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Updated 12 October, 2003

US National Assessment of
the Potential Consequences
of Climate Variability and Change
Educational Resources
Regional Paper: Great Plains

   

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Invasive Species and Biodiversity

 

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Natural systems in the Great Plains are currently stressed by a variety of agents. These agents include: fragmentation of grasslands through land conversions to agriculture, cities, and roads; sedimentation and water pollution from fertilizer and pesticide runoff; and introduction of invasive species through human activities and natural encroachment. Other stresses include: altered hydrology (water cycles) due to the impoundment of water in dams and reservoirs and diversion of water for irrigation and other uses; and changes to natural runoff from watersheds by human activities that alter the natural efficiency of watersheds and the permeability of soil surfaces (e.g., infilling and soil compaction). Increasing human demands on natural systems for consumable wildlife opportunities (such as hunting and fishing) and other recreational opportunities are also likely to stress natural systems that are being affected by climate change.

The pattern of remaining native species in the Great Plains is probably associated with the regional pattern of agriculture and urban development. In the agriculturally rich, eastern portions of the Great Plains, the native habitats are already absent or highly fragmented. In the central portion of the Plains, small areas of these habitats are still present but are largely disconnected. In the western edges, the native habitats are often more continuous, although the recent rapid expansion of urban areas along the Rocky Mountains is increasingly fragmenting these native communities as well. In that persistence of species often depends on sufficient habitat and connection between habitat patches, these natural communities are highly vulnerable to additional stresses.

Invasive species are currently a significant issue on the Great Plains. Invasive species are plant or animal species that have been introduced into an environment (often accidentally) in which they did not evolve. Such species usually have no natural enemies present to limit their reproduction and spread. Invasive species typically have high reproductive rates, fast growth rates, and good dispersal mechanisms. The costs and weed-associated losses from invasive species in crop and forage production in the agricultural sector are currently nearly $15 billion annually.

In native ecosystems, invasive species can compromise an ecosystem's ability to maintain its structure or function. For example, in grassland ecosystems, riparian areas next to streams and rivers are rich in native plant species and highly productive. These riparian areas also provide critical habitat for species living in the surrounding drier ecosystems, offering shelter and forage. Such riparian ecosystems can be easily invaded by invasive species, providing pathways for the exotic plants to become established and migrate into upland sites in grassland ecosystems. Natural disturbance regimes such as fire and grazing (first by buffalo and now by cattle) are seen as important in maintaining the native species. Changes in the frequency, intensity, spatial pattern, or scale of these disturbances through changes in climate could hasten the replacement of native species with exotics.

In the discussion that follows, potential environmental impacts of invasive species and changes in biodiversity in the Great Plains are examined; discussions of some of the social and economic impacts follow. General principles to guide strategic development of social responses to climate change conclude this discussion.

Distribution of Leafy Spurge in the Western US, By County, 1996

Environmental Impacts

The projected climate changes are very likely to alter the biodiversity of the Great Plains. The “new -- composition of species that could arise in response to the changing climatic conditions could or could not be detrimental to the ecological services on which society draws, but the rapid rate of change in climate is likely to be disadvantageous to native species. Invasive species have a history of exploiting habitats left vacant by native species. As climate changes, the indirect effects of weeds and pests seem likely to bring surprising challenges.

Some native species are unlikely to be able to adapt fast enough to the changing climate regimes, resulting in a lowered competitive edge and weakened resistance of ecosystems to infestations by invasive plants and animals. Potential impacts include shifts in the relative abundance and distribution of native species, significant changes in species richness and communities, and local extinctions of native species. Subtle changes in the diurnal (day/night) or seasonal patterns of temperature have also been shown to affect plant community composition. In the short-grass steppe, for instance, the slight warming of nighttime temperatures seen in the last 20 years has been linked to the decline of blue grama grass, the dominant grass of the short-grass prairie. Increased average temperature and annual precipitation in the central Great Plains could make it possible for invasive plants, such as kudzu and Johnson grass, now found further south, to migrate north. Additional land-use pressure on these native systems is likely if agricultural practices extend into these areas as a result of more favorable climatic conditions or increased demand for agricultural products.

Changes, such as in the nutritional value of plants or changes in the timing of insect emergence, could also contribute to a decline in bird populations in the Great Plains. At the same time, longer growing seasons and the possibility of increased plant productivity could increase the region's attractiveness for birds. Grassland bird species are currently declining due to a loss of habitat. Further alteration of their habitat from climate change would be a likely additional stress on these declining populations.

