Predictions of Mammal Diversity on Four Land Masses RODRIGO A. MEDELLÍN* AND JORGE SOBERÓN† *Instituto de Ecología, UNAM. Ap. Postal 70-275, Mexico, D.F., 04510, Mexico, email [email protected] †Comisión Nacional para el Conocimiento y Uso de la Biodiversidad, Fernández Leal 43, col. Barrio de la Concepción, Coyoacán, 04020, Mexico, D.F., Mexico Abstract: Knowledge about the number of living species is fundamental to the practice of conservation biology, but we are far from knowing the number of species even for relatively well-known groups such as mammals. We analyzed a database that contained information on the year of description, distribution, size class, and taxonomic order of each known mammalian species. Our goal was to predict the size class, order, and number of mammalian species on each of four land masses—America, Eurasia, Africa, Oceania. We constructed cumulative functions of species described versus year of description, and we fitted a logarithmic model to calculate instantaneous rates of species description in 1992 and 2032 and to estimate the number of species to be described in each group in the 40-year interval. Africa and Eurasia had the highest absolute number of species today and the greatest number of species expected to be described in species-rich orders (except for Rodentia, in which the highest number of known and expected species was in the American land mass). Per unit area, Oceania had the highest number of known species and the greatest number of species expected to be described. Our estimates, based on the historical patterns of species accumulation, place the total number of mammalian species in the year 2032 at 4875, which is 247 more than in 1992. The majority of the new species will be small (,100 g) and will be in the orders Insectivora, Chiroptera, and Rodentia. Our analyses will help identify particular groups and land masses for which field surveys, conservation efforts, and taxonomic study deserve particular attention. Predicciones de Diversidad de Mamíferos en Cuatro Masas Continentales Resumen: El número de especies vivas es una pieza de información clave para la biología de la conservación y la toma de decisiones. Aún estamos lejos de conocer el número exacto de especies vivientes incluso para un grupo relativamente bien conocido como los mamíferos. Analizamos la base de datos formada por el año de descripción, la distribución regional, el tamaño corporal y el orden taxonómico de todas las especies conocidas de mamíferos. Nuestro objetivo fue predecir el número total de especies de mamíferos en el mundo, y para cada región del mundo, clases de tamaño y orden taxonómico. Construímos funciones acumulativas de descripción de especies contra año de descripción y les ajustamos un modelo logarítmico para calcular las tasas instantáneas de descripción de especies en 1992 y en 2032 y el número estimado de especies que serán descritas en cada grupo en el lapso de 40 años hacia el futuro. Nuestras estimaciones, siguiendo los patrones históricos de acumulación de especies, colocan el total de especies de mamíferos en el año 2032 en 4875, 247 más que en 1992. La mayoría de las especies nuevas serán pequeñas (,100 g) y pertenecerán a los órdenes Insectivora, Chiroptera y Rodentia. Africa y Eurasia presentaron los números absolutos más altos de especies conocidas y los mayores números de especies esperadas en los órdenes grandes (excepto Rodentia; el más alto número de especies conocidas y esperadas fue en América), pero por unidad de área Oceanía arrojó los mayores números de especies conocidas y esperadas. Nuestros análisis contribuyen a enfocar estudios de reconocimiento, esfuerzos de conservación y a poner especial atención a trabajar en la taxonomía de grupos particulares en regiones determinadas. Paper submitted August 6, 1997; revised manuscript accepted March 31, 1998. 