Open access

Introductory Chapter: Managing Wildlife in a Changing World - Trends, Drivers and the Way Forward

Written By

Jafari R. Kideghesho

Submitted: 10 May 2021 Published: 08 December 2021

DOI: 10.5772/intechopen.98851

From the Edited Volume

Managing Wildlife in a Changing World

Edited by Jafari R. Kideghesho

Chapter metrics overview

247 Chapter Downloads

View Full Metrics

1. Introduction

The wildlife managers, scientists and policy makers globally, are striving to ensure the survival of wildlife resources in the face of rapid changes in socio-economic, ecological, political and technological aspects. One of the key and popular strategies that have been adopted to conserve wildlife species is the establishment of different categories of protected areas. A protected area is defined as “geographical space, recognized, dedicated and managed, through legal or other effective means, to achieve the long term conservation of nature with associated ecosystem services and cultural values” [1]. Since the establishment of Yellowstone National Park in 1872 - the first protected area in the world - a number of protected areas has been growing over time. In 2010, there were about 161,000 protected areas [2]. The 2016 Protected Planet Report [3] indicated an increase to 202,470 protected areas spanning about 20 million square kilometers (15% of the world’s land, excluding Antarctica). As of August 2020, the number increased beyond 260,000 [4].

Establishment of protected areas has been complemented with many other strategies. Local and global commitment have been apparent through enacting and enforcement of numerous laws; provision of alternative livelihood strategies as a substitution to ecologically destructive activities; and supporting community-based conservation programmes including conservation education and awareness creation, benefit-sharing schemes, among others.

Local, regional and international instruments have been established to spearhead the conservation efforts and stem the causes of species loss. The popular international instruments, among others, include Convention on International Trade in Endangered Species of Flora and Fauna – CITES (year of entry into force: 1975), Convention of Biological Diversity -CBD (1993), Convention on Wetlands -popularly known as the Ramsar Convention (1971), Convention on the Conservation of migratory species of wild animals -CMS or Bonn Convention (1975) and World Heritage Convention - WHC (1972). The regional instruments include The Lusaka Agreement on Co-operative Enforcement Operations Directed at Illegal Trade in Wild Fauna and Flora; The Southern Africa Development Community Protocol on Wildlife Conservation and Law Enforcement; The Convention on Conservation of Nature in the South Pacific; ASEAN Agreement on the Conservation of Nature and Natural Resources’ and Convention on the Conservation of European Wildlife and Natural Habitats (Bern Convention).

Advertisement

2. Declining trends and drivers

Despite efforts which are being devoted locally, regionally and globally to curb the threats facing wildlife, it is increasingly becoming evident that these efforts are not matching the rates of the threats. The UN Report titled Nature’s Dangerous Decline ‘Unprecedented’; Species Extinction Rates ‘Accelerating’ released by the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services (IPBES), indicates that roughly one million animal and plant species are currently threatened with extinction [5]. According to the Report, most major land-based habitats have lost at least 20% of the average abundance of their native species since 1900. Over 40% of amphibian species and 33% all marine mammals, respectively, are threatened with extinction. Since the 16th century about 680 vertebrate species have been driven to extinction [5]. Furthermore, the recent report of IUCN Redlist of Threatened Species has revealed that, out of 158,908 species of vertebrates assessed, 35,300 (equal to 28%) are threatened with extinction [6]. Among other species, the declining trends involve the umbrella, keystone and charismatic species such as black rhino (Bicornis diceros), African elephant (Loxodonta africana), tiger (Panthera tigris), African lion (Panthera leo) and leopard (Panthera pardus) [7, 8, 9, 10, 11, 12].

The declining trends of wildlife species and biodiversity in general, is a function of multiple factors (Figure 1) associated with socio-economic, ecological, technological or political changes. Growing human demand for food, timber, water and space is increasingly causing habitat loss and deterioration and, thus, subjecting many species to a risk of extinction [12]. According to IPBES Report (5), about 47% of natural ecosystems have declined globally and over 9% of the world’s estimated 5.9 million terrestrial species have insufficient habitat for long term survival without efforts to restore the degraded habitats. Reduced home ranges for different wildlife species and blockage of corridors are exacerbating property damage and human mortalities and, therefore, inciting pre-emptive or retaliatory killing [12, 13]. Likewise, poaching and illegal wildlife trade has accelerated declining rates to species of high economic value such as rhino, elephant, pangolins and tiger [14, 15, 16, 17, 18, 19].

