Deforestation(Redirected from Causes of deforestation)
Deforestation, clearance, or clearing is the removal of a forest or stand of trees from land which is then converted to a non-forest use. Deforestation can involve conversion of forest land to farms, ranches, or urban use. The most concentrated deforestation occurs in tropical rainforests. About 31% of Earth's land surface is covered by forests.
Deforestation can occur for several reasons: trees can be cut down to be used for building or sold as fuel (sometimes in the form of charcoal or timber), while cleared land can be used as pasture for livestock and plantation. The removal of trees without sufficient reforestation has resulted in habitat damage, biodiversity loss, and aridity. It has adverse impacts on biosequestration of atmospheric carbon dioxide. Deforestation has also been used in war to deprive the enemy of vital resources and cover for its forces. Modern examples of this were the use of Agent Orange by the British military in Malaya during the Malayan Emergency and by the United States military in Vietnam during the Vietnam War. As of 2005, net deforestation rates had ceased to increase in countries with a per capita GDP of at least US$4,600. Deforested regions typically incur significant adverse soil erosion and frequently degrade into wasteland.
Disregard of ascribed value, lax forest management, and deficient environmental laws are some of the factors that lead to large-scale deforestation. In many countries, deforestation–both naturally occurring and human-induced–is an ongoing issue. Deforestation causes extinction, changes to climatic conditions, desertification, and displacement of populations, as observed by current conditions and in the past through the fossil record. More than half of all plant and land animal species in the world live in tropical forests.
Between 2000 and 2012, 2.3 million square kilometres (890,000 sq mi) of forests around the world were cut down. As a result of deforestation, only 6.2 million square kilometres (2.4 million square miles) remain of the original 16 million square kilometres (6 million square miles) of forest that formerly covered the Earth. An area the size of a football pitch is cleared from the Amazon rainforest every minute, with 136 million acres (55 million hectares) of rainforest cleared for animal agriculture overall.
According to the United Nations Framework Convention on Climate Change (UNFCCC) secretariat, the overwhelming direct cause of deforestation is agriculture. Subsistence farming is responsible for 48% of deforestation; commercial agriculture is responsible for 32%; logging is responsible for 14%, and fuel wood removals make up 5%.
Experts do not agree on whether industrial logging is an important contributor to global deforestation. Some argue that poor people are more likely to clear forest because they have no alternatives, others that the poor lack the ability to pay for the materials and labour needed to clear forest. One study found that population increases due to high fertility rates were a primary driver of tropical deforestation in only 8% of cases.
Other causes of contemporary deforestation may include corruption of government institutions, the inequitable distribution of wealth and power, population growth and overpopulation, and urbanization. Globalization is often viewed as another root cause of deforestation, though there are cases in which the impacts of globalization (new flows of labor, capital, commodities, and ideas) have promoted localized forest recovery.
In 2000 the United Nations Food and Agriculture Organization (FAO) found that "the role of population dynamics in a local setting may vary from decisive to negligible", and that deforestation can result from "a combination of population pressure and stagnating economic, social and technological conditions".
The degradation of forest ecosystems has also been traced to economic incentives that make forest conversion appear more profitable than forest conservation. Many important forest functions have no markets, and hence, no economic value that is readily apparent to the forests' owners or the communities that rely on forests for their well-being. From the perspective of the developing world, the benefits of forest as carbon sinks or biodiversity reserves go primarily to richer developed nations and there is insufficient compensation for these services. Developing countries feel that some countries in the developed world, such as the United States of America, cut down their forests centuries ago and benefited economically from this deforestation, and that it is hypocritical to deny developing countries the same opportunities, i.e. that the poor shouldn't have to bear the cost of preservation when the rich created the problem.
Some commentators have noted a shift in the drivers of deforestation over the past 30 years. Whereas deforestation was primarily driven by subsistence activities and government-sponsored development projects like transmigration in countries like Indonesia and colonization in Latin America, India, Java, and so on, during the late 19th century and the earlier half of the 20th century, by the 1990s the majority of deforestation was caused by industrial factors, including extractive industries, large-scale cattle ranching, and extensive agriculture. Since 2001, commodity-driven deforestation, which is more likely to be permanent, has accounted for about a quarter of all forest disturbance, and this loss has been concentrated in South America and Southeast Asia.
Deforestation is a contributor to global warming, and is often cited as one of the major causes of the enhanced greenhouse effect. Tropical deforestation is responsible for approximately 20% of world greenhouse gas emissions. According to the Intergovernmental Panel on Climate Change deforestation, mainly in tropical areas, could account for up to one-third of total anthropogenic carbon dioxide emissions. But recent calculations suggest that carbon dioxide emissions from deforestation and forest degradation (excluding peatland emissions) contribute about 12% of total anthropogenic carbon dioxide emissions with a range from 6% to 17%. Deforestation causes carbon dioxide to linger in the atmosphere. As carbon dioxide accrues, it produces a layer in the atmosphere that traps radiation from the sun. The radiation converts to heat which causes global warming, which is better known as the greenhouse effect. Plants remove carbon in the form of carbon dioxide from the atmosphere during the process of photosynthesis, but release some carbon dioxide back into the atmosphere during normal respiration. Only when actively growing can a tree or forest remove carbon, by storing it in plant tissues. Both the decay and the burning of wood release much of this stored carbon back into the atmosphere. Although an accumulation of wood is generally necessary for carbon sequestration, in some forests the network of symbiotic fungi that surround the trees' roots can store a significant amount of carbon, storing it underground even if the tree which supplied it dies and decays, or is harvested and burned. Another way carbon can be sequestered by forests is for the wood to be harvested and turned into long-lived products, with new young trees replacing them. Deforestation may also cause carbon stores held in soil to be released. Forests can be either sinks or sources depending upon environmental circumstances. Mature forests alternate between being net sinks and net sources of carbon dioxide (see carbon dioxide sink and carbon cycle).
In deforested areas, the land heats up faster and reaches a higher temperature, leading to localized upward motions that enhance the formation of clouds and ultimately produce more rainfall. However, according to the Geophysical Fluid Dynamics Laboratory, the models used to investigate remote responses to tropical deforestation showed a broad but mild temperature increase all through the tropical atmosphere. The model predicted <0.2 °C warming for upper air at 700 mb and 500 mb. However, the model shows no significant changes in other areas besides the Tropics. Though the model showed no significant changes to the climate in areas other than the Tropics, this may not be the case since the model has possible errors and the results are never absolutely definite. Deforestation affects wind flows, water vapour flows and absorption of solar energy thus clearly influencing local and global climate.
Reducing emissions from deforestation and forest degradation (REDD) in developing countries has emerged as a new potential to complement ongoing climate policies. The idea consists in providing financial compensations for the reduction of greenhouse gas (GHG) emissions from deforestation and forest degradation".
Rainforests are widely believed by laymen to contribute a significant amount of the world's oxygen, although it is now accepted by scientists that rainforests contribute little net oxygen to the atmosphere and deforestation has only a minor effect on atmospheric oxygen levels. However, the incineration and burning of forest plants to clear land releases large amounts of CO2, which contributes to global warming. Scientists also state that tropical deforestation releases 1.5 billion tons of carbon each year into the atmosphere.
The water cycle is also affected by deforestation. Trees extract groundwater through their roots and release it into the atmosphere. When part of a forest is removed, the trees no longer transpire this water, resulting in a much drier climate. Deforestation reduces the content of water in the soil and groundwater as well as atmospheric moisture. The dry soil leads to lower water intake for the trees to extract. Deforestation reduces soil cohesion, so that erosion, flooding and landslides ensue.
Shrinking forest cover lessens the landscape's capacity to intercept, retain and transpire precipitation. Instead of trapping precipitation, which then percolates to groundwater systems, deforested areas become sources of surface water runoff, which moves much faster than subsurface flows. Forests return most of the water that falls as precipitation to the atmosphere by transpiration. In contrast, when an area is deforested, almost all precipitation is lost as run-off. That quicker transport of surface water can translate into flash flooding and more localized floods than would occur with the forest cover. Deforestation also contributes to decreased evapotranspiration, which lessens atmospheric moisture which in some cases affects precipitation levels downwind from the deforested area, as water is not recycled to downwind forests, but is lost in runoff and returns directly to the oceans. According to one study, in deforested north and northwest China, the average annual precipitation decreased by one third between the 1950s and the 1980s.
- their canopies intercept a proportion of precipitation, which is then evaporated back to the atmosphere (canopy interception);
- their litter, stems and trunks slow down surface runoff;
- their roots create macropores – large conduits – in the soil that increase infiltration of water;
- they contribute to terrestrial evaporation and reduce soil moisture via transpiration;
- their litter and other organic residue change soil properties that affect the capacity of soil to store water.
- their leaves control the humidity of the atmosphere by transpiring. 99% of the water absorbed by the roots moves up to the leaves and is transpired.
As a result, the presence or absence of trees can change the quantity of water on the surface, in the soil or groundwater, or in the atmosphere. This in turn changes erosion rates and the availability of water for either ecosystem functions or human services. Deforestation on lowland plains moves cloud formation and rainfall to higher elevations.
The forest may have little impact on flooding in the case of large rainfall events, which overwhelm the storage capacity of forest soil if the soils are at or close to saturation.
Deforestation disrupts normal weather patterns creating hotter and drier weather thus increasing drought, desertification, crop failures, melting of the polar ice caps, coastal flooding and displacement of major vegetation regimes.
Due to surface plant litter, forests that are undisturbed have a minimal rate of erosion. The rate of erosion occurs from deforestation, because it decreases the amount of litter cover, which provides protection from surface runoff. The rate of erosion is around 2 metric tons per square kilometre. This can be an advantage in excessively leached tropical rain forest soils. Forestry operations themselves also increase erosion through the development of (forest) roads and the use of mechanized equipment.
Deforestation in China's Loess Plateau many years ago has led to soil erosion; this erosion has led to valleys opening up. The increase of soil in the runoff causes the Yellow River to flood and makes it yellow colored.
