@article {1310,
	title = {Decomposition of Elephant Dung in an Arid, Tropical Environment},
	journal = {Oecologia},
	volume = {14},
	year = {1974},
	note = {have copy},
	pages = {111-125},
	keywords = {decomposition, dung beetle, ecological function, ecosystem service, Scarabaeinae},
	author = {J. M. Anderson and M. J. Coe}
}
@article {1324,
	title = {Effects of dung and seed size on secondary dispersal, seed predation, and seedling establishment of rain forest trees},
	journal = {Oecologia},
	volume = {139},
	number = {1},
	year = {2004},
	note = {801LKOECOLOGIA},
	month = {Mar},
	pages = {45-54},
	abstract = {Seeds dispersed by tropical, arboreal mammals are usually deposited singly and without dung or in clumps of fecal material. After dispersal through defecation by mammals, most seeds are secondarily dispersed by dung beetles or consumed by rodents. These post-dispersal, plant-animal interactions are likely to interact themselves, as seeds buried by dung beetles are less likely to be found by rodents than unburied seeds. In a series of three experiments with seeds of 15 species in central Amazonia (Brazil), we determined (1) how presence and amount of dung associated with seeds influences long-term seed fate and seedling establishment, (2) how deeply dung beetles bury seeds and how burial depth affects seedling establishment, and (3) how seed size affects the interaction between seeds, dung beetles, and rodents. Our overall goal was to understand how post-dispersal plant-animal interactions determine the link between primary seed dispersal and seedling establishment. On average, 43\% of seeds surrounded by dung were buried by dung beetles, compared to 0\% of seeds not surrounded by dung (n=2,156). Seeds in dung, however, tended to be more prone than bare seeds to predation by rodents. Of seeds in dung, probability of burial was negatively related to seed size and positively related to amount of dung. Burial of seeds decreased the probability of seed predation by rodents three-fold, and increased the probability of seedling establishment two-fold. Mean burial depth was 4 cm (0.5-20 cm) and was not related to seed size, contrary to previous studies. Probability of seedling establishment was negatively correlated with burial depth and not related to seed size at 5 or 10 cm depths. These results illustrate a complex web of interactions among dung beetles, rodents, and dispersed seeds. These interactions affect the probability of seedling establishment and are themselves strongly tied to how seeds are deposited by primary dispersers. More generally, our results emphasize the importance of looking beyond a single type of plant-animal interaction (e.g., seed dispersal or seed predation) to incorporate potential effects of interacting interactions.},
	keywords = {alouatta-palliata, beetles scarabaeidae, Central Amazonia, communities, ecology, fate, horse dung, howler monkeys, los-, plant, plant-animal interactions, rain forest, recruitment, seed, tuxtlas},
	url = {<Go to ISI>://000220097200006},
	author = {Andresen, Ellen and Levey, Douglas J.}
}
@article {1352,
	title = {Effects of forest fragmentation on the beetle assemblage at the relict forest of Fray Jorge, Chile},
	journal = {Oecologia},
	volume = {132},
	number = {2},
	year = {2002},
	month = {Jul},
	pages = {296-306},
	abstract = {Habitat fragmentation is recognized as one of the main factors associated with species extinction and is particularly acute in South American forest habitats. In this study, we examined the effects of forest fragmentation on the beetle assemblage at the relict temperate forest of Fray Jorge (Chile). We evaluated the following hypotheses: (1) there is a strong edge effect, so that the number of beetle species and individuals increases away from the edge, towards the inner part of each fragment, (2) this pattern should be apparent in the larger fragments but not in the smaller ones, where edge effects are expected to be stronger, and (3) there should be a