The Cost Efficiency of Wild Dog Conservation in South Africa

Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into is...

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Published in:Conservation biology Vol. 19; no. 4; pp. 1205 - 1214
Main Authors: LINDSEY, P. A., ALEXANDER, R., DU TOIT, J. T., MILLS, M.G.L.
Format: Journal Article
Language:English
Published: 350 Main Street , Malden , MA 02148 , USA , and 9600 Garsington Road , Oxford OX4 2DQ , UK Blackwell Publishing, Inc 01.08.2005
Blackwell Science
Blackwell
Blackwell Publishing Ltd
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ISSN:0888-8892, 1523-1739
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Abstract Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into isolated fenced reserves. Additional potential exists for conserving wild dogs on private ranch land. Establishing the metapopulation was an expensive process, accounting for approximately 75% of the US$380,000 spent on wild dog conservation in South Africa during 1997-2001. The principal goal of the metapopulation project was to reduce the risk of catastrophic population decline. Now that this has been achieved, we developed a uniform cost-efficiency index to estimate the cost efficiency of current and potential future conservation strategies in South Africa. Conserving wild dogs in large protected areas was predicted to be the most cost-efficient conservation strategy (449 packs/$100,000 expenditure). Establishing the metapopulation has been less cost efficient (23 packs/$ 100,000), and expansion of the metapopulation was predicted to be even less cost efficient if predation by wild dogs results in additional costs, as is to be expected if private reserves are used for reintroductions (3-13 packs/$100,000). Because of low logistical costs, conserving wild dogs in situ on private ranch land was potentially more cost efficient than reintroducing wild dogs (14-27 packs/$100,000). We recommend that donor funding be used to reintroduce wild dogs into transfrontier parks, when they are established, to maintain the existing metapopulation and to establish conservation programs involving wild dogs on private ranch land. Investing in the expansion of the metapopulation should be limited to state-owned nature reserves willing to carry predation costs without compensation.
AbstractList Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into isolated fenced reserves. Additional potential exists for conserving wild dogs on private ranch land. Establishing the metapopulation was an expensive process, accounting for approximately 75% of the US$380,000 spent on wild dog conservation in South Africa during 1997-2001. The principal goal of the metapopulation project was to reduce the risk of catastrophic population decline. Now that this has been achieved, we developed a uniform cost-efficiency index to estimate the cost efficiency of current and potential future conservation strategies in South Africa. Conserving wild dogs in large protected areas was predicted to be the most cost-efficient conservation strategy (449 packs-$100,000 expenditure). Establishing the metapopulation has been less cost efficient (23 packs-$100,000), and expansion of the metapopulation was predicted to be even less cost efficient if predation by wild dogs results in additional costs, as is to be expected if private reserves are used for reintroductions (3-13 packs-$100,000). Because of low logistical costs, conserving wild dogs in situ on private ranch land was potentially more cost efficient than reintroducing wild dogs (14-27 packs-$100,000). We recommend that donor funding be used to reintroduce wild dogs into transfrontier parks, when they are established, to maintain the existing metapopulation and to establish conservation programs involving wild dogs on private ranch land. Investing in the expansion of the metapopulation should be limited to state-owned nature reserves willing to carry predation costs without compensation.Original Abstract: Ademas del Parque Nacional Kruger, en Africa del Sur no existen otras reservas de suficiente tamano como para mantener una poblacion viable de perros salvajes (Lycaon pictus). En consecuencia, los esfuerzos de conservacion se han enfocado en la creacion de una metapoblacion por medio de una serie de reintroducciones en pequenas reservas cercadas. Hay un potencial adicional para la conservacion de perros salvajes en terrenos privados. El establecimiento de la metapoblacion fue un proceso costoso, similar to 75% de US $380,000 que fueron gastados en la conservacion de perros salvajes entre 1997 y 2001 en Africa del Sur. La meta principal del proyecto de metapoblacion fue la reduccion del riesgo de una declinacion catastrofica de la poblacion. Ya que esto se ha logrado, desarrollamos un indice de rentabilidad uniforme para estimar la rentabilidad de las actuales y potenciales estrategias de conservacion en Africa del Sur. Se predijo que la estrategia de conservacion de mas rentable (449manadas-$100,000 de gasto) era la conservacion de perros salvajes en areas protegidas grandes. El establecimiento de la metapoblacion ha sido menos rentable (23 manadas-$100,000), y se predijo que la expansion de la metapoblacion seria aun menos rentable si la depredacion por perros salvajes resulta en costos adicionales, como se esperaria si se utilizan reservas privadas para las reintroducciones (3-13 manadas-$100,000). Debido a los bajos costos de logistica, la conservacion de perros salvajes in situ en terrenos privados fue potencialmente mas rentable que reintroducir a los perros salvajes (14-27 manadas-$100,000). Recomendamos que el financiamiento de donantes sea utilizado para reintroducir perros salvajes en parque transfronterizos, cuando sean establecidos, para mantener a la metapoblacion existente y para establecer programas de conservacion que involucren a perros salvajes en terrenos privados. La inversion en la expansion de la metapoblacion debera limitarse a reservas naturales propiedad del estado que esten dispuestas a absorber los costos de la depredacion sin ser compensadas.
Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into isolated fenced reserves. Additional potential exists for conserving wild dogs on private ranch land. Establishing the metapopulation was an expensive process, accounting for approximately 75% of the US$380,000 spent on wild dog conservation in South Africa during 1997‐2001. The principal goal of the metapopulation project was to reduce the risk of catastrophic population decline. Now that this has been achieved, we developed a uniform cost‐efficiency index to estimate the cost efficiency of current and potential future conservation strategies in South Africa. Conserving wild dogs in large protected areas was predicted to be the most cost‐efficient conservation strategy (449 packs/$100,000 expenditure). Establishing the metapopulation has been less cost efficient (23 packs/$100,000), and expansion of the metapopulation was predicted to be even less cost efficient if predation by wild dogs results in additional costs, as is to be expected if private reserves are used for reintroductions (3‐13 packs/$100,000). Because of low logistical costs, conserving wild dogs in situ on private ranch land was potentially more cost efficient than reintroducing wild dogs (14‐27 packs/$100,000). We recommend that donor funding be used to reintroduce wild dogs into transfrontier parks, when they are established, to maintain the existing metapopulation and to establish conservation programs involving wild dogs on private ranch land. Investing in the expansion of the metapopulation should be limited to state‐owned nature reserves willing to carry predation costs without compensation.
Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into isolated fenced reserves. Additional potential exists for conserving wild dogs on private ranch land. Establishing the metapopulation was an expensive process, accounting for approximately 75% of the US$380,000 spent on wild dog conservation in South Africa during 1997-2001. The principal goal of the metapopulation project was to reduce the risk of catastrophic population decline. Now that this has been achieved, we developed a uniform cost-efficiency index to estimate the cost efficiency of current and potential future conservation strategies in South Africa. Conserving wild dogs in large protected areas was predicted to be the most cost-efficient conservation strategy (449 packs/$100,000 expenditure). Establishing the metapopulation has been less cost efficient (23 packs/$100,000), and expansion of the metapopulation was predicted to be even less cost efficient if predation by wild dogs results in additional costs, as is to be expected if private reserves are used for reintroductions (3-13 packs/$100,000). Because of low logistical costs, conserving wild dogs in situ on private ranch land was potentially more cost efficient than reintroducing wild dogs (14-27 packs/$100,000). We recommend that donor funding be used to reintroduce wild dogs into transfrontier parks, when they are established, to maintain the existing metapopulation and to establish conservation programs involving wild dogs on private ranch land. Investing in the expansion of the metapopulation should be limited to state-owned nature reserves willing to carry predation costs without compensation. [PUBLICATION ABSTRACT]
:  Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon pictus). Consequently, conservation efforts have been focused on creating a metapopulation through a series of wild dog reintroductions into isolated fenced reserves. Additional potential exists for conserving wild dogs on private ranch land. Establishing the metapopulation was an expensive process, accounting for approximately 75% of the US$380,000 spent on wild dog conservation in South Africa during 1997‐2001. The principal goal of the metapopulation project was to reduce the risk of catastrophic population decline. Now that this has been achieved, we developed a uniform cost‐efficiency index to estimate the cost efficiency of current and potential future conservation strategies in South Africa. Conserving wild dogs in large protected areas was predicted to be the most cost‐efficient conservation strategy (449 packs/$100,000 expenditure). Establishing the metapopulation has been less cost efficient (23 packs/$100,000), and expansion of the metapopulation was predicted