Greater erosion is not always a consequence of deforestation, as observed in the southwestern regions of the US. In these areas, the loss of grass due to the presence of trees and other shrubbery leads to more erosion than when trees are removed.
Soils are reinforced by the presence of trees, which secure the soil by binding their roots to soil bedrock. Due to deforestation, the removal of trees causes sloped lands to be more susceptible to landslides.
Deforestation on a human scale results in decline in biodiversity, and on a natural global scale is known to cause the extinction of many species. The removal or destruction of areas of forest cover has resulted in a degraded environment with reduced biodiversity. Forests support biodiversity, providing habitat for wildlife; moreover, forests foster medicinal conservation. With forest biotopes being irreplaceable source of new drugs (such as taxol), deforestation can destroy genetic variations (such as crop resistance) irretrievably.
Since the tropical rainforests are the most diverse ecosystems on Earth and about 80% of the world's known biodiversity could be found in tropical rainforests, removal or destruction of significant areas of forest cover has resulted in a degraded environment with reduced biodiversity. A study in Rondônia, Brazil, has shown that deforestation also removes the microbial community which is involved in the recycling of nutrients, the production of clean water and the removal of pollutants.
It has been estimated that we are losing 137 plant, animal and insect species every single day due to rainforest deforestation, which equates to 50,000 species a year. Others state that tropical rainforest deforestation is contributing to the ongoing Holocene mass extinction. The known extinction rates from deforestation rates are very low, approximately 1 species per year from mammals and birds which extrapolates to approximately 23,000 species per year for all species. Predictions have been made that more than 40% of the animal and plant species in Southeast Asia could be wiped out in the 21st century. Such predictions were called into question by 1995 data that show that within regions of Southeast Asia much of the original forest has been converted to monospecific plantations, but that potentially endangered species are few and tree flora remains widespread and stable.
Scientific understanding of the process of extinction is insufficient to accurately make predictions about the impact of deforestation on biodiversity. Most predictions of forestry related biodiversity loss are based on species-area models, with an underlying assumption that as the forest declines species diversity will decline similarly. However, many such models have been proven to be wrong and loss of habitat does not necessarily lead to large scale loss of species. Species-area models are known to overpredict the number of species known to be threatened in areas where actual deforestation is ongoing, and greatly overpredict the number of threatened species that are widespread.
A recent study of the Brazilian Amazon predicts that despite a lack of extinctions thus far, up to 90 percent of predicted extinctions will finally occur in the next 40 years.
Damage to forests and other aspects of nature could halve living standards for the world's poor and reduce global GDP by about 7% by 2050, a report concluded at the Convention on Biological Diversity (CBD) meeting in Bonn in 2008. Historically, utilization of forest products, including timber and fuel wood, has played a key role in human societies, comparable to the roles of water and cultivable land. Today, developed countries continue to utilize timber for building houses, and wood pulp for paper. In developing countries, almost three billion people rely on wood for heating and cooking.
The forest products industry is a large part of the economy in both developed and developing countries. Short-term economic gains made by conversion of forest to agriculture, or over-exploitation of wood products, typically leads to a loss of long-term income and long-term biological productivity. West Africa, Madagascar, Southeast Asia and many other regions have experienced lower revenue because of declining timber harvests. Illegal logging causes billions of dollars of losses to national economies annually.
The new procedures to get amounts of wood are causing more harm to the economy and overpower the amount of money spent by people employed in logging. According to a study, "in most areas studied, the various ventures that prompted deforestation rarely generated more than US$5 for every ton of carbon they released and frequently returned far less than US$1". The price on the European market for an offset tied to a one-ton reduction in carbon is 23 euro (about US$35).
Rapidly growing economies also have an effect on deforestation. Most pressure will come from the world's developing countries, which have the fastest-growing populations and most rapid economic (industrial) growth. In 1995, economic growth in developing countries reached nearly 6%, compared with the 2% growth rate for developed countries. As our human population grows, new homes, communities, and expansions of cities will occur. Connecting all of the new expansions will be roads, a very important part in our daily life. Rural roads promote economic development but also facilitate deforestation. About 90% of the deforestation has occurred within 100 km of roads in most parts of the Amazon.
Forest transition theoryEdit
The forest area change may follow a pattern suggested by the forest transition (FT) theory, whereby at early stages in its development a country is characterized by high forest cover and low deforestation rates (HFLD countries).
Then deforestation rates accelerate (HFHD, high forest cover – high deforestation rate), and forest cover is reduced (LFHD, low forest cover – high deforestation rate), before the deforestation rate slows (LFLD, low forest cover – low deforestation rate), after which forest cover stabilizes and eventually starts recovering. FT is not a "law of nature", and the pattern is influenced by national context (for example, human population density, stage of development, structure of the economy), global economic forces, and government policies. A country may reach very low levels of forest cover before it stabilizes, or it might through good policies be able to “bridge” the forest transition.
FT depicts a broad trend, and an extrapolation of historical rates therefore tends to underestimate future BAU deforestation for counties at the early stages in the transition (HFLD), while it tends to overestimate BAU deforestation for countries at the later stages (LFHD and LFLD).
Countries with high forest cover can be expected to be at early stages of the FT. GDP per capita captures the stage in a country’s economic development, which is linked to the pattern of natural resource use, including forests. The choice of forest cover and GDP per capita also fits well with the two key scenarios in the FT:
(i) a forest scarcity path, where forest scarcity triggers forces (for example, higher prices of forest products) that lead to forest cover stabilization; and
(ii) an economic development path, where new and better off-farm employment opportunities associated with economic growth (= increasing GDP per capita) reduce the profitability of frontier agriculture and slows deforestation.
The Carboniferous Rainforest Collapse was an event that occurred 300 million years ago. Climate change devastated tropical rainforests causing the extinction of many plant and animal species. The change was abrupt, specifically, at this time climate became cooler and drier, conditions that are not favorable to the growth of rainforests and much of the biodiversity within them. Rainforests were fragmented forming shrinking 'islands' further and further apart. Populations such as the sub class Lissamphibia were devastated, whereas Reptilia survived the collapse. The surviving organisms were better adapted to the drier environment left behind and served as legacies in succession after the collapse.
Rainforests once covered 14% of the earth's land surface; now they cover a mere 6% and experts estimate that the last remaining rainforests could be consumed in less than 40 years. Small scale deforestation was practiced by some societies for tens of thousands of years before the beginnings of civilization. The first evidence of deforestation appears in the Mesolithic period. It was probably used to convert closed forests into more open ecosystems favourable to game animals. With the advent of agriculture, larger areas began to be deforested, and fire became the prime tool to clear land for crops. In Europe there is little solid evidence before 7000 BC. Mesolithic foragers used fire to create openings for red deer and wild boar. In Great Britain, shade-tolerant species such as oak and ash are replaced in the pollen record by hazels, brambles, grasses and nettles. Removal of the forests led to decreased transpiration, resulting in the formation of upland peat bogs. Widespread decrease in elm pollen across Europe between 8400–8300 BC and 7200–7000 BC, starting in southern Europe and gradually moving north to Great Britain, may represent land clearing by fire at the onset of Neolithic agriculture.
The Neolithic period saw extensive deforestation for farming land. Stone axes were being made from about 3000 BC not just from flint, but from a wide variety of hard rocks from across Britain and North America as well. They include the noted Langdale axe industry in the English Lake District, quarries developed at Penmaenmawr in North Wales and numerous other locations. Rough-outs were made locally near the quarries, and some were polished locally to give a fine finish. This step not only increased the mechanical strength of the axe, but also made penetration of wood easier. Flint was still used from sources such as Grimes Graves but from many other mines across Europe.
Throughout prehistory, humans were hunter gatherers who hunted within forests. In most areas, such as the Amazon, the tropics, Central America, and the Caribbean, only after shortages of wood and other forest products occur are policies implemented to ensure forest resources are used in a sustainable manner.
Three regional studies of historic erosion and alluviation in ancient Greece found that, wherever adequate evidence exists, a major phase of erosion follows the introduction of farming in the various regions of Greece by about 500-1,000 years, ranging from the later Neolithic to the Early Bronze Age. The thousand years following the mid-first millennium BC saw serious, intermittent pulses of soil erosion in numerous places. The historic silting of ports along the southern coasts of Asia Minor (e.g. Clarus, and the examples of Ephesus, Priene and Miletus, where harbors had to be abandoned because of the silt deposited by the Meander) and in coastal Syria during the last centuries BC.
Easter Island has suffered from heavy soil erosion in recent centuries, aggravated by agriculture and deforestation. Jared Diamond gives an extensive look into the collapse of the ancient Easter Islanders in his book Collapse. The disappearance of the island's trees seems to coincide with a decline of its civilization around the 17th and 18th century. He attributed the collapse to deforestation and over-exploitation of all resources.
The famous silting up of the harbor for Bruges, which moved port commerce to Antwerp, also followed a period of increased settlement growth (and apparently of deforestation) in the upper river basins. In early medieval Riez in upper Provence, alluvial silt from two small rivers raised the riverbeds and widened the floodplain, which slowly buried the Roman settlement in alluvium and gradually moved new construction to higher ground; concurrently the headwater valleys above Riez were being opened to pasturage.
A typical progress trap was that cities were often built in a forested area, which would provide wood for some industry (for example, construction, shipbuilding, pottery). When deforestation occurs without proper replanting, however; local wood supplies become difficult to obtain near enough to remain competitive, leading to the city's abandonment, as happened repeatedly in Ancient Asia Minor. Because of fuel needs, mining and metallurgy often led to deforestation and city abandonment.
With most of the population remaining active in (or indirectly dependent on) the agricultural sector, the main pressure in most areas remained land clearing for crop and cattle farming. Enough wild green was usually left standing (and partially used, for example, to collect firewood, timber and fruits, or to graze pigs) for wildlife to remain viable. The elite's (nobility and higher clergy) protection of their own hunting privileges and game often protected significant woodland.