143 Conservation Biology, Pages 143–149 Volume 13, No. 1, February 1999 144 Predictions of Mammal Diversity Introduction Knowledge about the number of extant species is fundamental for scientific purposes and for decision-making processes related to conservation and sustainable development. Questions about numbers of species and factors determining species richness have been asked for decades (Hershkovitz 1958; Hutchinson 1959; Hagmeier 1966; Paine 1966; Whittaker 1972; Cody 1975; Schall & Pianka 1978; May 1990). Estimates of the number of living species vary widely, from 5 to 50 million or more (U.S. Congress 1987; Wilson 1988; McNeely et al. 1990; Hawksworth et al. 1995), with the uncertainty concentrated in groups such as fungi, insects, and nematodes. Even for groups considered well known, the number of species they contain and their geographic distributions remain incomplete. Mammals represent such a group, despite the fact that they are relatively large animals, they are charismatic species that people find easy to relate to, and they have ecological, scientific, cultural, and practical importance. Furthermore, mammals were among the first groups of animals to be studied by early naturalists; therefore, the number of species should be well known. Nonetheless, we are far from knowing the real number of mammalian species that exist (Morell 1996). Although we recognize 4628 species (Wilson & Reeder 1993), some nonquantitative estimates of species to be described after revision alone—not counting description of morphologically distinct species (e.g., Morell 1996)—place the total expected number at 8000. Of the 459 species added in the 10 years between the two editions of Mammal Species of the World, only 37% were new morphotypes unknown to science; the remainder were sibling spe- Medellín & Soberón cies separated thanks to technological advances. Over half of the known species are small, with a body mass of under 100 g. These are much less conspicuous than larger species, so a straightforward prediction is that most unknown mammal species will weigh under 100 g. Small mammals, however, belong to at least three mammalian orders distributed on at least three of the four land masses we considered (America, Africa, Eurasia, and Oceania): insectivores live in America, Africa, and Eurasia, and rodents and bats live in all four. Due to their differential evolutionary origin and radiation, we expect that these orders will differ in the number of species predicted to be described in each land mass. At a regional scale, the tropics harbor many more species than temperate areas of the same size, and countries exceptionally rich in species (“megadiversity” countries) are almost all included within the tropics and contain over one-half of the world’s species (Wilson 1988). Thus, temperate countries tend to contain far fewer species than tropical ones, even though tropical areas are much smaller. For example, Costa Rica (area: 322,460 km2) contains at least 203 species of mammals, 796 species of birds, and 218 species of reptiles, whereas Canada (area: 9,221,000 km2 ) has 94 species of mammals, 434 species of birds, and 32 species of reptiles (U.S. Congress 1987; McNeely et al. 1990). Similarly, insularity affects number of species through endemism, and regions containing numerous islands have more species than a continuous area equivalent in size, climate, and topography. Our goal was to generate numerical estimates of the expected number of mammal species to be added to current inventories through the year 2032. We calculated this number for different groups (taxonomic and size class) and land masses. Methods Figure 1. Cumulative curve of species description and fitted model for all land mammal species of the world. The curve and model start in the year 1890 (year 0 in the plot). The number of species in that year is 2364 (species 0 in the plot). Inset is the complete cumulative curve starting in 1758. Because of the shape of the curve, the model cannot be fitted to the complete curve. Conservation Biology Volume 13, No. 1, February 1999 We used Wilson and Reeder’s (1993) comprehensive listing of mammal species, taxonomic arrangement, type localities, and year of description to generate the initial database. We assigned each type locality to one of four land masses: America, Eurasia, Africa, and Oceania. We did not separate North from South America or Europe from Asia, and we lumped Oceania (including Australia) to avoid confusion in calculating the number of species inhabiting each land mass. With this arrangement we could assume that, with only a few exceptions, each species was endemic to one of those four land masses. The few species occurring in more than one land mass were assumed to be endemic to the land mass of their type locality and absent in the others. We also assigned each mammal species to one of five size categories: 1, ,100 g; 2, .100 and ,1000 g; 3, .1000 and ,10,000 g; 4, .10,000 and ,100,000 g; and 5, .100,000 g. To simplify analyses, we pooled the four orders of Oceanian marsupials and the three orders of American Medellín & Soberón Predictions of Mammal Diversity