Habitat destruction (also termed habitat loss and habitat reduction) is the process by which a natural habitat becomes incapable of supporting its native species. The organisms that previously inhabited the site are displaced or dead, thereby reducing biodiversity and species abundance. Habitat destruction is the leading cause of biodiversity loss. Fragmentation and loss of habitat have become one of the most important topics of research in ecology as they are major threats to the survival of endangered species.
Activities such as harvesting natural resources, industrial production and urbanization are human contributions to habitat destruction. Pressure from agriculture is the principal human cause. Some others include mining, logging, trawling, and urban sprawl. Habitat destruction is currently considered the primary cause of species extinction worldwide. Environmental factors can contribute to habitat destruction more indirectly. Geological processes, climate change, introduction of invasive species, ecosystem nutrient depletion, water and noise pollution are some examples. Loss of habitat can be preceded by an initial habitat fragmentation.
Attempts to address habitat destruction are in international policy commitments embodied by Sustainable Development Goal 15 "Life on Land" and Sustainable Development Goal 14 "Life Below Water". However, the United Nations Environment Programme report on "Making Peace with Nature" released in 2021 found that most of these efforts had failed to meet their internationally agreed upon goals.
Impacts on organismsEdit
Habitat loss is perhaps the greatest threat to organisms and biodiversity. Temple (1986) found that 82% of endangered bird species were significantly threatened by habitat loss. Most amphibian species are also threatened by native habitat loss, and some species are now only breeding in modified habitat. Endemic organisms with limited ranges are most affected by habitat destruction, mainly because these organisms are not found anywhere else within the world, and thus have less chance of recovering. Many endemic organisms have very specific requirements for their survival that can only be found within a certain ecosystem, resulting in their extinction. Extinction may also take place very long after the destruction of habitat, a phenomenon known as extinction debt. Habitat destruction can also decrease the range of certain organism populations. This can result in the reduction of genetic diversity and perhaps the production of infertile youths, as these organisms would have a higher possibility of mating with related organisms within their population, or different species. One of the most famous examples is the impact upon China's giant panda, once found in many areas of Sichuan. Now it is only found in fragmented and isolated regions in the southwest of the country, as a result of widespread deforestation in the 20th century.
As habitat destruction of an area occurs, the species diversity offsets from a combination of habitat generalists and specialists to a population primarily consisting of generalist species. Invasive species are frequently generalists that are able to survive in much more diverse habitats. Habitat destruction leading to climate change offsets the balance of species keeping up with the extinction threshold leading to a higher likelihood of extinction.
Habitat loss is one of the main environmental causes of the decline of biodiversity on local, regional, and global scales. Many believe that habitat fragmentation is also a threat to biodiversity however some believe that it is secondary to habitat loss. The reduction of the amount of habitat available results in specific landscapes that are made of isolated patches of suitable habitat throughout a hostile environment/matrix. This process is generally due to pure habitat loss as well as fragmentation effects. Pure habitat loss refers to changes occurring in the composition of the landscape that causes a decrease in individuals. Fragmentation effects refers to an addition of effects occurring due to the habitat changes. Habitat loss can result in negative effects on the dynamic of species richness. The order Hymenoptera is a diverse group of plant pollinators who are highly susceptible to the negative effects of habitat loss, this could result in a domino effect between the plant-pollinator interactions leading to major conservation implications within this group.
Destruction of populationsEdit
This section may need to be rewritten to comply with Wikipedia's quality standards. (October 2021)
Habitat fragmentation has a major impact on animal specie populations because it deprives species of what they are naturally accustomed to. This makes the species isolated, reduces the area where they can live, and creates new ecological boundaries. Some studies have shown that changes in the abiotic and biotic parameters have caused a greater impact on the ecology than the reduction in habitat size itself. They concluded that crowding a species into one space will eventually lead to the extinction of that species.
The destruction and fragmentation of natural habitats are currently the leading factors in species extinction. This is because the loss and fragmentation of habitats results in much smaller populations. Reduced population sizes ends up creating higher chances of extinction.
Studies have shown that there is no relationship between habitat patch and species number when it comes to habitat specialist plants species located in fragmented landscapes. This could potentially be due to drastic declines of plant species areas due to changes in the surrounding land.
Predators affecting the population of the preyEdit
In recent times the destruction of habitat has been the cause of the loss of many species. Sometimes the area may be small of destruction but as time goes by slowly that will cause an increase in extinction. Loss of habitat is not always the direct cause of extinction; there are other reasons causes for extinction that connect back to the loss of habitat. For example, if the sole predator in an ecosystem were to go extinct, prey populations would increase, which could possibly result in overpopulation. A higher amount of any species that can cause them to use too much of their resources. Since many species depend on limited natural resources, with the overuse they will eventually run out degrade their habitat.
