Diet of the Mogollon vole as indicated by stable-isotope analysis (δ 13 C and δ 15 N)

There are no published studies on the diet of Mogollon voles ( Microtus mogollonensis ) although this species occurs throughout the Southwest in montane forestlands. Mogollon voles are believed to be herbivorous, selecting the vegetative portion of grass as their dominant food source. Herbivores frequently select more easily digested C 3 plants over C 4 plants; we thus expected Mogollon voles would feed primarily on C 3 plants. We collected hair samples from Mogollon voles captured in northern Arizona between 1967 and 2003 and plant samples from some capture sites. Then we compared stable carbon (δ 13 C) and nitrogen (δ 15 N) isotope ratios to investigate dietary preferences for C 3 or C 4 plants. Mean isotope ratios for C 3 plants we sampled were –26.84‰ ( s = 0.17) for δ 13 C and –0.02‰ ( s = 0.32) for δ 15 N. For C 4 plants, mean isotope ratios for δ 13 C and δ 15 N were –15.04 ‰ ( s = 0.38) and –0.74‰ ( s = 0.55), respectively. Mogollon voles were largely herbivorous based on δ 15 N (mean and standard error: 3.77 ± 0.17‰) and used C 3 plants more than C 4 based on δ 13 C (–24.21 ± 0.14‰). Activities that lead to changes in plant species composition or reduction in C 3 plants in montane grasslands and forests (e.g., excessive ungulate grazing) may reduce habitat quality for Mogollon voles.     

Avian use of desert wildlife water developments as determined by remote videography

In the desert Southwest, migrating birds have been documented using upland habitat and xeroriparian washes as well as riparian areas. Yet aside from the river corridors, natural water sources (e.g., natural rock tanks [tinajas], springs, and ephemeral washes) in upland areas are scarce. Because of this scarcity, state and federal resource managers augmented water sources throughout the Southwest by constructing permanent wildlife water developments with the intention of enhancing game populations. However, despite these increases in free-standing water, there is a paucity of information on the use of water by birds during migration. Our objectives were to document use of these wildlife water developments by resident and migratory songbirds and assess the effectiveness of monitoring these species using remote color videography. We placed color video cameras at 2 wildlife water developments in southwestern Arizona during the spring and fall of 2004. Although we observed more use by migrants during spring than fall, overall use by migratory birds was low. However, the wildlife water developments were frequently used by resident birds. Remote videography provided continuous information on daily and seasonal patterns of bird use at wildlife water catchments with negligible disturbance by observers, yet for passerines, we felt that the benefits of remote videography did not justify the high cost of equipment purchase, installation, maintenance, and data processing.