Major parts in the spread (and thus more durable growth) of the population were played by monastical 'pioneering' (especially by the Benedictine and Commercial orders) and some feudal lords' recruiting farmers to settle (and become tax payers) by offering relatively good legal and fiscal conditions. Even when speculators sought to encourage towns, settlers needed an agricultural belt around or sometimes within defensive walls. When populations were quickly decreased by causes such as the Black Death or devastating warfare (for example, Genghis Khan's Mongol hordes in eastern and central Europe, Thirty Years' War in Germany), this could lead to settlements being abandoned. The land was reclaimed by nature, but the secondary forests usually lacked the original biodiversity.
From 1100 to 1500 AD, significant deforestation took place in Western Europe as a result of the expanding human population. The large-scale building of wooden sailing ships by European (coastal) naval owners since the 15th century for exploration, colonisation, slave trade–and other trade on the high seas consumed many forest resources. Piracy also contributed to the over harvesting of forests, as in Spain. This led to a weakening of the domestic economy after Columbus' discovery of America, as the economy became dependent on colonial activities (plundering, mining, cattle, plantations, trade, etc.)
In Changes In the Land (1983), William Cronon analyzed and documented 17th-century English colonists' reports of increased seasonal flooding in New England during the period when new settlers initially cleared the forests for agriculture. They believed flooding was linked to widespread forest clearing upstream.
The massive use of charcoal on an industrial scale in Early Modern Europe was a new type of consumption of western forests; even in Stuart England, the relatively primitive production of charcoal has already reached an impressive level. Stuart England was so widely deforested that it depended on the Baltic trade for ship timbers, and looked to the untapped forests of New England to supply the need. Each of Nelson's Royal Navy war ships at Trafalgar (1805) required 6,000 mature oaks for its construction. In France, Colbert planted oak forests to supply the French navy in the future. When the oak plantations matured in the mid-19th century, the masts were no longer required because shipping had changed.
Europeans had lived in the midst of vast forests throughout the earlier medieval centuries. After 1250 they became so skilled at deforestation that by 1500 they were running short of wood for heating and cooking. They were faced with a nutritional decline because of the elimination of the generous supply of wild game that had inhabited the now-disappearing forests, which throughout medieval times had provided the staple of their carnivorous high-protein diet. By 1500 Europe was on the edge of a fuel and nutritional disaster [from] which it was saved in the sixteenth century only by the burning of soft coal and the cultivation of potatoes and maize.
In the 19th century, introduction of steamboats in the United States was the cause of deforestation of banks of major rivers, such as the Mississippi River, with increased and more severe flooding one of the environmental results. The steamboat crews cut wood every day from the riverbanks to fuel the steam engines. Between St. Louis and the confluence with the Ohio River to the south, the Mississippi became more wide and shallow, and changed its channel laterally. Attempts to improve navigation by the use of snag pullers often resulted in crews' clearing large trees 100 to 200 feet (61 m) back from the banks. Several French colonial towns of the Illinois Country, such as Kaskaskia, Cahokia and St. Philippe, Illinois, were flooded and abandoned in the late 19th century, with a loss to the cultural record of their archeology.
The wholescale clearance of woodland to create agricultural land can be seen in many parts of the world, such as the Central forest-grasslands transition and other areas of the Great Plains of the United States. Specific parallels are seen in the 20th-century deforestation occurring in many developing nations.
Rates of deforestationEdit
Global deforestation sharply accelerated around 1852. It has been estimated that about half of the Earth's mature tropical forests—between 7.5 million and 8 million km2 (2.9 million to 3 million sq mi) of the original 15 million to 16 million km2 (5.8 million to 6.2 million sq mi) that until 1947 covered the planet—have now been destroyed. Some scientists have predicted that unless significant measures (such as seeking out and protecting old growth forests that have not been disturbed) are taken on a worldwide basis, by 2030 there will only be 10% remaining, with another 10% in a degraded condition. 80% will have been lost, and with them hundreds of thousands of irreplaceable species. Some cartographers have attempted to illustrate the sheer scale of deforestation by country using a cartogram.
Estimates vary widely as to the extent of tropical deforestation. Over a 50-year period, percentage of land cover by tropical rainforests has decreased by 50%. Where total land coverage by tropical rainforests decreased from 14% to 6%. A large contribution to this loss can be identified between 1960 and 1990, when 20% of all tropical rainforests were destroyed. At this rate, extinction of such forests is projected to occur by the mid 21st century.
A 2002 analysis of satellite imagery suggested that the rate of deforestation in the humid tropics (approximately 5.8 million hectares per year) was roughly 23% lower than the most commonly quoted rates. Conversely, a newer analysis of satellite images reveals that deforestation of the Amazon rainforest is twice as fast as scientists previously estimated.
Some have argued that deforestation trends may follow a Kuznets curve, which if true would nonetheless fail to eliminate the risk of irreversible loss of non-economic forest values (for example, the extinction of species).
A 2005 report by the United Nations Food and Agriculture Organization (FAO) estimated that although the Earth's total forest area continued to decrease at about 13 million hectares per year, the global rate of deforestation has recently been slowing. The 2016 report by the FAO reports from 2010 to 2015 there was a worldwide decrease in forest area of 3.3 million ha per year. During this five-year period, the biggest forest area loss occurred in the tropics, particularly in South America and Africa. Per capita forest area decline was also greatest in the tropics and subtropics but is occurring in every climatic domain (except in the temperate) as populations increase.
Others claim that rainforests are being destroyed at an ever-quickening pace. The London-based Rainforest Foundation notes that "the UN figure is based on a definition of forest as being an area with as little as 10% actual tree cover, which would therefore include areas that are actually savannah-like ecosystems and badly damaged forests". Other critics of the FAO data point out that they do not distinguish between forest types, and that they are based largely on reporting from forestry departments of individual countries, which do not take into account unofficial activities like illegal logging.
Despite these uncertainties, there is agreement that destruction of rainforests remains a significant environmental problem. Up to 90% of West Africa's coastal rainforests have disappeared since 1900. In South Asia, about 88% of the rainforests have been lost. Much of what remains of the world's rainforests is in the Amazon basin, where the Amazon Rainforest covers approximately 4 million square kilometres. The regions with the highest tropical deforestation rate between 2000 and 2005 were Central America—which lost 1.3% of its forests each year—and tropical Asia. In Central America, two-thirds of lowland tropical forests have been turned into pasture since 1950 and 40% of all the rainforests have been lost in the last 40 years. Brazil has lost 90–95% of its Mata Atlântica forest.Paraguay was losing its natural semi humid forests in the country’s western regions at a rate of 15.000 hectares at a randomly studied 2-month period in 2010, Paraguay’s parliament refused in 2009 to pass a law that would have stopped cutting of natural forests altogether.
Madagascar has lost 90% of its eastern rainforests. As of 2007, less than 50% of Haiti's forests remained. Mexico, India, the Philippines, Indonesia, Thailand, Burma, Malaysia, Bangladesh, China, Sri Lanka, Laos, Nigeria, the Democratic Republic of the Congo, Liberia, Guinea, Ghana and the Ivory Coast, have lost large areas of their rainforest. Several countries, notably Brazil, have declared their deforestation a national emergency. The World Wildlife Fund's ecoregion project catalogues habitat types throughout the world, including habitat loss such as deforestation, showing for example that even in the rich forests of parts of Canada such as the Mid-Continental Canadian forests of the prairie provinces half of the forest cover has been lost or altered.
Rates of deforestation vary around the world.
In 2011 Conservation International listed the top 10 most endangered forests, characterized by having all lost 90% or more of their original habitat, and each harboring at least 1500 endemic plant species (species found nowhere else in the world).
Top 10 Most Endangered Forests 2011 Endangered forest Region Remaining habitat Predominate vegetation type Notes Indo-Burma Asia-Pacific 5% Tropical and subtropical moist broadleaf forests Rivers, floodplain wetlands, mangrove forests. Burma, Thailand, Laos, Vietnam, Cambodia, India. New Caledonia Asia-Pacific 5% Tropical and subtropical moist broadleaf forests See note for region covered. Sundaland Asia-Pacific 7% Tropical and subtropical moist broadleaf forests Western half of the Indo-Malayan archipelago including southern Borneo and Sumatra. Philippines Asia-Pacific 7% Tropical and subtropical moist broadleaf forests Forests over the entire country including 7,100 islands. Atlantic Forest South America 8% Tropical and subtropical moist broadleaf forests Forests along Brazil's Atlantic coast, extends to parts of Paraguay, Argentina and Uruguay. Mountains of Southwest China Asia-Pacific 8% Temperate coniferous forest See note for region covered. California Floristic Province North America 10% Tropical and subtropical dry broadleaf forests See note for region covered. Coastal Forests of Eastern Africa Africa 10% Tropical and subtropical moist broadleaf forests Mozambique, Tanzania, Kenya, Somalia. Madagascar & Indian Ocean Islands Africa 10% Tropical and subtropical moist broadleaf forests Madagascar, Mauritius, Reunion, Seychelles, Comoros. Eastern Afromontane Africa 11% Tropical and subtropical moist broadleaf forests
Montane grasslands and shrublands
Forests scattered along the eastern edge of Africa, from Saudi Arabia in the north to Zimbabwe in the south.
