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PREDICTS.json
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Thoisy","Ofori-Boateng","Oke","Oliveira","Rodrigues","Barlow","Bernard","Kutt","Shannon","Devineau","Vasconcelos","Scott","Andersen","Freire","Schumann","Strauch","Breedt","Vasconcelos","Vasconcelos","Aumann","Woinarski","Sakchoowong","Sedlock","Nyeko","Parry","Vu","Felton","Krauss","Ancrenaz","Cleary","Krauss","Pineda","Clarke","Hietz","Kessler","Kumar","Cleary","Lachat","Wunderle","Barlow","Borges","Bos","Bragagnolo","Barlow","Fredriksson","MacSwiney","Ranganathan","Shahabuddin","Uehara-Prado","Wells","Willig","Bihn","Farwig","Gardner","Gomes","Grogan","Hanson","Kapoor","Presley","Ranganathan","Hawes","Horgan","Hylander","Kessler","Matsumoto","Bicknell","Krauss","Peters","Mico","Gray","Maeto","Bldi","Summerville","Chapman","Cagle","Lantschner","Pillsbury","Berg","Brunet","Cerezo","Savage","Summerville","Yoshikura","Fensham","Jonsell","Krsi","Lantschner","Naoe","Pelegrin","Threlfall","Peres","McShea","Kittle","Kutt","Garmendia","Ramos-Robles","Cassano","Alcala","Struebig","Watling","Cceres","Sodhi","Wang","Vallan","Pons","Schilthuizen","Borges","zden","Gutierrez","Suarez-Rubio","Gunawardene","Azman","Alguacil","Pethiyagoda","Gould","Hoffmann","Uehara-Prado","Littlewood","Shafie","Henschel","Hayward","Endo","Wiafe","Koivula","Arroyo","Vanbergen","Baur","Zaitsev","Chauvat","Woodcock","Boutin","Buscardo","Paritsis","Dumont","Schon","Vassilev","Littlewood","Schmidt","Turner","Centro Agronmico Tropical de Investigacin y Enseanza (CATIE)","Hashim","Sheldon","Phalan","Munyekenye","O'Farrell","Joubert","Lehouck","Haarmeyer","Granjon","Virgilio","Malonza","Adum","Nakashima","Ndang'ang'a","Reynolds","Summerville","Hylander","Kolb","Marsh","Richardson","Benedick","Mayfield","Urbina-Cardona","Garca-R","Eigenbrod","Gaublomme","Urbina-Cardona","Baral","Christensen","Meyer","Williams","Baeten","Giordani","Marsh","Rey-Benayas","Brearley","D'Cruze","Meijer","Rubio","Stouffer","Vu","Barrico","Danquah","Gendreau-Berthiaume","Power","Schepp","Alignier","Fernandez","Jalilova","Kazerani","Poggio","Fowler","Kurz","Raub","Sam","Louhaichi","D'Aniello","Lucas-Borja","Brito","Giordani","Kati","Numa","Santana","Verdasca","Gutierrez-Lamus","Armbrecht","Noriega","Parra-H","Smith-Pardo","Dominguez-Haydar","Higuera","Arbelez-Corts","Isaacs-Cubides","Navarro","Rosselli","Cabra-Garca","Lpez-Quintero","Noriega","Poveda","Rey-Velasco","Otavo","Moir","Dolia","Craig","Gaigher","McCarthy","Craig","Brandt","Frizzo","Garcia","Hassan","Craig","Craig","Bsing","Wronski","Floren","Bonham","Sheil","Shochat","O'Connor","Vu","Nicolas","Ims","Norfolk","CIFOR","CIFOR","Norfolk","Peri","Walker","Roth","Owiunji","Fermon","Nakagawa","Soh","Bouyer","Castro-Luna","Gardner","O'Dea","Luja","Ngai","Fukuda","Furlani","Peters","Boutin","Lo-Man-Hung","Carpenter","Walker","St-Laurent","Buddle","Noreika","Strm","Edenius","Jung","Lgar","Paradis","Zimmerman","Hylander","Noreika","Otto","Bayne","Gu","Hu","Zhang","Wang","Liu","Sung"],"First_author_initials":["L.H.","A.","D.P.","B.","M.","R.","M.E.","S.","R.E.","K.R.","T.","E.J.P.","Q.S.","R.G.","F.","B.","E.","R.","R","M","D.","F.","K.S.","N.","H.E.","M.E.","C.H.","M.","E.S.","D.","L.","C.","N.","A.J.","M.E.","R.J.","S.A.","S.","M.E.","A.","A.","E.F.","M.H.","U.","C.","R.","C","M.M.","P.E.","S","L.M.","H.A.F.","Yuichi","H.J.","S.A.","Ingo","A.L.V","M.S","Y","M.F","D","M.","B.K.C","E.M","H. K.","N. V.","V.","I.","A.","I.","R.J.","B.","D.","R.","N.","N.","B.","C.","E.","R.","S","E.","J.","R","A.","E.","L. P.","N.","S.","J.","L.","N.","S.","B.","E.","S.","M","S.","A.","B.","Z.","E.","C.","G.","S.","J.","T.","C.","Z.","G.","H.","X","Xiaoli","Yi","Baoming","Xiaoli","Shining","A.","E.","R.","A.","J.","D.","J.","N.","H.","T.","J.","R.","J.","E.","C.","P","M.","L.","B.","A.","L.","P.","K.L.","C.","Y.","J.R.","J.","V.","R.","A.B.","V.","T.F.","J.H.C.","O. C.","S.","J. C. Z.","R.","A.","H.","David","C.","C.T.","M.S.","M.","V.M.","F.","R. A.","P.G.","S.","N.A.D","D.","M.","E.","L.","J.","N.","D. B.","S.J.","O.","P.","B.","C.","O. C.","D.E.","M.","J","H","A S","Dr.","JL","H.","Ken","Alan","G","K.","Ayron","J","H.L","H.L","T.","J.C.Z","W","J.L","P","L","L.V","Annika M.","J.","M","D.F.R.","J.","E.","F.M.","P.","M.","R","D.F.R.","T.","J.M.","J.","S.","Merijn","C.","J","G. M.","M.C.","J.","G.","M.","K.","M.R.","J.H.","N.","T.A.","Laurens","J.","T.","V.","S.J.","J.","J.","F.G.","K.","M.","T.","Jake","J.","Marcell","E","C.","K","A.","K","K","N","M","F.","A","J.","A","J","K","S","R.","M","A","M","S","N","C.","Carlos","William","Andrew","Alex","Adriana","Michelle","Camila","E. L","M. J","J. I","N. C","N. S","Y","D.","P.","M.","P. A. V.","O.","A. G.","M.","N. R.","N. M.","M. del M.","R. S.","R. K.","Anke","M","N","N.J.","P","Matt","Whaldener","E","Matti","Julio","Adam","Bruno","Andrey","Matthieu","Ben","Cline","Erika","Juan","Bertrand","Nicole","Kiril","Nick","Amanda","E","","","F","","FB.","Patrick","L.","V.","D. H.","L.","M.","P.K.","G.B.","Y.","Paul Kariuki","C.","K.","K.","A.","C.","B.A.","S.","M.M.","J.N.","J.C.","F.","E.","J.N.","S.K.","M.","B.","C.D.","L.","P","C.","J.M.","F.Q.","N","S.","A.","P.C.","L.V.","L.","E.","B.","E.F.","C.","A.","I.C.","G.","F.","S.","R.E.","D.J.","F.","K.","M.","B.","M. E.","I.","P.","V.","C.","J.","M. J.","D.L.","I.","J.A","A.","A.","Y.","D.","E.","P.J.","L.","L.","J.","C.A","J.A.","K.","J.C.","S.E.","M.","J.","M.","R.","J.","M.","J.","T.","K.","S.","M.","M.","B.","T.","A.","K.J.","D.","E.","Tim","L.","V","Rolf","O.","","","O.","P.L.","S.","D.S.","I.","H","M","M.C.K","J","A.A","T.A.","N","V.H","J.T.","D","D","M.K.","C","N.F.","D","T.","M-H","M","N.","L","L","T","J-P","S.","G","K","N","C","E.","Wei Bin","Cheng","Jingnan","Hua Feng","Yunhui","Yik Hei"],"Year_of_publication":["2001","2002","2002","2004","2004","2005","2005","2005","2005","2006","2006","2006","2006","2007","2007","2007","2007","2007","2008","2008","2008","2008","2008","2009","2009","2009","2009","2010","2010","2010","2010","2010","2010","2011","2011","2011","2011","2011","2011","2011","2011","2011","2011","2011","2011","2011","2011","2012","2012","2012","2012","2012","2012","2012","2013","2013","2005","2007","2008","2008","2008","2010","2011","2011","2009","2010","2011","2011","2012","2014","2004","2005","2006","2007","2008","2010","2012","2012","2012","2013","2013","2013","2014","2014","2002","2007","2007","2008","2009","2009","2010","2010","2011","2012","2012","2012","2003","2004","2004","2004","2007","2007","2008","2010","2010","2010","2010","2011","2011","2012","2012","2008","2008","2012","2012","2013","2013","2003","2004","2004","2005","2005","2006","2007","2008","2008","2010","2010","2010","2011","2011","2012","2012","2012","2012","2013","2013","2013","2004","2005","2005","2007","2007","2008","2008","2008","2009","2009","2009","2009","2009","2009","2009","2010","2010","2010","2010","2010","2010","2010","2010","2010","2010","2010","2011","2011","2011","2011","2012","2012","2012","2012","2012","2012","2012","2013","2013","2013","2013","2013","2013","2013","2007","2009","2007","2008","2009","2009","2010","2011","2011","2011","2012","2013","1999","2000","2001","2002","2008","2008","2009","2009","2009","2003","2003","2004","2004","2004","2004","2005","2005","2005","2005","2006","2006","2006","2007","2007","2007","2007","2007","2007","2007","2007","2007","2007","2007","2007","2008","2008","2008","2008","2008","2008","2008","2008","2008","2009","2009","2009","2009","2009","2010","2010","2011","2013","2014","2004","2005","2006","2007","2008","2008","2008","2011","2011","2011","2011","2011","2011","2012","2012","2012","2012","2012","2012","2012","2006","2009","2012","2012","2013","2013","2014","2004","2008","2009","2010","2010","2010","2002","2005","2005","2006","2008","2009","2009","2010","2011","2012","2012","2013","2005","2005","2008","2011","2008","2009","2010","2012","2004","2005","2005","2006","2006","2007","2007","2008","2008","2008","2009","2011","2011","2012","2012","2009","2010","2010","2010","2011","2008","2008","2009","2009","2010","2011","2011","2012","2013","2013","2013","2013","2002","2004","2004","2005","2005","2006","2006","2006","2007","2008","2008","2008","2009","2009","2009","2009","2010","2010","2010","2010","2011","2011","2011","2011","2011","2011","2012","2012","2012","2012","2012","2013","2013","2013","2013","2013","2014","2014","2014","2014","2009","2011","2011","2012","2012","2012","2012","2012","2012","2004","2006","2007","2007","2007","2010","2010","2011","2011","2011","2011","2012","2012","2012","2012","2012","2013","2005","2008","2009","2010","2010","2012","2013","2013","2013","2013","2014","2014","2014","2014","2001","2002","2002","2004","2005","2005","2009","2012","2012","2013","2013","2013","2013","2014","1994","1998","2005","2006","2006","2007","2007","2007","2007","2008","2008","2009","2009","2009","2009","2011","2012","2006","2007","2008","2009","2009","2011","2011","2011","2011","2011","2012","2012","2012","2013","2004","2008","2010","2011","2012","2012"],"Source_title":["Bee diversity along a disturbance gradient in tropical lowland forests of south-east Asia","Grazing intensity and the diversity of grasshoppers, butterflies, and trap-nesting bees and wasps","Ecological specialization and susceptibility to disturbance: Conjectures and Refutations","Use of genetic markers to quantify bumblebee foraging range and nest density","Wild bees in agroecosystems and semi-natural landscapes. 1997-2000 collection period in Italy","Rain forest provides pollinating beetles for Atemoya crops","Unpublished data of bee diversity in UK croplands","Ecological and seasonal patterns in the diversity of a species-rich bee assemblage (Hymenoptera: Apoidea: Apiformes)","Farming practices influence wild pollinator populations on squash and pumpkin","Proximity to rainforest enhances pollination and fruit set in orchards","Effects of landscape elements on the distribution of the rare bumblebee species Bombus muscorum in an agricultural landscape","Impacts of an agri-environment field margin prescription on the flora and fauna of arable farmland in different landscapes","Are urban parks refuges for bumble bees Bombus spp. (Hymenoptera: Apidae)?","Patch and landscape factors shape community assemblage of bumble bees, Bombus spp. (Hymenoptera: Apidae), in montane meadows","Genetic diversity and mass resources promote colony size and forager densities of a social bee (Bombus pascuorum) in agricultural landscapes","Patch size and landscape effects on pollinators and seed set of the Horseshoe Vetch, Hippocrepis comosa, in an agricultural landscape of Central Europe","Semi-natural grasslands as population sources for pollinating insects in agricultural landscapes","Effect of human disturbance on bee communities in a forested ecosystem","Indicators for biodiversity in agricultural landscapes: a pan-European study","How can we preserve and restore species richness of pollinating insects on agricultural land?","Diet breadth, coexistence and rarity in bumblebees","At what spatial scale do high-quality habitats enhance the diversity of forbs and pollinators in intensively farmed landscapes?","Diversity and abundance of bees (Hymenoptera : Apiformes) in native and ruderal grasslands of agriculturally dominated landscapes","Isolation from forest reduces pollination, seed predation and insect scavenging in Swiss farmland","Wild bee abundance and pollination service in cultivated pumpkins: Farm management, nesting behavior and landscape effects","Bumblebee nest density and the scale of available forage in arable landscapes","Pollinator diversity increases fruit production in Mexican coffee plantations: The importance of rustic management systems","Effects of ecological compensation meadows on arthropod diversity in adjacent intensively managed grassland","Landscape effects on extremely fragmented populations of a rare solitary bee, Colletes floralis","Effects of land use at a landscape scale on bumblebee nest density and survival","Observations on bee species visiting white clover in New Zealand pastures","Effects of anthropogenic habitat disturbance on local pollinator diversity and species turnover across a precipitation gradient","Crofting and bumblebee conservation: The impact of land management practices on bumblebee populations in northwest Scotland","Changing bee and hoverfly pollinator assemblages along an urban-rural gradient","Unpublished data of bee diversity in UK croplands and urban habitats","Enhancing habitat to help the plight of the bumblebee","Patterns of widespread decline in North American bumble bees","Microsatellite analysis reveals the spatial dynamics of Bombus humilis and Bombus sylvarum","Increased bumblebee abundance along the margins of a mass flowering crop: evidence for pollinator spill-over","Expansion of mass-flowering crops leads to transient pollinator dilution and reduced wild plant pollination","Assessing bee species richness in two Mediterranean communities: importance of habitat type and sampling techniques","Organic dairy farming: impacts on insect-flower interaction networks and pollination","Bee diversity in naturalizing patches of Carolinian grasslands in Southern Ontario, Canada","Gardens benefit bees and enhance pollination in intensively managed farmland","Differential effects of habitat isolation and landscape composition on wasps, bees, and their enemies","A comparison of bee communities of Chicago green roofs, parks and prairies","Land use intensity in grasslands: Changes in biodiversity, species composition and specialisation in flower visitor networks","Effect of biotic factors on the spatial distribution of stingless bees (Hymenoptera: Apidae, Meliponini) in fragmented Neotropical habitats","Supporting wild pollinators in a temperate agricultural landscape: Maintaining mosaics of natural features and production","Pollinator diversity (Hymenoptera and Diptera) in semi-natural habitats in Serbia during summer","The use of off-farm habitats by foraging bumblebees in agricultural landscapes: implications for conservation management","Sex in the city: Reproductive success of Digitalis purpurea in a gradient from urban to rural sites","Biodiversity of man-made open habitats in an underused country: a class of multispecies abundance models for count data","Local Distribution and Floral Preferences of Founder Bumblebee Queens in Korea","Movement and phenology of bees in a subtropical Australian agricultural landscape","Additive effects of exotic plant abundance and land-use intensity on plant-pollinator interactions","Effect of deforestation on a southwest Ghana dung beetle assemblage (Coleoptera: Scarabaeidae) at the periphery of Ankasa conservation area","Changes in Brazilian Drosophilidae (Diptera) Assemblages Across an Urbanisation Gradient","Changes in Arthropod Assemblages along a Wide Gradient of Disturbance in Gabon","Land Use and Mosquito Diversity in the Peruvian Amazon","Dung beetle (Coleoptera: Scarabaeidae: Scarabaeinae) diversity in continuous forest, forest fragments and cattle pastures in a landscape of Chiapas, Mexico: the effects of anthropogenic changes","Diversity and abundance of terrestrial ants along a gradientof land use intensification in a transitional forest-savannahzone of Cte d'Ivoire","Habitat fragmentation alters the structure of dung beetle communities in the Atlantic Forest","Biodiversity and ecosystem function of tropical forest dung beetles under contrasting logging regimes","Assessment of grazing effect on sheep fescue (Festuca valesiaca) dominated steppe rangelands, in the semi-arid Central Anatolian region of Turkey","Plant diversity in sacred forest fragments of Western Ghats: a comparative study of four life forms","MONITORING PHEASANTS (Phasianidae) IN THE WESTERN HIMALAYAS TO MEASURE THE IMPACT OF HYDRO-ELECTRIC PROJECTS","Unpublished data of woody species study in Nepal","Bird community structure in natural and urbanized habitats along an altitudinal gradient in Pauri district (Garhwal Himalaya) of Uttarakhand state, India","Assessing the impact of reforestation on the diversity of Mediterranean terrestrial Gastropoda","Spider biodiversity and density following cultivation in pastures in the Waikato, New Zealand","Biodiversity of indigenous tussock grassland sites in Otago, Canterbury and the central North Island of New Zealand I. The macroinvertebrate fauna","Influence of pastoral management on plant biodiversity in a depleted short tussock grassland, Mackenzie Basin","Synergistic interactions between edge and area effects in a heavily fragmented landscape","Soil fauna in grazed New Zealand hill country pastures at two management intensities","Separating the effects of defoliation and dairy cow treading pressure on the abundance and diversity of soil invertebrates in pastures","Biodiversity of indigenous tussock grassland sites in Otago, Canterbury and the Central North Island of New Zealand VI. Coleoptera biodiversity, community structure, exotic species invasion, and the effect of disturbance by agricultural development","Plant-mediated and nonadditive effects of two global change drivers on an insect herbivore community","Arboreal arthropod sampling methods for urban trees","Altered species interactions at forest edges: contrasting edge effects on bumble bees and their phoretic mite loads in temperate forest remnants","Honeybee declines in a changing landscape: interactive effects of honeybee declines and land-use intensification on pollinator communities","Resource availability and foraging of Silvereyes (Zosterops lateralis) in urban trees","Big and aerial invaders: dominance of exotic spiders in burned New Zealand tussock grasslands","The winners and losers of land use intensification: pollinator community disassembly is non-random and alters functional diversity","Oribatid mite diversity and community dynamics in a spruce chronosequence","Long-term patterns in tropical reforestation: plant community composition and aboveground biomass accumulation","Structure and diversity of secondary tropical dry forests in Mexico, differing in their prior land-use history","The value of primary, secondary, and plantation forests for Neotropical epigeic arachnids","Rapid Recovery of Biomass, Species Richness, and Species Composition in a Forest Chronosequence in Northeastern Costa Rica","The earthworm fauna of regenerating forests and anthropogenic habitats in the coastal region of Paran","Early Trajectories of Spontaneous Vegetation Recovery after Intensive Agricultural Land Use","The high value of logged tropical forests: lessons from northern Borneo","Butterfly community recovery in degraded rainforest habitats in the Upper Guinean Forest Zone (Kakum forest, Ghana)","Recovery of amphibian species richness and composition in a chronosequence of secondary forests, northeastern Costa Rica","Understory plant species and functional diversity in the degraded wet tropical forests of Kolombangara Island, Solomon Islands","Primary tree species diversity in secondary fallow forests of Laos","Changes in carabid beetle assemblages across an urban-rural gradient in Japan","Biodiversity and trace element content of epiphytic bryophytes in urban and extraurban sites of southern Italy","Biodiversity on urban roundabouts - Hemiptera, management and the species-area relationship","Carabid beetle community composition, body size, and fluctuating asymmetry along an urban-rural gradient","Patterns in ground beetle (Coleoptera: Carabidae) assemblages along an urbanisation gradient in Denmark","Changes of isopod assemblages along an urban-suburban-rural gradient in Hungary","Preliminary data on the species diversity of Collembola (Hexapoda: Collembola) along an urban gradient in Bucureti","Extreme life history plasticity and the evolution of invasive characteristics in a native ant","The confounding influence of homogenising invasive species in a globally endangered and largely urban biome: Does habitat quality dominate avian biodiversity?","Multi-scaled habitat considerations for conserving urban biodiversity: native reptiles and small mammals in Brisbane, Australia","Effects of urbanization on ground-dwelling spiders in forest patches, in Hungary","Screening of xylophagous fungi associated with Platanus acerifolia in urban landscapes: Biodiversity and potential biodeterioration","Decline in the diversity of willow trunk-dwelling weevils (Coleoptera: Curculionoidea) as a result of urban expansion in Beijing, China","The Effect of Urbanization on Ant Abundance and Diversity: A Temporal Examination of Factors Affecting Biodiversity","Urban summer heat load: meteorological data as a proxy for metropolitan biodiversity","Structure and species composition of ground bryophyte community of high-altitude young silvicultural cutovers in Rangtang County, China: evaluation on effects of clear-cutting and silvicultural management","Evaluation of species composition and development of bryophyte community during early natural recovery progress of high-altitude spruce cutovers","Recovery of woody plant diversity in tropical rain forests in southern China after logging and shifting cultivation","Communities of soil macrofauna in green spaces of an urbanizing city at east China","Regeneration strategies influence ground bryophyte composition and diversity after forest clearcutting","Species richness and guild composition in rubber plantations compared to secondary forest on Hainan Island, China","Using soil and litter arthropods to assess the state of rainforest restoration","A comparison of orang-utan density in a logged and unlogged forest on Sumatra","Species richness and community composition of songbirds in a tropical forest-agricultural landscape","Methods for conservation outside of formal reserve systems: The case of ants in the seasonally dry tropics of Veracruz, Mexico","Spatiotemporal variation in the diversity of Hymenoptera across a tropical habitat gradient","The impacts of forest clearance on lizard, small mammal and bird communities in the arid spiny forest, southern Madagascar","Beetle (Coleoptera) and spider (Araneae) diversity in a mosaic of farmland, edge, and tropical forest habitats in western Costa Rica","Disturbance effects on diversity of epiphytes and moths in a montane forest in Ecuador","Mammal persistence and abundance in tropical rainforest remnants in the southern Western Ghats, India","Oil palm expansion into rain forest greatly reduces ant biodiversity in canopy, epiphytes and leaf-litter","Effects of farm and landscape management on bird and butterfly conservation in western Honduras","Abundance responses of frugivorous bats (Stenodermatinae) to coffee cultivation and selective logging practices in mountainous central Veracruz, Mexico","Bird communities of the lower Waria Valley, Morobe Province, Papua New Guinea: a comparison between habitat types","Effects of forest modification on bird community composition and seed removal in a heterogeneous landscape in South Africa","The distribution and abundance of small mammals in agroecosystems of southeastern Brazil","Terrestrial non-volant small mammals in agro-silvicultural landscapes of Southeastern Brazil","Land use practices and their implications on soil macro-fauna in Maasai Mara ecosystem","Avian Habitat Preference in Tropical Forest Restoration in Southern Costa Rica","The influence of agricultural system, stand structural complexity and landscape context on foraging birds in oil palm landscapes","Effects of Oil-Palm Plantations on Diversity of Tropical Anurans","Soil macrofauna as indicators of soil quality and land use impacts in smallholder agroecosystems of western Nicaragua","Avian responses to fragmentation of the Maulino Forest in central Chile","Presence and abundance of birds in an Atlantic forest reserve and adjacent plantation of shade-grown yerba mate, in Paraguay","Impacto da implementao de medidas de gesto do habitat nas populaes de coelho-bravo (Oryctolagus cuniculus algirus) no Parque Natural do Sudoeste Alentejano e Costa Vicentina","Termite (Insecta, Isoptera) richness in primary and secondary Atlantic Forest in southeastern Bahia","Grazing promotes dung beetle diversity in the xeric landscape of a Mexican Biosphere Reserve","Human Disturbance affects a Deciduous Forest Bird Community in the Andean Foothills of Central Bolivia","Effect of the forest succession on the anurans (Amphibia: Anura) of the Reserve Catuaba and its periphery, Acre, southwestern Amazonia","Diversidad de lagartijas en cafetales y bosque primario en el Soconusco chiapaneco","Avian Assemblages in Altered and Natural Grasslands in the Northern Campos of Uruguay","Diversidad y distribucin de palmas (Arecaceae) en tres fragmentos de bosque muy hmedo en Costa Rica","Effects of pasture implantation on the termite (Isoptera) fauna in the Central Brazilian Savanna (Cerrado)","Ants as biological indicators of Wayana Amerindian land use in French Guiana","The effect of land use on snail species richness and diversity in the tropical rainforest of south-western Nigeria","Small off-shore islands can serve as important refuges for endemic beetle conservation","Fauna assemblages in regrowth vegetation in tropical open forests of the Northern Territory, Australia","Riqueza e abundncia de aves em trs estgios sucessionais da floresta ombrfila densa submontana, Antonina, Paran","Floristic and structural comparisons among palm communities in primary and secondary forest fragments of the Raimundo Irineu Serra Environmental Protection Area - Rio Branco, Acre, Brazil","Functional response traits in relation to land use change in the Montado","Long-term effects of fragmentation and fragment properties on bird species richness in Hawaiian forests","Recovery of plant species composition and ecosystem function after cessation of grazing in a Mediterranean grassland","How might intensification of farming influence dung beetle diversity (Coleoptera: Scarabaeidae) in Maputo Special Reserve (Mozambique)?","Flying Foxes Prefer to Forage in Farmland in a Tropical Dry Forest Landscape Mosaic in Fiji","Unexpected changes in the bird assemblage in areas under selective logging in piedmont forest in northwestern Argentina","Plant and bird diversity in natural forests and in native and exotic plantations in NW Portugal","Study of the Dung Beetle (Coleoptera: Scarabaeidae) Community at Two Sites: Atlantic Forest and Clear-Cut, Pernambuco, Brazil","Efecto del grado de disturbio sobre el ensamble de aves en la reserva provincial Parque Luro, La Pampa, Argentina","Espcies de Scarabaeinae (Coleoptera: Scarabaeidae) de fragmentos florestais com diferentes nveis de alterao em Santa Maria, Rio Grande do Sul","Patterns and magnitude of temporal change in avian communities in the Ecuadorian Andes","Population densities of understorey birds across a habitat gradient in Palawan, Philippines: implications for conservation","Effects of land use on nocturnal birds in a Mediterranean agricultural landscape","Do eucalypt plantations provide habitat for native forest biodiversity?","Efectos de la extraccin de turba sobre la composicin y estructura de una turbera de Sphagnum explotada y abandonada hace 20 aos, Chile","Empobrecimiento de bosques fragmentados en el norte de la Gran Sabana, Venezuela","Vascular epiphytes and climbing plants diversity in an agroforestal landscape in southern Chile: a comparison among native forest fragments","Assessing the effects of selective logging on birds in Neotropical piedmont and cloud montane forests","The effect of reduced-impact logging on fruit-feeding butterflies in Central Amazon, Brazil","Patterns of plant species richness of temperate and tropical grassland in South Africa","Spiders (Arachnida, Araneae) associated to agroecosystems in the Elqui Valley (Coquimbo Region, Chile)","Distribution of nocturnal birds (Strigiformes and Caprimulgidae) in relation to land-use types, extent and configuration in agricultural landscapes of Central Italy","Rapid evaluation of threats to biodiversity: human footprint score and large vertebrate species responses in French Guiana","Differences in the Effects of Selective Logging on Amphibian Assemblages in Three West African Forest Types","Land snail diversity in post extraction secondary forest reserves in Edo State, Nigeria","Species Composition of Termites (Isoptera) in Different Cerrado Vegetation Physiognomies","Dung beetles (Coleoptera: Scarabaeoidea) in three landscapes in Mato Grosso do Sul, Brazil","The value of primary, secondary and plantation forests for Amazonian birds","A case study on the effects of disturbance and conversion of tropical lowland rain forest on the non-volant small mammals in north Borneo: Management implications","The effects of grazing and fire on vegetation and the vertebrate assemblage in a tropical savanna woodland in north-eastern Australia","The utilization of large savanna trees by elephant in southern Kruger National Park","\"Ordinary biodiversity\" in western Burkina Faso (West Africa): what vegetation do the state forests conserve?","Dynamics of the leaf-litter arthropod fauna following fire in a neotropical woodland savanna","Fire tolerance of perennial grass tussocks in a savanna woodland","Conservation value of low fire frequency in tropical savannas: Ants in monsoonal northern Australia","Effects of experimental fire regimes on the abundance and diversity of cursorial arachnids of Brazilian savannah (cerrado biome)","Impact of land-use type and harvesting on population structure of a non-timber forest product-providing tree in a semi-arid savanna, West Africa","The influence of fire frequency on the abundance of Maerua subcordata in the Serengeti National Park, Tanzania","Post-wildfire regeneration of rangeland productivity and functionality - observations across three semi-arid vegetation types in South Africa","Effects of forest disturbance on the structure of ground-foraging ant communities in central Amazonia","Responses of ants to selective logging of a central Amazonian forest","The structure of raptor assemblages in riparian environments in the south-west of the Northern Territory, Australia","Responses of vertebrates to pastoralism, military land use and landscape position in an Australian tropical savanna","Diversity of pselaphine beetles (Coleoptera: Staphylinidae: Pselaphinae) in eastern Thailand","Bat diversity in tropical forest and agro-pastoral habitats within a protected area in the Philippines","Dung Beetle Assemblages and Seasonality in Primary Forest and Forest Fragments on Agricultural Landscapes in Budongo, Uganda","Hunting for Sustainability in Tropical Secondary Forests","Diversity and similarity of butterfly communities in five different habitat types at Tam Dao National Park, Vietnam","Orangutan population density, forest structure and fruit availability in hand-logged and unlogged peat swamp forests in West Kalimantan, Indonesia","How does landscape context contribute to effects of habitat fragmentation on diversity and population density of butterflies?","Determination of ape distribution and population size using ground and aerial surveys: a case study with orang-utans in lower Kinabatangan, Sabah, Malaysia","Diversity and community composition of butterflies and odonates in an ENSO-induced fire affected habitat mosaic: a case study from East Kalimantan, Indonesia","Effects of habitat area, isolation, and landscape diversity on plant species richness of calcareous grasslands","Species diversity and habitat fragmentation: frogs in a tropical montane landscape in Mexico","Life after logging: Post-logging recovery of a neotropical bat community","Conservation of Vascular Epiphyte Diversity in Mexican Coffee Plantations","Tree diversity in primary forest and different land use systems in Central Sulawesi, Indonesia","Effects of biomass extraction on vegetation structure, diversity and composition of forests in Sariska