新疆农田土壤有机质含量及组成特征

目前新疆农田土壤有机质含量在5．30～24．21g／kg之间，平均14．65g／kg，与第二次土壤普查相比，新疆农田土壤有机质含量呈上升趋势；胡敏素碳含量占到有机质碳量的53％～70％，平均61％，腐殖酸碳量只占39％。     

利用人工增雨为农田需水服务的信息系统框架

针对我国北方地区水资源严重短缺、农田水分供需矛盾日益尖锐的现状 ,提出了首选人工增雨为农田补水的思路 ,并初步设计了一个利用人工增雨为农田需水服务的农田需水信息系统框架。     

格式塔知觉组织原则在废弃铁路景观营造中的应用

废弃铁路是一种宝贵的精神财富,对其进行改造与再利用具有突出的现实价值。格式塔心理学在景观空间设计中具有独到的优势。以设计实例阐述格式塔知觉组织原则在废弃铁路景观营造中的应用,以期为废弃铁路景观营造理论研究提供参考。     

黄河三角洲台田间渗水池塘的水质变动规律分析

以黄河三角洲地区台田间渗水池塘为研究对象,分析了渗水池塘的水质因子变动规律。结果表明:不同池塘间水质因子差异较大,但均表现出水体盐度较高、氮磷等营养物质含量较低、K+离子含量相对较低、Ca2+离子和Na+离子含量相对较高及K+/Na+显著低于正常海水等特点。结果说明,黄河三角洲地区台田间渗水池塘的水质条件不适合直接进行水产养殖,应对水质调整后才可做养殖之用。     

县域耕地土壤养分时空变异特征研究

土壤养分空间变异研究是精准农业实施的前提,对提高粮食作物单位面积产量和保护农业生态环境具有重要作用。为掌握陕西渭北旱塬区土壤养分时空变异规律,综合空间自相关和重心模型,分析1980—2007年、2007—2017年白水县耕地土壤有机质(SOM)、速效磷(AP)和速效钾(AK)的时空变异特征。结果表明：(1)研究区土壤SOM的平均含量分别增加了1.29、3.22 g·kg^-1,AP的平均含量分别增加了6.89、24.45 mg·kg^-1,仅有AK的平均含量呈现出先减少后增加的趋势。(2)三期耕地土壤养分的变异系数范围为30.2%～90.8%,属于中等变异。1980—2017年,耕地土壤SOM、AP和AK的全局Moran’s I指数均降低,空间结构性减弱,随机因素作用增强。(3)土壤SOM、AP和AK含量均有不同程度的增加,土壤SOM含量总体呈北低南高分布,土壤AP、AK含量分布情况较为一致,呈东高西低。(4)土壤SOM含量重心在东南方向发生偏移,AP、AK含量重心在东北方向发生偏移。土壤养分标准差椭圆空间分布格局同研究区分布方向一致,转角呈现“...     

Metal contamination from open-cast copper and sulphur mining in southeast Ireland

The metal content was determined in soil and vegetation around the eastern zone of the disused sulphur and copper mines at Avoca (southeast Ireland). A 250 m × 250 m grid survey was conducted covering a total area of 4 km². The mining belt was in the centre of the investigated site and was sampled separately. Iron, Zn, Cu and Cd concentrations in soil and plant material were determined, in addition to soil organic matter content and soil pH. Soil samples taken from the spoil showed elevated Cu and Cd concentrations, and low soil pH and organic matter content. At least 50 per cent of the agricultural sites examined around the East Avoca Mine showed elevated soil Cu and Cd concentrations, whereas Zn and Fe soil concentrations were within the range for unpolluted soils. None of the vegetation analysed had elevated Zn, Cd, Fe or Cu concentrations. Overall there was no indication of serious metal contamination in either soils or vegetation surrounding the mine in spite of extensive dust deposition during open-pit mining activity 15–30 years ago. However, a plume of elevated Cu in the soil was identified, which originated from a large spoil heap and had been spread for some 2·0 km by the prevailing wind.     

