Posted on September 18, 2001

Determination of Environmental Refugees:
Cases for Inclusion and Expansion


Ruth E. Baker

ruth_e_baker@hotmail.com
Macalester College
1600 Grand Avenue
St. Paul, MN 55105


Abstract

The fate of an environment has direct repercussions on the inhabitants of the area. People are often displaced from their lands because of changes to their environment.  In this paper, I propose a framework in which to examine this arising form of displaced peoples.  Natural disasters, development, resource abuse, and degradation have forced millions of people from their homes and means of subsistence.  I analyze these existing causes of environmental displacement and propose another, which includes those displaced because of the establishments of parks, wildlife refuges, and other protected areas.  I also attempt to address the complex power structures which limit the rights of the people who are most effected by these problems.


Environmental refugees are emerging as a significant proportion of the world’s displaced peoples. Norman Myers, an Oxford University ecologist, estimates that currently 25 million people worldwide have been uprooted for environmental causes, exceeding the 22 million refugees from civil war and persecution (Douglas 1996).  As the world weather systems are becoming more erratic, the resources scarcer, and the integrity of the environment is being continuously degraded, people across the world are losing their lands, homes, and means of subsistence.  I will discuss how this arising form of refugee complicates the accepted definitions, arguing that the determination of refugee status should be modified to include all environmental refugees because of the special circumstances they must face. 

 Environmental refugees experience persecution because of hegemonic discrimination embedded in the world culture.  By hegemonic persecution, I refer to the uneven power structures that place the affluent above the poor and majority ethnic or religious groups above the minorities.  This persecution is found throughout the examples of environmental refugees, almost all of who are indigenous peoples.  This is because non-subsistence people overuse their resources, and have the power to take from those who have no capitalistic influence in the national or global spheres.  Indigenous groups have often been moved, without reparation or voice in the system.  The more affluent and powerful have the resources necessary to relocate if the land degrades beyond repair, leaving the subsistence groups homeless and hungry.

I will argue why environmental refugees should be granted refugee status, but first I will discuss why they currently are not.  The concept of environmental refugees is extremely difficult, complicated by a combination of biological and social aspects.  By including this group within the central definition of refugees, it would distort the definitions and strain the few resources available for international programs (Suhrke 1994).  Because of this factor, most governing bodies, including the U.S. State Department and the U.N. High Commissioner for Refugees, choose to ignore the issue (Hugo 1996).  Also, because these governments do not collect data on this issue, research is extremely difficult due to a significant lack of information.  The categorization can also be ambiguous, for example volcanoes can cause both permanent and temporary displacement, and the definition of ‘permanent’ could be defined as 20 years or 200.  However, this field needs to be addressed, as the number of environmental refugees is increasing as the impact of humans on the land becomes greater.  If we identify the problems, and implement temporary solutions, we can buy time to develop remedies.

I will examine the three main types of environmental refugees proposed by Hinnawi (1985) and the United Nations, and modify this list to include a fourth, emerging category.  The first category is comprised of people temporarily displaced because of environmental stress.  This classification applies mainly to victims of natural disasters, such as earthquakes and volcanoes; massive storms, such as hurricanes; and environmental accidents, such as Chernobyl.  The resulting damage is severe, but the land and people’s lives can usually be reestablished after clean up and rebuilding.  The second category of environmental refugees includes those peoples permanently displaced and resettled in another area.  This classification is usually associated with human caused permanent environmental changes, such as dams, but can also be associated with natural disasters that permanently damage an area, such as destructive volcanoes.  The final category defined by Hinnawi is composed of those individuals or groups who can no longer be supported by their lands because of environmental degradation.  This type of environmental refugee is displaced by massive changes in the environment that render it practically obsolete for human survival, often due to human actions.  Examples are deforestation and desertification.  However this status rests on a fine line, and is accorded only to those who are involuntarily forced to leave for survival, not if they migrate because of economic situations or by choice.  Hence, I propose a fourth type of environmental refugee: those displaced because of policy implementation affecting the environment. In these cases there is no significant change to the land, only to the policy governing the land that force people to involuntarily migrate.  This is almost specifically applied to conservation units such as national parks that either directly displace people or cut off their means of subsistence.