Figure 1.

Increasing trends of protected areas globally from 1990 to 2016 [3].

Human population growth is the main driving force behind most of the threats facing wildlife species. It is linked to current trends of invasive species, climate change, wildlife crime, pollution, and habitat loss and human-wildlife conflicts. The current world population of 7.8 billion [20] is projected to reach 8.6 billion in 2030; 9.8 billion in 2050 and 11.2 billion in 2100 [21]. These projections signify that demand and consumption for resources such as food, fuel, timber and space will increase significantly at the expense of wildlife species as more land will be transformed into human settlements and infrastructures. It is estimated that humans and domesticated livestock account for about 36 and 60 percent of the biomass of all mammals on Earth, respectively, while wild mammals have declined to only 4 percent [22].

Blockage of wildlife corridors and, subsequently, habitats fragmentation is rendering many protected areas isolated as ecological islands [23, 24, 25]. Disruption of the ecological linkage between different animal populations, consequently, reduces the genetic variability due to inbreeding depression [12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25, 26, 27]. Furthermore, loss of wildlife corridors and dispersal areas compromise their roles in minimizing human-wildlife conflicts, provision of alternative foraging or breeding grounds and serving as a refuge against adverse weather conditions [27].

Technological advancement, improved accessibility to remote areas and availability of markets for wildlife products have also worsened the destruction of habitats and depletion of wildlife species [28, 29, 30, 31]. Emerging of new economic opportunities and increasing need for development are giving rise to adoption of policy choices that are economically rewarding but ecologically damaging such as mining, industrial agriculture and construction of infrastructures [32, 33, 34, 35, 36, 37]. Political unrest and associated effects such as insecurity, proliferation of firearms, influx of refugees and disruption of operations of protected areas has contributed enormously to the increased decimation of wildlife populations and destruction of habitats [38, 39, 40].

Climate change is increasingly featuring as one of the important global agenda impacting nature and human life. The main driver of climate change is destruction of nature through human actions such as increased use of fossil fuels, deforestation and intensive agriculture. Food insecurity and income poverty ensuing as a result of climate change leave people with limited livelihood options, a situation that may prompt engagement of people in poaching and habitat destruction [41]. Climate change accelerates habitat threshold and increases risk to species in fragmented habitats [42]. Climate change is confirmed to facilitate the increase of wildlife diseases [43, 44, 45], spread of invasive species [45, 46, 47] and escalation of human-wildlife conflicts [12, 48].

In recent decades the number of invasive alien species has kept on growing and thus posing a serious threat to native wildlife species [49, 50, 51, 52]. Nearly 40% of introductions of invasive alien species in the past two centuries occurred between 1970 and 2014 [46]. According to Seebens et al. [53] the projected overall increase of alien species between 2005 and 2050 was 36% per continent. The challenge is increasing in tandem with the changes which are taking place globally such as international trade; global transport of goods, population changes, migration, pollution, tourism, recreation, climate change and economic development such as land use and energy consumption [54, 55, 56, 57, 58, 59]. Invasive alien species present threat to native species by outcompeting them for food and other resources, destroying their habitats, introducing diseases, thwarting reproduction of native species, preying on native species or killing the young of native species [60, 61, 62, 63]. The proportion of threatened or endangered species facing a risk of extinction because of invasive species is estimated at 42% [64]. Among other threats, Invasive species are currently threatening 27% of the globally threatened terrestrial species of mammals, birds and reptiles included on the IUCN Red List, and 40% of the critically endangered species, in particular [52].

