In Kenya, wildlife numbers have drastically declined due to land use changes (LUCs) over the past three decades. This has affected wildlife habitats by converting them into farmlands and human settlements. This study used remote sensing data from landsat satellite to analyze the changing land use patterns between 1980 and 2013 and their impacts on wild ungulates in KWE. The objective of the study was to map out LUCs, determine the possible causes of LUCs, and examine the effects of LUCs on wild ungulates. The results showed a noticeable increase in the size of farmland, settlement, and other lands and a decline in forestland, grassland, wetland, and woodland. The main possible causes of LUC were found to be agricultural expansions, human population dynamics, economic factors, changing land tenure policy, politics, and sociocultural factors. The main effects of LUCs on wild ungulates in KWE include a decline in wild ungulate numbers, habitat destruction, increased human-wildlife conflicts, land degradation, and displacement of wild ungulates by livestock. The study recommends land use zoning of KWE and establishment of an effective and efficient wildlife benefit-sharing scheme(s). 1. Introduction Wild ungulates are hoofed wild mammals comprising large grazers and browsers. They account for the vast majority of large herbivores currently on earth and are found in nearly every biome especially in arid and semiarid grasslands [1]. Their abundance and spatial distribution is highly related to availability of quality forage and water resources [2]. Wild ungulates have high economic values as a source of revenue through consumptive and nonconsumptive utilization [3, 4]. Their resources provide environmental goods and services for the livelihood of the people, sociocultural, aesthetic, and ecological values. In Kenya, wildlife resources accounted for 70% of the gross tourism earnings, 25% of the gross domestic product (GDP), and more than 10% of total formal sector employment in 2011 [5]. Although Africa has been exceptional in retaining a considerable diversity and concentration of its wildlife compared to America and Australia, the populations of many of its wild ungulate species have declined substantially inside and outside protected areas over the past three decades [6, 7]. East Africa was incomparable in sustaining relatively intact wildlife but in the last three decades the wild ungulate population has declined sharply [8]. Kenya is ranked second highest among African countries, in bird and mammal species richness with an estimate of 394 mammals, 1100
References
[1]
T. Flannery, The Eternal Frontier: An Ecological History of North America and Its Peoples, Atlantic Monthly Press, New York, NY, USA, 2001.
[2]
H. H. T. Prins, “The pastoral road to extinction: competition between wildlife and traditional pastoralism in East Africa,” Environmental Conservation, vol. 19, no. 2, pp. 117–123, 1992.
[3]
C. Van Der Waal and B. Dekker, “Game ranching in the Northern Province of South Africa,” South African Journal of Wildlife Research, vol. 30, no. 4, pp. 151–156, 2000.
[4]
Z. A. Ogutu, “The impact of ecotourism on livelihood and natural resource management in Eselenkei, Amboseli Ecosystem, Kenya,” Land Degradation and Development, vol. 13, no. 3, pp. 251–256, 2002.
[5]
Government of Kenya, The National Wildlife Conservation and Management Policy, 2012, Ministry of Forestry and Wildlife, Government Printer, 2011.
[6]
D. T. Bolger, W. D. Newmark, T. A. Morrison, and D. F. Doak, “The need for integrative approaches to understand and conserve migratory ungulates,” Ecology Letters, vol. 11, no. 1, pp. 63–77, 2008.
[7]
D. Western, S. Russell, and I. Cuthil, “The status of wildlife in protected areas compared to non-protected areas of Kenya,” PLoS ONE, vol. 4, no. 7, Article ID e6140, 2009.
[8]
D. Western and D. L. Manzolillo-Nightingale, “Environmental change and the vulnerability of pastoralists to drought: a case study of the Maasai in Amboseli, Kenya,” in Africa Environment Outlook Case Studies: Human Vulnerability to Environmental Change, pp. 35–50, UNEP, Nairobi, Kenya, 2004.
[9]
J. M. Grunblatt, M. Said, and P. Wargute, National Rangelands Report. Summary of Population Estimates of Wildlife and Livestock (1977–1994), Department of Resource Surveys and Remote Sensing, Ministry of Planning and National Development, Nairobi, Kenya, 1996.