- Table source:
Main international organizations including the United Nations and the World Bank, have begun to develop programs aimed at curbing deforestation. The blanket term Reducing Emissions from Deforestation and Forest Degradation (REDD) describes these sorts of programs, which use direct monetary or other incentives to encourage developing countries to limit and/or roll back deforestation. Funding has been an issue, but at the UN Framework Convention on Climate Change (UNFCCC) Conference of the Parties-15 (COP-15) in Copenhagen in December 2009, an accord was reached with a collective commitment by developed countries for new and additional resources, including forestry and investments through international institutions, that will approach USD 30 billion for the period 2010–2012. Significant work is underway on tools for use in monitoring developing country adherence to their agreed REDD targets. These tools, which rely on remote forest monitoring using satellite imagery and other data sources, include the Center for Global Development's FORMA (Forest Monitoring for Action) initiative and the Group on Earth Observations' Forest Carbon Tracking Portal. Methodological guidance for forest monitoring was also emphasized at COP-15. The environmental organization Avoided Deforestation Partners leads the campaign for development of REDD through funding from the U.S. government. In 2014, the Food and Agriculture Organization of the United Nations and partners launched Open Foris – a set of open-source software tools that assist countries in gathering, producing and disseminating information on the state of forest resources. The tools support the inventory lifecycle, from needs assessment, design, planning, field data collection and management, estimation analysis, and dissemination. Remote sensing image processing tools are included, as well as tools for international reporting for Reducing emissions from deforestation and forest degradation (REDD) and MRV (Measurement, Reporting and Verification) and FAO's Global Forest Resource Assessments.
In evaluating implications of overall emissions reductions, countries of greatest concern are those categorized as High Forest Cover with High Rates of Deforestation (HFHD) and Low Forest Cover with High Rates of Deforestation (LFHD). Afghanistan, Benin, Botswana, Burma, Burundi, Cameroon, Chad, Ecuador, El Salvador, Ethiopia, Ghana, Guatemala, Guinea, Haiti, Honduras, Indonesia, Liberia, Malawi, Mali, Mauritania, Mongolia, Namibia, Nepal, Nicaragua, Niger, Nigeria, Pakistan, Paraguay, Philippines, Senegal, Sierra Leone, Sri Lanka, Sudan, Togo, Uganda, United Republic of Tanzania, Zimbabwe are listed as having Low Forest Cover with High Rates of Deforestation (LFHD). Brazil, Cambodia, Democratic People's Republic of Korea, Equatorial Guinea, Malaysia, Solomon Islands, Timor-Leste, Venezuela, Zambia are listed as High Forest Cover with High Rates of Deforestation (HFHD).
Control can be made by the companies. In 2018 the biggest palm oil traider, Wilmar, decided to control his suppliers for avoid deforestation. This is an important precedent
Payments for conserving forestsEdit
In Bolivia, deforestation in upper river basins has caused environmental problems, including soil erosion and declining water quality. An innovative project to try and remedy this situation involves landholders in upstream areas being paid by downstream water users to conserve forests. The landholders receive US$20 to conserve the trees, avoid polluting livestock practices, and enhance the biodiversity and forest carbon on their land. They also receive US$30, which purchases a beehive, to compensate for conservation for two hectares of water-sustaining forest for five years. Honey revenue per hectare of forest is US$5 per year, so within five years, the landholder has sold US$50 of honey. The project is being conducted by Fundación Natura Bolivia and Rare Conservation, with support from the Climate & Development Knowledge Network.
Transferring rights over land from public domain to its indigenous inhabitants is argued to be a cost effective strategy to conserve forests. This includes the protection of such rights entitled in existing laws, such as India’s Forest Rights Act. The transferring of such rights in China, perhaps the largest land reform in modern times, has been argued to have increased forest cover. In Brazil, forested areas given tenure to indigenous groups have even lower rates of clearing than national parks.
New methods are being developed to farm more intensively, such as high-yield hybrid crops, greenhouse, autonomous building gardens, and hydroponics. These methods are often dependent on chemical inputs to maintain necessary yields. In cyclic agriculture, cattle are grazed on farm land that is resting and rejuvenating. Cyclic agriculture actually increases the fertility of the soil. Intensive farming can also decrease soil nutrients by consuming at an accelerated rate the trace minerals needed for crop growth. The most promising approach, however, is the concept of food forests in permaculture, which consists of agroforestal systems carefully designed to mimic natural forests, with an emphasis on plant and animal species of interest for food, timber and other uses. These systems have low dependence on fossil fuels and agro-chemicals, are highly self-maintaining, highly productive, and with strong positive impact on soil and water quality, and biodiversity.
There are multiple methods that are appropriate and reliable for reducing and monitoring deforestation. One method is the “visual interpretation of aerial photos or satellite imagery that is labor-intensive but does not require high-level training in computer image processing or extensive computational resources”. Another method includes hot-spot analysis (that is, locations of rapid change) using expert opinion or coarse resolution satellite data to identify locations for detailed digital analysis with high resolution satellite images. Deforestation is typically assessed by quantifying the amount of area deforested, measured at the present time. From an environmental point of view, quantifying the damage and its possible consequences is a more important task, while conservation efforts are more focused on forested land protection and development of land-use alternatives to avoid continued deforestation. Deforestation rate and total area deforested, have been widely used for monitoring deforestation in many regions, including the Brazilian Amazon deforestation monitoring by INPE. A global satellite view is available.
Efforts to stop or slow deforestation have been attempted for many centuries because it has long been known that deforestation can cause environmental damage sufficient in some cases to cause societies to collapse. In Tonga, paramount rulers developed policies designed to prevent conflicts between short-term gains from converting forest to farmland and long-term problems forest loss would cause, while during the 17th and 18th centuries in Tokugawa, Japan, the shōguns developed a highly sophisticated system of long-term planning to stop and even reverse deforestation of the preceding centuries through substituting timber by other products and more efficient use of land that had been farmed for many centuries. In 16th-century Germany, landowners also developed silviculture to deal with the problem of deforestation. However, these policies tend to be limited to environments with good rainfall, no dry season and very young soils (through volcanism or glaciation). This is because on older and less fertile soils trees grow too slowly for silviculture to be economic, whilst in areas with a strong dry season there is always a risk of forest fires destroying a tree crop before it matures.
In the areas where "slash-and-burn" is practiced, switching to "slash-and-char" would prevent the rapid deforestation and subsequent degradation of soils. The biochar thus created, given back to the soil, is not only a durable carbon sequestration method, but it also is an extremely beneficial amendment to the soil. Mixed with biomass it brings the creation of terra preta, one of the richest soils on the planet and the only one known to regenerate itself.
Certification, as provided by global certification systems such as Programme for the Endorsement of Forest Certification and Forest Stewardship Council, contributes to tackling deforestation by creating market demand for timber from sustainably managed forests. According to the United Nations Food and Agriculture Organization (FAO), "A major condition for the adoption of sustainable forest management is a demand for products that are produced sustainably and consumer willingness to pay for the higher costs entailed. Certification represents a shift from regulatory approaches to market incentives to promote sustainable forest management. By promoting the positive attributes of forest products from sustainably managed forests, certification focuses on the demand side of environmental conservation." Rainforest Rescue argues that the standards of organizations like FSC are too closely connected to timber industry interests and therefore do not guarantee environmentally and socially responsible forest management. In reality, monitoring systems are inadequate and various cases of fraud have been documented worldwide.
Some nations have taken steps to help increase the number of trees on Earth. In 1981, China created National Tree Planting Day Forest and forest coverage had now reached 16.55% of China's land mass, as against only 12% two decades ago.
In many parts of the world, especially in East Asian countries, reforestation and afforestation are increasing the area of forested lands. The amount of woodland has increased in 22 of the world's 50 most forested nations. Asia as a whole gained 1 million hectares of forest between 2000 and 2005. Tropical forest in El Salvador expanded more than 20% between 1992 and 2001. Based on these trends, one study projects that global forest will increase by 10%—an area the size of India—by 2050.
In the People's Republic of China, where large scale destruction of forests has occurred, the government has in the past required that every able-bodied citizen between the ages of 11 and 60 plant three to five trees per year or do the equivalent amount of work in other forest services. The government claims that at least 1 billion trees have been planted in China every year since 1982. This is no longer required today, but 12 March of every year in China is the Planting Holiday. Also, it has introduced the Green Wall of China project, which aims to halt the expansion of the Gobi desert through the planting of trees. However, due to the large percentage of trees dying off after planting (up to 75%), the project is not very successful. There has been a 47-million-hectare increase in forest area in China since the 1970s. The total number of trees amounted to be about 35 billion and 4.55% of China's land mass increased in forest coverage. The forest coverage was 12% two decades ago and now is 16.55%.
An ambitious proposal for China is the Aerially Delivered Re-forestation and Erosion Control System and the proposed Sahara Forest Project coupled with the Seawater Greenhouse.
In Western countries, increasing consumer demand for wood products that have been produced and harvested in a sustainable manner is causing forest landowners and forest industries to become increasingly accountable for their forest management and timber harvesting practices.
The Arbor Day Foundation's Rain Forest Rescue program is a charity that helps to prevent deforestation. The charity uses donated money to buy up and preserve rainforest land before the lumber companies can buy it. The Arbor Day Foundation then protects the land from deforestation. This also locks in the way of life of the primitive tribes living on the forest land. Organizations such as Community Forestry International, Cool Earth, The Nature Conservancy, World Wide Fund for Nature, Conservation International, African Conservation Foundation and Greenpeace also focus on preserving forest habitats. Greenpeace in particular has also mapped out the forests that are still intact and published this information on the internet. World Resources Institute in turn has made a simpler thematic map showing the amount of forests present just before the age of man (8000 years ago) and the current (reduced) levels of forest. These maps mark the amount of afforestation required to repair the damage caused by people.
In order to acquire the world’s demand for wood, it is suggested that high yielding forest plantations are suitable according to forest writers Botkins and Sedjo. Plantations that yield 10 cubic meters per hectare a year would supply enough wood for trading of 5% of the world’s existing forestland. By contrast, natural forests produce about 1–2 cubic meters per hectare; therefore, 5–10 times more forestland would be required to meet demand. Forester Chad Oliver has suggested a forest mosaic with high-yield forest lands interspersed with conservation land.