Habitat destruction and fragmentation are the two most important factors in species extinction. The negative effects of decreasing size and increasing isolation of habitat are misinterpreted by fragmentation, but in reality they are much more larger effects on the population. Fragmentation generally has either no effect or a negative effect on population survival. Since habitat loss of fragmentation typically occurs together it is still not clear which process has a larger effect on extinction. Increasing isolation and habitat loss with fragmentation are all connected in a way that has negatively affected the environment.
Biodiversity hotspots are chiefly tropical regions that feature high concentrations of endemic species and, when all hotspots are combined, may contain over half of the world's terrestrial species. These hotspots are suffering from habitat loss and destruction. Most of the natural habitat on islands and in areas of high human population density has already been destroyed (WRI, 2003). Islands suffering extreme habitat destruction include New Zealand, Madagascar, the Philippines, and Japan. South and East Asia—especially China, India, Malaysia, Indonesia, and Japan—and many areas in West Africa have extremely dense human populations that allow little room for natural habitat. Marine areas close to highly populated coastal cities also face degradation of their coral reefs or other marine habitat. These areas include the eastern coasts of Asia and Africa, northern coasts of South America, and the Caribbean Sea and its associated islands.
Regions of unsustainable agriculture or unstable governments, which may go hand-in-hand, typically experience high rates of habitat destruction. South Asia, Central America, Sub-Saharan Africa, and the Amazonian tropical rainforest areas of South America are the main regions with unsustainable agricultural practices and/or government mismanagement.
Areas of high agricultural output tend to have the highest extent of habitat destruction. In the U.S., less than 25% of native vegetation remains in many parts of the East and Midwest. Only 15% of land area remains unmodified by human activities in all of Europe.
Currently, changes occurring in different environments around the world are changing the specific geographical habitats that are suitable for plants to grow. Therefore, the ability for plants to migrate to suitable environment areas will have a strong impact on the distribution of plant diversity. However, at the moment, the rates of plant migration that are influenced by habitat loss and fragmentation are not as well understood as they could be.
Tropical rainforests have received most of the attention concerning the destruction of habitat. From the approximately 16 million square kilometers of tropical rainforest habitat that originally existed worldwide, less than 9 million square kilometers remain today. The current rate of deforestation is 160,000 square kilometers per year, which equates to a loss of approximately 1% of original forest habitat each year.
Other forest ecosystems have suffered as much or more destruction as tropical rainforests. Deforestation for farming and logging have severely disturbed at least 94% of temperate broadleaf forests; many old growth forest stands have lost more than 98% of their previous area because of human activities. Tropical deciduous dry forests are easier to clear and burn and are more suitable for agriculture and cattle ranching than tropical rainforests; consequently, less than 0.1% of dry forests in Central America's Pacific Coast and less than 8% in Madagascar remain from their original extents.
Plains and desert areas have been degraded to a lesser extent. Only 10–20% of the world's drylands, which include temperate grasslands, savannas, and shrublands, scrub, and deciduous forests, have been somewhat degraded. But included in that 10–20% of land is the approximately 9 million square kilometers of seasonally dry-lands that humans have converted to deserts through the process of desertification. The tallgrass prairies of North America, on the other hand, have less than 3% of natural habitat remaining that has not been converted to farmland.
Wetlands and marine areas have endured high levels of habitat destruction. More than 50% of wetlands in the U.S. have been destroyed in just the last 200 years. Between 60% and 70% of European wetlands have been completely destroyed. In the United Kingdom, there has been an increase in demand for coastal housing and tourism which has caused a decline in marine habitats over the last 60 years. The rising sea levels and temperatures have caused soil erosion, coastal flooding, and loss of quality in the UK marine ecosystem. About one-fifth (20%) of marine coastal areas have been highly modified by humans. One-fifth of coral reefs have also been destroyed, and another fifth has been severely degraded by overfishing, pollution, and invasive species; 90% of the Philippines' coral reefs alone have been destroyed. Finally, over 35% of the mangrove ecosystems worldwide have been destroyed.
Habitat destruction through natural processes such as volcanism, fire, and climate change is well documented in the fossil record. One study shows that habitat fragmentation of tropical rainforests in Euramerica 300 million years ago led to a great loss of amphibian diversity, but simultaneously the drier climate spurred on a burst of diversity among reptiles.
Habitat destruction caused by humans includes land conversion from forests, etc. to arable land, urban sprawl, infrastructure development, and other anthropogenic changes to the characteristics of land. Habitat degradation, fragmentation, and pollution are aspects of habitat destruction caused by humans that do not necessarily involve over destruction of habitat, yet result in habitat collapse. Desertification, deforestation, and coral reef degradation are specific types of habitat destruction for those areas (deserts, forests, coral reefs).
