@article {1420,
	title = {Body-Size, Abundance, and Geographical-Distribution of Afrotropical Dung Beetles (Coleoptera, Scarabaeidae)},
	journal = {Acta Oecologica},
	volume = {15},
	number = {2},
	year = {1994},
	note = {Times Cited: 11Cited Reference Count: 25Cited References:      BLACKBURN TM, 1993, J ANIM ECOL, V62, P519     BLACKBURN TM, 1993, J ANIM ECOL, V62, P694     BLACKBURN TM, 1992, OIKOS, V65, P107     BROWN JH, 1989, SCIENCE, V243, P1145     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P36     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P51     CAMBEFORT Y, 1991, DUNG BEETLE ECOLOGY, P156     COTGREAVE P, 1993, TRENDS ECOL EVOL, V8, P244     CURRIE DJ, 1993, OIKOS, V67, P56     CURRIE DJ, 1993, OIKOS, V66, P353     DAMUTH J, 1987, BIOL J LINN SOC, V31, P193     DAMUTH J, 1993, NATURE, V365, P748     DAMUTH J, 1991, NATURE, V351, P268     GASTON KJ, 1988, AM NAT, V132, P662     GRIFFITHS D, 1992, J ANIM ECOL, V61, P307     GRIFFITHS D, 1987, NATURE, V328, P117     HANSKI I, 1991, DUNG BEETLE ECOLOGY, P283     HEINRICH B, 1979, PHYSIOL ZOOL, V52, P484     LAWTON JH, 1989, OIKOS, V55, P429     LAWTON JH, 1991, PHILOS T ROY SOC B, V330, P2833     LUMARET JP, 1992, J APPL ECOL, V29, P349     NEE S, 1991, NATURE, V351, P312     PAGEL MD, 1991, AM NAT, V138, P836     STORK NE, 1993, OIKOS, V67, P483     WHITE F, 1986, VEGETATION AFRICAEnglishArticlePJ666ACTA OECOL},
	pages = {165-179},
	abstract = {Local and regional abundances of Afrotropical dung beetle species, as well as their regional and continental distributions, have been found to depend on their average individual fresh weight. At the local and regional scales, small-bodied species are numerically more abundant than their larger relatives, but large-bodied species have a larger total biomass and control a larger proportion of available resources. At the regional scale, large dung beetle species occur in fewer localities than small ones, but, at the continental scale, geographical distribution is wider.},
	keywords = {abundance, afrotropical region, beetles, biomass, communities, Dung, dynamics, energy use, energy-use, geographical distribution, natural animal assemblages, patterns, population-density, size},
	url = {<Go to ISI>://A1994PJ66600005},
	author = {Cambefort, Y.}
}
@article {1548,
	title = {The role of the subelytral cavity in water loss in the flightless dung beetle, Circellium bacchus (Coleoptera : Scarabaeinae)},
	journal = {European Journal Of Entomology},
	volume = {99},
	number = {2},
	year = {2002},
	note = {digital copy},
	pages = {253-258},
	abstract = {Circellium bacchus is a flightless telecoprid (ball-rolling) dung beetle, endemic to the afrotropical region, where it is found in a few restricted populations in the eastern Cape of South Africa. Its apterous condition and large size (mass ranges from 6 to 12 g) are considered to be adaptations to a semi-arid habitat. This beetle is active in the sun for long periods, walking between widely scattered dung pats, thus is under selection pressure to reduce water loss. C bacchus has eight spiracles on each side of the body. The metathoracic spiracle and six abdominal spiracles open into the sub-elytral cavity, which is closed. The mesothoracic spiracle is the largest and most exposed, occurring ventrally in the membrane connecting the prothorax and mesothorax. When at rest a cyclic form of respiration, known as discontinuous gas exchange cycle, is used by C. bacchus, releasing a burst of carbon dioxide approximately once an hour when the spiracles open for about 33 minutes. Flow-through respirometry was used to measure water loss from the thorax (being the head, prothorax and mesothorax) and elytral case (containing the metathorax and abdomen) separately. The total water loss of C. bacchus could be divided up as 65\% cuticular water loss from the thorax, 35\% cuticular water loss from the elytral case, 4\% respiratory water loss from the thorax and no measurable respiratory water loss from the elytral case. 1.51 mug of water is lost for every mul of CO2 emitted during respiration in the thorax. Thus, the main avenue for both respiration and respiratory water loss is via the mesothoracic spiracles, suggesting that the primary function of the subelytral cavity is not to reduce respiratory water loss.},
