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Libros sobre el tema "Vegetation disturbance"

Autor: Grafiati
Publicado: 4 de junio de 2021
Última modificación: 1 de febrero de 2022

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1

H, Webb Robert. The response of vegetation to disturbance in Death Valley National Monument, California. Washington: U.S. G.P.O., 1988.

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2

Fiddler, Gary. Treatment duration and time since disturbance affect vegetation development in a young ponderosa pine plantation. Albany, CA: U.S. Dept. of Agriculture, Forest Service, Pacific Southwest Research Station, 1999.

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3

Ager, Alan A. Software for calculating vegetation disturbance and recovery by using the equivalent clearcut area model. Portland, OR: U.S. Dept. of Agriculture, Forest Service, Pacific Northwest Research Station, 2005.

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4

Coleman, T. W. Disturbance from Southern pine beetle, suppression, and wildfire affects vegetation composition in central Louisiana: A case study. Asheville, NC: U.S. Dept. of Agriculture, Forest Service, Southern Research Station, 2010.

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5

Gradowski, Tomasz Aleksander. The influences of geoclimatic site conditions, disturbance type and canopy composition on the composition of understorey vegetation of boreal mixedwoods. Ottawa: National Library of Canada, 2001.

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6

McPherson, Guy R. Disturbance and climate change in United States/Mexico borderland plant communities: A state-of-the-knowledge review. Fort Collins, CO (240 W. Prospect Rd., Fort Collins 80526-2098): U.S. Dept. of Agriculture, Forest Service, Rocky Mountain Research Station, 2000.

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7

Miller, Richard F. A field guide for rapid assessment of post-wildfire recovery potential in sagebrush and Piñon-Juniper ecosystems in the Great Basin: Evaluating resilience to disturbance and resistance to invasive annual grasses and predicting vegetation response. Fort Collins, CO: United States Department of Agriculture, Forest Service, Rocky Mountain Research Station, 2015.

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8

Huebner, Cynthia D. Effects of disturbance and environment on the chaparral-woodland-grassland landscape mosaic of central Arizona. 1996.

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9

Quinby, Peter Allan *. Vegetation, environment, and disturbance in the upland forested landscape of Algonquin Park, Ontario. 1988.

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10

Gecy, Jeanne Leslie. Propagule sources, disturbance characteristics and the inital establishment of riparian vegetation after debris flows. 1988.

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11

Clark, Deborah Louise. Factors determining species composition of post-disturbance vegetation following logging and burning of an old growth Douglas-fir forest. 1990.

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12

Leary, Cathlene Irene. The effects of hardwood reforestation and planting disturbance on vegetation composition, woody recruitment, and microclimate in southwestern Ohio. 2001.

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13

Lefroy, Ted, Allan Curtis, Anthony Jakeman y James McKee, eds. Landscape Logic. CSIRO Publishing, 2012. http://dx.doi.org/10.1071/9780643103559.

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In 2005, researchers from four Australian universities and CSIRO joined forces with environmental managers from three state agencies and six regional catchment management authorities to answer the question: 'Can we detect the influence of public environmental programs on the condition of our natural resources?' This was prompted by a series of national audits of Australia's environmental programs that could find no evidence of public investment improving the condition of waterways, soils and native vegetation, despite major public programs investing more than $4.2 billion in environmental repair over the last 20 years. Landscape Logic describes how this collaboration of 42 researchers and environmental managers went about the research. It describes what they found and what they learned about the challenge of attributing cause to environmental change. While public programs had been responsible for increase in vegetation extent, there was less evidence for improvement in vegetation condition and water quality. In many cases critical levels of intervention had not been reached, interventions were not sufficiently mature to have had any measurable impact, monitoring had not been designed to match the spatial and temporal scales of the interventions, and interventions lacked sufficiently clear objectives and metrics to ever be detectable. In the process, however, new knowledge emerged on disturbance thresholds in river condition, diagnosing sources of pollution in river systems, and the application and uptake of state-and-transition and Bayesian network models to environmental management. The findings discussed in this book provide valuable messages for environmental managers, land managers, researchers and policy makers.
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14

Wilsey, Brian J. Factors Maintaining and Regulating Grassland Structure and Function. Oxford University Press, 2018. http://dx.doi.org/10.1093/oso/9780198744511.003.0003.

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Intrinsic disturbances are processes that have occurred on an evolutionary time scale, and include fire, wind-damage, digging or burrowing by fossorial mammals, defoliation, and trampling by native large mammals. Grassland species evolved with intrinsic disturbances, and they can be important in maintaining grassland community structure and functioning. Adaptations to fire include short herbaceous stature, high allocation belowground, ability to resprout, and smoke-induced seed germination. Fire interacts with grazing because grazing reduces litter (fuel) load, and fires affect forage quality. Plants can tolerate some level of herbivory in most grasslands. Adaptations that enable grassland plants to resist grazing are similar to plant adaptations to fire. Drought can affect grasslands at a variety of time scales. Vegetative reproduction can allow rapid recolonization after droughts have ended. Plowing is the most common disturbance affecting grasslands, and it has been used to transform native grasslands into crop fields and simplified pasture.
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15

Dolman, A. Johannes, Luis U. Vilasa-Abad y Thomas A. J. Janssen. Ecohydrological Concepts of Water-Vegetation Interaction in the Drylands of Africa. Oxford University Press, 2017. http://dx.doi.org/10.1093/acrefore/9780190228620.013.554.

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Drylands cover around 40% of the land surface on Earth and are inhabited by more than 2 billion people, who are directly dependent on these lands. Drylands are characterized by a highly variable rainfall regime and inherent vegetation-climate feedbacks that can enhance the resilience of the system, but also can amplify disturbances. In that way, the system may get locked into two alternate stable states: one relatively wet and vegetated, and the other dry and barren. The resilience of dryland ecosystems derives from a number of adaptive mechanisms by which the vegetation copes with prolonged water stress, such as hydraulic redistribution. The stochastic nature of both the vegetation dynamics and the rainfall regime is a key characteristic of these systems and affects its management in relation to the feedbacks. How the ecohydrology of the African drylands will change in the future depends on further changes in climate, human disturbances, land use, and the socioeconomic system.
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16

Lyndaker, Brett R. Effect of road-related disturbance, vegetative diversity and other habitat factors on elk distribution in the northern Blue Mountains. 1994.

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