Geist and Lambin (2002) assessed 152 case studies of net losses of tropical forest cover to determine any patterns in the proximate and underlying causes of tropical deforestation. Their results, yielded as percentages of the case studies in which each parameter was a significant factor, provide a quantitative prioritization of which proximate and underlying causes were the most significant. The proximate causes were clustered into broad categories of agricultural expansion (96%), infrastructure expansion (72%), and wood extraction (67%). Therefore, according to this study, forest conversion to agriculture is the main land use change responsible for tropical deforestation. The specific categories reveal further insight into the specific causes of tropical deforestation: transport extension (64%), commercial wood extraction (52%), permanent cultivation (48%), cattle ranching (46%), shifting (slash and burn) cultivation (41%), subsistence agriculture (40%), and fuel wood extraction for domestic use (28%). One result is that shifting cultivation is not the primary cause of deforestation in all world regions, while transport extension (including the construction of new roads) is the largest single proximate factor responsible for deforestation.
Rising global temperatures, caused by the greenhouse effect, contribute to habitat destruction, endangering various species, such as the polar bear. Melting ice caps promote rising sea levels and floods which threaten natural habitats and species globally.
While the above-mentioned activities are the proximal or direct causes of habitat destruction in that they actually destroy habitat, this still does not identify why humans destroy habitat. The forces that cause humans to destroy habitat are known as drivers of habitat destruction. Demographic, economic, sociopolitical, scientific and technological, and cultural drivers all contribute to habitat destruction.
Demographic drivers include the expanding human population; rate of population increase over time; spatial distribution of people in a given area (urban versus rural), ecosystem type, and country; and the combined effects of poverty, age, family planning, gender, and education status of people in certain areas. Most of the exponential human population growth worldwide is occurring in or close to biodiversity hotspots. This may explain why human population density accounts for 87.9% of the variation in numbers of threatened species across 114 countries, providing indisputable evidence that people play the largest role in decreasing biodiversity. The boom in human population and migration of people into such species-rich regions are making conservation efforts not only more urgent but also more likely to conflict with local human interests. The high local population density in such areas is directly correlated to the poverty status of the local people, most of whom lacking an education and family planning.
According to the Geist and Lambin (2002) study, the underlying driving forces were prioritized as follows (with the percent of the 152 cases the factor played a significant role in): economic factors (81%), institutional or policy factors (78%), technological factors (70%), cultural or socio-political factors (66%), and demographic factors (61%). The main economic factors included commercialization and growth of timber markets (68%), which are driven by national and international demands; urban industrial growth (38%); low domestic costs for land, labor, fuel, and timber (32%); and increases in product prices mainly for cash crops (25%). Institutional and policy factors included formal pro-deforestation policies on land development (40%), economic growth including colonization and infrastructure improvement (34%), and subsidies for land-based activities (26%); property rights and land-tenure insecurity (44%); and policy failures such as corruption, lawlessness, or mismanagement (42%). The main technological factor was the poor application of technology in the wood industry (45%), which leads to wasteful logging practices. Within the broad category of cultural and sociopolitical factors are public attitudes and values (63%), individual/household behavior (53%), public unconcern toward forest environments (43%), missing basic values (36%), and unconcern by individuals (32%). Demographic factors were the in-migration of colonizing settlers into sparsely populated forest areas (38%) and growing population density—a result of the first factor—in those areas (25%).
There are also feedbacks and interactions among the proximate and underlying causes of deforestation that can amplify the process. Road construction has the largest feedback effect, because it interacts with—and leads to—the establishment of new settlements and more people, which causes a growth in wood (logging) and food markets. Growth in these markets, in turn, progresses the commercialization of agriculture and logging industries. When these industries become commercialized, they must become more efficient by utilizing larger or more modern machinery that often has a worse effect on the habitat than traditional farming and logging methods. Either way, more land is cleared more rapidly for commercial markets. This common feedback example manifests just how closely related the proximate and underlying causes are to each other.
Impact on human populationEdit
Habitat destruction can vastly increase an area's vulnerability to natural disasters like flood and drought, crop failure, spread of disease, and water contamination.[page needed] On the other hand, a healthy ecosystem with good management practices can reduce the chance of these events happening, or will at least mitigate adverse impacts. Eliminating swamps—the habitat of pests such as mosquitoes—has contributed to the prevention of diseases such as malaria. Completely depriving an infectious agent (such as a virus) of its habitat—by vaccination, for example—can result in eradicating that infectious agent.
Agricultural land can suffer from the destruction of the surrounding landscape. Over the past 50 years, the destruction of habitat surrounding agricultural land has degraded approximately 40% of agricultural land worldwide via erosion, salinization, compaction, nutrient depletion, pollution, and urbanization. Humans also lose direct uses of natural habitat when habitat is destroyed. Aesthetic uses such as birdwatching, recreational uses like hunting and fishing, and ecotourism usually[quantify] rely upon relatively undisturbed habitat. Many[quantify] people value the complexity of the natural world and express concern at the loss of natural habitats and of animal or plant species worldwide.