to be even less cost efficient if predation by wild dogs results in additional costs, as is to be expected if private reserves are used for reintroductions (3‐13 packs/$100,000). Because of low logistical costs, conserving wild dogs in situ on private ranch land was potentially more cost efficient than reintroducing wild dogs (14‐27 packs/$100,000). We recommend that donor funding be used to reintroduce wild dogs into transfrontier parks, when they are established, to maintain the existing metapopulation and to establish conservation programs involving wild dogs on private ranch land. Investing in the expansion of the metapopulation should be limited to state‐owned nature reserves willing to carry predation costs without compensation. Resumen:  Además del Parque Nacional Kruger, en África del Sur no existen otras reservas de suficiente tamaño como para mantener una población viable de perros salvajes (Lycaon pictus). En consecuencia, los esfuerzos de conservación se han enfocado en la creación de una metapoblación por medio de una serie de reintroducciones en pequeñas reservas cercadas. Hay un potencial adicional para la conservación de perros salvajes en terrenos privados. El establecimiento de la metapoblación fue un proceso costoso, ∼75% de US $380,000 que fueron gastados en la conservación de perros salvajes entre 1997 y 2001 en África del Sur. La meta principal del proyecto de metapoblación fue la reducción del riesgo de una declinación catastrófica de la población. Ya que esto se ha logrado, desarrollamos un índice de rentabilidad uniforme para estimar la rentabilidad de las actuales y potenciales estrategias de conservación en África del Sur. Se predijo que la estrategia de conservación de más rentable (449manadas/$100,000 de gasto) era la conservación de perros salvajes en áreas protegidas grandes. El establecimiento de la metapoblación ha sido menos rentable (23 manadas/$100,000), y se predijo que la expansión de la metapoblación sería aun menos rentable si la depredación por perros salvajes resulta en costos adicionales, como se esperaría si se utilizan reservas privadas para las reintroducciones (3‐13 manadas/$100,000). Debido a los bajos costos de logística, la conservación de perros salvajes in situ en terrenos privados fue potencialmente más rentable que reintroducir a los perros salvajes (14‐27 manadas/$100,000). Recomendamos que el financiamiento de donantes sea utilizado para reintroducir perros salvajes en parque transfronterizos, cuando sean establecidos, para mantener a la metapoblación existente y para establecer programas de conservación que involucren a perros salvajes en terrenos privados. La inversión en la expansión de la metapoblación deberá limitarse a reservas naturales propiedad del estado que estén dispuestas a absorber los costos de la depredación sin ser compensadas.
Author ALEXANDER, R.
MILLS, M.G.L.
DU TOIT, J. T.
LINDSEY, P. A.
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  fullname: DU TOIT, J. T.
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  givenname: M.G.L.
  surname: MILLS
  fullname: MILLS, M.G.L.
  organization: Mammal Research Institute, University of Pretoria, Pretoria, 0002, South Africa
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Issue 4
Keywords Fissipedia
Carnivora
Costs
Metapopulation
Extensive rearing
game ranching
Population structure
Canis familiaris
Reintroduction
Vertebrata
Lycaon pictus
Mammalia
Game
donor funding
Environmental protection
Language English
License CC BY 4.0
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PublicationCentury 2000
PublicationDate August 2005
PublicationDateYYYYMMDD 2005-08-01
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  text: August 2005
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PublicationPlace 350 Main Street , Malden , MA 02148 , USA , and 9600 Garsington Road , Oxford OX4 2DQ , UK
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PublicationTitle Conservation biology
PublicationYear 2005
Publisher Blackwell Publishing, Inc
Blackwell Science
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References Lindsey , P. A. , J. T. du Toit , and M. G. L. Mills . 2004 . The distribution and population status of African wild dogs Lycaon pictus outside protected areas in South Africa . South African Journal of Wildlife Research 34 : 143 - 151 .
