Natural Hazards: Causes and Effects - Disaster Management Center ...
Natural Hazards: Causes and Effects - Disaster Management Center ... Natural Hazards: Causes and Effects - Disaster Management Center ...
enterprises are enormously expensive. Such considerations stress the importance of maintaining existing irrigation schemes by countering desertification with preventive action whenever it affects them. Salinization. The most prevalent form of desertification in irrigated cropping systems occurs when waterlogging causes salts and alkali to infect soils, particularly where drainage is poor and leaching inadequate. It is a problem that emphasizes the importance of preliminary surveys and testing of proposed irrigation projects to assure adequate design. Most salinization problems arise from irrigation system design deficiencies. Irrigation System Design. Good design should be based on an understanding of how much water is available for irrigation and on the knowledge of its silt and salt loads, including seasonal variations. A close study of the soils must be made in the area embraced by a land-use project. Such study must consider their texture and salinity, and especially their water properties, as these will determine drainage requirements and water availability to crops. Water requirements for proposed cropping systems should be determined. The position and salt content of the groundwater table should also be determined, as there are seasonal fluctuations in both. This will require some understanding of the hydraulic properties of the soil’s lower layers, and of how these layers store and transmit water. Field Test Results. These investigations should yield a map showing salt hazards and how they might restrict the proposed cropping system. On the basis of the map and the surveys, design work can continue with particular emphasis on the distribution of the water and on effective drainage systems and the subdivisions of the system as determined by estimated water needs. Finally, design should take account of the services and communications the system will require and the settlements that serve and are served by it. Maintaining Balance of Groundwater Supplies. Irrigation projects based on groundwater supplies encounter special difficulties because groundwater quality is usually lower than that of surface waters and the threat of salinization is generally higher. Limitations in groundwater supplies may hinder proper leaching. Groundwater supplies must be kept in balance with the requirements of land use, and enough water must be provided for both irrigation and leaching. Generally, discipline applied to water use must be stricter when irrigation is based on groundwater rather than surface water. Reclamation of Salinized Lands. When irrigated lands have suffered salinization or other forms of desertification, they should be surveyed as a first step to reclamation. By determining what topographic changes have occurred and the degree of salinization of soil and groundwater levels, an individual can estimate what is needed to leach and drain affected lands and what else might be required to restore the system—by releveling of ground surfaces, for example, or renewal of irrigation channels. How drainage will be carried out—whether by tubewells, tile drainage or open ditches—will depend on groundwater conditions, soil properties and costs of land and labor. To decide among alternatives, a cost-benefit analysis may be needed. Secondary Physical Effects It must also be borne in mind that desertification has an impact beyond the lands immediately affected. Dust storms can move soil great distances, and increased flooding may occur far downstream due to overly rapid runoff from lands denuded of trees and plants in upstream catchments undergoing desertification.
Issues in Reconstruction Peculiar to Desertification When working to prevent, mitigate, or recover from the results of desertification, an individual should keep in mind the following information that can make reconstruction efforts more successful. Desertification Feeds on Itself The need for action to combat desertification is all the more urgent because the process is a dynamic one. Desertification can feed on itself and become self-accelerating. With delay, rehabilitation becomes increasingly lengthy and expensive, and degradation may reach a threshold beyond which it is irreversible in practical and economic terms. Fundamental preventive measures should be introduced as soon as possible. These should be in the form of socio-economically appropriate land-use practices that improve the fertility of microclimates and soils and prevent desertification from making further encroachments. Monitoring Dryland Conditions Apart from limitations set by climate, dryland ecosystems will remain sensitive to land-use pressure because their soils and dynamics are delicately balanced. The best-designed dryland livelihood system will still require constant surveillance if balance is to be sustained. It is therefore essential that campaigns against desertification must incorporate systems of monitoring that will indicate how campaigns are proceeding and when people should be alerted about pending problems. This requirement strongly underlines the need to develop indigenous science and technology, so that assessment, monitoring and planning will not be added to the list of imported items. A Flexible Plan of Action A geographical spread as immense as the drylands comprises a vast variety of biophysical, economic and social settings. Desertification processes and problems are correspondingly varied and complex. Any plan of action to combat desertification will recognize this, and with it that there can be no single set of remedies. Recommendations must take account of different situations and be flexible enough to encompass a wide range of conditions. The Problem of Applying Current Knowledge A review of the desertification problem strongly supports the contention that past failures to maintain balanced livelihood systems in the drylands are the outcome of an inability to apply existing knowledge of physical processes rather than lack of understanding of what those processes are. The same is true of the design of measures to combat desertification. Accordingly, plans of action should address, first of all, the application of existing knowledge, the adaptation of existing knowledge to local situations in the social and physical spheres, and problems of acceptance and participation among local communities. Desertification and Government Goals It should not be take for granted that action to combat desertification will take first place among national commitments. A plan of action to combat desertification should not appear to pre-empt already-established national priorities. Nevertheless, it should be kept in mind that action on the ground will largely be carried out by national organizations, and presentation of the plan should accordingly aim to influence governmental attitudes toward the problem of desertification and should seek to secure the active commitment of governments. This is most likely to occur when combative measures, linked to broad national plans for development, appear to be consistent with national goals.