Tiger Reserve, India","Burning and logging differentially affect endemic vs. widely distributed butterfly species in Borneo","Arthropod Diversity in Lama Forest Reserve (South Benin), a Mosaic of Natural, Degraded and Plantation Forests","Short-term responses of birds to forest gaps and understory: An assessment of reduced-impact logging in a lowland Amazon forest","The value of primary, secondary and plantation forests for fruit-feeding butterflies in the Brazilian Amazon","Bird assemblages in secondary forests developing after slash-and-burn agriculture in the Brazilian Amazon","The contribution of cacao agroforests to the conservation of lower canopy ant and beetle diversity in Indonesia","Harvestmen in an Atlantic forest fragmented landscape: Evaluating assemblage response to habitat quality and quantity","Quantifying the biodiversity value of tropical primary, secondary, and plantation forests","Impacts of El Nino related drought and forest fires on sun bear fruit resources in lowland dipterocarp forest of East Borneo","The importance of cenotes in conserving bat assemblages in the Yucatan, Mexico","Satellite detection of bird communities in tropical countryside","Effects of extractive disturbance on bird assemblages, vegetation structure and floristics in tropical scrub forest, Sariska Tiger Reserve, India","Species richness, composition and abundance of fruit-feeding butterflies in the Brazilian Atlantic Forest: comparison between a fragmented and a continuous landscape","Effects of rain forest logging on species richness and assemblage composition of small mammals in southeast Asia","Phyllostomid bats of lowland Amazonia: Effects of habitat alteration on abundance","Do secondary forests act as refuges for old growth forest animals? Recovery of ant diversity in the Atlantic forest of Brazil","Conservation value of forest plantations for bird communities in western Kenya","Understanding the biodiversity consequences of habitat change: the value of secondary and plantation forests for neotropical dung beetles","Tolerance of frugivorous birds to habitat disturbance in a tropical cloud forest","What loggers leave behind: Impacts on big-leaf mahogany (Swietenia macrophylla) commercial populations and potential for post-logging recovery in the Brazilian Amazon","Pollen dispersal and genetic structure of the tropical tree Dipteryx panamensis in a fragmented Costa Rican landscape","Effects of rainforest fragmentation and shade-coffee plantations on spider communities in the Western Ghats, India","Effects of reduced-impact logging and forest physiognomy on bat populations of lowland Amazonian forest","Sustaining biodiversity in ancient tropical countryside","Diversity and composition of Amazonian moths in primary, secondary and plantation forests","Invasion and retreat: shifting assemblages of dung beetles amidst changing agricultural landscapes in central Peru","Complementary roles of home gardens and exotic tree plantations as alternative habitats for plants of the Ethiopian montane rainforest","Alpha and beta diversity of plants and animals along a tropical land-use gradient","Traditional land use associated with swidden agriculture changes encounter rates of the top predator, the army ant, in Southeast Asian tropical rain forests","Vertebrate population responses to reduced-impact logging in a neotropical forest","Habitat fragmentation causes immediate and time-delayed biodiversity loss at different trophic levels","Deforestation and the population decline of the army ant Dorylus wilverthi in western Kenya over the last century","Explaining the saproxylic beetle diversity of a protected Mediterranean area","Do riparian reserves support dung beetle biodiversity and ecosystem services in oil palm-dominated tropical landscapes?","Impacts of forestry on ant species richness and composition in warm-temperate forests of Japan","Effects of grazing intensity on bird assemblages and populations of Hungarian grasslands","Species traits as predictors of lepidopteran composition in restored and remnant tallgrass prairies","Land use and habitat gradients determine bird community diversity and abundance in suburban, rural and reserve landscapes of Minnesota, USA","Snake species distributions and temperate grasslands: A case study from the American tallgrass prairie","Bird assemblages in pine plantations replacing native ecosystems in NW Patagonia","Habitat and landscape characteristics underlying anuran community structure along an urban-rural gradient","Butterfly distribution and abundance is affected by variation in the Swedish forest-farmland landscape","Understory succession in post-agricultural oak forests: Habitat fragmentation affects forest specialists and generalists differently","Pasture area and landscape heterogeneity are key determinants of bird diversity in intensively managed farmland","Effects of Habitat Size, Vegetation Cover, and Surrounding Land Use on Diptera Diversity in Temperate Nearctic Bogs","Managing the forest for more than the trees: effects of experimental timber harvest on forest Lepidoptera","Comparative study of forest-dwelling bats' abundances and species richness between old-growth forests and conifer plantations in Nikko National Park, central Japan","The effect of clearing on plant composition in mulga (Acacia aneura) dry forest, Australia","Old park trees as habitat for saproxylic beetle species","Effects of grazing, vegetation structure and landscape complexity on grassland leafhoppers (Hemiptera: Auchenorrhyncha) and true bugs (Hemiptera: Heteroptera) in Hungary","Habitat use by carnivores at different spatial scales in a plantation forest landscape in Patagonia, Argentina","Effect of forest shape on habitat selection of birds in a plantation-dominant landscape across seasons: comparison between continuous and strip forests","Effects of habitat degradation on the lizard assemblage in the Arid Chaco, central Argentina","Sensitivity of insectivorous bats to urbanization: Implications for suburban conservation planning","Impact of game hunting by the Kayapo of south-eastern Amazonia: implications for wildlife conservation in tropical forest indigenous reserves","The importance of secondary forest blocks for terrestrial mammals within an Acacia/secondary forest matrix in Sarawak, Malaysia","Status and distribution of the leopard in the central hills of Sri Lanka","Spatial and temporal effects of grazing management and rainfall on the vertebrate fauna of a tropical savanna","Landscape and patch attributes impacting medium- and large-sized terrestrial mammals in a fragmented rain forest","Habitat and human factors associated with white-tailed deer density in the tropical dry forest of Tehuacan-cuicatlan biosphere Reserve, Mexico","Forest loss or management intensification? Identifying causes of mammal decline in cacao agroforests","Amphibians and reptiles in tropical rainforest fragments on Negros Island, the Philippines","Conservation value of forest fragments to Palaeotropical bats","Nested species subsets of amphibians and reptiles on Neotropical forest islands","Mammals in a fragmented savannah landscape in south-western Brazil","Deforestation and Avian Extinction on Tropical Landbridge Islands","Nestedness for different reasons: the distributions of birds, lizards and small mammals on islands of an inundated lake","Effects of anthropogenic environmental changes on amphibian diversity in the rain forests of eastern Madagascar","The impact of fire and forest conversion into savanna on the bird communities of West Madagascan dry forests","Effects of karst forest degradation on pulmonate and prosobranch land snail communities in Sabah, Malaysian Borneo","Invasibility and species richness of island endemic arthropods: a general model of endemic vs. exotic species","Butterfly diversity in Mediterranean islands and in Pentadaktylos Pinus brutia forests of Cyprus","Structural and environmental characterization of old-growth temperate rainforests of northern Chiloe Island, Chile: Regional and global relevance","Landscape and patch-level factors influence bird communities in an urbanized tropical island","Investigating residual effects of selective logging on ant species assemblages in Sinharaja Forest Reserve, Sri Lanka","Avian diversity and feeding guilds in a secondary forest, an oil palm plantation and a paddy field in riparian areas of the Kerian River basin, Perak, Malaysia","Changes in the diversity of soil arbuscular mycorrhizal fungi after cultivation for biofuel production in a Guantanamo (Cuba) tropical system","Endangered anurans in a novel forest in the highlands of Sri Lanka","Forest restoration and parasitoid wasp communities in montane Hawai'i","Influence of variations in land use intensity on species diversity and abundance of small mammals in the Nama Karoo, Namibia","Effects of land use on ant species composition and diaspore removal in exotic grasslands in the Brazilian Pantanal (Hymenoptera: Formicidae)","Grazing impacts on moth diversity and abundance on a Scottish upland estate","Diversity Pattern of Bats at Two Contrasting Habitat Types along Kerian River, Perak, Malaysia","The Conservation biology of the Leopard Panthera pardus in Gabon: Status, threats and strategies for conservation","Bushmeat hunting in Dwesa and Cwebe Nature Reserves, Eastern Cape, South Africa","Game Vertebrate Densities in Hunted and Nonhunted Forest Sites in Manu National Park, Peru","Forest duiker (Cephalophus spp.) abundance and hunting activities in the Kakum conservation area, Ghana","Carabid beetles (Coleoptera: Carabidae) at forest-farmland edges in southern Finland","Oribatid mite (Acari) community structure in steppic habitats of Burgos Province, central northern Spain","Effect of land-use heterogeneity on carabid communities at the landscape scale","Effects of abandonment of subalpine hay meadows on plant and invertebrate diversity in Transylvania, Romania","Long-term succession of oribatid mites after conversion of croplands to grasslands","Response of collembolan communities to land-use change and grassland succession","The potential of grass field margin management for enhancing beetle diversity in intensive livestock farms","Plant diversity in crop fields and woody hedgerows of organic and conventional farms in contrasting landscapes","The early effects of afforestation on biodiversity of grasslands in Ireland","Effects of exotic conifer plantations on the biodiversity of understory plants, epigeal beetles and birds in Nothofagus dombeyi forests","How does grazing intensity influence the diversity of plants and insects in a species-rich upland grassland on basalt soils?","Soil fauna in sheep-grazed hill pastures under organic and conventional livestock management and in an adjacent ungrazed pasture","Effect of land abandonment on the vegetation of upland semi-natural grasslands in the Western Balkan Mts., Bulgaria","Grazing impacts on Auchenorrhyncha diversity and abundance on a Scottish upland estate","Does Cattle Grazing Affect Ant Abundance and Diversity in Temperate Grasslands?","The impact of forest conversion to oil palm on arthropod abundance and biomass in Sabah, Malaysia","Unpublished data of reptilian and amphibian diversity in six countries in Central America","Ant diversity in a Peninsular Malaysian mangrove forest and oil palm plantation","Bird species richness in a Bornean exotic tree plantation: A long-term perspective","Reconciling Food Production and Biodiversity Conservation: Land Sharing and Land Sparing Compared","Bird species richness and abundance in different forest types at Kakamega Forest, western Kenya","Small mammal diversity and density on the Bokkeveld escarpment, South Africa - implications for conservation and livestock predation","The effect of ploughing and augmenting natural vegetation with commercial fynbos species on the biodiversity of Overberg Sandstone fynbos on the Agulhas Plain, South Africa","Habitat disturbance reduces seed dispersal of a forest interior tree in a fragmented African cloud forest","How does grazing intensity affect different vegetation types in arid Succulent Karoo, South Africa? Implications for conservation management","Guinean biodiversity at the edge: Rodents in forest patches of southern Mali","A quantitative comparison of frugivorous tephritids (Diptera: Tephritidae) in tropical forests and rural areas of the Democratic Republic of Congo","Amphibian community along elevational and habitat disturbance gradients in the Taita Hills, Kenya","Two-Stage Recovery of Amphibian Assemblages Following Selective Logging of Tropical Forests","Population density and habitat preferences of forest duikers in Moukalaba-Doudou National Park, Gabon","Vegetation composition and structure influences bird species community assemblages in the highland agricultural landscape of Nyandarua, Kenya","Grassland bird response to vegetation structural heterogeneity and clearing of invasive bramble","Effects of timber harvest on forest Lepidoptera: community, guild and species responses","Effects of Buffer-strip retention and clearcutting on land snails in Boreal Riparian Forests","Effects of environment, habitat configuration and forest continuity on the distribution of forest plant species","The birds of the Comoro Islands","Separating the effects of forest type and elevation on the diversity of litter invertebrate communities in a humid tropical forest in Puerto Rico","Impacts of rain forest fragmentation on butterflies in northern Borneo: species richness, turnover and the value of small fragments","The diversity and conservation of plant reproductive and dispersal functional traits in human-dominated tropical landscapes","Herpetofauna diversity and microenvironment correlates across a pasture-edge-interior ecotone in tropical rainforest fragments in the Los Tuxtlas Biosphere Reserve of Veracruz, Mexico","Relationship between anurans diversity and successional stages of a very humid low montane forest in Valle del Cauca, southwestern of Colombia","Accessible habitat: an improved measure of the effects of habitat loss and roads on wildlife populations","The effects of forest patch size and matrix type on changes in carabid beetle assemblages in an urbanized landscape","Spatio-temporal dymanics of snake diversity in four habitats with different degrees of anthropogenic disturbance in the Gorgona Island National Natural Park in the Colombian Pacific","Diversity of vascular plant communities along a disturbance gradient in a central mid-hill community forest of Nepal","Forest biodiversity gradients and the human impact in Annapurna Conservation Area, Nepal","Contrasting resource-dependent responses of hoverfly richness and density to landscape structure","Hydrology and management of turloughs (temporary lakes) affect marsh fly (Sciomyzidae: Diptera) communities","Unexpected understorey community development after 30 years in ancient and post-agricultural forests","Land use intensity drives the local variation of lichen diversity in Mediterranean ecosystems sensitive to desertification","Community-level diversity modelling of birds and butterflies on Anjouan, Comoro Islands","Differential effects of vegetation restoration in Mediterranean abandoned cropland by secondary succession and pine plantations on bird assemblages","Below-ground secondary succession in tropical forests of Borneo","Effects of anthropogenic activities on lizard communities in northern Madagascar","The effects of land-use change on arthropod richness and abundance on Santa Maria Island (Azores): unmanaged plantations favour endemic beetles","Lizard assemblages in a fragmented landscape of central Chile","Understory bird communities in Amazonian rainforest fragments: species turnover through 25 years post-isolation in recovering landscapes","Diversity pattern of butterfly communities (Lepidoptera, Papilionoidae) in different habitat types in a tropical rain forest of southern Vietnam","Biodiversity in urban ecosystems: Plants and macromycetes as indicators for conservation planning in the city of Coimbra (Portugal)","Effect of protected area category on mammal abundance in Western Ghana","Effects of partial cutting and partial disturbance by wind and insects on stand composition, structure and growth in boreal mixedwoods","Organic Farming and Landscape Structure: Effects on Insect-Pollinated Plant Diversity in Intensively Managed Grasslands","High bee and wasp diversity in a heterogeneous tropical farming system compared to protected forest","Patterns of forest vegetation responses to edge effect as revealed by a continuous approach","Small mammal assemblages in fragmented shrublands of urban areas of Central Chile","Evaluating the effects of habitats on birds in the walnut fruit forests: a case study from Kyrgyzstan","Diversity of the genus Dolichopus Latreille in three different habitats of East Azerbaijan Province, with new records for Iran","The arable plant diversity of intensively managed farmland: Effects of field position and crop type at local and landscape scales","An investigation into bee assemblage change along an urban-rural gradient","Forest-land use complementarity modifies community structure of a tropical herpetofauna","The conservation value of secondary forests in the southern Brazilian Mata Atlantica from a spider perspective","Effect of forest fragmentation on bird species richness in Papua New Guinea","Effect of Small Ruminant Grazing on the Plant Community Characteristics of Semiarid Mediterranean Ecosystems","Haying and grazing effects on the butterfly communities of two Mediterranean-area grasslands","The effects of human trampling on the microbiological properties of soil and vegetation in Mediterranean mountain areas","Impact of tillage system on arbuscular mycorrhiza fungal communities in the soil under Mediterranean conditions","Assessing the effects of forest management on epiphytic lichens in coppiced forests using different indicators","Butterfly and grasshopper diversity patterns in humid Mediterranean grasslands: the roles of disturbance and environmental factors","Comparing Dung Beetle Species Assemblages Between Protected Areas and Adjacent Pasturelands in a Mediterranean Savanna Landscape","Long-term responses of Mediterranean birds to forest fuel management","Forest fuel management as a conservation tool for early successional species under agricultural abandonment: The case of Mediterranean butterflies","Composition and abundance of Anura in two forest types (natural and planted) in the Eastern Cordillera of Colombia","Limitation of nesting resources for ants in Colombian forests and coffee plantations","Diversidad de escarabajos coprofagos (Coleoptera: Scarabaeidae) en un bosque de galeria con tres estadios de alteracion","Variation of the orchid bees community (Hymenoptera : Apidae) in three altered habitats of the Colombian \"llano\" piedmont","Diversidad de abejas (Hymenoptera: Apoidea) en estados sucesionales del bosque humedo tropical","Response of Ants and Their Seed Removal in Rehabilitation Areas and Forests at El Cerrejon Coal Mine in Colombia","Vascular epiphytes in dry oak forests show resilience to anthropogenic disturbance, Cordillera Oriental, Colombia","Mixed bird flocks: patterns of activity and species composition in a region of the Central Andes of Colombia","Anthropogenic Disturbance and Edge Effects on Anuran Assemblages Inhabiting Cloud Forest Fragments in Colombia","Seasonal variation in dung beetles (Coleoptera: Scarabaeidae: Scarabaeinae) from Serrania de Coraza, Sucre (Colombia)","Factores ambientales relacionados con la presencia y abundancia de las aves de los humedales de la Sabana de Bogot","Cross-taxon congruence of alpha and beta diversity among five leaf litter arthropod groups in Colombia","Macrofungal diversity in Colombian Amazon forests varies with regions and regimes of disturbance","Estructura de un ensamblaje de escarabajos coprofagos (Coleoptera: Scarabaeinae) en tres sitios con diferente uso del suelo en Antioquia, Colombia","Landscape simplification and altitude affect biodiversity, herbivory and Andean potato yield","Unpublished data of the response of ground beetles (Coleoptera: Carabidae) in the northeastern Colombian Andes to habitat modification","Scarabaeoidea superfamily (Insecta: Coleoptera) as a bioindicator element of anthropogenic disturbance in an amazon national park","Restoration of a forest ecosystem: The effects of vegetation and dispersal capabilities on the reassembly of plant-dwelling arthropods","Adult butterfly communities in coffee plantations around a protected area in the Western Ghats, India","Does habitat structure influence capture probabilities? A study of reptiles in a eucalypt forest","Surface-active arthropods in organic vineyards, integrated vineyards and natural habitat in the Cape Floristic Region","Assessing variation in wildlife biodiversity in the Tien Shan mountains of Kyrgyzstan using ancillary camera-trap photos","Identifying unidirectional and dynamic habitat filters to faunal recolonisation in restored mine-pits","Sacred forests are keystone structures for forest bird conservation in southwest China's Himalayan Mountains","The potential role of scattered trees for ant conservation in an agriculturally dominated neotropical landscape","Assessing rodent community responses in disturbed environments of the Chilean Patagonia","Human-induced disturbances influence on bird communities of coastal forests in Eastern Tanzania","Does coarse woody debris density and volume influence the terrestrial vertebrate community in restored bauxite mines?","Unpublished data of terrestrial vertebrates in South West Australia","Effects of livestock grazing and habitat characteristics on small mammal communities in the Knersvlakte, South Africa","Species richness and meta-community structure of land snails along an altitudinal gradient on Bioko Island, Equatorial Guinea","Anthropogenic disturbance changes the structure of arboreal tropical ant communities","Diversity and abundance of some ground-dwelling invertebrates in plantation vs. native forests in Tasmania, Australia","Exploring biological diversity, environment and local people's perspectives in forest landscapes: Methods for a multidisciplinary landscape assessment","URBANIZATION AND SPIDER DIVERSITY: INFLUENCES OF HUMAN MODIFICATION OF HABITAT STRUCTURE AND PRODUCTIVITY","Influence of land use on plant community composition and diversity in Highland Sourveld grassland in the southern Drakensberg, South Africa","Unpublished data of diversity and similarity of butterfly communities in five different habitat types at Tam Dao National Park, Vietnam","Shrew species diversity and abundance in Ziama Biosphere Reserve, Guinea: comparison among primary forest, degraded forest and restoration plots","Collapse of an arctic bird community resulting from ungulate-induced loss of erect shrubs","Rainwater harvesting and arthropod biodiversity within an arid agro-ecosystem","Multidisciplinary Landscape Assessment - Cameroon","Multidisciplinary Landscape Assessment - Philippines","Traditional agricultural gardens conserve wild plants and functional richness in arid South Sinai","Diversity patterns in the steppe of Argentinean southern Patagonia: environmental drivers and impact of grazing","Complementarity of indigenous flora in shrublands and grasslands in a New Zealand dryland landscape","The Effects of Management Systems on Ground-Foraging Ant Diversity in Costa Rica","Bird communities in logged and unlogged compartments in Budongo Forest, Uganda","Forest use and vertical stratification in fruit-feeding butterflies of Sulawesi, Indonesia: impacts for conservation","The effects of various forest uses on small mammal communities in Sarawak, Malaysia","High sensitivity of montane bird communities to habitat disturbance in Peninsular Malaysia","Identification of ecological indicators for monitoring ecosystem health in the trans-boundary W Regional park: A pilot study","Bat diversity and abundance associated with the degree of secondary succession in a tropical forest mosaic in south-eastern Mexico","The Value of Primary, Secondary, and Plantation Forests for a Neotropical Herpetofauna","How resilient are Andean montane forest bird communities to habitat degradation?","Secondary rain forests are not havens for reptile species in tropical Mexico","The impact of land-use change on larval insect communities: Testing the role of habitat elements in conservation","Bat diversity in the vegetation mosaic around a lowland dipterocarp forest of Borneo","Deforestation and the structure of frog communities in the Humedale Terraba-Sierpe, Costa Rica","Species compensation maintains abundance and raid rates of African swarm-raiding army ants in rainforest fragments","Arthropod Diversity as Affected by Agricultural Management (Organic and Conventional Farming), Plant Species, and Landscape Context","Impact of different land management on soil spiders (Arachnida: Araneae) in two Amazonian areas of Brazil and Colombia","Biodiversity of soil macrofauna in the New Forest: a benchmark study across a national park landscape","An assessment of pollution impacts due to the oil and gas industries in the Pechora basin, north-eastern European Russia","Effects of stand structure and landscape characteristics on habitat use by birds and small mammals in managed boreal forest of eastern Canada","Effects of experimental harvesting on spider (Araneae) assemblages in boreal deciduous forests","New records of rare species of Coleoptera found in Ukmerg district in 2004-2005","Different long-term and short-term responses of land snails to clear-cutting of boreal stream-side forests","Can Repeated Fertilizer Applications to Young Norway Spruce enhance Avian Diversity in Intensively Managed Forests?","Spatial distribution of meadow jumping mice (Zapus hudsonius) in logged boreal forest of northwestern Canada","Alternative Silvicultural Practices in Irregular Boreal Forests: Response of Beetle Assemblages","Partial cutting does not maintain spider assemblages within the observed range of natural variability in Eastern Canadian black spruce forests","Response of breeding songbirds to vegetation management in conifer plantations established in boreal mixedwoods","Do time-lagged extinctions and colonizations change the interpretation of buffer strip effectiveness? - a study of riparian bryophytes in the first decade after logging","Forest edge contrasts have a predictable effect on the spatial distribution of carabid beetles in urban forests","Songbird response to green-tree retention prescriptions in clearcut forests","The raw soil arthropods dataset and the raw trees & snags dataset from Prototype Phase (2003-2006) and Rotation 1 (2007-2012)","Carabid community and its fluctuation in farmland of salinity transforming area in the North China Plain: a case study in Quzhou County, Hebei Province","Nematode community structure under compost and chemical fertilizer management practice, in the north China plain","Effect of acetochlor and carbofuran on soil nematode communities in a Chinese soybean field","Understory plant diversity assessment of Eucalyptus plantations over three vegetation types in Yunnan, China","Ground Beetle (Coleoptera: Carabidae) Assemblages of Restored Semi-natural Habitats and Intensively Cultivated Fields in Northern China","Terrestrial herpetofaunal assemblages in secondary forests and exotic Lophostemon confertus plantations in South China"],"Publication_type":["Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific 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report (published)","Scientific article","Scientific article","Authored unpublished data","Scientific article","Scientific article","Scientific report (published)","Internet database","Internet database","Scientific article","Scientific book","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific article","Scientific report (published)","Internet database","Scientific article","Scientific article","Scientific article","Scientific 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granted","Full permission granted","Uncertain","Full permission granted","Uncertain","Full permission granted","For pollinator analysis only","Full permission granted","Full permission granted","Uncertain","Full permission granted","Full permission granted","Full permission granted","Uncertain","Full permission granted","Uncertain","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Uncertain","Uncertain","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Other - see notes for details","Other - see notes for details","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","For publication with proper referencing","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Data can be used, but cannot be redistributed","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","For pollinator analysis only","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Author requested consultation prior to publication; permission for incorporating data in the PREDICTS database WAS GRANTED","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Uncertain","Full permission granted","Full 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granted","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","For publication with proper referencing","Other - see notes for details","Full permission granted","Full permission granted","Uncertain","Full permission granted","Other - see notes for details","Other - see notes for details","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","For publication with proper referencing","Full permission granted","For publication with proper referencing","Full permission granted","Full permission granted","For publication with proper referencing","Full permission granted","For publication with proper referencing","Full 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granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Contacting authors - awaiting response","For publication with proper referencing","Other - see notes for details","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Data can be used, but coordinates must be coarsened in published material","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission 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proper referencing","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","Uncertain","Uncertain","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","For publication with proper referencing","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Other - see notes for details","Other - see notes for details","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Other - see notes for details","Other - see notes for details","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Other - see notes for details","Other - see notes for details","Full permission granted","Uncertain","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Uncertain","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Other - see notes for details","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Uncertain","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted","Full permission granted"],"Journal_title":["Journal of Applied Ecology","Conservation Biology","The American Naturalist","Oikos","Bulletin of Insectology","Horticultural Entomology","","European Journal of Entomology","Field and Forage Crops","Journal of Applied Ecology","Biodiversity and Conservation","Agriculture, Ecosystems and Environment","Biological Conservation","Biological Conservation","Molecular Ecology","Entomologia Generalis","Journal of Applied Ecology","Conservation Biology","Journal of Applied Ecology","Ecography","Biodiversity and Conservation","Journal of Applied Ecology","Agriculture, Ecosystems and Environment","Landscape Ecology","Journal of