@article {1478,
	title = {The effects of rainforest canopy loss on arboreal dung beetles in Borneo: implications for the measurement of biodiversity in derived tropical ecosystems},
	journal = {Diversity and Distributions},
	volume = {4},
	year = {1998},
	pages = {167-173},
	keywords = {ainforest canopy, arthropods, diversit, Dung beetles, selectiv logging, species richness},
	author = {Davis, A. J. and Sutton, S. L.}
}
@article {1744,
	title = {Resource partitioning in six guilds of dung-inhabiting beetles (Coleoptera)},
	journal = {Annales Entomologici Fennici},
	volume = {45},
	number = {1},
	year = {1979},
	note = {Using Smart Source ParsingillustrArticle},
	pages = {1-12},
	keywords = {arthropods, Coleopterans/Beetles, insects, Invertebrates},
	author = {Hanski, I. and Koskela, H.}
}
@inbook {1746,
	title = {Elevational distributions of dung and carrion beetles in northern Sulawesi},
	booktitle = {Insects and the rain forests of South East Asia},
	year = {1990},
	note = {Using Smart Source Parsing1 343. Chapter pagination: 145 152, illustrEnglishBook Chapter},
	pages = {145-152},
	keywords = {arthropods, Coleopterans/Beetles, insects, Invertebrates},
	author = {Hanski, I. and Niemela, J.},
	editor = {Knight, W. J. and Holloway, J. D.}
}
@article {1978,
	title = {Biogeografia de areas y biogeografia de artropodos holarticos y mediterraneos},
	journal = {Boletin de la Sociedad Entomologica Aragonesa},
	volume = {26},
	year = {1999},
	pages = {535-560},
	keywords = {arthropods, dispersal, historical biogeography, holartic region, phylogeny, vicariance},
	author = {Martin-Piera, Fermin and Sanmartin, Isabel}
}
@article {1676,
	title = {Elevation and climatic tolerance: a test using dung beetles},
	journal = {Oikos},
	volume = {86},
	number = {3},
	year = {1999},
	note = {Times Cited: 8Cited Reference Count: 47Cited References:      ALLEE WC, 1949, PRINCIPLES ANIMAL EC     BENNETT AF, 1997, EVOLUTION, V51, P36     BLOCK W, 1982, COMP BIOCHEM PHYS A, V73, P581     BLOCK W, 1990, PHILOS T ROY SOC B, V326, P613     BRATTSTROM BH, 1968, COMP BIOCHEM PHYSIOL, V24, P93     CHOWN SL, 1999, IN PRESS BIOL REV     CHOWN SL, 1992, S AFR J ANTARCT RES, V22, P51     DAVIS ALV, 1997, AFR J ECOL, V35, P10     DAVIS ALV, IN PRESS J BIOGEOGR     DENLINGER DL, 1991, INSECTS LOW TEMPERAT, P131     DOBZHANSKY T, 1950, AM SCI, V38, P209     EDNEY EB, 1971, J EXP BIOL, V55, P253     FERGUSON SH, 1996, ECOGRAPHY, V19, P382     FLEISHMAN E, 1998, ECOLOGY, V79, P2482     GASTON KJ, 1999, OIKOS, V84, P309     GASTON KJ, 1998, TRENDS ECOL EVOL, V13, P70     HOCHACHKA PW, 1984, BIOCH ADAPTATION     HODKINSON ID, 1996, FUNCT ECOL, V10, P314     HOFFMANN AA, 1995, TRENDS ECOL EVOL, V10, P1     HUEY RB, 1996, ANIMALS TEMPERATURE, P205     JAMES AC, 1997, GENETICS, V146, P881     JANZEN DH, 1967, AM NAT, V101, P233     JOHNSTON IA, 1996, ANIMALS TEMPERATURE     KLOK CJ, 1998, J INSECT PHYSIOL, V44, P615     KLOK CJ, 1997, J INSECT PHYSIOL, V43, P685     KLOK CJ, 1998, J THERM BIOL, V23, P131     LEE RE, 1991, INSECTS LOW TEMPERAT, P17     LUTTERSCHMIDT WI, 1997, CAN J ZOOL, V75, P1553     LUTTERSCHMIDT WI, 1997, CAN J ZOOL, V75, P1561     MELLANBY K, 1932, J EXP BIOL, V9, P222     MILLER K, 1982, COMP BIOCHEM PHYS A, V73, P595     MITCHELL JD, 1993, J INSECT PHYSIOL, V39, P523     MONGOLD JA, 1996, ANIMALS TEMPERATURE, P239     MULLER MJ, 1982, SELECTED CLIMATIC DA     PURVIS A, 1995, COMPUT APPL BIOSCI, V11, P247     RAPOPORT EH, 1982, AREOGRAPHY GEOGRAPHI     ROBERTS CS, 1991, PHYSIOL ENTOMOL, V16, P463     ROSENBERG NJ, 1983, MICROCLIMATE BIOL EN     RUGGIERO A, 1998, BIOL J LINN SOC, V63, P283     SNYDER GK, 1975, AM NAT, V109, P93     SOMME L, 1989, BIOL REV, V64, P367     SOMME L, 1982, COMP BIOCH PHYSL A, V73, P519     SOMME L, 1991, INSECTS LOW TEMPERAT, P318     STANLEY SM, 1980, AUST J ZOOL, V28, P413     STEVENS GC, 1992, AM NAT, V140, P893     STEVENS GC, 1989, AM NAT, V133, P240     STOREY KB, 1996, ANNU REV ECOL SYST, V27, P365EnglishArticle230JNOIKOS},