Human population growth, urbanization, habitat loss, poverty, climate change and improved conservation measures, among other drivers, are intensifying human-wildlife conflicts in many parts of the world. Numerous wildlife species are subjected to risk as human-wildlife conflicts intensify. Economic loss and mortalities caused by problem and dangerous animals incite retaliation in form of killing and destroying wildlife and their habitats [48]. Similarly, population growth, destruction of ecosystems, climate change along with increased human activities such as industrialization, mining, water-waste, metal refining and the burning of fossil fuels are exacerbating pollution in form of synthetic chemicals, oil spills, toxic metals and acid rain. The documented impacts of pollutants to wildlife species include immediate deaths, habitat destruction, reduced or impaired reproduction, cancer, neurological damage, liver damage, muscle atrophy and immune suppression to diseases [65, 66, 67].

Increasing human impacts on ecosystems, climate change, invasive alien species and pollution are attributed to emerging and re-emerging of diseases affecting humans and non-human species [65, 68, 69, 70, 71]. Human-induced changes on land use and land cover through modification of natural habitats are responsible for over 50% of the emerging zoonoses [72, 73, 74, 75, 76]. Given the global human population growth and deforestation rate, estimated at 10 million hectares per annum [76], it is indisputably that the risk of animal-to-human diseases transmission will increase talong with increased proximity of humans and livestock to natural habitats. Diseases have both direct and indirect impacts on wildlife species. Direct impacts involve effect of a disease on the health of animal species which can subsequently lead to deaths. Examples of diseases with direct impact on the health of animals are anthrax and Canine Distemper Virus Disease. Indirect impacts are impacts which disrupt the management interventions of the species and habitats. For instance, emerging of pandemics (e.g., Ebola and COVID-19) and, consequently, imposition of travel restrictions and lockdown had reduced revenues from tourism and impacted the livelihood of many people. This has denied conservation authorities adequate resources for conservation and, therefore, subjecting wildlife species to risks including poaching [75].

Advertisement

3. The way forward

Reversing the declining and extinction trends that the world is experiencing today calls for effective planning, innovations and adoption of approaches that are developed through scientific realities. Understanding of the factors and the mechanisms in which they influence the survival of wildlife is critical in devising the mitigation against the current challenges facing wildlife. Deliberate efforts are required to address the underlying and proximate causes of the declining trends and extinction of wildlife species. This book “Managing Wildlife in a Changing World” presents issues and possible options for effective management of wildlife in a world where the changes are no longer speculative, but a reality and inevitable. By reading the Book, you will realize that not all conservation issues require biological solutions. Sociological approaches are essential as most of the current challenges are anthropogenic in nature. Issues such as poverty, human population growth, human-wildlife conflicts, illegal use of resources, habitat loss, proliferation of invasive species and diseases, among others, call for informed policies, public awareness, wide stakeholder involvement in planning, decision-making and implementation of conservation measures.