Creel , S. and N. M. Creel . 1995 . Communal hunting and pack size in African wild dogs, Lycaon pictus . Animal Behaviour 50 : 1325 - 1339 .
Moran , D. , D. Pearce , and A. Wendelaar . 1997 . Investing in biodiversity: an economic perspective on global priority setting . Biodiversity and Conservation 6 : 1219 - 1243 .
Balmford , A. and T. Whitten . 2003 . Who should pay for tropical conservation and how should the costs be met ? Oryx 37 : 238 - 250 .
Maddock , A. H. and M. G. L. Mills . 1994 . Population characteristics of African wild dogs Lycaon pictus in the eastern Transvaal Lowveld, South Africa, as revealed through photographic records . Biological Conservation 67 : 57 - 62 .
Ando , A. , J. Camm , S. Polasky , and A. Solow . 1998 . Species distributions, land values and efficient conservation . Science 279 : 2126 - 2128 .
James , A. N. , K. J. Gaston , and A. Balmford . 1999 . Balancing the earth's accounts . Nature 401 : 323 - 324 .
Myers , N. , R. A. Mittermeier , C. G. Mittermeier , G. A. B. da Fonseca , and J. Kent . 2000 . Biodiversity hotspots for conservation priorities . Nature 403 : 853 - 858 .
Woodroffe , R. , P. A. Lindsey , S. S. R. Romanach , A. Stein , and S. M. K. Ole Ranah . 2005 . Livestock predation by endangered African wild dogs Lycaon pictus in northern Kenya . Biological Conservation 124 : 225 - 234 .
Restani , M. , and J. M. Marzluff . 2002 . Funding extinction? Biological needs and political realities in the allocation of benefits to endangered species recovery . BioScience 52 : 169 - 177 .
Pyare , S. and J. Berger . 2003 . Beyond demography and delisting: ecological recovery for Yellowstone's grizzly bears and wolves . Biological Conservation 113 : 63 - 73 .
Balmford , A. , et al. 2002 . Economic reasons for conserving wild nature . Science 297 : 950 - 953 .
Falkena , H. 2000 . Bulls, bears and lions: game ranch profitability in South Africa . The S.A. Financial Sector Forum, Rivonia , South Africa .
Cumming , D. H. M. 1991 . Developments in game ranching and wildlife utilisation in east and southern Africa . Pages 96 - 108 in L. A. Renecker and R. J. Hudson , editors . Wildlife production: conservation and sustainable development . University of Alaska , Fairbanks .
Main , M. B. , F. M. Roka , and R. F. Noss . 1999 . Evaluating costs of conservation . Conservation Biology 13 : 1262 - 1272 .
Blumenschine , R. and T. Caro . 1986 . Unit flesh weights of some East African bovids . African Journal of Ecology 24 : 273 - 286 .
Skinner , J. D. , and R. H. N. Smithers . 1990 . The mammals of the southern African subregion . University of Pretoria Press , Pretoria .
Woodroffe , R. , and J. R. Ginsberg . 1998 . Edge effects and the extinction of populations inside protected areas . Science 280 : 2126 - 2128 .
Hughey , K. F. D. , R. Cullen , and E. Moran . 2003 . Integrating economics into priority setting and evaluation in conservation management . Conservation Biology 17 : 93 - 103 .
Mills , M. G. L. and M. L. Gorman . 1997 . Factors affecting the density and distribution of wild dogs in the Kruger National Park . Conservation Biology 11 : 1397 - 1406 .
van der Waal , C. , and B. Dekker . 2000 . Game ranching in the Northern Province of South Africa . South African Journal of Wildlife Research 30 : 151 - 156 .
Fuller , T. and P. W. Kat . 1990 . Movements, activity and prey relationships of African wild dogs (Lycaon pictus) near Aitong, southwestern Kenya . African Journal of Ecology 28 : 330 - 350 .