	keywords = {Circellium bacchus, desert tenebrionid beetles, discontinuous gas exchange cycle, Discontinuous gas-exchange, dung beetle, insects, patterns, physiology, respiration, Scarabaeidae, subelytral cavity, terrestrial, trait information, ventilation, water loss},
	url = {<Go to ISI>://000177174200016 },
	author = {Duncan, F. D.}
}
@article {1574,
	title = {Effects of the attractiveness for dung beetles of dung pat origin and size along a climatic gradient},
	journal = {Environmental Entomology},
	volume = {33},
	number = {1},
	year = {2004},
	note = {digital copy},
	month = {Feb},
	pages = {45-53},
	abstract = {Dung beetle (Coleoptera:Geotrupidae, Scarabaeidae) assemblages were monitored by dung-baited pitfall trapping at three sites distributed along a bioclimatic gradient from semiarid to mesic temperate. For each type of dung, both small and large sized baits were used. Under semiarid conditions{\textquoteright}(Morocco), three dung beetle assemblages were distinguished: small bait assemblages in any dung; large cattle bait assemblages; large sheep bait assemblages. Under more temperate conditions (southern France and the Alps), only large and small bait assemblages were observed, whatever the origin of the dung. Large baits attracted significantly more species and more beetles than did small baits, and very few species were attracted significantly more by either sheep or goat baits than by cattle baits. A significant, positive correlation between dung beetle size and dung pat size was observed in Morocco where the large species are predominant, whereas a negative relationship was observed in southern France where the small species are predominant. Cattle pats were more attractive for beetles under xeric and Mediterranean conditions (Morocco and southern France) that under cold temperate conditions (Alps).},
	keywords = {aphodius, assemblage composition, ba, baited pitfall traps, cattle, COLEOPTERA, colonization, dung beetle, GUILD, IVERMECTIN, mammal, patterns, Scarabaeidae, Scarabaeoidea, scarabaeoidea col communities, spatial, trophic resource, variability},
	url = {<Go to ISI>://000189311200006 },
	author = {Errouissi, F. and Haloti, S. and Jay-Robert, P. and Janati-Idrissi, A. and Lumaret, J. P.}
}
@article {1934,
	title = {Modelling the species richness distribution of French dung beetles (Coleoptera, Scarabaeidae) and delimiting the predictive capacity of different groups of explanatory variables},
	journal = {Global Ecology and Biogeography},
	volume = {11},
	number = {4},
	year = {2002},
	month = {Jul},
	pages = {265-277},
	abstract = {Aim To predict French Scarabaeidae dung beetle species richness distribution, and to determine the possible underlying causal factors. Location The entire French territory has been studied by dividing it into 301 grid cells of 0.72 x 0.36 degrees. Method Species richness distribution was predicted using generalized linear models to relate the number of species with spatial, topographic and climate variables in grid squares previously identified as well sampled (n = 66). The predictive function includes the curvilinear relationship between variables, interaction terms and the significant third-degree polynomial terms of latitude and longitude. The final model was validated by a jack-knife procedure. The underlying causal factors were investigated by partial regression analysis, decomposing the variation in species richness among spatial, topographic and climate type variables. Results The final model accounts for 86.2\% of total deviance, with a mean jack-knife predictive error of 17.7\%. The species richness map obtained highlights the Mediterranean as the region richest in species, and the less well-explored south-western region as also being species-rich. The largest fraction of variability (38\%) in the number of species is accounted for by the combined effect of the three groups of explanatory variables. The spatially structured climate component explains 21\% of