Invasive Species
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This study investigated downy brome and seeded species responses to variable rates of imazapic in two plant communities (salt desert shrub and Wyoming big sagebrush). Overall, imazapic was useful for helping establish desirable perennial species, but unless downy brome is reduced below a critical threshold, favorable precipitation can return sites to pretreatment levels within two years.
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The main objectives of this ecological risk assessment were to evaluate the potential ecological risks from imazapic to the health and welfare of plants and animals and their habitats and to provide risk managers with a range of generic risk estimates that vary as a function of site conditions. The categories and guidelines listed below were designed to help the BLM
determine which of the proposed alternatives evaluated in the EIS should be used on BLM lands.
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This study describes a three-step process to reduce crested wheatgrass competition, introduce desired species, and manage to maintain desired species for use long term.
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This study used BehavePlus to model fire behavior in fuel breaks created by treating annual grasses with herbicides and releasing perennial bunch grasses. Flame height reductions of up to 90% were possible.
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Less than half of the studies reviewed in this synthesis showed reduced sediment movement with seeding. In all vegetation types, successful growth of seeded grasses—enough to affect erosion—appears to displace native or naturalized species, including shrub and tree seedlings. In burned sagebrush range, postfire seeding is frequently used to replace non-native cheatgrass (Bromus tectorum) with native or introduced bunchgrasses, with at least short-term success. In recent years, native species and sterile cereal grains have increasingly been used for seeding. Use of aerially applied straw mulch has increased as well, with the risk of weed introduction from contaminated bales.
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This synthesis discusses that fire can be used to either control invasive species or to restore historical fire regimes. However, the decision to use fire as a management tool must consider the potential interrelationships between fire and invasive species. Historical fire regimes did not occur in the presence of many invasive plants that are currently widespread, and the use of fire may not be a feasible or appropriate management action if fire-tolerant invasive plants are present. The management of fire and invasive plants must be closely integrated for each to be managed effectively.
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