From January 1999 to April 2002, 14 free-ranging elk were darted with a mixture of Telazol reconstituted with xylazine hydrochloride (HCl) in a forested habitat in southwestern Oklahoma and north-central Arkansas. Elk were darted from ground blinds, tree stands, or a vehicle at distances of 14-46 m and were recovered 37-274 m from the dart site. Elk were located using radiotelemetry with 3-cc disposable Pneu-dart transmitter darts. MeanϮSD dose of Telazol and xylazine HCl was 590Ϯ192 mg/ml and 276Ϯ153 mg/ml, respectively, and mean time to standing after injection of reversal agent was 27 min (range: 1-65 min). The combination of Telazol and xylazine HCl successfully immobilized free-ranging elk, and transmitter-equipped darts permitted successful location of sedated elk by two people in areas of dense forest cover. The dose required to sedate elk appeared to vary depending on physiology and behavior, but no drug-induced mortality occurred despite the wide variance in the doses administered. We recommend 500 mg Telazol reconstituted with 300 mg xylazine HCl as an initial dose for a Ն200 kg elk. If needed to achieve full sedation, up to 3 additional ml of the mixture may be administered without adverse effects.

We used spatial data to identify potential areas for elk (Cervus elaphus) restoration in Arkansas. To assess habitat, we used locations of 239 elk groups collected from helicopter surveys in the Buffalo National River area of northwestern Arkansas, USA, from 1992 to 2002. We calculated the Mahalanobis distance (D2) statistic based on the relationship between those elk‐group locations and a suite of 9 landscape variables to evaluate winter habitat in Arkansas. We tested model performance in the Buffalo National River area by comparing the D2 values of pixels representing areas with and without elk pellets along 19 fixed‐width transects surveyed in March 2002. Pixels with elk scat had lower D2 values than pixels in which we found no pellets (logistic regression: Wald χ2 = 24.37, P < 0.001), indicating that habitat characteristics were similar to those selected by the aerially surveyed elk. Our D2 model indicated that the best elk habitat primarily occurred in northern and western Arkansas and was associated with areas of high landscape heterogeneity, heavy forest cover, gently sloping ridge tops and valleys, low human population density, and low road densities. To assess the potential for elk‐human conflicts in Arkansas, we used the analytical hierarchy process to rank the importance of 8 criteria based on expert opinion from biologists involved in elk management. The biologists ranked availability of forage on public lands as having the strongest influence on the potential for elk‐human conflict (33%), followed by human population growth rate (22%) and the amount of private land in row crops (18%). We then applied those rankings in a weighted linear summation to map the relative potential for elk‐human conflict. Finally, we used white‐tailed deer (Odocoileus virginianus) densities to identify areas where success of elk restoration may be hampered due to meningeal worm (Parelaphostrongylus tenuis) transmission. By combining results of the 3 spatial data layers (i.e., habitat model, elk‐human conflict model, deer density), our model indicated that restoration sites located in west‐central and north‐central Arkansas were most favorable for reintroduction.

ABSTRACT:Surveys for disease agents were conducted in introduced free-ranging elk (Cervus elaphus nelsoni) in Arkansas and Kentucky. Elk had been captured in Colorado and Nebraska and released in Arkansas during [1981][1982][1983][1984][1985]. From 1997 through 2002 elk were captured in Arizona, Kansas, North Dakota, New Mexico, Oregon, and Utah and released in southeastern Kentucky. Specimens were collected from 170 hunter-killed elk in Arkansas during 1998 , and 44 elk in Kentucky during 2001. Significant findings included isolation of Mycobacterium avium paratuberculosis from one elk in Kentucky and evidence of previous or current infections by Parelaphostrongylus tenuis in several animals in Arkansas. Serological tests provided evidence of previous infection by epizootic hemorrhagic disease virus, bluetongue virus, bovine viral diarrhea virus, infectious bovine rhinotracheitis virus, parainfluenza-3 virus, and multiple serovars of Leptospira interrogans. Mycobacterium bovis, Brucella abortus, chronic wasting disease (CWD), and hemoparasites such as Anaplasma spp. were not detected. Results from elk obtained through these surveys were consistent with exposure to disease agents endemic in livestock and wildlife in Arkansas and Kentucky.

In order to be able to track the movement of pollutant plumes during geotechnical centrifuge and other geo-environmental experiments, a number of techniques have been investigated: fibre-optic photometric sensors, resistivity probes, resistivity tomography, and copper ion-selective electrodes. Methods of image analysis, signal processing techniques and multi-spectral image analysis were also explored and applied to images of moving plumes. In addition, an optical technique for detecting NAPL by cone probe was investigated. Their relative merits are discussed. This work was conducted as part of an EU-funded network programme: NECER (Network of European geotechnical Centrifuges for Environmental Research), and this paper summarises the conclusions of the sensors and imaging working group.

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