Probably the most profound impact that habitat destruction has on people is the loss of many valuable ecosystem services. Habitat destruction has altered nitrogen, phosphorus, sulfur, and carbon cycles, which has increased the frequency and severity of acid rain, algal blooms, and fish kills in rivers and oceans and contributed tremendously to global climate change.[need quotation to verify] One ecosystem service whose significance is becoming better understood is climate regulation. On a local scale, trees provide windbreaks and shade; on a regional scale, plant transpiration recycles rainwater and maintains constant annual rainfall; on a global scale, plants (especially trees in tropical rainforests) around the world counter the accumulation of greenhouse gases in the atmosphere by sequestering carbon dioxide through photosynthesis. Other ecosystem services that are diminished or lost altogether as a result of habitat destruction include watershed management, nitrogen fixation, oxygen production, pollination (see pollinator decline),waste treatment (i.e., the breaking down and immobilization of toxic pollutants), and nutrient recycling of sewage or agricultural runoff.
The loss of trees from tropical rainforests alone represents a substantial diminishing of Earth's ability to produce oxygen and to use up carbon dioxide. These services are becoming even more important as increasing carbon dioxide levels is one of the main contributors to global climate change. The loss of biodiversity may not directly affect humans, but the indirect effects of losing many species as well as the diversity of ecosystems in general are enormous. When biodiversity is lost, the environment loses many species that perform valuable and unique roles in the ecosystem. The environment and all its inhabitants rely on biodiversity to recover from extreme environmental conditions. When too much biodiversity is lost, a catastrophic event such as an earthquake, flood, or volcanic eruption could cause an ecosystem to crash, and humans would obviously suffer from that. Loss of biodiversity also means that humans are losing animals that could have served as biological-control agents and plants that could potentially provide higher-yielding crop varieties, pharmaceutical drugs to cure existing or future diseases (such as cancer), and new resistant crop-varieties for agricultural species susceptible to pesticide-resistant insects or virulent strains of fungi, viruses, and bacteria.
The negative effects of habitat destruction usually impact rural populations more directly than urban populations. Across the globe, poor people suffer the most when natural habitat is destroyed, because less natural habitat means fewer natural resources per capita, yet wealthier people and countries can simply pay more to continue to receive more than their per capita share of natural resources.
Another way to view the negative effects of habitat destruction is to look at the opportunity cost of destroying a given habitat. In other words, what do people lose out on with the removal of a given habitat? A country may increase its food supply by converting forest land to row-crop agriculture, but the value of the same land may be much larger when it can supply natural resources or services such as clean water, timber, ecotourism, or flood regulation and drought control.[need quotation to verify]
The rapid expansion of the global human population is increasing the world's food requirement substantially. Simple logic dictates that more people will require more food. In fact, as the world's population increases dramatically, agricultural output will need to increase by at least 50%, over the next 30 years. In the past, continually moving to new land and soils provided a boost in food production to meet the global food demand. That easy fix will no longer be available, however, as more than 98% of all land suitable for agriculture is already in use or degraded beyond repair.
The impending global food crisis will be a major source of habitat destruction. Commercial farmers are going to become desperate to produce more food from the same amount of land, so they will use more fertilizers and show less concern for the environment to meet the market demand. Others will seek out new land or will convert other land-uses to agriculture. Agricultural intensification will become widespread at the cost of the environment and its inhabitants. Species will be pushed out of their habitat either directly by habitat destruction or indirectly by fragmentation, degradation, or pollution. Any efforts to protect the world's remaining natural habitat and biodiversity will compete directly with humans' growing demand for natural resources, especially new agricultural lands.
Tropical deforestation: In most cases of tropical deforestation, three to four underlying causes are driving two to three proximate causes. This means that a universal policy for controlling tropical deforestation would not be able to address the unique combination of proximate and underlying causes of deforestation in each country. Before any local, national, or international deforestation policies are written and enforced, governmental leaders must acquire a detailed understanding of the complex combination of proximate causes and underlying driving forces of deforestation in a given area or country. This concept, along with many other results of tropical deforestation from the Geist and Lambin study, can easily be applied to habitat destruction in general.
Shoreline erosion: Coastal erosion is a natural process as storms, waves, tides and other water level changes occur. Shoreline stabilization can be done by barriers between land and water such as seawalls and bulkheads. Living shorelines are gaining attention as new stabilization method. These can reduce damage and erosion while simultaneously providing ecosystem services such as food production, nutrient and sediment removal, and water quality improvement to society
To prevent an area from losing its specialist species to generalist invasive species depends on the extent of the habitat destruction that has already taken place. In areas where habitat is relatively undisturbed, halting further habitat destruction may be enough. In areas where habitat destruction is more extreme (fragmentation or patch loss), restoration ecology may be needed.