In order to account for all refugees, we must redefine the context used to assess refugee status.  The US and the United Nations need to encompass “environmental refugees,” according to Hinnawi’s definition, in order to protect, assist, and legitimize their struggles.  To demonstrate the scope that environmental refugees envelop, and the necessity of their inclusion in the UN’s classification of refugees, I will present four cases, corresponding to the aforementioned categories.

Assigning Definitions

To answer the question, Who is an environmental refugee?  We must first answer the questions:  Who is a refugee? and Who are internally displaced peoples?  Basically every nation and organization has a unique definition for refugees.  These questions beg another:  Why does it matter?  Refugee status is a privilege that comes with assistance, protection, and even international rights.  Academics argue over the definitions while masses of people are left suffering and waiting.

The definitions of refugees are thus important because they determine who receives aid and resettlement.  For nearly the past 30 years, the United Nations has been using the definition of refugees as persons who:

"owing to a well-founded fear of being persecuted for reasons of race, religion, nationality, membership in a particular social group, or political opinion, is outside the country of his nationality, and is unable to or, owing to such fear, is unwilling to avail himself of the protection of that country." (UNHCR 2000).

The United States also assigned its own definition in the 1980 Refugee Act, which described refugees as:

“any person who is outside any country of such person’s nationality or, in the case of a person having no nationality, is outside any country in which such person last habitually resided, and who is unable or unwilling to return to, and is unable or unwilling to avail himself or herself of the protection of, that country because of persecution or a well-founded fear of persecution on account of race, religion, nationality, membership in a particular social group, or political opinion...” (Holman 1997:13-14).

Neither of the above definitions would explicitly encompass environmental refugees.  Both assign meaning by persecution founded on race, religion, or nationality but ignore the strife of people unable to survive as they traditionally have because the land they lived on was destroyed or terribly modified.

In order to establish a framework, I feel it is more appropriate to look at environmental refugees in a context including internally displaced peoples.  One of the most universally accepted definitions for internally displaced peoples is currently found in the Secretary General’s report to the United Nations in 1992.  He identifies internally displaced peoples as:

“persons who have been forced to flee their homes suddenly or unexpectedly in large numbers, as a result of armed conflict, internal strife, systematic violations of human rights or natural or man-made disasters, and who are within the territory of their own country” (Cohen and Deng 2000:16).

This definition includes the plight of some environmental refugees.  Environmental refugees need special protection during environmental crises, natural or human caused, because of neglect, persecution, and systematic violation of their human rights, provoked by environmental disasters and exacerbated by the generally underprivileged status of those most affected by these events.

  It is apparent that a definition of environmental refugees also needs to include environmentally internally displaced peoples.  Especially in larger nations, many environmental refugees are relocated within their own political borders.  However, because most environmental refugees are those people marginalized within a nation (i.e. minority groups, indigenous peoples, and the poverty-stricken), it can be inferred that they will be unable to avert this persecution.  For the remainder of this paper, the term “environmental refugee” will be used to represent both refugees and internally displaced peoples as a result of environmentally caused, involuntary movement.  I will discuss the systematic persecution associated with each type to demonstrate the need to assign refugee status to these environmentally displaced peoples (both internal and external).

For purposes of this paper, it is necessary to establish a definition of environmental refugees.  I will use the definition accepted into the United Nations, but since abandoned because of the problems discussed in the introduction. It defines environmental refugees as:

“those people who have been forced to leave their traditional habitat, temporarily or permanently, because of a marked environmental disruption (natural and/or triggered by people) that jeopardized their existence and/or seriously affected their quality of life (Hinnawi 1985:4).