significant interaction between number of species/individuals found inside and outside fragments (i.e., in the matrix) and season, because of an increase in aridity and water stress during austral summer months. We found that the relationship between the number of individuals and number of species vs distance from the matrix towards the forest interior was affected by fragment size and season. In general, both number of species and individuals tended to increase from the matrix towards the forest edge and then either decrease, increase or maintain a constant level, depending on fragment size and season. The result of an ANOVA analysis, which used season, size, and position (inside vs outside fragments) as factors and number of individuals as the response variable, showed a significant effect of fragment size, position, and season and a significant interaction between fragment size and season, season and position, and size and position. ANOVA analysis using number of species as the response variable showed that area, season, and position all had significant effects. The results also showed a significant interaction between size and season and between season and position. Our results emphasize the existence of strong fragment-size and seasonal effects modulating both the response of beetles to fragmentation and their abundance and distribution in temperate areas. Thus, seasonal dynamic effects can be of paramount importance to demonstrate and understand the effect of habitat fragmentation upon arthropod assemblages in temperate areas.},
	keywords = {Dung beetles, fragmentation, South America, temperate forests},
	author = {Barbosa, Olga and Marquet, Pablo A.}
}
@article {1438,
	title = {Patterns of daily flight activity in onitine dung beetles (Scarabaeinae: Onitini)},
	journal = {Oecologia},
	volume = {103},
	number = {4},
	year = {1995},
	pages = {444-452},
	keywords = {Diel activity, Dung beetles, Endothermy, Flight behaviour},
	author = {Caveney, Stanley and Scholtz, Clarke H. and McIntyre, Peter}
}
@article {1459,
	title = {Ungulate community structure and ecological processes: body size, hoof area and trampling in African savannas},
	journal = {Oecologia},
	volume = {134},
	number = {4},
	year = {2003},
	note = {Times Cited: 0Cited Reference Count: 37Cited References:      ABDELMAGID AH, 1987, J RANGE MANAGE, V40, P303     ABDELMAGID AH, 1987, J RANGE MANAGE, V40, P307     ALTMANN SA, 1987, J ZOOL, V211, P215     BARDSLEY WG, 2001, SIMFIT REFERENCE MAN     BENNETT MB, 1999, J ZOOL 3, V247, P365     BROWN JH, 2000, SCALING BIOL     CALDER WA, 1984, SIZE FUNCTION LIFE H     COE MJ, 1976, OECOLOGIA, V22, P341     COLLINSON RFH, 1982, INKWE, V1, P1     CUMMING DHM, 1982, ECOLOGY TROPICAL SAV, P217     CUMMING DHM, 1997, S AFR J SCI, V93, P231     CUMMING DHM, 1999, STUDY DEV TRANSBOUND     DADKHAH M, 1980, WATER RESOUR BULL, V16, P979     DAMUTH J, 1981, BIOL J LINN SOC, V15, P185     ECKERT RE, 1986, J RANGE MANAGE, V39, P414     FRITZ H, 1994, P ROY SOC LOND B BIO, V256, P77     GARLAND T, 1983, AM NAT, V121, P571     GIFFORD GF, 1980, UTAH AGR EXP STN RES, V50, P1     JOLICOEUR P, 1990, J THEOR BIOL, V144, P257     LABARBERA M, 1989, ANNU REV ECOL SYST, V20, P97     LAWS RM, 1970, OIKOS, V21, P1     LAWTON JH, 1994, OIKOS, V71, P367     LULL HW, 1959, USDA FOREST SERV MIS, V768, P1     MENTIS MT, 1981, VELD PASTURE MANAGEM, P287     OWENSMITH RN, 1988, MEGAHERBIVORES INFLU     OWENSMITH RN, 1993, P 17 INT GRASSL C NZ, V1, P691     PETERS RH, 1983, ECOLOGICAL IMPLICATI     PLUMPTRE AJ, 1993, AFR J ECOL, V32, P115     PROTHERO J, 1986, J THEOR BIOL, V118, P259     SKINNER JD, 1990, MAMMALS SO AFRICAN S     SMITHERS RHN, 1983, MAMMALS SO AFRICAN S     SOKAL RR, 1995, BIOMETRY PRINCIPLES     SPRUGEL DG, 1983, ECOLOGY, V64, P209     SSEMAKULA J, 1983, AFR J ECOL, V21, P325     VILJOEN PJ, 1990, S AFR J WILDL RES, V20, P65     WARREN SD, 1986, J RANGE MANAGE, V39, P491     WESTERN D, 1979, AFR J ECOL, V17, P185EnglishArticle655ZDOECOLOGIA},
