Impact of Climate Change on Human Wildlife Conflict and Social Implications

Dr. Reji D. Nair

Abstract

Paper reviews the extent of climate change on forest ecosystems and that impact the Human Wildlife Conflict (HWC). Historical dimension of HWC, implication of HWC on society, and social dimensions of HWC are all part of discussion in the paper. Human perceptions on wildlife are influenced by socio-cultural factors and also their influence on public policy. Paper concludes that interventions to reduce HWC are designed to reduce the frequency of interaction between people and wild animals along with initiatives to enhance the tolerance of societies in conflict situations.

Key words: Human-Wildlife Conflict (HWC), Climate change, Forest management, Implications of HWC, Social dimensions

Introduction

Human Wildlife Conflict (HWC) is described as conflict between humans and wildlife wherein the actions of latter affect the former and vice-versa. Threats to human life, economic loss, food security, etc. are some of the major impacts of HWC (Redpath, SM, et.ail., 2013). HWC is predicted to intensify in response to global environmental issues such as climate change and the destruction of wildlife habitats and forests (Mason et al., 2018). HWC fosters widespread environmental, social, economic, and political problems across the globe (Guerra, 2019). Human-Wildlife Conflict (HWC) management is a multi-disciplinary concept involving animal behaviour, conservation biology, ecology, genetics, wildlife ecology, zoology, anthropology, economics, environmental studies, geography, history, natural resources management, political science, psychology, technology and so on (Nair, 2009). In the last two decades HWC management has attracted increased attention due to growing recognition that HWC affect societies globally and hinder conservation efforts along with the attainment of goals of sustainable development.

Major objective of the paper is to review the gravity of climate change on HWC and implications of the HWC on society. Paper also discusses the impact of climate change on forest ecosystems and biodiversity, leading to species extinction. Historical dimension of HWC and implication of HWC including costs and gender dimension are also discussed in detail in the paper. Review of social dimensions of HWC with emphasis on cultural diversity is also part of the paper.

Climate change as drivers

Deforestation and climate change are reciprocally related; temperature, radiation, rainfall and carbon dioxide in the atmosphere are the backbone of forest dynamics, whereas forests in turn will influence climate by seizing atmospheric carbon, solar radiation, cooling atmosphere through evapotranspiration and even producing cloud-forming aerosols. Figure-1 depicts the relationship between forest and climate change.

Climate change is anticipated to have significant impacts on forest ecosystems and accordingly forest management should adapt to changing scenarios. Impact of climate change on forest ranged from large-scale biome shifts to relatively less extensive disruptions in forest growth (Aber, et al. 2001). The increasing temperature and droughts will have negative impact on species diversity as well as ecosystem goods and services to humanity (Gnacadja and Lesch 2009). Major drivers of climate change includes anthropogenic causes such as land use changes, deforestation and forest degradation, fossil fuel burning and industrial processes and natural causes such as solar radiation changes and volcanic activity. Deforestation and forest degradation play a critical role in global climate change, and reciprocally, deforestation is indirectly affected by climate change too. In the past, nearly 45% of the land surface was covered by forest, which dwindled to nearly 30% due to shifting cultivation and other human activities. FAO reports show that current deforestation rate is 0.14%, which is 5.2 million hectares per annum (FAO, 2012). Greenhouse gas (GHG) emissions from deforestation and forest degradation are reported to account for about one-fifth of the total GHG emissions.

Figure: 1 Inter-relationship between Forest and Climate Change

Deforestation $\longleftrightarrow$ Climate Change $\longrightarrow$ Carbon Sequestration $\longrightarrow$ Impact on Forest $\longrightarrow$ Deforestation

Source: Khaine, Inkyin & Su Young Woo (2015)

Forest growth rate is reported to be correlated with climate, especially the water availability (Toledo et al. 2011). Increasing temperature and precipitation will directly influence tree growth, whereas increases in dry period will have a negative impact on growth of forest. Even the solar radiation has an impact on forest growth. The role of forests in environmental management is very important and it ranges from carbon sequestration to water and soil conservation. Carbon storage capacity of forest is significantly affected by environmental conservation. The global forests store over 650 billion tons of carbon in various forms including 44% as biomass, 45% in the soil and 11% in dead wood and litter (FAO 2010).