To explain further, Hinnawi defines an “environmental disruption” to encompass all types of ecosystem agitation, including chemical or biological changes in the environment or essential resources that render the area useless.  This definition assigns meaning to the concept of “environmental refugees,” broadens the definition of refugees, but it also does not specify that one must leave the country, cross often undefined, arbitrary political boundaries, in order to secure this special protection.  Hence this definition is in accordance with the premises I set forth, including internally displaced peoples within the definition of an environmental refugee.

Temporarily Displaced Due to Environmental Stress

Natural disasters displace millions of people every year.  In India alone, approximately 15 million people are negatively impacted by natural disasters each year (Gadgil, Madhav and Ramachandra Guha. 1995).  Floods, earthquakes, hurricanes, volcanoes, and droughts, are just a few examples of the powerful, unexpected cause of many deaths, massive destruction, and the displacement of people.  These are examples of environmental refugees who are temporarily displaced due to natural environmental stress.  The causes are clear-cut and the effects are universal, regional, and nondiscriminatory, however, the policies determining the fate of these people are none of the above.  The privileged have the economic opportunities to leave, and generally have some sort of back-up support, while the oppressed groups generally live the closest to the areas most at risk and suffer the most damage, yet have the least available support.  I will present a case study of a natural disaster and describe how it fits into the context of environmental refugees.

On January 17, 1995, an earthquake measuring 7.2 on the Richter scale devastated an area 20km long and 1km wide, and destroyed over 400,000 houses in Kobe, Japan (Tanida 1996).  Almost 6,000 people died in the collapsing structures and approximately 600-700 more in the resulting fires.  This earthquake was estimated to cost $114 billion US dollars, three times the cost of any other natural disaster ever recorded in history (Horwich 2000).  Many privileged people moved in with family or to the mainland of China, while over 300,000 marginalized people became homeless (Horwich 2000).  Because of post-quake policies, recovery was slow, assistance was inaccessible, and the suffering was great, especially for impoverished refugees.

Initial response to the disaster was quick for volunteers, but Japanese officials were extremely regimented in their policies and rejected much assistance.  Many US doctors volunteered to help with the immediate aftermath, but they were not certified to practice medicine in Japan (Oakes 1998).  Even assistance from the Japanese Association of Acute Medicine was initially rejected because the officials were unfamiliar with the organization.  Likewise, plumbers, construction workers, and service people from other cities in Japan were not allowed to help with reconstruction because of certification problems.  A Japanese official described the situation to a reporter from the L.A. Times:  “Even in an emergency, we don’t desire letting in simple laborers” (Oakes 1998:32).  The officials making these decisions were not living in temporary housing with no water or heat, waiting for medical attention that was not to come.

Due to the slow recovery and lack of public assistance, of the 50,000 households that lived in temporary shelters, 27,000 families still remained in 1998 and 5,000 remained in 1999, with no prospects for relocation (Oakes 1998; Yoshimune 1999).  The policy in Japan said the people needed to rebuild their lands, or forgo their property rights.  As a result, most of the less affluent lost these rights because they could not afford to hire the few construction workers certified to work in that region.  Nearly 300 families lived in a park in downtown Kobe and requested wooden shelters for more security and better living conditions.  The Japanese government rejected their request, so they were forced to build their own shelters (Yoshimune 1999).

The conditions in the temporary shelters were extremely harsh.  Temperatures were below freezing at times and heating was not allowed due to fire code restrictions.  Food and water were scarce and delivery was erratic because of the confusion after the quake and the lack of a central organization of volunteers (Tanida 1996).  The emotional duress compounded by the quake, the loss of home, the deaths of friends and family, and the unfamiliar surrounding caused Post Traumatic Stress Disorder in many of the temporary shelter inhabitants, which went almost completely untreated (Tanida 1996).  Many of the elderly and women were left behind in these shelters as the young and able rebuilt their homes.