Economic Entomology","Insect Conservation and Diversity","Agriculture, Ecosystems and Environment","Biological Conservation","Molecular 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Conservation","New Zealand Journal of Agricultural Research","Journal of The Royal Society of New Zealand","New Zealand Journal of Ecology","Ecology","Applied Soil Ecology","Applied Soil Ecology","Journal of the Royal Society of New Zealand","Ecology","Journal of Insect Conservation","Insect Conservation and Diversity","","Emu","Biological Invasions","Diversity and Distributions","Soil Biology & Biochemistry","Ecological Applications","Forest Ecology & Management","Journal of Arachnology","Biotropica","Pesquisa Agropecuria Brasileira","Restoration Ecology","Biodiversity and Conservation","Journal of Insect Conservation","Biological Conservation","Biological Conservation","Forest Ecology & Management","Ecography","Plant Ecology","Basic and Applied Ecology","Basic and Applied Ecology","Acta Oecologica","European Journal of Soil Biology","Travaux du Musum National dHistoire Naturelle Grigore Antipa","Biological Invasions","Biological Conservation","Landscape Ecology","Landscape 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Research","PhD Thesis","South African Journal of Wildlife Research","Biotropica","Journal Of Ecology and Natural Environment","Journal of Insect Conservation","Journal of Natural History","Ecography","Biological Conservation","Applied Soil Ecology","Ecography","Journal of Applied Ecology","Agriculture, Ecosystems and Environment","Biodiversity and Conservation","Forest Ecology & Management","Grass and Forage Science","Pedobiologia","Plant Biosystems","Insect Conservation and Diversity","Rangeland Ecology and Management","Journal of Tropical Ecology","","Asian Myrmecology","Biological Conservation","Science","Ostrich","African Zoology","South African Journal of Botany","Oikos","Biological Conservation","Mammalian Biology","Bulletin of Entomological Research","Herpetotropicos","Conservation Biology","African Zoology","Ostrich","African Zoology","Ecological Applications","Conservation Biology","Journal of Vegetation Science","","Journal of Animal Ecology","Journal of Applied 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1DU","","","","","","","","","","","","","","","Universidad de las Amricas Puebla","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","Department of Zoology and Entomology, University of Pretoria, 1 Lynnwood Rd., Pretoria 0002, South Africa","1Lab. de Drosophila, Depto. Gentica, IB, Univ. Federal do Rio Grande do Sul, C. postal 15.053, 91501-970\nPorto Alegre, RS","Smithsonian Tropical Research Institute, Apartado 0843-03092, Balboa, Ancon, Panama City, Republic of Panama","Department of Ecology, Evolution and Environmental Biology, Columbia University, 1200 Amsterdam Ave., New York, NY 10027","El Colegio de la Frontera Sur, Carretera Panamericana y Periferico Sur, C.P. 29290 San Cristobal de\nlas Casas, Chiapas, Mexico","Universit de Cocody-Abidjan (UFR Biosciences)\nStation d'Ecologie de Lamto","Programa de Ps-Graduao em Biologia Animal, Universidade Federal de Pernambuco, Recife, PE 50670-901, Brazil","","UAF Cooperative Extension Service Tanana District \n724 27th Ave., Suite 2 and 3 \nP.O. Box 758155 \nFairbanks, AK 99775-8155","Samradni, 58 Lokmanya Colony, Kothrud, Pune 411038,\nIndia","Biodiversity & Environmental Sustainability (BEST) \nFirst Floor,143, F-17, \nSector-8, Rohini, \nNew Delhi-110085 \nIndia","University of Bergen\nP.O.Box 7800\n5020 Bergen","Avian Diversity and Bioacoustics Laboratory, Department of Zoology and Environmental Science, Gurukula Kangri University, Haridwar 249 404, Uttarakhand, India","CIBIO/InBIO, Centro de Investigacao em Biodiversidade e Recursos Geneticos, Universidade do\nPorto, Campus Agrario de Vairao, 4485-661 Vairao, Portugal","Ruakura Research Centre , AgResearch , Private Bag 3123, Hamilton, New Zealand","AgResearch Invermay , Private Bag 50 034, Mosgiel, New Zealand","School of Forestry, University of Canterbury, Private Bag 4800, Christchurch, New Zealand","","Ecology, Institute of Natural Resources, Massey University, Private Bag 11222, Palmerston North 4442, New Zealand","Ecology, Institute of Natural Resources, Massey University, Private Bag 11222, Palmerston North 4442, New Zealand","AgResearch Invermay, Mosgiel, New Zealand","School of Biological Sciences, University of Canterbury, Christchurch 8041 New Zealand","Botany Department, University of Otago, PO Box 56,\nDunedin 9010, New Zealand","Department of Life Sciences, Imperial College London, Ascot, UK","","Botany Department, University of Otago, PO Box 56, Dunedin, New Zealand.","Center for Macroecology, Evolution and Climate, Natural\nHistory Museum of Denmark, University of Copenhagen,\nUniversitetsparken 15, 2100 Copenhagen E, Denmark","Ecosystem Management, School of Environment and Rural Sciences, University of New England, Armidale, NSW, Australia","","","","","","","","","","","","","Hiroshima University, Hiroshima, Japan","University of Naples Federico II, Naples, Italy","Anglia Ruskin University, Cambridge","Institute of Zoology, University of Hamburg, Germany","MTA-ELTE-MTM, Ecology Research Group, Budapest, Hungary","","Institute of Biology, Romanian Academy, Bucharest, Romanian","Purdue University, IN, USA","Imperial College London, Silwood Park, SL5 7PY","Griffith Environmental Futures Centre, Griffith University, Brisbane, Australia","University of Debrecen, Debrecen, Hungary","University of Buenos Aires - Facultad de Ciencias Exactas y Naturales","Research Center of Eco-Environmental Sciences, Chinese Academy of Sciences in Beijing","Purdue University, Indiana","Cologne Biocenter, Zoological Institute, University of Cologne, Germany","Chengdu Institute of Biology, Chengdu 610041, China","Chengdu Institute of Biology, Chinese Academy of Sciences, Chengdu 610041","Key Laboratory of Forest Ecology and Environment, The State Forestry Administration, Institute of Forest Ecology, Environment and Protection,Chinese Academy of Forestry, Beijing 100091, China","Jiangsu Provincial Key Laboratory of Coastal Wetland Bioresources and Environmental Protection, Yancheng Teachers University, Yancheng, 224051, China","Graduate University of Chinese Academy of Sciences, Beijing 100049, Peoples Republic of China","Guangdong Entomological Institute/South China Institute of Endangered Animals, Guangzhou 510260, China","Rainforest CRC and Environmental Sciences, Griffith University, Nathan, QLD 4111, Australia","Zoological Museum of the\nUniversity of Zurich, Winterthurerstr. 190, 8057 Zurich, Switzerland.","Conservation Science Program, World Wildlife Fund \n(U.S.), Washington, DC","Department of Environmental Biology, Curtin University of Technology, P.O. Box U 1987, Perth, WA 6845, Australia","Agroecology, University of Goettingen, Georg-August-Universitat, Waldweg 26, D-37073 Goettingen, Germany","Biology Division, University of Brighton, Cockcroft Building, Moulsecoomb, Brighton, East Sussex BN2 4GJ, UK","Interdisciplinary Arts & Sciences, University of Washington, Tacoma, 1900 Commerce Street (Box 358436), Tacoma, Washington 98402","Botanic Garden and Botanical Museum Berlin-Dahlem, Free University of Berlin, Konigin-Luise-Str. 6-8, 14195 Berlin, Germany","Nature Conservation Foundation, 3076/5, IV Cross, Gokulam Park, Mysore 570 002, India","Insect Ecology Group, University Museum of Zoology, Downing Street, Cambridge CB2 3EJ, UK","Department of Natural Resources, Cornell University, Ithaca, New York 14853 USA","Instituto de Ecologa A. C., Apdo. Postal 63, CP 91000 Xalapa, Ver, Mexico","Coral Cay Conservation, 1st Floor Block, 1 Elizabeth House, 39 York Road, London SW1 7NQ UK","Biodiversity and Climate Research Centre (BiK-F)\nProject Area B: Biodiversity Dynamics and Climate\nSenckenberganlage 25\nD-60325 Frankfurt am Main\nGermany","Isotopic Ecology Laboratory, University of So Paulo, Piracicaba, P.O. Box 96, 13416-000 Piracicaba, So Paulo, Brazil","Universidade Sagrado Corao (USC), Rua Irm Arminda, 10-50, Jardim Brasil, 17011-160 Bauru, SP, Brazil","Department of Botany, National Museums of Kenya, P. O. Box 40658-00100, Nairobi, Kenya","Environmental Studies Department, University of California, Santa Cruz, CA 95064, U.S.A.","Department of Forest Management, Faculty of Forestry, Universiti Putra Malaysia, Serdang, Selangor, Malaysia","Institute of Zoology, Zoological Society of London, Regents Park, NW1 4RY London, United Kingdom","Institut de Recherche pour le Developpement (IRD), 93143 Bondy Cedex, France","","","CIBIO, Centro de Investigao em Biodiversidade e Recursos\nGenticos, Universidade do Porto,\nRua Padre Armando Quintas,\n4485-661 Vairo, Portugal","Laboratrio de Isoptera, Museu de Zoologia da Universidade de So Paulo, Av. Nazar 481, Ipiranga, 04263-000 So Paulo, SP, Brasil.\n(ecancell@usp.br)","Instituto de Biodiversidad CIBIO, Universidad de Alicante, 03080 Alicante, Spain","","","","Department of Biology, Research Building 223,University of Missouri-St. Louis, One University Boulevard,\nSt. Louis, MO 63121-4499","Escuela de Biologa, Universidad de Costa Rica, 11501-2060, San Jos, Costa Rica","Diviso de Entomologia, Museu de Zoologia da Universidade de So Paulo, Avenida Nazar, 481, Ipiranga, So Paulo, SP CEP 04263-000, Brazil","","Department of Animal & Environmental Biology, Faculty of Life Science, University of Benin, Benin City, Edo State, Nigeria","","Department of Natural Resources Environment, the Arts and Sport, PO Box 496,\nPalmerston, NT 0831, Australia.","","Instituto Nacional de Pesquisas da Amaznia","Centre for Functional Ecology, Department of Life Sciences, University of Coimbra, PO Box 3046, 3001-401 Coimbra, Portugal","Noblet Building 115, School of Forest Resources and Environmental Science, Forestry and Wood Products Building, 1400 Townsend Dr.,Houghton, Michigan 49931-1295","Institute for Plant Sciences and Genetics in Agriculture, Robert H. Smith Faculty of Agriculture, Food and Environment, The Hebrew University of Jerusalem, PO Box 12, 76100 Rehovot, Israel","Scarab Research Group, Department of Zoology & Entomology, University of Pretoria, Lynnwood Rd, Pretoria 0002, South Africa","Department of Environmental Science, Policy, and Management, University of California at Berkeley, Berkeley, California 94720, U.S.A.","","Centre of Environmental Biology, Dept. Animal Biology, Faculty of Sciences, Univ. of Lisbon, PT-1749-016 Lisboa, Portugal","Departamento de Biologia, Instituto de Cincias Biolgicas, Universidade de Pernambuco, Pernambuco 50100-010, Brazil.","Dpto. de Recursos Naturales. Facultad de Ciencias Exactas y Naturales. Universidad Nacional de La Pampa. Uruguay 151, LB6300CLB, Santa Rosa, La Pampa","Programa de Ps-Graduao em Ecologia, Universidade Federal de Santa Catarina, Rua Joo Pio Duarte Silva, Crrego Grande, 88040-900, Florianpolis, SC, Brasil.","National Aviary (USA), Allegheny Commons West, Pittsburgh, PA 15212","Fauna & Flora InternationalPhilippines Programme, c/o\nThe International Institute of Rural Reconstruction, Y.C. James Yen Centre,\nSilang, Cavite 4118, Philippines","Integrative Biology Department, University of California at Berkeley, 1005 Valley Life Sciences Building, Berkeley, CA\n94720, USA","Departamento de Ecoloxa e Bioloxa Animal, Universidade de Vigo, EUET Forestal, Campus Universitario, 36005 Pontevedra, Spain","","Universidad Nacional Experimental de Guayana (UNEG), Venezuela. Address: Apartado postal 8050. Ciudad Guayana, estado Bolvar, Venezuela","","","Departamento de Biologia Animal, Instituto de Biologia,\nUniversidade Estadual de Campinas, P. O. Box 6109,\nCampinas, Sao Paulo 13083-970, Brazil","A.P. Goossens Herbarium, School of Environmental Sciences and Development, North-West University, Private Bag X 6001, Potchefstroom\n2520, South Africa","","COT (Tuscan Ornithological Society), cp 470, 57100 Livorno, Italy","Association Kwata Study and Conservation of French Guianan Wildlife, BP 672,\n97335 Cayenne cedex, French Guiana, France","Forestry Research Institute of Ghana, P. O. Box 63, Fumesua, Kumasi, Ghana","Department of Animal & Environmental Biology, Faculty of Life Science, University of Benin, Benin City, Edo State, Nigeria","Universidade de So Paulo, Ribeiro Preto SP, Brazil","","","","","","","","","CSIRO Sustainable Ecosystems, Tropical Ecosystems Research Centre, PMB 44 Winnellie, NT 0822, Australia","","J.W. Goethe University, Institute of Ecology, Evolution and Diversity, Siesmayerstrae 70, 60323 Frankfurt am Main, Germany","","","Coordenac ao de Pesquisas em Ecologia, Instituto Nacional de Pesquisas da Amazonia (INPA), CP 478, 69011-970,\nManaus, AM, Brazil","","","PO Box 148, Christmas Island, WA, 6798.","Watana Sakchoowong, Forest Entomology and Microbiology Group, National Parks, Wildlife and Plant Conservation Department, 60 Praholyothin Road, Chatuchak, Bangkok 10900, Thailand","Biology Department, Lawrence University, P.O. Box 599, Appleton, WI 54911, USA\nDepartment of Zoology, The Field Museum, 1400 S. Lakeshore Drive, Chicago, IL 60605, USA","Department of Forest Biology and Ecosystems Management, Faculty of Forestry and Nature Conservation, Makerere University, P.O. Box 7062,\nKampala, Uganda","","Vietnam-Russian Tropical\nCenter, Nguyen Van Huyen Street, Nghia\nDo, Cau Giay, Hanoi, Vietnam","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","Appl Ecol Serv Inc, 21938 Mushtown Rd, Prior Lake, MN 55372 USA","","","","","","","","","","","","","","","","","","","The Wilderness & Wildlife Conservation Trust, Sri Lanka","School of Marine and Tropical Biology, James Cook University","Centro de Investigaciones en Ecosistemas, Universidad Nacional Autonoma de Mexico (UNAM), Antigua carretera a Patzcuaro No.8701, Ex Hacienda de San Jose de\nla Huerta, Morelia 58190, Michoacan, Mexico","","","Silliman University-Angelo King Center for Research and EnvironmentalManagement (SUAKCREM),Marine Laboratory, Silliman University,\nDumaguete City, Philippines 6200","School of Biological and Chemical Sciences, Queen Mary, University of London, London E1 4NS, United Kingdom","Department of Biological Sciences, Florida International University, Miami, FL, USA","Laboratory of Mammal Ecology, Departamento de Biologia, Universidade Federal de Santa\nMaria, Camobi, Santa Maria, RS, 97.110-970, Brazil","Department of Biological Sciences, National University of Singapore, 14 Science Drive 4, Singapore 117543, Republic of Singapore","College of Life Sciences, Zhejiang University, and Key Laboratory of Conservation Biology for Endangered Wildlife, Ministry of Education, Hangzhou, China","Zoological Institute, University of Bern, Baltzerstrasse 6, 3012 Bern, Switzerland","Departament de Ciencies Ambientals, Universitat de Girona, Campus de Montilivi, E-17071 Girona, Catalonia, Spain","Institute for Tropical Biology and Conservation, Universiti Malaysia Sabah, Locked Bag 2073, 88999 Kota Kinabalu, Malaysia","Departamento de Ciencias Agrarias, CITA-A, Universidade dos Acores, Acores, Portugal","Faculty of Agricultural Sciences and Technologies, European University of Lefke, Gemikonagi,\nLefke, Guzelyurt Mersin 10, Cyprus","Department of Ecological Modelling, Helmholtz Centre for Environmental Research (UFZ), Permoser Str. 15, 04318 Leipzig, Germany","Institute for Tropical Ecosystem Studies, University of Puerto Rico, P.O. Box 21910, San Juan, PR 00931-1910, USA","Centre for Ecosystem Diversity and Dynamics, Department of Environmental and Aquatic Sciences, Curtin University of Technology, Perth, WA 6845, Australia","School of Biological Sciences, Universiti Sains Malaysia, 11800 USM, Pulau Pinang","CSIC-Centro de Edafologa y Biologa Aplicada del Segura, Department of Soil and Water Conservation, Campus de Espinardo, Murcia, Spain","Department of Zoology, University of Cambridge, Downing Street, Cambridge CB2 3EJ, UK","Emmett Interdisciplinary Program in Environment and Resources, Stanford University, Stanford, California, United States of America","Museum fur Naturkunde, Institut fur Systematische Zoologie, Invalidenstr. 43, 10115 Berlin, Germany","Programa de Ps-graduao em Ecologia, Museu de Histria Natural, Universidade Estadual de Campinas (Unicamp), CP 6109, 13084-971, Campinas, SP, Brazil","The James Hutton Institute, Invergowrie Dundee DD2 5DA","School of Biological Sciences, Universiti Sains Malaysia, 11800 USM Pulau Pinang, Malaysia","Panthera","","School of Biological Sciences, University of East Anglia, Norwich, Norfolk NR47TJ UK","","","","","","","","","","","","","","","","","","","Department of Environmental Sciences, Faculty of Environmental Studies,\nUniversiti Putra Malaysia, 43400 UPM, Serdang, Selangor, Malaysia","Louisiana State Univ, Museum Nat Sci, 119 Foster Hall, Baton Rouge, LA 70803 USA","Univ Cambridge, Dept Zool, Downing St, Cambridge CB2 3EJ, England","National Museums of Kenya, Ornithology Department, PO Box 40658, 00100 Nairobi, Kenya","CSIR, Natural\nResources and the Environment, P.O. Box 320, Stellenbosch,\n7599 South Africa","Department of Conservation Ecology and Entomol-\nogy, Stellenbosch University, Private Bag X1, Matieland 7602, South Africa.","Terrestrial Ecology Unit,\nGhent Univ., K.L. Ledeganckstraat 35, BE9000 Ghent, Belgium.","Plant Systematics and Vegetation Ecology, Biocentre Klein Flottbek, University of Hamburg, Ohnhorststr. 18, 22609 Hamburg, Germany","IRD, CBGP (UMR IRD/INRA/CIRAD/MontpellierSupAgro), Campus de Bel-Air, BP 1386, Dakar, CP 18524, Senegal","Royal Museum for Central Africa, Leuvensesteenweg 13, B-3080 Tervuren","Herpetology Section\nNational Museums of Kenya\nMuseum Hill Road\nP. O. Box 40658-00100\nNAIROBI, KENYA","","Graduate School of Science, Kyoto University, Oiwake-cho, Kitashirakawa, Sakyo-ku,\n606-8502 Kyoto City, Kyoto, Japan","BirdLife International Africa Partnership Secretariat, PO Box 3502 00100, Nairobi, Kenya","School of Animal, Plant and Environmental Sciences, University of the Witwatersrand,\nPrivate Bag 3, WITS, 2050 South Africa","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","Coleccin Herpetolgica y Laboratorio de Biologa Reproductiva de Vertebrados, Escuela de Biologa, Grupo de Estudios en Biodiversidad, Universidad Industrial de Santander, Bucaramanga, Colombia.","Universidad del Valle, Departamento de Biologia: Apartado Areo 25360, Cali, Colombia.","","Laboratorio de Investigaciones en Abejas LABUN, Departamento de Biologa, Universidad Nacional de Colombia,\nBogot, Carrera 30 N 45-03","","Calle 13 # 100-00, Edificio 320, Oficina 3025, Cali, Colombia","Carrera 70H No. 122 98, Apartamento 101","Cra 15, Cll 12 N, Armenia, Quindo","Laboratorio de Herpetologa, Pontificia Universidad Javeriana, Bogot, Colombia","Facultad de Educacin y Ciencias, Departamento de Biologa, Universidad de \nSucre, Sincelejo Colombia.","Instituto de Ciencias Naturales, Universidad Nacional de Colombia, Apartado 7945, Bogot, Colombia","Rua do Mato, travessa 14, n 321","Calle 67 # 53-108, Medelln, Colombia","","Agroecology, Department of Crop Sciences, Georg-August University, Griesbachstrae 6, 37077 Gottingen,\nGermany, and Department of Entomology, Cornell University, 4142 Comstock Hall, Ithaca, NY 14853. USA.","Laboratorio de Sistematica y Biogeografa, Coleccion de Entomologa /Escuela de\nBiologa, Universidad Industrial de Santander, Bucaramanga, Santander, Colombia","Laboratorio de Zoologia y Ecologia Acuatica - LAZOEA, Universidad de Los Andes, Bogota, Colombia","School of Plant Biology\nThe University of Western Australia (M090)\n35 Stirling Highway\nCRAWLEY WA 6009\nAustralia","","","","263 Townsend Hall\nDepartment of Entomology and Wildlife Ecology\nUniversity of Delaware\nNewark, DE 19716","","","","","","","","Biodiversity, Evolution and Ecology of Plants (BEE)\nBiocenter Klein Flottbek and Botanical Garden\nUniversity of Hamburg\nOhnhorststr. 18\n22609 Hamburg, Germany","","Dep/ aj\nEcology and Tropical Biology, Biozcntiuin. Am liiibluml. D-97074 Wuerzhiirg. Germany","School of Geography and Environment Sciences, University of Tasmania, GPO Box 252-78, Hobart, Tasmania 7001, Australia","CIFOR, PO Box 6596, JKPWB Jakarta 10065, Indonesia","","","Vietnam-Russian Tropical Center, Hanoi, Vietnam","Museum Natl Hist Nat, USM 601, Dept Systemat & Evolut, Lab Mammiferes & Oiseaux, 57 Rue Cuvier,CP51, F-75005 Paris, France","Northern Populations and Ecosystems Group\nArctic and Marine Biology\nUniversity of Troms","","","","","Jefe de Grupo Forestal - Silvopastoril EEA Santa Cruz - UNPA - CONICET\nDireccin postal: CC 332, (CP 9400), Ro Gallegos, Santa Cruz, ARGENTINA","Landcare Research, Private Bag 1930, Dunedin 9054, New Zealand","","","Centre for Nature Conservation (Department I), University of Gottingen, Von-Siebold-Strae","Research Institute for Humanity and Nature, Kyoto 603-8047, Japan","Institute of Biological Sciences, University of Malaya, 50603 Kuala Lumpur, Malaysia","Centre de cooperation internationale en recherche agronomique pour le developpement, Departement systemes\nbiologiques, Montpellier, France\nCentre international de recherche-developpement sur lelevage en zone subhumide, BP454, Bobo-Dioulasso, Burkina Faso","","","Biodiversity Research Group, Centre for the Environment, University of Oxford, South Parks\nRoad, Oxford OX1 3QY, United Kingdom","El Colegio de la Frontera Sur, Unidad Chetumal, Av. Centenario Km 5.5, A. P. 424, Chetumal, Quintana Roo 77000, Mexico","Biodiversity Research Centre, Department of Zoology, University of British Columbia,\n6270 University Boulevard, Vancouver, British Columbia V6T 1Z4, Canada","IDEA Consultants, Inc.\nOKINAWA BRANCH OFFICE\nDepartment of Research and Study on Subtropical Environments\n2-6-19 Aja, Naha city, Okinawa 900-0003, Japan","1Dipartimento di Biologia, Universit degli Studi di Milano, V. Celoria 26, Milano 20133, Italy","Department of Animal Ecology and Tropical Biology \nBiocenter \nUniversity of Wrzburg \nAm Hubland \n97074 Wrzburg \nGermany","Science & Technology Branch, Environment Canada, 1125 Colonel By Drive (Raven Road),\nCarleton University, Ottawa, Ontario K1A 0H3, Canada","Museu Paraense Emlio\nGoeldi, Coordenacao de Zoologia, Belem, Para , Brazil","Parks & Countryside Service, Bracknell Forest Council, Time Square, Market Street, Bracknell, RG12 1JD","Dillon Consulting Limited, 137 Chain Lake Drive, Halifax, NS, B3S 1B3, Canada","Univ Quebec, Dept Biol Chim & Geog, Rimouski, PQ G5L 3A1, Canada","Department of Natural Resource Sciences, McGill University, Macdonald Campus, 21,111\nLakeshore Road, Sainte-Anne-de-Bellevue, Quebec, Canada H9X 3V9","Department of Ecology and Genetics, Aarhus University, Ny Munkegade 114, Building 1540,\nDK-8000 Aarhus C, Denmark.","Umea Univ, Dept Ecol & Environm Sci, SE-90187 Umea, Sweden","Sweedish University of Agricultural Sciences","Yukon Department of Environment, P.O. Box 2703, Whitehorse, Yukon Y1A 2C6, Canada","Centre de foresterie des Laurentides \n1055, rue du P.E.P.S., Case postale 10380 \nQubec (Qubec) Canada G1V 4C7","","School of Biological Sciences, Lake Superior State University, Sault Sainte Marie, MI 49783.","Stockholm Univ, Dept Bot, SE-10691 Stockholm, Sweden","University of Helsinki\nFaculty of Biological and Environmental Sciences\nUrban Ecology Research Group\nViikinkaari 2a, P.O. Box 65\nFI-00014 Helsinki, Finland","Michigan State Univ, Dept Fisheries & Wildlife, E Lansing, MI 48824 USA","","Institute of Botany,Chinese Academy of Sciences,Bijing 100093","Department of Ecology and Ecological Engineering, College of Resources and Environmental Science, China Agricultural University, Beijing 100193, China","Liaoning Key Laboratory of Soil Environmental Quality and Agro-product Safety, Institute of Applied Ecology, Chinese Academy of Science, Shenyang 110016, China","Beijing Urban Ecosystem Research Station, State Key Laboratory of Urban and Regional Ecology,\nResearch Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China","College of Agricultural Resources and Environmental Sciences, China\nAgricultural University, Beijing 100193, China","School of Biological Sciences, The University of\nHong, 3N-04, Kadoorie Biological Sciences Building, The University of Hong Kong,\nPokfulam Road, Hong Kong SAR, China"],"Contributor_s_URL":["NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA","NA"],"Compiler_s_comments":["Only site-level diversity data available from paper. I have not attempted to contact the author.\nData taken from paper, so no permission necessary.","AD1 13/01/2014 Blocking information not available.","AD1 21/11/2013 Split into two studies (all inverts sampled, only specific plants sampled), updated max linear distance and habitat patch area.","CM1 08/07/2013 updated predominant habitat and source for predominant habitat. AD1 21/11/2013 No block structure, habitat patch, maximum linear distance and fragmentation layout updated, species indication and target spp added.","Only data from 2000 entered. Data from 1997-2000 available.\n\nCM1 08/07/2013 updated predominant habitat and source for predominant habitat. AD1 21/11/2013 updated max linear distance, fragmentation layout, species indication, study target.","Beetles nest in flowers over night. The flowers were collected and beetles extracted. Flowers therefore act as a baited trap.","AD1 21/11/2013 Updated fragmentation layour, sampling target and taxon status, blocks are not needed. \nAD1 21/05/2014 Added max linear distance","Cluster sites. Coordinates given as one of the sites (so that the habitat type is correct), but coordinate precision is large (12km) to indicate that the coordinates were just one set of many potential sites. Abundance measurements are summed across all sites within a cluster (i.e., total individuals rather than mean individuals). Sample effort is summed across sites (1 hour per each of the 5 sites in cluster = 5 hours total). Max linear distance was similarly calculated.","AD1 21/11/2013 Updated fragmentation layout and permissions\nAD1 03/01/2014 Updated sampling target and taxon status","Unsure of sampling year.\nAD1 21/11/2013 Updated fragmentation layout, use-intensity is truly unknown\nAD1 15/01/2014 Changed predominant habitat for orchards to plantation forest","This form is extended to allow for 124 sites.\nAdded habitat types from Google earth.\nAD1 21/11/2013 Updated study target, taxon status, assessed that some habitat types and fragmentation layouts are cannot decide, blocks not required, updated max. linear distance.","This data set is part of the Fifth-framework EU-project EASY (see www.ncp.wur.nl/UK/research/EASY/). The two studies within this source have the same sites but different sampling methods.\n\nAD1 21/11/2013 Updated fragmentation layout, maximum linear distance, patch area, taxon indication, study target, permissions","Data from 2003 and 2004 are different studies as they were sampled for different amounts of time and in different times of year.\n\nAD1 21/11/2013 Updated permissions, fragmentation layout, site area, sampling target, taxon status, no need for blocks.\n\nSH1 21/05/2014 Checked urban habitats for consistency with new definitions. Paper states that some urban parks contain \"remnant fragments that have been largely unchanged by human activity\" and gives % of park that is natural (Appendix 1). Any park that has more than 50% natural I have changed from Urban to Primary. As the authors state that all parks are impacted by humans and have alien species etc. I have assigned all parks classified as Primary as having a Light use intensity. The parks which were changed are: Hawk_hill, Mt.Davidson, Twin Peaks, Glen Canyon, Bernal Hill, Corona Heights, Duncan/Castro, and Tank Hill. Also the authors state that two large wild parks outside of the city limits were also sampled, San Bruno and Sweeny Ridge, so have changed these from Urban to Primary with a Minimal use intensity.","AD1 21/11/2013 Pseudo-replicated blocks needs addressing: abundances need to be summed and central coordinates taken.","AD1 21/11/2013 Updated permissions, corrected diversity metric, fragmentation layout, sampling target, taxon status, no need for blocks\n\nAD1 21/05/2014 Changed land-use type to young secondary vegetation, in accordance with new land-use intensity matrix","Data from 2000 and 2005 use slightly different methodologies (2005 data measures number of visitors to H. commosa, 2000 data counts number of individuals within patch).\nData from 2000 and 2005 use slightly different methodologies not apparent in this form - in 2000, 15 influorescences within a fixed plot were randomly chosen for flower-visitor observations. In 2005, all influorescences within a fixed plot were observed.\n\n2013-07-07 CM1 updated predomniant habitat and source for predominant habitat\n\nAD1 22/11/2013 Updated permissions, fragmentation layout, site area, added information on distance to nearest fragment, taxon status, study target, no blocks needed","Transect lengths differed between sites. Abundances reported are therefore calculated as the number of individuals per 100m of transect. Abundance data will need to be adjusted for different sampling efforts. Some sites appeared to have more than one abundance column - these were summed.\n\n2013-06-11 LH1 Taxa Inserted spaces between generic and specific names\n\n2013-07-07 CM1 updated predominant habitat and source for predominant habitat\n\nAD1 22/11/2013 Updated permissions, taxon status, study target, max linear sampling, blank abundance values, fragmentation layout. Checked coordinates - they look fine.","Data collected along a transect by hand-netting and pan trapping\n\nAD1 22/11/2013 Updated permissions, added habitat, use intensity, fragmentation layout, study target, species status. Blocks not needed.","AD1 22/11/2013 Updated permissions, max. linear distance, patch area and fragmentation layout.","Note: original data files had errors (2003 was meant to be 2005, T\u00e5ngarne E was meant to be T\u00e5ngarne O). These have been corrected before data was input into database.\n\nThere are more than 100 species so there are two excel sheets for this source (ADP_1_Franzen2008.xlsx and ADP_1_Franzen2008_2.xlsx).\n\n08-07-2013 CM1 updated predominant habitat and source for predominant habitat.\n\nAD1 22/11/2013 Updated permissions, study target, taxon status, site area and fragmentation layout","AD1 22/11/2013 Updated permissions, fragmentation layout, max linear distance, no blocks needed.\n\nAD1 21/05/2014 Altered habitat type according to altitude (sites below 600m tend to be agriculture, sites above tend to be pasture).","08-07-2013 CM1 updated predominant habitat, source for predominant habitat, and years since fragmentation or conversion for Study_1\n\nAD1 26/11/2013 Updated permissions, max. linear extent, study target, taxon status, fragmentation layout, no blocks needed.","2013-07-07 CM1 updated predominant habitat, source for predominant habitat, and years since fragmentation or conversion.\n\nAD1 07/01/2014 updated permissions, fragmentation layout, sampling target, taxon status, maximum linear extent sampled, habitat patch area.","AD1 13/01/2014 No blocks required","AD1 26/11/2013 Updated permissions, max. linear distance, site area, additional threats, sampling target, taxon status, fragmentation layout, added blocking structure","AD1 07/01/2014 Updated permissions, study target, taxon status, max linear distance, fragmentation layout. No blocks required.","Information on management practices are available from his Thesis.\n\nAD1 26/11/2013 Updated permissions, sampling target, taxon status, fragmentation layout, blocks not needed","AD1 06/01/2014 Updated sampling target, taxon status.\nAD1 02/05/2014 Added Habitat as described in source.","AD1 06/01/2014 Updated fragmentation layout, sampling target, taxon status. No blocks needed. Study is coastal so sites outside ecoregion or country area may not be unexpected.","Only data from the late season are used as these represent surviving colonies at the end of colony establishment.