variation, while the pure climate and pure spatial components explain 14\% and 11\%, respectively. The effect of topography was negligible. Conclusions Delimiting the adequately inventoried areas and elaborating forecasting models using simple environmental variables can rapidly produce an estimate of the species richness distribution. Scarabaeidae species richness distribution seems to be mainly influenced by temperature. Minimum mean temperature is the most influential variable on a local scale, while maximum and mean temperature are the most important spatially structured variables. We suggest that species richness variation is mainly conditioned by the failure of many species to go beyond determined temperature range limits.},
	keywords = {auto, biodiversity, conservation biology, determinants, diversity, Dung beetles, environmental components, France, modelling distributions, northern finland, patterns, scale, species richness, species richness distribution, variance partitioning, wildlife},
	url = {<Go to ISI>://000176648100001},
	author = {Lobo, J. M. and Lumaret, J. P. and Jay-Robert, P.}
}
@article {1936,
	title = {Searching for a predictive model for species richness of Iberian dung beetle based on spatial and environmental variables},
	journal = {Conservation Biology},
	volume = {16},
	number = {1},
	year = {2002},
	note = {digital copy},
	month = {Feb},
	pages = {158-173},
	abstract = {In Mediterranean countries, inventories of many animal groups particularly insects, are incomplete or nonexistent. Hence, a feasible spatial picture of unequally surveyed areas is required to ascertain which faunistic surveys are good enough to produce reliable estimates of species richness. We used generalized linear models to build a multiple-regression function through which we predicted the distribution of Iberian dung beetle species richness. Given the scarcity and unevenness of the species-richness spatial distribution, the number of records of a dung beetle database (BANDASCA), falling within each of the 50 x 50 km grid squares, was chosen as a measure of the sampling effort for that square. Examining the asymptotic relationship between the number of dung-beetle species and database records for each physioclimatic Iberian subregion, we found that 82 grid squares (32\% of the total) were adequately sampled. Dung-beetle species richness was related in each of these 82 cells to 24 explanatory variables. Curvilinear functions, interaction terms, and the significant third-degree polynomial terms of latitude and longitude were included to model species-richness distribution. The final model accounted for 62.4\% of the total deviance after we eliminated seven outlier squares, with maximum elevation, grassland area, land-use diversity, forest area, geological diversity, interaction of terrestrial area and maximum elevation, and interaction between calcareous rock, and geological diversity and latitude being the most significant independent variables. The residuals of the function were not spatially autocorrelated, and we validated the final model by a jackknife procedure. Large and environmentally complex hotspots in the Iberian Central, Baetic, and Subbaetic mountain ranges stand out from the emerging map of species richness. Further detailed research is required to determine the complementarity of the faunas of these two main hotspots, the key question in conservation planning for a dung-feeding beetle.},
	keywords = {Africa, atlas, autocorrelation, biodiversity, butterflies, communities, conservation, insects, patterns, plants},
	url = {<Go to ISI>://000173726400016},
	author = {Lobo, J. M. and Martin-Piera, F.}
}
@article {2085,
	title = {Log-normal distribution of species abundances is not a universal indicator of rain forest disturbance},
	journal = {Journal of Applied Ecology},
	volume = {35},
	number = {3},
	year = {1998},