These problems were caused and exacerbated by the recession that Japan was facing even before the devastation of the quake (Yoshimune 1999).  This made government assistance nearly impossible to receive and the government discouraged foreign aid and volunteer doctors and workers.  Fukunga, editor of Tokyo Business Today, commented on the handling of the disaster by the government:

“It now seems clear that even in a national emergency the nation’s pen-pushers will not swerve a millimeter from official procedures, even if fellow citizens’ lives were at stake… While hours slopped by and thousands lost their lives in the fiery ruins left by the Kobe disaster, Japanese officials’ top priorities were observing protocol and following precedent” (Oakes 1998:32).

This situation fits into the framework of environmental refugees.  Most victims lost everything and no aid was provided for them.  Many spent over five years in temporary shelters, under severe living conditions, while denied foreign aid by their own government.  The wealthy people affected by this disaster had the means to rebuild and much of their property was insured, while nearly none of the lower classes could afford such a luxury.  If they had been accorded the rights and privileges of refugees, they would have had the assistance of the United Nations and many other international organizations, even with the denial of this aid by the Japanese government. In fact, the government denying this aid to the victims is, in and of itself, a form of persecution.

Permanently Displaced Due to Problems Created by Human Actions

Another major category of environmental refugees is comprised of people permanently displaced and resettled.  This type of environmental refugees is generally caused by human-made environmental disasters that permanently transform the land.  When humans modify an environment in attempts to control it, there are many ramifications not only for the inhabitants, but also for the immediate surroundings and the environment at large.

Often the decision to construct, and the placement of, dams is implemented as a result of uneven power structures.  The governments or powerful agencies make these decisions, without consulting the people of the designated area, and reap the benefits without distributing them to the people who have lost their lands and livelihoods.  This constitutes persecution because of the power structure, which is often also based on race, subsistence strategies, and socio-economic status.  For example, a dam would not be considered in an affluent area, so the marginalized groups must face the ramifications because they occupy the land of little or no value.  I will discuss human-caused, permanently displaced environmental refugees specifically resulting from the massive construction of dams throughout India.

The Indian government has been a major dam builder in the past four decades.  This development has displaced between 20 and 50 million people (Judge 1997).  Many of the displaced people were not consulted or properly compensated, and most of these refugees are also indigenous and tribal groups.  For example, the Karjan and Sukhi reservoirs in the state of Gujarat displaced only tribal people.  In the state of Orissa, indigenous people constituted 98% of the people displaced by the Balimela Hydro Project, and 96% of those displaced by the Upper Kolar Dam (Judge 1997).  Also, due to the land specifications necessary to construct dams, the displaced people generally were hill or river inhabitants, but were moved to plains, deserts, or mountains—less desirable, less productive lands.

This displacement and resettlement to unfamiliar areas is especially traumatic in India because people differentiate themselves in terms of religion, race, caste, marital practice, and observation of festivals and rituals.  The first of India’s many dams, the Bhakhra Dam, built in 1959, submerged the town of Bilaspur.  The people were resettled in other villages, where they have since been considered a new ethnic community known as Bilaspuris (Judge 1997).  The Bilaspuris keep familial bonds and made contracts through marriages, but these people were of different social and economic classes before the construction of the dam.

Resettlement created new health problems for refugees.  People who subsisted on the river or in the hills for many generations encountered problems learning how to subsist off of their new lands.  Also, they encountered new health risks that traditional healers were not armed to address.  Not only were the diseases and other health risks unfamiliar, but also the flora and fauna were different and the traditional medicines could not be properly made.  In one case, the refugees from Maharashtra, resettled in Parvetha Village, suffered severe health problems from the drastic move and change of environment.  These problems escalated to the point that not a single baby survived beyond infancy in the second half of 1989 (Judge 1997).