[10]
IUCN, IUCN Red List of Threatened Species, IUCN, Gland, Switzerland, 2008, http://www.iucnredlist.org/.
[11]
M. Loibooki, H. Hofer, K. L. I. Campbell, and M. L. East, “Bushmeat hunting by communities adjacent to the Serengeti National Park, Tanzania: the importance of livestock ownership and alternative sources of protein and income,” Environmental Conservation, vol. 29, no. 3, pp. 391–398, 2002.
[12]
M. Norton-Griffiths, M. Y. Said, S. Serneels et al., “Land use economics in the mara area of the serengeti ecosystem,” in Serengeti III: Human Wildlife Interactions, C. Packer and A. R. E. Sinclair, Eds., pp. 379–416, University of Chicago Press, Chicago, Ill, USA, 2009.
[13]
O. E. Sala, F. S. Chapin, J. J. Armesto et al., “Global biodiversity scenarios for the year 2100,” Science, vol. 287, no. 5459, pp. 1770–1774, 2000.
[14]
E. F. Lambin, B. L. Turner, H. J. Geist, et al., “The causes of land-use and land-cover change: moving beyond the myths,” Global Environmental Change, vol. 11, no. 4, pp. 261–269, 2001.
[15]
J. M. Maitima, M. M. Simon, R. S. Robin et al., “The linkages between land use change, land degradation and biodiversity across East Africa,” African Journal of Environmental Science and Technology, vol. 3, no. 10, pp. 310–325, 2009.
[16]
I. J. Gordon, “What is the future for wild, large herbivores in human-modified agricultural landscapes,” Wildlife Biology, vol. 15, no. 1, pp. 1–9, 2009.
[17]
M. M. Okello, E. Buthmann, B. Mapinu, and H. C. Kahi, “Community opinions on wildlife, resource use and livelihood competition in Kimana group ranch near Amboseli, Kenya,” Open Conservation Biology Journal, vol. 5, no. 1, pp. 1–12, 2011.
[18]
W. D. Newmark, “The role and design of wildlife corridors with examples from Tanzania,” Ambio, vol. 22, no. 8, pp. 500–504, 1993.
[19]
D. J. Campbell, H. Gichohi, A. Mwangi, and L. Chege, “Land use conflict in Kajiado District, Kenya,” Land Use Policy, vol. 17, no. 4, pp. 337–348, 2000.
[20]
I. Sindiga, “Wildlife based tourism in Kenya: land use conflicts and government compensation polices over protected areas,” Journal Tourism Study, vol. 6, no. 2, pp. 45–55, 1995.
[21]
M. M. Okello, “Land use changes and human-wildlife conflict in the Amboseli Area,” Human Dimension Wildlife, vol. 10, no. 1, pp. 19–28, 2005.
[22]
M. M. Okello and J. W. Kiringe, “Threats to biodiversity and their implications in protected and adjacent dispersal areas of Kenya,” Journal of Sustainable Tourism, vol. 12, no. 1, pp. 55–69, 2004.
[23]
M. M. Okello, “Contraction of wildlife dispersal area and displacement by human activities in Kimana Group Ranch near Amboseli National Park, Kenya,” Conservation Biology Journal, vol. 3, pp. 49–56, 2009.
[24]
J. H. Zar, Biostatistical Analysis, Prentice-Hall, Upper Saddle River, NJ, USA, 4th edition, 1999.
[25]
Government of Kenya, Loitokitok District Development Plan 2008–2012, The Government Printer, Nairobi, Kenya, 2008.
[26]
KWS, Amboseli Ecosystem Management Plan 2008–2018, KWS, Nairobi, Kenya, 2009.
[27]
T. P. Young and T. R. McClanahan, “Island biogeography and species extinction,” in East African Ecosystems and Their Conservation, T. R. McClanahan and T. P. Young, Eds., pp. 292–293, Oxford University Press, New York, NY, USA, 1996.