	note = {Times Cited: 8Cited Reference Count: 27Cited References:      BAZZAZ FA, 1975, ECOLOGY, V56, P485     BEALL G, 1935, ECOLOGY, V16, P216     DELONG DM, 1932, ANN ENTOMOL SOC AM, V25, P13     GRAY JS, 1979, MAR POLLUT B, V10, P142     GRAY JS, 1987, ORG COMMUNITIES PAST, P53     HILL JK, 1998, IN PRESS J APPL ECOL, V35     HILL JK, 1995, J APPL ECOL, V32, P754     JANZEN DH, 1973, ECOLOGY, V54, P661     KREBS CJ, 1989, ECOLOGICAL METHODOLO     LANGDALEBROWN I, 1964, VEGETATION UGANDA     LINDHOLM T, 1983, SILVA FENNICA, V17, P289     MAY RM, 1975, ECOLOGY EVOLUTION CO, P81     NUMMELIN M, 1992, AFR J ECOL, V30, P213     NUMMELIN M, 1991, AFRICAN J ECOLOGY, V30, P10     NUMMELIN M, 1989, FAUNA NORVEGICA B, V36, P17     NUMMELIN M, 1989, J TROP ECOL, V5, P349     NUMMELIN M, 1992, TROP ZOOL, V5, P155     NUMMELIN M, 1996, TROPICAL ECOLOGY, V37, P201     PATRICK R, 1973, ASTM STP, V528, P76     RITCHIE M, 1986, INT S TROP ENT NAIR     SKORUPA JP, 1984, ORYX, V18, P96     STRUHSAKER TT, 1997, ECOLOGY AFRICAN RAIN     SUGIHARA G, 1980, AM NAT, V116, P770     TOKESHI M, 1993, ADV ECOL RES, V24, P111     VANDERMAAREL E, 1971, SCI MANAGEMENT ANIMA, P45     WHITTAKER RH, 1975, COMMUNITIES ECOSYSTE     WHITTAKER RH, 1965, SCIENCE, V147, P250EnglishArticle122YZJ APPL ECOL},
	month = {Jun},
	pages = {454-457},
	abstract = {1. The fit to log-normal distribution of species abundances of grasshoppers, ladybird beetles, tortoise beetles and dung beetles and forest floor vegetation in unlogged and selectively felled sites in Kibale Forest, western Uganda was analysed. It was shown that the fit to log-normal distribution cannot be used as a straightforward universal indicator of rainforest disturbance.},
	keywords = {bioindicator, community structure, diversity, kibale forest, logging, patterns, tropical forest management, Uganda, virgin},
	url = {<Go to ISI>://000076100200009},
	author = {Nummelin, M.}
}
@article {2112,
	title = {Primary dispersal of seeds by primates and secondary dispersal by dung beetles in Tikal, Guatemala},
	journal = {Biotropica},
	volume = {38},
	number = {3},
	year = {2006},
	month = {May},
	pages = {390-397},
	abstract = {We linked primary dispersal by spider monkeys (Ateles geoffroyi) and howler monkeys (Alouatta pigra) to post-dispersal seed fate by studying the effects of dung type and defecation pattern on secondary seed dispersal by dung beetles. First, we described the defecation patterns for both primate species. Howler monkeys generally defecated in groups (88\% of observed defecations), with each individual producing on average 31 g of dung, resulting in a large area of the forest floor (31 m(2)) covered by large amounts of dung (clumped spatial pattern). Spider monkeys generally (96\% of observed defecations) defecated individually, each individual producing an average of 11 g of dung, resulting in a small area of the forest floor (2 m(2)) covered by small amounts of dung (scattered spatial pattern). Secondly, we captured dung beetles using as bait the dung of both primate species, to detect differences in the assemblages of these secondary seed dispersers attracted to the dung of both primates. More individual dung beetles, but not more species, were attracted to howler monkey dung than to spider monkey dung. Finally, we assessed experimentally (using plastic beads as seed mimics) how dung type (Ateles vs. Alouatta) and defecation pattern (scattered vs. clumped) affect secondary seed dispersal by dung beetles. We found that post-dispersal seed fate was affected by dung type, with more seeds being buried when present in howler monkey dung, than in spider monkey dung, but was not affected by defecation pattern. It is important to consider post-dispersal processes, such as secondary seed dispersal by dung beetles, when comparing species of primary dispersers.},
	keywords = {alouatta-palliata, Ateles, CEBUS-CAPUCINUS, DEFECATION, GERMINATION literature review function service seed dispersal mammal value, howler monkeys, los-tuxtlas, Mexico, patterns, Scarabaeidae, tropical rain-forest},
	url = {<Go to ISI>://000236766500014 },
	author = {Ponce-Santizo, G. and Andresen, E. and Cano, E. and Cuaron, A. D.}
}
@article {2190,
	title = {Changes in mammalian body length over 175 years - Adaptations to a fragmented landscape?},
	journal = {Conservation Ecology},
	volume = {7},
	number = {2},
	year = {2003},
	note = {digital copy},
