Explanations to the archived files Title: Spatial variation in human disturbances and their effects on forest structure and biodiversity across an Afromontane Forest See methods section in the paper for complementary descriptions and explanations of column names. R-code for analyses and some figures: Enviromental1.R: Tests for Appendix S1, (based on GeramodelA _Appendex 2_dfs.csv) Enviromental2.R: Tests for Appendix S3, (based on humands.csv) Landscape1.R:  Test for Appendix S2, (based on GeramodelA _Appendex 2_l.csv) Landscape on human disturbance.R: Statistical code for results presented in Table 2 and Figure 3, (based on HDLgradients.csv) Forest structure and biodiveristy.R: Statistical code for results presented in Table 3 and Figure 4, (based on HDLgradients.csv) Tree species compostion and disturbances.R: Statistical code for results presented in Figure 5, (based on richness3_coded.csv and threeACx_new.csv) Tree species compostion.R: Statistical code for results presented in main text and Figure 5, (based on richness3+.csv and threeACx_new.csv)   Data files used in the R-script: GeramodelA _Appendex 2_dfs.csv: (used in Enviromental1.R, data for result presented in Appendix S1) column names: SiteID=Site ID, Coffeemanagement= Coffee management, Coffeedominance= Coffee dominance, Stumps= Stumps (presence absence, see main paper, Burnings= Burnings, Signsofhumanpresence= Signs of human presence, Grazing= Grazing, Spices= Spices, Canopycover= Canopy cover, Treecircumference=Tree circumference, Largestcircumference= Largest circumference, Treebasalarea= Tree basal area, Circumference’sshannon= Circumference’s Shannon, Naturaldeadtrees= Natural dead trees, Decomposingtrees= Decomposing trees, Walkability= Walkability, Thickets= Thickets, Longestmoss= Longest moss, Non-coffeewoodyplants= Non-coffee woody plants, Treeabundance= Tree abundance GeramodelA _Appendex 2_l.csv: (used in Landscape1.R, data for result presented in Appendix S2) column names: SiteID=Site ID, Distancetohome= Distance to home, Distancetostream= Distance to stream, Closest footpathdistance= Closest footpath distance, Distancetoagricultural edge= Distance to agricultural edge, Distancetoroad= Distance to road, Slope, Forestcover= Forest cover, Elevation, Heatload, Costdistance= Cost distance humands.csv: (used in Enviromental2.R, data for result presented in Appendix S3) column names: SiteID=Site ID, Coffeemanagement= Coffee management, Coffeeoccurrence= Coffee occurrence, Signsofhumanpresence= Signs of human presence, Burnings, Stumps, Grazing, Spices, Coffeedominance= Coffee dominance HDLgradients.csv: (used in Landscape on human disturbance.R and Forest structure and biodiveristy.R , data for result presented in Table 2, Table 3, Figure 3, Figure 4) Column names: Coffeemanagement= Coffee management,Grazing, Signsofhumanpresence= Signs of human presence, Stumps, Spices, Distancetostream= Distance to stream, Closestfootpathdistance= Closest footpath distance, Distancetoagriculturaledge= Distance to agricultural edge, Distancetoroad= Distance to road, Slope, Forestcover= Forest cover, Elevation, Heatload,Canopycovergradient= Canopy cover gradient, Largesttreegradient= Largesttreegradient, Deadwoodgradient= Dead wood gradient, Lianacover= Liana cover, Treespeciesrichness= Tree species richness, EpiphyllousBryophyteRichness= Epiphyllous Bryophyte Richness richness3_coded.csv: ( used in Tree species compostion and disturbances.R, data for result presented in Figure 5) column names: Row Labels=Site ID, algr=Albizia grandibracteata, algu=Albizia gummifera, alsc=Albizia schimperiana, alab=Allophylus abyssinicus, apdi=Apodytes dimidiata, beab=Bersama abyssinica, bran=Brucea antidysenterica, ceaf=Celtis africana, chmi=Chionanthus mildbraedii, coaf=Cordia africana, crma=Croton macrostachyus, culu=Cupressus