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Lindsey , P. A. , J. T. du Toit , and M. G. Mills . 2005a . Attitudes of ranchers towards African wild dogs Lycaon pictus: conservation implications on private land . Biological Conservation 125 : 113 - 121 .
Knobel , D. L. and J. T. du Toit . 2003 . The influence of pack social structure on oral rabies vaccination coverage in captive African wild dogs Lycaon pictus . Applied Animal Behaviour Science 80 : 61 - 70 .
Mills , M. G. L. and H. C. Biggs . 1993 . Prey apportionment and related ecological relationships between large carnivores in the Kruger National Park . Symposia of the Zoological Society of London 65 : 253 - 268 .
Balmford , A. , K. Gaston , S. Blyth , A. James , and V. Kapos . 2003 . Global variation in terrestrial costs, conservation benefits, and unmet conservation needs . Proceedings of the National Academy of Science 100 : 1046 - 1050 .
Coe , M. , D. Cumming . and J. Phillipson . 1976 . Biomass and production of large African herbivores in relation to rainfall and primary production . Oecologia 22 : 341 - 354 .
Baker , B. 1999 . Spending on the Endangered Species Act-too much or not enough ? BioScience 49 : 279 .
Creel , S. and N. M. Creel . 2002 . The African wild dog: behaviour, ecology and conservation . Princeton University Press , Princeton , New Jersey .
Nagy , K. A. 2001 . Food requirements of wild animals: predictive equations for free living mammals, reptiles and birds . Nutrition Abstracts and Reviews 71 : 1 - 12 .
Miller , J. K. , J. M. Scott , C. R. Miller , and L. P. Waits . 2002 . The Endangered Species Act: dollars and sense ? BioScience 52 : 163 - 168 .
Frantzen , M. A. J. , J. W. H. Ferguson , and M. S. Devilliers . 2001 . The conservation role of captive African wild dogs (Lycaon pictus) . Biological Conservation 100 : 253 - 260 .
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2001; 100
1998; 26
2001; 71
1995; 50
1998; 280
2003; 80
1976; 22
2002; 52
2002; 297
1999; 49
1993; 65
1999; 26
1994; 67
1998
1997
2003; 37
1995
2003; 17
1998; 279
1993
1992
2002
1991
1997; 6
1999; 401
2003; 113
1999; 248
1999
1997; 11
1990
2000
1990; 28
2005; 124
2000; 403
1986; 24
2004; 34
2000; 30
1999; 13
2005a; 125
2005b; 123
2003; 100
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Mills M. G. L. (e_1_2_6_29_1) 1993; 65
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Davies H. T. (e_1_2_6_12_1) 2000
Lindsey P. A. (e_1_2_6_22_1) 2004; 34
van der Waal C. (e_1_2_6_39_1) 2000; 30
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Woodroffe R. (e_1_2_6_42_1) 1997
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Skinner J. D. (e_1_2_6_38_1) 1990
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– reference: Balmford , A. and T. Whitten . 2003 . Who should pay for tropical conservation and how should the costs be met ? Oryx 37 : 238 - 250 .
– reference: Nagy , K. A. 2001 . Food requirements of wild animals: predictive equations for free living mammals, reptiles and birds . Nutrition Abstracts and Reviews 71 : 1 - 12 .
– reference: Knobel , D. L. and J. T. du Toit . 2003 . The influence of pack social structure on oral rabies vaccination coverage in captive African wild dogs Lycaon pictus . Applied Animal Behaviour Science 80 : 61 - 70 .
– reference: Woodroffe , R. , P. A. Lindsey , S. S. R. Romanach , A. Stein , and S. M. K. Ole Ranah . 2005 . Livestock predation by endangered African wild dogs Lycaon pictus in northern Kenya . Biological Conservation 124 : 225 - 234 .
– reference: Balmford , A. , K. Gaston , S. Blyth , A. James , and V. Kapos . 2003 . Global variation in terrestrial costs, conservation benefits, and unmet conservation needs . Proceedings of the National Academy of Science 100 : 1046 - 1050 .
– reference: Creel , S. and N. M. Creel . 1995 . Communal hunting and pack size in African wild dogs, Lycaon pictus . Animal Behaviour 50 : 1325 - 1339 .
