特大暴雨下不同土地利用类型坡面切沟发育特征

切沟侵蚀是黄土高原丘陵沟壑区水土流失的重要形式之一，然而极端暴雨条件下不同土地利用类型坡面切沟侵蚀研究还鲜见报道。该研究以陕北2017年"7·26"特大暴雨为例，研究了岔巴沟流域3种土地利用类型（农地、休闲地和撂荒地）坡面切沟发育形态特征及体积估算模型。结果表明：1）农地、休闲地和撂荒地切沟长度分布在20 m内的占比分别为55.6%、34.8%和44.8%；农地切沟平均深度为110 cm，分别比休闲地和撂荒地高18.3%、19.2%；农地和休闲地切沟平均宽深比分别为0.87和0.84，横断面呈"宽-浅型"，而撂荒地切沟呈"方型"（宽深比1.01）。2）撂荒地切沟侵蚀体积分别比农地和休闲地减少47.8%和28.3%，表明植被恢复有效地削弱了极端暴雨作用下的切沟侵蚀。3）农地切沟不同坡段侵蚀体积由高到低为下坡、上坡、中坡，而休闲地和撂荒地切沟侵蚀体积沿坡长方向呈递增趋势；3种土地利用类型切沟在上坡段的沟岸拓宽速率大于下切速率，中下坡则相反。4）农地、休闲地和撂荒地切沟侵蚀体积均与切沟长度、横断面面积呈极显著幂函数关系（P<0.001），横断面面积是切沟体积估算更为有效的参数。研究结果可为黄土高原丘陵沟壑区不同土地利用类型坡面切沟侵蚀体积估算及其防治提供重要依据。     

重庆市主城区街道地表物中重金属的污染特征

分析了重庆市主城区街道地表物的基本性质及As、Cd、Cr、Cu、Hg，Ni、Pb，Zn等元索的全置、模拟酸雨（pH4．5）的浸出量。结果表明：各功能区中街道地表物的自然组成均以中等粒径的为主；就元素而言，粒径越细对重金属的贡献率越高；就功能区而言．细粒径与中等粒径的颗粒对重金属贡献率较为接近。街道地表物呈碱性，有潜在的有机物污染。重庆市主城区街道地表物重金属元素含量有较大的差异，受人为活动干扰严重的重金属种类为Cr、Cd、Hg、Cu。内梅罗指数评价结果显示除Ni外，其他元素均有不同程度的污染，各功能区均受到重金属的严重污染。重庆市主城区街道地表物中的重金属只与其中的磷素含量显著正相关。     

重金属迁移与土壤性质的关系

Cu, Zn, Pb and Hg runoff from yellow limestone soil and purple soils and the relationships between the mobility of the heavy metals and the soil characteristics were studied in laboratory using a rainfall simulator. The results showed that the concentrations of soluble Zn in surface runoff were significantly negatively correlated with the contents of < 0.002 mm particles and CEC of the soils, indicating that Zn was mostly adsorbed by clays in the soils. The contents of Cu and Hg in surface runoff were positively related to their contents in the soils. The amounts of Cu, Zn, Pb and Hg removed by surface runoff were influenced by the amounts of soil and water losses and their contents in the soils, and were closely related to the contents of soil particles 1~0.02 mm in size.     

用稀悬液Wien效应测量法来研究重金属离子与水稻土的相互作用

Interactions of three heavy metal ions, Cu²⁺, Cd²⁺, and Pb²⁺, and, for comparison, Na⁺ with electrodialytic clay fractions (less than 2 μm in diameter) of four paddy soils as well as a yellow-brown soil as a control soil were evaluated based on measurements of the Wien effect in dilute suspensions with a clay concentration of 10 g kg^?1 in four nitrate solutions of 2 × 10^?4/z mol L^?1, where z is the cation valence, and a nitric acid solution of 3 × 10^?5 mol L^?1. Field strengths ranging from 15 to 230 kV cm^?1 were applied for measuring the electrical conductivities (ECs) of the suspensions. The mean free binding energies between the various cations and all of the soils determined from exchange equilibrium increased in the order: Na⁺ < Cd²⁺ < Cu²⁺ < Pb²⁺. In general, the ECs of the suspensions in the sodium nitrate solution were smaller than those of the suspensions in the heavy metal solutions because of the lower electrophoretic mobility of sodium compared to the divalent cations. In terms of relative electrical conductivity-field strength relationships, relative electrical conductivity (REC) of suspensions containing various cations at field strengths larger than about 50 kV cm^?1 were in the descending order: Na⁺ > Cu²⁺ > Cd²⁺ > Pb²⁺ for all tested soils. A characteristic parameter of the REC-field strength curves, ΔREC₂₀₀, REC at a field strength of 200 kV cm^?1 minus that at the local minimum of the concave segment of the REC-field strength curves, characterized the strength of adsorption of the cations stripped off by the applied strong electrical field, and for all soils the values of ΔREC₂₀₀ were generally in the order: Na⁺ < Cu²⁺ ≤ Cd²⁺ ≤ Pb²⁺.     