Recent researches shows gloomy picture for the future of forests and due to global warming, carbon regulation services of forests will be lost, as land ecosystems may turn into a net source of carbon dioxide by end of the century (Seppala et al. 2009). Studies also indicate that climate change will have moderate to large-scale impact on forest through shift in vegetation and biodiversity. Studies conducted in India demonstrate that nearly 39% of forested grids are vulnerable to climate change (Chaturvedi, et. al, 2011). The climate impact assessment studies done on Indian forests show that nearly 68% to 77% of the forested grids are likely to experience changes including loss of area under current forest type as well as replacement by a different type by 2085 (Ravindranath, et. al., 2010). Climate change may damage unique forest ecosystems and biodiversity, leading to species extinction.

Sustainable forest management as a tool to climate change adaptation management has provided positive results across the world. Sustainable forest management measures helps to ensure that adaptation and mitigation measures are carried out by accounting the economic, social and environmental value of forests (Nair, 2010). Adoption of landscape approach will help in implementing forest-based climate change adaptation and mitigation measures that lead to optimal economic, social and environmental outcomes. Adaptation to climate changes includes adjustments in ecological, social, and economic systems in response to the effects of changes in climate (Smit et al. 2000). Adaptation to climate change in forest management requires a planned response well in advance.

Adaptation requires setting up of objectives for the future forest under changed scenario, increased awareness and education, determining the vulnerability of forest ecosystems and society, development of cost-effective adaptive actions, reduction of vulnerability and enhancement of recovery, continuous monitoring of the state of the forest, and measures for speedy recovery (Holling, 2001). Climate change adaptation strategies are to be viewed as part of risk management plans, and the precautionary strategies would reduce the risk of losses in the future. Current forest growth and management is the result of how it developed in the past climatic conditions.

Policy-makers and forest managers should accept that climate change is probable and that forests and communities face significant impacts (Nair, 2022). Adaptation requires auditing of research requirements, auditing of educational needs, evaluation requirements, forest management actions, analysis of existing barriers, required forest policies, development of monitoring systems, and level of interventions including spatial (Spittlehouse and Stewart, 2003). Detailed action plan for climate adaptation action in forest management is provided in Table-1.

Table: 1 Climate Adaptive Actions in Forest Management

Areas Actions Remarks
1. Gene Management

i. Determining the responses of species and genotypes to climate and the limits of their transferability, and developing climate-based seed zones that will change over time


ii. Breeding for pest resistance and for a wider tolerance to a range of climate stresses and extremes in specific genotypes


iii. Re-evaluating seed orchard locations.


iv. Planting a mixture of provenances at a site


v. Re-evaluating conservation and recovery programs.

Climate change will affect the geographic extent of the zones
2. Forest Protection

i. Any future increases in wildfire are expected to overwhelm the ability of fire management agencies to respond to all occurrences.


ii. Altering forest structure (e.g., tree spacing and density, standing dead trees, or coarse woody debris on the forest floor) to reduce the risk and extent of disturbance; increasing use of prescribed burning to minimize fuel loading.


iii. Developing “fire-smart” landscapes by using harvesting, regeneration, and stand-tending activities that manage fuels to control the spread of wildfire.


iv. Enhancing forest recovery after fire disturbances.


v. Partial cutting or thinning to increase stand vigour and lower the susceptibility to attack.


vi. Reducing disease losses through sanitation cuts that remove infected trees.


vii. Shortening the rotation length to decrease the period of stand vulnerability to damaging insects and diseases and facilitating change to more suitable species.


viii. Using insecticides and fungicides in situations where silvicultural activities for insect pest management are ineffective or inappropriate.


ix. Using genotypes bred for improved resistance to pests.