\n\nAD1 06/01/2014 Updated permissions status, fragmentation layout, site area, sampling target, taxon status. Blocks are not needed.\n\nAD1 21/05/2014 Updated predominant habitat according to new land-use intensity matrix (field margin with over 100m linear extent becomes young secondary)","Same site, different years. Only used data from the same time of year.\n\nAD1 06/01/2014 Updated insightly permissions e-mail id, removed blocks (they were initially given all one block as there is no blocking structure in this study). No gradient and same coordinates is correct - this is a multi-year study.\nAD1 02/05/2014 Added Habitat as described in source.","AD1 06/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status. No blocks needed.\nAD1 02/05/2014 Added habitat as described by source","Grid refs are approximate - there were 31 transects but only 11 distinguishable locations. Will need to approach author again for abundance data.\n\n08-07-2013 CM1 updated predominant habitat and source for predominant habitat.\n\nAD1 06/01/2014 Updated permissions status, fragmentation layout, sampling target, taxon status. Sites are outside ecoregion and country shape file, most likely because they are coastal sites.","Three different survey methods were used (Pan traps, sweep netting and hand searching) to give the most comprehensive view of the bee communities. Data are summed for all traps combined but sampling effort was equal for each site.\n\nAD1 06/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status, max. linear extent. No blocks required.","Data collected by a project student supervised by Mick Hanley.\n\n2013-06-12 LH1 Taxa Removed numeric prefixes from specific names e.g. Psyllobora 22 - punctata becomes Psyllobora vigintiduopunctata\n\nAD1 07/01/2014 Updated permissions status, fragmentation layout, sampling target, taxon status. Blocks not required.\nAD1 05/01/2014 Changed predominant habitat type for vineyards to Plantation forest\nAD1 21/05/2014 Changed predominant habitat from cropland to young secondary vegetation in accordance with updated land use matrix","AD1 13/01/2014 No blocks required\nAD1 02/05/2014 Added habitat as described in source\nAD1 21/05/2014 Changed habitat type to secondary vegetation in accordance with updated land use matrix","Sampling efforts differ so this will need to be transformed into encounter rates by dividing the abundance by the sampling efforts.\n\nAD1 07/01/2014 Updated permissions status, sampling target, taxon status. No blocks required (already split into two separate studies for east and west USA, in accordance with the paper)","2013-07-07 CM1 updated predominant habitat and source for predominant habitat","AD1 07/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status, max linear distance.","Broad taxonomic groupings only\n\n08-07-2013 CM1 updated predominant habitat and source for predominant habitat.\n\nAD1 07/01/2014 Updated permissions status and insightly e-mail, diversity metric, fragmentation layout, sampling target, maximum linear distance, taxon status.\n\nAD1 13/01/2014 Added blocks","Only access to total number of bees\n\n2013-07-07 CM1 updated predominant habitat and source for predominant habitat, sampling target, taxon status. No blocks needed.\n\nData to species level available as cluster sites only.\n\nAD1 07/01/2014 Updated permissions, fragementation layout, habitat as described in source, maximum linear distance.\nAD1 15/01/2014 Updated predominant habitat to plantation forest","Data on floral numbers, not percentages, recorded.\n\nAD1 07/01/2014 Updated permissions, fragmentation layout, maximum linear distance,","","08-07-2013 CM1 updated predominant habitat and source for predominant habitat.\n\nAD1 07/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status, max linear distance. No blocks required.","AD1 07/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status, max linear distance. No blocks needed.","AD1 07/01/2014 Updated permissions. No blocks required. Some duplicated taxon names due to certain and uncertain identifications of speciments.","40 sites were sampled but some of these were repeated twice within the year (before and after mowing) - there are only 29 unique locations.\n\nAD1 07/01/2014 Updated max linear distance, fragmentation layout, habitat patch area, sampling target, taxon status, \n\nAD1 21/05/2014 Adjusted so that plants are a separate study. Flower abundances changed to occurrences (flower number is not a helpful measure of abundance unless you are relating it to pollinators).","AD1 08/01/2014 Only tree nesting species are included in this dataset as the data are available from a table published in the paper, although there is one more species with low nest density also found (it nests underground and the data are only available from a figure).","","Data taken from paper\n\nAD1 07/01/2014 Updated permissions e-mail link, permissions status, sampling target, taxon status, fragmentation layout, predominant habitat. Cannot determine use intensity for cropland sites. Removed data for cropland sites as these are actually measurements in a 1km radius surrounding 8 of the secondary vegetation sites already in the spreadsheet.","Road verges have been classed as 'Cannot decide'. Although they are urban structures, they are only a minor proportion of the agricultural landscape.\n\n08-07-2013 CM1 updated predominant habitat, source for predominant habitat, and years since fragmentation or conversion.\n\nAD1 07/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status. No blocks required.","AD1 07/01/2014 Updated permissions, fragmentation layout, sampling target, taxon status, max linear distance. No blocks required.","Originally contacted by Helen Phillips and data formatted by Tamera Husseini. Cluster sites only so coordinates for each site are given as a single site from the correct land-use class, with wide estimates for coordinate precision. Diversity measurement, sampling effort and max linear distance are given as the total per cluster.","AD1 07/01/2014 Updated insightly permission URL.\nAD1 21/05/2014 Changed secondary vegetation to cannot decide (we can't know if it's primary or not)","AD1 07/01/2014 Cannot decide land-use intensity.","Data from paper, no permission needed. Flower visiting insects and plants are separated into two different studies - although the same length transect was used for both, the sampling intensity (time) differed. Samples were taken along forest edges which bordered agricultural and suburban land-uses. In many of the fragments adjacent to human-use areas, there was a high abundance of exotic and invasive plant species, changing the nature of the ecoystem; these were classified as lightly-used primary vegetation. Areas which did not suffer so badly from plant invasions were classified as minimal use. Abundance of plants was assessed by mean abundance of floral units.","\"The title of the journal is \"\"Environmental Entomology\"\"\"\nAccess ID [310]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSC1 18/2/2014 Corected Diversity metric to \"effort-corrected abundance\"\nSC1 18/2/2014 Checked block structure and it is ok.","\"The title of the journal is \"\"Neotropical Entomology\"\"\"\nAccess ID [305]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSC1 18/2/2014 Removed habitat patch size value as that was the old site area value.\nSC1 18/2/2014 Changed \"Sampled-end date\" from 2000/8 to 2003/8 as described in the journal article \nSH1 21/05/2014 Changed predominant habitat in LU from Urban to Primary forest as article indicates that the site is within a remnant patch of degraded rain forest. As author mentions that LU is degraded and aerial photographs show some human use, possible areas of clearing, have judged use intensity to be Light.","\"See \"\"Basset Supp Info\"\" for detailed abundance recordings\"\nAccess ID [308]\n12/11/2013 LH1 Changed empty site by species cells to zeroes\n\n27/11/2013 SH1 Checked blocking structure and no blocks present. Added linear extent and checked patch size.","Access ID [307]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSH1 27/11/2013 Changed diversity metric from abundance to 'effort-corrected abundance' as this more accurately reflects the sampling methodology. Checked taxon status and not reported in paper. Added linear extent. In this study the linear extent refers to the trap itself - I looked up the trap online and estimated size from photos. Added patch size (entered as -1 as part of a large city). Blocking structure is correct - no blocks present.","Access ID [311]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSH1 27/11/2013 Added species status 'Not reported'. Added linear extent (350m which is length of transect). Changed use intensity 'cannot decide' for cattle pastures to 'light'. The paper reports that the natural vegetation in the cattle pastures had been replaced therefore, was able to judge that should be at least light, but does not report whether pesticides and herbicides are used, therefore could not judge if intense use. As the primary forests sites are on protected land I added minimal use intensity for these sites. The use intensity of other habitats is not posssible to ascertain from the paper. Added patch size for primary forest sites (-1) as large reserve but this info is not given for the other sites.","\"The title of the journal from which the paper was extracted is \"\"Journal of Applied Biosciences\"\"\"\nAccess ID [309]\n\n2013-07-17 LH1 Removed duplicated generic names\n\n2015-04-28 SH1 transferred PDF and excel data into new (v7) forms. Data was originally entered as cluster sites - have removed this structure by taking the coordinates of the 2nd of the three sites in each cluster. Have plotted sites and have added distance between points to transect length to estimate location accuracy.","\"See \"\"Filgueiras Supp Info\"\" in PDF file (word format) for abundance measures of all species sampled\"\nAccess ID [312]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSH1 27/11/2013 Checked blocking structure and is correct. Added 'not reported' for taxon status. Added linear extent measure and checked habitat patch area.","\"See Appendix or \"\"Slade & Mann Supplementary Data\"\" in PDF file, for the actual data.\"\nAccess ID [303]\n\n2013-07-17 LH1 Removed duplicated generic names\n\nSH1 18/11/2013 into V7 forms. Added linear extent. Checked blocking structure (not present) and patch size (not given).","","","","","","","","Density of snails and slugs are not included. Coordinates (Longtiude) for Tukino site entered here is obtained from Tukino native site from CC1_2012_Barratt as the one reported in Barratt et al (2005) i.e. 175' 74E is above 60 minutes.","Field data were entered onto a spreadsheet with cover abundance scores converted to the mid-points of their respective cover classes.","The pasture matrix has been defined to be under 'Minimal use' as no grazing or fertilizer input has been reported.","Sampling effort (3 cores per site) listed as 3 catches per site","Sampling effort (3 cores per site) listed as 3 catches per site. Maximum linear extent for macrofauna is 3 x 15.5 = 46.5 cm; mesofauna is 5 x 5 = 25 cm and microfauna is 5 x 2.5 = 12.5 cm.","Cultivated tussock are classified as Mature Secondary Vegetation as no grazing was reported. Site description in reported in an earlier paper, Barratt et al. (2005) 'The locations have been selected on the basis of their relatively undisturbed soils (no history of cultivation) and \"naturalness\" of the vegetation, but all sites have almost certainly been grazed and possibly burnt at some time in their post-human history.' Barratt et al. (2005) Biodiversity of indigenous tussock grassland sites in Otago, Canterbury and the central North Island of New Zealand I. The macro-invertebrate fauna.","","Data from branch bagging from two other seasons (spring and autumn) are also used (site_study_2) although not reported in the paper. Habitat description was obtained under author's recommendation from Freeman, C. & Buck, O. (2003) Development of an ecological mapping methodology for urban areas in New Zealand. Landscape and Urban Planning 63 (2003), 161-173. 6 non-integer values for abundance has been rounded up to nearest highest integer (Abund_Study_1).","The traps were placed for 10 weeks i.e. 7 x 10 = 70 days for sampling effort. The pasture matrix has been defined to be under 'Minimal use' as no grazing or fertilizer input has been reported.","Crop sites are categorized as pasture due to high stock density. Unpublished article but permission has been given and data is relevant.","Habitat description was obtained under author's recommendation from Freeman, C. & Buck, O. (2003) Development of an ecological mapping methodology for urban areas in New Zealand. Landscape and Urban Planning 63 (2003), 161-173. Citation for data also from: \nWaite, E.M. (2012) The role of large, isolated trees in supporting urban biodiversity. Unpublished PhD thesis, University of Otago, New Zealand.","Non-burned plots: 1,6,7. Spring-burned plots: 3, 4, 9. Summer-burned plots: 2, 5, 8. Samples from 1999 were omitted.","Land use intensity was accessed using information in Supplementary information, according to PREDICTS guidelines","SC1 20/1/2014 Corrected diversity metric","Individual coordinates for each site were unavailable as all sites were on private land.\nNot blocked\n\nSC1 20/1/2014 Added sampled effort\nSC1 20/1/2014 Added maximun linear extent sampled","Not blocked\n12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSC1 20/1/2014 Added maximum linear extent","Not blocked\nSC1 20/1/2014 Added maximum linear extent\nSC1 20/1/2014 Changed sampled effort","Not blocked\nSC1 Added Maximum linear extent","Not blocked\nSC1 21/01/2014 Removed habitat patch area values","Not blocked\nSC1 21/1/2014 Curation. Added Maximum linear extent.","Not blocked\nSC1 21/1/2014 Added Habitat patch area. \nSC1 21/1/2014 Added maximum linear extent\nSC1 21/1/2014 No blocking structure","Not blocked\nSC1 21/1/2014 Curation. Added maximum linear extent.\nSC1 21/1/2014 Added Fragmentation layout","Not blocked\n12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSC1 21/1/2014 Added habitat patch area\nSC1 21/1/2014 Added Maximum linear extent (it couldn't be calculated exactly as the distance between the transect is not known)","Not blocked\nSC1 22/1/2014 Added Maximum linear extent\nSC1 22/1/2014 Added Species status (native or alien)","Not blocked\n12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSC1 27/01/2014 Added sampled effort unit\nSC1 27/01/2014 Couldn't calculate maximun linear extent as the distance between the transects is not specified","Data provided by Ishitani consists of four datasets collected in 2001 and 2002 for carabid beetles and butterflies. Only the 2001 carabid dataset is published, but all datasets use the sites outlined in this publication and similar sampling techniques.\n\nCoordinates provided were completely wrong. I instead superimposed the map provided onto Hiroshima city (with Google Earth, screw ArcGis!) and took the coordinates from there.\n\nI simply followed the authors descriptions of the sites when determining the predominant habitat:\nMotoujina: secondary forest in an urban environment -- urban minimal use\nTakadayama: secondary forest ina suburban environemnt -- secondary forest intense use\nGogenzan: secondary forest in a rural area -- seconday forest minimal use\n\nSC1 27/1/2014 Changed the data use permission to Full permission granted \nSC1 27/1/2014 Changed Abundancy study data for carabids in the excel as it reported the wronf data set (it was the data from 2002 and not the sum of 2001 and 2002).\nSC1 27/1/2014 Changed abundancey metric unit\nSC1 27/1/2014 Maximun linear extent and Habitat patch are could not be determined\n\nSH1 28/05/2014 Changed predom habitat and use intensity as per new definitions, \nMotoujina: secondary forest in an urban environment -- urban light use (small patch of green within dense urban area)\nTakadayama: secondary forest ina suburban environemnt -- urban minimal use (large patch of green within less dense urban area)\nGogenzan: secondary forest in a rural area -- seconday forest light use (part of continuous secondary forest extending away from town limits, but still close to urban and author mentions used for hiking and recreation, therefore light use)","Extraurban sites are deemed 'Primary forest -- minimal use'. Urban sites where put into two intensity categories based on whether they come from a large park or a garden. An 'F' stat was available which seems to be either and both a proxy for coverage of the moss/liverwort. I opted not to use it as the categories (1-5) strike me as quite arbritrary also for one site there are no F stats. \n\nOn 27/05/2013 I received the following information on 'rural' sites:\n\"AC: is a natural primary forest, no use by humans\nCA: is a natural primary forest with some recent plantation, some use by humans it is a walk in Capri island\nVMR,VPG, VCE: a mix of natural primary forest and recent plantation in a nature reservoir (Parco Nazionale del Vesuvio) http://www.parconazionaledelvesuvio.it/\nOT: is a natural primary forest, some use by humans for wood from under storey and old trees\nAM: is a natural primary forest, some use by humans for wood from under storey and old trees\nCM: is a natural primary forest, some use by humans for wood from under storey and old trees\nSSW: is a natural primary forest, some use by humans, it is a WWF reservoir.\"\n\nMinimal use is therefore a good approximation for all of these sites\n\nSH: curation - changed Abundance Metric Type to 'Occurrence' (previously was biomass) 14.11.13\nSC1 27/1/2014 Changed Predominant habitat type from Primary forest to Secondary Vegetation\nSC1 27/1/2014 Added Fragmentation Layout","Data was collected from 18 different roundabouts or roundabout-like habitats. Data was collected for grassland plants, trees, grassland hemiptera and tree hemiptera.\n\nEach roundabout had different management regimes. These were only recorded in the article by frequecny of lawn mowing. Here, I've taken this as a proxy for use intensity for trees and grasslands. My categorisation was thus:\n\nintense use: all sites with mowing every 7 or 14 days\nlight use: all sites with mowing every 40 days\nminimal use: all sites with mowing once or less a year\n\nSH: curation - changed site 3, abundance metric type to 'Occurrence' (was entered as 'abundance') 14.11.13\n\nSC1 27/1/2014 Filled in the Abund_Study 2 sheet in the excel form as the values were all wrong\nSC1 27/1/2014 Filled in the Abund_Study 3 sheet in the excel form as the presence/absent values were all wrong\nSC1 27/1/2014 Added Habitat patch area which were provided by the author as: Area of grassland (m2)\nSH1 21/05/2014 Altered Use intensity to match new classification scheme. Two sites (7 & 11) are parkland, the rest are all small patches of vegetation within a town. Therefore have classified all as light use apart from the parkland sites which are minimal.","They split their sites into 3 levels of urabnisation based on the number of roads and surrounding buildings in forested areas. I interpreted these three levels as: Primary Forest (light use), Primary Forest (intense use), Urban (light use).\n\nSc1 28/1/2014 Added Maximun linear extent sampled\nSC1 28/1/2014 Added functional trait reference into \nSC1 28/1/2014 Changed diversity metric from Indivuals/Trap to Individuals\nSC1 28/1/2014 Changed predominant habitat from \"Primary forest\" to \"Secondary vegetation\"\nSC1 28/1/2014 Added Source of predominant habitat and Fragmentation layout\nSC1 28/1/2014 No blocking design structure\n\nSH1 21/05/2014 As per new habitat definitions, have changed Hagenbecks Tierpark from Secondary Intense to Urban with Minimal use (as is in large man-made park within urban area), have changed Bergedorf to Primary forest as web search revealed that the wood has been in place for hundreds of years, however there are many paths through the wood and invasive species are known to be in the wood, so have given use intensity of Light, same for Stadtpark (once a private hunting ground, public park for 100y), changed Klein Borstel from Secondary Intense to Urban Light as is a fairly large manmade park surrounded by urban habitat.","SC1 28/1/2014 Changed diversity metric from Individuals/trap to individuals\nSC1 28/1/2014 Changed Predominant habitat from Primary forest to Secondary Vegetation\nSC1 28/1/2014 Changed fragmentation layout from Well within unfragmented habitat to Within remnant patch..\nSH1 23/05/2014 Changed Urban use intensity to Minimal as site is within large park on the outskirts of the town. Changed the suburban category from 'Urban' to Secondary indeterminate as the site is within a large patch of remnant woodland. Use intensity is light as author states that there is an area of hardstanding within the site, fertiliser has been applied, and weeds are changing the structure.","SH1 27/05/2014 checked urban sites to check if they matched new definitions,have changed the Suburban site from Secondary to Urban.","Ivanescu must be her maiden name.\nShe provided me with supplementary material collected in 2013 on top of that described in the original publication\nSH1 20.05.14 edited urban sites as per new classification scheme. I searched for information on the parks mentioned in the publication online to distinguish the history of the parks (whether or not they are remnant patches of primary, or managed greenspace). See 'Flora' in http://books.google.co.uk/books?id=lUA-LzswzNsC&lpg=PA181&ots=h3xTMxkK3F&dq=Pantelimon%20forest%20bucharest&pg=PA181#v=onepage&q=Pantelimon%20forest%20bucharest&f=false . I changed Titan park from Intense to Light use. According to book and online, Pantelimon forest seems to be remant patch, therefore changed to Primary vegetation, but book mentions that the disturbance is heavy, and ruderal species and alien species are changing the natural structure of the vegetation, therefore have entered as Light use. Same with Pusnicu and Cernica forests. Izvor Park (http://www.videoguide.ro/en/izvor-park-bucharest.html) is a new, large park, but not much green space, more public amenities, therefore have classified Urban Light. IBB (Institute of Biology) has lots of mature trees, but still seems to be a planted garden within an urban location, therefore have classified as Urban Light. Unirea Park is probably Unirii Park, a small manmade park in the town centre, have classified as Urban Light. The coordinates provided by the author for Cismigiu Park do not match up with a park according to Google, and google marks the gardens as within the town centre (which is where the paper verbally places them) so have changed the coordinates to match the location of the gardens in google. Cismigiu Park is a large city-centre park which was produced in 1846 from former fields and wetlands, so have entered as Urban Minimal. Not possible to determine history of Magurele Forest. From aerial photos it appears as if at least some patches of trees appear to have been planted (lines of planting are visible). Natural forest is oak - some images show oak forest whereas others show pine trees. Therefore to be conservative have put as Secondary Mature (the images show a mature forest) with Minimal use intensity. Documents online refer to Stefanesti forest as a protected deciduous oak woodland so have entered as Primary Forest. I cannot find any information on use intensity but as it is refered to as protected, have entered as 'minimal' use. Same with Comana Forest. Calugareni Forest is historical remnant but cannot find any information as to use intensity so have entered as Primary Forest with Cannot decide for use intensity. As above for Peris Forest.","The study was has sites in three habitat types: natural, semi-natural and urban.\n\nI interpreted these into PREDICTS terminology as:\nNatural: primary forest minimal use, well within fragment\nSemi-natural: pasture minimal use, part of a fragmented landscape. based on google earth images, i interpreted that all the sites took place in grassland areas next to plantation forests. i interpreted these as minimal use.\nUrban: urban light use. based on satelltie images i saw a fair amount of greenspace and a lot of suburbia -- even thought they describe it as 'highly' urbanised\n\nSC1 28/1/2014 Added Habitat patch size as they are given by the author (pag. 3345)\nSC1 28/1/2014 Changed Predominant habitat within the site from Primary forest to Mature Secondary vegetation, as indicated by the author.\nSH1 21/05/2014 Changed predominant habitat for sites 29 & 30 (Prophetston State Park) from Pasture to Young Secondary as website says is site of restored prairie grassland. Also same for 27 & 28 as this is restored marshland (restoration began 1994). 24-26 (Purdue U. Hort Park) appears to be large area of mature woodland, unclear if primary or secondary, but is part of protected area so have changed former classification of 'Pasture' to Mature Secondary. Changed sites 16-23 from Pasture to Young secondary as, although they are located within farms, the actual sampling sites are around buildings, driveways, etc","I converted the common names given to scientific names as best I could through google.\n\nI determined the use intensity of each site with Urbanness @ r = 2500m (as 250m is probably too small an area for birds, plus the sampling site is often larger than this). Sites that had a value less than 1/3 of the max were minimal, sites that had a value less than 2/3 of the max were light, the rest were intense.\n\nFor two species (Cossypha caffra, Hirundo rustica) their names were replicated either due to my translating the names or due to duplication in the original dataset (for instance, is there a difference between a Barn Swallow and a Europena Swallow -- not according to wiki!). In this instance, I took the sum of these duplicated species.\n\n12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\n21/11/2013 LH1 Replaced Dom's latin binomials with the common names suppplied by the authors. In the process, I noticed that Dom had incorrectly entered the site x species matrix - there were more sites on the Sites_study_1 tab than there filled columns in Abund_study_1. I reformatted the site x species matrix to correctly match the sites. There are therefore some empty columns in the site x species matrix. The author's datafile 'All_Data_Durescumming.xls' is not internally consistent. The 'site-spp matrix common tab' does not contain rows for sites 101,102,103,105 and 110 yet the tabs for each of these sites shows that species were found. This needs further investigation.\n21/11/2013 The name 'Cape Robin Chat' was duplicated. On looking at Appendix S3.doc (the list of species), it is clear that the first occurrence of 'Cape Robin Chat' should be 'Cape Longclaw'.\n21/11/2013 LH1 Added habitat descriptions.\n26/11/2013 SH1 As LH1 noticed inconsistencies between the data provided by the author and the spreadsheet, I have been back through the data provided by the author and have added data for 5 sites which were previously blank - sites 101,102,103,105 and 110. Within the data for these sites were three species not recorded within any other sites, therefore I added three new species rows in the site by species matrix. Note that neither the species nor the sites appear in the summarised data provided by the author in 'All_Data_Durescumming.xls' - the data is only contained in the tabs for each of the sites. It appears that the summarised datafile was what was used for the paper as these species do not appear in the paper either.\n\nSH1 26/11/2013 Changed fragmentation layout from 'cannot decide' to 'part of remnant patch' for all sites. Looked at blocking structure and is correct - there are no blocks of sampling. Added linear extent value and checked habitat patch size and is correctly entered.\nSH1 28/05/14 Changed predominant habitat from Urban to Primary for all sites as samples were taken within remnant patches of primary. Use intensity was assessed using Google Maps - areas with obvious footpaths, cleared patches etc were classified as Intense use, other areas were assessed as Light use.","Live traps were used to capture both reptiles and mammals -- I've separated the two regardless if they share the same sampling efforts. I'm not sure whether this is a good idea or not.\n\nI used google maps to ascertain the use intensity of each site. If the site was deep in a forest with a large distance between it and houses and roads, I set it to minimal. If it was near houses or near gardens in a smaller path, I set it to light. If it was in a small patch surrounded by houses I set it to intense.\n\nSH: curation - changed Abundance metric type from 'abundance' to 'occurrence' 14.11.13\nSC1 29/1/2014 Added fragmentation layout\nSc1 29/1/2014 Merged the 2 studies togehter as methodology, location and date applied were the same for mammals and reptiles so they shouldn't have been separated\n\nSH1 28/05/14 Changed Predominant habitat from Urban to Primary Forest as paper states that areas sampled are remnants of natural vegetation. Did not check use intensity as DB's definition sounds reasonable.","They followed the Globenet protocol. They worked on a forest of English oaks of over 100 years old. They split their 3 sampling habitats into rural, suburban and urban based on the percentage of land taken up by buildings (0%, 30% and 60% respectively for the three types). I interpreted this in PREDICTS nomenclature, based on descriptions of the locations in the article as well, as: Primary Forest (minimal), Primary Forest (intense) and Urban (minimal).\n\nSC1 29/1/2014 Added: Habitat has descibed in the source\nSC1 29/1/2014 Changed the sourse name from Horvath to Magura (who is the first author of the paper)\nSC1 29/1/2014 Added source for predominant habitat\nSC1 29/1/2014 Added habitat patch area\n\nSH1 27/05/2014 Checked urban sites for consistency with new definitions. These sites are the same as those described in DB1_2007_Hornung. Have checked forest description online and unlikely to be primary forest, so have changed classifications to match those of DB1_2007_Hornung - suburban and rural is Secondary indeterminate with Minimal use (previously Primary with Intense and Light respectively), urban is Urban with Minimal use (as previously).","SH curation: changed Abundance metric type from 'Abundance' to 'Occurrence' as is presence/absence data 14.11.13\nSC1 29/1/2014 Added Fragmentation layout and Habitat as described in the source\nSH1 20.05.14 after discussion with TN, changed use intensity from minimal (for sites within A) and light (for sites within B) to all Intense.","The sites were split into 5 urbanisation categories. I interpreted these using the descriptions and google maps thusly:\n\nUZ1 -- urban intense\nUZ2 -- urban intense\nUZ3 -- urban light\nUZ4 -- urban minimal\nUZ5 -- young secondary forest\n\nI set zones 1-4 as well within the unfragmented habtiat type (i.e. all were well within the urban environment) and I set zone 5 as part of a fragmented landscape (consisting of suburbs and new growth forests on old crop and pasture land)\n\nSC1 25/2/2014 checked blocking design and it is correct, there are not block. Couldn't ad maximun linear extent but ad Habitat patch are equal to -1 (use -1 if patch area if unknown but large, extending far beyond the sampled area) as indicated in the guidelines as the samples are in the city of Beijing, China.