土壤水分资源生产能力及其利用研究

采用人工控制土壤贮水量，在陕西关中气候条件下，研究作物土壤水分生产能力结果表明：土壤水分生产能力小麦最高为１７．５９ｋｇ／（ｈm₂·ｍｍ），谷子１１．６１ｋｇ／（ｈm₂·ｍｍ），豌豆１０．３３ｋｇ／（ｈm₂·ｍｍ），油菜１０．６ｋｇ／（ｈm₂·ｍｍ）；获得一定籽粒产量的最低土壤水分临界值约为：小麦１６０ｍｍ，豌豆１５０ｍｍ，谷子和油菜３００ｍｍ，土壤水分超过此临界值后，增加水分，作物产量大幅度提高，但当水分超过一定量（豌豆３００ｍｍ，小麦４００ｍｍ，谷子５００ｍｍ，油菜６５０ｍｍ时），产量则渐趋于稳定；低供水多施肥和高供水少施肥土壤水分的无谓消耗增加，不利于提高土壤水分的生产能力，必须量水施肥，才能提高土壤水分生产能力。     

应用地质累积指数评价攀枝花地区土壤重金属污染

应用地质累积指数对攀枝花地区昔格达组粘土中重金属污染进行了评价研究。结果表明，各重金属元素污染较严重的地区分布在宝顶煤矿、太平煤矿、攀钢冶钢厂、攀钢矿山、尾矿坝等工矿区，污染较轻微的地区分布在红格、新九等农业区。各元素的污染程度上看，该区As和Cu污染较重，Cd,Pb,Zn次之，而Cr污染最轻微。     

含铬废渣的综合利用

着重介绍了重庆东风化工厂铬渣综合治理的成效。其中包括该厂已成功应用于工业化生产的铬渣作玻璃着色剂，钙镁磷肥助熔剂，炼铁烧结熔剂等利用途径及其还原解毒机理，以及在水泥等建材方面的应用尝试。     

内蒙古癌死亡率与土壤环境中化学元素的关系

利用中国癌死亡率与土壤环境中化学元素的相关性研究成果，研究了内蒙古癌死亡率与土壤环境中化学元素：As、Cd、Co、Cu、Hg、Mn、Ni、Pb、Se、V、Li、Na、K、Rb、Cs、Mg、Ca、Sr、Ba、B、Al、Ga、In、Tl、Sc、Y、La、Ce、Pr、Nd、Tb、Dy、Ho、Er、Tm、Yb、Lu、Th、U、Sn、Ti、Zr、Hf、Sb、Bi、Ta、Te、Mo、W、Br、I、Fe等52个元素含量的关系。     

重庆市近郊蔬菜基地土壤和蔬菜中重金属的质量现状

通过对重庆市近郊蔬菜基地土壤和蔬菜中重金属的监测和评价得出：重庆市近郊蔬菜基地部分土壤受到 Ｃｄ和Ｈｇ的污染；部分蔬菜受到Ｐｂ和Ｃｄ的污染。     

煤飞灰中铬铁元素的形态分析研究

用连续提取法将煤飞灰中的铬、铁元素依结合态区分为水溶态,交换态,表面氧化物和碳酸结合态,铁锰氧化物结合态,金属有机物和硫化物结合态,磁性四氧化三铁结合态和硅铝酸盐矿物态,用原子吸收法及X-衍射分析进行测定。并对煤飞灰化学形态分布进行了讨论。     

土著微生物修复铬(Ⅵ)污染土壤的条件实验研究

根据铬(Ⅵ)污染土壤中筛选出的土著微生物初步解毒实验结果,将土著菌种制成六价铬还原菌剂,通过时间、温度、菌量、pH值、有机质用量等单因素条件实验,发现温度和有机质含量对六价铬还原影响显著,在上述各项较佳条件下施用该菌剂1个月后,对于浸出液六价铬浓度范围从10-55mg/L的污染土壤,六价铬的还原效果都可达到90%以上,高于化学法,这说明该菌剂可有效应用于六价铬土壤的生物修复。     

显像管玻壳铅尘污染特性的研究

以石家庄市显像管玻壳厂排放的铅尘为研究对象，通过在该玻壳厂周围土壤布点采样，较系统地研究了铅尘在大气和周围土壤中的迁移和转化规律，研究表明，用高斯模式能成功地预测铅尘在大气中的迁移扩散规律，玻壳厂周围土壤表层铅含量较大值出现在当地年主导风向（SSE，N）下风向，铅在土壤中的分布主要集中在0－20cm的耕作层，在20－40cm深度范围内，铅含量呈下降趋势，最大降幅达50％。     

Alteration in Rhizosphere Soil Properties of Afforested <Emphasis Type="Italic">Rhamnus lycioides</Emphasis> Seedlings in Short-Term Response to Mycorrhizal Inoculation with <Emphasis Type="Italic">Glomus intraradices</Emphasis> and Organic Amendment

The reestablisment of autochthonous plant species is an essential strategy for recovering degraded areas under semiarid conditions. A field experiment was carried out to assess the short-term effect of two reafforestation methods involving mycorrhizal inoculation and compost addition on soil quality parameters and Rhamnus lycioides seedling growth. The nutrient content (NPK) and enzymatic activities (dehydrogenase, urease, protease-BAA, acid phosphatase and β-glucosidase) increased and bulk density decreased in the rhizosphere soil with the organic amendment. Biomass C of rhizosphere soil increased by at least 240% with respect to the control soil after mycorrhizal inoculation and the combination of compost addition + mycorrhizal inoculation. Both mycorrhizal inoculation and composted organic residue addition increased R. lycioides seedling growth in the same proportion. In the short term, we conclude that the application of both reafforestation methods not only enhances the establishment of R. lycioides seedlings, but also improves soil quality.     

Effect of soil solids concentration in batch tests on the partition coefficients of organic pollutants in landfill liner-soil materials

 The effect of the soil solids concentration in batch tests on the measured values of the partition coefficient (K _p) of organic pollutants in landfill liner-soil material was investigated. Since this study was based on the results of batch and column tests conducted independently, there were limitations to the conclusions derived. The organic compounds tested were benzene, methylene chloride, toluene, trichloroethylene, and p-xylene. The results of this study showed that as soil solids concentrations increased, the measured K _p values of these organic compounds strongly decreased. The observed values of K _p stabilized when the soil solids concentration was above a certain value. Typical K _p values obtained from batch tests conducted under high soil solids concentrations were close to those obtained from column tests. It was concluded that the K _p values of organic compounds measured under low soil solids concentrations, i.e., less than 100 g/l, may not correctly simulate the field situation. Consequently, the values of K _p obtained with low soil solids concentrations can result in an overestimation of the retardation factor of the landfill liner material. Received: March 14, 2002 / Accepted: August 25, 2002