Rapid changes are the outcome of fire, wind, ice storms, and pests. Existing forests are quite resistant to climate variability, it is the regeneration phase that will initially be susceptible to the changed climate.
3. Forest Regeneration

i. Identifying drought-tolerant genotypes.


ii. Assisting the migration of commercial tree species from their present to future ranges through artificial regeneration.


iii. Planting provenances that grow adequately under a wide range of conditions and planting stock from a range of provenances at a site.


iv. Controlling undesirable plant species, which become more competitive in a changed climate, through vegetation management treatments.

4. Silvicultural Management

i. Pre-commercially thinning or selectively removing suppressed, damaged, or poor quality individuals to increase light, water, and nutrient availability to the remaining trees.


ii. Reducing vulnerability to future disturbances by managing tree density, species composition, forest structure


iii. Under-planting with other species or genotypes where the current advanced regeneration is unacceptable as a source for the future forest.


iv. Reducing the rotation age followed by planting to speed the establishment of better-adapted forest types.

Nutrient availability and acclimation by trees are likely to limit the potential for increased growth due to higher concentration of atmospheric carbon dioxide. Warmer sites may see increased respiration, offsetting any gains.
5. Forest Operations

i. Increasing the amount of timber from salvage logging of fire- or insect-disturbed stands.


ii. Advanced planning for climate change allows for infrastructure replacement as part of the normal replacement cycle.


iii. Mitigating the impacts on infrastructure, fish, and potable water supplies, of changes in the timing of peak flow and volume in streams resulting from increased precipitation.


iv. Including adaptation planning in forest certification as part of a risk management strategy.


v. Mitigating climate change through forest carbon management, and evaluating the risk of climate change to carbon stocks.


vi. Increasing the use of forests for biomass energy.


vii. Developing policies to facilitate the creation and implementation of adaptive management responses to climate change.

Biological and climate changes have implications for forest operations. Climate change will affect habitat quality and availability for wildlife and influence predator/prey synchrony
6. Non-timber Resources

i. Minimizing fragmentation of habitat and maintaining connectivity.


ii. Maintaining representative forest types across environmental gradients and protecting primary forests.


iii. Maintaining diversity of functional groups as well as species within groups.

7. Wilderness Area Management

i. Managing to delay, ameliorate, and direct change.


ii. Identifying and planting alternate tree species.


iii. Conserving biodiversity and maintaining connectivity in a varied, dynamic landscape to aid vegetation and wildlife migration as the climate changes.

Traditional measures may not be feasible under changed climate, given that the values and attributes the park or wilderness areas were designed to protect may no longer exist within the protected area.

Source: Spittlehouse DL & R B. Stewart (2003)

Historical dimensions of HWC

In many civilizations wildlife and nature played an important role in framing customs, traditions, and the religion itself. The Nanai and Udege communities of the Russian Far East believe that seeing an Amur tiger is auspicious. In the Hindu religion of India, the goddess Durga is believed to ride on lion especially fighting with demons. In the Mesoamerican Mayan culture, jaguar is considered as a god; wanderer between the living and spirit worlds. In the Hindu cultures of South Asia, elephants are associated with Ganesha and is said to be the remover of obstacles.

The evolution of human civilizations is fundamentally a story of human interactions with other flora and fauna. The competition for food and water in drastic climatic situations and environment forced the human to dominate other living creatures. Human intelligence helped them even in conquering the territory of physically strong wild animals like elephant and lion in the terrestrial ecosystems and sharks in oceans. In due course humans emerged as a super predator and started dominating their living environment (Worm, B, 2015). It has led to the extraction and hunting on large scale and resulted in the extinction of many species. There are evidences that humans contributed to the extinction of large mammals during the late Pleistocene glacial period (Surovell, TA, et. al., 2016).