Education of the general public is possibly the best way to prevent further human habitat destruction. Changing the dull creep of environmental impacts from being viewed as acceptable to being seen a reason for change to more sustainable practices. Education about the necessity of family planning to slow population growth is important as greater population leads to greater human caused habitat destruction.
The biggest potential to solving the issue of habitat destruction comes from solving the political, economical and social problems that go along with it such as, individual and commercial material consumption, sustainable extraction of resources, conservation areas, restoration of degraded land and addressing climate change.
Governmental leaders need to take action by addressing the underlying driving forces, rather than merely regulating the proximate causes. In a broader sense, governmental bodies at a local, national, and international scale need to emphasize:
- Considering the irreplaceable ecosystem services provided by natural habitats.
- Protecting remaining intact sections of natural habitat.
- Finding ecological ways to increase agricultural output without increasing the total land in production.
- Reducing human population and expansion. Apart from improving access to contraception globally, furthering gender equality also has a great benefit. When women have the same education (decision-making power), this generally leads to smaller families.
It is argued that the effects of habitat loss and fragmentation can be counteracted by including spatial processes in potential restoration management plans. However, even though spatial dynamics are incredibly important in the conservation and recovery of species, a limited amount of management plans are taking the spatial effects of habitat restoration and conservation into consideration.
- Calizza, Edoardo; Costantini, Maria Letizia; Careddu, Giulio; Rossi, Loreto (17 June 2017). "Effect of habitat degradation on competition, carrying capacity, and species assemblage stability". Ecology and Evolution. Wiley. 7 (15): 5784–5796. doi:10.1002/ece3.2977. ISSN 2045-7758. PMC 5552933. PMID 28811883.
- Sahney, S; Benton, Michael J.; Falcon-Lang, Howard J. (1 December 2010). "Rainforest collapse triggered Pennsylvanian tetrapod diversification in Euramerica" (PDF). Geology. 38 (12): 1079–1082. Bibcode:2010Geo....38.1079S. doi:10.1130/G31182.1. Archived from the original on 11 October 2011. Retrieved 29 November 2010 – via GeoScienceWorld.
- Marvier, Michelle; Kareiva, Peter; Neubert, Michael G. (2004). "Habitat Destruction, Fragmentation, and Disturbance Promote Invasion by Habitat Generalists in a Multispecies Metapopulation". Risk Analysis. 24 (4): 869–878. doi:10.1111/j.0272-4332.2004.00485.x. ISSN 0272-4332. PMID 15357806. S2CID 44809930. Archived from the original on 23 July 2021. Retrieved 18 March 2021.
- WIEGAND, THORSTEN; REVILLA, ELOY; MOLONEY, KIRK A. (February 2005). "Effects of Habitat Loss and Fragmentation on Population Dynamics". Conservation Biology. 19 (1): 108–121. doi:10.1111/j.1523-1739.2005.00208.x. ISSN 0888-8892. S2CID 33258495.
- Pimm & Raven, 2000, pp. 843–845.
- United Nations Environment Programme (2021). Making Peace with Nature: A scientific blueprint to tackle the climate, biodiversity and pollution emergencies. Nairobi. https://www.unep.org/resources/making-peace-nature Archived 2021-03-23 at the Wayback Machine
- Scholes & Biggs, 2004.
- Barbault & Sastrapradja, 1995.
- Beebee, Trevor J.C.; Griffiths, Richard A. (31 May 2005). "The amphibian decline crisis: A watershed for conservation biology?". Biological Conservation. 125 (3): 271. doi:10.1016/j.biocon.2005.04.009.
- Borzée, Amaël; Jang, Yikweon (28 April 2015). "Description of a seminatural habitat of the endangered Suweon treefrog Hyla suweonensis". Animal Cells and Systems. 19 (3): 216. doi:10.1080/19768354.2015.1028442. S2CID 86565631.
- "The Panda's Forest: Biodiversity Loss". 24 August 2011. Archived from the original on 23 September 2011. Retrieved 6 September 2011.
- Evangelista, Paul H.; Kumar, Sunil; Stohlgren, Thomas J.; Jarnevich, Catherine S.; Crall, Alycia W.; Norman III, John B.; Barnett, David T. (2008). "Modelling invasion for a habitat generalist and a specialist plant species". Diversity and Distributions. 14 (5): 808–817. doi:10.1111/j.1472-4642.2008.00486.x. ISSN 1366-9516. S2CID 14148713. Archived from the original on 23 July 2021. Retrieved 18 March 2021.