marsupials into a single “order” because these orders are more closely related than others, and because until recently they were in fact considered a single order. We did not include Cetacea, Otariidae, Odobenidae, or Pho- 145 cidae because we cannot assume that marine species are endemic to one region. To estimate species richness and the degree of completion of inventories, and to provide an assessment of the rate of description of new species, Table 1. Land mass north-south latitudinal span, surface area, mammal species groupings used, equation parameters,a annual rates of species descriptiona in years 1992 and 2032, known number of species in 1992, and predicted number of species in year 2032 of each mammal group. Land mass (latitude span in degrees) Surface area (km2) America (136) 42,081,000 Eurasia (90) Africa (72) Oceania (72) 54,430,000 30,271,000 8,503,195 Mammal species grouping zb ac Annual description rate in 1992 Annual description rate in 2032 Number of known species (1992) Species predicted in 40 years 4875 1608 953 390 214 38 13 67 27 80 290 84 75 28 922 Entire world Total size 1 size 2 size 3 size 4 size 5 Didelphimorphia Lagomorpha Insectivora Chiroptera Primates Carnivora Artiodactyla Rodentia 0.001 0.00375 0.0055 0.0175 0.0371 88.38 48.758 36.29 11.25 2.191 8.53 2.48 1.70 0.53 0.24 6.29 1.83 1.25 0.39 0.18 0.0743 0.651 0.0647 0.015 0.066 0.209 0.411 0.00609 1.434 7.914 3.239 3.987 0.301 0.622 0.113 39.966 0.12 0.02 0.14 0.56 0.10 0.04 0.02 1.55 0.09 0.01 0.11 0.43 0.08 0.03 0.02 1.14 4628 1538 905 375 207 38 13 63 26 74 280 84 73 27 868 Total size 1 size 2 size 3 size 4 size 5 Insectivora Chiroptera Primates Carnivora Artiodactyla Rodentia Lagomorpha 0.00299 0.00384 0.0146 0.17 0.22 0.26 0.015 0.0126 0.282 0.743 0.098 0.0056 0.117 20.305 12.41 6.026 3.19 0.89 0.09 2.41 4.339 1.4 1.126 0.24 10.96 0.324 2.82 2.12 0.60 0.06 0.51 0.66 0.03 0.01 0.07 1.51 0.07 2.39 1.86 0.49 0.04 0.03 0.03 0.48 0.57 0.03 0.01 0.07 1.28 0.06 1463 818 322 171 104 48 166 337 62 96 99 621 44 1543 881 341 171 104 48 186 356 63 96 99 663 44 Total size 1 size 2 size 3 size 4 size 5 Insectivora Chiroptera Primates Carnivora Artiodactyla Rodentia Lagomorpha 0.0044 0.00486 0.047 0.107 0.462 21.97 13.88 5.34 3.029 5.18 2.02 1.76 0.20 0.09 0.02 1.51 1.33 0.15 0.07 0.01 0.0115 0.022 0.232 0.22 0.33 0.009 3.077 4.04 2.91 1.38 7.36 10.39 0.67 0.40 0.04 0.04 0.03 0.99 0.52 0.30 0.03 0.03 0.02 0.74 1069 645 183 123 79 39 188 195 87 67 94 394 10 1129 693 193 125 81 39 201 209 87 69 94 425 10 Total size 1 size 2 size 3 size 4 Chiroptera Marsupials Rodentia 0.0056 0.0056 0.026 0.065 3.97 1.67 1.36 1.09 1.21 0.85 0.30 0.13 0.97 0.72 0.23 0.10 0.014 0.0199 0.014 0.78 1.286 1.93 0.37 0.36 0.51 0.31 0.28 0.40 451 208 126 97 20 113 203 132 474 208 132 99 20 122 204 146 a Parameters and rates are given only in those cases in which there was an increase in number of species. The z is related to the slowing down of description rate. c Rate of description of new species near the origin. b Conservation Biology Volume 13, No. 1, February 1999 146 Predictions of Mammal Diversity Medellín & Soberón Figure 2. Cumulative curves of species description and fitted models of four of the five size categories of mammals analyzed on four land masses. The curves start in the year 1890 (year 0), when the number of species was treated as zero. Real numbers of species in that year in each size category and land mass were, respectively, body size 1, 2, 3, 4, 5: 342, 201, 146, 34, 13, America; 350, 164, 146, 87, 44, Eurasia; 210, 116, 90, 68, 36, Africa; 77, 63, 62, 19, 0, Oceania. Numbers for size 4 were too small to attempt adjusting a continuous model. we used cumulative curves as a tool to model the process of adding new species (Soberón & Llorente 1993; Colwell & Coddington 1995). We generated cumulative curves of species as a function of time elapsed since the beginning of modern scientific explorations for each land mass and within each land mass for each of the size categories and each mammalian order with more than 60 species. Most such curves have a pronounced S shape because from 1758 to about 1850 the number of species accumulated slowly; subsequently, an explosive period of new descriptions lasted from about 1875 to 1930. Later, the addition of species slowed significantly as the number of species approached a hypothetical “true” number in a given land mass and category (Fig. 1). To fit the accumulation equations to those data, after 1890 we ignored early data and used only