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close this bookDiversity, Globalization, and the Ways of Nature (IDRC, 1995, 234 p.)
View the document(introduction...)
View the documentAcknowledgments
View the documentForeword
close this folder1. Introduction
View the documentGlobalization and the ways of nature
View the documentThe new globalization processes
close this folder2. Global trends and their effects on the environment
View the documentThe information revolution
View the documentDevelopment of global financial markets
View the documentDevelopment of more effective transportation networks
View the documentMovement of people
View the documentGlobalization and the unequal distribution of wealth
View the documentInternational migration
View the documentThe development of free markets
close this folder3. Planet-wide deterioration
View the document(introduction...)
View the documentOur sister planet
View the documentThe unusual, oxygenated planet
View the documentThe paradox of ozone
View the documentOceans can be degraded too
View the documentThe rivers are becoming muddy
View the documentOvershooting
close this folder4. Forests under attack
View the document(introduction...)
View the documentDeforestation in the 20th century
View the documentRain-forest environments
View the documentTemperate forests
close this folder5. Grasslands
View the documentSavannas
View the documentThe temperate grasslands
View the documentModifying grassland ecosystems
View the documentEnvironmental balance in grassland ecosystems
close this folder6. Aquatic ecosystems
View the documentExtractive exploitation
View the documentThe future of fish production
close this folder7. Managing planetary thirst
View the documentSome basic facts
View the documentWater supply and options
View the documentThe demand side of the issue
View the documentWater issues throughout the world
close this folder8. Protecting air quality
View the document(introduction...)
View the documentAir and its principal contaminants
View the documentProcesses of contamination in industrial and urban areas
View the documentCurrent and future trends
close this folder9. Clean energy for planetary survival
View the document(introduction...)
View the documentThe industrial revolution
View the documentThe use of hydroelectricity
View the documentThe age of petroleum
View the documentNuclear power
View the documentThe clean options
close this folder10. Africa in the 21st Century: Sunrise or sunset?
View the document(introduction...)
View the documentThe causes of poverty
View the documentHistorical causes of the current situation
View the documentWars are environmentally unfriendly
View the documentEvolution of environmental management in Africa
View the documentOld and new development models
close this folder11. Latin America and the Caribbean: A history of environmental degradation
View the document(introduction...)
View the documentIndigenous cultures
View the documentThe colonial period
View the documentExploitation of natural resources after independence
View the documentEffects of globalization on the environment
View the documentThe maquiladora phenomenon
close this folder12. The urban environmental challenge
View the documentThe development of modern cities
View the documentLarge cities in the Third World
View the documentThe megacities of today
close this folder13. Diversity and human survival
View the document(introduction...)
View the documentDocumenting diversity
View the documentResources for the future
View the documentDiversity of living systems
View the documentCauses and effects of the loss of natural diversity
View the documentDiversity and culture
View the documentRestoring what is lost
View the documentBiodiversity and research
close this folder14. Strategies for the future
View the document(introduction...)
View the documentDecentralize decision-making
View the documentPeople value their environment
View the documentProblems and responsibilities are global
View the documentBibliography

Modifying grassland ecosystems

Globalization of the economy and encroachment of land-intensive and labour-intensive agriculture on some savanna lands is producing some important environmental changes. Undulating and hilly savannas are being eroded by water, reducing the thickness of their soils and, consequently, their agricultural potential. In flatter areas, soils are less affected by water, but may be seriously degraded by aeolian (wind) action. Irrigation may also have long-term consequences, such as waterlogging, salinization, or alkalinization.

In all cases, repeated cultivation of the same plots brings about a gradual loss of nutrients, reducing fertility and having a negative effect on the biological potential of the exploited areas. When fertilizers are used to compensate for decreasing fertility, other side effects can occur. Not all soil nutrients are replaced by the application of fertilizers; some, especially micronutrients, may not be added, and some impoverishment takes place in any case. Second, some nutrients may be applied in excessive volumes with potential deleterious effects, not only on the soil, but also on the natural water systems, giving rise to algal growth and, in some cases, to eutrophication of lakes and reservoirs.

Pesticides can have an even greater impact because of their natural toxicity (obviously, the main purpose of pesticides is to kill pests). They may find their way not only into the leaves, fruit, and vegetative tissues of crops, but also into surface water bodies and groundwater. Some long-lasting pesticides may appear a few years after their application in the water supply of nearby towns or rural communities.

One of the land uses of savannas, particularly in Africa, is for raising livestock. In drier savannas or in steppes, overgrazing can produce extensive desertification patterns. This can be seen in many African countries (particularly in the Sahelian region), where overgrazing has reduced vegetation density and diversity, promoting soil erosion, decay, and loss of productivity.

An important factor associated with overgrazing is the indiscriminate drilling of wells in the countryside. In pastoral societies, cattle ownership is frequently a sign of prestige. Raising animals can be an important social function, allowing a man to find a wife or to obtain more power. The main factor limiting the size of a herd has always been the availability of water. Areas around the main water holes are heavily overgrazed, but peripheral areas may be almost intact. When many new wells are drilled, people increase their herds and move them into the new locations. After a few years, the whole landscape is degraded beyond recognition and irreversible desertification takes place. Examples of this situation can be found throughout the African continent - northern Senegal (Kerkhof 1992, pp. 105-112), northern Kenya, Sudan, Mali, and Niger.

In South America, a number of savanna ecosystems are being used for agricultural purposes. Those of Brazil are typical. The savanna areas of southern and central Brazil have developed as a result of the removal of forests. In Mato Grosso, the tropical rain forest, which was slightly less dense than the Amazon jungle, was gradually burned and logged to make way for various crops, particularly rice and soybeans.