\n\nSH1 21/05/2014 Changed sites categorised as Young secondary (sites 20-25) to Urban as still within the city (with minimal intensity as more greenspace around and appear to have been sampled within greenspace). Those sites classified with Urban Minimal use (12-19) I have changed to Urban Light use as small green spaces within city.","15 locations where sampled at different time points: before, during and after construction. The sites were originally a disused orchard, habitat desgiantions were therefore: plantation (minimal), urban (intense) and urban (light)\n\nSC1 29/1/2014 Added Fragmentation layout\n\nSH1 22/05/2014 As orchard habitat had been abandoned 20y prior to the study and the site was 'successionally advanced', have changed 'Plantation' to 'Intermediate Secondary' wiht Minimal use. The year of construction I have changed from 'Plantation' to 'Intermediate secondary' with Intense use. Post construction the area is urbanised an samples from gardens, therefore remains 'Urban' with Light use.","Data came with urbanisation gradient scores: 0-1.6. I split this into three categories: 0 - 0.53, 0.53 - 1.07 and 1.07 - 1.6 (minimal, light and intense). I then put each site into one of these categories.\n\nI considered 'empty' shell as presence\n\nSC1 03/02/2014 Added Fragmentation layout and Source of predominant habitat\nSC1 03/02/2014 Added Maximum linear extent sampled\n\nSH curation: changed Abundance Metric Type from 'Abundance' to 'Occurrence' as is presence/absence data 14.11.13\nSH1 27/01/14 looked at Predominant habitat classifications with regard to new landuse matrix. Previously DB1 classified according to level of urbanisation according to amt of sealed surfaces surrounding, have looked at this and at description in paper and on google earth and have reclassified the use intensities as follows: Riedberg_2 from minimal to light, Bockenheim_4 from intense to light, Riedberg_7 from minimal to light, Frankfurt_8 from light to minimal, Wiesenau_9 from minimal to light, Frankfurt_15 from minimal to light, Ginnheim_16 from minimal to light, Frankfurt_18 from minimal to light, Kalbach_24 from intense to light, Riedberg_25 from intense to light, Bockenheim_26 from intense to light, Bockenheim_29 from light to intense, Bockenheim_30 from light to intense, Messe_31 from light to intense, Messe_32 from light to intense.","","","","","","","SH1 V7 forms. Added linear extent. Checked blocks - none. Habitat patch area not supplied.","11/12/2013 SH1 V7 forms. Added blocks, linear extent and habitat patch size.","12/12/2013 SH1 Checked blocks (blocks present according to map, but not possible to distinguish from text) and habitat patch size - not provided. Added linear extent.","12/12/2013 SH1 V7 forms. Checked blocks - information not provided and habitat patch size - not provided. Added linear extent (3 * 164m).","V7 forms. Changed cell AP39 on the site by species matrix to zero (was blank). SH 12.11.2013\nSH1 12/12/2013 Checked habitat patch size - not provided. Added linear extent (50 x 50m sampling block). Paper states that study was designed in blocks of three of more habitat types but does not specify which sites were in each block.","SH 04.09.13 changed predominant habitat classification for mammals (Sites Study 2) as nomenclature was entered in the old format for secondary habitats.\nSH1 16.01.14 V7 forms. Changed diversity metric from relative abundance and relative number individuals to abundance and individuals for Study 1. The paper does refer to relative abundance when lizards are monitored, but on inspection of the data and methodology, there is no indication that the measures are corrected for effort. Added linear extent (lizards 100m transect, but also searches within 6000m2 of site, therefore approximated 60 x 100m search area, with linear extent through the diagonal of 116m: mammals, 20m x 100m extent of traps (with 1m in height) therefore approximately 102m diagonal). No blocking structure. Habitat patch size ok.","La Cangreja is a national park, only sampled once by one transect, data is included. Only beetles were sampled, not spiders therefore left cells blank to indicate species not looked for. SH curation: removed block labels as incorrect. Separated data into one year per study (previously had been summed into a three year period). 12.11.13\nSH1 16.01.14 Curation V7 forms. Changed data again so that years are kept seperate by rows, but multiple years within single study. As spiders were not monitored during all years of the trial, kept spiders and beetles as separate studies. Added linear extent. Habitat patch size not provided.","Moth data for paper not included, as data has not come in.\n15/12/13 SH1 V7 forms. Checked blocks and not present. Estimated linear extent - paper specifies two 0.5ha plots - approximated 100m linear extent x 2 = 200m. Habitat patch size not available.","SH1 16.01.14 Curation. V7 forms. Looked at habitat/use intensity and no gradient is correct. No blocking structure. Added linear extent.","15/12/13 SH1 V7 forms. Added linear extent (midpoint in range of transect lengths). Added habitat patch size. Added blocks.","Authors comments: \"I would request that anywhere that credits are given, that Cornell and CATIE are cited as the institutions that supported the work. Both Jeffrey Milder and Fabrice De Clerck to be co-authors. I also want to make sure that the field scientists who conducted the actual field work to generate these data are acknowledged appropriately. These are:\n\u00b7 Dalia Sanchez for the vegetation data\n\u00b7 Diego Tobar for the butterfly data\n\u00b7 Cliff Cordy for the bird data\n Depending on the nature of the publication you are producing, I am not sure it would be appropriate to include these people as authors, but perhaps there is another way to acknowledge their work, as you deem appropriate.\"\n\n12/11/2013 LH1 Changed empty cells in site by species matrix for Honduras Butterflies to zeroes.\n16/12/13 SH1 V7 forms. Changed Data use permitted from full permission to author consultation reqd (see comments by Daniel above). No blocks present. No habitat patch size data.\n\n27-05-2014 AP1: Max linear extent was previously given as 54m for all sites, but it should be longer for riparian forest (100m) and live fences (200m), so I have made these changes","See page 2113 of the paper for a table of % of land use around each site\n16/12/13 SH1 V7 forms. Added blocks. Linear extent and habitat patch size unclear.","Not blocked\n16/12/13 SH1 V7 forms. Checked habitat patch size - is ok. Changed abundance metric 'prevalence' and unit of 'index of relative detectability' to 'occurrence frequency' with 'proportion of plots'. While this is not perfect, for our purposes this is what was recorded as the data refers to the proportion of the lists within which each species is recorded. Linear extent not possible to ascertain.","NOTE: Prof Nina Farwig must also be made co-author of the database paper. Point counts (15 mins each) were repeated 3 times per study site during the day. SH curation: replaced blank with zero in site by species matrix in cell AO50. 12.11.2013\n17/12/13 SH1 Added blocks. Added linear extent. Added habitat patch area where possible.","17/12/13 SH1 V7 forms. No blocking design. Habitat patch areas described in text are large ranges, so left field blank. Added linear extent.","Data from Martin, given by Carla Gheler-Costa - contact through her.\n17.12.13 SH1 Changed Insightly status to Completed (from In progress) and 'Data received / permission obtained' (from Ongoing correspondence with author). No blocking design. Added linear extent. No habitat patch area provided.","Also put Muchane Muchai as a co-author too, as well as Mary Nyawira Muchane.\nSH1 21/01/14 V7 forms. Altered data permission to 'full permission granted' from 'uncertain' following email correspondence with authors. No blocking structure. Added linear extent (diagonal of 1km x 2km square). Removed habitat patch size as had been entered as 3km, but habitat patch size not provided by authors. Added sample effort (3km).","This study is about habitat restoration: The sites here are 9 year old abandoned pasture, old growth fragmented forest, abandoned pasture burned to the ground 7 years previously, 7 year old native tree re-planting restoration.\n17/12/13 SH1 V7 forms. Changed 'cannot decides' in Predominant habitat type to 'plantation forest' as text specifies area was replanted as plantation. No blocking structure possible to determine (map in paper shows sampling conducted in pairs, but not pairs are not labelled as such in data). Added linear extent. Checked habitat patch size and added -1 for the primary forest.","Each of the 74 sites which encompass plantation, logged forest and small holding in this study where sampled between 1 and 10 times by transect. So do not forget to divide by 'effort' i.e. 1-10 when analysing. Not blocked.\n\n17/12/13 SH1 V7 forms. Added linear extent. Checked habitat patch size and not provided by author.","17.12.13 SH1 V7 forms. Checked habitat patch size and data not provided by author. Added linear extent. Checked blocks and ok.","SH1 V7 forms. Changed abudance metric from 'abundance' to 'effort-corrected abundance'. Changed unit from 'individuals/trap' to 'individuals/unit effort'. Changed soil core sampling effort unit from 'trap' to 'square m'. Added linear extent and habitat patch size.","","No suitable crop type was found for yerba mate at FF3, so I classified it as \"various crops combined\" (1.3.4)","Part of this data was also published on a scientific article (Influence of habitat management on the abundance and diet of wild rabbit (Oryctolagus cuniculus algirus) populations in Mediterranean ecosystems), which was published in the European Journal of Wildlife Research in 2009. That paper is also on the dropbox.\nTranslated title: Influence of habitat management on the abundance and diet of wild rabbit (Oryctolagus cuniculus algirus) populations in the Southwest Alentejo and Vincentine Coast Natural Park","The author sent some data but the one on the paper appears to be more complete. Hence, only the data from the paper was processed.","As the Biosphere Reserve the study took place doesn't appear to have any primary vegetation, I assumed that the distance to the nearest edge of habitat supporting high diversity was the distance to the closest Biosphere Reserve (Sierra del Abra Tanchipa), which has been officially protected since 1994.","","Data taken directly from the paper. However, coordinates are only available for the study area, not for the sampling points.","Extra data that was not published on the paper was also added. This data includes other reptiles and amphibians. Sample sites P and P2 were removed because site properties and methodologies could not be confirmed.\nTitle in English is 'Lizard diversity in coffee crops and primary forest in the Soconusco Chiapaneco'.","","Translated Title: Palm (Arecaceae) diversity and distribution in three humid forest fragments in Costa Rica.\nFabiola Jim\u00e9nez Hern\u00e1ndez should also be included as a co-author.","Site area was assumed to be the area of the Serra do Jaragu\u00e1 State Park (Not to be confused with the Jaragu\u00e1 State Park).\nFeeder group data is available.","As it is described in the paper that \"the village and all of the plots were set up at the edge of the terra firma forest\", the distance to the nearest habitat supporting high diversity was set at 500m.","Species are probably native but the status was not reported.","Data taken directly from the paper.\nNo distance to the nearest edge of habitat supporting high diversity was set on Chichijima because it is an island where such high quality habitat does not exist.\n\nSC1 04/03/2014 Added Geographic coordinates sent by the author.","Regarding the habitat: All sample quadrats (including intact forest quadrats) were on pastoral lands, and subject to variably intensive management by pastoral landholders. In this setting, regrowth resulted from clearing for intensification of pastoral development. Regrowth (or rehabilitation to forest) was not a state sought by the landholders, but rather was an unsought consequence of management neglect or inaction. In most cases, cleared lands, regrowth and intact forests were subject to continuing grazing pressure, frequent fires and incursions by non-native plants (usually through deliberate introductions, then spread, of exotic pasture grasses, particularly gamba grass Andropogon gayanus).","Title in English: Bird abundance and species richness in three successional stages of the dense sub-montane broadleaf forest in Antonina, Paran\u00e1\n\nThe data was provided in a relative abundance index which I backtransformed to individuals. I.e. data was in a Point Abundance Index (PAI), which equals n/72. Hence, in order to obtain n, I did PAI*72","","","Data processing started by Lawrence Hudson","Distance to nearest edge supporting high diversity habitat was considered to be the distance to the closest Nature Reserve found: Mount Meron Nature Reserve. The exclosures are quite small (average 0.4-2 ha)","","Could only get the GPS coordinates from each island, not from the exact place in each island that was sampled. Nevertheless, all the islands area really small.","","","","Translated title: Effect of different degrees of disturbance on a bird community in the provincial reserve of Parque Luro, La Pampa, Argentina\nFor the distance to the nearest edge of habitat supporting high diversity I assumed it was the distance to the closest National Park: Lihue Calel (9.901 ha) in La Pampa.","Translated title: Scarabaeinae species (Coleoptera Scarabaeidae) of forest fragments with different levels of modification in Santa Maria, Rio Grande do Sul","Coordinates were obtained by analysing Maz\u00e1n Reserve's orography through Google Earth and matching them with the height values mentioned in the study (e.g. 2950 - 3100m for \"Bosque Introducido\")","Each site corresponds to a 2km long (generally) non-linear transect that usually goes through different habitat types. Hence, the sites are blocked according to each transect. As only the GPS coordinates of the starting and end points of each transect were available, approximate GPS coordinates for each habitat type in each transect were obtained via Google Earth. As the transects were not linear, an average of 1000m was considered as the maximum linear extent sampled for all transects.","Land use (predominant habitat within the site) was determined through cover percentages for each plot (>50% land cover of a certain habitat). For example, if on one plot 60% was Scrubland, 30% was Vineyard and 10% were other land uses, that site was classified as Secondary Vegetation (Indeterminate Age).","The difference between the two studies is the sampling effort. For Shrubs & Ferns they used 10 1m2 plots, while for Trees & Shrubs they used 30 1m2 plots. \nThe plots in these 2 studies are the same plots studied in DL_2013__CalvinoCancela.","","Title in English: Impoverishment of fragmented woodlands in the North of Gran Sabana, Venezuela","","","","Only part of the data was used for this paper, which was published in 2011. The rest of the data was provided but was not used in this paper. Since some of the data was published in 2012, I had to put the publication year as 2012.\n\nSH1 21/05/2014 Changed name back to 2011 so that it matches the paper from which the methodology details etc were taken. After chat with TN, changed sites 61-64 from Intermediate Secondary to Primary non-forest as the presence of invasive species does not constitute a change to secondary. Changed sites 5-8 from Secondary (Indeterminate) to Primary non-forest and dried up riverbank is still primary.\n\nLH1 29/05/2014 The author provided some data collected in 2012 - after the article was published. I discussed this with Andy and we decided to rename to DL1_2012__Siebert.","Distance to the nearest edge of habitat supporting high diversity was considered to be the distance to the closest protected area (Pichasca Natural Monument)","","The main paper was published on 2010. However, since we're using additional data that wasn't on the paper and that was collected after 2010, I had to put the year of publication as 2013. Block structure groups the same sites that we're sampled on more than one year.","","","T.F. Carrijo, one of the co-authors, was the one who sent us the paper and gave us permission to use the data.","Author was contacted but did not reply. Nevertheless, all data required is available on the paper.","data amalgamated from Abi's original excel spreadsheets (AB1_2007_Barlow_19_16 and AB1_2007_Barlow_19_17) and data from author. Note that author provided map of sampling sites in paper, but coordinates taken from data sent by Hawes (see Hawes etal 2009). 27/01/2015 - HP1 Data based on cluster sites. A single lat long was taken from the original sites within each cluster (ie. appropriate land use), and assigned to the cluster.","Site locations for oil palm sampling sites are not known. Also. \"Cannot Decide\" should be plantation forest. 25/06/2013 - Updated by HP1. 07/01/2013 HP1 curate maximum linear extent, estimated coordinate precision.","Three different sample areas","Raw data was of every individual tree sampled. Excel data sheets are the total abundance for each species for each transect.","Braun Blanquet index converted to presence/absence data. Author is particular about data use, and has contact PREDICTS about contractual data use.","Site specific coordinates unavailable but treatment area coordinates have been estimated through use of google maps.","Data was initially organised into a number of plots that were divided into sub plots that was then further divided by sample and fire regime. The data is the totals for the sites by species for the three years total. Each site is specific to a certain fire regime. Numbers were collated using R script located in dropbox.","Site specific coordinates un-available. Coordinates given are for the study area provided in the paper, all study sites are with in 2km of each other.","Data is compiled from multiple traps within a single treatment area.","Sites numbered in provided data and given coordinates but map of region doesn't contain numbered sites. So fragmentation layout options are estimated from habitat type and coordinates. Square metre measurements were taken between may and july both years, not continuously through out.","","If data is going to be used by third parties other than predicts, consultation is required.","SH1 02.06.15 data was stored in old WCMC database, migrated onto V6 forms using Tim's code. I have pasted into V7 forms and have contacted author to obtain abundance data. Data provided for two sampling visits within same year - have summed data. Made corrections when author had duplicated sp names (compared to mean data that author also sent through where the duplicated names had already been corrected). Max linear extent = 4 plots of 20x20m with at least 100m between = at least 380x20m.","SH1 03.06.15 Data originally in WCMC database. Data migrated onto V6 forms using Tim's code. Have copied and pasted into V7 forms. Have contacted author for abundance and coordinates. Max linear extent = 3x 4ha plots with mean distance of 1200m between, so max is 1200+1200+100x4=2800m","SH1 08/06/2015 Data was originally stored in WCMC database, V6 forms produced using Tim's code. I have copied onto V7 forms.Have also seperated data per year (previously summed over 3 yrs) as per Appendix 1 in paper.","Access ID [169]\nSH1 29/04/2015 was entered as a cluster site, so took mid-point of coordinates and increased uncertainty of coordinates to 3km as this was the maximum distance between points. Pasted into new vesion of forms (V7). Dates incorrectly entered so have corrected to those provided in paper. Changed use intensity for Pasture from Intense to Light as high stocking density but no pesticides used","Access ID [91] Combined with Excel spreadsheet entitled EP1_2008_Sakchoowong. No indication given of the intensity of agriculture in the teak plantation\n\nSH1 28.11.13 V7 forms. Checked blocking structure - not present. Changed old area size to new habitat patch size. Could not add linear extent - paper outlines that 10x1m2 quadrats are sampled and that the quadrats are randomly placed wihtin the site, but does not say the size of the site.","Access ID [88]\n\nSH1 10/12/2013 V7 forms. Changed 'relative abundance/individuals per unit effort' to 'effort-corrected abundance/effort-corrected individuals'. Added blocking structure. Added linear distance - difficult, as various trapping methods were used and no information on spacing is provided (also see results - different methods targeted for different species), but approximated linear distance by adding together the width of all nets and traps which may have been used. No habitat patch size information provided.","Access ID [73] This data has been migrated from the pilot study database. Data was originally entered as cluster sites. Cluster sites refer to pitfall traps along transects (abundance data is available per transect), so have taken location data from midpoint of transect (#4) for each transect. Accuracy of coordinates is 400m as the transects were 800m in length. Use intensity was gathered from 'Main threats' description in Table 1. Changed Study Target from 'Selected Species' to 'Entire Community'. Species abundance data were incorrectly entered (data entered against wrong forest fragment, some abundance data entered as 0.5 etc) so have re-entered using Table S1. SH1 28.04.15","30/01/2015- HP1 - Form changed to v7. Cluster sites were present, so to deal with this, each land use was summed with species individuals (as presented in the paper). Coordinates from one site within each land use were then choosen to represent the entire cluster. Data was orginally in Barlow et al. 2007 study","Access ID [101]\nSH1 19.05.15 Data from Jake Simpson's database, data entered into PREDICTS' forms using code written by Tim. Originally formatted as cluster sites as we have coordinates for each transect but only summarised data for each habitat type. See map in Figure 1 for positions of transects. I selected a single pair of coordinates for each habitat type by taking the first pair of coordinates for each habitat type (as entered by Hollie).","25/11/2013 HP1 \n03/12/2013 HP1 changed sample effort field to reflect distance rather than number of plots per site","","25/11/2013 - HP1 Data curation","Coordinates taken from georectified map in Cleary et al 2003. \n\n25/11/2013 - HP1 Data curations","","","22/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for primary habitat.\n\n28/11/2013 HP1 data curation","12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\n3/12/2013 HP1 Curated indication of taxa name and indication of higher taxa level","Data is used in Kessler 2009 analysis, and was originally added to the database as part of HP1_2009__Kessler. However, it is now being added as its own source.\n3/12/2013 HP1 curated maximum linear extent, habitat patch size and indication of species name.","Raw data has multiple (but probably unsuitable) metrics not included in this form. 03/12/2013 HP1 curated maximum linear extent, habitat patch area, source of predominant habitat, species names, and diversity metrics","Coordinates taken from georectified map in Cleary et al 2003\n09/12/2013 HP1 Curated habitat patch size. Linear extent and taxon status","23/06/2013 CM1 updated predominant habitat classifications and source for predominant habitat.09/12/2013 HP1 curated maximum linear distance, taxon status, fragmentation layout. 02/06/2015 HP1 found error in distance to habitat edge field (reported in metres rather than kms), corrected.","09/12/2013 HP1 curated missing taxon status and habitat patch size","27/01/2015 - HP1 Cluster sites were dealt with by taking one coordiante from within each cluster (same habtat type), and applying it to the entire cluster.","","Data is used in Kessler 2009 analysis, and was originally added to the database as part of HP1_2009__Kessler. However, it is now being added as its own source. 09/12/2013 HP1 curated the maximum linear extent, habitat patch area, and diversity metric.","23/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat. 09/12/2013 HP1 curated habitat patch size,maximum linear distance, fragment layout, and species status, and sampling target","1/08/2013 - HP1 - This source contains the datasets in Barlow 2007c PNAS paper that were not found in other scientific articles. 27/01/2015 HP1- Contains cluster sites, so one coordinate was taken from within each cluster (of the same land use) to represent the cluster. Coordinate precision is large to reflect this.","18 sites as pairs along 9 transects. Each transect was treated as a block as author had used a paired t-test. 26/01/2014 HP - Cluster was dealt with by taking one site from within each cluster for the lat and long. Site precision reflects this by having a large distance (ie. covering the entire study area).","09/12/2013 HP1 curated diversity metric unit, taxon status, sample effort, habitat patch area, source of predominant habitat type and fragmentation layout","Blocks based on PATCH number (each patch had a site from each type of land use)","04/01/2014 HP1 curated taxon status, maximum linear extent, removed habitat patch size, source of predominant habitat, diversity metric and target species. Dataset includes 20 more sites than in the study. Site info for additional sites taken from Kumar 2005","HP1 - 2015/02/19 - Coordinates taken from georectified map. Area of Continuous forest taken from Uehara Prado et al. 2009.","23/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat. 4/01/2014 HP1 curated the diversity metric, study target, taxon status, maximum linear distance, sample effort, fragmentation layout. ALL site information was changed to incorpoate different sampling dates. Abundances were changes accordingly.","22/06/2013 CM1 updated predominant habitat classifications for secondary sites, years since fragmentation or conversion, and source for predominant habitat. 06/01/2014 Updated target species, taxon status, maximum linear distance, habitat patch area, ALL site information was altered due to incorrection sitename and latlong combination - abundances were calcualated accordingly, blocking was added,","23/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n\n06/01/2014 HP1 Changed diversity metric. Changed data to presence/absence. Curated species status, sampling targets, habitat patch area, maximum linear distance,","12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes. 06/01/2014 HP1 curated maximum linear distance,","23/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n\n06/01/2014 HP1 Curated study target, species status, fragmentation layout, habitat patch area, maximum linear distance.","HP1 - Bird densities could only be calcualted for the most abundance (19) species. Therefore species observation data were used.","24/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat. 06/01/2014 HP1 Curated study target, maximum linear distance sampled,","06/01/2014 HP1 curated maximum linear distance, source for predominant habitat, taxon status, study target,","06/01/2014 HP1 curated source for predominant habitat, fragmentation layout, taxon status, study target, predominant habitat.","4/01/2013 HP1 curated taxon status.","Some site information taken from Ranganathan et al 2010","22/06/2013 CM1 updated 'predominant habitat' classifications for secondary habitat sites, years since fragmentation or conversion, and source for predominant habitat. 06/01/2014 HP1 Curated taxon status, study target, habitat patch area, fragment layout, maximum linear distance, sample effort,","06/01/2013 HP1 curated study target, site name, fragmentation layout,","07/01/2014 HP1 curated study target, taxon status, fragmentation layout, source for predominant habitat, some predominant habitat classifications, maximum linear distance, habitat patch size and diversity metric.","There are many more studies - only bees, wasps and butterflies are entered here.\n\n07/01/2014 HP1 curated estiamted precision for coordinates, habitat patch area, source for predominant habitat, fragmentation layout, maximum linear distance, species status.","24/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n\n07/01/2014 HP1 curated estimate of coordinate prescision, maximum linear distance, habitat patch area, split data to two different sampling dates, added taxon status, and study target.","07/01/2014 HP1 Curated maximum linear distance, study target, diversity metric","HP1- 19/02/2015 Paper orginally analysed data from Estonia, Finland, Germany, Spain and Sweden. Not all authors sent through their data, so we didn't get any from Finland or Sweden. German data is included in Krauss 2003 and 2004. Study 1 (Estoninan plants) converted to presence absence data from ordinal abundance.","29/05/2015 - Data is a combination of the 2011 Peters paper, and the 2009 Peters paper (also in the database). Where >10 trees had been removed in the past 20 years I have classified the use intensity as Light, others Minima","","Email correspondance will provide additional information for classifiation of data. Transects were designated as blocks. Location of individual trap determined the predominant habitat. Some transects bordered riparian reserves and oil palm where that was the case, traps in RR were labelled as primary forest and those in teh oil palm were labelled as plantation. Some traps were removed from the excel form as theyhad been destroyed (NAs in data given by author).","Abundance measure is number of 15 minute bins species was observed in out of a total of 12,treat missing value as 0\n\n24/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n27/06/2013 AP1 curated block structure (study does not have blocks).\n05/08/2013: AP1 curated study target (whole community)\n12/11/2013: LH1 changed empty site by species cells to zeros","06/08/2013: AP1 curated block structure (sites are matched pairs) and sampling target (whole community). Checked LU, LC (fine).\n\nSH1 28.11.13 V7 forms. Changed permission from 'For this ongoing project analysis only' to 'full permission granted'. Changed abundance metric from 'individuals per site' to 'individuals'. Added linear extent (based on sampling square of 12.5 ha). Deleted patch size as was entered as the size of the sampling patch and the size of the habitat is not provided (note that the data provided by the author has a row for field size (ha) per site, but that this does not correspond to the description in the paper of sizes 100-1000 ha). Changed fragmentation from old 'Part of an unfragmented habitat' to new 'Part of the matirx surrounding remnant patches\". Added source for predominant habitat as the paper. Added species status - 'not reported'. Added study target. Deleted coordinate precision as is likely to be greater than 1 degree (as was originally entered). Author provided data in Hungarian EOV coordinate system.","24/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n27/06/2013 AP1 added site area from the author's spreadsheet (Summerville 2006.xls); changed years since conversion for the 2005 sites (as they're a year older than in 2004); added ages for the restored sites (paper specified \"> 5 yrs\"; I've multiplied this by 1.25 for the first year of sampling and then added one for the second year); added info on fragmentation layout for the primary and restored sites; and curated block structure (not blocked).