References

  1. 1. Borrini-Feyerabend, G., N. Dudley, T. Jaeger, B. Lassen, N. Pathak Broome, A. Phillips and T. Sandwith (2013). Governance of Protected Area: From understanding to action. IUCN. ISBN 978-2-8317-1608-4
  2. 2. Soutullo, A. (2010). Extent of the global network of terrestrial protected areas. Wildlife Biology, 24 (2): 362-363
  3. 3. UNEP-WCMC and IUCN (2016). Protected Planet Report2016. UNEP-WCMC and IUCN: Cambridge UK and Gland, Switzerland
  4. 4. UNEP-WCMC (2020). August 2020 update of the WDPA”. Protected Planet.UNEP-WCMC. https://www.protectedplanet.net/c/monthly-updates/2020/august-2020-update-of-the-wdpa. Retrieved 19 August 2020.
  5. 5. IPBES (2019): Summary for policymakers of the global assessment report on biodiversity and ecosystem services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services. IPBES secretariat, Bonn, Germany. 56 pages
  6. 6. IUCN 2021. The IUCN Red List of Threatened Species. Version 2020-3. https://www.iucnredlist.org>
  7. 7. Riggio J., Jacobson A, Dollar L., Bauer H., Becker M., Dickman A., et. al. (2012). The size of savannah Africa: a lion’s (Panthera leo) view. Biodiversity Conservation, DOI: 10.1007/s10531-012-0381-4
  8. 8. World Bank (2005). Going, Going, Gone: The Illegal Trade in Wildlife in East and Southeast Asia. Environment and Social Development East Asia and Pacific Region Discussion Paper. www.worldbank.org/biodiversity & www.worldbank.org/eapenvironment
  9. 9. WWF (2018). Second-biggest direct threat to species after habitat destruction. https://wwf.panda.org/discover/our_focus/wildlife_practice/problems/illegal_trade/
  10. 10. Jacobson AP, Gerngross P, Lemeris Jr. JR, Schoonover RF, Anco C, Breitenmoser-Würsten et al. (2016). Leopard (Panthera pardus) status, distribution, and the research efforts across its range. Peer Journal 4:e1974 https://doi.org/10.7717/peerj.1974
  11. 11. Stephens P.A. (2015).Land sparing, land sharing, and the fate of Africa’s lions. PNAS 112 (48):14753-14754
  12. 12. Kideghesho JR, Mseja GA, Dulle HI and Nyakunga OC. (2020). Conservation of large mammals in the face of increasing human population and urbanization in Tanzania. Can Artificial Nest Boxes be Effective Conservation Tools? In Martin EH, Hadfield LA, Melubo K, Jensen RR, Durrant J0, Hardin PJ & Weisler L. (Eds.). Protected Areas in Northern Tanzania, pp.157-179. Springer Nature Switzerland AG 2020
  13. 13. Trinkel, M. and Angelici F.M. (2016). The Decline in the Lion Population in Africa and Possible Mitigation Measures. In F.M. Angelici (Ed.), Problematic Wildlife, DOI 10.1007/978-3-319-22246-2_
  14. 14. Moneron S, Armstrong A and Newton D. (2020). The People Beyond the Poaching: Interviews With Convicted Offenders in South Africa. TRAFFIC International, Cambridge, United Kingdom. https://www.traffic.org/publications/reports/the-people-beyond-the-poaching/
  15. 15. WWF (2018). The status of African elephants (Loxodonta Africana). https://www.worldwildlife.org/magazine/issues/winter-2018/articles/the-status-of-african-elephants
  16. 16. EIA (2021). Illegal trade Seizures: Pangolins. Environmental Investigation Agency UK
  17. 17. Nuwer, R. (2020). Illegal trade in pangolins keeps growing as criminal networks expand. National Geographic Magazine,https://www.nationalgeographic.com/animals/article/pangolin-scale-trade-shipments-growing
  18. 18. Cooke J. G. and Schilckeisen D. (2015). Africa’s Wildlife Poaching and Trafficking Crisis. The Need for Urgent Action. CSIS (Center for Strategic and International Studies). https://www.csis.org/analysis/africas-wildlife-poaching-and-trafficking-crisis
  19. 19. Conciatore, J. (2019). Up to 2.7 million pangolins are poached every year for scales and meat. African Wildlife Foundation, https://www.awf.org/blog/27-million-pangolins-are-poached-every-year-scales-and-meat
  20. 20. PRB (2020). 2020 World Population Data Sheet Shows Older Populations Growing, Total Fertility Rates Declining.https://www.prb.org/2020-world-population-data-sheet/
