Introducing spatial grazing impacts into the prediction of moorland vegetation dynamics

Grazing by large herbivores is a major determinant of vegetation dynamics in many semi-natural ecosystems, including ghe replacement of heather moorland by rough grassland in the British uplands. Herbivore foraging is influenced by vegetation patterns and, in turn, their grazing drives vegetation dynamics. Although vegetation impacts are local, spatially heterogeneous local impacts can have different conseqences as would the same impact distributed uniformly. We constructed a simulation model of the spatial effects of grazing by sheep on the vegetation dynamics of heather moorland, a vegetation community of international conservation importance in the UK. The model comprised three sub-models to predict (1) annual average heather utilisation, (2) spatial variation in heather utilisation (higher near the edge of grass patches) and (3) competition between heather and grass. Here we compare the predicted heather utilisation and vegetation dynamics of the spatial model, relative to those of a non-spatial model. The spatial model resulted in a reduced loss of heather cover for a given sheep stocking rate. The model demonstrtaes how spatial interactions between large herbivores and their forage drive vegetation dynamics, leading to changes in community structure and composition. Indeed, omitting spatial effects in grazing models may lead to inaccurate predictions. We have shown that ecosystem modelling, based around an iterative dialogue between developers and experienced researchers, has the potential to make a substantial contribution towards the conservation and management of vulnerable landscapes. Combining modelling with experimental studies will facilitate progress towards understanding long-term vegetation/herbivore dynamics.     

Seismic Cutlines,Changing Landscape Metrics and Grizzly Bear Landscape use in Alberta

Besides providing habitat to the grizzly bear (Ursus arctos) and other wildlife, the Rocky Mountain foothills of Alberta, Canada hosts considerable mining, seismic oil and gas exploration and production, and forest harvesting activities. Worldwide, such human activities influence the configuration and composition of the landscape. We assessed seismic cutline effects on landscape structure and grizzly bear use during early summer of 1999 and 2000. We studied five female and two male bears, which were GPS-collared in the spring following den emergence. The area available to this population was stratified into 49 km² hexagon-shaped sub-landscapes. The scale of this stratification was determined by patterns of bear movement. Fourteen compositional and configurational landscape metrics were calculated within each landscape unit, and bear use points were pooled or ‘binned’ within each unit. Landscape use was related to landscape metrics using a Generalized Linear Model (GLM). We found that seismic cutline proportion did not explain landscape use by grizzly bears; however secondary effects of cutlines on landscape structure did. Declining use was mainly associated with increasing proportions of closed forest, and increasing variation of inter-patch distances, while use was mainly increasing with increasing mean patch size. An earlier investigation had demonstrated that adding seismic cutlines to grizzly bear habitat caused increases in the variation of inter-patch distances. Since the landscape structure of this grizzly bear population will continue to change as a function of increased levels of resource extraction activities in the near future, it is crucial to further study the detailed meaning of landscape structure at the large and small scale for effective conservation efforts.     

Serosurvey of horses with evidence of equine monocytic ehrlichiosis

In August 1986, an extensive serosurvey for prevalence of IgG and IgM antibodies against Ehrlichia risticii, the causative agent of equine monocytic ehrlichiosis (EME), was performed at 2 Ohio racetracks, River Downs (RD) and Beulah Park (BP). Of 840 horses at RD and 574 at BP, 13 and 20%, respectively, were IgG antibody-positive (by indirect fluorescent antibody test results), with antibody titer ranging from 1:20 to 1:10,240. The titer observed at highest frequency at both racetracks was 1:80. A higher proportion of horses was ill at RD (operating during the summer months) than at BP (winter track). Of ill horses, 41% (24/58) at RD and 58% (11/19) at BP were seropositive. At RD, 70% (589/840) of all horses and 95% (102/107) of IgG seropositive horses had been stabled only at RD during the month prior to testing. Analysis of these sera by use of an ELISA to detect IgM antibody against E risticii antigen indicated that at RD, 42% (57/137) of the seropositive horses were IgM seropositive. At BP, 17% (20/120) of seropositive horses were IgM seropositive. The larger number of IgM seropositive horses at RD indicates that more horses were recently infected at RD than at BP (P = 0.0001). Therefore, at least half the seropositive horses at RD seemed to have acquired the infection at RD. These serosurvey data also indicate that at BP and RD, 78% (85/109) and 91% (111/122) of IgG seropositive horses, respectively, had subclinical infection. At less than or equal to 1:40 titer, there was no difference in seropositive rates between healthy and ill horses.(ABSTRACT TRUNCATED AT 250 WORDS)     

Tularaemia transmitted by ticks (Dermacentor andersoni) in Saskatchewan.

Common wood ticks (Dermacentor andersoni) collected from Saskatchewan Landing Provincial Park, Saskatchewan in the spring of 1982 transmitted a lethal tularaemia infection to four of six rabbits. Francisella tularensis organisms were isolated from tissues taken from the dead rabbits and identified from subcultures using an indirect immunofluorescent antibody assay. One human associated with the animals developed symptoms of tularaemia and, after successful therapy, had a significant increase in titre of specific antibodies to F. tularensis. This is the first time tick-transmitted tularaemia has been reported in Saskatchewan in more than 25 years.