- Travis, J. M. J. (7 March 2003). "Climate change and habitat destruction: a deadly anthropogenic cocktail". Proceedings of the Royal Society of London. Series B: Biological Sciences. 270 (1514): 467–473. doi:10.1098/rspb.2002.2246. ISSN 0962-8452. PMC 1691268. PMID 12641900.
- Helm, Aveliina; Hanski, Ilkka; Partel, Meelis (9 November 2005). "Slow response of plant species richness to habitat loss and fragmentation". Ecology Letters. 9 (1): 72–77. doi:10.1111/j.1461-0248.2005.00841.x. ISSN 1461-023X. PMID 16958870.
- Spiesman, Brian J.; Inouye, Brian D. (December 2013). "Habitat loss alters the architecture of plant–pollinator interaction networks". Ecology. 94 (12): 2688–2696. doi:10.1890/13-0977.1. ISSN 0012-9658. PMID 24597216.
- Ewers, Didham, Robert M., Raphael K. (15 March 2007). "Confounding factors in the detection of species responses to habitat fragmentation". Wiley Online Library. Vol. 81. p. 117. doi:10.1017/S1464793105006949. Archived from the original on 15 April 2021. Retrieved 15 March 2021.
- Fahrig, Lenore (1997). "Relative Effects of Habitat Loss and Fragmentation on Population Extinction". The Journal of Wildlife Management. 61 (3): 603–610. doi:10.2307/3802168. ISSN 0022-541X. JSTOR 3802168.
- Nakagiri, Tainaka, Nariyuki, Kei-ichi (1 May 2004). "Indirect effects of habitat destruction in model ecosystems". Science Direct. Archived from the original on 23 July 2021. Retrieved 30 March 2021.
- Fahrig, Lenore (July 1997). "Relative Effects of Habitat Loss and Fragmentation on Population Extinction". JOURNAL ARTICLE. JSTOR 3802168. Archived from the original on 15 April 2021. Retrieved 30 March 2021.
- "Tierras Bajas Deforestation, Bolivia". Newsroom. Photo taken from the International Space Station on April 16, 2001. NASA Earth Observatory. 16 April 2001. Archived from the original on 20 September 2008. Retrieved 11 August 2008.
- Cincotta & Engelman, 2000.
- Primack, 2006.
- Stein et al., 2000.
- Higgins, Steven I.; Lavorel, Sandra; Revilla, Eloy (25 April 2003). "Estimating plant migration rates under habitat loss and fragmentation". Oikos. 101 (2): 354–366. doi:10.1034/j.1600-0706.2003.12141.x. hdl:10261/51883. ISSN 0030-1299.
- Laurance, 1999.
- Kauffman & Pyke, 2001.
- White et al., 2000.
- Ravenga et al., 2000.
- "United Kingdom: Environmental Issues, Policies and Clean Technology". AZoCleantech.com. 8 June 2015. Archived from the original on 30 March 2019. Retrieved 12 December 2017.
- Burke et al., 2000.
- Millennium Ecological Assessment, 2005.
- "File:Burnt forest GJ.jpg", Wikipedia, archived from the original on 23 July 2021, retrieved 18 March 2021
- Butler, Rhett A. (31 March 2021). "Global forest loss increases in 2020". Mongabay. Archived from the original on 1 April 2021. ● Mongabay graphing WRI data from "Forest Loss / How much tree cover is lost globally each year?". research.WRI.org. World Resources Institute — Global Forest Review. January 2021. Archived from the original on 10 March 2021.
- Geist & Lambin, 2002.
- Durner, George M.; Douglas, David C.; Nielson, Ryan M.; Amstrup, Steven C.; McDonald, Trent L.; Stirling, Ian; Mauritzen, Mette; Born, Erik W.; Wiig, Øystein; Deweaver, Eric; Serreze, Mark C.; Belikov, Stanislav E.; Holland, Marika M.; Maslanik, James; Aars, Jon; Bailey, David A.; Derocher, Andrew E. (2009). "Predicting 21st-century polar bear habitat distribution from global climate models". Ecological Monographs. 79: 25–58. doi:10.1890/07-2089.1. S2CID 85677324.
- Baker, Jason D.; Littnan, Charles L.; Johnston, David W. (24 May 2006). "Potential effects of sea level rise on the terrestrial habitats of endangered and endemic megafauna in the Northwestern Hawaiian Islands". Endangered Species Research. 2: 21–30. doi:10.3354/esr002021. ISSN 1863-5407.
- Galbraith, H.; Jones, R.; Park, R.; Clough, J.; Herrod-Julius, S.; Harrington, B.; Page, G. (1 June 2002). "Global Climate Change and Sea Level Rise: Potential Losses of Intertidal Habitat for Shorebirds". Waterbirds. 25 (2): 173–183. doi:10.1675/1524-4695(2002)025[0173:GCCASL]2.0.CO;2. ISSN 1524-4695. S2CID 86365454.
