SUPPLEMENTARY INFORMATION FOR WRIGHT ET AL “THE WORLDWIDE LEAF ECONOMICS SPECTRUM” 1. GLOPNET DATASET (see additional file) 2. DATA SOURCES Dataset code from leaf economics dataset MAT Rain VPD RAD PET Refs Ackerly_Jasper 14.6 652 0.44 170 1004 Unp Baruch&Goldstein_Hawaii_High_Old 12.0 3000 0.59 152 852 1 Baruch&Goldstein_Hawaii_High_Rec 12.0 3000 0.59 152 852 “ Baruch&Goldstein_Hawaii_Low_Old 22.4 2182 0.64 153 1552 “ Baruch&Goldstein_Hawaii_Med_Old 18.6 3300 0.95 152 1087 “ Baruch&Goldstein_Hawaii_Med_Rec 18.6 3300 0.95 152 1087 “ 7.3 1101 0.27 127 Bongers_et_al_Los_Tuxtlas 24.6 4725 0.85 163 1303 3 Cavender_Bares_Florida 20.5 1358 0.60 159 1405 Unp Chapin_etc_Toolik_Lake -8.8 0.14 Bassow&Bazzaz_Petersham_Ma 318 69 775 2 461 4,5, Unp Christodoulakis_Malakasa 16.7 635 0.72 175 1529 6,7 Chua_et_al_Malaysia 25.2 2688 0.42 146 1283 8 Coley_BCI 26.2 2606 0.51 179 1121 9,10 Cornelissen_UK_Sheffield 8.7 773 0.18 DeLucia91Ecol_Reno_Nevada 7.3 536 0.66 160 1194 11,12 DeLucia95_Okefenokee_Swamp 19.5 1303 0.55 157 1334 13 Diemer_Korner_Austria_high -2.0 2165 0.12 118 775 14 Diemer_Korner_Austria_low 7.6 1024 0.27 119 744 “ Diemer-Ecuador_high 6.7 1040 0.58 137 800 15,16 Diemer-Ecuador_highest 5.2 1040 0.42 137 744 “ Diemer-Ecuador_low 8.1 1040 0.51 137 852 “ Diemer-Ecuador_lowest 8.7 1040 0.37 137 875 “ 0.44 170 1004 17 Field_et_al_83_Jasper_Ridge 14.6 652 91 647 Unp Franco&Luttge_Brasilia 21.9 1535 0.81 155 1431 18 Garnier_etal_F/CR 12.9 0.52 149 1233 19-21, 772 Unp Garnier_etal_Les_Agros 14.3 1010 0.48 164 1259 “ Garnier_etal_SM/C 11.7 1148 0.45 144 1239 “ Gulias_Binifaldó 13.6 1265 0.30 154 1244 22, Unp Gulias_Puigpunyent 16.3 751 0.54 153 1244 “ Gulias_Sóller 16.8 857 0.62 153 1244 “ Gulias_UIB 16.8 514 0.70 153 1244 “ Hikosaka-Japan_Chiba_Japan 13.9 2288 0.33 139 1111 23 Hikosaka-Malaysia_Mt_Kinabalu_high 10.8 2842 0.45 156 815 24 7.5 2842 0.39 156 692 “ Hikosaka-Malaysia_Mt_Kinabalu_low 23.4 2842 0.23 156 1511 “ Hikosaka-Malaysia_Mt_Kinabalu_med 18.5 2842 0.57 156 1102 “ Hogan_etal_PNM_crane 26.3 1657 0.60 183 1146 25 Jayasekara_Sri_Lanka 15.2 2234 0.30 168 1012 26 Jose_Gillespie_Indiana 11.3 1049 0.41 137 943 27,28 811 0.24 124 542 29,30 26.3 1657 0.60 183 1146 31 Koike_SAPPORO__JAPAN 6.8 1216 0.23 119 667 32-34 Korner_et_al_86_Haast_Valley_NZ 9.5 5302 0.30 123 982 35 0.14 76 339 36, Hikosaka-Malaysia_Mt_Kinabalu_highest Jurik86_Pellston_MI Kitajima_Panama Kudo_Cornelissen_Abisko 5.2 -2.3 446 Unp Kudo_Cornelissen_Latnjajaure -3.1 978 0.18 70 331 “ Kudo_Cornelissen_Svalbard -6.8 505 0.13 64 261 “ Kudo96_high -2.4 1113 0.16 114 453 37 Kudo96_low 4.3 1362 0.18 114 677 “ Kuppers_Bayreuth 7.2 652 0.26 106 814 38 Lal_etal_Inceptisol 25.9 1011 1.42 192 1314 39,40 Lal_etal_Ultisol 25.6 1081 1.36 187 1286 “ Lamont_S_Africa_1_Citrusdal 15.5 0.71 182 1369 41 396 Lamont_S_Africa_10_Kylemore 15.6 714 0.43 175 1179 “ Lamont_S_Africa_11_Soetanysberg 17.9 