Similar cases of environmental refugees from the reservoirs of dams have been recorded all over Southeast Asia and are beginning to appear in South America.  There is a contemporary proposition for another dam along the Mekong River in Cambodia. The Sambor dam would flood 310 square miles and displace 60,000 people.  The villagers of the area have not been informed of this, except that they will be moved 30 miles away to the mountains, in a known malarial-infected region.  They will be completely cut off from the river, which has been their home since the Khmer Rouge resettled them there. Communal chief Len Chou commented: “Here we have our houses, our land, our river…there’s no water, no fish up there.”  A tribal elder known as Grandfather Dolphin remarked: “In a sense we died under the Khmer Rouge, but then we were reborn…The Mekong saved our lives” (Mecir 1999).  Now they will be moved again, and must adjust their subsistence means while fighting to survive new elements.

The problem with the construction of dams is not only the loss of the land, but also the manner in which the displaced are treated.  Virtually all are minority groups in the country, for if not indigenous groups, they are communal people in the hills, cut off from mainstream society and not afforded the same voice and rights.  The abuses extend far beyond not consulting and misinforming these groups.  The displaced have received little to no compensation for the loss of their lands, subsistence, and livelihoods. The governments have also habitually lied to the refugees and punished them for disobedience or protest. For example, protesters of the Narmada dam were repeatedly beaten, arrested, robbed, and killed (Gadgil and Guha 1995).  Also, during the construction of the Pong Dam, the Rajasthan government had agreed to resettle 66% of the displaced peoples, while only 4% were ultimately resettled (Judge 1997).

These environmental refugees should be included in the traditional definitions of refugees, although they did not cross international borders.  The people moved were obviously marginalized groups.  They were not consulted; they were given no rights and insufficient compensation; they were almost all minorities in the country; and they were violently suppressed when they protested.  These refugees were persecuted against and exploited by their own governments.  Their persecution is not only from geographical location, but also their race, class, and way of life.  They had no power to fight their governments, and no means to ask for aid from other nations.  Once again, these people could have been deemed “refugees” had they vacated their county of origin.  These instanced demonstrate that the definition of refugees is limited and thus should encompass those environmental refugees who are persecuted within their own country.

Environmental Degradation Rendering the Land Unlivable

Environmental degradation is another source of environmental displacement, caused almost exclusively by humans. By exploiting our natural resources, we are destroying the integrity of the earth and taking the opportunity to subsist on the land from others.  For example, deforestation in the Amazon rainforest strips the ecosystem of vital protection from erosion and causes nutrient leaching, which depletes the productivity of the entire area.  The indigenous people lose their source of sustenance, their homes, their safety, and their lands.  Because they are at the bottom of the power structure, they receive no compensation for this.  An example of this is the flooding and erosion in Bangladesh that causes approximately a million people each year to abandon their homes (Indra 2000). Inhabitants of the area frequently lose their lands because of flooding and erosion, or in order to claim better lands made available from drainage from another area.  The result is extremely complicated land ownership problems.  The poor are generally left to move to the flood banks, which are not intended to be permanent structures, or other areas not legally claimed (Indra 2000).

The major types of environmental degradation that displace people have been identified as deforestation, desertification, and rise in sea level (Douglas 1996; Suhrke 1994).  Overgrazing of livestock or overuse of the land causes desertification.  This creates poor grazing and growing conditions, so that eventually the cattle are killed and the seeds are consumed (Suhrke 1994).  As these people lose their means of subsistence, they quickly become environmental refugees.  Desertification has been especially devastating in the Sahel belt of northern and western Africa, because of increases in pastoralism (Douglas 1996; Suhrke 1994).

Deforestation—the clear-cutting of forests and burning of ground cover—causes more and longer periods of drought, and exposes the soil to nutrient leaching (Douglas 1996).  In Haiti, intense population growth caused deforestation by increasing demands on the resources.  This led to severe soil erosion, which increased poverty because the inhabitants could not produce for themselves.  Eventually this led to the abandonment of the land (Suhrke 1994).  Finally, rising sea levels are results of increased global temperature, which is caused by human pollution and deforestation.  Some predictions estimate the sea level may rise 30 to 110 centimeters by 2100 (Suhrke 1994; Douglas 1996).  Increasing sea levels are affecting coastal populations in China, Bangladesh, and Egypt, islands in the South Pacific and the Maldives, and urban populations in Karachi, Pakistan, and Dhaka, Bangladesh (Suhrke 1994; Douglas 1996).  However, this problem has not been directly linked to humans and remains highly controversial.