INTEGRATED CROP-LIVESTOCK SYSTEMS: LESSONS FROM NEW YORK,BRITISH COLUMBIA,AND THE SOUTH-EASTERN UNITED STATES

• Livestock production in North America has moved to fewer farms with greater inventories • Land application of livestock manures is a preferred nutrient recycling strategy • Confined animal feeding operations have challenges to utilize livestock manure sustainably • Integration of livestock and cropping systems is possible on a farm or among farms • Nutrient balance is needed for environmental sustainability Livestock production in the United States (US) and Canada is diverse, but shows a common trend in most livestock sectors toward fewer farms producing the majority of animal products despite a large number of farms still small in production scale. The migration to larger and more concentrated animal feeding operations in beef finishing and poultry, swine, and dairy production allows processors to streamline supplies to meet market demand for abundant, low-cost livestock products, whether that be for packaged meat, dairy products, or eggs. With concentration of livestock operations comes the challenge of managing manures. When sufficient land is available and nutrients are needed, livestock manure is an excellent nutrient source and land application is the preferred method of recycling this resource. However, when livestock production is constrained in a geographical area and animal densities are high, manure may become an environmental liability with potentially greater risk for runoff and leaching of nutrients, emission of odors, ammonia, and greenhouse gases, and release to the environment of pathogens and chemicals of emerging concern. Addressing these challenges now and into the future requires learning from mistakes and adopting successful approaches. We describe different levels of integration between livestock and crop producers in New York, British Columbia, and the south-eastern US as learning opportunities to improve economic and environmental sustainability. Examples show that effective solutions should recognize (1) manure has value and is not just a cost, (2) farmers, farm advisors, extension educators, nutrient management planners, crop advisors, nutritionists, state agency personnel, regulators, and university researchers need to be active participants in development of solutions, and (3) change to a sustainable future requires a combination of government regulation and outcome-based incentives.     

不同降水年型黄土高原半干旱撂荒草地水分收支特征

以黄土高原六道沟流域半干旱撂荒草地为研究对象,根据2014—2017年连续观测得到的降水量(P)、蒸散量(ET)、土壤贮水量(S)和植被组成等数据,研究了不同降水年型下撂荒草地的水分收支特征。结果显示:(1)观测前期平水年下0—50cm土层土壤贮水量呈现缓慢下降趋势,以第三年的一场暴雨(109.60mm/d)为分界,后期土壤贮水量总体增加,但波动幅度大增,受蒸散量增加的影响,土壤水分消耗明显;(2)年总蒸散量呈逐年升高的趋势,在平水年下,地表蒸散年际变化主要受气候条件影响,丰水年下,地上生物量的作用明显;(3)水分收支呈现季节性,2—6月为撂荒草地的缺水期,7月—次年1月为丰水期,四年观测结果显示草地处于总体水分亏缺状态(总亏缺165.60mm),存在对深层土壤水(50cm以下)的大量消耗。研究结果表明:撂荒草地水分的持续损失是导致撂荒草地发生演替的重要原因,演替过程中植物深层土壤水的大量消耗可能会导致形成的次生草地土壤水分条件更差,需要加强人为干预措施,防止草地再次退化。     

生产建设项目弃渣(土)场水土流失特征与防治措施

生产建设项目弃渣场种类繁多,弃渣成分、结构复杂,各类弃渣场的侵蚀形式、机制不尽相同,不易实施适宜的水土保持措施,致使弃渣场水土流失十分严重。通过介绍弃渣场存在的各类土壤侵蚀型式、归纳土壤侵蚀类型、分析岩土侵蚀特点,指出影响弃渣场土壤侵蚀的主要因素有排弃方式、组成物质、坡面以及堆积时间等。结合保证弃渣场安全稳定、恢复土地生产力的弃渣场水土流失防治目标,分析现有水土保持措施特点,提出健全弃渣场水土流失防治措施体系的建议,为弃渣场的水土流失防治提供科学依据。     

某废弃铅冶炼企业周边土壤和蔬菜的铅含量及分布特征

为了解并掌握废弃铅冶炼企业对周边环境的影响程度及范围,在湖北某废弃铅冶炼企业周边按照扇形布点法采集表层土壤样品102个、蔬菜样品69个,分别采用石墨炉原子吸收分光光度法和电感耦合等离子体原子发射光谱法检测样品铅含量,分析土壤环境和蔬菜样品铅含量的空间分布。结果表明,废弃铅冶炼企业周边土壤铅含量的几何均数为39.8 mg·kg~(-1),高于湖北省土壤背景值(26.7 mg·kg~(-1))。土壤铅的地质累积指数平均值为0.09,其中,36.4%的土壤采样点地质累积指数大于0。距离废弃铅冶炼企业500、1 000 m和1 500 m采样点的地质累积指数平均值分别为2.11、0.61和0.33,而2 000 m及其以外土壤铅的地质累积指数平均值均小于0。白菜、萝卜和葱铅含量的超标率分别为24.0%、36.0%和6.3%,其内梅罗综合指数分别为8.12、4.38和1.26。废弃铅冶炼企业周边土壤和蔬菜在500 m范围内污染最为严重,土壤在500~2 000 m之间呈轻度或中度污染;白菜、萝卜和葱受到铅污染的最大影响距离分别在500~1 000、1 000~1 500 m和500~1 000 m之间,其分别呈现重度、重度和轻度污染,且在企业周边呈现明显的污染和富集特征。