437 0.79 192 1240 “ Lamont_S_Africa_12_Salmonsdam 15.0 828 0.74 193 1311 “ Lamont_S_Africa_13_Salmonsdam 16.1 558 0.56 171 1285 “ Lamont_S_Africa_14_Herrmanus 16.1 699 0.52 175 1285 “ Lamont_S_Africa_2_Stellenbosch 17.0 596 0.64 188 1241 “ Lamont_S_Africa_3_Opdieberg 16.6 369 0.90 202 1303 “ Lamont_S_Africa_4_Matjies_River 13.7 240 0.82 199 1509 “ Lamont_S_Africa_5_Algeria 11.3 720 0.65 202 1022 “ Lamont_S_Africa_6_Scarborough 17.0 596 0.64 188 1241 “ Lamont_S_Africa_7_Hopefield 18.0 385 0.85 195 1182 “ Lamont_S_Africa_9_Jonkershonk 12.9 1200 0.40 175 1012 “ Lamont_WA_Darling_Scarp 17.2 1100 0.93 184 1378 “ Lamont_WA_Eneabba 18.5 479 0.97 195 1607 “ Lamont_WA_Esperance 16.5 555 0.63 166 1143 “ Lamont_WA_Fitzgerald_River 16.0 574 0.65 159 1208 “ Lamont_WA_Kalbarri 20.6 369 1.05 204 1626 “ Lamont_WA_Lake_King 16.3 365 0.82 169 1174 “ Lamont_WA_Merridin_etc 17.5 304 1.03 181 1316 “ Lamont_WA_Millbrook 15.3 831 0.46 153 1265 “ Lamont_WA_Stirling_Ranges 15.5 681 0.58 153 1177 “ Lamont_WA_Walpole 14.5 794 0.61 159 1399 “ Lamont_WA_Watheroo 18.1 497 1.01 193 1604 “ Lee_Cedar_Creek2 6.3 730 0.42 127 940 Unp Lee_NZ_Murchison_Mtns 5.5 2225 0.32 123 882 Unp Lusk_saplings_Cordillera_Pelada 10.6 2795 0.49 167 811 42 Lusk-adults_Concepción 12.9 1308 0.35 183 1244 43,44, Unp 765 “ 6.6 1308 0.66 180 Lusk-adults_Puyehue 10.6 3200 0.26 167 1002 “ Marin_Medina_Piritu_Venezuela 25.7 506 0.70 176 1612 45 Martin_etal_Guanacaste 23.8 2220 0.55 189 1433 46 Lusk-adults_Los Lleuques McAllister_Konza 12.6 854 0.60 148 1194 47 Mediavilla_et_al_Salamanca 11.8 513 0.58 162 1314 48 MidgelySA_Alexandria 18.4 694 0.51 161 1254 49 MidgelySA_Amatolas 12.9 1024 0.56 165 1033 “ MidgelySA_Dukuduku 19.0 1250 0.54 160 1606 “ MidgelySA_Jonkershoek_Mtn 14.9 2500 0.76 186 MidgelySA_Jonkershoek_Rip 14.9 1600 0.86 186 1046 “ MidgelySA_Knysna 15.0 870 0.60 179 1412 “ MidgelySA_Mapelane 19.0 989 0.54 160 1606 “ MidgelySA_Sand_Forest 17.7 767 0.61 162 1447 “ MidgelySA_Umtiza 18.9 790 0.59 161 1447 “ MitchellNC_Coweeta 11.6 1740 0.31 146 1035 50 Miyazawa_Chiba_M 14.7 1790 0.38 136 1125 51 Mooney_etal_81_desert 18.6 133 1.52 179 1416 52 Mooney_etal_81_old-field 10.7 982 0.45 137 Mooney_etal83_Jonk_Mtn 17.0 2500 0.93 188 1062 53 Mulkey9193_BCI_Panama 25.9 2893 0.51 179 1121 54,55 Nelson_etal_Texas 22.1 733 0.71 160 1152 56 Niinemets_Kull94_Estonia 4.8 589 0.20 98 588 57 Niinemets_Kull98_Tartu 5.3 653 0.20 99 581 58 13.9 2288 0.33 139 1111 59 565 0.29 114 23.1 1027 0.63 165 1541 60, Nitta_Chiba_N OleksynPol_Siemanice Olivares_Caracas_Venezuela 8.4 985 “ 953 “ 657 Unp Unp Osada_Thomas_Pasoh Poorter_de_Jong_Along_ditch 25.5 1875 9.3 802 0.47 0.21 148 1262 61,62 98 746 63, Unp Poorter_de_Jong_Chalk_grassland 9.8 804 0.26 101 588 “ Poorter_de_Jong_Dry_heath 9.8 804 0.26 101 588 “ Poorter_de_Jong_Dry_open_grassland 9.8 804 0.26 101 588 “ Poorter_de_Jong_Poor_hay_meadow 9.3 802 0.21 98 746 “ Poorter_de_Jong_Quaking_Fen 9.3 802 0.21 98 746 “ Poorter_de_Jong_Reed_marsh 9.3 802 0.21 98 746 “ Poorter_de_Jong_Wet_heath 9.8 804 0.26 101 588 “ Prado&DeMoraes1997_Sao_Carlos 20.2 1470 0.69 131 1232 64 Prior_dry monsoon forest 27.3 1575 1.18 186 1543 65 Prior_open forest 27.3 1575 1.18 186 1459 “ Prior_swamp 27.3 1575 1.18 186 1459 “ Prior_woodland 27.3 1575 1.18 186 1459 “ Pyankov_Tadjikistan_Tadjikistan_high -2.2 164 0.61 155 430 66 Pyankov_Tadjikistan_Tadjikistan_higher -4.4 243 0.52 155 401 “ Pyankov_Tadjikistan_Tadjikistan_highest -5.3 225 0.49 153 465 “ 2.4 470 0.32 108 714 67,68 Reichetal_Colorado -1.5 959 0.38 142 506 69,70 Reichetal_N_Carolina 11.6 1740 0.31 146 1035 “ Reichetal_New_Mexico 13.5 272 0.96 179 1630 “ Reichetal_S_Carolina 18.2 1295 0.58 152 1020 “ Reichetal_Venezuela 26.0 3171 0.47 154 894 “ Pyankov_Urals_Yekaterinburg Reichetal_Wisconsin 8.2 909 0.37 134 927 “ Ricklefs_SE_Ontario 6.1 883 0.28 129 740 71 Schulze_Kapalga 27.5 1370 1.24 187 1647 72 Schulze_Katherine 26.7 1079 1.48 194 1764 “ Schulze_Kidman Springs 27.1 720 1.81 199 1796 “ Schulze_Melville Island 27.3 1749 1.09 185 1397 “ Schulze_Mt_Sanford 26.2 494 2.01 206 1977 “ Shipley_Sherbrooke 4.5 1110 0.26 122 731 73 Small1972_Ottawa 5.5 898 0.30 129 763 74 Sobrado&Medina_SanCarlos_bana 26.0 3171 0.47 154 894 75 Sobrado_Charallave 24.6 917 0.67 164 1541 76 Specht_Rundel_Dark_Island_heath 15.0 467 0.64 153 1308 77 Specht_Rundel_Dark_Island_mallee 15.0 467 0.64 153 1308 “ Specht_Rundel_Mt_Lofty 12.0 1193 0.61 165 Tan_et_al_adinandra_trema_belukar 26.7 2146 0.55 146 1394 78 Terashima_Nepal -2.8 1015 0.54 156 979 “ 672 79 Tezara_etal98_Coro Tjoelker_Cedar_Creek 26.8 495 0.96 176 1305 80 6.3 730 0.42 127 940 81, Unp Tuohy_etal_Zimbabwe_CHID 21.8 498 0.72 182 1355 82 Tuohy_etal_Zimbabwe_CRST_MCLW 18.9 840 0.62 179 1514 “ Tuohy_etal_Zimbabwe_MAT 18.9 623 0.78 182 1486 “ Turner_&_Tan_Adinandra_Belukar 26.7 2146 0.55 146 1394 83 Turner_&_Tan_Beach_forest 26.7 2146 0.55 146 1394 “ Turner_&_Tan_Mangroves 26.7 2146 0.55 146 1394 “ Turner_&_Tan_Undegraded_secondary_fore 26.7 2146 0.55 146 1394 “ Veneklaas_W_Australia 18.3 690 0.85 182 1272 Unp Villar_Andalucía_mesic 17.2 609 0.66 173 1490 84 Villar_Andalucía_xeric 17.2 609 0.66 173 1490 “ Villar_California_chaparral 14.1 636 0.44 170 1004 “ Villar_California_forest 12.3 1020 0.33 172 Villar_Canary_Is_lauriphyll 16.6 394 0.56 166 1244 “ Villar_Canary_Is_xeric 16.6 394 0.56 166 1244 “ Villar_Chihuahua 18.2 349 1.19 174 1577 “ -16.1 168 0.06 Villar_Douala-Edea Forest, Cameroon 26.5 2731 0.60 124 1033 “ Villar_Kibale Forest, Uganda 21.7 1329 0.60 158 1171 “ Villar_N_Carolina_forest 15.9 1206 0.50 151 980 “ st Villar_Devon_Is_Canada 75 920 “ 207 “ Villar_Tierra_del_Fuego 4.3 787 0.26 103 531 “ Villar_Toronto 6.8 792 0.28 132 763 “ Williams et al_LosTuxtlas2 24.6 4725 0.85 163 1303 85,86 Williams_Linera_Mexico 15.8 1837 0.47 156 1231 87 Wright_Oz_syd_hiP 17.5 1148 0.63 162 1166 88-90 Wright_Oz_syd_loP 17.5 1148 0.63 162 1166 “ Wright_Oz_wnsw_hiP 17.1 412 0.95 177 1390 “ Wright_Oz_wnsw_loP 17.1 412 0.95 177 1390 “ Zotz_Fortuna_Panama 22.6 2875 0.40 184 1169 91 Notes. 