Unfortunately, companies are profiting greatly from this degradation, and some have been accused of intentionally forcing migration so that they may deforest and develop more land, and increase their profits (Manser-Fonds 1998).  In Malaysia, several companies are being prosecuted for the intentional destruction of the land and displacement of people; 43 of the companies are Malaysian, one is American, and five are Singaporean.  In fact, because of the rapid deforestation and burning of the rainforest, more than 10,000 people were sent to the hospital for respiratory problems.  The smoke generated by these companies had an Air Pollutant Index of 839; to put this into context, a rating of 100-200 API is considered unhealthy, and 300-500 API is extremely hazardous (Manser-Fonds 1998).

A major complication with environmental degradation caused refugees is that people are both the origins and victims of these problems (Hinnawi 1985).  Deforestation is directly the result of human resource abuse, and human pollutants and deforestation arguably indirectly cause the rise in sea level.  Droughts are caused by all three of the aforementioned types of degradation, as are the increased numbers and intensities of storms and unpredictable weather patterns.  Most of these types of degradation have a gradual onset, until a threshold is reached, after which it is too late to correct.

Indigenous people are most directly and readily impacted.  They are bound to the land in cultural, social, and economic ways that make them more vulnerable to changes (Suhrke 1994).  There is much more debate as to whether these people are actually environmental refugees or economic migrants.  However, I argue that because they are involuntarily moving due to environmental pressures that render their homes unsustainable, they should be granted refugee status.  The people who reap the benefits of the degradation are not those who are adversely affected by it.  Rather they are generally the multinational companies who cause and fund most of the deforestation.  Politically, it is a fine line, but people forced to evacuate an area because of various sources—toxic burning and quickly approaching fires; unrelenting floods and storms; and drought and famine—are obviously victims of unnatural, biological events, not economic migrants.

Policy Changes Causing Environmental Refugees

Finally, I propose a fourth type of environmental refugees comprised of persons displaced due to policy implementation regarding their surrounding environment.  There is no change to the land, only to the policies governing the land that displace people.  This is almost specifically applied to conservation units such as national parks that either directly displace people or cut off their means of subsistence.  However, it also pertains to instances when the land has been otherwise allocated and rendered useless to the inhabitants.  This type of environmental displacement is the direct result of those in power claiming the land for themselves, from those who have traditionally resided on it.  This strategy has been practiced since colonialism in Africa.  I will briefly discuss several examples of this, describing the essential features of this type of oppression.

In 1906, British colonial authorities prohibited indigenous hunting by declaring all wild animals the sole property of the royal crown (Naughton-Treves 1997). Ironically, they were also eradicating “problem animals,” including elephants, hippopotami, and leopards, at the same time, in order to expand the agricultural potential. During colonialism in the 19th century in Africa, indigenous groups were frequently moved, involuntarily and usually by force, out of lands claimed by the British, French, and Dutch.  This was usually under the guise of establishing a wildlife refuge, which was actually a hunting ground for the wealthy elites. The Masai in Kenya were displaced by the establishment of the Amboseli National Park, the Shanga in South Africa by Krueger National Park, and the Eek tribe from northeastern Uganda, by the establishment of Kidepo Valley National Park, who eventually starved to extinction (Armstrong 1991; Hitchcock 1995; Turnbull 1972).