In dry rice farming, fertilizers are usually not applied. Thus, the nutrients in the soil, which, like most tropical soils, has low fertility, are further reduced and the land quickly becomes inappropriate for further cultivation - without heavy applications of costly fertilizers. Normally, after 3 or 4 years of dry rice cultivation, the land is no longer productive and is converted to cattle ranching. (The secondary savanna in Mato Grosso is a low-productivity rangeland for cattle.)

Soybean cultivation is carried out on a large scale, for commercial purposes, on large farms using a similar nonsustainable approach. Fertilizers and pesticides are applied with little concern for the environment, seriously affecting the aquatic ecosystems in nearby streams. Many indigenous communities of South America that depend on fish for their existence have seen their livelihood and incomes curtailed because of aggressive agricultural practices in these secondary savanna lands (see also Chapter 4).

In southern Brazil, from Sao Paulo to Rio de Janeiro, the original vegetation was subtropical rain forest and an almost monospecific ecosystem of Araucaria (Brazilian pine). Sao Paulo’s forest was gradually eliminated, at the end of the 19th century and during the first half of the 20th century, to make way for coffee plantations and other crops. In many places, a savanna-type vegetation has replaced the forest. More recently, sugarcane (for alcohol fuel production) has been planted throughout the Sao Paulo region, often supplanting coffee plantations. The Araucaria forest suffered a similar fate. From the 1950s through the 1970s, almost all of the forest was logged; ranching and cultivation of crops such as soybean now occur on the secondary savannas that developed. In some cases, the Araucaria forests were replaced with artificial forests of exotic trees.

Modification of natural ecosystems may have unexpected effects on neighbouring farming systems. Planting some types of trees can alter the nesting habits of some birds and favour their reproduction. For example, if a bird’s natural predators cannot reach the nest, the species may reproduce without constraint. Many crops, including sunflowers, corn, and fruit trees, can be severely affected by increases in the number of budgies and pigeons. Some of these birds may have wide ranges (more than 50 kilometres) and, therefore, may affect crops some distance from their nesting area. Exotic trees (such as pine trees in South American prairies) may also provide a feeding area for birds or insects. Indiscriminate planting of such trees in grasslands and associated farming areas can have a significant destabilizing effect on both the natural ecosystems and the crops.

The eucalyptus tree, which is native to Australia, has a very high growth rate. Because of this, they are planted throughout the world for many purposes. Eucalyptus is also a good nesting tree. It grows to 30 metres or more and, therefore, is difficult for grassland predators (mammals and other vertebrates) to climb. Frequently, farmland close to eucalyptus forests is plagued by an overabundance of birds that nest on the upper branches of the eucalyptus trees, where they thrive in the absence of predators that otherwise could prevent their multiplication (see box 3).

In addition, eucalyptus has been pinpointed as a strong ‘‘aridifier.’’ Poore and Fries (1987) found that, by its third year, Eucalyptus grandis reduced stream flow (measured as equivalent millimetres of rainfall) by between 300 and 380 millimetres per year. In Nigeria, Sharda et al. (1988) found that eucalyptus trees reduced the amount of water flowing from a basin by about 23%. Similar studies in India revealed a decrease in runoff of 28% (Poore and Fries 1987).

Eucalyptus also effects soil fertility. A decrease in soil nutrients, such as phosphorus, has been recorded in many cases. However, the main effects on fertility come from logging, which removes large volumes of key elements from the ecosystem, reducing its potential for other uses. After eucalyptus trees have been harvested two to four times - over about 30 years - the land is rendered useless for any other productive purpose. Not only do the soils become infertile and dry, but they are also crisscrossed by the remains of many root systems. Farming is impossible without major, expensive corrective measures, which are not cost-effective for most agricultural activities. For all practical purposes, “eucalyptus soils” are no longer usable for farming.

In a number of African projects, described in Agroforesny in Africa (Kerkhof 1992), eucalyptus trees were introduced to traditional African societies without much consideration of their suitability to local ecosystems or cultures. As in Uruguay, the effects have frequently been deleterious to the local environment or quality of life. In spite of this result, strong pressure and funding is coming from many sources to expand this nonsustainable type of forestation. Uruguay, for example, received over $50 million from international banks for such forestation projects.

3. Planting trees in grassland ecosystems

Lately, as a result of globalization and the transfer of labour- and land-intensive activities to developing countries, large-scale forestation has reached the pampas. The trees used are mainly eucalyptus and pine: Eucalyptus globulus, E. grandis, E. rostrata, Pinus pinaster, and P. maritimus. Large tracts of former grasslands have been dedicated to monospecific plantations of these trees, which are grown for lumber, fuel, or paper pulp, often for export, but also for consumption in the pampas countries.

The consequences of this widespread planting of exotic trees are becoming apparent. Indigenous trees are not very tall and are sparsely distributed. The new, exotic trees offer an interesting nesting niche for many birds that have spread beyond their natural habitat.

The prairie predators of birds - raccoons, foxes, opossums, wildcats - are unable to climb the tall trees, resulting in an population explosion of some species of birds, such as budgies and wild pigeons. These birds plague nearby crops, reducing their quality or destroying them completely.

Although the eucalyptus plantations are the main nesting habitat, they do not provide a feeding ground for birds; there is little or no undergrowth in the forests and the seeds of eucalyptus trees cannot be eaten by most birds. As a result, birds make feeding forays into nearby agricultural crops. These crops supply food for only a few months of the year, usually late spring to fall. Artificial pine plantations provide food for the birds during winter. The frequent association of eucalyptus and pine trees in agricultural areas can be a recipe for disaster. Eucalyptus trees provide a nesting place, pine trees the winter food, and crops the main staple for the rest of the year. A new artificial ecosystem is formed, but it is not in the best interests of farmers nor does it contribute to local biodiversity (Gutierrez et al. 1993).