	month = {Dec},
	abstract = {The potential consequences of anthropogenic habitat fragmentation on species diversity and extinction have drawn considerable attention in recent decades. In many cases, traditional island biogeography theory has been applied to explain the observed patterns. Here, we propose that habitat fragmentation as a selective force can be traced in mammalian body length changes. By exploring historical sources, we are able to show that the body length of Danish mammals has altered over a period of 175 years, possibly in response to increasing habitat fragmentation. The rate of body length change was generally lowest in medium-sized mammals, and increased with both smaller and larger body mass. Small mammals have generally increased, whereas large mammals have decreased in length. In addition to habitat fragmentation, some species may experience other selective forces, such as traffic, and may be trapped in an evolutionary tug-of-war, where the selective forces pull in opposite directions.},
	keywords = {AREA mammals, DENMARK, GERMANY, ISLAND, OTTERS LUTRA-LUTRA, patterns, population-density, ROAD-KILLS, RULE, size, TERRESTRIAL MAMMALS},
	url = {<Go to ISI>://000189307800009 },
	author = {Schmidt, N. M. and Jensen, P. M.}
}
@article {2218,
	title = {Biogeographic crossroads as priority areas for biodiversity conservation},
	journal = {Conservation Biology},
	volume = {16},
	number = {6},
	year = {2002},
	note = {Times Cited: 0Cited Reference Count: 61Cited References:      BALMFORD A, 1995, CONSERV BIOL, V9, P1539     BATES JM, 1998, BIOL ASSESSMENT PARQ, P112     BROOKS DR, 1992, TRENDS ECOL EVOL, V7, P55     BROOKS T, 2000, NATURE, V403, P26     BROWN JH, 1984, AM NAT, V124, P255     BROWN JH, 1995, MACROECOLOGY     CHANNELL R, 2000, NATURE, V403, P84     DALLMEIER F, 1996, MANU DIVERSITY SE PE, P61     DAVIS FW, 1996, BIOSCIENCE, V46, P74     DINERSTEIN E, 1995, CONSERVATION ASSESSM     EDMONDS WD, 1994, REVISION PHANAEUS MA     EDMONDS WD, 1972, U KANSAS SCI B, V49, P731     EMMONS LH, 1998, BIOL ASSESSMENT PARQ, P129     ENSERINK M, 1997, SCIENCE, V276, P1791     ERWIN TL, 1996, MANU BIODIVERSITY SE, P359     ERWIN TL, 1991, SCIENCE, V253, P750     FELGER RS, 1994, BIODIVERSITY MANAGEM, P36     FJELDSA J, 1997, TROPICAL FOREST REMN, P466     FOREMAN D, 2000, WILD EARTH SPR, P11     FORSYTH AB, 1998, BIOL ASSESSMENT PARQ, P181     FREITAG S, 1997, BIOL CONSERV, V82, P263     HALFFTER G, 1993, BIOL INT, V27, P15     HANSKI I, 1991, DUNG BEETLE ECOLOGY     HARVEY MB, 1998, BIOL ASSESSMENT PARQ, P144     HOLDRIDGE LR, 1967, LIFE ZONE ECOLOGY     JOHNSON N, 1995, BIODIVERSITY BALANCE     KERR JT, 1997, CONSERV BIOL, V11, P1094     KILLEEN TJ, 1998, BIOL ASSESSMENT PARQ, P61     KITCHING IJ, 1996, BIODIVERS CONSERV, V5, P841     KREMEN C, 1993, CONSERV BIOL, V7, P796     LOMOLINO MV, 1998, CONSERV BIOL, V12, P481     LOMOLINO MV, 1995, J MAMMAL, V76, P335     MARGULES CR, 2000, NATURE, V405, P243     MAYR E, 1963, ANIMAL SPECIES EVOLU     MCKENZIE NL, 1989, BIOL CONSERV, V50, P231     MITTERMEIER RA, 1998, CONSERV BIOL, V12, P516     MYERS N, 2000, NATURE, V403, P853     OLIVER I, 1998, CONSERV BIOL, V12, P822     OLSON DM, 1998, CONSERV BIOL, V12, P502     PEARSON DL, 1992, CONSERV BIOL, V6, P376     PEARSON DL, 1999, J BIOGEOGR, V26, P1079     POGUE MG, 1996, MANU BIODIVERSITY SE, P313     PRENDERGAST JR, 1999, CONSERV BIOL, V13, P484     PRENDERGAST JR, 1997, ECOGRAPHY, V20, P210     PRENDERGAST JR, 1993, NATURE, V365, P335     PRESSEY RL, 1993, TRENDS ECOL EVOL, V8, P124     REID WV, 1998, TRENDS ECOL EVOL, V13, P275     REMSEN V, 1995, BIRD CONSERV INT, V5, P181     RICKETTS TH, 1999, BIOSCIENCE, V49, P369     RODRIGUES ASL, 1999, P ROY SOC LOND B BIO, V266, P1453     ROTHLEY KD, 1999, ECOL APPL, V9, P741     SARMIENTO J, 1998, BIOL ASSESSMENT PARQ, P167     SCHNEIDER CJ, 1999, P NATL ACAD SCI USA, V96, P13869     SMITH TB, 1997, SCIENCE, V276, P1855     SPECTOR S, 1998, CONSERVATION CHANGIN, P181     VANEWRIGHT RI, 1991, BIOL CONSERV, V55, P235     WARSHALL P, 1994, BIODIVERSITY MANAGEM, P408     WHITTAKER RH, 1972, TAXON, V21, P213     WIKRAMANAYAKE E, 1998, BIODIVERSITY ASSESSM     WILLIAMS P, 1996, CONSERV BIOL, V10, P155     WILLIAMS PH, 1996, BIOL J LINN SOC, V58, P125EnglishArticle618LTCONSERV BIOL},