“Many of the beautiful game reserves of Africa became and remain oases of plenty in deserts of rural poverty” (Armstrong 1991:54).  The land turned into national parks is generally the most productive, with the highest density and diversity of flora and fauna.  Conversely, the land to which the displaced peoples are assigned is usually of very poor quality.  Most of these parks, once used for elite hunting, now serve as tourist attractions, and the land the tribes remain on perpetually degrades.  Also, the land assigned to the people is not always of the same type as that which they were removed from; many forest people have been displaced into mountainous environments, where they have neither the skills nor the familiarity to survive (Turnbull 1972).  

Although historical accounts of these abuses are abundant, and current examples are extremely rare, this abuse still occurs.  Currently, peasant farmers in Kosi Bay, northern Zululand, are fighting to halt the establishment of a coastal nature reserve that will displace them. One resident said “The bureau is more concerned with the animals than the people and as a result we are dying” (Armstrong 1991:55).  Conversely, some of the lands are being reinstated. In 1990, Namibia was declared a nation and the Ovambo people finally cut down the fences surrounding the Etosha National Park.  Etosha was established in 1973, without any consultation of the Ovambo and their subsistence rights were literally cut off from them.  They were specifically excluded from the park as visitors until 1978 (Armstrong 1991).

The wounds are still fresh and violence is still a threat to many of these displaced peoples.  Many subsistence farmers refer to elephants as “the government’s cattle” and chimpanzees as the property of foreign researchers because they have no rights to hunt them for food or protect their farms (Naughton-Treves 1997).  Many reports of killings, torture, and arrests continue to surround these pristine parks.  The World Wide Fund and Nature who donated a helicopter to Zimbabwe to help curb poaching, found that it had been used to trap and kill 57 poachers, and withdrew the gift (Armstrong 1991).  These drastic actions do not halt starving people from finding a way to eat, and hunting is the only means many of them have ever known to survive. 

I will now examine the case of the Tyua tribe of Botswana and Zimbabwe in depth, providing historical and contextual background.  Botswana currently has more of its land allocated to wildlife management and conservation purposes than any other country in Africa; and Zimbabwe is not far behind (Hitchcock 1995).  Hunting, gathering, and fishing were predominant strategies for Tyua subsistence needs in the Nata region in the 19th century.  Later in the century some animals were declared “royal game,” only for the elites to kill, and were thus made illegal for use by subsistence hunters.  The Game and Fish Preservation Act of 1929 established several game reserves and national parks in Zimbabwe.  These included what is now considered Hwange Game Reserve in the northern part of the Nata region, where Tuya resided and were subsequently forced to move (Hitchcock 1995).

In the late 1940s, some of the Tyua were still being rounded up within the park by police patrols and violently forced to migrate south, were they were resettled in villages.  Erosional processes made fishing unproductive, and hunting and gathering was not permitted, so they were forced to adopt agricultural subsistence strategies.  By the 1970s the Tyua had shifted almost completely away from foraging, although some still risked their lives by continuing to hunt within the boundaries of the park (Hitchcock 1995).  In the late 1970’s the Botswana government allocated several ranches to small groups of cattle ranchers—forcing the local and indigenous people to move once again.

In the past several decades, many Tyua and other local people have been arrested, tortured, and killed by the Department of Wildlife and National Parks on the grounds of illegal poaching.  Some official numbers claim that at least 20, and possibly over 92 people were killed in 1992 alone (Armstrong 1991; Hitchcock 1995).  In the past 2 years, at least a dozen people, many of them unarmed and women and children, have been killed in the nearby villages when questioning by the DWNP proved unsuccessful.  Some people assert that these incidents are genocide under the guise of wildlife management.  One Tyua woman from northern Botswana proclaimed:  “Just because these people say that they are helping preserve the environment does not mean that they should be able to violate our human rights” (Hitchcock 1995:82).