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Strategy-shifts in leaf physiology, structure and nutrient content between species of high and low rainfall, and high and low nutrient habitats. Functional Ecology 15, 423-434 (2001). 89. Wright, I. J. & Westoby, M. Leaves at low versus high rainfall: coordination of structure, lifespan and physiology. New Phytologist 155, 403-416 (2002). 90. Wright, I. J. & Westoby, M. Nutrient concentration, resorption and lifespan: leaf traits of Australian sclerophyll species. Functional Ecology 17, 10-19 (2003). 91. Zotz, G., Tyree, M. T., Patino, S. & Carlton, M. R. Hydraulic architecture and water use of selected species from a lower montane forest in Panama. Trees 12, 302-309 (1998). 3. FURTHER DETAILS OF BIVARIATE TRAIT RELATIONSHIPS The Standardised Major Axis gives the central slope through a cloud of points (e.g. the central axis of a bivariate-normal ellipse). SMA analyses are appropriate when the purpose is to estimate the relationship between two variables, usually when the slope of the relationship is of primary interest. The fitting of an SMA slope involves simultaneous minimisation of sums of squares in both Y and X dimensions. By contrast, standard model I regression involves minimisation of sums of squares in the Y dimension only. For many purposes this is a desirable property, especially for calculating predictive regression equations. These equations would be appropriate if one wanted to apply the results from the source paper to other datasets where one wants to predict values for one trait based on known values for another trait. This section of Supplementary Information provides further details relevant to bivariate trait analyses presented in the source paper (Tables 1 and 3). In the following tables the grand mean of Y and X variables for each analysis is given (Y variables in left hand column, X variables in top row). Using these data together with SMA slope and r2 data from Tables 1 and 3 the following parameters can be calculated: 1. Y-intercept for the Standardised Major Axis equation with Y and X variables as treated in the text. 2. SMA slope and intercept for the analysis if Y and X variables were swapped. 3. Standard model I regression parameters (slope, intercept) for Y on X, or if Y and X variables were swapped. A worked example is given below the data tables. Further information on SMA analysis and its relationship to model I regression can be found in Sokal, R. R. & Rohlf, F. J. Biometry: the principles and practice of statistics in biological research (W. H. Freeman and Company, New York, 1995). A free DOS-based program for running