pregnancy Loss. Taylor & Francis Group, 2014.

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44

Recurrent Pregnancy Loss. Wiley-Blackwell, 2014.

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45

Christiansen, Ole Bjarne. Recurrent Pregnancy Loss. Wiley & Sons, Limited, John, 2013.

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46

Esler, Karen J., Anna L. Jacobsen i R. Brandon Pratt. The Biology of Mediterranean-Type Ecosystems. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198739135.001.0001.

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The world’s mediterranean-type climate regions (including areas within the Mediterranean, South Africa, Australia, California, and Chile) have long been of interest to biologists by virtue of their extraordinary biodiversity and the appearance of evolutionary convergence between these disparate regions. Comparisons between mediterranean-type climate regions have provided important insights into questions at the cutting edge of ecological, ecophysiological and evolutionary research. These regions, dominated by evergreen shrubland communities, contain many rare and endemic species. Their mild climate makes them appealing places to live and visit and this has resulted in numerous threats to the species and communities that occupy them. Threats include a wide range of factors such as habitat loss due to development and agriculture, disturbance, invasive species, and climate change. As a result, they continue to attract far more attention than their limited geographic area might suggest. This book provides a concise but comprehensive introduction to mediterranean-type ecosystems. As with other books in the Biology of Habitats Series, the emphasis in this book is on the organisms that dominate these regions although their management, conservation, and restoration are also considered.
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47

Esler, Karen J., Anna L. Jacobsen i R. Brandon Pratt. Planning for the future. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198739135.003.0009.

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Mediterranean-type climate (MTC) regions are highlighted in several global analyses of conservation risk and priorities. These regions have undergone high levels of habitat conversion and yet of all terrestrial biomes they have the second lowest level of land protection. With transformation pressures set to continue (Chapter 8), planning for a sustainable conservation future in MTC regions is therefore essential. Conservation activities are represented by a variety of philosophies and motives, partially driven by the underlying differences in transformation drivers and sociopolitical contexts across MTC regions. These activities include investment in, and best-practice management of, protected areas (land sparing), an interdisciplinary focus on integrated management of production landscapes (land sharing; stewardship), as well as ecological restoration to increase habitat, improve connectivity, and provide a hedge against the impacts of future climate change. These responses need to be applied in a strategic, synergistic manner to minimize future biodiversity loss.
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48

Clarke, Charles, Adam Cross i Barry Rice. Conservation of carnivorous plants. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198779841.003.0027.

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Approximately 20% of carnivorous plant species are threatened worldwide. Key threats include habitat degradation and loss, altered fire regimes or hydrology, and collection of plants for trade. In most parts of the world, conservation efforts are focused on documenting the threats to species, a necessary precursor to the implementation of conservation strategies and actions. To date, North America is the only region where species-specific conservation actions have been implemented. In southwestern Australia, inappropriate land management practices and urbanization threaten a number of species, whereas in Southeast Asia, Nepenthes pitcher plants are threatened by habitat destruction and collection for trade. Some iconic carnivorous plant species in these two biodiversity hotspots are critically endangered and the need for recovery plans and actions is urgent. There is an equally urgent need for baseline data on the conservation status of carnivorous plant species from other regions, particularly Africa and South America.
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Nackoney, Janet, Jena Hickey, David Williams, Charly Facheux, Takeshi Furuichi i Jef Dupain. Geospatial information informs bonobo conservation efforts. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198728511.003.0017.

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The endangered bonobo (Pan paniscus), endemic to the Democratic Republic of Congo (DRC), is threatened by hunting and habitat loss. Two recent wars and ongoing conflicts in the DRC greatly challenge conservation efforts. This chapter demonstrates how spatial data and maps are used for monitoring threats and prioritizing locations to safeguard bonobo habitat, including identifying areas of highest conservation value to bonobos and collaboratively mapping community-based natural resource management (CBNRM) zones for reducing deforestation in key corridor areas. We also highlight the development of a range-wide model that analysed a variety of biotic and abiotic variables in conjunction with bonobo nest data to map suitable habitat. Approximately 28 per cent of the range was predicted suitable; of that, about 27.5 per cent was located in official protected areas. These examples highlight the importance of employing spatial data and models to support the development of dynamic conservation strategies that will help strengthen bonobo protection. Le bonobo en voie de disparition (Pan paniscus), endémique à la République Démocratique du Congo (DRC), est menacé par la chasse et la perte de l’habitat. Deux guerres récentes et les conflits en cours dans le DRC menacent les efforts de conservation. Ici, nous montrons comment les données spatiales et les cartes sont utilisées pour surveiller les menaces et prioriser les espaces pour protéger l’habitat bonobo, inclut identifier les zones de plus haute valeur de conservation aux bonobos. En plus, la déforestation est réduite par une cartographie collaborative communale de gestion de ressources dans les zones de couloirs essentiels. Nous soulignons le développement d’un modèle de toute la gamme qui a analysé un variété de variables biotiques et abiotiques en conjonction avec les données de nid bonobo pour tracer la carte d’un habitat adéquat. Environ 28 per cent de la gamme est prédit adéquat; de cela, environ 27.5 per cent est dans une zone officiellement protégée. Ces exemples soulignent l’importance d’utiliser les données spatiales et les modèles pour soutenir le développement de stratégies de conservations dynamiques qui aideront à renforcer la protection des bonobos.
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50

Carp, Howard J. A. Recurrent Pregnancy Loss: Causes, Controversies and Treatment. Taylor & Francis Group, 2007.

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