• 1 January 1976
    • journal article
    • research article
    • Vol. 10 (2), 44-53
Abstract
In 1973, 119 bats of 3 spp. were collected from 4 localities in Maryland (Md.) and West Virginia (W.Va.) [USA]. The collection included 43 big brown bats (Eptesicus fuscus), 43 little brown bats (Myotis lucifugus) and 33 eastern pipistrelles (Pipistrellus subflavus). The bats were collected from Round Top Mountain, Washing Co. [County], Md.; Trout Cave, Pendleton Co., W. Va.; Montpelier Barn, Prince Georges Co., Md. and North East Methodist Church in Cecil Co., Md. Residues of .SIGMA.DDT were highest in carcasses of bats from Round Top Mountain, which is surround by apple orchards. Bats from Trout Cave had the lowest residues, a circumstance which probably reflects the absence of agriculture and industry in the area. A polychlorinated biphenyl (PCB) and oxychlordane were highest at Montpelier Barn. Sources of the PCB are unknown, but chlordane is used against termites and in gardening at nearby housing developments. Residues in bats from North East Methodist Church were low except for dieldrin. Among species, little brown bats usually had the highest residue concentrations in their carcasses; big brown bats had the lowest. When DDE in carcass fat of all species was > 60-90 ppm, it became measurable in brain tissue. Above 60-90 ppm, DDE levels in brains rose with increasing levels in carcass lipids. Residues of the PCB tended to respond similarly. Residue levels in brains were greatest in little brown bats; the maximum level of the PCB, 7.9 ppm, was more than twice that of DDE. [According to other authors, organochlorine insecticides may have caused declines in bat populations.].