- McKee et al., 2003.
- Tibbetts, 2006.
- Mumba, Musonda; Munang, Richard; Rivington, Mike (27 June 2013). "Ecosystem Management: The Need to Adopt a Different Approach Under a Changing Climate". Resources Report. United Nations Environment Programme/Macaulay Land Use Research Institute. Archived from the original on 15 April 2021. Retrieved 15 April 2021.
- Bull, David (1982). A Growing Problem: Pesticides and the Third World Poor. OXFAM. p. 29. ISBN 9780855980641. Archived from the original on 24 April 2021. Retrieved 24 April 2021.
It was drainage of swampland which eradicated the disease [malaria] from the Fenlands in Britain and the Pontine marshes of Italy.
Reiter, Paul (1997). "Surveillance and Control of Urban Dengue Vectors". In Gubler, Duane J.; Ooi, Eng Eong; Vasudevan, Subhash; Farrar, Jeremy (eds.). Dengue and Dengue Hemorrhagic Fever. CAB books (2, revised ed.). Wallingford, Oxfordshire: CABI (published 2014). p. 504. ISBN 9781845939649. Retrieved 30 September 2021.
The eradication of smallpox virus [...] is also a perfect example of habitat destruction: smallpox vaccination gives life-long immunity, and humans are the only host. Mass vaccination therefore resulted in total elimination of the habitat of the virus.
- "Valuing nature". World Wildlife Foundation. WWF. Archived from the original on 25 April 2021. Retrieved 15 April 2021.
- Benoît Geslin; Benoit Gauzens; Elisa Thébault; Isabelle Dajoz (2013). "Plant Pollinator Networks along a Gradient of Urbanisation". PLOS ONE. 8 (5): e63421. Bibcode:2013PLoSO...863421G. doi:10.1371/journal.pone.0063421. PMC 3661593. PMID 23717421.
- Tilman et al., 2001.
- Sanderson et al., 2002.
- "Living Shorelines". NOAA Habitat Blueprint. Archived from the original on 18 March 2021. Retrieved 23 March 2021.
- Liao, Jinbao; Bearup, Daniel; Wang, Yeqiao; Nijs, Ivan; Bonte, Dries; Li, Yuanheng; Brose, Ulrich; Wang, Shaopeng; Blasius, Bernd (2 May 2017). "Robustness of metacommunities with omnivory to habitat destruction: disentangling patch fragmentation from patch loss". Ecology. 98 (6): 1631–1639. doi:10.1002/ecy.1830. hdl:10067/1418100151162165141. ISSN 0012-9658. PMID 28369715. Archived from the original on 23 July 2021. Retrieved 18 March 2021.
- Morrison, M.L. (1999), "Habitat and habitat destruction", Environmental Geology. Encyclopedia of Earth Science, Encyclopedia of Earth Science, Dordrecht: Springer, pp. 308–309, doi:10.1007/1-4020-4494-1_165, ISBN 0-412-74050-8
- Ehrlich, P. R.; Pringle, R. M. (11 August 2008). "Where does biodiversity go from here? A grim business-as-usual forecast and a hopeful portfolio of partial solutions". Proceedings of the National Academy of Sciences. 105 (Supplement 1): 11579–11586. doi:10.1073/pnas.0801911105. ISSN 0027-8424. PMC 2556413. PMID 18695214.
- Townsend, Patricia A.; Levey, Douglas J. (2002). "An Experimental Test of Whether Habitat Corridors Affect Pollen Transfer". Ecology. 86 (2): 466–475. doi:10.1890/03-0607. ISSN 0012-9658. Archived from the original on 23 July 2021. Retrieved 18 March 2021.
- Bringezu, Stefan (2009), "Visions of a sustainable resource use", Sustainable Resource Management: Global Trends, Visions and Policies, Greenleaf Publishing Limited, pp. 155–215, doi:10.9774/gleaf.978-1-907643-07-1_5, ISBN 978-1-907643-07-1, retrieved 18 March 2021
- Elmarsdottir, Asrun; Aradottir, Asa L.; Trlica, M. J. (26 September 2003). "Microsite availability and establishment of native species on degraded and reclaimed sites". Journal of Applied Ecology. 40 (5): 815–823. doi:10.1046/j.1365-2664.2003.00848.x. ISSN 0021-8901.
- Huxel, Gary R.; Hastings, Alan (September 1999). "Habitat Loss, Fragmentation, and Restoration". Restoration Ecology. 7 (3): 309–315. doi:10.1046/j.1526-100x.1999.72024.x. ISSN 1061-2971. S2CID 86235090.
