Agronomic Practices to Improve Water Use Efficiency

C. Pimentel
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Abstract

Water scarcity, which already occurs for more than a billion people worldwide, will worsen further, and the water supply available for future generations, especially for use in agriculture, will be increasingly restricted (FAO, 2017). Above all, in arid and semi-arid regions, irrigated agriculture uses more than 70 to 80% of the total water available and is essential to increase food production in these regions, where the population is rapidly increasing (TURNER, 2004) [1]. The world’s population in 2004 was more than 6,000,000, of which around 5,000,000 were in developing countries, and 20% of this population has remained undernourished since the 1990s [2]. For this time, water management in agriculture, in the current era of scarcity, should be engaged to implement water use efficiency (WUE), spending fewer resources and producing less expensive plant protein [3,4]. In the past, during the post-war “green revolution”, the paradigm of agriculture was to modify the environment (heavy fertilization, irrigation, and mechanization, with energy expenditure) to adapt it to the plant, with the generation of so-called high-yield varieties (HYVs), with high harvest index (HI: Dry Weight [DW] of the organ harvested. plant DW-1), for mechanized harvesting and responsive to the application of fertilizers, which were cheap at the time [1], but less adapted to the stresses, which was mitigated by energy expenditure, in irrigation and mechanization, and fertilizers applied [5]. For example, in grasses, the induction of progressive tillering, as occurs in the millet and sorghum, is one of the mechanisms of escape from environmental stresses because each inflorescence will have a different period of fertilization increasing the chances of producing some viable panicles [5]. However, this characteristic would prevent mechanized harvesting, but small farmers in marginal areas of agriculture do not use mechanic harvesting. Marginal agriculture areas are frequently subjected to environmental stresses and have soils with poor nutrient content [3]. In the past, during the green revolution, it was always a characteristic undesirable for plant breeding programs to improve yield. In addition, the increase in HI was often obtained with a reduction of volume and root area, which is very important to implement the WUE [6]. Therefore, the genetic basis for the environmental adaptation of the most improved crop by man, such as maize, has been dramatically diminished. After the oil and energy crisis in the 1970s, the paradigm of agriculture has become to modify the plant to adapt it to the environment, with WUE, generating varieties with Low Technological Cost (LCVs) for agricultural production (Figure 1). This adaptation to environmental stresses can also be found in local landraces used by the small farmers living in marginal areas for agriculture, which needs to be better studied and recommended to increase food safety in these areas [3].
提高水资源利用效率的农艺实践
水资源短缺已经影响到全球超过10亿人,未来情况将进一步恶化,可供子孙后代使用的水资源,特别是用于农业的水资源,将日益受到限制(粮农组织,2017)。最重要的是,在干旱和半干旱地区,灌溉农业使用了70%至80%以上的总可用水,对于增加这些地区的粮食产量至关重要,这些地区的人口正在迅速增加(TURNER, 2004)[1]。2004年世界人口超过600万,其中发展中国家人口约500万,其中20%的人口自20世纪90年代以来一直处于营养不良状态[2]。因此,在当前水资源匮乏的时代,农业用水管理应致力于实现水资源利用效率(WUE),减少资源消耗,降低植物蛋白的生产成本[3,4]。过去,在战后的“绿色革命”期间,农业的模式是改变环境(大量施肥、灌溉和机械化,消耗能量),使其适应植物,产生所谓的高产品种(hyv),具有高收获指数(HI:收获器官干重[DW])。植物dw1),用于机械化收获和对肥料施用的响应,当时肥料很便宜[1],但对压力的适应能力较差,灌溉和机械化以及肥料的能量消耗减轻了压力[5]。例如,在禾草中,诱导进行性分蘖,就像在谷子和高粱中发生的那样,是逃避环境胁迫的机制之一,因为每个花序将有不同的受精期,增加了产生一些活穗的机会[5]。然而,这一特点会阻碍机械化收割,但农业边缘地区的小农不使用机械收割。边缘农业区经常受到环境压力,土壤养分含量差[3]。在过去,在绿色革命期间,提高产量总是不受植物育种计划的欢迎。此外,HI的增加往往伴随着体积和根面积的减少,这对于实现WUE非常重要[6]。因此,人类改良最多的作物(如玉米)适应环境的遗传基础已经大大减少。在20世纪70年代的石油和能源危机之后,农业的范式已经变成了改造植物以适应环境,利用WUE,产生低技术成本(lcv)的品种用于农业生产(图1)。这种对环境压力的适应也可以在生活在边缘地区的小农使用的当地土种中找到,需要更好地研究和推荐,以提高这些地区的食品安全[3]。
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