  21. 21. United Nations Department of Economic and Social Affairs Population Dynamics (2019). World Population Prospects 2019.https://population.un.org/wpp/
  22. 22. The biomass distribution on Earth. (2018). Proceedings of the National Academy of Sciences of the United States of America, 115 (25):6506-6511
  23. 23. Quinn, J. F. and S. P. Harrison. 1988. Effects of habitat fragmentation and isolation on species richness: evidence from biogeographic patterns. Oecologia 75: 132-140
  24. 24. Robinson G.R. and Quinn J.F. (1992) Habitat fragmentation, species diversity, extinction, and design of nature reserves. In: Jain S.K., Botsford L.W. (eds) Applied Population Biology. Monographiae Biologicae, 67. Springer, Dordrecht. https://doi.org/10.1007/978-0-585-32911-6_10
  25. 25. Kideghesho, J. R.; Rija, A. A.; Mwamende, K. A. and Selemani, I. (2013). Emerging issues and challenges in conservation of biodiversity in the rangelands of Tanzania. Nature Conservation 6: 1-29. doi: 10.3897/natureconservation.6.5407
  26. 26. Kideghesho, J.R. (2015) Realities on deforestation in Tanzania: trends, drivers, implications and the way forward. In Zlatic M (Ed) Precious Forests - Precious Earth. ISBN 978-953-51-2175-6, INTECH Open Science/Open minds
  27. 27. Kideghesho J.R., Nyahongo, J.W., Hassan, S.N., Tarimo, T.C. and Mbije, N.E. (2006). Factors and ecological impacts of wildlife habitat destruction in the Serengeti Ecosystem in Northern Tanzania. African Journal of Environmental Assessment and Management, 11:17-32 http://www.ajeam-ragee.org/
  28. 28. Kioko, J., Kiffner, C., Jenkins, N. and Collinson, W.J. 2014. Wildlife road kill patterns on a major highway in northern Tanzania. African Zoology 50: 17-22
  29. 29. Coffin, A. W. (2007). From road kill to road ecology: A review of the ecological effects of roads. Journal of Transport Geography, 15:396-406
  30. 30. Maschio, G. F., Santos-Costa, M. C., Prudente, A. L. (2016). Road-kills of snakes in a tropical rainforest in the central Amazon basin, Brazil. South American Journal of Herpetology, 11:46-53
  31. 31. Loss, S.R., Will, T. and Marra, P.P. (2018). Refining estimates of bird collision and electrocution mortality at power lines in the United States. PLoS One. 2014;9(7):e101565
  32. 32. Giam, X., Olden, J.D. & Simberloff, D. Impact of coal mining on stream biodiversity in the US and its regulatory implications. Nature Sustainability 1:176-183 https://doi.org/10.1038/s41893-018-0048-6
  33. 33. G.W. Fernandes, F.F. Goulart, B.D. Ranieri, M.S. Coelho, K. Dales, N. Boesche, M. Bustamante, F.A. et al. (2016). Deep into the mud: ecological and socio-economic impacts of the dam breach in Mariana, Brazil. Perspectives of Ecological Conservation (Natureza & Conservação), 14:35-45
  34. 34. BirdLife International (2008) Campaign to save Mabira Forest in Uganda from sugarcane plantation for biofuels. Downloaded from http://www.birdlife.org on 15/11/2020
  35. 35. L.J. Sonter, D.J. Barrett, B.S. Soares-Filho. Offsetting the impacts of mining to achieve no net loss of native vegetation. Wildlife Biology, 28 (2014), pp. 1068-1076
  36. 36. Redmond, I. 2001. Coltan boom, gorilla bust: the impact of coltan mining on gorillas and other wildlife in eastern DR Congo. Report for The Dian Fossey Fund International, Atlanta , and The Born Free Foundation, Horsham , Rhode Island
  37. 37. Michael B. Mascia & Sharon Pailler (2011). Protected area downgrading, downsizing, and degazettement(PADDD) and its conservation implications. Conservation Letters 9-20
  38. 38. Dudley, J. P., J. R. Ginsberg, A. J. Plumptre, J. A. Hart, and L. C. Campos. 2002. Effects of war and civil strife on wildlife and wildlife habitats. Conservation Biology 16: 319– 329
  39. 39. Jeffrey A. McNeely (2018) Wildlife at War in Angola: The rise and fall of an African Eden, Transactions of the Royal Society of South Africa, 73:2, 202-204, DOI: 10.1080/0035919X.2017.1409494