Changes in precipitation, temperature, and the hydrological (water) cycle are likely to affect aquatic systems and the terrestrial animals dependent on these ecosystems. The abundance of wetlands is closely tied to the year-to-year variations in climate, both precipitation and temperature. Changes in yearly precipitation in the northern regions are likely to have significant impacts on breeding duck populations. Changes in precipitation and river flow are also likely to aggravate land-use conflicts and competition for water supply including conservation needs.

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Soil Carbon & Net Primary Productivity, 1961-1990 and 2100

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 Social Impacts

Managing the region's land resources to maintain natural biodiversity -- the full array of native plants, animals, natural communities, and ecosystems that occur within the Great Plains -- is likely to be difficult as climate changes. Important resources in the northern Great Plains include the relatively undisturbed landscapes of the Indian reservations, which contain a variety of micro-environments supporting a wide range of indigenous (native) plant and animal species. In addition, the scattered federal land holdings in the northern and central Great Plains also offer refuges for species and opportunities to enhance native vegetation. In the southern Great Plains, however, there is very little protected land. A potential opportunity in this area may arise from private sector land management for ecotourism, which may be an effective route to maintaining some degree of biodiversity.

Economic Impacts

Introduced in 1827 as a contaminant in seed, leafy spurge occurs in all of the Great Plains states except Oklahoma and Texas. More than 10 to 20% leafy spurge cover leads to a significant reduction in the grazing capacity of most areas. The direct and secondary economic impacts of leafy spurge infestations on over 1.6 million acres in North and South Dakota, Montana, and Wyoming were approximately $129 million. Crop losses in Kansas are annually $40 million from the invasive species of field bindweed. With an ability to reduce wheat yield by 25%, the invasive jointed goatgrass has infested 5 million acres of winter wheat and is spreading at a rate of 50,000 acres or more a year. If climate changes contribute to increasing infestations of invasive species, even larger economc impacts could result.

Strategies to Address Potential Impacts from Invasive Species and Changes in Biodiversity

Rather than identify specific strategies, the following is a proposed set of general principles to guide strategic development of social responses to climate change. The five principles can be articulated as follows:

  • “No regrets -- strategies: These strategies respond to existing stresses while also making the system more resilient to climate change, all without incurring significant costs. Because there is a high level of uncertainty in regional climate projections and even greater uncertainty associated with how natural systems are likely to respond to those changes, developing detailed adaptation strategies based on predictions of future behavior of natural systems is currently not feasible. Under such conditions, no-regrets strategies are particularly appropriate for natural systems because current environmental stresses can be addressed and limited through such strategies. The expectation is then that implementation of beneficial strategies today is likely to have a positive influence on future stresses/impacts that could result from a changing climate;
  • Alternative pathways: Alternatives to adaptation can be provided by developing effective coping strategies for present and future stresses. For example, enhancing the heterogeneity of landscapes and connected aquatic and terrestrial systems can provide a more diverse set of alternative pathways for adaptation. Landscape heterogeneity includes both the diversity among ecosystems, such as grasslands and forests, and within ecosystems, such as different successional stages. This latter type of diversity depends on allowing an appropriate range of disturbances to affect the ecosystems, for example by allowing periodic fires. In many cases, disturbance activities need to be created by management actions, such as livestock grazing and prescribed burning, in order to compensate for the loss of natural disturbances, such as from buffalo herds and wildfire. The idea of enhancing land stewardship by private landowners is central to the success of this management principle;
  • Preserve diverse habitats: By focusing on preserving current land uses that promote integrity in natural systems, biodiversity can be enhanced. This would entail, to the extent possible, encouraging conservation and restoration through appropriate land management techniques. A fundamental need in implementing this principle is to identify actions that foster long-term economic vitality while at the same time enhancing ecosystem resiliency;
  • Adaptive management: Adaptive management involves learning by doing and continually evaluating what works and what fails to work in an attempt to lessen the impacts of climate change on natural systems. There will be surprises no matter how well prepared stakeholders might be; therefore management that is flexible and responds quickly will be most effective for dealing with uncertainties; and
  • Information dissemination: Effective coping strategies depend on informing the public and decision makers about the implications of climate change for natural systems, and what these effects mean to the quality of human life. For example, why is the role of wetlands in flood control important to society? What could changes in this natural system mean to a community or to other natural systems - both locally and regionally?

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