Predator avoidance might be one of the major challenges faced by the early hominids. Effective intelligence, social adaptation in the form of group formation, and usage of weaponry are some of the strategies used in the past (Hart D & Sussman, W, 2009). Ancient records of human-wildlife interface can be seen in the cave paintings (Guthrie, RD, 2005). Ancient civilizations such as Indus Valley, Chinese, Greece, and Egyptian have also records of HWC to protect crops, livestock and even human life. Elephant crop raids are reported in Asia as early as 300 BC (Sukumar, R, 1989). Kingdoms and colonial empires even had predator eradication initiatives, which led to the extinction or nearer to obliteration of much wildlife such as Chinese tiger, wolves in Europe, jaguars in Americas, lions and wild dogs in Africa, and Falkland Wolf.

In modern times, governments around the globe started framing laws and policies to address Human-Wildlife Interface. Important milestones as part of HWC management are provided in Table-2.

Table: 2 Important global milestones in the development of HWC management

Year Events/mile stones
1987 The International Bear Association and the International Union for the Conservation of Nature (IUCN) Bear Specialist Group starts to focus on HWC.
1990-2005 IUCN African elephant specialist group gave recommendations on human-elephant conflict management.
2004 IUCN World Parks Congress, South Africa, recognises the need to address growing challenges of HWC.
2005 Book People and Wildlife: Conflict or Coexistence? Broadens the discussion on HWC.
2008 Pathways Conference discusses the need to better integrate the human dimension into HWC management.
2009 Human-wildlife conflict collaboration, later renamed CPeace, launches capacity building programme on conflict transformation.
2010-2015 Scientists and conservation practitioners recognize HWC as including conflicts among different groups of people regarding wildlife.
2016 IUCN SSC Human-Wildlife Conflict Task Force is set up to support professionals working on HWC.
2019 Book Human-Wildlife Conflicts and the need to include Coexistence broadens the discussion of coexistence concepts.

Source: Gross E, et. al, 2021, A Future for All: The Need for Human-Wildlife Coexistence, WWF, Gland, Switzerland.

Human population have evolved from pre-history to modern history by competing with wildlife for food, resources, and space; in most cases led to the extinction of some sort of flora and fauna. But later societies started realising the significance of biodiversity and conservation for their own survival. Accordingly coexistence models were developed with the support of new laws, policies, assisted by institutions, tools and technology, and new values.

Implications of HWC

The HWC has significant impact on human health, safety, and welfare as well as ecosystem health and biodiversity. Direct impacts include attack on people resulting injury and death, collision with automobiles, transmission of zoonotic diseases or parasites, economic damage to crops, property and livestock, etc. (Woodroffe, RT, et.al., 2005). Indirect impacts include opportunity costs to farmers, diminished psychological wellbeing, disruption of livelihoods, food insecurity and so on.

Usually the hidden costs of HWC are not counted in quantifying the implications as it is mostly non-economical and includes impact on individuals, psychological impacts, and other opportunity costs (Barua, et. al., 2013). Studies show that the women and women-headed families used to experience a disproportionate burden of HWC compared to their male counterparts (DeMotts, R & P. Hoon, 2012). Emotional costs encompass physical safety issues, livelihood issues, and even frustration with outsiders. Some of the major impact of HWC in selected countries are provided in Table-3.

HWC results in stress and shock to livelihood and food security of the forest fringe communities. Stress is continuous, predictable, slowly increasing disruption to livelihoods with a cumulative impact, whereas shock is a large disturbance with immediate impact (Scoones, 1998). Vulnerable sections of people in the forest fringe areas in developing countries are not in a position to face such shock or stress, especially women. These shocks and stress adversely affect the women due to the following reasons (Khumalo & Young, 2015): i. Women are more vulnerable to shocks (short-term) and stress (long-term) due to poverty, marital status, lack of farm land, limited entitlements; ii. Crop loss, livestock depredation, and death or injury of a family member hit women harder. iii. Above losses magnify their vulnerability to other stresses and shocks as they are already marginalised.

Important costs of HWC at direct and indirect level are given in Table-4.