Globally, planted forests increased from 4.1% to 7.0% of the total forest area between 1990 and 2015. Plantation forests made up 280 million ha in 2015, an increase of about 40 million ha in the last ten years. Globally, planted forests consist of about 18% exotic or introduced species while the rest are species native to the country where they are planted. In South America, Oceania, and East and Southern Africa, planted forests are dominated by introduced species: 88%, 75% and 65%, respectively. In North America, West and Central Asia, and Europe the proportions of introduced species in plantations are much lower at 1%, 3% and 8% of the total area planted, respectively.
In the country of Senegal, on the western coast of Africa, a movement headed by youths has helped to plant over 6 million mangrove trees. The trees will protect local villages from storm damages and will provide a habitat for local wildlife. The project started in 2008, and already the Senegalese government has been asked to establish rules and regulations that would protect the new mangrove forests.
While demands for agricultural and urban use for the human population cause the preponderance of deforestation, military causes can also intrude. One example of deliberate deforestation played out in the U.S. zone of occupation in Germany after World War II ended in 1945. Before the onset of the Cold War, defeated Germany was still considered a potential future threat rather than a potential future ally. To address this threat, the victorious Allies made attempts to lower German industrial potential, of which forests were deemed[by whom?] an element. Sources in the U.S. government admitted that the purpose of this was that the "ultimate destruction of the war potential of German forests". As a consequence of the practice of clear-felling, deforestation resulted which could "be replaced only by long forestry development over perhaps a century".
Operations in war can also cause deforestation. For example, in the 1945 Battle of Okinawa, bombardment and other combat operations reduced a lush tropical landscape into "a vast field of mud, lead, decay and maggots".
Deforestation can also result from the intentional tactics of military forces. Clearing forest became an element in the Russian Empire's successful conquest of the Caucasus in the mid-19th century. The British (during the Malayan Emergency) and the United States (in the Korean War and in the Vietnam War) used defoliants (like Agent Orange or others).[need quotation to verify]
Public health contextEdit
Deforestation eliminates a great number of species of plants and animals which also often results in an increase in disease. Loss of native species allows new species to come to dominance. Often the destruction of predatory species can result in an increase in rodent populations which can carry plague. Additionally, erosion can produce pools of stagnant water that are perfect breeding grounds for mosquitos, well known vectors of malaria, yellow fever, nipah virus, and more. Deforestation can also create a path for non-native species to flourish such as certain types of snails, which have been correlated with an increase in schistosomiasis cases.
Deforestation is occurring all over the world and has been coupled with an increase in the occurrence of disease outbreaks. In Malaysia, thousands of acres of forest have been cleared for pig farms. This has resulted in an increase in the zoonosis the Nipah virus. In Kenya, deforestation has led to an increase in malaria cases which is now the leading cause of morbidity and mortality the country. A 2017 study in the American Economic Review found that deforestation substantially increased the incidence of malaria in Nigeria.
Another pathway through which deforestation affects disease is the relocation and dispersion of disease-carrying hosts. This disease emergence pathway can be called "range expansion", whereby the host’s range (and thereby the range of pathogens) expands to new geographic areas. Through deforestation, hosts and reservoir species are forced into neighboring habitats. Accompanying the reservoir species are pathogens that have the ability to find new hosts in previously unexposed regions. As these pathogens and species come into closer contact with humans, they are infected both directly and indirectly.
A catastrophic example of range expansion is the 1998 outbreak of Nipah virus in Malaysia. For a number of years, deforestation, drought, and subsequent fires led to a dramatic geographic shift and density of fruit bats, a reservoir for Nipah virus. Deforestation reduced the available fruiting trees in the bats’ habitat, and they encroached on surrounding orchards which also happened to be the location of a large number of pigsties. The bats, through proximity spread the Nipah to pigs. While the virus infected the pigs, mortality was much lower than among humans, making the pigs a virulent host leading to the transmission of the virus to humans. This resulted in 265 reported cases of encephalitis, of which 105 resulted in death. This example provides an important lesson for the impact deforestation can have on human health.
Another example of range expansion due to deforestation and other anthropogenic habitat impacts includes the Capybara rodent in Paraguay. This rodent is the host of a number of zoonotic diseases and, while there has not yet been a human-borne outbreak due to the movement of this rodent into new regions, it offers an example of how habitat destruction through deforestation and subsequent movements of species is occurring regularly.
A now well-developed theory is that the spread of HIV it is at least partially due deforestation. Rising populations created a food demand and with deforestation opening up new areas of the forest the hunters harvested a great deal of primate bushmeat, which is believed to be the origin of HIV.
- Deforestation and desertification portal
- Agricultural expansion
- Deforestation and climate change
- Deforestation by region
- Deforestation during the Roman period
- Economic impact analysis
- Environmental issues with paper
- Environmental philosophy
- CDM & JI A/R projects
- Illegal logging
- Intact forest landscape
- International Year of Forests
- Land degradation
- Land use, land-use change and forestry
- Moisture recycling
- Mountaintop removal
- Natural landscape
- Richard St. Barbe Baker
- Terra preta
- World Forestry Congress
- "Un dizième des terres sauvages ont disparu en deux décennies" (Radio Télévision Suisse) citing Watson, James E.M.; Shanahan, Danielle F.; Di Marco, Moreno; Allan, James; Laurance, William F.; Sanderson, Eric W.; MacKey, Brendan; Venter, Oscar (2016). "Catastrophic Declines in Wilderness Areas Undermine Global Environment Targets". Current Biology. 26 (21): 2929–2934. doi:10.1016/j.cub.2016.08.049. PMID 27618267.
- SAFnet Dictionary|Definition For [deforestation] Archived 25 July 2011 at the Wayback Machine. Dictionary of forestry.org (29 July 2008). Retrieved 2011-05-15.
- Bradford, Alina. (4 March 2015) Deforestation: Facts, Causes & Effects. Livescience.com. Retrieved 2016-11-13.
- Deforestation | Threats | WWF. Worldwildlife.org. Retrieved 13 November 2016.
- Kauppi, P. E.; Ausubel, J. H.; Fang, J.; Mather, A. S.; Sedjo, R. A.; Waggoner, P. E. (2006). "Returning forests analyzed with the forest identity". Proceedings of the National Academy of Sciences. 103 (46): 17574–9. Bibcode:2006PNAS..10317574K. doi:10.1073/pnas.0608343103. PMC 1635979. PMID 17101996.
- "Use Energy, Get Rich and Save the Planet", The New York Times, 20 April 2009.
- Henkel, Marlon. 21st Century Homestead: Sustainable Agriculture III: Agricultural Practices. Lulu.com. ISBN 9781312939752.
- 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.
- Rainforest Facts Archived 22 October 2015 at the Wayback Machine. Nature.org (1 November 2016). Retrieved 2016-11-13.
- "Facts About Rainforests" Archived 22 October 2015 at the Wayback Machine. The Nature Conservancy. Retrieved 19 October 2015.
- "Amazon Destruction". Mongabay. Retrieved 13 December 2017.
- UNFCCC (2007). "Investment and financial flows to address climate change" (PDF). unfccc.int. UNFCCC. p. 81.
- Angelsen, Arild; Kaimowitz, David (February 1999). "Rethinking the causes of deforestation: Lessons from economic models". The World Bank Research Observer. Oxford University Press. 14 (1): 73–98. doi:10.1093/wbro/14.1.73. JSTOR 3986539. PMID 12322119.
- Laurance, William F. (December 1999). "Reflections on the tropical deforestation crisis" (PDF). Biological Conservation. 91 (2–3): 109–117. doi:10.1016/S0006-3207(99)00088-9. Archived from the original (PDF) on 2006-09-08.
- Geist, Helmut J.; Lambin, Eric F. (February 2002). "Proximate Causes and Underlying Driving Forces of Tropical Deforestation" (PDF). BioScience. 52 (2): 143–150. doi:10.1641/0006-3568(2002)052[0143:PCAUDF]2.0.CO;2. Archived from the original (PDF) on 26 July 2011. Retrieved 17 May 2009.
- Burgonio, T.J. (3 January 2008). "Corruption blamed for deforestation". Philippine Daily Inquirer.[permanent dead link]
- "WRM Bulletin Number 74". World Rainforest Movement. September 2003. Archived from the original on 4 October 2008. Retrieved 17 October 2008.
- "Global Deforestation". Global Change Curriculum. University of Michigan Global Change Program. 4 January 2006. Archived from the original on 15 June 2011.
- Marcoux, Alain (August 2000). "Population and deforestation". SD Dimensions. Sustainable Development Department, Food and Agriculture Organization of the United Nations (FAO). Archived from the original on 28 June 2011.
- Butler, Rhett A. "Impact of Population and Poverty on Rainforests". Mongabay.com / A Place Out of Time: Tropical Rainforests and the Perils They Face. Retrieved 13 May 2009.
- Stock, Jocelyn; Rochen, Andy. "The Choice: Doomsday or Arbor Day". umich.edu. Archived from the original on 16 April 2009.
- Ehrhardt-Martinez, Karen. "Demographics, Democracy, Development, Disparity and Deforestation: A Crossnational Assessment of the Social Causes of Deforestation". Paper presented at the annual meeting of the American Sociological Association, Atlanta Hilton Hotel, Atlanta, GA, 16 August 2003. Archived from the original on 10 December 2008. Retrieved 13 May 2009.
- "The Double Edge of Globalization". YaleGlobal Online. Yale University Press. June 2007.
- Butler, Rhett A. "Human Threats to Rainforests—Economic Restructuring". Mongabay.com / A Place Out of Time: Tropical Rainforests and the Perils They Face. Retrieved 13 May 2009.
- Hecht, Susanna B.; Kandel, Susan; Gomes, Ileana; Cuellar, Nelson; Rosa, Herman (2006). "Globalization, Forest Resurgence, and Environmental Politics in El Salvador" (PDF). World Development. 34 (2): 308–323. doi:10.1016/j.worlddev.2005.09.005. Archived from the original (PDF) on 29 October 2008. Retrieved 17 October 2008.
- Pearce, David W (December 2001). "The Economic Value of Forest Ecosystems" (PDF). Ecosystem Health. 7 (4): 284–296. doi:10.1046/j.1526-0992.2001.01037.x.