lusitanica, cuho=Cussonia holstii, diab=Diospyros abyssinica, drst=Dracaena steudneri, ehcy=Ehretia cymosa, ekca=Ekebergia capensis, elbu=Elaeodendron buchananii, eura=Euclea racemosa, euab=Euphorbia abyssinica, faan=Fagaropsis angolensis, fisu=Ficus sur, fith=Ficus thonningii, fiva=Ficus vasta, gasa=Gallineria saxifraga, maca=Macaranga capensis, mala=Maesa lanceolata, maun=Maytenus undata, mife=Millettia ferruginea, olwe=Olea welwitschii, oxsp=Oxyanthus speciosus, pofu=Polyscias fulva, poad=Pouteria adolfi-friederici, praf=Prunus africana, ryne=Rytigynia neglecta, sael=Sapium ellipticum, scab=Schefflera abyssinica, sygu=Syzygium guineense, teno=Teclea nobilis, veam=Vernonia amygdalina, veau=Vernonia auriculifera, veda=Verpis dainellii threeACx_new.csv: ( used in Tree species compostion and disturbances.R, and Tree species compostion.R, data for result presented in main text and Figure 5) column names: SiteID=Site ID, Coffeemanagement= Coffee management, Signsofhumanpresence= Signs of human presence, Stumps, Grazing, Spices richness3+.csv: ( used in Tree species composition.R, data for result presented in main text and Figure 5) column names: Row Labels=Site ID, Albizia grandibracteata, Albizia gummifera, Albizia schimperiana, Allophylus abyssinicus, Apodytes dimidiata, Bersama abyssinica, Brucea antidysenterica, Celtis africana, Chionanthus mildbraedii, Cordia africana, Croton macrostachyus, Cupressus lusitanica, Cussonia holstii, Diospyros abyssinica, Dracaena steudneri, Ehretia cymosa, Ekebergia capensis, Elaeodendron buchananii, Euclea racemosa, Euphorbia abyssinica, Fagaropsis angolensis, Ficus sur, Ficus thonningii, Ficus vasta, Gallineria saxifraga, Macaranga capensis, Maesa lanceolata, Maytenus undata, Millettia ferruginea, Olea welwitschii, Oxyanthus speciosus, Polyscias fulva, Pouteria adolfi-friederici, Prunus africana, Rytigynia neglecta, Sapium ellipticum, Schefflera abyssinica, Syzygium guineense, Teclea nobilis, Vernonia amygdalina, Vernonia auriculifera, Verpis dainellii

Context Human disturbances can have large impacts on forest structure and biodiversity, and thereby result in forest degradation, a property difficult to detect by remote sensing. Objectives To investigate spatial variation in anthropogenicdisturbances and their effects on forest structure and biodiversity. Methods In 144 plots of 20 x 20 m distributed across a forest area of 750 km2 in Southwest Ethiopia, we recorded: landscape variables (e.g., distance to forest edge), different human disturbances, forest structure variables, and species composition of trees and epiphyllous bryophytes. We then first assessed if landscape variables could explain the spatial distribution of disturbances. Second, we analysed how forest structure and biodiversity were influenced by disturbances. Results Human disturbances, such as coffee management and grazing declined with distance to forest edges and penetrated at least a kilometer into the forest. The slope was not related to disturbance levels, but several types of disturbances were less common at higher elevations. Among human disturbance types, coffee management reduced liana cover and was associated with altered species composition of trees. The presence of large trees and basal areas was not related to any of the disturbance gradients. Conclusions Although most anthropogenic disturbances displayed clear edge effects, surprisingly the variation in the chosen forest degradation indices was only weakly related to these disturbances. We suggest that the intersection between edge effects and forest degradation is very context-specific and relies much on how particular societies use the forests. For example, in this landscape coffee management seems to be a key driver.

For method of data collection and how it is processed ( see the method section of article)