Table: 3 Gravity of HWC around the world

Country Type of Implication Units Implication
Sri Lanka 2019 People killed by wild elephants Number 121
Sri Lanka 2019 Elephants killed due to HWC Number 405
Tanzania per year People killed by lions in per year Number 60
Tanzania per year Lions killed due to HWC Number 150
Bardia, Nepal Average per-species cost of crop damage per household and incident USD 20
Bardia, Nepal Average cost of property damage by elephant per household and incident USD 73
Europe – 2005-2012 Average annual compensation for all livestock damage by carnivores USD – million 41.38
Europe-2005-2012 Average cost per year per wolf USD 3500
Europe-2005-2012 Average cost per year per bear USD 2,600
Europe-2005-2012 Average cost per year per lynx USD 1,000

Source: Gross E, et. al, 2021, A Future for All: The Need for Human-Wildlife Coexistence, WWF, Gland, Switzerland.

Table: 4 Important Costs of HWC

Type of cost Continuous events Discrete events
i. Direct costs Time lost from chasing animals away as they try to enter fields

Physical risk


Crop loss


Livestock predation


Human injury


Infrastructure damage


Death

ii. Indirect costs

Additional time investment


Fear of what will happen if one encounters a dangerous animal; fear of what will happen if crop is lost; anger at the conservancy; uncertainty about being able to provide for one’s household


Lost sleep staying on the lookout for animals

Fear/stress during animal encounters


Food loss, hunger


Income loss


Lost opportunity cost


Lost labour investment


Lost financial investment

Source: Khumalo K E (2015)

Social dimensions of HWC

HWC is sometimes viewed as a manifestation of human-human conflict, such as between authorities and local people or between people of diverse cultures. Studies prove that societies used to accept snags and risks of wildlife voluntarily than when imposed externally. People who have experience of living alongside wild animals tend to be less fearful of the animals (Roskaft, et. al., 2003). Societies respond differently to wildlife attack in different countries and sometime a small incident can instil huge wildlife causality. In Hokkaido, Japan a bear alert in 1966 resulted in the killing of 39 bears (Knight, 2000). As retaliation to an incident in Namibia in 1980s, 700 Namibian Cheetahs were killed (Marker, 2002). Reports from some of the countries in Asia and Africa reveal that societal belief system can also influence hostility towards wildlife. In Mozambique, there is a belief that some of the ethnic groups can use sorcery to transform tree twigs into spirit-lions, which are then used to attack rival ethnic groups; resulted in large-scale killing of lions (West, 2001).

Figure: 2 Factors Affecting Intensity of HWC – A Model

Environmental Risk Factors: Environmental Characteristics, Land use & Management, Human Behaviour (Asset Protection & Mgmt.), Behaviour and mgmt. of conflict (Causing conflict) $\longrightarrow$ Costs $\longrightarrow$ Actual Cost of Conflict / Perceived Cost of Conflict $\longrightarrow$ Response (Direct Impact) / Level of Hostility (Indirect Impact) $\longrightarrow$ Consequences Social Risk Factors: Inequality and power, Distrust & animosity, Vulnerability & wealth, Beliefs & Values Source: Dickman AJ (2010)

It has been proved that many of the HWCs stem from differences in objectives of various stakeholder and pressure groups, especially when the wildlife is treated as a resource that can be exploited for economic or cultural benefit, or where the conservation of wildlife is uncertain due to human population growth and the resultant development pressure (White & Alastair Ward, 2010).

Environmental factors such as the characteristics of the physical environment (forest-fringe areas), availability of alternative food sources for the wildlife, etc. can also influence the HWC. The beliefs and values of society are also important in determining the perception of society towards HWC. Hazzah (2006) reported that the Evangelical Christian beliefs have been linked to particular hostility toward wildlife. Ale (1998) reported that Buddhist herders in Nepal used to accept the depredation of snow leopard by treating it as a punishment of the mountain God.