– reference: Baker , B. 1999 . Spending on the Endangered Species Act-too much or not enough ? BioScience 49 : 279 .
– reference: Mills , M. G. L. and M. L. Gorman . 1997 . Factors affecting the density and distribution of wild dogs in the Kruger National Park . Conservation Biology 11 : 1397 - 1406 .
– reference: Hughey , K. F. D. , R. Cullen , and E. Moran . 2003 . Integrating economics into priority setting and evaluation in conservation management . Conservation Biology 17 : 93 - 103 .
– reference: Skinner , J. D. , and R. H. N. Smithers . 1990 . The mammals of the southern African subregion . University of Pretoria Press , Pretoria .
– reference: Blumenschine , R. and T. Caro . 1986 . Unit flesh weights of some East African bovids . African Journal of Ecology 24 : 273 - 286 .
– reference: Moran , D. , D. Pearce , and A. Wendelaar . 1997 . Investing in biodiversity: an economic perspective on global priority setting . Biodiversity and Conservation 6 : 1219 - 1243 .
– reference: Creel , S. and N. M. Creel . 2002 . The African wild dog: behaviour, ecology and conservation . Princeton University Press , Princeton , New Jersey .
– reference: Guikema , S. , and M. Milke . 1999 . Quantitative decision tools for conservation programme planning: practice, theory and potential . Environmental Conservation 26 : 179 - 189 .
– reference: Mech , L. D. 1998 . Estimated costs of maintaining a recovered wolf population in agricultural regions of Minnesota . Wildlife Society Bulletin 26 : 817 - 822 .
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– reference: Main , M. B. , F. M. Roka , and R. F. Noss . 1999 . Evaluating costs of conservation . Conservation Biology 13 : 1262 - 1272 .
– reference: Lindsey , P. A. , J. T. du Toit , and M. G. L. Mills . 2004 . The distribution and population status of African wild dogs Lycaon pictus outside protected areas in South Africa . South African Journal of Wildlife Research 34 : 143 - 151 .
– reference: Mills , M. G. L. and H. C. Biggs . 1993 . Prey apportionment and related ecological relationships between large carnivores in the Kruger National Park . Symposia of the Zoological Society of London 65 : 253 - 268 .
– reference: Myers , N. , R. A. Mittermeier , C. G. Mittermeier , G. A. B. da Fonseca , and J. Kent . 2000 . Biodiversity hotspots for conservation priorities . Nature 403 : 853 - 858 .
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– reference: Miller , J. K. , J. M. Scott , C. R. Miller , and L. P. Waits . 2002 . The Endangered Species Act: dollars and sense ? BioScience 52 : 163 - 168 .
– reference: Maddock , A. H. and M. G. L. Mills . 1994 . Population characteristics of African wild dogs Lycaon pictus in the eastern Transvaal Lowveld, South Africa, as revealed through photographic records . Biological Conservation 67 : 57 - 62 .
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Snippet Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon...
:  Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs (Lycaon...
Aside from Kruger National Park, no other suitable reserves of sufficient size exist in South Africa that will hold a viable population of wild dogs ( Lycaon...
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SubjectTerms Animal, plant and microbial ecology
Applied ecology
Biological and medical sciences
Conservation
conservation areas
Conservation biology
conservation programs
Conservation, protection and management of environment and wildlife
Cost benefit analysis
Cost efficiency
Cost estimates
crianza de especies cinegéticas
Dogs
donor funding
financiamiento de donantes
Fundamental and applied biological sciences. Psychology
funding
game ranching
Habitat conservation
Lycaon pictus
Mammalia
metapoblación
metapopulation
Metapopulation ecology
Metapopulations
National parks
Nature conservation
Nature reserves
Parks, reserves, wildlife conservation. Endangered species: population survey and restocking
Population decline
population dynamics
predation
Protected areas
Ranches
ranching
reintroducción
reintroduction
risk
Risk reduction
South Africa
Vertebrates: general zoology, morphology, phylogeny, systematics, cytogenetics, geographical distribution
Wildlife conservation
Title The Cost Efficiency of Wild Dog Conservation in South Africa
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