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Management of Natural Resources in Sustainable Surface

机译:可持续表面自然资源管理

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Since late nineteen, there has been ever increasing concern for adverse environmental impacts of intensive arable farming in varied land situations. Concerns like pollution of waters due to excess use of insecticides/pesticides, indiscriminate use of inorganic fertilizers and excessive irrigation under canal systems have attracted world wide attention in recent times. During the mid-sixties, the major goal of Indian agriculture was to increase food-grain production to cope up with the ever-increasing population. A composite strategy of introduction of high yielding varieties along with assured irrigation and fertilizers, and institutional support were provided to achieve quantum jump in agricultural production, which in turn provided additional employment in rural sector. A sizable investment has been made in creating assured irrigation facilities through major and medium irrigation projects with the target to increase food grain to a tune of 4 t/ha-5 t/ha in long term without causing any adverse effects on environment. Unfortunately, the introduction of canal irrigation resulted into development of soil salinity and shallow water-table in arid and semi-arid regions, which has serious negative impact on agricultural environment in the areas covered under canal irrigation systems. Despite massive invertment in creating canal irrigation systems, the present level of food grain production under canal command area is only around 1.7 t/ha (Satpate, 1988). The basic principal of soil and water conservation is to use the land according to its capability and treat the land according to its Performance (Tideman, 1996). The production performance of a crop is directly guided by soil characteristics viz., soil depth, texture, slope, water-holding capacity, internal drainage, etc. Based on these criteria, land has been classified in eight categories called 'land capability classes'. The first four land capability classes are considered suitable for crop production. The remaining four land capabilities classes are considered fit for pasture, wood lots and wild-life use. The choice of crops and cropping patterns based on capabilities in order to produce higher returns per unit area with adequate provision of conserving the natural resource (Van wambeke and Rossiter, 1987). Under the irrigated conditions these land capabilities are called 'land irrigability classes'. Of late researchers and planners have laid much emphasis on 'Land Capability Classes' as such to achieve sustainability in agricultural production(Alagh, 1990). Therefore, what is urgently called for is an appropriate land use policy so that optimal use of land resources based on land capability or sustainability is taken care of (Khosoo and Deekshatulu, 1992). In the present analysis, an attempt has been made to document the crop production under different land irrigability classes and its impact on natural resources like soil and other causative factors in semi-arid region of Gujarat State, India.
机译:自20晚,一直在变化的情况下,土地集约农业耕地不良环境影响的日益增加的关注。像水的污染问题,由于过度使用农药/杀虫剂,乱用无机肥料和下渠系灌溉过多的吸引了全世界的广泛关注,近倍。在六十年代中期,印度农业的主要目标是增加粮食粮食生产与人口的不断增加,以应付了。分别提供引进有保证灌溉和肥料,以及机构支持以及高产品种的组合策略,实现农业生产的重大突破,而这又是在农村部门提供更多的就业机会。投入大笔资金在创造通过大中灌溉项目保证灌溉设施与目标,以增加粮食4一调已经取得吨/公顷-5吨/公顷长期而不会造成对环境的任何不利影响。不幸的是,引入运河灌溉导致土壤成盐度和浅水表在干旱和半干旱地区,这对下运河灌溉系统所覆盖区域农业生态环境造成严重负面影响的发展。尽管在创建管灌溉系统大规模invertment,粮食生产的管命令区域下的本水平仅约1.7吨/公顷(Satpate,1988)。水土保持的基本原理是根据其能力,使用土地,并根据其性能(泰德曼,1996)把土地。作物的生产性能是直接由土壤特性即引导。,土壤深度,纹理,坡度,持水容量,内部排水等。基于这些标准,土地已被分类在八类被称为“陆地能力等级” 。前四个土地能力等级被认为适合作物生产。剩下的四个土地功能类被认为适合草场,大量的木材和野生生活中使用。作物和种植模式,以便与保护自然资源的充分提供生产每单位面积较高的回报基础上的功能选择(范wambeke和罗斯特,1987)。在灌溉条件下,这些土地的能力,被称为“土地irrigability班”。后期研究者和规划者奠定地强调“土地能力等级”这样实现农业生产(Alagh,1990)可持续性。因此,什么是迫切需要的,是一个适当的土地利用政策,根据土地能力和可持续发展的土地资源是最佳利用取(Khosoo和Deekshatulu,1992年)的护理。在目前的分析中,已经尝试来记录不同土地irrigability类下的作物产量和古吉拉特邦,印度的半干旱地区的像土壤和其他致病因素自然资源的影响。

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