浙江武义县木本植物资源的开发利用

浙江武义县木本植物资源丰富，计有９２科２６８属６８０种，论述了这些资源植物的基本特点后，按其经济性状，将其分为材用、果类、纤维、油脂、芳香、鞣料、观赏、密源、药用、淀粉共１０类，最后对它们的综合利用提了一些建议，将为今后的开发利用提供依据。     

赤峰市木本植物资源的研究

赤峰市共有木本植物278种,隶属于44科,92属.其中裸子植物3科,7属,17种;被子植物41科,85属,261种;野生植物种222种,常见栽培种56种.     

林檎生物学特性及开发利用前景的研究

研究了林檎的生物学特性、叶的化学成分及在不同时期其化学成分含量的变化规律，综述了林檎的开发利甲前景．     

农田灌溉限量开采地下水的主要途径与方法

针对山西省运城地区因地下水超采而产生的地面下沉、地裂、农用机井报废等一系列环境问题，通过计算分析，提出了一个既能满足农业发展对水的需求，又能维持地下水资源环境平衡的地下水可开采量，并就实施限量开采地下水的途径、技术措施、管理机制、水价体系及政策保障等进行了综合分析与阐述。     

引黄灌区引水补源优化运行模型研究

应用非线性优化理论 ,并基于 Philip入渗方程和其它边界约束条件 ,建立了引水补源区优化运行数学模型。模型目标是确定在补源区自然物理条件、地下水流运动、入渗以及连续方程等约束下 ,使得入渗量最大的运行准则 ,应用非线性优化规划法对模型求解 ,得到了满意效果。以黄河下游陈垓引黄灌区 1 993年 3月对灌区下游补源区一个单周期引水补源过程为例 ,计算了一次引黄最大优化入渗补源量 ,本方法对开辟学术研究新思路 ,指导生产实践具有重要参考价值     

井渠结合灌区水资源多目标优化配置模型与应用

将灌区的经济效益和生态环境效益结合在一起综合考虑，在灌区水资源配置时不仅只追求获得最大经济效益，同时尽量将地下水位控制在适宜范围内，以维持地下水资源的采补平衡，实现水资源的可持续利用。按此原则，建立了井渠结合灌区水资源多目标优化配置模型。实例计算表明：应用此模型指导井渠结合灌区的水资源配置可实现真正意义上的地表水和地下水联合运用，提高水资源利用效率。     

灌区土壤盐渍化发展模拟预测与对策研究

以秦王川灌区观测和调查资料为依据,采用目前广为实用的MODFLOW地下水模拟软件,对灌区地下水动态进行了预测和分析,并对地下水质的发展趋势作出评价。灌溉实施以来,秦王川灌区地下水位逐年上升。未来10年内盐沼区面积扩大约为28 km2,并且将继续增加,地下水埋深0~2 m的面积达31.4 km2,占灌区面积的比例约为6%。未来20年地下水埋深0~2 m的面积达47 km2,占灌区面积的比例为10%左右。根据地下水位的变化特征,对控制土壤盐渍化发展的因素和对策进行了分析,提出以明沟排水为主,加大灌区下游地下水排泄能力;以渠灌为主,适度发展井灌,大力推行田间节水灌溉技术等对策。     

基于灰色关联度变权法的浅层地下水环境质量综合评价

引入指数型白化权函数对灰色关联度变权法中的白化权函数进行修正,使得能够对地下水更合理、客观、准确地评价。将晋江市浅层地下水看作一个灰色系统,在灰色关联度变权法模型基础上,对各水质监测点不同类别的隶属度和灰色关联度作对比分析判断其评价等级以及质量优劣次序,说明灰色关联度变权法对地下水环境质量综合评价方法适当。研究区内绝大多数地区水质状况良好,影响区域地下水质量的指标主要为TDS、锰、硝酸盐、亚硝酸盐、氨氮、氯化物,水质较差区主要分布于沿海工业分布较密集区及引污水灌溉农田地区,说明工农业发展、人类活动加剧及海水入侵是造成本区水质变化的主要原因之一。     