	month = {Mar},
	pages = {560-568},
	abstract = {A wide range of bioenergetic, production, life history and ecological traits scale with body size in vertebrates. However, the consequences of differences in community body-size structure for ecological processes have not been explored. We studied the scaling relationships between body mass, shoulder height, hoof area, stride length and daily ranging distance in African ungulates ranging in size from the 5 kg dik-dik to the 5,000 kg African elephant, and the implications of these relationships on the area trampled by single and multi-species herbivore communities of differing structure. Hoof area, shoulder height and stride length were strongly correlated with body mass (Pearson{\textquoteright}s r >0.98, 0.95 and 0.90, respectively). Hoof area scaled linearly to body mass with a slope of unity, implying that the pressures exerted on the ground per unit area by a small antelope and an elephant are identical. Shoulder height and stride length scaled to body mass with similar slopes of 0.32 and 0.26, respectively; larger herbivores have relatively shorter legs and take relatively shorter steps than small herbivores, and so trample a greater area of ground per unit distance travelled. We compared several real and hypothetical single- and multi-species ungulate communities using exponents of between 0.1 and 0.5 for the body mass to daily ranging distance relationship and found that the estimated area trampled was greater in communities dominated by larger animals. The impacts of large herbivores are not limited to trampling. Questions about the ecological implications of community body-size structure for such variables as foraging and food intake, dung quality and deposition rates, methane production, and daily travelling distances remain clear research priorities.},
	keywords = {African herbivores, allometry, body mass, ecosystems, elephants, infiltration, livestock, mammals, pressures, scaling, soil, vegetation},
	url = {<Go to ISI>://000181582700014},
	author = {Cumming, D. H. M. and Cumming, G. S.}
}
@article {1524,
	title = {Altered leaf-litter decomposition rates in tropical forest fragments},
	journal = {Oecologia},
	volume = {116},
	number = {3},
	year = {1998},
	note = {121VDOECOLOGIA},
	month = {Sep},
	pages = {397-406},
	abstract = {The effects of forest fragmentation on leaf-litter decomposition rates were investigated for the first time in an experimentally fragmented tropical forest landscape in Central Amazonia. Leaf-litter decomposition rates were measured at seven distances (0-420 m) along forest edge-to-interior transects in two 100-ha fragments, two continuous forest edges, and at an identical series of distances along two deep continuous forest transects, as well as at the centers of two 1-ha and two 10-ha fragments. Decomposition rates increased significantly towards the edge of 100-ha forest fragments. Litter turnover times were 3-4 times faster within 50 m of the edge of 100-ha fragments than normally found in deep continuous forest. In contrast, there was no significant change in the rate of leaf-litter decomposition from the interior to the edge of continuous forest. It is difficult to account for these very different edge responses. Decomposition rates were not correlated with air temperature differentials, evaporative drying rates, litter depth, biomass or moisture content, or with total invertebrate densities, either within individual edge transects or across all sites. The difference in edge response may be due to chance, particularly the patchy removal of vast quantities of litter by litter-feeding termites, or may be a real, area-dependent phenomenon. Clearly, however, forest fragmentation increases the variability and unpredictability of litter decomposition rates near forest edges. In addition to edge effects, decomposition. rates were strongly affected by decreasing fragment area. While sites at the centers of 10-ha and 100-ha forest fragments and continuous forest had equivalent decomposition rates, rates were markedly lower at the centers of 1-ha fragments. Litter turnover times were 2-3 times slower in I-ha fragments than in continuous forest, and up to 13 times slower than at 100-ha edges. Litter structure and nutrient cycling dynamics are inevitably altered by forest fragmentation.},