- Bulte, Erwin H; Joenje, Mark; Jansen, Hans GP (2000). "Is there too much or too little natural forest in the Atlantic Zone of Costa Rica?". Canadian Journal of Forest Research. 30 (3): 495–506. doi:10.1139/x99-225.
- Butler, Rhett A.; Laurance, William F. (August 2008). "New strategies for conserving tropical forests" (PDF). Trends in Ecology & Evolution. 23 (9): 469–472. doi:10.1016/j.tree.2008.05.006.
- Rudel, T.K. (2005) Tropical Forests: Regional Paths of Destruction and Regeneration in the Late 20th Century. Columbia University Press ISBN 0-231-13195-X
- Curtis, P. G.; Slay, C. M.; Harris, N. L.; Tyukavina, A.; Hansen, M. C. (2018). "Classifying drivers of global forest loss". Science. 361 (6407): 1108–1111. doi:10.1126/science.aau3445.
- "NASA DATA SHOWS DEFORESTATION AFFECTS CLIMATE". Nasa. 9 June 2004.
- Mweninguwe, Raphael (15 February 2005). "Massive deforestation threatens food security". newsfromafrica.org. Archived from the original on 18 July 2011.
- Confirmed: Deforestation Plays Critical Climate Change Role, ScienceDaily, 11 May 2007.
- Clearing Forests May Transform Local—and Global—Climate; Researchers are finding that massive deforestation may have a profound, and possibly catastrophic, impact on local weather Archived 13 April 2013 at the Wayback Machine. Scientific American (4 March 2013)
- Deforestation causes global warming, FAO
- Fearnside, Philip M.; Laurance, William F. (2004). "Tropical Deforestation and Greenhouse-Gas Emissions". Ecological Applications. 14 (4): 982. doi:10.1890/03-5225.
- "Fondation Chirac ' Deforestation and desertification".
- IPCC Fourth Assessment Report, Working Group I Report "The Physical Science Basis", Section 22.214.171.124.5. p. 527
- Van Der Werf, G. R.; Morton, D. C.; Defries, R. S.; Olivier, J. G. J.; Kasibhatla, P. S.; Jackson, R. B.; Collatz, G. J.; Randerson, J. T. (2009). "CO2 emissions from forest loss". Nature Geoscience. 2 (11): 737–738. Bibcode:2009NatGe...2..737V. doi:10.1038/ngeo671.
- Mumoki, Fiona (18 July 2006). "The Effects of Deforestation on our Environment Today". Panorama. TakingITGlobal..
- Clemmensen, K. E.; Bahr, A.; Ovaskainen, O.; Dahlberg, A.; Ekblad, A.; Wallander, H.; Stenlid, J.; Finlay, R. D.; Wardle, D. A.; Lindahl, B. D. (2013). "Roots and Associated Fungi Drive Long-Term Carbon Sequestration in Boreal Forest". Science. 339 (6127): 1615–8. Bibcode:2013Sci...339.1615C. doi:10.1126/science.1231923. PMID 23539604.
- Prentice, I.C. "The Carbon Cycle and Atmospheric Carbon Dioxide". IPCC
- NASA Data Shows Deforestation Affects Climate In The Amazon. NASA News. 9 June 2004.
- Findell, Kirsten L.; Knutson, Thomas R.; Milly, P. C. D. (2006). "Weak Simulated Extratropical Responses to Complete Tropical Deforestation". Journal of Climate. 19 (12): 2835–2850. Bibcode:2006JCli...19.2835F. CiteSeerX 10.1.1.143.9090. doi:10.1175/JCLI3737.1.
- Chakravarty, Sumit; Ghosh, S. K.; Suresh, C. P.; Dey, A. N.; Shukla, Gopal. "Causes, Effects and Control Strategies, Global Perspectives on Sustainable Forest Management" (PDF). InTech. InTech. Retrieved 23 August 2017.
- Wertz-Kanounnikoff, Sheila; Rubio Alvarado; Laura Ximena. "Why are we seeing "REDD"?". Institute for Sustainable Development and International Relations. Archived from the original on 25 December 2007. Retrieved 14 November 2016.
- "How can you save the rain forest. 8 October 2006. Frank Field". The Times. London. 8 October 2006. Retrieved 1 April 2010.
- Broeker, Wallace S. (2006). "Breathing easy: Et tu, O2". Columbia University
- Moran, Emilio F. (1993). "Deforestation and land use in the Brazilian Amazon". Human Ecology. 21: 1–21. doi:10.1007/BF00890069.
- Defries, Ruth; Achard, Frédéric; Brown, Sandra; Herold, Martin; Murdiyarso, Daniel; Schlamadinger, Bernhard; De Souza, Carlos (2007). "Earth observations for estimating greenhouse gas emissions from deforestation in developing countries" (PDF). Environmental Science Policy. 10 (4): 385–394. doi:10.1016/j.envsci.2007.01.010. Archived from the original (PDF) on 18 January 2012.
- "Underlying Causes of Deforestation". UN Secretary-General’s Report. Archived from the original on 11 April 2001.
- Rogge, Daniel. "Deforestation and Landslides in Southwestern Washington". University of Wisconsin-Eau Claire.
- China's floods: Is deforestation to blame? BBC News. 6 August 1999.
- Raven, P. H. and Berg, L. R. (2006) Environment, 5th ed, John Wiley & Sons. p. 406. ISBN 0471704385.
- Hongchang, Wang (1 January 1998). "Deforestation and Desiccation in China A Preliminary Study". In Schwartz, Jonathan Matthew. The Economic Costs of China's Environmental Degradation: Project on Environmental Scarcities, State Capacity, and Civil Violence, a Joint Project of the University of Toronto and the American Academy of Arts and Sciences. Committee on Internat. Security Studies, American Acad. of Arts and Sciences. Archived from the original on 30 December 2009.
- Mishra, D.D. (2010). Fundamental Concept in Environmental Studies. S. Chand Publishing. pp. 14–15. ISBN 978-8121929370.
- "Soil, Water and Plant Characteristics Important to Irrigation". North Dakota State University.
- Morgan, R.P.C (2009). Soil Erosion and Conservation. John Wiley & Sons. p. 343. ISBN 9781405144674.
- Henkel, Marlon. 21st Century Homestead: Sustainable Agriculture III: Agricultural Practices. Lulu.com. p. 110. ISBN 9781312939752.
- Nilsson, Sten (March 2001). Do We Have Enough Forests?, American Institute of Biological Sciences.
- Rainforest Biodiversity Shows Differing Patterns, ScienceDaily, 14 August 2007.
- "Medicine from the rainforest". Research for Biodiversity Editorial Office. Archived from the original on 6 December 2008.
- Single-largest biodiversity survey says primary rainforest is irreplaceable, Bio-Medicine, 14 November 2007.
- Tropical rainforests – The tropical rainforest, BBC
- Tropical Rain Forest. thinkquest.org
- U.N. calls on Asian nations to end deforestation, Reuters, 20 June 2008.
- "Rainforest Facts".
- Tropical rainforests – Rainforest water and nutrient cycles Archived 13 February 2009 at the Wayback Machine, BBC
- Butler, Rhett A. (2 July 2007) Primary rainforest richer in species than plantations, secondary forests, mongabay.com,
- Flowers, April. "Deforestation In The Amazon Affects Microbial Life As Well As Ecosystems". Science News. Redorbit.com. Archived from the original on 2 May 2013. Retrieved 12 March 2013.
- Rainforest Facts. Rain-tree.com (20 March 2010). Retrieved 2010-08-29.
- Leakey, Richard and Roger Lewin, 1996, The Sixth Extinction : Patterns of Life and the Future of Humankind, Anchor, ISBN 0-385-46809-1.
- The great rainforest tragedy, The Independent, 28 June 2003.
- Biodiversity wipeout facing South East Asia, New Scientist, 23 July 2003.
- Pimm, S. L.; Russell, G. J.; Gittleman, J. L.; Brooks, T. M. (1995). "The Future of Biodiversity". Science. 269 (5222): 347–350. Bibcode:1995Sci...269..347P. doi:10.1126/science.269.5222.347. PMID 17841251.
- Pimm, S. L.; Russell, G. J.; Gittleman, J. L.; Brooks, T. M. (1995). "The future of biodiversity". Science. 269 (5222): 347–50. Bibcode:1995Sci...269..347P. doi:10.1126/science.269.5222.347. PMID 17841251.
- Whitmore, Timothy Charles; Sayer, Jeffrey; International Union for Conservation of Nature and Natural Resources. General Assembly; IUCN Forest Conservation Programme (15 February 1992). Tropical deforestation and species extinction. Springer. ISBN 978-0-412-45520-9. Retrieved 4 December 2011.
- Sohn, Emily (12 July 2012). "More extinctions expected in Amazon". Discovery.
- Nature loss 'to hurt global poor', BBC News, 29 May 2008.
- Forest Products. (PDF). Retrieved 4 December 2011.
- "Destruction of Renewable Resources". rainforests.mongabay.com.
- Deforestation Across the World's Tropical Forests Emits Large Amounts of Greenhouse Gases with Little Economic Benefits, According to a New Study at CGIAR.org Archived 9 June 2012 at the Wayback Machine, 4 December 2007.
- "New ASB Report finds deforestation offers very little money compared to potential financial benefits". asb.cgiar.org.
- Chomitz, Kenneth; Gray, David A. (1999). "Roads, lands, markets, and deforestation: a spatial model of land use in Belize". Policy Research Working Papers. doi:10.1596/1813-9450-1444.
- Ferraz, Silvio Frosini de Barros; Vettorazzi, Carlos Alberto; Theobald, David M. (2009). "Using indicators of deforestation and land-use dynamics to support conservation strategies: A case study of central Rondônia, Brazil". Forest Ecology and Management. 257 (7): 1586–1595. doi:10.1016/j.foreco.2009.01.013.