The expression of values differs among people, and it will be reflected on their perception of wildlife. Some justify wildlife killing for the sake of human welfare, whereas others treat this action as inhumane and unjustifiable (Nair, Reji, 2024). Individual differences in value expressions are conceptualised by basic beliefs and are the outcome of central beliefs that is usually modelled early in the childhood. In this regard, the concept of Wildlife Value Orientation (WVO) was developed, which reveals the pattern and direction of basic belief about wildlife (Fulton, et. al., 1996). Accordingly two diverse views are formed; the first one is Wildlife Protection Orientation (WPO) and the second, Wildlife Use Orientation (WUO). The WPO emphasize that wildlife have rights on nature similar to human beings and some cultures completely follow this view. The WUO believe that wildlife should be used for the benefit of the human beings and they follow an extraction approach towards the environment.

Social Issues of HWC

i. Conflict level-I: Anger and distress over losses caused by wildlife are immediate reactions and are considered to be disputes that make up conflict level-I.

ii. Conflict level-II: People who experience negative HWC raises underlying issues, including poor governmental response or compensation for HWC incidents that complicate the situation.

iii. Conflict level-III: Deep-rooted conflicts include complex social, cultural, and historical contexts of HWC. Unfair resettlement of affected people, access issues in culturally important places, or the criminalization of hunting by local communities is examples in the context (Gross E.M, 2019).

Culturally the human attitude towards the environment is generally of either subjugation by nature or domination of nature. These diversions of view mark the transition from hunter-gatherers to pastoral societies and some cultures believe that cultural advancement was attained through the domination (Ingold, 1994). The Western origin religions are believed to have spawned the human-nature separation and advanced the prominent view of human domination over nature (White, 1967). On the other hand, the Eastern origin religions believe in the equality of all living creatures thereby treating the nature as the mother (Dwitvedi, 2001). Even some argue that scientific thought and the Calvinist ethic of domination laid the foundation of Capitalism and the European expansion to North America (Weber, 1948). Generally the cultures which are individualistic in nature would demonstrate competition over nature and wildlife, whereas collectivist cultures emphasise sharing of natural and wildlife resources.

In the post-materialistic world the emphasis would be on quality of life and self-expressions. Major difference between materialists and post-materialists is that the materialists prefer WUO, whereas, post-materialists are more likely to follow WPO (Manfredo, MJ & Ashley A D, 2004). Recent trends pose two fundamental challenges to wildlife professionals; the first being shift from conservation to management, that is transformation from increasing wildlife population to wildlife population control (Marchini & Crawshaw, 2015). The second is change in people’s tolerance to wildlife that is human dimension to wildlife. These developments exhibit an interdisciplinary approach to HWC integrating natural, social, and behavioural issues into research, conservation, management, and public policy.

Human perceptions on wildlife are influenced by variety of factors such as social or interest groups and also their influence on public policy is limited by their closeness to and special interest with in the Government (Lute, et. al., 2014). Studies show that economic growth has affected societal values from sustenance based acquisitive values towards self-expression and it has real effect on human perception on wildlife. At the same time cultural differences may have diverse effect, especially in India and Mongolia, where traditional societies are highly tolerant to wildlife (Athreya, et. al. 2013). It means human tolerance to wildlife conflict is not only about perceptions but also is dynamic and is affected modernization.

Conclusion

Climate change is altering the entire ecosystems around the world. The increasing frequency of HWC has resulted in deadly consequences on both sides, and various initiatives are under way in all parts of the globe to address the problem. Interventions to reduce HWC included actions that are designed to reduce the severity or frequency of encounters between people and wild animals or activities that enhance the tolerance of people in conflict situations. Frequency of interactions can be reduced through construction of barriers, guards, and deterrents, relocation of wild animals, relocation of people, and changes in human actions such as cropping pattern changes. In the worst case scenario of human causalities, such wild animals need to be killed. Usually multiple strategies are simultaneously required to settle the issue as a long-term measure. Tolerance of affected people can be enhanced through compensation programmes, incentive schemes, environmental education, and regulated public harvests. However, in most cases permanent solution of HWC in the forest fringes are distant realities as mitigation is ineffective and violate the conservation initiatives.

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