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enterprises are enormously expensive. Such considerations stress the importance of<br />
maintaining existing irrigation schemes by countering desertification with preventive action<br />
whenever it affects them.<br />
Salinization. The most prevalent form of desertification in irrigated cropping systems occurs<br />
when waterlogging causes salts <strong>and</strong> alkali to infect soils, particularly where drainage is poor <strong>and</strong><br />
leaching inadequate. It is a problem that emphasizes the importance of preliminary surveys <strong>and</strong><br />
testing of proposed irrigation projects to assure adequate design. Most salinization problems<br />
arise from irrigation system design deficiencies.<br />
Irrigation System Design. Good design should be based on an underst<strong>and</strong>ing of how much<br />
water is available for irrigation <strong>and</strong> on the knowledge of its silt <strong>and</strong> salt loads, including seasonal<br />
variations. A close study of the soils must be made in the area embraced by a l<strong>and</strong>-use project.<br />
Such study must consider their texture <strong>and</strong> salinity, <strong>and</strong> especially their water properties, as<br />
these will determine drainage requirements <strong>and</strong> water availability to crops. Water requirements<br />
for proposed cropping systems should be determined. The position <strong>and</strong> salt content of the<br />
groundwater table should also be determined, as there are seasonal fluctuations in both. This<br />
will require some underst<strong>and</strong>ing of the hydraulic properties of the soil’s lower layers, <strong>and</strong> of how<br />
these layers store <strong>and</strong> transmit water.<br />
Field Test Results. These investigations should yield a map showing salt hazards <strong>and</strong> how they<br />
might restrict the proposed cropping system. On the basis of the map <strong>and</strong> the surveys, design<br />
work can continue with particular emphasis on the distribution of the water <strong>and</strong> on effective<br />
drainage systems <strong>and</strong> the subdivisions of the system as determined by estimated water needs.<br />
Finally, design should take account of the services <strong>and</strong> communications the system will require<br />
<strong>and</strong> the settlements that serve <strong>and</strong> are served by it.<br />
Maintaining Balance of Groundwater Supplies. Irrigation projects based on groundwater<br />
supplies encounter special difficulties because groundwater quality is usually lower than that of<br />
surface waters <strong>and</strong> the threat of salinization is generally higher. Limitations in groundwater<br />
supplies may hinder proper leaching. Groundwater supplies must be kept in balance with the<br />
requirements of l<strong>and</strong> use, <strong>and</strong> enough water must be provided for both irrigation <strong>and</strong> leaching.<br />
Generally, discipline applied to water use must be stricter when irrigation is based on<br />
groundwater rather than surface water.<br />
Reclamation of Salinized L<strong>and</strong>s. When irrigated l<strong>and</strong>s have suffered salinization or other forms<br />
of desertification, they should be surveyed as a first step to reclamation. By determining what<br />
topographic changes have occurred <strong>and</strong> the degree of salinization of soil <strong>and</strong> groundwater<br />
levels, an individual can estimate what is needed to leach <strong>and</strong> drain affected l<strong>and</strong>s <strong>and</strong> what<br />
else might be required to restore the system—by releveling of ground surfaces, for example, or<br />
renewal of irrigation channels. How drainage will be carried out—whether by tubewells, tile<br />
drainage or open ditches—will depend on groundwater conditions, soil properties <strong>and</strong> costs of<br />
l<strong>and</strong> <strong>and</strong> labor. To decide among alternatives, a cost-benefit analysis may be needed.<br />
Secondary Physical <strong>Effects</strong><br />
It must also be borne in mind that desertification has an impact beyond the l<strong>and</strong>s immediately<br />
affected. Dust storms can move soil great distances, <strong>and</strong> increased flooding may occur far<br />
downstream due to overly rapid runoff from l<strong>and</strong>s denuded of trees <strong>and</strong> plants in upstream<br />
catchments undergoing desertification.