- "Stolen Goods: The EU's complicity in illegal tropical deforestation" (PDF). Forests and the European Union Resource Network. 17 March 2015. Archived from the original (PDF) on 2 April 2015. Retrieved 31 March 2015.
- "Reducing Emissions from Deforestation and Forest Degradation (REDD): An Options Assessment Report" (PDF). The Government of Norway. 28 March 2010. p. 16.
- Meyfroidt, Patrick; Lambin, Eric F. (2011). "Global Forest Transition: Prospects for an End to Deforestation". Annual Review of Environment and Resources. 36: 343. doi:10.1146/annurev-environ-090710-143732.
- Baofu, Peter (2014). Beyond Natural Resources to Post-Human Resources: Towards a New Theory of Diversity and Discontinuity. Cambridge Scholars Publishing. p. 309. ISBN 9781443867061.
- Taylor, Leslie (2004). The Healing Power of Rainforest Herbs: A Guide to Understanding and Using Herbal Medicinals. Square One. ISBN 9780757001444.
- Flannery, T (1994). The future eaters. Melbourne: Reed Books. ISBN 0-7301-0422-2.
- Brown, Tony (1997). "Clearances and Clearings: Deforestation in Mesolithic/Neolithic Britain". Oxford Journal of Archaeology. 16 (2): 133–146. doi:10.1111/1468-0092.00030.
- "hand tool: Neolithic tools". Encyclopædia Britannica Online.
- "Neolithic Age from 4,000 BC to 2,200 BC or New Stone Age".
- Hogan, C. Michael (22 December 2007). "Knossos fieldnotes", The Modern Antiquarian
- Diamond, Jared (2005) "The world as a polder: what does it all mean to us today?" pp. 522–523 in Collapse: How Societies Choose to Fail or Survive, Penguin Books. ISBN 978-0-241-95868-1.
- Encyclopćdia Britannica Online School Edition. School.eb.com. Retrieved 29 August 2010.
- Van Andel, Tjeerd H.; Zangger, Eberhard; Demitrack, Anne (2013). "Land Use and Soil Erosion in Prehistoric and Historical Greece" (PDF). Journal of Field Archaeology. 17 (4): 379–396. doi:10.1179/009346990791548628.
- "The Mystery of Easter Island", Smithsonian Magazine, 1 April 2007.
- "Historical Consequences of Deforestation: Easter Island (Diamond 1995)". mongabay.com.
- "Jared Diamond, Easter Island's End". hartford-hwp.com.
- Iyyer, Chaitanya (2009). Land Management: Challenges & Strategies. Global India Publications. p. 11. ISBN 9789380228488.
- Chew, Sing C. (2001). World Ecological Degradation. Oxford, England: AltaMira Press. pp. 69–70.
- Baofu, Peter (2014). Beyond Natural Resources to Post-Human Resources: Towards a New Theory of Diversity and Discontinuity. pg.309: Cambridge Scholars Publishing. p. 703. ISBN 9781443867061.
- Cantor, Norman F. (9 June 1994). The civilization of the Middle Ages: a completely revised and expanded edition of Medieval history, the life and death of a civilization. HarperCollins. p. 564. ISBN 978-0-06-092553-6. Retrieved 4 December 2011.
- Norris, F. Terry (1997) "Where Did the Villages Go? Steamboats, Deforestation, and Archaeological Loss in the Mississippi Valley", in Common Fields: an environmental history of St. Louis, Andrew Hurley, ed., St. Louis, MO: Missouri Historical Society Press, pp. 73–89. ISBN 978-1-883982-15-7.
- Duke Press policy studies / Global deforestation and the nineteenth-century world economy / edited by Richard P. Tucker and J. F. Richards
- E. O. Wilson, 2002, The Future of Life, Vintage ISBN 0-679-76811-4.
- Map reveals extent of deforestation in tropical countries, guardian.co.uk, 1 July 2008.
- Maycock, Paul F. Deforestation[permanent dead link]. WorldBookOnline.
- Ron Nielsen, The Little Green Handbook: Seven Trends Shaping the Future of Our Planet, Picador, New York (2006) ISBN 978-0-312-42581-4.
- Victor Vescovo. (2006). The Atlas of World Statistics. The Caladan Press. Retrieved 3 August 2012.
- Teja Tscharntke; Christoph Leuschner; Edzo Veldkamp; Heiko Faust; Edi Guhardja, eds. (2010). Tropical Rainforests and Agroforests Under Global Change. Springer. pp. 270–271. ISBN 978-3-642-00492-6.
- Intergovernmental Panel on Climate Change (2000). Land Use, Land Use Change and Forestry. Cambridge University Press.[page needed]
- Achard, F; Eva, H. D.; Stibig, H. J.; Mayaux, P; Gallego, J; Richards, T; Malingreau, J. P. (2002). "Determination of deforestation rates of the world's humid tropical forests". Science. 297 (5583): 999–1003. Bibcode:2002Sci...297..999A. doi:10.1126/science.1070656. PMID 12169731.
- Jha, Alok (21 October 2005). "Amazon rainforest vanishing at twice rate of previous estimates". The Guardian.
- Satellite images reveal Amazon forest shrinking faster, csmonitor.com, 21 October 2005.
- Culas, Richard J. (2007). "Deforestation and the environmental Kuznets curve: An institutional perspective" (PDF). Ecological Economics. 61 (2–3): 429–437. doi:10.1016/j.ecolecon.2006.03.014. Archived from the original (PDF) on 4 March 2016. Retrieved 8 December 2018.
- Whitehead, John (22 November 2006) Environmental Economics: A deforestation Kuznets curve?, env-econ.net .
- Koop, Gary & Tole, Lise (1999). "Is there an environmental Kuznets curve for deforestation?". Journal of Development Economics. 58: 231. doi:10.1016/S0304-3878(98)00110-2.
- "Pan-tropical Survey of Forest Cover Changes 1980–2000". Forest Resources Assessment. Rome, Italy: Food and Agriculture Organization of the United Nations (FAO).
- Committee On Forestry. FAO (16 March 2001). Retrieved 2010-08-29.
- FAO. 2016. Global Forest Resources Assessment 2015. How are the world’s forests changing?
- Worldwatch: Wood Production and Deforestation Increase & Recent Content, Worldwatch Institute
- Butler, Rhett A. (16 November 2005). "World deforestation rates and forest cover statistics, 2000–2005". mongabay.com.
- The fear is that highly diverse habitats, such as tropical rainforest, are vanishing at a faster rate that is partly masked by the slower deforestation of less biodiverse, dry, open forests. Because of this omission, the most harmful impacts of deforestation (such as habitat loss) could be increasing despite a possible decline in the global rate of deforestation.
- "Remote sensing versus self-reporting".
- The World Bank estimates that 80% of logging operations are illegal in Bolivia and 42% in Colombia, while in Peru, illegal logging accounts for 80% of all logging activities. (World Bank (2004). Forest Law Enforcement.) (The Peruvian Environmental Law Society (2003). Case Study on the Development and Implementation of Guidelines for the Control of Illegal Logging with a View to Sustainable Forest Management in Peru.)
- "Forest Holocaust". National Geographic.
- "THE SIZE OF THE RAINFORESTS". csupomona.edu. Archived from the original on 2012-09-30.
- The Amazon Rainforest, BBC, 14 February 2003.
- Revington, John. "The Causes of Tropical Deforestation". New Renaissance Magazine.
- "What is Deforestation?". kids.mongabay.com.
- "Paraguay es principal deforestador del Chaco". ABC Color newspaper, Paraguay. Retrieved 13 August 2011.
- "Paraguay farmland". Archived from the original on 18 September 2012. Retrieved 13 August 2011.
- IUCN – Three new sites inscribed on World Heritage List, 27 June 2007.
- "Madagascar's rainforest map". New Scientist.
- "Haiti Is Covered with Trees". EnviroSociety. Tarter, Andrew. Retrieved 14 November 2016.
- Chart – Tropical Deforestation by Country & Region. Mongabay.com. Retrieved 4 December 2011.
- Rainforest Destruction. rainforestweb.org
- Amazon deforestation rises sharply in 2007, USATODAY.com, 24 January 2008.
- Vidal, John (31 May 2005). "Rainforest loss shocks Brazil". The Guardian. London. Retrieved 1 April 2010.
- The World's 10 Most Threatened Forest Hotspots, Conservation International, 2 February 2011.
- Indo-Burma, Conservation International.
- New Caledonia, Conservation International.
- Sundaland, Conservation International.
- Philippines, Conservation International.
- Atlantic Forest Archived 12 December 2011 at the Wayback Machine, Conservation International.
- Mountains of Southwest China, Conservation International.
- California Floristic Province Archived 14 April 2011 at the Wayback Machine, Conservation International.
- Coastal Forests of Eastern Africa, Conservation International.
- Madagascar & Indian Ocean Islands, Conservation International.
- Eastern Afromontane, Conservation International.
- "Copenhagen Accord of 18 December 2009" (PDF). UNFCC. 2009. Retrieved 28 December 2009.
- Forest Monitoring for Action (FORMA) : Center for Global Development : Initiatives: Active. Cgdev.org (23 November 2009). Retrieved 2010-08-29.
- Browser – GEO FCT Portal[permanent dead link]. Portal.geo-fct.org. Retrieved 29 August 2010.
- "Methodological Guidance" (PDF). UNFCC. 2009. Retrieved 28 December 2009.
- Agriculture Secretary Vilsack: $1 billion for REDD+ « Climate Progress. Climateprogress.org (16 December 2009). Retrieved 2010-08-29.
- "FAO sets standards to improve national forest monitoring systems".
- Steininger, Marc. "REDD+ MEASUREMENT, REPORTING AND VERIFICATION (MRV) MANUAL" (PDF). Conservation.org. US Aid. Retrieved 1 September 2017.