\n\n05/08/2013: AP1 curated study target (whole community).","SH1 07/01/2014 V7 forms. Added species status - not reported. The author does undertake an analysis including native and non-native bird species but this info is not given in the paper or provided in the data provided by the author. Perhaps could be chased though.. Added blocking structure. All habitat was entered as Urban and use intensities as 'Cannot decide'. Changed habitats and use intensity according to land use types (see data from author LandUse302-00) and vegetation classifications (see data from author 100m302-00) using matrix compiled for this source (see Sam's landuse decision matrix). Added linear extent. Habitat patch size not provided. Added fragmentation layout.","28/06/2013 AP1 curated blocks (no block structure, though sites are in six reserves), and site area (areas of the reserves - though reserves aren't purely prairie - there's some agricultural use). Also changed fragmentation layout data as paper says all sites are tallgrass prairie (not fields etc). Distance to edge added from file from author (Cagle land use data.xls: I used whichever was lower of distance to grassland edge or distance to non-natural cover). Use intensity added based on threat from agriculture - I scored sites with > agricultural land within 1km as \"light use\" rather than \"minimal use\" based on potential threat from e.g. fertilizer; other sites \"minimal use\" because these are preserves.\n05/08/2013: AP1 curated study target (whole community).","06/08/2013: AP1 curated sampling target (whole community), age of plantation sites, fragmentation layout (using Google imagery; fragmentation layout not relevant for plantation sites), use intensity (was overestimated for sparse plantation plots), blocking (authors treated data as being in two large blocks).\n\nSH1 V7 forms. Changed abundance metric and unit from 'detection' 'individuals per point' to 'effort corrected abundance' with 'effort corrected individuals'. Added source for predominant habitat (paper). Removed habitat patch area as had been entered in old forms as sampling area and information is not provided in the paper. Linear extent 700m - methodology includes up to 7 point counts per site, each with a radius of 50m - therefore approximated 700m. Added Species status (not reported).","anuran call index as follows: 0, no individuals of a given species heard; 1, one individual heard; 2, multiple individuals with no overlap in calls; 3, full chorus; have chosen the highest for each species in each site. Abundances for P.crucifer and R. blairi are included despite the author excluding them from his analysis (due to area being at limit of species' range).\n\n24/06/2013 CM1 updated predominant habitat classifications, and source for predominant habitat.\n\n1/8/2013 AP1 Study has no blocks. Primary sites are remnant fragments; original excel file from author has ages of the wetland (i.e., the breeding habitat) for most sites, on a coarse scale (<3, 3-10, >10 years). The same excel file contains quantitative data on a wide range of threats\n05/08/2013: AP1 curated study target (whole community).","06/08/2013: AP1 curated block structure (from paper and Excel file from author), changed PredominantHabitat (plots are in secondary forest, surrounded by primary), added ages to two categories of sites and distances for two others, and added study target.\n\n03.12.13 SH1 V7 forms. Changed 'individuals per site' to 'individuals' as the 'per site' was redundant. Added Source for Predominant Habitat (publication). Removed habitat patch area as had been entered in old forms as the size of the sampling location. Added linear extent (200m transect). Added species status (not reported). Changed coordinate precision from 0.1 degrees to 1m - not sure why was entered as 0.1 degrees as author provided UTM coordinates.","I did enjoy filling up the description of the data source and had no problems with identifying necessary information, formatting or dealing with the form fields.\n\n24/06/2013 CM1 updated predominant habitat classifications and years since fragmentation or conversion.\n\n1/8/2013 AP1 added SC1's Use Intensity data (from the paper and Google Earth); replaced plot areas (constant, 500m2) with site area (stand area) from author's spreadsheet; replaced low-resolution age data with values from same spreadheet (the Continuity column in that spreadsheet has years since each site became forest, which is typically older than the stand). Edited PredominantHabitat in the light of some young stand ages - I've classed stands < 20 years old as intermediate rather than mature. Looked at blocks - none.\n05/08/2013: AP1 curated study target (whole community).","Not much site info as sites were a cline from landscape dominated by pastureland to that dominated by soybean crop. Authors defined four landscape strata using indices put into FRAGSTATS\nSH1 08/01/2014 V7 forms. Added study target, species status, habitat taken from email from author (see Insightly and saved in file), use intensity is correctly entered as 'cannot decide'. Linear extent is not provided - each 'site' refers to a point count of birds along a transect and paper does not report the visual/auditory range of the habitat. Added fragmentation layout. Patch size not provided. Added agricultural fields.","1/8/2013: AP1 implemented SC1's corrections of the coordinates of sites (see note pasted below); also added area of each patch from the source paper, fragmentation layout, blocking (no blocks) and SC1s estimates of use intensity Pasted note from SC1: Sara Contu added data about Use Intensity on November 2012. Coordintes entered by Hannah White are not correct. Correct coordiantes are\n45\u00b002.4\u2032N 72\u00b010.4\u2032W 45.03444 -72.16778\n44\u00b057.2\u2032N 72\u00b052.9\u2032W 44.95056 -72.86917\n45\u00b020.7\u2032N 71\u00b044.2\u2032W 45.33528 -71.73389\n45\u00b058.1\u2032N 71\u00b009.1\u2032W 45.96694 -71.15028\n45\u00b059.8\u2032N 73\u00b018.0\u2032W 45.98556 -73.3\n45\u00b007.5\u2032N 74\u00b013.5\u2032W 45.11806 -74.21806\n05/08/2013: AP1 curated study target (whole community).","SH curation: some cells in the site by species matrix were blank - replaced blanks with zeros. 12.11.2013\nSH1 19.11.2013: changed abundance metric unit from 'individuals per site' to 'individuals' and updated fragmentation layout from old 'part of unfragmented habitat' to new 'well within unfragmented habitat\n\n03/12/13 SH1 V7 forms. changed 'Data use permitted' from 'uncertain' to 'Full permission granted'. Added species status (not reported). Added patch size as 4ha (paper reports that stands were 3-5ha). Added linear extent - single light trap - I estimated this to be 1m. Added blocks - block per watershed. Changed habitat and use intensity from all being 'primary forest' with 'light use' to all being intermediate secondary with minimal use apart from those sites where either 80% or 100% clearcutting had occured. These sites I entered as young secondary with minimal use. Added years since fragmentation. Added sampling target.","Treat missing value as 0\n\n1/8/2013: AP1 curated. Looked at blocking (no blocks); added age of plantation stands.\n5/8/2013: AP1 added study target (whole community)","Ordinal relative abundance where 5=found in 4sq.m subplot, 4=found in 8sq.m subplot, 3=found in 16sq.m subplot, 2=found in 32sq.m subplot and 1=found in 64sq.m subplot\nLH 2013/12/19 Changed 'Abundance metric type' to 'presence/absence' and converted non-zero values to 1, after discussion with the group. Added study target and taxon native/alien status.\nSH 2014/8/1 Added blocks. Changed Predominant habitat. HW had entered all as Primary non-forest, but in each block of 4 transects, 2 sites were in primary and 2 sites were in cleared (with varying levels of grazing intensity). Through the vegetation characteristics provided by the author in the data sent to HW, it was clear that the first 2 sites were the primary and the second 2 sites were the cleared (based on number of live trees, amount of shrub etc). Added use intensity for primary (minimal) but not possible to discern for the pasture as author mentions varying stocking intensity but does not specify per transect. Added fragmentation layout and linear distance. Habitat patch size not provided by author. Entered habitat description.","I did enjoy filling up the description of the data source and had no problems with identifying necessary information, formatting or dealing with the form fields.\n\n24/06/2013 CM1 updated predominant habitat classifications, years since fragmentation or conversion, and source for predominant habitat.\n\n1/8/13: AP1 checked block structure - no blocks.\n5/8/2013: AP1 added study target (whole community)","I did enjoy filling up the description of the data source and had no problems with identifying necessary information, formatting or dealing with the form fields.\n\nSH1 4/12/13 Changed data use permitted from 'this project only' to 'full permission granted' (see emails in Insightly). Added study target (community). Changed diversity metric unit from 'individuals/plot' to 'individuals' as effort unit is plot and value is 1. Changed Fragmentation layout from 'Part of unfragmented landscape' to 'Part of the matrix surrounding remnant patches'. Added 'Source for predominant habitat'. Added blocks (matched pairs). Added linear extent. Added taxon and species status and removed habitat patch size as this had been brought over incorrectly from the old forms.","1/8/2013: AP1 checked for blocks (study is not blocked), updated fragmentation layout, filled in missing Predominant habitat values, and added ages of dense conifer plantations from the paper.\n5/8/2013: AP1 added study target (whole community)","SH1 04/12/2013 V7 forms. Added blocking structure (from map in paper it appears that there are two spatially distinct patches). Changed data use permission to reflect permission emails in Insightly. Added study target. Changed abundance metric from abundance/mean abundance to effort corrected abundance/effort corrected individuals as the data is averaged between sampling visits per year and the effort unit is 'visit' and the quantity is 1. Added species status. Added linear extent, habitat patch size, source of predominant habitat. Changed fragmentation layout from 'cannot decide' to unfragmented (old growth - within, and fragmented - unfragmented on edge) as per description in paper. Altered sampling dates in excel spreadsheet for breeding as did not match data provided by author and PDF.","Have used co-ordinates of 4 plots from georeferenced map, not lats/longs given by author as there are 25 traps within a 1000mx300m plot\n\n01/08/2013: AP1 - Checked blocks (not blocked). Changed fragmentation layout in line with Adriana's definitions.\n5/8/2013: AP1 added study target (whole community)","I did enjoy filling up the description of the data source and had no problems with identifying necessary information, formatting or dealing with the form fields.\n\nSH1 09.12.13 V7 forms. Changed permission status to 'full permission granted' as per emails in Insightly. Species status 'not reported'. Sampling target 'community'. No blocking structure. Added linear extent - 20m - approximate distance that static anabat will reliably pick up bat call (dependant on species). Added fragmentation layout as judgeed from map in paper an description. Habitat patch size not provided. Changed 'detection' and 'activity/night' to 'sign abundance/signs'\n\nSH1 28/05/2014 Checked urban classifications against new definitions - changed sites from Urban to Primary Forest when the site was within a remnant patch of forest or on the outskirts of continuous forest. Used google maps (together with web searches regarding the history of the national parks) to decide if a site was Urban or Primary. Have entered 'Google maps' as the Source for predominant habitat for all those sites which I changed in this manner (I added the Source as Direct from author for all other sites which were not altered).\n\nSH1 28/05/14 changed 'Sign abundance' and 'Signs' to 'Effort-corrected sign abundance' with 'Effort-corrected signs' as data is mean number of calls/night.","","","","","","Human land use intensity is from an overall evaluation of the variables in Appendix 1. Method used in this study is counting pellet-groups, and I used point count in the list to represent it.","1. The author donot have coordinates for primary forest, but these a few primary forest are 500 meter away from the nearest plantation forest site. So after checking at Google Earth, the same coordinates are adopted for these primary sites but different precision units are used. 2. Use intensity is indirected measured by the capture of dog image in camera traps.","Plot locations were estimated using map in paper and http://www.satsig.net/maps/lat-long-finder\nAccess ID [301]\nSH curation: changed Abundance metric unit from 'Individuals/trap' to 'Individuals/plot' as this is better description of data. Also changed Sampling effort unit from 'Catch' to 'Plot'. 14.11.13\n\nSC1 03/02/2014 Added Use intensity for the Sipalay site\nSC1 03/02/2014 Changed the Sample- end date from 12/2001 to 8/2002","F01-F27 are forest fragments where-as S01-S07 are part of Krau Wildlife Reserve. The area shown from S01-S07 is for the whole of Krau Wildlife Reserve.\nAccess ID [298]\n\nSC1 3/2/2014 Added use Intensity fr the records that were missing this information\nSC1 3/2/2014 Added Distance to the nearest edge of habitat supporting high biodiversity, as it is provided by the author (see pag. 2118)\nSC1 3/2/2014 Checked blocking structure and it is ok.","Species list can be found in Watling et al. 2009 appendix. GPS location was deduced using http://www.satsig.net/maps/lat-long-finder and the map in Watling et al. 2009.\nAccess ID [290]\n\nSC1 3/2/2014 Changed Sample end date from 2002/9 to 2004/3\nSC1 3/2/2014 Added Use intensity\nSC1 3/2/2014 Added Distance to the nearest edge of habitat supporting high diversity\nSC1 3/2/2014 Checked blocking structure and Old site area and they are ok.","Locations of sites estimated from map in paper and http://www.satsig.net/maps/lat-long-finder. Gallery forest 1 & 2 locations are put as the same as there is only 1 location given in the paper.\nAccess ID [299]\nCuration SH: changed 'Abundance metric unit' to 'Signs abundance' from 'abundance' for Study 1 and to 'Abundance' from 'Occurrence' for Study 2 as these more accurately represent the data. 14.11.13 \n\nSC1 3/2/2014 Added use intensity \nSC1 3/2/2014 No blocking structure","Species data found in Sodhi et al. 2010 appendix. Lat/Long estimated using http://www.satsig.net/maps/lat-long-finder. Lead author passed away, second author's email in form but second author has not been contacted.\nAccess ID [293]\n\nSH1 10.12.13 V7 forms. No linear extent provided in paper ('we walked through the forests'). Deleted habitat patch size as they only surveyed forests, but only total island size is given. Spp status added. No blocking structure. \n\nSC1 4/2/2014 Added Predominant habitat, use intensity and fragmentation layout","Species information found in Wang et al. 2010 appendix.\nAccess ID [288]\n\nSC1 10/2/2014 Deleted Habitat patch size as the value reported was the area of the islands (ha)\nSC1 10/2/2014 Added Use intensity\nSC1 10/2/2014 Checked block design and it is ok","Data from paper but author sent abundance matrix with corrections for species names\n\nLH1 2014/07/28 Replaced empty cells with zeroes","Old sampling (1994). Author rounded coordinates to the nearest minute, their precision is +/- 1 minute or +/- 2 minutes\n\nLH1 2014/07/28 Replaced empty cells with zeroes","The study has 12 sites, however, they belong to 6 outcrops, each one with 2 habitat ypes (primary and secondary). Since the author could only provide the coordinates for the 6 outcrops, the two sites of each outcrop will present the same coordinates, these two sites are only separated by 100 or 100 meters. Some species are not yet described, tehrefore, the author used special names sucha as: Microcystina sp. BO-01, Microcystina sp. BO-02, Everettia spec. 1\n\nLH1 2014/07/08 Added taxa indication","Sites refer to transects which belong to 5 different fragments. Each fragment presents different types of forest habitats (primary or secondary). Information about Habitat patch area refers to the size of the fragments, not the sites, since information about the habitat size of each site was not available. Species names were edited (see file in Dropbox folder). A couple of sites (TER-NFTB-T173 and TER-NFSB-T164, sampled in 2008 and 2010) were added by the author in his dataset, these were not taken into account in the paper and they were sampled after the year of publication, therefore I excluded them for PREDICTS files\n\nLH1 2014/07/08 Added taxa indication\nLH1 2014/07/28 Filled empty cells with zeroes","","SC1 2/9/2014 I have added the sampling dates to the sites as these were received too late from Katia to be processed.","","Each site was sampled with three collecting methods: baiting, pitfall traps and Winkler extraction.\nAuthor lost coordinates of each site but approximate coordinates were provided for the whole area of the study, therefore all sites will present the same coordinates in the Excel file. Sites are separated for approximately 20-25 m\nAbundance matrix lists Morphospecies and Indication of high level taxa refers to Genus (provided by author)","Data from paper. \nTwo sampling methods were used in this study (Point-count surveys and mist-netting) at three sites. Mist-netting was conducted only in the secondary forest and the oil palm plantation and point-count surveys were performed in each of the three habitat types. Therefore, intead of splitting the data in two studies, I used \"Various\" as sampling method.\nMaximum linear extent sampled was taken from details of point-count surveys.\nDOI for the paper was not found.","Fungal diversity was established through rRNA sequences, therefore abundance matrix presents the sequences names (20 fungal phylotipes). The number of clones detetected per sequence was converted into percentages in order to use relative abundance as abundance metric type.\nAuthor was contacted but she sent an incomplete table in an Excel file, therefore all data was taken from paper","The author did not named the sites (transects) properly, he only listed the type of habitat, therefore I assigned numbers to each transect of each habitat to create the sites' names.\nAuthor lost coordinates, therefore all sites present the coordinates for the whole study area which were provided in the paper","Author was contacted and she let me know that data was available at Plos One website: http://datadryad.org/resource/doi:10.5061/dryad.dr6s2.\nAbundance matrix was edited since the author reported species abundances per date, not per site. Each date was considered as one site\nI found a duplicated site name [CL-01.2007.07.06] (same site, same date). However, the author reported different abundances for these two sites (dates), therefore I labelled them with \"a\" and \"b\"","","SC1 6/11/2014 author provided coordinates for the initial and final coordiantes point from each site, intensive and extensive sites: \"Sampling points were placed 200 m from each other in a more and less 1 km straight line in each site (intensive and extensive use). I only have the initial and final coordinates from each site:\"\n\nA -19.548962 -56.241705\nF -19.572385 -56.248786\n\nG -19.574795 -56.244708\nL -19.56645 -56.250426","","","01/08/2013: AP1 - Added blocks (sites are in 4 blocks, which are even termed \"sites\" in the thesis). Removed \"Threat\" from the list of species. Updated fragmentation layout to Adriana's scheme.","SH1 23/01/2014 V7 forms curation. Changed species list, abundances, site list as author sent data on all transects and species. Added linear extent. Habitat patch size not possible to ascertain. Added blocking structure. Study target. Fragmentation layout.","SH curated - copied data into Version 6 PDF and Excel spreadsheets 28.08.13\nSampling effort unit should be 'relative effort' but could not re-enter into new sheets therefore entered as 'site' SH 03.09.13\nEntered into V7 forms 12.11.13\nSH curation: corrected abundance metric type to 'density' and abundance metric unit to 'individuals per km2'. Also replaced gaps in species by site matrix with zeros. 13.11.13\n\nSH1 19/11/2013 changed old style fragmentation layout terms to new ones (changed 'Part of unfragmented habitat' to 'Well within unfragmented habitat'.","01/08/2013: AP1 - Converted the data on threat intensities that were listed as a species to UseIntensities, using a logarithmic scale - >10 = intense; 1-10 = light; <1 =minimal. Added information on blocks; I treated dry and wet seasons as separate blocks rather than unifying them.","SC 26/11/2013 Added Predominant habitat and use intensity to some cannot decide fields \nSC26/11/2013 Added maximum linear distance and habitat patch area (this was given as >1ha, thus the 1.25 ha value to include an error). \nSC1 27/5/2014 Updated \"predominant habitat within the site\" in order to follow new criteria (if the site's Maximum Linear Extent is > 10m, the predominant habitat is the habitat within which the samples were taken). Discussed with Andy and decide to leave the center of the edge as CANNOT DECIDE.\nSC1 27/5/2014 Changed the fragmentation layout of the forest patch to \"Within remnant patch (perhaps at its edge) that is surrounded by other habitats\".","SC 26/11/2013 Added Endnote reference number. \nSC 26/11/2013 Checked blocking structure and is ok.\nSC 26/11/2013 Changed project category to Data from Paper","SC 03/12/2013 added DOI and EndNote Reference\nSC 03/12/2013 checked blocking structure and is ok. Entered linear distance and new area measurements. Added indication of high level taxa","12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSC 20/11/13 Added Endnote reference number\nSC 20/11/13 Check diversity metric and it is ok\nSC 20/11/13 Checked blocking structure and it is ok\nSC 20/11/13 Added Indication of high level taxa\nSC1 11/3/2014 Added Maximum linear extent to the studies","SC 03/12/2013 Added Endnote reference and Indication of high level taxa.\nSC 03/12/2013 Checked blocking structure and it is ok.","SC 03/12/2013 Checked blocking structure and it is ok.","SC 09/12/2013 Added Endnote reference number\nSC 09/12/2013 Checked blocking stucture and it is ok\nSC 09/12/2013 Added Maximum linear extent sampled \nSC1 27/5/2014 Updated \"Predominant habitat within the site\" to Secondary vegetation (following the new criteria).","SC 25/11/2013 Added Endnote reference number\nSC 25/11/2013 Curated diversity metric \nSC 25/11/2013 Added fragmentation layout \nSC 25/11/2013 Added Indication of high level taxa and Species status (native or alien)\nSC 25/11/2013 Checked blocking structure and it is ok","SH curation: changed 'Abundance metric type' from 'abundance' to 'semi-quantitative percent cover' as this more accurately represents the data. Also changed the abundance metric unit from 'percentage' to 'percent'. 14.11.13\nSC 11/12/2013 Added endnote reference number.\nLH 2013/12/19 Changed 'Abundance metric type' to 'presence/absence' and converted non-zero values to 1, after discussion with the group.\nSC 10/3/2014 Couldn't add Maximum linear extent sampled as the distance between the 3 10x10 plots is not given.","SC 10/12/2013 Added Endnote reference number\nSC 10/12/2013 Check diversity metric and added block number as blocking structure is present. \nSC1 10/3/2014 Changed sampled effort of study 2 to 28 plots, as indicated in the file sent by the author. Changed diversity metric to occurrence frequency and metric unit to \"Number of Plots\" as indicated in the file sent by the author.\nAdded Maximum linear extent to be the diagonal between the 3 parallel transect used for the survey as explained in the article.\n\nSC1 10/3/2014 Added indication of high level taxa in study 1 and study 2. \n\nSC1 10/3/2014 Coded up birds' diversity data as it was not entered from Morgan.","SH curation: changed 'Abundance metric type' from 'Abundance' to 'Percent cover' and the abundance metric from 'percentage' to 'percent' for Studies 4 and 5 as this more accurately represents the data. 14.11.13\nSC 11/12/2013 Added Endnote reference number\n\nSC1 11/3/2014 Merged the studies for the grosshoppers and plants into 2 single studies; before we had 5 different studies (as they were separeted for years, after discusiion with the team we decided to merge them into the same study).\nSC1 11/3/2014 Added all missing diversity data that wasn't entered before but that we were sent by the author.","","12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSC 18/12/2013 Added Endnote reference number\nSC1 28/5/2014 Added \"Maximum linear extent sampled\" as plot size (4x4m) was given in the text.","12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.","","Taxa identified to order level, not to species. Data from logged forest was not included in the spreadsheet as was a random sampling effort which did not correlate with that of primary forest and plantation sites. SH curation - changed study target field from blank to 'entire community' 28.08.13\n18/12/13 SH1 V7 forms. Changed abundance metric from 'abundance' to 'effort-corrected abundance' and metric unit from 'individuals/unit effort' to 'effort-corrected individuals'. Added linear extent. Changed fragmentation layout from old form's terminology to new (keeping same meaning). Checked 'cannot decide' in use intensity and is correct - not enough information is provided. Deleted habitat patch area as data was from old form and the habitat patch area is not provided by the author. Added species status (not provided).","Data provided by CATIE, so as yet unpublished. SH curation - changed study target field from blank to 'entire community' 28.08.13 \n18/12/13 SH1 V7 forms. Changed diversity metric unit from 'individuals/sampling effort unit' to 'individuals' as data has not been effort corrected. No identifiable blocks. Deleted habitat patch size as numbers provided were entered into old forms and refer to sampling size, not patch size, and no data available on habitat patch size. Added taxon status 'not reported'. No data on blocking structure.\nLH1 2013/12/19 Removed coordinates precisions, which were all 1 degree. The only raw coordinates I could find are in the file 'CATIE_converted coordinates.csv', which contains no indication of precision.","The author had provided abundance data for ants, but as they live in colonies, abundance of individuals is not accurate. So entered here (as reported also in the published papers) is the occurrence of each species per site. SH curation - endnote reference, author address, locations of data, study target - fields entered 28.08.13\n18/12/13 SH1 V7 forms. Added linear extent. Added habitat patch size. Changed fragmentation layout text to new form's text without changing meaning of Michelle's entry. Added taxon status (not reported).","This study compared 1982 data with that from 2005. Only data from 2005 has been included in the data set and the information below relates to only this data.\n\n2013-06-11 LH1 Taxa names - replace _ with space\n\nSH curation - DOI, endnote reference, author address, locations of data, study target - fields entered 28.08.13\n\nSH1 16/01/2014 V7 forms curation. Added linear extent. Habitat patch size not provided. No blocking structure. Changed abundance metric unit from 'individuals/unit effort' to 'individuals' as there is no evidence that the data has been effort corrected. Altered fragmentation layout to new wording.","SH curation - endnote reference, author address, study target - fields entered 28.08.13\nSH1 16/01/2014 curation V7 forms. Added linear extent, fragmentation layout. No info on habitat patch size. No blocking structure possible to ascertain from data. Changed abundance metric unit from 'individuals/km2' to 'individuals' as sampling unit was 1km2, so is not really effort corrected data. Changed coordinate precision for each site from 1 degree to 1m. I'm not sure why was entered as 1o as the data provided by the author gives very accurate coordinates.","Author sampled 4 Transects well within the respective Landuse category. Each Transect had 4 sampling points with point counts conducted at regular interval. Although the 4 nested sampling points are pseudo-replicated blocks within a transect I felt that we are losing spatial information and thus entered them as sites as well instead of aggregating the individual number per transect. Each Transect belongs to respective block (Sampled Forest) and all nested points on the transect thus had the same block structure. Common species name were used and converted to uppercase and formatted due to the many spelling mistakes in the names.","Classified Natural Renosterveld as Primary Non-Forest. The dolerite plains are primary non-forest as well after I consultated the author. Although he indicated that grazing occured on almost all sites... Fragmentation layout as indicated by Figure 1 in publication. I kicked out Absence from the data. Aggregated and entered per VegType-Site Combination.","Coordinates for individual plots could not be obtained, thus the data is pooled per Study location. Furthermore the transformed percentage values from the author are used. If instead occurence values should be entered, drop me a note. Maximum linear extent was measured as the diagonal assuming that all plots were next to each other (they were likely randomly placed). Abundance values is the mean percentage cover over all plots pooled to site (where we have coordinates)","Data from Point counts within Forest fragment and Focal Tree species observations entered seperately as different studies as they vary in count methodology and objective (frugivore observations vs whole community assessments). Not all species data could be entered as Author didn't have access to the coordinates of Yale and Wundanyi sites. There were thus removed by me. Furthermore I removed the 2005 observations of focal trees as they were only conducted in one forest fragment and thus don't allow comparisons between land-use classes. Landuse intensity of primary forest was assessed using the information from the author who seperated the sites into little and highly disturbed areas. The majority of the focal tree observations had to be removed as ether coordinates or abundance data was missing. Maximum Linear extent of tree observation estimated as 5m tree diameter. Point count maximal linear extent information from Lehouck et al. 2009 Ecography, who used the same dataset.","SH1 11/06/2014 Changed Predominant habitat for Quaggaskop from Pasture to Mature Secondary Vegetation as the area has not been grazed for 40 years. I had a look online and farm has been restored with the planting of local plants translocated to the farm during construction of a highway and is used as a nature reserve/nursery (see http://www.kokerboom.co.za/about-us.php) so have entered as light use. Entered zeros where blanks previously in spreadsheet.","Used multiple different sampling traps. The Author claims that all sites are comparable in terms of sampling effort and techniques. Species occasionally seen and not caught with the traps were excluded. Blocks were assigned to each sampling region as they might differ because of spatial distance and were designated as independent study region by the author. Sampling effort unit is \"#trap.nights\", which represent the total effort / site. It is the total number of traps set for a period of 24hrs: For example, if 4 traplines of 25 traps each are operated for 2 days/nights, the total \"trap.nights\" number is 4x25x2 = 200. Use Intensity was assumed to be minimal if not indicated as Author claimed to have sampled in the least disturbed sites possible. Savanna used as representative habitat in the landscape matrix as indicated by author.