points in the convex portion (Fig. 1). Conservation Biology Volume 13, No. 1, February 1999 The fitted equations were then used to extrapolate to a standard and arbitrary 40 more years of collecting effort, thus fixing predictions of species numbers to 2032. Instantaneous rates of species addition were also obtained from curves. Curves were fitted to only those data sets with enough species to be modeled by a continuous model. The equation used the logarithmic model because, as discussed by Soberón and Llorente (1993), in a large area the probability of adding a new species to a collection decreases without becoming zero for a long period of time. This is well modeled by the following equation: S = ( 1 ⁄ z )log ( 1 + zaT ), (1) where a is the rate of species description near the origin, z is another parameter related to the slowing of that rate, and T is the time in years. Medellín & Soberón Predictions of Mammal Diversity Table 2. Number of species of land mammals for each of the five size categories in each land mass, corrected for number of species per 100,000 km2, and number of species expected to be described in the next 40 years. Land massa Size Number category of species America Africa Eurasia Oceania Total 1 2 3 4 5 Total Absolute Corrected Expected Corrected Absolute Corrected Expected Corrected Absolute Corrected Expected Corrected Absolute Corrected Expected Corrected Absolute Corrected Expected Corrected Absolute Corrected Expected Corrected 905b 2.15 48 0.11 375b 0.89 15 0.04 207b 0.49 7b 0.02b 38 0.09 0 0.00 13 0.03 0 0.00 1538b 3.65 68 0.16 645 2.13 49 0.16 183 0.60 10 0.03 123 0.41 2 0.01 79 0.26b 2b 0.01b 39 0.13b 0 0.00 1069 3.53 59 0.19 818 208 2576 1.50 2.45b 61b 20 178 0.11 0.24b 322 126 1006 0.59 1.48b 19b 6 50 0.03 0.07b 171 97 598 0.31 1.14b 0 2 11 0.00 0.02b 104b 20 241 0.19 0.24 0 0 2 0.00 0.00 48b 0 100 0.09 0.00 0 0 0 0.00 0.00 1463 451 4521 2.69 5.30b 78b 22 227 0.14 0.26b a Land mass areas per 100,000 km2: America, 420.81; Africa, 302.70; Eurasia, 544.30; Oceania, 85.03; total, 1352.84. b Highest value in each row. Results and Discussion The analysis covered an interval of 234 years, from the establishment of the Linnean system of nomenclature (1758) through 1992. When the total time period is examined, the cumulative curve for all mammal species (Fig. 1) is not near the asymptote; in fact, the section of the curve depicting species descriptions in the last 70 years alone is linear and has a steep slope. The nonlinear fitting, however, reveals a significant curvature of the accumulation process. Over the last 15 years the process accelerated again because of the advent of newer taxonomic tools, such as karyology and molecular genetics (Baker 1984; Dipenaar & Rautenbach 1986; Baker et al. 1988), although it is also true that many species with distinct morphotypes are still being described (Flannery 1990; Reyes et al. 1991). Based on our analysis, we are still far from knowing how many species of mammals there are, but we may be able to predict where and in what groups new species are most likely to be found. Our analysis by size class indicates that small mammals are much less well known than any other size group, as expected. For example, in Africa there are now 645 mammal species of size class 1, and in 40 years we expect there will be approximately 147 693, an increase of 7.4% (Table 1; Fig. 2a). There are, however, 183 mammals of size class 2, and in 40 years we predict there will be 193, a 5.5% increase (Fig. 2b). There are 123 species of size class 3, and we predict only two species to be described in the next 40 years (Fig 2c). There are 79 species of size class 4, and two will be added; none will be added beyond the 39 known species of size class 5 (Table 1; Fig. 2d). We expect 228 species of small mammals (178 size 1 and 50 size 2) to be described in the next 40 years on all land masses (Table 2; Fig. 2). It is striking that the trend of number of species in sizes 1 and 2 is maintained on all land masses except Africa, which has a large drop in number of species from size 1 to size 2. Similarly, from size 2 to size 3 (Fig. 2c), Eurasia has a large drop in number of species, leaving only America with relatively high values. A greater number of species will be described from Eurasia in the next 40 years. If we correct for land mass area, however, Oceania has a higher value of expected new species per unit area than in any other land mass (Table 2). This is probably related to Oceania’s high degree of