various SMA routines, including an SMA analogue of ANCOVA, is Falster, D.S., Warton, D.I. & Wright, I.J. (2003) (S)MATR - (Standardised) Major Axis Tests & Routines. Available from http://www.bio.mq.edu.au/ecology/ Mean Y, mean X data for analyses in Table 1 (source paper) log LMA log LL log Amass log Nmass log Pmass log Rdmass 0.942, 2.018 0.945, 1.970 0.959, 0.238 1.061, -1.041 1.068, 0.975 log LMA 2.014, 1.985 2.019, 0.224 2.133, -1.098 2.108, 0.985 log Amass 1.987, 0.246 1.845, -1.073 1.915, 0.982 log Nmass 0.105, -1.10 log Pmass 0.181, 0.983 -1.245, 0.920 Mean Y, mean X data for analyses in Table 3 (source paper) log LMA log LL log Aarea log Narea log Parea log Rdarea 0.942, 2.108 0.942, 0.997 0.947, 0.253 1.056, -0.966 1.068, 0.117 log LMA 2.014, 0.999 2.019, 0.241 2.133, -0.971 2.108, 0.093 log Aarea 1.008, 0.272 0.958, -0.929 1.038, 0.104 log Narea log Parea 0.240, -0.957 0.292, 0.099 -1.062, 0.147 Worked example We use SMA data for log LL (Y) on log LMA (X). SMA slope = 1.71; mean Y = 0.942, mean X = 2.018, r2 = 0.422 (Table 1, source paper). 1. Just as for model I regression, a Standardised Major Axis slope always passes through the point (mean X, mean Y). Hence, the intercept is given by Y – bX = 0.942 – 1.71 * 2.018 = - 2.509 2. If the Y and X variables were swapped, the SMA slope for log LMA on log LL would be the reciprocal of that for log LL on log LMA, i.e. 1/1.71 = 0.585. As before, the intercept is then calculated from the slope and data for mean Y and X, in this case = 2.018 – 0.585 * 0.942 = 1.467. As before, the r2 value for the relationship is 0.422. 3. A SMA slope for Y on X is equal to the model I regression slope of Y on X divided by the correlation r value for the variables. The r2 value and hence correlation r are the same irrespective of whether one is interested in calculating SMA or model I regression parameters. Hence, the model I regression slope for log LL on log LMA = (0.422)0.5 * 1.71 = 1.11. Since the regression slope passes through the point (mean X, mean Y), the Y-intercept can be calculated as above, i.e. = 0.942 – 1.11 * 2.018 = - 1.30. Similarly, parameters for the model I regression of log LMA on log LL can be calculated from the SMA parameters for log LMA on log LL, i.e. regression slope = (0.422)0.5 * 0.585 = 0.38; intercept = 2.018 – 0.38 * 0.942 = 1.66. Geometrically, the SMA slope bisects the model I slopes Y on X and 1 / (X on Y), i.e. it is the geometric mean of the two. Taking the model I slopes for log LL on log LMA (1.11) and log LMA on log LL (0.38), the SMA slope could be calculated as 1.11 *1 / 0.38 = 1.71 = 1.11 / (0.422)0.5 (the model 1 slope divided by the correlation r). 