	keywords = {forest change biodiversity dung beetles forest function},
	url = {<Go to ISI>://000076034600013},
	author = {Didham, R. K.}
}
@article {1549,
	title = {Discontinuous gas exchange in dung beetles: patterns and ecological implications},
	journal = {Oecologia},
	volume = {122},
	number = {4},
	year = {2000},
	note = {Times Cited: 11Cited Reference Count: 40Cited References:      BARTHOLOMEW GA, 1985, J COMP PHYSIOL B, V155, P155     BERNON G, 1981, THESIS U BOWLING GRE     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P22     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P36     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P51     CHOWN SL, 1995, FUNCT ECOL, V9, P30     DAVIS ALV, 1995, ACTA OECOL, V16, P641     DAVIS ALV, 1996, AGR ECOSYST ENVIRON, V58, P157     DOUBE BM, 1990, B ENTOMOL RES, V80, P259     DOUBE BM, 1983, B ENTOMOL RES, V73, P357     DOUBE BM, 1991, DUNG BEETLE ECOLOGY, P133     DUNCAN FD, 1997, PHYSIOL ENTOMOL, V22, P310     DUNCAN FD, 1993, PHYSIOL ENTOMOL, V18, P372     FERREIRA MC, 1972, REV ENT MOCAM, V11, P5     HADLEY NF, 1994, PHYSIOL ZOOL, V67, P175     HEINRICH B, 1979, PHYSIOL ZOOL, V52, P489     HOLTER P, 1991, PEDOBIOLOGIA, V35, P281     KESTLER A, 1985, ENV PHYSL BIOCH INSE, P137     KLOK CJ, 1994, THESIS U PRETORIA     LIGHTON JRB, 1996, ANNU REV ENTOMOL, V41, P309     LIGHTON JRB, 1991, CONCISE ENCY BIOL BI, P201     LIGHTON JRB, 1993, J COMP PHYSIOL B, V163, P11     LIGHTON JRB, 1995, J EXP BIOL, V198, P521     LIGHTON JRB, 1995, J EXP BIOL, V198, P1613     LIGHTON JRB, 1992, J EXP BIOL, V173, P289     LIGHTON JRB, 1991, J EXP BIOL, V159, P249     LIGHTON JRB, 1990, J EXP BIOL, V151, P71     LIGHTON JRB, 1988, J EXP BIOL, V134, P363     LIGHTON JRB, 1988, J INSECT PHYSL, V34, P361     LIGHTON JRB, 1994, PHYSIOL ZOOL, V67, P142     LIGHTON JRB, 1985, PHYSIOL ZOOL, V58, P390     MILLER PL, 1981, LOCOMOTION ENERGETIC, P367     OSBERG D, 1988, THESIS U WITWATERSRA     OSBERG DC, 1992, J ENTOMOL SOC S AFR, V55, P85     OSBERG DC, 1993, TROP ZOOL, V6, P243     PASCHALIDIS KM, 1974, THESIS RHODES U GRAH     SCHMIDTNIELSEN K, 1980, ANIMAL PHYSL ADAPTAT     SLAMA K, 1988, WOODS HOLE OCEANOGR, V175, P289     TRIBE GD, 1976, THESIS U NATAL PIETE     ZAR JH, 1984, BIOSTATISTICAL ANALEnglishArticle303YGOECOLOGIA},
	month = {Mar},
	pages = {452-458},
	abstract = {This study correlates a distinctive pattern of external gas exchanger referred to as the discontinuous gas exchange cycle (DGC), observed in the laboratory, with habitat associations of five species of telecoprid dung beetles. The beetles were chosen from a variety of habitats that would be expected to present different amounts of water stress. All five species exhibited DGC. Sisyphus fasciculatus has been recorded only in woodland areas, and does not have strict spiracular control during its DGC. Anachalcos convexus and Scarabaeus rusticus are associated with open mesic habitats. Both species exhibit a distinct DGC, previously found in some other insect species, but intermediate within this study group. Sc. flavicornis and Circellium bacchus are typically found in arid regions, and have the most unusual form of DGC with spiracular fluttering during the burst phase. These results support the hypothesis that spiracular fluttering reduces respiratory water loss. From this study we conclude that the DGC is an ancestral adaptation. most probably as a result of anoxic environments in underground burrows, but that spiracular control is enhanced to reduce respiratory water lass in beetle species that live in arid habitats.},