	month = {Sep},
	pages = {584-590},
	abstract = {An increase in the altitudinal range of occurrence of species in an assemblage with increasing elevation has been explained as a consequence of individual organisms having to be able to withstand a broader range of climatic conditions at higher elevations; the climatic variability hypothesis. Here we show that for scarab dung beetles (26 species) across an elevational transect (approx. 2500 In) in southern Africa thermal tolerance range does increase with increasing elevation across individuals and across species. The maximal thermal tolerance range exhibited increases slowly with elevation and the minimum range increases more rapidly. The mechanistic basis of the change appears to be one of rapidly changing critical thermal minimum (CTmin) with elevation and only small changes in critical thermal maximum (CTmax). Of course, even if the pattern of tolerance of species assumed by the climatic variability hypothesis is correct, an increase in altitudinal range with increasing elevation need not necessarily follow. However, although sampling has been limited, there does appear to be an elevational increase in altitudinal range for this species assemblage.},
	keywords = {arthropods, cold-hardiness, critical thermal maximum, desert, drosophila-melanogaster, latitudinal gradient, lepidoptera, namib, rapoports rule, temperature tolerance, tenebrionid beetles, terrestrial},
	url = {<Go to ISI>://000082248200019},
	author = {Gaston, K. J. and Chown, S. L.}
}
@article {2150,
	title = {Game and cattle trampling, and impacts of human dwellings on arthropods at a game park boundary},
	journal = {Biodiversity and Conservation},
	volume = {5},
	year = {1996},
	pages = {1545-1556},
	abstract = {Seven grassland sites were sampled at South Africa{\textquoteright}s Hluhluwe-Umfolozi Game Park boundary with the surrounding land, to assess changes in arthropod diversity in response to land use. Epigaeic arthropods were sampled using pitfall traps and a sweep net. In all, 262 morphospecies were collected, but this is an underestimate of total local species richness. Fifty percent of the species caught were single occurrences. The number of species, families and orders represented at each of the seven sites was not significantly different, but the number of individuals was significantly different. Between-site comparisons, using multivariate statistics, did not reveal any strong site groupings, with all sites being unique. The conclusion is that the reserve boundary does not significantly divide arthropod diversity on a simple inside-versus-outside basis. A major factor influencing the arthropod assemblages was intensity of land use. Indigenous game animals and domestic cattle had the same effect, and it was the intensity of trampling that was important rather than the type of trampling. Human settlements had a major impoverishing effect. The Coleoptera families, Cicindelidae, Staphylindae and Carabidae, were particularly sensitive indicator taxa of land use. Scarabaeidae species were the only group that were severely affected by the fence boundary, simply because their food source, the faeces of large native mammals, was inside, leaving them without resources outside the reserve.},
	keywords = {arthropods, boundary., Game Park, impacts, south africa, trampling},
	author = {Rivers-Moore, N. A. and Samways, M. J.}
}