  40. 40. Braga-Pereira F, Peres CA, Campos-Silva JV, Santos CV, Alves RRN (2020). Warfare-induced mammal population declines in Southwestern Africa are mediated by species life history, habitat type and hunter preferences. Scientific Reports, 10(1): 15428 https://doi.org/10.1038/s41598-020-71501-0
  41. 41. Kideghesho and Msuya (2013). Managing the wildlife protected areas in the face of global economic recession, HIV/AIDS pandemic, political instability and climate change: Experience of Tanzania. In Sladonja, B. (Ed.). Protected Areas Management. INTECH Open Science/Open minds, pp 65-91. ISBN: 980-953-307-448-6
  42. 42. Travis, J.M.J. (2003). Climate change and habitat destruction: A deadly anthropogenic cocktail. Proceedings of Royal Society of London. B.270467-473. http://doi.org/10.1098/rspb.2002.2246
  43. 43. Harvell, D., Altizer, S., Cattadori, I.M., Harrington, L. and Weil, E. (2009). Climate change and wildlife diseases: When does the host matter the most? Ecology 90(4):912-920i
  44. 44. Lips, K. R., F. Brem, R. Brenes, J. D. Reeve, R. A. Alford, J.Voyles, C. Carey, L. Livo, A. P. Pessier, and J. P. Collins.2006. Emerging infectious disease and the loss of biodiversityin a Neotropical amphibian community. Proceedings of theNational Academy of Sciences (USA) 103:3165-3170
  45. 45. Lips, K. R., J. Diffendorfer, J. R. Mendelson, and M. W. Sears. 2008. Riding the wave: reconciling the roles of disease and climate change in amphibian declines. PLoS Biology 6(3):e72
  46. 46. Seebens, H., Blackburn, T., Dyer, E. et al. [2017]. No saturation in the accumulation of alien species worldwide. Nature Communication 8, 14435. https://doi.org/10.1038/ncomms14435
  47. 47. Hellmann, J.J., Byers, J.E., Bierwagen, B.G., and Dukes, J.S. (2008). Five potential consequences of climate change for invasive species. Conservation Biology 22(3):534-543
  48. 48. Otiang’a-Owiti, G. E., Nyamasyo, S., EMalel, E., and Onyuro, R. (2011). Impact of climate change on human-wildlife conflicts in East Africa. Kenya Veterinarian 35:103-110. Available online at: https://www.ajol.info/index.php/kenvet/article/view/87548
  49. 49. Atkinson, I.A.E. (1996). Introductions of wildlife as a cause of species extinctions. Wildlife Biology, 2(3):135-141 (1996). https://doi.org/10.2981/wlb.1996.011
  50. 50. Linders, T.E.W., Schaffner, U., Eschen, R., Abebe, A., Choge, S.K., Nigatu, L, Mbaabu, P.R., Shiferaw, H, and Allan, E. (2019). Direct and indirect effects of invasive species: Biodiversity loss is a major mechanism by which an invasive tree affects ecosystem functioning. Journal of Ecology, 107(6): 2660-2672
  51. 51. Bellard, C., Genovesi, P., Jeschke, J.M. (2016). Global patterns in threats to vertebrates by biological invasions. Proceedings of the Royal Society B: Biological Sciences 283 (1823) (2016), p. 20152454
  52. 52. Bellard, C., Cassey, P. and Blackburn, T.M. (2016). Alien species as a driver of recent extinctions. Biological Letters 12 (2016), p. 20150623
  53. 53. Seebens, H., Bacher, S., Blackburn, T.M., Capinha, C., Dawson, W., Dullinger, S., Genovesi, P., Hulme, P.E., Kleunen, M., Kühn, I., Jeschke, J.M., Lenzner, B., Liebhold, A.M., Pattison, Z., Pergl, J., Pyšek, P., Winter, M. and Essl, F. (2020). Projecting the continental accumulation of alien species through to 2050. Global Change Biology 27(1):16. DOI: 10.1111/gcb.15333
  54. 54. Mueller, J. M. & Hellmann, J. J. (2008).An assessment of invasion risk from assisted migration. Conservation Biology 22:562-567
  55. 55. Hulme, P. E. Trade, transport and trouble: managing invasive species pathways in an era of globalization. Journal of Applied Ecology, 46:10-18 (2009)
  56. 56. Banks, N. C., Paini, D. R., Bayliss, K. L. & Hodda, M. (2015).The role of global trade and transport network topology in the human-mediated dispersal of alien species. Ecological Letters 18:188-199
  57. 57. Skarpaas, O. & Økland, B. Timber. (2009). import and the risk of forest pest introductions. Journal of Applied Ecology 46, 55-63