\n\nSH1 11/06/2014 The sample effort unit is trap nights. However, this cannot be entered into the excel spreadsheet so to pass validation checks have had to change the sample effort unit to 'trap' as this is the closest option available. Have checked over predominant habitat classifications and MJ1 has classified correctly: primary minimal use for pristine sites, primary light for disturbed sites, urban minimal for villages and gardens, cropland for sites classified by authors in the 'herbaceous/cultivated' category. Rocky outcrops are cannot decide - probably primary but not enough info to decide. Added maximum linear extent of 490m as the authors state that trap lines were 20-50 traps at 10m apart. Habitat patch area not provided. Added zeros to spreadsheet where blanks previously.","Classified all Forests as Mature secondary Forests, even though author could not discriminate between Pristine and Mature secondary. The author said though that the majority was mature secondary. \nAt each location there are 3 sites surveyed and 3 traps at each sites (so the study has replicates and blocks design).\nSC1 16/10/2014 Added block as the study has a blocking design. Added Use Intensity as minimal for both Predominant habitat types as indicated in the text by the author.","Transects were walked (600m) long, but the modus operandi was rather a systematic timed search of one hour per transect. Each transect at the given coordinate was walked x times. Thus I used the number of visits x for each site and each transect as sampling effort. Possible other values fort sampling effort: length in meter = 600*x visits or hours = visits * 1hour. Furthmore I used the classification matrix to assign the Light use intensity to the mixed timber plantations as they are described by the author as purely monocultural. Dams and stream within agricultural land removed.","Maximum linear distance was estimated with 200m x 100m rectangle for simplicity","Asked Author for specifics on Landuse for the given sites. As following \nGrid5: old secondary forest on dry soil\nGrid16: Swamp forest\nGrid17: young secondary forest on dry soil\nGrid22: old secondary gallery forest\nGrid25: primary forest on dry soil\nSwamp and gallery forest both secondary according to Author. Coordinates represent the start/end point of the respective transect. Density estimates were entered from both the quick survey and the slow","Two Sites omitted due to missing coordinates. Blocks were entered as individual Transects as Transects spanned multiple land-use types. In the end all rounds in were entered aggregated per year. This allows for even more accurate linking with MODIS RS products. This results in four studies in total seperated studies.SEE ACCOMPANIED OUT.CSV FILE AND R-SCRIPT HOW TO DO THIS. Non-transformed land-use data was used to calculate the dominant land-use at 30m radius (max value). Only the abundance data on the 30m circle was used (Bands 1) and the mean was calculated per year. Beyond that 30m circle land-use could not be assigned for certain. The authors for instance don't discriminate here between fallows and grassland anymore. Grassland was assumed to be used as pasture as indicated in the paper.\n\nLH1 2014/07/28 Altered empty cells to zeroes","Sites that were burned and cleared with pesticides and tractors the year before are marked as young secondary. All others are mature secondary.\nSH1 15/07/2014 Sampling method of 'point counts' does not validate with unit of 'plots' so have changed metric to 'visits' (as this fits with the measure of effort being 2 as entered by MJ).","","Coordinates given in RT90 coordinates system. Conversion code included into the study folder.","SC1 18/2/2014 Checked blocking structure and it is correct, no blocks present.","","","Sampling sites georeferenced using Google Earth, Gazetteers and Sabah Conservation Areas and Monitoring System(http://www.sabah.gov.my/htan_caims/Level%201%20frame%20pgs/index_main_fr.htm). \nThe oil palm site has been georeferenced using the indication given by the author (the accurancy of this site is very low due to the lack of precise information).","Maximun linear extent is 22.5 km , as the survey was conducted in three 7.5 km diameter study areas.","","","RESTRICTION on coordinates: IMPORTANT: Please DO NOT publish this data in its raw form, but coarsen the coordinates to the nearest km (they are currently at the metre resolution) before publishing it any sort of public repository. Also, make sure that any non-numeric identifiers are removed from the data which could be used to identify the private landowners on whose land this data was found, and whom I promised would never be identified. \n\nSC1 25/2/2015 Land use was assessed using the shapefile provided by the author and assesses using Google Earth. The KML file has been saved in the Formatted Data folder.","Coordiantes converted from UTM to decimal degrees using the EPSG:31370 Belge 1972 / Belgian Lambert 72 conversion system.\n\"Sampling was performed in three different areas in the city. The first set of sites were situated in the Soignes forest\n(4383 ha). This is the largest area of forest in the northern part of Belgium accounting for 60% of the Brussels public green\nareas. The second set were in the southeast of Brussels, the relics of Soignes, also with old trees that, prior to its definitive\nprotection (since 1842), were part of large private estates and were later incorporated into prosperous neighbourhoods of\nvillas or large forested parks. The third set of sites were in the northwest (Jette) of the city, and originates fromafforestation\nin the 18th century of old calcareous limestone quarries. In total we investigated 13 sites that differed in degree of\nurbanization (Fig. 1). The percentage of urbanization (Table 1) was objectively calculated for each site and as such used\nin the analyses (see urbanization measurements).","SC1 11/8/2014 Coordinates used were set on the center of the island, with estimated precison of 12000metres, as precise coordinates of sampling sites were not provided in the article. Coordiantes for the prison site were found on Google earth and the estiamted precision set to 1km.\nPredominant habitat: the predominant habitat associated to the Prison's sites has been assessed as Secondary interdetminate age, as the prison has been abandoned and the use intesity is light.","Maximum linear extent sampled: calculated as the sum of the 8 plots(10m) sampled along the transect plus the distance between plots (50m) and the disantce to the edge (20m), which is equal to 145m. \nCoordinates converted from UTM to Decimal Degrees usign the R code saved into the study folder.","SC1 13/10/2014 Use intensity for this study has been saved,as indicated by the auhtor, with the distance to villages (this has been saved in the Known Threat 1 section in the excel file, with the distance calculated as the minutes from the plot to the village).","The dataset has been published on two different papers:\nSyrphids data on: Contrasting resource-dependent responses of hoverfly richness and density to landscape structure, 2009, Basic and Applied Ecology\nBees data: Linking life history traits to pollinator loss in fragmented calcareous grasslands, 2013, Landscape Ecology. SC1 19/11/2013 added zeros to empty cells \nSC1 19/11/2013 Checked blocking structure and it is correct, no blocks present.\nAD1 10/06/2015 Changed sampling target to entire community rather than certain species (All apid species were sampled not just a select list of targeted species)","SC1 19/2/2014 Removed habitat patch area values as they were the Old size area values.\nSC1 19/2/2014 Checked blocking structure and it is correct, no blocks present.","SC 17/12/2013 Correct diversity metrics\nSC 17/12/2013 Added Endnote reference number\nLH 2013/12/19 Changed 'Abundance metric type' to 'presence/absence' and converted non-zero values to 1, after discussion with the group.\nSC1 19/2/2014 Added maximun linear extent sampled, as for each forest site a plot of 100x150 m was surveyed. COuldn't add Habitat patch size as this is not given in the text.","The study has been divided in two different studies, one with biodiversity data of species collected on trees and the other one about species collected on rocks.","The dataset was used in Charles Marsh Master Thesis, the protocol followed in the study is explained in the excel files the author sent us.\nThe datasets has been splitted in two studies for difference in the methology used to survey butterflies and birds.","","","Maximun linear extent: calculated assuming that the 0.8 hectars plot have a square shape. So the diagonal of the square has been calculated to be 126m.","","Habitat patch area: for the forest fragments is given as the avarage between the 1.5 to 20 hectar size given in the paper.","","Author was not able to provide precise coordinates for the study sites as he only has the coordinates of the National Park (Research was carried out in Bu Gia Map National Park, Binh Phuoc province, Vietnam (12 08 ,12 17 North and 107 03, 107 14 East). He also sent photos of the different habitat types but I was not able to use that to georeference the study sites.","Percentage cover was taken from the tables prepared by Dominic Bennet.\nPredominant habitat was assessed using the description given in the papaer by the auhtor according to the PREDICTS definition.\nThe data source has been divided in 3 studies due to the differnece in sampling effort (size of the plots were 5x5, 3x3, 2x2).","Endnote accession number: ZOOREC:ZOOR14909037450\nThe data has been treated as presence/absence.\nUse intensity has been assessed according to the auhtor description \" The wildlife reserves are fully protected areas and wildlife protection is enforced by the Ghana Wildlife Division. Absolutely no human activity is permitted in them. Trespassers are prosecuted by law when arrested. The only human activity permitted in wildlife reserves are official research and some level of low impact tourism. Over the years, our wildlife reserves have benefited from several conservation-oriented projects, where research and law enforcement have increased and patrol staff trained and equipped with modern monitoring and research tools.\n\nOn the other hand, the forest reserves are managed by the Ghana Forestry Division, which does not focus on conserving wildlife. Management priorities are directed at sustaining logging regimes. Forest reserves have not benefited from any major wildlife conservation-related projects and human pressure including hunting and illegal logging from fringe communities is high. Hunting pressure has severely affected wildlife populations, including several large mammals. \" (email Sent: 31 October 2014 07:06\nTo: Sara Contu).","In this study they looked at \"stands partially disturbed by anthropogenic or natural disturbances in the past 10 years (1998-2008) were examined. Two experimental partial harvesting treatments were included in this study: \"succession cuts\" (SC) and \"diameter limit cuts\" (DL). The primary difference between the harvesting treat ments was a greater removal of stems in the DL treatment than in the SC treatment.The primary difference between the harvesting treat ments was a greater removal of stems in the DL treatment than in the SC treatment.\"\nIn 2008, sampling was conducted in three 20m long x 6m wide strip plots established in all stands (three partially harvested stands of each treatment and three naturally disturbed stands).\nSC1 8/9/2014 the data used for biodiversity composition for this study is the one of the table \"Tree BA live\" sent by the author. I used this table as the others also count dead stem of tree, but I only wanted the composition of the live trees.","They surveyed 20 farms. 3 different fields in each farm. Each field 10 times (5 quadrats on a transect within 1 meter from the edge, the other 5 quadrats on a transect within 25 m from the edge). We have pooled the data of each 5 quadrats together (please see the code and csv file saved into the dropbox study folder), and calculated as the average of the percentage cover of the quadrats.\n\nSC1 10/3/2014 Added maximum linear extent sampled: 100 m, as each transect was 100 m long. Also added habitat patch size as it is given in the text as mean of the organic field size and mean of the conventional field size.","SH curation: changed abundance metric type from 'Occurrence' to 'Abundance' as this more acurately reflects the data. 14.11.13\nSC1 19/2/2014 Checked blocking structure and it is correct, no blocks present. Maximum linear extent and habitat patch area couldn't be determined.","","Site description: La Dehesa is a relatively new residential zone (less than\n30 years old) composed mainly of low density housing, parks, golf courses and forest\nfragments embedded in the urban landscape. The rural landscape is mainly composed of\nremnant fragments located in hill tops and riparian areas immersed in a shrub matrix\ndegraded by historical clearance for timber, charcoal and pastures.","","I added the reference manually into Endnote, so the record doesn't have a WOS reference number (the paper was not known by WOS, hence i entered it manually).","","The study is associated to the Chapter 2 of the PhD thesis sent by the author.\nThe predominant habitat has been assessed using the classification given by the author and the use of Google Earth.","SC1 07/07/2014 Data has been reported as: two transects for the forest habitat (one 'near' the edge as 0-50 m into the forest; one 'far' from the edge as 50-100m form the edge) and two transects for the other habitat type (one 'near' the edge as 0-50 m into the forest; one 'far' from the edge as 50-100m form the edge. These four sites have the same set of coordinates.","Coordinates: assessed using the map published on the journal article (Fig 1 Page 53).\nMultile sampling methods were used in this study (they pooled the complementary captures from the different methods and strata for all analyses):\na) Ground hand sampling ('looking down' of Coddington\net al. 1991): two experienced persons sampled for one\nhour at night with headlights, exploring all structures\nbelow knee level, resulting in one sample per person, two\nsamples per site.\nb) Aerial hand sampling ('looking up' of Coddington et al.\n1991): one person sampled for one hour at night,\nexploring all structures from knee height upwards to\noverhead arm's reach; i.e., lower vegetation, resulting in 1\nsample per site.\nc) Beating: Three persons striking vegetation at any\nreachable level (i.e., lower vegetation) with a stick,\ncollecting the spiders falling on a 50 x 50-cm tray held\nbelow, for one hour. Twenty beating points made one\nsample. Depending on the person sampling, a different\nnumber of samples per site (3-9) resulted.\nd) Pitfall trapping: Ten traps per site were installed to\ncapture active ground spiders for one week, usually\nresulting in 10 samples per site, with a few failures. Traps\nwere 330 ml PE cups with an opening diameter of 7.5 cm,\nfilled with 100 ml of 4% formaldehyde solution and\nprotected against rain by transparent plastic plates.","Habitat type has been described as primary forest for all the sites. The use intensity has been assessed following the description given by the author: continuous forest as minimal use and the fragments as light use due to selective logging.\nThe data has been pulled together to make it comparable between sites. Details are in the study Compiler's comments.","11/12/2013 SH1 V7 forms. Changed study target from 'certain species' to 'entire community' as I think this more accurately reflects the sampling. Added linear extent. Added blocks. Removed habitat patch size as not provided in paper. Changed predominant habitat from 'primary non-forest' to 'pasture' and use intensity from 'light' to 'minimal' for grazed sites.","11/12/2013 SH1 V7 forms. Added linear extent. Changed diversity metric unit from 'individuals/unit effort' to 'individuals' as data refers to total num of indiv summed over 2 years of sampling. Checked blocks. Checked habitat patch size and is correct. Added sample effort value of '1'. Changed study target from 'certain species' to 'entire community' as I think that more accurately reflects sampling.","SH1 15/01/2014 Curation. V7 forms. Changed most of the data in the excel spreadsheet. SC2 had entered data as two sites, one high use and one low use. Asked AP and he advised to enter in the format which I have now entered: 9 sites - 3 per sampling area with three blocks. Therefore have altered habitat, use intensity (from AP's suggestions and looking at Table 2 in the paper), fragmentation layout, species list, number of species, abundance metric, coordinates (obtained new coordinates from author), coordinate precision (note that as author has provided coordinates for the midpoints of the sampling blocks, the precision is entered as half of the length of the trail), sample effort and blocking structure. Habitat patch size not possible to ascertain.","","1. Sampling effort unit is trees, not site. 2. Awaiting actual sampling dates from author.\n11/12/2013 SH1 V7 forms. added linear extent. Changed study target from 'certain species' to 'entire community'. Note that data comes from author's PhD dataset and includes more sites and species than listed in Giordani 2012. Changed sampling effort unit from 'site' to 'plot' as I thought it would be less confusing. Is not enough information to assess blocking structure. Changed abundance metric unit from 'individuals/unit effort' to 'effort-corrected individuals' with 'effort-corrected abundance'. Not enough info to establish fragmentation. Note that it is unclear how Sylvester established the use intensity - may require investigation.\nSH1 20.05.14 changed predominant habitat of olive groves from cropland to plantation. Emailed author with questions regarding landuse. Author reports that all forest is secondary. If woodland habitat with a \"non-forestal\" management (see data from author) then author reports that this refers to an area that has been cleared of all vegetation in the past. Have entered these sites as Young Secondary with Minimal use. Rural areas (non-forested) refer to cropland. Aged coppicewood means that coppicing no longer occurs. If site has coppicing have selected Light intensity, otherwise have entered as minimal. Not enough info to judge use intensity of cropland or olive groves (plantation), so have changed all to Cannot Decide. Use intensity of urban sites judged using google maps.","","SH1 21/01/2014 V7 forms. Data was entered as four sites in the national park and four sites in the farm, all with the same coordinates. Have emailed the author and have coordinates for each sampling location, so have changed the data into 23 sites. Samples were entered by SC as accurate to 1 minute, but as author has provided UTM, have changed to 1m. Changed unit of effort from 1 site to 1 trap. Linear extent is the size of the pitfall trap, as unknown, have estimated as 1m. Changed habitat patch size to 6300 ha for sites within the park, and 1000 ha for sites in the farm. SC had entered the park habitat as 'Primary forest' but as the paper refers to 'open grasslands with scattered trees' have changed it to 'Primary non-forest'. SC had entered the use intensity of the sheep farm as 'light' but have changed it to minimal as the paper mentions that the stock density in the farm is low and not enough to change the vegetation structure. Added fragmentation layout through plotting the coordinates on google maps. Added blocking structure. Changed species abundances to those per trap. Changed abundance metric unit from 'individuals/unit effort' to 'individuals'. Changed study target from 'certain species' to 'entire community'.","SH1 22/01/2014 V7 forms curation. After consultation with TN and AP, changed Predominant Habitat from 'Mature Secondary Vegetation' to 'Primary'. If the area had been cleared within one year of the first sampling date (see spr.age in 'database_birds') then classified as 'Light' use intensity as ongoing impacts, if one year or more, then classified as minimal use. Linear extent is not provided (site is a point count of bird song). Habitat patch size not provided. Blocking structure not provided. Changed abundance metric unit from 'individuals/unit effort' to 'individuals' as unit effort is just one site.","Trait data available in dropbox folder.\nSH1 22/01/2014 V7 forms curation. See discussion on google groups - have changed predominant habitat from 'Mature Secondary Vegetation' to 'Primary forest'. Use intensity according to age since understorey last cleared - under 1 year is light use, 1 year or more is minimal use (see 'spr_age' in 'database_butterflies' in data provided by author folder). Removed habitat patch area measure (all rows were entered as 1km) as not provided in paper. Changed fragmentation layout from cannot decide to 'Well within unfragmented habitat' as per author's description. Blocking structure not provided. Added linear extent. Changed sample effort from plot with blank value to 5 visits. Changed abundance metric unit from 'individuals/plot' to 'individuals'. Changed study target from 'certain species' to 'entire community'.","","18/12/13 SH1 V7 forms. Added linear extent. Added blocks. Added study target. Added fragmentation layout. Changed diversity metric and unit from 'abundance' with 'colonies per substrate' to 'group abundance' with 'number of groups'.\n\n27/01/2014 SE1 V7 forms. Changed habitat predominant habitat from \"Cropland\" to \"Plantation\" (From coffee crops to coffee plantations)","http://revistas.javeriana.edu.co/index.php/scientarium/article/view/4873","","AD1 10/06/2015 Sample target field filled in","SH1 16/01/2014. Curation V7 forms. The predominant habitat within site '0 years' was recorded as primary, but I think this was a typo and have changd to young secondary. Fragmentation layout is correctly entered as 'cannot decide' as not enough information to tell layout. No blocking structure. Added study target, linear extent and habitat patch size.","SH1 16/01/2014 V7 forms. Checked linear distance and not possible to ascertain. No blocking structure. Habitat patch size not provided in paper. Added fragmentation layout and sampling target.","This study was based on Mixed birds flocks observations (MBF). The data reported or the abundance metric is times of the species was found in each MBF per Site.\nSH1 16/01/2014 V7 forms curation. Added study target. Added linear extent (paper states 2-3km, so entered as 2500m). Added fragmentation layout. Habitat patch size not provided in paper. No blocking structure.","SH1 21/01/2014 V7 forms. Added habitat patch size and fragmentation layout. Linear extent not possible to determine as paper states that 2 transects 50m in length were placed in each of three habitats (all three habitats compose one site), but no information is given as to how far apart the habitats are. Changed permission from 'uncertain' to full permission granted as per Insightly data.","<Go to ISI>://CABI:20123039204","The author request to have a restriction in publication of the location of the species \"Cistothorus apolinari\" due to its endangered status and attraction to tourists.\nhttp://www.bdigital.unal.edu.co/5356/\nSH1 22/01/2014 V7 forms. Blocking structure not present. Linear extent not provided (point count samples at varying number of locations around the site - possibly could calculate an estimate based upon the size of the site?). Changed diversity metric from 'abundance' with 'individuals' to 'occurrence' with 'presence/absence' as only presence/absence data has been provided. Added study target. Added fragmentation layout.","The coordinates don't overlap the map provided by the author. Therefore, I checked every single coordinate and I can confirmed that the coordinates are more precise than the map. \nTHE BLOCK FIELD HAS BEEN CURATED.\nSH1 21/01/2014 V7 forms. Changed data use permission from 'uncertain' to 'full permission granted' as per Insightly. Added linear extent, patch size not possible to ascertain.\n\n27/01/2014 V7 forms. Changed predominant habitat from \"Plantations\" to \"cropland\" (Sugar cane crops).","The first 7 geographical points provided by the author are not congruent with the locations in google maps. Ask again for the points or determine the correct points.\nSH1 21.01.14 V7 forms. Added blocks.\n27/01/2014 SE1. The author was asked to provide the coordinates of the points MF, 1y, 18y, 23y, 42y, 30y, MF and PR. He replied that the locations are 200m separated and the GPS resolution was low. I changed then the coordinates of these locations geo-referencing the map in the paper and google earth. \nSE1 24.04.14. Changed abundance metric unit in study 2. From individuals to presence/absence","","SH1 22/01/2012 V7 forms. Added linear extent. No blocking structure. No gradient in site predominant habitats or use intensities. After discussion with HP left fragmentation layout as Cannot decide. Unsure as the site is such as small area (20x12m) so should we ignore site when considering layout? Left as cannot decide for now. Added study target. Added location precision.","","http://www.scielo.sa.cr/scielo.php?pid=S0034-77442013000300019&script=sci_arttext","","Coordinates were given for each transect (there were 2 transects at each site). So I averaged the coordinates to get coordinates for each site. However, for one of the sites (Shivgange) the averaged coordinates was on a building in the middle of the coffee plantation so it was moved a few metres so it was on plantation to avoid misrepresenting the habitat.","","","","","Grey-crested Tit (GCTI) and Grey-headed Bullfinch (GHBF) had the same species name (Pyrrhula erythaca), found that Grey-crested Tit should be Lophophanes dichrous.\nLemon-rumped Warbler (LRUW) and Palla's Leaf Warbler (PALW) had the same species name (Phylloscopus proregulus), found that Lemon-rumped Warbler should be Phylloscopus chloronotus.","Three studies were made as there were three different types of baited pitfall traps used: \n1) Soil surface pitfall traps = 4 cm diameter plastic containers (80 ml vol.) which had their openings leveled off with the soil surface\n2) Subsoil pitfall traps = closed plastic containers (250 ml vol.) - with four 1 cm holes made in the side - that were buried to a depth of 20 cm\n3) Tree canopy baited pitfall traps = eight traps (4 cm diameter plastic containers) were fixed in the branches of each tree with masking tape.\n\nSite CMG2 classed as Mature secondary vegetation as it \"was a farm (30 years ago) but is now fully recovered\".\n\nSites PGO1, PGO2, PMG1, PMG2 were referred to as \"cultivated pasture\" in the paper, however, no grazing was mentioned and the area was planted with grass species so I classed it as cropland.","","Due to inconsistensies between the paper and the data the author sent (numbers of individuals were not the same in the paper and author's data) presence/absence was calculated from the author's data.\n\nThe coordinates for each site are the coordinates for the start of the transect and the end coordinates are given in the \"For details of documented line transect census\" column in the excel sheet.","","Data from an unpublished paper under review - the author sent the manuscript see file \"6. Edge effects paper.docx\"","In each site the 90 small mammal traps were set for 4 consecutive nights.","Data use permission - not needed as all data was in supplementary materials of the paper","SH1 17.05.15 transferred data from the old forms automatically generated from Jake's database. Each sampling point is a single tree. Max linear extent estimated to be 10m as approximate size of tree. Predominant habitat - primary forest within national park entered as primary forest with minimal use intensity. Others are secondary with age corresponding to age provided by author - 5 years is young, 15 years is intermediate, 40 years is mature. No information on use intensity within secondary habitat. Author specifies that the secondary are patches close together surrounded by mature forest therefore have entered all as within unfragmented habitat.","SH1 14.05.15. Have copied data from old (version 6 forms). Max linear distance based on 10m x 10m survey. Coordinates provided by author in old Australian grid UTM (AGD66) - have converted using R, code and converted coordinate files stored in project folder. Plantation forest use intensities - monoculture timber plantations therefore light or intense, then selected light or intense categories based on age of plantation (under 20y = intense), also read description in text and in data provided by author and text descriptions tally with these categories based on age. Primary forest vs secondary forest description provided by author. Author states that has been at least 50y since cut for secondary, so intermediate secondary unless author specifies as 'old regrowth' - these are entered as mature secondary.","all data downloaded from http://www.cifor.org/mla/action.asp?frmref=search/searchDB.htm&searchType=home on 18.09.13\nUTM coordinates converted using spreadsheet provided by http://www.uwgb.edu/dutchs/usefuldata/howuseexcel.htm locations were then checked using Google Map and map provided in paper. Predominant habitat was taken from \"PlotList\".\nFor calculation of use intensity see the current use checkboxes provided in the \"Site description\" table in the database \"MLA_Malinau_final_29July05\". If 'cut stems' checked then entered as 'Light use'. Also if text description of \"PlotList\" mentioned vegetation removal or modification of site then entered as either Light or Intense (depending on description).\n\nSH1 27/11/2013 placed into V7 forms. Checked blocking structure and blocks not present. Added linear extent and checked habitat patch size. Checked 'cannot decides' in use intensity and is correct.\n\nSH1 28/05/2014 Checked urban site against new definition and changed from Urban to Young Secondary (site 62 - fruit garden was abandoned 5 y previous to study).","","12/11/2013 LH1 Renamed from MG1_2005__OConnor\n12/11/2013 LH1 Changed empty site by species cells to zeroes\n20/11/2013 SH1 changed abundance metric unit from 'percentage' to 'percent'. Added linear extent measures, habitat patch sizes, blocking structure and years since conversion. Also added use intensity when 'cannot decide' had been selected.","SH1 22.05.15 Methodology published in Vu 2009 Diversity and similarity of butterfly communities in fivedifferent habitat types at Tam Dao National Park, Vietnam. J. Zool. 277. See author's emails for description of habitat plus description in paper. Data from author in 80 seperate excel spreadsheets. Abundance data summed for each transect over season. Transects are 100m, effort reflects uneven number of transect replications.","Abundances were derived from bar graphs. 25-06-2013 - Updated by HP1\nSH curation - endnote reference, author address, locations of data, study target - fields entered in PDF 28.08.13 \nSH curation - Habitat and fragmentation fields changed in Excel spreadsheet 28.08.13\nSH1 20/11/2013 curated cropland use intensity fields as were 'cannot decide' previously, also double checked blocking structure and is ok. Entered linear distance and new area measurements.","","","Data taken from online database at http://www.cifor.org/mla/_ref/method/index.htm. Year of publication refers to date the database was downloaded. See also \"exploring_bio.pdf\" for details of sampling methodology (report details methodology for Indonesia but same methodology was employed in Cameroon - see \"CIFOR about MLA\" chrome file). Data is zipped into Cameroon.zip file. Note that hunting threat was entered if was recorded to occur 'often' or 'very often'. Also note that the short site description (as provided for the sampling undertaken in 2003 - the first 35 sites) does not always match the long description provided in the Access database, when uncertain the Access database was taken as correct. Note that the abundance measures for plants other than trees refer to the occurence of the species within each of 10 cells. Data was manipulated using R (\"R script for CIFOR indonesian data.R\")\n\n12/11/2013 LH1 Changed empty site by species cells to zeroes\n\nSH1 27/11/2013 Checked blocking structure and use intensity and all correct. Added linear extent and checked patch size (not provided in paper).","Data taken from online database at http://www.cifor.org/mla/_ref/method/index.htm. Year of publication refers to date the database was downloaded. See also \"MLA Palawan.pdf\" and \"exploring_bio.pdf\" for details of sampling methodology. Data is zipped into Philippines.zip file. Note that the abundance measures actually refer to the occurence of the species within each of 8 cells for tree species and 10 cells for all other plants.