	keywords = {ant, COLEOPTERA, discontinuous gas exchange cycle, formicidae, habitat association, hymenoptera, namib desert, respiration, Scarabaeidae, Scarabaeinae, south-africa, telecoprid, tenebrionid beetles, terrestrial insects, ventilatory patterns},
	url = {<Go to ISI>://000086455000002},
	author = {Duncan, F. D. and Byrne, M. J.}
}
@article {1694,
	title = {Effects of brood parasitism on host reproductive success: evidence from larval interactions among dung beetles},
	journal = {Oecologia},
	volume = {134},
	number = {2},
	year = {2003},
	note = {Times Cited: 0Cited Reference Count: 57Cited References:      BEGON M, 1995, ECOLOGY INDIVIDUALS     BORNEMISSZA GF, 1971, PEDOBIOLOGIA, V11, P1     BORNEMISSZA GF, 1969, PEDOBIOLOGIA, V9, P223     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P156     CHAPMAN TA, 1869, ENTOMOL MONTH MAG, V5, P273     CLOUDSLEYTHOMPS.JL, 1991, ECOPHYSIOLOGY DESERT     CLUTTONBROCK TH, 1991, EVOLUTION PARENTAL C     DAVIS ALV, 1996, AFR J ECOL, V34, P258     DAY RW, 1989, ECOL MONOGR, V59, P433     DELLACASSA G, 1983, B MUS REG SCI NAT TO, V1, P1     DOUBE BM, 1990, ECOL ENTOMOL, V15, P371     GILLER PS, 1989, J ANIM ECOL, V58, P129     GITTINGS T, 1997, ECOGRAPHY, V20, P55     GITTINGS T, 1999, PEDOBIOLOGIA, V43, P439     GONZALEZMEGIAS A, 1999, THESIS U GRANADA GRA     HALFFTER G, 1966, FOLIA ENTOMOL MEXICO, V12, P1     HALFFTER G, 1982, NESTING BEHAV DUNG B     HAMMOND PM, 1976, COLEOPT B, V30, P245     HANSKI I, 1980, ANN ENTOMOL FENN, V46, P57     HIRSCHBERGER P, 1996, ECOL ENTOMOL, V21, P352     HIRSCHBERGER P, 1998, OECOLOGIA, V116, P136     HOLTER P, 1979, ECOL ENTOMOL, V4, P317     HOLTER P, 1982, OIKOS, V39, P213     HOWDEN HF, 1955, J TENNESSEE ACAD SCI, V30, P64     HOWDEN HF, 1963, P US NAT MUS, V114, P1     KLEMPERER HG, 1980, ECOLOGICAL ENTOMOLOG, V5, P143     KREBS JR, 1993, INTRO BEHAV ECOLOGY     LANDIN BO, 1961, OPUSC ENTOMOL LUND S, V19, P1     LUMARET JP, 1987, ACTA ZOOL MEX, V24, P1     LUMARET JP, 1989, B ECOLOGIE, V20, P51     MARTINPIERA F, 1993, ACTA ZOOLOGICA MEXIC, V57, P15     MARTINPIERA F, 1984, EOS, V60, P101     MUNSTERSWENDSEN M, 2000, ECOL ENTOMOL, V25, P63     NOYMEIR I, 1979, ISRAEL J BOT, V28, P1     PAULIAN R, 1982, ENCY ENTOMOLOGY, V43     PETANIDOU T, 1995, BIOL J LINN SOC, V55, P261     PITTINO R, 1986, GIORNALE ITALIANO EN, V3, P1     POLIS GA, 1991, AM NAT, V138, P123     RASA OAE, 1996, NATURWISSENSCHAFTEN, V83, P575     RICE WR, 1989, EVOLUTION, V43, P223     ROSENHEIM JA, 1989, BEHAV ECOL SOCIOBIOL, V25, P335     ROTHSTEIN SI, 1998, PARASITIC BIRDS THEI     ROUGON D, 1982, B SOC ENTOMOL FR, V87, P272     ROUGON D, 1980, CR ACAD SCI D NAT, V291, P417     ROUGON D, 1991, DUNG BEETLE ECOLOGY, P230     ROUGON D, 1980, REV ECOL BIOL SOL, V17, P379     SANCHEZPINERO F, 1994, THESIS U GRANADA GRA     SMITH JN, 2000, ECOLOGY MANAGEMENT C     SPOFFORD M, 1986, J NAT HIST, V26, P993     STEVENSON BG, 1985, COLEOPTERISTS B, V39, P215     TALLAMY DW, 1984, BIOSCIENCE, V34, P20     TORCHIO PF, 1992, ANN ENTOMOL SOC AM, V85, P713     TORCHIO PF, 1972, MELANDERIA, V10, P1     TRINE CL, 1998, PARASITIC BIRDS THEI, P273     TRUMBO ST, 1990, ECOL ENTOMOL, V15, P347     VOLLRATH F, 1984, STRATEGIES EXPLOTATI, P61     ZAR JH, 1996, BIOSTATISTICAL ANALEnglishArticle642UHOECOLOGIA},
	month = {Jan},
	pages = {195-202},
	abstract = {This paper investigates the effect of brood parasitism in a dung beetle assemblage in an arid region of Spain. The study was conducted during the spring season (March-May 1994-1998) using mesh cylinders buried into the ground, filled with sand and with sheep dung on top. We quantified the proportion of nests containing larvae of parasitic beetles and their effect on host larvae survival. Experiments on the effect of parasitic larvae on host-larvae survival were conducted by placing scarab brood masses (raised from captive scarabs in the laboratory) in containers with and without aphodiid larvae. During the spring, dung desiccation is rapid, preventing aphodiids nesting in the dung, and forcing these species to adopt