- Barbault, R. and S. D. Sastrapradja. 1995. Generation, maintenance and loss of biodiversity. Global Biodiversity Assessment, Cambridge Univ. Press, Cambridge pp. 193–274. ISBN 9780521564816
- Burke, L.; Y. Kura; K. Kassem; C. Ravenga; M. Spalding; D. McAllister (2000). Pilot Assessment of Global Ecosystems: Coastal Ecosystems. World Resources Institute, Washington, D.C. ISBN 9781569734582. Archived from the original on 4 May 2018. Retrieved 19 February 2020.
- Cincotta, R.P., and R. Engelman. 2000. Nature's place: human population density and the future of biological diversity. Population Action International. Washington, D.C.
- Geist H. J.; Lambin E. E. (2002). "Proximate causes and underlying driving forces of tropical deforestation". BioScience. 52 (2): 143–150. doi:10.1641/0006-3568(2002)052[0143:PCAUDF]2.0.CO;2.
- Kauffman, J. B. and D. A. Pyke. 2001. Range ecology, global livestock influences. In S. A. Levin (ed.), Encyclopedia of Biodiversity 5: 33–52. Academic Press, San Diego, CA.
- Laurance W. F. (1999). "Reflections on the tropical deforestation crisis". Biological Conservation. 91 (2–3): 109–117. CiteSeerX 10.1.1.501.3004. doi:10.1016/S0006-3207(99)00088-9.
- McKee J. K.; Sciulli P.W.; Fooce C. D.; Waite T. A. (2003). "Forecasting global biodiversity threats associated with human population growth". Biological Conservation. 115: 161–164. doi:10.1016/s0006-3207(03)00099-5.
- Millennium Ecosystem Assessment (Program). 2005. Ecosystems and Human Well-Being Archived 2016-06-10 at the Wayback Machine. Millennium Ecosystem Assessment. Island Press, Covelo, CA.
- Primack, R. B. 2006. Essentials of Conservation Biology. 4th Ed. Habitat destruction, pages 177–188. Sinauer Associates, Sunderland, MA.
- Pimm Stuart L.; Raven Peter (2000). "Biodiversity: Extinction by numbers". Nature. 403 (6772): 843–845. Bibcode:2000Natur.403..843P. doi:10.1038/35002708. PMID 10706267. S2CID 4310784.
- Ravenga, C., J. Brunner, N. Henninger, K. Kassem, and R. Payne. 2000. Pilot Analysis of Global Ecosystems: Wetland Ecosystems. World Resources Institute, Washington, D.C.
- Sahney S.; Benton M.J.; Falcon-Lang H.J. (2010). "Rainforest collapse triggered Pennsylvanian tetrapod diversification in Euramerica". Geology. 38 (12): 1079–1082. Bibcode:2010Geo....38.1079S. doi:10.1130/G31182.1.
- Sanderson E. W.; Jaiteh M.; Levy M. A.; Redford K. H.; Wannebo A. V.; Woolmer G. (2002). "The human footprint and the last of the wild". BioScience. 52 (10): 891–904. doi:10.1641/0006-3568(2002)052[0891:thfatl]2.0.co;2.
- Scholes, R. J. and R. Biggs (eds.). 2004. Ecosystem services in Southern Africa: a regional assessment. The regional scale component of the Southern African Millennium Ecosystem Assessment. Archived 2020-10-02 at the Wayback Machine CSIR, Pretoria, South Africa.
- Stein, B. A., L. S. Kutner, and J. S. Adams (eds.). 2000. Precious Heritage: The Status of Biodiversity in the United States. Oxford University Press, New York.
- Temple S. A. (1986). "The problem of avian extinctions". Current Ornithology. Ornithology. Vol. 3. pp. 453–485. doi:10.1007/978-1-4615-6784-4_11. ISBN 978-1-4615-6786-8.
- Tibbetts John (2006). "Louisiana's Wetlands: A Lesson in Nature Appreciation". Environ Health Perspect. 114 (1): A40–A43. doi:10.1289/ehp.114-a40. PMC 1332684. PMID 16393646.
- Tilman D.; Fargione J.; Wolff B.; D'Antonio C.; Dobson A.; Howarth R.; Schindler D.; Schlesinger W. H.; Simberloff D.; et al. (2001). "Forecasting agriculturally driven global environmental change". Science. 292 (5515): 281–284. Bibcode:2001Sci...292..281T. doi:10.1126/science.1057544. PMID 11303102. S2CID 23847498.
- White, R. P., S. Murray, and M. Rohweder. 2000. Pilot Assessment of Global Ecosystems: Grassland Ecosystems. World Resources Institute, Washington, D. C.
- WRI. 2003. World Resources 2002–2004: Decisions for the Earth: Balance, voice, and power. 328 pp. World Resources Institute, Washington, D.C.