insularity, which correlates with species density because of high endemism and small distribution ranges. Insectivores occur in three of the four land masses and are more species-rich in Africa; when area is corrected for, they are twice as rich in Africa as in Eurasia and over 3.5 times richer in Africa than in America (Table 3). Surprisingly, a greater number of species is expected to be described in Eurasia in the next 40 years, although Africa Table 3. Number of species for each of the 10 most species-rich orders of land mammals in each land mass corrected for number of species per 100,000 km2, and number of species expected to be described in the next 40 years. Order Land mass Number of species America Africa Eurasia Oceania Total Insectivora Absolute 74 Corrected 0.18 Expected 6 Corrected 0.01 Chiroptera Absolute 280 Corrected 0.67 Expected 9 Corrected 0.02 Primates Absolute 84 Corrected 0.20 Expected 0 Corrected 0.00 Carnivora Absolute 73 Corrected 0.17 Expected 2* Corrected 0.00 Artiodactyla Absolute 27 Corrected 0.06 Expected 1* Corrected 0.00 Rodentia Absolute 868* Corrected 2.06* Expected 51* Corrected 0.12 188* 166 0.62* 0.30 13 19* 0.04* 0.03 195 337* 0.64 0.62 13 18* 0.04 0.03 87* 62 0.29* 0.11 0 1* 0.00 0.00 67 96* 0.22* 0.18 2* 0 0.01* 0.00 94 99* 0.31* 0.18 0 0 0.00 0.00 394 621 1.30 1.14 32 42 0.11 0.08 428 38 113 1.33* 9 0.11* 925 49 233 1 236 4 220 1 132 1.55 14 0.16* 2015 139 * Highest value in each row. Conservation Biology Volume 13, No. 1, February 1999 148 Predictions of Mammal Diversity still has a greater predicted species description rate per unit area (Fig. 3a). Eurasia is the land mass richest in bat species, although America, Africa, and Eurasia have a similar bat- Medellín & Soberón species richness once area is corrected for. Bat species richness in Oceania is about half that of the other three land masses. Eurasia will have the greatest number of new species, although, per unit area, Oceania again has the highest number of species to be described. This is probably also related to Oceania’s high degree of insularity (Fig. 3b). The absolute species richness of rodents is highest in America, where by far the highest species density and the largest expected number of species to be described also occurs. Although for methodological restrictions we pooled North and South America, intuitively South America will be the main source of new species. As with Chiroptera, Oceania has the highest number of species expected to be described per unit area (Table 1; Fig. 3c). Primates and carnivores show similar values of species richness and species packing on all four land masses. Eurasia is relatively poor in primates, and Africa has the greatest values per unit area. There remain few species to be described in the next 40 years. Artiodactyls show far fewer species in America, probably a result of Pleistocene extinctions. The emerging pattern shows that, as expected, small mammals will compose the bulk of the species to be described in the next half century. If past description patterns continue, bats and insectivores in Eurasia will contribute an important percentage of those species. Although we pooled North and South America, the North American mammal fauna is clearly much better known than that of South America. Similarly, Asia and Europe were combined in our analyses, but most of the new species will surely come from Asia. Africa and Oceania will yield a greater number of species per unit area (Table 1). Unless there are radical shifts with discoveries of unknown hotspots of undescribed species or a change in taxonomic philosophy, our predictions should be robust enough to be useful as a tool to plan prospective and exploratory work and as a guide to focus conservation and research efforts. Acknowledgments Figure 3. Cumulative curves of species description and fitted model of the orders Insectivora, Chiroptera, and Rodentia on four land masses. The curves start in the year 1890 (year 0), when the number of species was treated as zero. Real numbers of species in that year in each order and land mass are Insectivora, Chiroptera, Rodentia, respectively: 27, 142, 339, America; 64, 185, 263, Eurasia; 47, 93, 147, Africa; 0, 56, 35, Oceania. Conservation Biology Volume 13, No. 1, February 1999 We thank H. Gómez de Silva, D. Wilson, G. Meffe, E. Main, and two anonymous reviewers for critically reading an earlier version of this manuscript. H. Arita, G. Ceballos, M. Equihua, and C. 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