Contamination of shallow groundwater system and soil-plant transfer of trace metals under amended irrigated fields

This study focuses on experimental pilot assessment of contamination of shallow groundwater systems and soil-plant transfer of trace metals under amended irrigated fields. The study approach involved a pilot experimental (greenhouse) set-up of organo-mineral amended test plots/troughs (40 cm × 47 cm × 46 cm) planted with two common vegetable crops (Amaranthus hybridus and Abelmoschus esculentus) and irrigated with wastewater. In addition to the geochemical analyses of the primary un-amended and amended soils before planting as well as residual soils after harvesting, measurements of the physico-chemical parameters and chemical analyses of trace metals concentrations in irrigation leachates and harvested vegetable tissues were also undertaken following appropriate standard sample preparation and analytical methods.The results of the geochemical analyses carried out on irrigation leachate samples collected during the sprouting stage revealed that most of the analyzed trace metals in the collected leachates exhibited 2-10 folds depletion (except for Cu and Co with enrichment of about 1.5-3 folds) compared to the initial wastewater used for irrigation. A situation attributed to uptake/bioaccumulation of these metals and selective enrichment in the residual soils as well as to leaching by infiltrating irrigation water. Nonetheless, the observed higher trace elements concentrations in the second sets of leachates collected during harvesting stage compared to the first sets of leachates collected during the sprouting/vegetative stage is an indication of higher plant uptake during sprouting/vegetative stage or initial sorption/complexation of biosolids amendment before later vertical re-mobilization by infiltrating irrigation water.Although, virtually all of the analyzed metals exhibited elevated concentrations (2-173 ppm) in both A. hybridus and A. esculentus, a closer evaluation revealed 1.2-8.2 folds enrichment of Cr, Co, Ni, Cd, Cu, and Pb in A. esculentus compared to that of A. hybridus, an indication of the fact that phyto-accumulation of trace metal is plant-specific and dependent on physiological set-up. The overall evaluation had clearly demonstrated the potential danger of bioaccumulation of toxic trace metals under biosolid amended soils as well as impacts of irrigation-induced leaching on the shallow groundwater quality, while the need to evolve a sustainable agricultural practices is also highlighted.

Capsule

Organo-mineral amendment can lead to trace metal bioaccumulation (in plants) and irrigation-induced leaching to shallow groundwater system.     

Irrigated land retirement

Land retirement is ceasing irrigation withthe goal of reducing load, in general, ofdissolved constituents and, in particular,of trace elements, present in subsurfacedrainage generated from irrigated lands. Retirement is achieved through a process ofgoal setting, strategy development anddetermining effects, developing landselection criteria, implementation, andmonitoring. In this study, effects of landretirement are evaluated using hydrologic,soil and economic models as well as resultsfrom a field demonstration study. From themodeling and field monitoring, a process isdeveloped to meet the goals of a landretirement program in the San JoaquinValley of California.Potential negative effects listed for landretirement included loss of agriculturalproductivity, perhaps permanently, and lossof revenue to surrounding communities. Uncertainties included those associatedwith reuse of retired lands as wildlifehabitat, with retired-land maintenanceincluding dust control, with potentialpreservation of retired lands in reservefor future re-introduction to irrigated ordry-land agriculture, and withinstitutional changes concerning repaymentof federal and state water contracts. Benefits would accrue from economic returnto the landowner from the sale of property,the sale or lease of irrigation watersupply, the reduced cost of handlingdrainage, and allocation of freed-up waterto beneficial uses, and the reduced risk ofselenium exposure to fish and wildlife.A recommended sequential approach to selectand manage retired land is to identifyprimary objectives; formulate and implementarea-specific land retirement scenarios;measure biologic, hydrologic, soils andeconomic consequences in the short term andthe long term and manage and monitorretired lands based on dynamic biologic,hydrologic and soil conditions.