4. DETAILS OF MULTIPLE REGRESSION EQUATIONS MENTIONED IN THE SOURCE PAPER Standard errors for regression coefficients are given in parentheses for the following regression equations. All coefficients were highly significant (p < 0.0001) except where noted. r2 values describe the explanatory power of each model, sample n refers to the number of species included in each analysis. Units (prior to log10 transformation in many cases): Amass nmol g-1 s-1; Aarea mol m-2 s-1; Nmass %; Narea g m-2; LMA g m-2; Rdmass nmol g-1 s-1; rain mm y-1; MAT oC; VPD kPa; PET mm y-1; RAD W m-2; (Ca – Ci) ppm CO2; gs mmol m-2s-1. 1. Photosynthetic capacity (mass basis, Amass) on leaf N per mass (Nmass) and leaf mass per area (LMA) log Amass = 0.74 (0.05) log Nmass – 0.57 (0.04) log LMA + 2.96 (0.09) r2 = 0.63, n = 706 2. Photosynthetic capacity (area basis, Aarea) on leaf N per area (Narea) and LMA log Aarea = 0.69 (0.05) log Narea – 0.28 (0.04) log LMA + 1.40 (0.07) r2 = 0.20, n = 705 3. Dark respiration rate (mass basis, Rdmass) on Nmass and LMA log Rdmass = 0.75 (0.07) log Nmass – 0.35 (0.05) log LMA + 1.59 (0.12) r2 = 0.62, n = 267 4. Dark respiration rate (areas basis, Rdarea) on Narea and LMA log Rdarea = 0.68 (0.08) log Narea – 0.03 (0.06) log LMA – 0.03 (0.11) r2 = 0.34, n = 267. P-value for LMA = 0.568, P-value for intercept = 0.755 4. LMA on site mean annual temperature (MAT) and rainfall. log LMA = 0.015 (0.001) MAT – 0.25 (0.02) log rain + 2.56 (0.06) r2 = 0.15, n = 2370 5. Leaf lifespan (LL) on LMA and rainfall. log LL = 1.23 (0.05) log LMA + 0.47 (0.04) log rain – 2.95 (0.18) r2 = 0.51, n = 678 6. LL on LMA and MAT log LL = 1.70 (0.08) log LMA – 0.048 (0.005) [log LMA * MAT] + 0.106 (0.010) MAT – 2.59 (0.16) r2 = 0.54, n = 678 7. LL on LMA and vapour pressure deficit (VPD) log LL = 0.580 (0.074) log LMA – 1.56 (0.18) [log LMA * log VPD] + 3.37 (0.37) LAVPD – 0.118 (0.155) r2 = 0.49, n = 678. P-value for intercept = 0.446. 8. LL on LMA and Penman-Monteith potential evapotranspiration (PET) log LL = 2.69 (0.16) log LMA – 0.0015 (0.0001) [log LMA * PET] + 0.0031 (0.0003) PET – 4.63 (0.32) r2 = 0.52, n = 678 9. LL on LMA and irradiance (RAD) log LL = 3.01 (0.23) log LMA – 0.013 (0.001) [log LMA x RAD] + 0.030 (0.003) RAD – 5.56 (0.47) r2 = 0.52, n = 678 10. CO2 drawdown (Ca – Ci) on Narea and stomatal conductance to water (gs) (Ca – Ci) = 64.8 (9.98) log Narea – 107.2 (6.56) log gs + 344.3 (15.59) r2 = 0.47, n = 343 11. Aarea on gs and rainfall log Aarea = 0.455 (0.023) log gs – 0.333 (0.025) log rain + 0.928 (0.091) r2 = 0.52, n = 498. 5. PCA (PRINCIPAL COMPONENTS ANALYSIS) LOADINGS FOR AREABASED ANALYSIS OF LEAF TRAITS Traits: leaf mass per area (LMA), leaf lifespan (LL), photsynthetic capacity (Aarea), dark respiration rate (Rdarea), leaf N per area (Narea), leaf P per area (Parea). All traits logtransformed prior to analysis. Axis 1 explained 43% of the total trait variation, axis 2 explained a further 29% (total 72 %). Trait Loading on axis 1 Loading on axis 2 LL 0.25 0.91 LMA 0.67 0.61 Narea 0.91 0.03 Parea 0.66 -0.23 Aarea 0.44 -0.62 Rdarea 0.80 -0.30