	month = {Dec},
	pages = {1480-1487},
	abstract = {Threats to biodiversity outpace the resources of the conservation community and necessitate careful prioritization of conservation actions. I suggest that targeting the regions where biogeographic assemblages intersect - " biogeographic crossroads" - is a strategy that may achieve significant conservation economy by focusing on areas that satisfy many conservation criteria. I used a combination of data on Scarabaeine beetles in Bolivia and on other taxa and locations from the literature to consider the short- and long-term benefits of conserving these biogeographic crossroads. Biogeographic crossroads are areas of high species richness and beta diversity, often across many taxonomic groups. They are also regions where representativeness can be achieved with relative efficiency. Recent evidence that ecotones may be loci of evolution suggests that evolutionary processes such as speciation and coevolution may be conserved at biogeographic crossroads. Biogeographic crossroads appear to be areas of high conservation priority and opportunity in both the short and long term and require increased attention in the process of setting conservation priorities.},
	keywords = {assemblages, complementary areas, congruence, diversity, forest, hotspots, patterns, species richness, strategies, tiger beetles},
	url = {<Go to ISI>://000179420100009},
	author = {Spector, S.}
}
@article {2220,
	title = {Rapid turnover and edge effects in dung beetle assemblages (Scarabaeidae) at a Bolivian Neotropical forest-savanna ecotone},
	journal = {Biotropica},
	volume = {35},
	number = {3},
	year = {2003},
	note = {744QYBIOTROPICA},
	month = {Sep},
	pages = {394-404},
	abstract = {Habitat fragmentation and the widespread creation of habitat edges have recently stimulated interest in assessing the effects of ecotones on biodiversity. Ecotones, natural or anthropogenic, can greatly affect faunal movement, population dynamics, species interactions, and community structure. Few data exist, however, on insect community response to forest- savanna ecotones, a natural analog to anthropogenically cleared areas adjacent to forest. In this study, the abundance, total biomass, average individual biomass, and distribution of scarabaeine dung beetles were examined at a sharp tropical evergreen forest-savanna ecotone in Santa Cruz, Bolivia. The abundance, total biomass, and average individual biomass of dung beetles varied significantly across the forest, edge, and savanna habitats. Species richness (S-obs) also varied significantly across the three habitats, but statistical estimations of true species richness (S-est) did not. Habitat specificity of the dung beetles in this study was extremely high. Of the 50 most common species collected during the study, only 2 species were collected in both the forest and savanna habitats, signaling nearly complete community turnover in just a few meters. Strong edge effects were evidenced by the decline in abundance, total biomass, and species richness at the forest-savanna boundary.},
	keywords = {beta diversity, Bolivia, boundaries, Central Amazonia, COLEOPTERA, communities, conservation, Dung beetles, dynamics, ecotone, edge, fragmented forests, gradients, patterns, responses, savanna, tropical forest},
	url = {<Go to ISI>://000186644700009},
	author = {Spector, S. and Ayzama, S.}
}
@article {2272,
	title = {Climatic stress, food availability and human activity as determinants of endemism pattersn in the Mediterranean region: the case of dung beetles (Coleoptera, Scarabaeoidea) in the Iberian Peninsula},
	journal = {Diversity and Distributions},
	volume = {8},
	year = {2002},
	note = {have copy and digital copy},
	pages = {259-274},
	keywords = {bioclimatic indices, climate, community assemblages mammals, Distribution, dung beetle, ecosystem, endemicity, food availability, human activity, Iberian Peninsula, patterns, Scarabaeoidae, stress},
	author = {Verdu, Jose and Galante, E.}
}