  58. 58. McNeill, M. et al. (2011). Transportation of non-indigenous species via soil on international aircraft passengers’ footwear. Biological Invasions 13:2799-2815
  59. 59. Huang, Z., Das, A., Qiu, Y. & Tatem, A. (2012).Web-based GIS: the vector-borne disease airline importation risk (VBD-AIR) tool. International Journal of Health Geogaphy 11, 33
  60. 60. Witte, F., Goldschmidt, T., Wanink, J. et al. (1992). The destruction of an endemic species flock: quantitative data on the decline of the haplochromine cichlids of Lake Victoria. Environment Biology of Fish 34, 1-28 https://doi.org/10.1007/BF00004782
  61. 61. Savidge, J.A. (1987). Extinction of an Island Forest Avifauna by an Introduced Snake. Ecology, 68(3): 660-668
  62. 62. Aloo, P. A., Njiru, J., Balirwa, J. S., and Nyamweya, C. S. 2017. Impacts of Nile Perch, Lates niloticus, introduction on the ecology, economy and conservation of Lake Victoria, East Africa. Lakes and Reservoirs: Research and Management. 22(4): 320-333. doi: https://doi.org/10.1111/lre.12192
  63. 63. Wiles, G.J., Bart, J., Beck, R.E. Jr., and Aguon, C.F. (2003). Impacts of the Brown Tree Snake: Patterns of Decline and Species Persistence in Guam’s Avifauna. Conservation Biology, 17(5):1350-1360
  64. 64. NWF. The National Wildlife Federation -Invasive Species, Available at: https://www.nwf.org/Educational-Resources/Wildlife-Guide/Threats-to-Wildlife/Invasive-Species
  65. 65. Acevedo-Whitehouse, K. and Duffus, A.L.J. (2009) Effects of environmental change on wildlife health. Philosophical Transactions: Biological Sciences, 27; 364(1534): 3429-3438. doi: 10.1098/rstb.2009.0128
  66. 66. Newman, J.R. (1979). Effects of industrial air pollution on wildlife. Biological Conservation, 15(3):181-190
  67. 67. Preeti, Reen,J.K., Thakur,M., Suman, M. and Kumar, R. (2018). Consequences of pollution in wildlife: A review. The Pharma Innovation Journal, 7(4): 94-102
  68. 68. Harvell, D., Altizer, S., Cattadori, I.M., Harrington, L. and Weil, E. (2009). Climate change and wildlife diseases: When does the host matter the most? Ecology, 90(4):912-920
  69. 69. Lips, K. R., F. Brem, R. Brenes, J. D. Reeve, R. A. Alford, J.Voyles, C. Carey, L. Livo, A. P. Pessier, and J. P. Collins. 2006. Emerging infectious disease and the loss of biodiversity in a Neotropical amphibian community. Proceedings of theNational Academy of Sciences (USA) 103:3165-3170
  70. 70. Lips, K. R., J. Diffendorfer, J. R. Mendelson, and M. W. Sears. 2008. Riding the wave: reconciling the roles of disease and climate change in amphibian declines. PLoS Biology 6(3):e72
  71. 71. McMichael, A., and M. J. Bouma. 2000. Global change, invasive species and human health. Pages 191-210 in H.Mooney and R. Hobbs, (Eds). The Impact of Global Change on Invasive Species. Island Press, Covelo, California, USA
  72. 72. Loh, E.H., Zambrana-Torrelio, C., Olival, K.J., Bogich, T.L., Johnson, C.K., Mazet, J.A.K., Karesh, W. and Daszak, P. (2015). Targeting transmission pathways for emerging zoonotic disease surveillance and control. Vector Borne and Zoonotic Diseases, 15(7), 432-437
  73. 73. WWF (2020).The loss of nature and rise of pandemics: protecting human and planetary health.WWF International, Gland, Switzerland. 19pp
  74. 74. Kaneda, T. and Greenbaum, C. (2020). How demographic changes make us more vulnerable to pandemics like the coronavirus. Available at: https://www.prb.org/how-demographic-changes-make-us-more-vulnerable-to-pandemics-like-the-coronavirus/
  75. 75. Kideghesho, J.R., Kimaro, H.S., Kisingo, A.W. and Mayengo, G.M. (2021). Will Tanzania’s wildlife sector survive the COVID-19 pandemic? Tropical Conservation Science,https://doi.org/10.1177/19400829211012682
  76. 76. Food and Agriculture Organization of the United Nations (2020). Global Forest Resources Assessment 2020. Rome: FAO. https://doi.org/10.4060/ ca8753en

Written By

Jafari R. Kideghesho

Submitted: 10 May 2021 Published: 08 December 2021