This type of environmental refugee coincides with the definition of refugees and internally displaced peoples.  Their own governments victimize them: they are usually poor, foraging societies, they receive little or no compensation, and they have no means to defend themselves—so they need the protection of refugee status.  Their own governments directly persecute them because of many reasons: some would claim race, class, subsistence means, or simply because they are at the bottom of the power structure.  In the case of the Eek of northern Uganda, the displacement of the foragers into the mountains caused the starvation and the eventual extinction of the race, as is told by Turnbull (1972) in a horrifying ethnographic account.  These people are directly persecuted because the government does not acknowledge them as full citizens of the country.  They are a constant obstacle to development.  These displaced people must be considered environmental refugees, and they need the protection of this distinction.

Conclusions: The Implications of My Argument

Through this examination of environmental refugee status and classifications, I have presented examples of people persecuted by their own government and involuntarily forced to resettle in another location, generally of undesirable quality.  This feature alone warrants the inclusion of these refugees under international human rights laws and policies.  Although in the examples the refugees did not cross international borders, their situations take precedence over this requirement because of the hegemonic persecution and the sources of their displacement—natural disasters, human formed policy, and resource abuse.

The examples that I have given demonstrate the dichotomy within the power structures between the displaced and those in command.  Generally the ruling government or powerful elites have the power to control where and how the displaced can live, and they force unattractive, dangerous, and unsustainable living conditions, regardless of the foundation for discrimination (i.e. race, class, or subsistence means).  In the case of the Kobe earthquake in Japan, the people were being persecuted as their basic needs were neglected and assistance was withheld.  The people displaced in India because of dams were resettled on extremely barren, unfamiliar lands, if they were resettled at all.  Generally, the compensation was not sufficient even to cover the cost of relocating.  The inhabitants were not consulted and violently punished in the few protest attempts made.

The argument is more complex for those people displaced due to environmental degradation.  The causes of environmental degradation are generally from wealthy foreign or domestic lumber companies, development agencies, polluting businesses in the industrialized North, along with many other powerful sources.  Conversely, the people most adversely affected by these actions are the indigenous people living off the land.  Their subsistence is fragile and can easily be thrown out of balance, as my examples have demonstrated.  Because the displaced peoples are losing the most and gaining the least, while the industries are reaping the benefits at virtually no cost, this reflects an unbalanced power structure, which serves as a form of oppression.

Finally, the category I included regarding people displaced because of policy changes, generally due to the establishment of conservation units, is an obvious case of persecution based on race and class.  The foragers all around Africa have historically been displaced because of the value of the lands they require for subsistence.  They have been moved and their subsistence deemed illegal, beginning with the British Crown and continuing today by their own governments.  These actions have led to genocide in the case of the Eek, killings, brutality under the guise of wildlife management, and recurring persecution because they have no resources for protection from their own governments or other powerful institutions.

This type of persecution must encompass those who do not cross international political boundaries.  They are environmental refugees because their environment, for one reason or another, cannot sustain them any longer.  Thus they must move environments.  Especially for indigenous people, this is an extremely difficult feat.  For people who live off the land, a change in the ecosystem can mean starvation, deprivation of their subsistence methods, loss of traditions and connections to other people and the land, and even extinction.

I would like to emphasize that by defining people as internally displaced as opposed to refugees, without considering the amount of suffering incurred and automatically excluding them from most international assistance, is that some may cross greater distances and suffer more severe economic, social, and security losses than traditional refugees.  Thus, since internally displaced people may cross longer distances, suffer greater persecution, and have more difficulties assimilating to a new culture, even within the same national boundaries, they should not be automatically excluded from the assistance given to refugees.  Rather they should be evaluated by the factors mentioned above and assigned aid and protection accordingly.

Bibliography

Armstrong, Sue. 1991. The People Who Want Their Park Back. New Scientist 131(1776): 54(2).

Cohen, Roberta and Francis M. Deng. 1998. Masses in Flights: The Global Crisis of Internal Displacement. Washington, D.C.: Brookings Institute Press, pp.15-72.

Douglas, David. 1996. Environmental Eviction. The Christian Century. 113(26):839(3).  

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