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United States Department of Agriculture

Agricultural Research Service

Research Project: Ecological Interactions in Integrated and Biologically-Based Management of Invasive Plant Species in Western Rangelands

Location: Great Basin Rangelands Research

2011 Annual Report

1a. Objectives (from AD-416)
Objective 1. Conduct foreign exploration and biological evaluation for biological control agents of weeds of western rangelands such as the annual grass medusahead rye and perennial pepperweed. Sub-objective 1.1: Conduct foreign exploration for natural enemies of medusahead rye and perennial pepperweed. Sub-objective 1.2: Conduct host-specificity testing and impact evaluation to assess biological control candidates of target weeds for risk to non-target organisms. Objective 2. Understand the ecology, biology and genetic variation of invasive weeds such as saltcedar, perennial pepperweed, and medusahead rye, and their natural enemies. Sub-objective 2.1: Conduct ecological studies of seed predators and other natural enemies of medusahead rye in the native and invaded ranges. Sub-objective 2.2: Characterize genetic variation of Lepidium latifolium (perennial pepperweed) in its native and invaded ranges. Objective 3. Determine the effects of integrated weed suppression (particularly saltcedar) and woody plant removal (pinyon and juniper) on ecosystem processes such as water and carbon cycling, and on long-term successional processes (including plants and wildlife), insect impacts on invasion, and restoration processes to facilitate science-based rehabilitation and restoration of lands invaded by these weeds. Sub-objective 3.1: Long-term monitoring of the effects of Diorhabda carinulata (northern Tamarisk beetle) on ecosystem functions, tree mortality and wildlife populations in areas affected by saltcedar biological control. Sub-objective 3.2: Determine guidelines for secondary control methods and restoration planning. Sub-objective 3.3: Determine the effects of two pinyon and juniper removal treatments on the hydrologic budget, particularly soil moisture, as well as understory composition. Objective 4. Develop restoration methodologies to prevent the invasion of annual grasses (such as cheatgrass, medusahead rye, and/or red brome) following destructive events (such as fire) in rangeland ecosystems.

1b. Approach (from AD-416)
Over the next five years we will conduct research to develop appropriate strategies to control exotic weeds and encroaching native species in western rangelands and riparian areas. Control measures will focus on using classical biological control to find insect enemies of exotic weeds, as well as other control measures, such as mechanical treatments. Genetic analyses of exotic weed species will determine the diversity of populations in the invaded range and identify similar populations in the native range to improve our ability to select effective control agents. There is little research on the ecosystem impacts of control measures; we will determine the impacts of control measures on ecosystem functions including carbon and water cycling, plant community composition and small animal diversity. We will also conduct research to determine appropriate restoration strategies for these ecosystems, by testing planting techniques and novel seed mixtures. These investigations will include basic and applied studies using hypothesis-driven experiments conducted in the laboratory, greenhouse, and field.

3. Progress Report
We continued to measure the ecosystem effects of saltcedar biological control by the northern tamarisk beetle. We measured tree mortality, bird and small mammal diversity, changes in saltcedar leaf area, beetle density, understory vegetation composition and carbon and water fluxes. We monitored faunal diversity in native riparian habitats and in saltcedar habitats as indicators of the effects of saltcedar invasion and subsequent biocontrol effort. We expanded bird and small mammal studies to one more site (a total of four sites) and added invertebrate sampling to three of these sites. Wildlife monitoring was mandated as part of the APHIS permit for the release of the beetle, and is essential to future efforts to continue the saltcedar biological control program, which has currently been discontinued by the US Fish and Wildlife Service due to concerns about the endangered southwestern willow flycatcher. A manuscript was submitted on 10 years of wildlife monitoring in saltcedar and native riparian habitats. Sites were selected in beetle affected saltcedar areas for restoration. Installation was initiated for a large common garden experiment designed to test appropriate seeding mixes for sagebrush restoration efforts in areas where medusahead and cheatgrass are present in the seedbank. Sites were selected on clay soil and sandy loam soils and the required field soil and seeds were collected. We completed the first year of a two year field experiment at Keystone Canyon on the impact of cheatgrass invasion on the persistence of native annual species. In preparation for determining the impacts of pinyon-juniper removal methods on the water balance, a site was instrumented with soil moisture probes in plots where the trees will be cut and burned and in control plots that will not be harvested. In addition to foreign exploration for natural enemies of target weeds in their native ranges and subsequent testing for host-specificity and impact (done in collaboration with colleagues in Europe, Agreement No. 5325-22000-023-05S), natural enemies of target weeds have been collected, identified, and studied here in the invaded range. A white rust fungus was collected from two perennial pepperweed populations in Nevada. Similar collections were made by collaborators at California Department of Food and Agriculture and samples were provided to us for laboratory study. Species identification was performed in collaboration with Nevada Department of Agriculture for these four isolates and greenhouse experiments of the host-specificity of the two Nevada isolates were conducted. On single-leaf pinyon pine, a species in the "pinyon-juniper" complex of invasive trees, larvae of the sawfly Neodiprion edulicolis were collected from an outbreak in central Nevada and are being studied in the laboratory. Studies of the ecology and insect diversity are ongoing in Great Basin invasions of both medusahead and saltcedar. Molecular genetic studies of perennial pepperweed and cheatgrass are continuing while molecular biology studies were initiated on medusahead as well as tamarisk beetles, which were released as biological control agents against saltcedar.