- Angelsen, Arild; et al. (2009). "Reducing Emissions from Deforestation and Forest Degradation (REDD): An Options Assessment Report" (PDF). Meridian Institute for the Government of Norway. pp. 75–77. Retrieved 24 November 2011.
- Holder, Michael. "'Potential breakthrough': Palm oil giant Wilmar steps up 'no deforestation' efforts". Business Green. Retrieved 11 December 2018.
- Payments for watershed services: A driver of climate compatible development, Climate & Development Knowledge Network, 30 December 2013.
- "India should follow China to find a way out of the woods on saving forest people". The Guardian. 22 July 2016. Retrieved 7 August 2016.
- "China's forest tenure reforms". rightsandresources.org. Retrieved 7 August 2016.
- "Global Forest Change – Google Crisis Map". Google Crisis Map. Retrieved 12 October 2016.
- "Warning to forest destroyers: this scientist will catch you". Nature News & Comment. 4 October 2016. Retrieved 12 October 2016.
- Diamond, Jared Collapse: How Societies Choose To Fail or Succeed; Viking Press 2004, pp. 301–302 ISBN 0-14-311700-9.
- Diamond, Jared Collapse: How Societies Choose To Fail or Succeed; Viking Press 2004, pp. 320–331 ISBN 0-14-311700-9.
- Rosenberg, Tina (13 March 2012). "In Africa's vanishing forests, the benefits of bamboo". New York Times. Retrieved 26 July 2012.
- "State of the World's Forests 2009". United Nations Food and Agriculture Organization.
- Facts about Tropical Timber. Rainforest Rescue. Retrieved 13 November 2016.
- Gittings, John (20 March 2001). "Battling China's Deforestation". The Guardian.
- Foley, J. A.; Defries, R; Asner, G. P.; Barford, C; Bonan, G; Carpenter, S. R.; Chapin, F. S.; Coe, M. T.; Daily, G. C.; Gibbs, H. K.; Helkowski, J. H.; Holloway, T; Howard, E. A.; Kucharik, C. J.; Monfreda, C; Patz, J. A.; Prentice, I. C.; Ramankutty, N; Snyder, P. K. (2005). "Global Consequences of Land Use". Science. 309 (5734): 570–574. Bibcode:2005Sci...309..570F. doi:10.1126/science.1111772. PMID 16040698.
- James Owen, "World's Forests Rebounding, Study Suggests". National Geographic News, 13 November 2006.
- The world’s last intact forest landscapes. intactforests.org
- "World Intact Forests campaign by Greenpeace". intactforests.org.
- The World's Forests from a Restoration Perspective, WRI
- "Alternative thematic map by Howstuffworks; in pdf" (PDF).
- Botkin, Daniel B. (2001). No man's garden: Thoreau and a new vision for civilization and nature. Island Press. pp. 246–247. ISBN 978-1-55963-465-6. Retrieved 4 December 2011.
- Payn, T. et al. 2015. Changes in planted forests and future global implications, Forest Ecology and Management 352: 57–67
- FAO. 2015. Global Forest Resources Assessment 2015. How are the world’s forests changing?
- Stenstrup, Allen (2010). Forests. Greensboro, North Carolina: Morgan Reynolds Publishing. p. 89. ISBN 978-1-59935-116-2.
- Balabkins, Nicholas (1964) "Germany Under Direct Controls; Economic Aspects Of Industrial Disarmament 1945–1948, Rutgers University Press. p. 119. The two quotes used by Balabkins are referenced to, respectively: U.S. office of Military Government, A Year of Potsdam: The German Economy Since the Surrender (1946), p. 70; and U.S. Office of Military Government, The German Forest Resources Survey (1948), p. II. For similar observations see G.W. Harmssen, Reparationen, Sozialproduct, Lebensstandard (Bremen: F. Trujen Verlag, 1948), I, 48.
- Higa, Takejiro. Battle of Okinawa, The Hawaii Nisei Project
Arreguín-Toft, Ivan. How the Weak Win Wars: A Theory of Asymmetric Conflict. Cambridge Studies in International Relations ISSN 0959-6844. 99. Cambridge: Cambridge University Press. p. 61. ISBN 9780521839761. Retrieved 2018-06-17.
[...] Voronzov [...] then set about organizing a more methodical destruction of Shamil and the subsequent conquest of the Caucasus. Over the next decade, this involved nothing more complicated or less deadly than the deforestation of Chechnia.
- "DEFOLIANT DEVELOPED BY US WAS FOR KOREAN WAR". States News Services. 29 May 2011.
- Pesticide Dilemma in the Third World: A Case Study of Malaysia. Phoenix Press. 1984. p. 23.
- "Encyclopedia of World Environmental History". Routledge, 2004. ISBN 0-415-93733-7.
- Marchak, M. Patricia (18 September 1995). Logging the globe. McGill-Queen's Press – MQUP. pp. 157–. ISBN 978-0-7735-1346-4. Retrieved 4 December 2011.
- Biodiversity and Infectious Diseases, Center for Health and the Global Environment, Harvard T.H. Chan School of Public Health, Harvard University (last accessed May 15, 2017.
- Bruce A. Wilcox & Brett Ellis, Forests and emerging infectious diseases of humans, United Nations Food and Agriculture Organization Corporate Document Repository.
- Moslemi, Jennifer M.; Snider, Sunny B.; MacNeill, Keeley; Gilliam, James F.; Flecker, Alexander S. (2012). "Impacts of an Invasive Snail". PLoS ONE. 7 (6): e38806. Bibcode:2012PLoSO...738806M. doi:10.1371/journal.pone.0038806. PMC 3382606. PMID 22761706.
- Deforestation and emerging diseases | Bulletin of the Atomic Scientists. Thebulletin.org (15 February 2011). Retrieved 2016-11-13.
- African Politics Portal | Tag Archive | Environmental impact of deforestation in Kenya. African-politics.com (28 May 2009). Retrieved 2016-11-13.
- 2014 Kenya Economic Survey Marks Malaria As Country’s Leading Cause Of Death | The Henry J. Kaiser Family Foundation. Kff.org (1 May 2014). Retrieved 2016-11-13.
- Julia, Berazneva; S., Byker, Tanya (2017-05-01). "Does Forest Loss Increase Human Disease? Evidence from Nigeria". American Economic Review. 107 (5). doi:10.1257/aer.p20171132&etoc=1. ISSN 0002-8282.
- Scheidt, Spencer N.; Hurlbert, Allen H. (2014). "Range Expansion and Population Dynamics of an Invasive Species: The Eurasian Collared-Dove (Streptopelia decaocto)". PLoS ONE. 9 (10): e111510. Bibcode:2014PLoSO...9k1510S. doi:10.1371/journal.pone.0111510. PMC 4213033. PMID 25354270.
- Lam, Sai Kit; Chua, Kaw Bing (2002). "Nipah Virus Encephalitis Outbreak in Malaysia". Clinical Infectious Diseases. 34: S48–51. doi:10.1086/338818. PMID 11938496.
- "Nipah Virus (NiV)". cdc.gov.
- Deforestation sparks giant rodent invasions. News.mongabay.com (15 December 2010). Retrieved 2016-11-13.
- General references
- BBC 2005 TV series on the history of geological factors shaping human history (name?)
- A Natural History of Europe – 2005 co-production including BBC and ZDF
- Runyan, C.W., and D'Odorico, P. (2016) Global Deforestation, Cambridge University Press, New York.
- Whitney, Gordon G. (1996). From Coastal Wilderness to Fruited Plain : A History of Environmental Change in Temperate North America from 1500 to the Present. Cambridge University Press. ISBN 0-521-57658-X
- Williams, Michael. (2003). Deforesting the Earth. University of Chicago Press, Chicago. ISBN 0-226-89926-8
- Wunder, Sven. (2000). The Economics of Deforestation: The Example of Ecuador. Macmillan Press, London. ISBN 0-333-73146-8
- FAO&CIFOR report: Forests and Floods: Drowning in Fiction or Thriving on Facts?
- Fenical, William (September 1983). "Marine Plants: A Unique and Unexplored Resource". Plants: the potentials for extracting protein, medicines, and other useful chemicals (workshop proceedings). DIANE Publishing. p. 147. ISBN 1-4289-2397-7.
- Ethiopia deforestation references
- Parry, J. (2003). Tree choppers become tree planters. Appropriate Technology, 30(4), 38–39. Retrieved 22 November 2006, from ABI/INFORM Global database. (Document ID: 538367341).
- Hillstrom, K & Hillstrom, C. (2003). Africa and the Middle east. A continental Overview of Environmental Issues. Santabarbara, CA: ABC CLIO.
- Williams, M. (2006). Deforesting the earth: From prehistory to global crisis: An Abridgment. Chicago: The university of Chicago Press.
- Mccann, J.C. (1990). "A Great Agrarian cycle? Productivity in Highland Ethiopia, 1900 To 1987". Journal of Interdisciplinary History. xx: 3, 389–416.
|Wikimedia Commons has media related to Deforestation.|
- Global map of deforestation based on Landsat data
- JICA-JAXA Forest Early Warning System in the Tropics: JJ-FAST (FOREST GOVERNANCE INITIATIVE)- JICA-JAXA
- Old-growth forest zones within the remaining world forests
- EIA forest reports: Investigations into illegal logging.
- EIA in the USA Reports and info.
- Cocaine destroys 4 m2 of rainforest per gram The Guardian
- "Avoided Deforestation" Plan Gains Support – Worldwatch Institute
- OneWorld Tropical Forests Guide
- Some Background Info to Deforestation and REDD+
- General info on deforestation effects
- Deforestation and Climate Change
- In the media
- 14 March 2007, Independent Online: Destruction of forests in developing world 'out of control'
- Pappas, S. (14 November 2013). "Vanishing Forests: New Map Details Global Deforestation". LiveScience.com. TechMediaNetwork. Retrieved 16 November 2013.
- 31 August 2017, Independent Online: New Amazonian species discovered every two days while the rainforest is trashed by 'relentless deforestation'
- Films online