brood parasitism as a nesting strategy. Parasitic aphodiids were found in 12-47\% of scarab nests of three species. The incidence of brood parasitization was positively related with the number of brood masses contained in the nests, being also higher in the most abundant species. Field data and experiments showed that brood parasites significantly reduced host larvae survival from 74.8\% in non-parasitized nests to 8.8\% in parasitized nests. Because different rates of nest parasitization and mortality were caused by parasites, brood parasitism had a differential effect on different host species. Thus, brood, parasitism constitutes an important mortality factor reducing the reproductive success of the host species and potentially affecting the beetle abundance in the area.},
	keywords = {abundance, aphodius ater, assemblage, cleptoparasite, COLEOPTERA, community, coprophagous beetles, desert ecology, hymenoptera, intraspecific competition, kleptoparasitism, Larval mortality, resource utilization, Scarabaeidae},
	url = {<Go to ISI>://000180822900005},
	author = {Gonzalez-Megias, A. and Sanchez-Pinero, F.}
}
@article {1742,
	title = {Niche Relations among Dung-Inhabiting Beetles},
	journal = {Oecologia},
	volume = {28},
	number = {3},
	year = {1977},
	note = {DG182OECOLOGIA},
	pages = {203-231},
	keywords = {Dung beetles},
	url = {<Go to ISI>://A1977DG18200001},
	author = {Hanski, I. and Koskela, H.}
}
@article {1764,
	title = {Spatial distribution, resource utilisation and intraspecific competition in the dung beetle Aphodius ater},
	journal = {Oecologia},
	volume = {116},
	year = {1998},
	month = {Apr},
	pages = {136-142},
	keywords = {aggregation, density dependence, dung beetle, egg-laying behaviour, Scarabaeidae},
	author = {Hirschberger, Petra}
}
@article {2163,
	title = {Distribution and abundance of dung beetles in fragmented landscapes},
	journal = {Oecologia},
	volume = {127},
	number = {1},
	year = {2001},
	note = {digital \& hard copy copy},
	month = {Mar},
	pages = {69-77},
	abstract = {Related species utilising similar resources are often assumed to show similar spatial population structures and dynamics. This paper reports substantial ecological variation within a set of Aphodius dung beetles occurring in the same patchily distributed resource, livestock dung in pastures. We show how variation in habitat and resource selectivity, in the rate of movements between pastures, and in the distribution of local population sizes all contribute to interspecific differences in spatial population structures. Local dung beetle assemblages are compared between two landscapes with different densities of pastures. In one of the landscapes, we contrast the abundances and regional distributions of Aphodius before and after 15 years of rapid habitat loss. Different species show very dissimilar responses to changes in the structure of the landscape. Our results suggest that generalist Aphodius species, and specialist species with high dispersal powers, occur as large "patchy" populations in the landscape. In contrast? a strict pasture specialist species with limited dispersal powers (A. pusillus) forms classical metapopulations. At the community level, interspecific differences in spatial population structures make the local community composition a function of the structure of the surrounding landscape.},
	keywords = {aphodius, APHODIUS SCARABAEIDAE, assemblage, COLEOPTERA, community, diversity, dynamics, europe mammals, habitat loss, metapopulation, patchy, population, resource utilization, serpentine, spatial population structure, stability},
	url = {<Go to ISI>://000167629200008},
	author = {Roslin, T. and Koivunen, A.}
}
@article {2195,
	title = {Factors Affecting Post-Dispersal Seed Survival in a Tropical Forest},
	journal = {Oecologia},
	volume = {76},
	number = {4},
	year = {1988},
	note = {Q0705OECOLOGIA},
	pages = {525-530},
	keywords = {dung beetles forest function},
	url = {<Go to ISI>://A1988Q070500007},
	author = {Schupp, E. W.}
}