4. Accomplishments

Review Publications
Chen, L.Z., Liang, G.M., Zhang, J., Wu, K.M., Guo, Y.Y., Rector, B.G. 2010. Proteomic analysis of novel Cry1Ac binding proteins in Helicoverpa armigera (Hübner). Archives of Insect Biochemistry and Physiology. 73:61-73.

Clements, C.D., Henderson, D., Young, J.A. 2010. Basin wildrye: the forgotten grass revisited. The Progressive Rancher. 20(2):24-25.

Clements, D.D., Young, J.A., Harmon, D.N., Mccuin, G. 2010. Revegetation of disturbed winter fat communities. Rangelands. 32(5):37-40.

Hultine, K.R., Belnap, J., Van Riper III, C., Ehleringer, J.R., Dennison, P.E., Lee, M.E., Nagler, P.L., Snyder, K.A., Uselman, S.M., West, J.B. 2010. Tamarisk biocontrol in the western United States: ecological and societal implications. Frontiers in Ecology and the Environment. 8(9):467-474.

Rector, B.G., De Biase, A., Cristofaro, M., Primerano, S., Belvedere, S., Antonini, G., Sobhian, R. 2010. DNA fingerprinting to improve data collection efficiency and yield in an open-field host-specificity test of a weed biological control candidate. Journal of Invasive Plant Science and Management. 3:429-439.

Perez-Quezada, J.F., Delpiano, C., Franck, N., Snyder, K.A., Johnson, D.A. 2011. Carbon pools in an arid shrubland in Chile under natural and afforested conditions. Journal of Arid Environments. 75:29-37.

Uselman, S.M., Snyder, K.A., Blank, R.R. 2010. Insect biological control accelerates leaf litter decomposition and alters short-term nutrient dynamics in a Tamarix-invaded riparian ecosystem. Oikos. 120:409-417.

Snyder, K.A., Uselman, S.M., Jones, T.J., Duke, S. 2010. Ecophysiological responses of salt cedar (Tamarix spp. L.) to the northern tamarisk beetle (Diorhabda carinulata Desbrochers) in a controlled environment. Biological Invasions. 12:3795-3808.

Nagler, P.L., Shafroth, P.B., Labaugh, J.W., Snyder, K.A., Scott, R.L., Merritt, D.M., Osterberg, J. 2010. The potential for water savings through the control of saltcedar and russian olive. In: Shafroth, P.B., Brown, C.A., Merritt, D.M., editors. Saltcedar and Russian Olive Control Demonstration Act Science Assessment. USGS Scientific Investigations Report 2009-5247. p. 35-47.

Clements, D.D., Harmon, D.N., Young, J.A. 2010. Diffuse knapweed (Centaurea diffusa) seed germination. Weed Science. 58(4):369-373.

Uselman, S.M., Snyder, K.A., Blank, R.R., Jones, T.J. 2011. UVB exposure does not accelerate rates of litter decomposition in a semiarid riparian ecosystem. Soil Biology and Biochemistry. 43:1254-1265.

Last Modified: 10/15/2017
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