\n\nSH1 20/11/2013 changed abundance metric type from 'individuals' to 'number of plots' and changed data use permitted from 'uncertain' to 'Other - see notes for details'\n\nSH1 27/11/2013 Checked blocking structure and use intensity and all correct. Added linear extent and checked patch size (not provided in paper).","","SH1 The data provided by the author has not been published, but this publication describes the sampling methodology and the landscape where the sampling was undertaken. Study 1 refers to data saved as 'Biodiversity and Ecological long-term plots in Southern Patagonia (PEBAN....xls' and description of Santa Cruz study in publication. Plot size of 20x50m, therefore max linear extent of 54m. Note that the abundance measures are %cover, but the author included rock and bare earth in the total %, therefore the numbers do not total 100%. Author provides grazing density of 0-3, where 0 is ungrazed (to the author's knowledge this has not been historically grazed - at least not for the last 50y - some sampling locations fall within protected areas), 1 is light stocking density, 2 is medium and 3 is high. Have entered 0 grazing as Primary with Minimal use intensity, 1 as Pasture with Minimal use intensity, and 2 and 3 as Pasture with Light use intensity. Study 2 refers to data saved as 'Biodiversity and Ecological long-term plots in Southern Patagonia (PEBANPA network)_TDF1_(Mar\u00eda Vanessa Lencinas).xls' and description of Tierra del Fuego study in publication. Lat/Long entered as -xxxxxx.xxxx/-xxxxxx.xxxx . This refers to degdegminminsecsec.secsecsecsec. (Plotted on Google Earth and compared to maps in publication to make sure). Predominant habitat: if 0 grazing then recorded as Primary, if harvesting 0 then minimal use, if harvesting 1 then light use. If 1 grazing then recorded as Pasture with minimal use unless harvesting is 1 or 2 then light use. If 2 grazing then recorded as Pasture with Light use. Replaced blank cells with zeros in species abundance table. Linear distance - assumed plot size of 50x10m.","This data arises from two papers by the same authors within the same journal. \"Complementarity of indigenous flora in shrublands and grasslands in a New Zealand dryland landscape\" is plant data and is entered as study 1. \"Effects of secondary shrublands on bird, lizard and invertebrate faunas in a dryland landscape\" refers to studies 2 and 3 (bird and invert respectively). Study 1 - sampling technique measures presence of each species within each sampling point and takes proportion over sampling area, however, samples also extend vertically (in 10cm boxes) up to maximum height of vegetation so if plant occurs in more than one vertical box then proportion will exceed 100%! Those listed as <1 were entered as 1.\n\nDid not enter intermediate sites as unclear how would be classified in our land use scheme. Classified grassland as pasture (as specifies that area has been grazed since 1850's) and shrubland as Secondary Intermediate (paper specifies that shrubland vegetation arose through secondary succesion over the last 30 to 70 years).","SH1 08.06.15 Data was originally stored in WCMC database - data transferred over using Tim's code to V6 forms. Have copied onto V7 forms. Coordinates georeferenced using Google maps and a map provided by the author apart from plantation sites. These were located on Google maps through description of sampling site provided in text of paper and in email from author. However, high level of uncertainty around coordinates so have entered 5km precision estimate. Paper gives proportional abundance num(spx)/num(all). Have multiplied by 100 to give percentages. Max linear extent calculation: 10 transects up to 15m apart = 135 wide, and 100m long, diagonal is 168m.","SH1 04.06.15 Data was in WCMC database, transferred to V6 forms using Tim's code. I have copied into V7 forms. Coordinates obtained using google maps and Figure 1. Abundance data from Appendix. Max linear extent: 5 parallel transects of 2km each with all birds within 30m recorded, does not give distance between transects so have estimated 2500m for max linear extent.","Access ID [41]\n\nSH1 10.12.13 V7 forms. Checked and no blocks. Added linear extent - 6ha sampling shown as rectangle in map, approximated 300m x 200m, therefore 360m diagonal. No info on patch size provided.","18.06.15 data was in Jake Simpson's database, transferred to V6 forms using code written by Tim. Comment from old database: \"Sampling effort differed among habitatsAccess ID [82]\"\n27.05.15 SH1 data entered as cluster site. Have transferred to V7 forms and have selected the first pair of coordinates for each land use in the cluster form to represent that land use. Coordinates georeferenced by Edwin Pynegar - precision was also estimated by Edwin. Sampling effort unit should be 'trap nights' but this option is not available on the excel form so have entered as 'trap'. Max linear extent: 22 traps with 10m space = 210m","Access ID [90] Curated by SH 27.08.13\n\nSH1 10/12/2013 Diversity metric and unit changed from 'abundance/indivduals per unit effort' to 'effort-corrected abundance/effort-corrected individuals'. Added linear extent. Checked habitat patch size. Added blocks.","Coordinate and abundance data provided by author. Access ID [32]. SH changed predominant habitat as some secondary vegetation was entered following the old nomenclature 04.09.13.\n\nSH1 10.12.2013 V7 forms. Changed diversity metric unit from 'presence' to 'presence/absence' for consistency. Added blocking structure.Added linear extent (the sum of the width of the openings for the three traps used in each site). Added fragmentation layout. Checked empty cells and zeros - is correct as for some reason the author has not provided the vegetation data (see Study 1) for some of the sites. As unknown if was looked for, is correct to leave blank rather than have as zero.","Access ID [34] Curation 14.11.13: data placed in V7 forms. Blanks in site by species matrix replaced by zeros as read through paper and could see no reason why species could not have been recorded at all sites as sampling was identical. SH\n\nSH1 10.12.13 No blocks. Added linear extent, checked patch size. Added use intensity where possible.","25th July 2013 - HP1 Data curation. HP1 - 19/02/2015 - To allow input into the database, a single site within each cluster was used for coordinates.","Access ID [75] Curated by SH 27.08.13 Abundance and coordinate data provided by author. SH 04.09.13 changed predominant habitat as the secondary habitat had been entered using the old nomenclature.\n12/11/2013 LH1 Changed empty cells on site by species matrix to zeroes.\nSH1 11/12/2013 V7 forms. Added linear extent. Changed 'cannot decides' in predominant habitat as per descriptions in paper. Added blocks. Removed habitat patch area as not provided in paper.","Access ID [62] \nSH1 10/12/13 V7 forms. Added linear extent. Added blocks using map provided in paper (appears that all mature forest sites are aggregated). Habitat patch sizes not provided. Checked use intensity 'cannot decide' is correct.","Access ID [71] Data taken from Jake Simpson's database and automatically entered onto V6 forms using Tim's code. Curated by SH 27.08.13. The following comment was attached to the data in Jake's database \"Coordinates were quoted as degrees and minutes, but in both cases the minutes were > 60. I assumed that these were decimal degrees.\"\nSH1 26.05.15 Forms were entered as cluster sites on V6 forms. Have copied into V7 forms. As we do not have abundance data for each sample, have selected the first coordinate pair for each land-use type and have entered against the averaged data. Have reflected the distance between sampling points in the Estimated precision for coordinates field. Maximum linear extent was also estimated from distance between sampling points in cluster form.","Access ID [45]\nSH1 10/12/13 V7 forms. Curated blocks (added block for SFORCH). Sampling details are vague, using different numbers (unspecified) of varying sized nets, but approximated 30m of net. Added linear extent, checked habitat patch size. Checked use intensity.","Access ID [46]\n\nSH1 10/12/2013 Changed 'abundance/mean abundance' diversity metric and unit to 'effort-corrected sign abundance/effort-corrected signs' as reflects data better. Added linear extent. Added blocks (see map in Ficetola et al 2008). Corrected habitat patch area (deleted area for pasture as the measure provided in the paper is a sum of all pasture-land in the area and does not give the area of the individual pastures sampled). Checked use intensity 'cannot decide' and is ok. Added species status (native).","SH1 29.04.15 Data was originally taken from paper and entered into spreadsheets without coordinates and without predominant habitats etc. Therefore have started again. Author has provided coordinates and data on number of colonies encountered on every sampling trip. Have calculated the mean number of colonies encountered per km of transect to produce a single abundance measure for the year. Peters reports that selective logging has occurred in the past 20y within the primary forest and provides the number of trees removed (see \"PetersMK_army_ant_data\"). Where >10 trees had been removed in the past 20 years I have classified the use intensity as Light, others Minimal. Author reports at least 100m between transects, and as transects were 500m in length, have calculated linear extent as 510m.","","Co-ordinates converted from UTM. Also note easting/northings reversed for BPC in author's data. \nSampling effort = 3 x soil monoliths per site = 18.75m2","","SPICE programme (PhD thesis -supporting material, Methods pg. 30 onwards). NO BLOCKING\nLH 2013/12/19 Changed 'Abundance metric type' to 'presence/absence' and converted non-zero values to 1, after discussion with the group.\nSC 13/1/2013 Updated Data use permission to: Full permission granted.\nSC 13/1/2013 Updated Indication of high level taxa to Lichen.\nSH 21/05/2014 Checked Urban classification against new guidelines, discussed with TN, no changes required.","NO BLOCKING","SC1 13/1/2013 Updated Date use permitted to Full permission granted\nSC1 13/1/2013 Added DOI to the jounal article\nSC1 13/1/2013 Added Fragmentation layout categories","NO BLOCKING\nSC1 13/1/2013 Check blocking structure and it is ok.","SC1 13/1/2013 Chnaged the Source ID name form VK1_2009__Dynesius to VK1_2009__Strom\nSC1 13/1/2013 Changed Data use permitted to Full permission granted\nSC1 13/1/2013 Added Fragmetation layout categories","NO BLOCKING. Would like to contribute. Conditions agrred to: \n1) co-author Dr. Grzegorz Mikusinsk; \n2) Chance to input to data paper (vk response - have the chance to see draft before publication + receive quarterly newsletters to monitor direction of project.\nSC1 14/1/2013 Added Endnote Reference Number\nSC1 14/1/2013 Habitat patch area used is the area of the stands given by the author.\nSC1 14/1/2013 Checked bloking structure and it is ok.","SC1 15/1/2013 Added Maximun linear extent sampled\nSC1 15/1/2013 Added Sampled effort\nSC1 15/1/2013 Changed the blocking structure so that now there are 5 blocks and not 3 as Victoria indicated (which were pseudoreplication).","SC1 15/1/2010 Changed source ID from VK1_2011__Hebert to VK1_2011__Legare (Legare is the first author).\nSC1 15/1/2013 Added Fragmentation layout category.","SC1 3/3/2015 I have georeferenced the sampling site for Cramolet area.\nAll data was taken from paper. Victoria didn't manage to get the coordinates for the sampling sites so I used the map provided in the paper but the accuracy is quite low.\nThe study presents a block and cluster design. The cluster sites represent the 4 treatments (clear cut, partial cut with low retention, partial cut with high retention, control uncut) of the 3 sites (F\u00e9n\u00e9lon, Gaudet and Puiseaux), combined together have not been coded up due to the problem linked to the cluster and blocking structure in this study and the problem that would arise when analysing this study.","Coordinates converted from Northing & Easting UTM 16 to Lat & Long using http://www.uwgb.edu/dutchs/usefuldata/ConvertUTMNoO\nSC1 15/1/2013 Corrected diversity metric\nSC1 15/1/2013 Added maximun linear extent sampled (calculated from the block grid size 60x60m).\nSC1 15/1/2013 Added fragmentation layout","NO BLOCKING\nSC1 15/01/2013 Updated Data use permitted to full permission granted\nSC1 15/01/2013 Corrected diversity metric to Occurrence frequency\nSC1 15/01/2013 Added maximun linear extent sampled (based on plot size 20x50m)","SC1 16/1/2013 Added Maximun linear extent sampled (One 66 m long transect was set up per site).\nSC1 16/1/2013 Added habitat patch area (the selected forests ranged in size from 35 to 130 ha, mean = 74 ha)","SC1 16/1/2014 Corrected Diversity metric, as metric type is Occurrence.\nSC1 16/1/2014 Updated Data use permitted to Full permission granted.\nSC1 16/1/2014 Added maximun linear extent sampled (Detection was recorded within a 50 m sampling radius of the point-count center)\nSC1 16/1/2014 Added fragmentation layout category","Online raw database with publicly availbale coarsened site coordinates, available at www.abmi.ca","05/08/2013: AP1 (with help from YP1): Sites are blocked; study tried to reflect whole community; updated fragmentation layout in line with AD1's suggestions.","05/08/2013: AP1 added block structure from paper, study target from paper, coordinate precision (rough estimate), sampling effort (was constant - 100g of soil), indicated higher taxon (from paper); added some of the agricultural fields (from paper). Note: paper includes functional group data in Table 3 (p490).","05/08/2013: AP1 added block structure, coordinate precision, study target - all from paper.\n14.11.13: SH1 changed abundance metric type from 'Abundance' to 'Relative abundance' as this more accurately reflects the data.","05/08/2013: AP1 checked blocks (not blocked), recorded that these are Vascular plants (indicated higher taxon), sample effort and study target. Agreed that fragmentation layout is hard to apply (though it's a fragmented landscape).\n2014-08-22 LH1 Converted empty cells to zeroes.","05/08/2013: AP1 - checked blocks (not blocked; actually anti-blocked but sites argued to be independent),changed LC from Pasture to Intermediate Secondary Vegetation for four sites (grazing exclusion, so not pasture), corrected ages (which were in years before present rather than years before sampling), filled in study target and sample effort.","05/08/2013: AP1 - Added block structure, age of habitat, sampling effort (constant within blocks but not among blocks; the actual sampling effort isn't necessarily accurately recorded by these numbers as numbers reflect a combination of transects and pitfall traps, but the sampling effort remains constant within blocks), study target."],"Publication_data_locations":["","","","Fig 1 (p.472)","Table 2 (p.14-17).","","","","p.791-792, Fig. 1","","Figure 1 (p.59)","","Fig. 1 (p. 374), Methods p. 374-375","","Fig 1 (p.1169), Table 1 (p. 1172)","p.175-176","p.51-52","Methods p.214-215","","Methods (p.699), Fig. 2 (p.700)","p.3271 and Appendix 1 (p. 3283)","p. 755","p.201","","Fig 1 (p. 564), Methods (p. 564-565)","Figure 1 (p.118) and Table 1 (p.119)","p.118","Data provided separately by author","Table 1 (p.4925)","Table 2 and 3 (p. 1211) and supplementary material Figure S1.","","p.260","","Materials and Methods p.6","","","Supplementary material 1 Methods and Supplementary table 1","Fig. 1 (p.214), Table 1. (p.217)","p 1620, table 1","Methods (p.3445-3446).","Methods p.971-972Supplementary Material Table S1 and S2","Methods p.562","","p. 2603 - Methods and Fig. 1","","","","","","Table 1 & 3","Methods p.114","","","","","","data received from author","Figure 2Table 1","Figure 1 - site map\nTable 1 - description of sampling locations\nTable 2 - functional trait data","Figure 1 map of sampling locations\nTable 1 abundance of species","Figure 1 Map of sampling locationsAppendix A species abundance dataTable 2 functional trait data","page 1810-1811 sampling site descriptionsTable 2 abundance dataauthor provided coordinates, saved in file \"Plots Kone.xls\"","Figure 1 map of study location\nTable 1 for abundance data","Table 1: sampling site coordinates\nSupplementary data: abundance and functional guild","Data from author","Table 1 - Site locations\nData sent from author","Table 1\nData sent from author","","p801 - text - site locations\nData from author","Supplementary data","","Site description located in Page 290 - Table 1.","","Information on study sites given on Page 98 - Table 1","","","Location of study sites in Pg 219 - Table 1 of Paper","","","","Study site descriptions are given in Page 19, 20 and 22 of the thesis","","","Within the publication - map of study site available in Suppinfo_AppendixS1.doc","Table A1 (page 1925)","Table 2 (p. 832)","Appendix A (p. 44-45)","Table 1 (p. 396)\nFigure 2 (p. 396)","Table S1 and S2 (supporting information)","Table 1 (p. 1042)","","Table 1 (p. 990)\nTable 2 (p. 991)","Table 3 (p. 357-358)","Table 1 (p. 174)\nTable A1 (p. 175)","Table 1 (p. 217)\nFigure 2 (p. 218)","","","","","","","","","","","","","","","","","page 820, Table 3","page 114-115, Table 3","","page 221, Table 2","page 854-860, table 6 & 7","page 1121-1122, Table 1","","","","","","","","","","","","","Appendix 1. (p. 340 - 344)","","","","","","","","","Map - Figure 1\nData - Table 1","Map - Figure 1\nAbundance data - Appendix 1","Figure 2.1, page 12Figure 2.32, page 24","Data: Table 1","Table 1, page 5","Map: Figure 1","GPS coordinates: Material e M\u00e9todosData: Table II","","","","Table 1, page 4\nTable 2, page 5","Data - Table 1","","Map - Fig. 1\nCoordinates - Materials and Methods: Study sites\nData - Table 2","","Table 1, page 45-50","Map - Figura 1","","Taxa from Table 1, p 283. Site by species matrix in Table 2, p 284.","","Map: Fig. 1, page 2\nData: Table 1, page 5","","GPS Coordinates - \"\u00c1rea de estudio\"Data - Tabla 2","Table 1, 3","","Table 1, page 5","Figure 1, page 33Table 2, page 36Table 3, page 38","GPS Coordinates: Material & Methods - Study sites\nData: Table 1","Map: Figure 1","Table 1, page 4\nAppendix 1","Table 1 - GPS coordinates and patch size\nAppendix 2 - Data","Map - Figure 1Data - Table 1","Map: Figure 1, Page 2","Map - Figure 1\nSampling methodology data - Table 1\nData - Table 2","Map - Figure 1Data - Table 3","Figure 1, page 3\nTable 1, page 5","Map - Figure 1","Coordinates - Figura 1\nData - Tabla 1","","Map: Figure 1","Map - Figure S1\nData - Table S1","Coordinates - Table 1\nAbundance - Table 2","Data: Table 1, page 5","Data - Table 1\nGPS Coordinates - 2.1 Experimental Area text","","Table 1Text","Figure 1 = Page 3Table 1 = Page 5Table 2 = Page 6Table 3 and Figure 2 = Page 7Table 4 = Page 8Figure 3 = Page 9","Figure 1 = Page 2Figure 2 and Table 1 = Page 4Figure 3 and 4 = Page 5Figure 5 = Page 6","Figure 1 = Page 5\nTable 1 = Page 8\nTable 2 = Pages 9-11\nFigure 2 and 3 = Page 12\nTable 3 and Figure 4 = Page 13\nTable 4 and Figure 5 = Page 14\nTable 6 = Page 16-18","Figure 1 = Page 3Table 1 = Page 4Figure 2 = Page 4Figure 3 = Page 5Table 2 = Page 6Figure 4 = Page 7Figure 5 = Page 8","Table 1 = Page 2\nFigure 1 = Page 3","Table 1 = page 3\nFigure 1 = page 4","Table 1 = Pages 3 - 5Figure 1 = Page 6Figures 2 and 3 = Page 7Figures 4 and 5 = Page 8Table 2 and Figure 6 = Page 9Figure 7 = Page 10","Figure 1 = Page 3Figure 2 = page 4Table 1 = page 5Figure 3 = page 5Figure 4 = page 6Table A1 = page 7","Figure 1 = Page 3\nFigure 2 = Page 4\nTable 1 = Page 4\nTable 2 = Page 4\nFigure 3 = Page 5","Figure 1 = Page 4Figure 2 = Page 5Table 1 = page 6Figure 3 = Page 6","","","","pp 316-317, Table 2 abundance data","p 302, Figure 1 map of study sitesp 312 Appendix I abundance data","p351 figure 1 map of sampling sites\np352 Table 1 abundance data and foraging strategy data\np358 Appendix II body mass and body length data","p476 Table 1 sampling site characteristics \np476 Figure 1 map\nTable SI abundance data (file: BTP_499_sm_suppltables1s2)","","p16 Figure 1 map of sites Appendix S1 abundance data (file: \"Vu 2009 supp info\")","Text and map","Provided dataAppendix","Figure 1Table 1Table 2Acquired data","","Provided data","Figure 1\nTable 1\nTable 2","Table 1Table 3","","","Acquired data","","Acquired data","Acquired data","","Acquired files","","Figure 1Table 1Acquired data","","Text\nTable 1\nFig 1","Acquired data","Acquired data","Acquired data","Table 1, Map","TextAcquired data","Figure 1Supplemental files","Figure 1.\nAcquired data","Data from author","Acquired data","Email from author, data from authors.","Table 1Table 2","Acquired GIS files","Acquired dataAppendix","Acquired data","Acquired data","Figure 1Table 2Appendix 1","Table 1Table 4Figure 1","Acquired data","Acquired data","Figure 1Table 2Provided data sheet","","Provided data","","Data tables, and supplementary material","Provided by author, also available online at:\n\nhttp://figshare.com/articles/Riparian_buffer_zone_dung_beetle_conservation_Borneo/928091","Abundance and location data provided separately by author","Abundance data provided by authorLocation data same as Korosi et al. (2012)","Abundance data provided separately by author\nLocations within paper","p. 529 Figure 1 map of study sites\nAbundance and location data provided separately by author","Table 1 co-ordinates of sitesTable 3 abundances","Data provided separately by author","Abundance and location data provided separatly by author","Data provided separately by author","Data provided separately by author","Data provided separately by author","Table 1 Site co-ordinates\nAppendix 6 Abundance data","Data provided separately by author","Data provided separately by author","Data provided separately by author","Abundance data provided separately by authorSwedish grid references in appendix","Abundance data provided separately by authorLocations within paperLocations within paper","Data provided separately by author","Abundance data provided separately by author. \nMap Fig. 1 page 220 (site labels provided by author)","Data provided separately by author","Data provided separately by author","","","","","","Appendix 1","","p255 Figure 1 map of study sitep259 Table 2 abundance data","p2114 Figure 1 map of study site\np2122 Appendix 1 coordinate data, species richness and abundance data","Appendix 1 for abundance data (filename: \"Watling et al. 2009 appendix\")\np468 Figure 1 map of study site","p493 Figure 1 map of sampling sitesp501 Table 3 abundance datap505 Table 5 abundance data","Species data found in Sodhi et al. 2010 appendix. Lat/Long estimated using http://www.satsig.net/maps/lat-long-finder.","p864 Figure 1 map of sampling sites\np865 Table 1 island characteristics\nAppendix (saved as \"Wang et al. 2010 appendix.pdf\") for abundance and trait data","","","","","","","","","Coordinates and sites description: Materials and MethodsAbundance matrix: Table 1","","","","","Table 1, page 5","","","Map of sites: Page 27. Details on sites: page 28, table 2.1, physical characteristics of sites: Table 3.1, page 45. Camera trap sampling effort table 3.2, page 52. Relative abundance index of leopards and prey: table 3.5, page 54.","Page 4 (Fig 1), aquired data","Map of sites on page 2. Site locations EndoEtAl2010Biotropica-tableS1.doc. Adundance data in EndoEtAl2010Biotropica-tableS2.pdf.","Map page 2, methods page 1 and 3, kilometric indices page 3 and 4","","Table 1 p 3455, Table 2 p 3457, Appendix 1 p 3465.","Appendix p16.","Table 1 p 263","Table A1. p236","Table 2 p187","","","","Table 2 p1578","","Table 1 p162, Table 3 p166.","","Table 2 p 72","","Acquired from author","Acquired from CATIE","Acquired data\np.5 Figure 1 map of study site\np.7 Table 1 presence/absence data","Acquired from author\np.401 map of study site","Acquired from author","Figure 1, Table 2","page 119, Table 1","Page 2 Text","Table 1, Figure 2, Appendix","Fig. 1, Table 1, Appendix 1","Figure 1, Table 1","Figure 1, Table 1","Figure 1, Table 2","Ghana, page 357. Figure 1","Figure 1, Page 1 and 2","Figure 1, Page 172","Page 230 top","","","","","","Map of the sampling sites: Page 969 Fig. 1","","Diagram of study area, Fig 1 site page 63","","","Figure 1 and table 1 on page 2587are respectively 'Sampling locations in and around Brussels' and 'Site description of the 13 sampling locations (plot)'","Table 2 page 486: Species abundance table.","","","","","","","","","","","","Fig 1 on page 196: Map of the study area","","Table 1: Species list and abundance of butterflies in different habitats, pag 3-5","","","","","","","Fig 1 Page 380 Study area in central Chile\nTable 3 page 383 Smal mammal assemblages in assessed fragments.","","Map of the sampling locations: Page36 Fig. 1 and page 37 Fig. 2","","","","Map of the study area: Figure 1 page 53","","pp. 682-684","pp. 1733-1739\nTable 1\nFigure 2","pp. 384-386","pp. 64-66","pp. 629-631","pp. 808-810","pp. 138-140","pp. 633-636","pp. 15-17","Page 250. Table 1. Relative abundance of the species in each site. Page 253. Table 2. Richness and abundance in each site per sampling method.","","","","","Page 179: Schematic map of sampling sites","Page 163: Figure 1. MapPage 166: Table 2. Epiphyte species biomass in each site","","","","Page 104. Table 3-6: Bird species heard or seen in 19 Sabana de Bogot\u00e1 wetlands in three visits between July 2009 and March 2010, migration status and habits in the area.\n\nPage 23: Map\n\nPage 104: Migratory status, Guilds and habitat preference","","Table 2-3: 2231-33. Abundance data","Abundance information per habitat. Table 1. Page 5.Map of sampling area. Figure1. Page 3.","","Geographic records page 20Habitat description page 21","","","","","","","","","","","Coordinates given - Table 1","","","","Supplementary materials","p548 methodology and study site description.Abundance and coordinate data provided by author (\"AntsEcography_2001.xls\")","p237-239 for landscape description and methodology. Figure 1 map of sampling sites. Author provided abundance data for each sampling site, coordinates and site descriptions.","data downloaded from http://www.cifor.org/mla/action.asp?frmref=search/searchDB.htm&searchType=home","","","Data provided by author is unpublished. Paper describes sampling methodology and landscape.","p.2045 Figure 1 map of study sitesp.2047-48 Table 1 habitat and sampling methodology","species list p4 Table 1, sampling method and site description p2\nOther data provided by author \"Henden_table.xls\"","p9 sampling description, abundances and coordinates provided by author (see Norfolk_et_al_2012_arthropod_data)","see zipped file \"Cameroon.zip\" for database \"MLA_final_web\" also sampling site descriptions \"Cameroon_site_descriptions\". Methodology is outlined in \"exploring_bio.pdf\"","see \"Phillipines.zip\" folder\"MLA_Palawan.pdf\" gives sampling methodology\"MLA Palawan.mdb\" provides abundance data","Figure 1, map of sites, p 662\ndescription of sites p 661","Unpublished data, 2013 paper for methodsStudy 1: Pp74-7 & data from author: \"Biodiversity and Ecological long-term plots in Southern Patagonia.xls\"Study 2: Pp82-3 & data from author: \"Biodiversity ... Southern Patagonia (PEBANPA network....xls\"","Appendix S2 - biodiversity data\nTable 1 - site info\nAppendix S4 - km sampled for birds and number of traps used in analysis for inverts","","","p335 Figure 1 map of study site\np335 text gives coordinates\npp338-339 Table 1 abundance data","p56 Figure 1 map of study site\np59 Table 3 abundance data","p.150 Figure 1 map of sites\np.151 Table 1 site descriptions incl coordinates\np.162 Appendix 1 mean abundance per 100 sampling hours","p75 Figure 1 map of site\nCoordinate and abundance data in \"data from author\" zip archive","p220 Figure 1 map of study site\n\"Castro Luna\" zipped file for coordinates and abundance data","","","p749 Figure 1 map of study site\nAbundance and coordinate data in \"Luja_etal_2008_Biotropica_Raw data\"","p.163 Table 1 abundance data","p215 Figure 1 map of study site\nabundance and coordinate data in \"Abundance data for the individual sites (Bat diversity in the vegetation mosaic around a lowland dipterocarp forest of borneo)_shoko\"","coordinates and abundance data within zipped folder \"Furlani\"","Methods section for description of sampling technique, raw abundance data and coordinates provided by author in file (\"army_ants_2013_PREDICTS_1\"), site descriptions provided in emails.","","","","Data is in Word document \"Data from Pechora Basin, NE European Russia\"","","","BScThesis - Pg. 27 Site map & Pg. 28 site coordinates (although not the ones entered for site locations on PREDICTS excel spreadsheet as their representation is unclear)","","Pg 524. Table 2 \"Mean Abundance bird speciesFunctional trait data --- table Includes GUILD DESIGNATION","","","Map of Study Area Fig 1. page 2081\nAbundance of spiders in partial cut netweork 2087-2091","","","Page 4/15: Table 1 Means, standard errors of means, and minimum and maximum abundance values of the ground beetle species collected in Helsinki and Vantaa (no sites = 12; 4 replicates of 3 treatment types)","","","Hebei Province","Quzhou agricultural experiment station of the China Agricultural University in the North China Plain","Shenyang experimental station of ecology, Northeast China","Lancang, Menglian, and Ximeng counties of Pu\u0090er, Yunnan Province, China","Chongli County in Northern China","Hong Kong"],"Functional_trait_data_filenames":["","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","Richards et al (2011) bee diversity in naturalizing patches of carolinian grasslands in southern ontario canada.pdf","","","","","","Lentini et al 2012.pdf","","","","","","","","","","Basset et al. (2008).pdf (Table 2 in paper) and \"Copy of RawData_Basset.xls\"","","","","","\"Slade & Mann Supplementary Data\"","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","","ecological_data.xlsx","","","Life history traits, in table 1, pag 196. Mean body lenght of carabis species, table 2, pag 198","functional_data.csv","","","ecological_data.xlsx","","","","","Su 2012 What's Under a Plastic Strip Hidden Urban Biodiversity in the Beijing Metropolitan Area.pdf","ecological_data.xlsx","","","","","","","","","","bird species summary daniel ingram.xls","","","","","","","","Milder%2c bird species x traits matrix","","","NeuschulzFarwig_Oikos2011.xlsx","","","","Reid 2012 BITR Natural History Data.csv","","","","","Appendix 1","","","Data on feeding behaviour: Verdu 2007.xlsx (3rd sheet: ecology)","","","","Azpiroz 2009 Trait Data.jpeg ; Trait data label.txt","","Carrijo et al. 2009.xls (sheet 3)","","","","","Bocon 2012 - Data.xlsx","","Castro 2010.xlsx","","Golodets et al 2010.xlsx","","","","","","","","Paper: Table 1","","","Plant Trait Data.pdf","","","","Table 3","","","","","","","","Feeding Groups - Oliveira et al. 2013.xlsx","","","","","","","","","","","","","","","","","","","p352 Table 1 foraging strategy data, p358 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