Clay dispersion and its relation to surface charge in a paddy soil of the Red River Delta,Vietnam

Dispersion is an important issue for clay leaching in soils. In paddy soils of the Red River Delta (RRD), flooding with fresh water and relatively high leaching rates can accelerate dispersion and the translocation of clay. For the clay fraction of the puddled horizon of a typical paddy soil of the RRD, the effect of various cations and anions as well as humic acid (HA) at different pH values on the surface charge (SC) were quantified and the dispersion properties were determined in test tubes and described by the C₅₀ value. In the <2 µm fraction, dominated by illite, the proportion of 2:1 vs. 1:1 clay minerals is 5:1. The organic‐C content of the clay fraction is 2.2%. Surface charge was found to be highly pH‐dependent. At pH 8 values of –32 and at pH 1 of –8 mmol_c kg^–1 were obtained. Complete dispersion was observed at pH > 4, where SC is > –18 mmol_c kg^–1. The flocculation efficiency of Ca strongly depends on the pH. At pH 4, the C₅₀ value is 0.33, 0.66 at pH 5, and 0.90 mmol L^–1 at pH 6. At pH 6, close to realistic conditions of paddy soils, the effect of divalent cations on the SC and flocculation decreases in the order: Pb > Cu > Cd > Fe^II > Zn > Ca > Mn^II > Mg; Fe^II was found to have a slightly stronger effect on flocculation than Ca. An increase in concentrations of Ca, Mn^II, and Mg from 0 to 1 mmol L^–1 resulted in a change in SC from –25 to approx. –15 mmol_c kg^–1. In comparison, the divalent heavy‐metal cations Pb, Cu, Cd, and Zn were found to neutralize the SC more effectively. At a Pb concentration of 1 mmol L^–1, the SC is –2 mmol_c kg^–1. From pH 3 to 5, the dispersion of the clay fraction is facilitated rather by SO than by Cl^–, which can be explained by the higher affinity of SO to the positively charged sites. With an increase of the amount of HA added, the SC continuously shifts to more negative values, and higher concentrations of cations are needed for flocculation. At pH 3, where flocculation is usually observed, the presence of HA at a concentration of 40 mg L^–1 resulted in a dispersion of the clay fraction. While high anion concentrations and the presence of HA counteract flocculation by making the SC more negative, Fe^II and Ca (C₅₀ at pH 6 = 0.8 and 0.9 mmol L^–1, respectively) are the main factors for the flocculation of the clay fraction. For Fe^II and Ca, the most common cations in soil solution, the C₅₀ values were found to be relatively close together at pH 4, 5, and 6, respectively. Depending on the specific mineralogical composition of the clay fraction, SC is a suitable measure for the determination of dispersion properties and for the development of methods to keep clay particles in the soil in the flocculated state.     

北京地区基本农田土壤环境质量分析与评价

对北京地区基本农田的土壤环境质量和污染状况进行了系统的调研，并对采样区农田土壤的环境质量按照国家标准进行了单因子评价和综合评价。结果表明，重金属的污染程度依次为Cd > Cu > As > Pb > Cr > Hg，Cd，Cu，As高于北京市土壤重金属背景值，Pb、Cr接近或略低于背景值，相比较而言，Cd污染为北京市基本农田中的主要污染元素。土壤中的农药残留的主要成分为滴滴涕。只有1处农田的Cd含量超过了国家二级标准限量，其余指标均低于二级标准。整体而言，北京地区的基本农田土壤环境质量属于清洁和安全范围，符合发展都市型现代农业的要求。     

四种草本植物对铅锌尾矿土壤重金属的抗性与吸收特性研究

盆栽试验的结果表明,高羊茅、早熟禾、黑麦草和紫花苜蓿在铅锌尾矿土壤或处理的尾矿土壤上都能生长,但在处理土壤上生长的植物长势明显优于对照,其中紫花苜蓿的生物量所受影响比其他几种草本植物更大,说明其重金属抗性低于其他几种植物.单位面积上4种植物体内重金属含量均为Zn>Pb>Cu>Cd,但每种植物对Cd、Pb、Zn和Cu的吸收浓度和分布均不相同,一般为根系浓度大于茎叶.加入改良剂和有机肥(菜枯)使生长在铅锌尾矿污染土壤上的4种草本植物生物量显著增加,植物体中的Cd、Pb和Zn元素浓度下降,但Cu元素浓度反而上升,结果单位面积上4种草本植物吸收各重金属元素的量均有所增加,可见利用改良措施与草本植物相结合的方法来修复重金属污染土壤具有可行性.     

杨梅根瘤Frankia菌对重金属的抗性

采用生长抑制分析法研究从杨梅根瘤分离的10个Frankia菌菌株对9种重金属元素的抗性。一般所有供试菌株对Hg^2 和Ag^ 敏感，大部分菌株对Pb^2 (5～10mmol／L)、Cr2O7^2-(5～10mmol／L)、AsO2^-(5～10mmol／L)不敏感，部分菌株对Cu^2 、Co^2 、Ni^2 和Cd^2 也不敏感(MICs≥O．5mmol／L，有的菌株达到5mmol／L)。菌株之间对各种重金属的抗性存在较大差异，其中菌株Mda21对所有供试重金属都敏感，而菌株Mpall几乎能抗所有供试重金属，且有几个菌株能同时抗多种重金属。低浓度铅能促进抗铅菌株的生长，而高浓度铅对其生长有一定的抑制；抗铅菌株在含铅的培养基中仍具有固氮酶活性，在一定浓度范围内，随铅离子浓度的升高，固氮酶活性有所增强。Frankia菌的抗铅机理可能是其具有结合或螯合铅离子作用，对其他重金属的抗性机制尚不清楚。     

湿地生态系统对污水中重金属的修复作用

湿地污水处理技术的研究是国内外众多学者关注的热点之一。综合国内外在污水湿地处理技术方面的研究成果,对湿地生态系统及其各组成要素对重金属污染的修复作用及其作用机理进行了讨论,针对目前利用湿地生态系统进行重金属污染废水修复过程中应注意的几个问题进行了探讨,并对今后研究发展方向进行了评述。     

青海省玉树州高原暴雨型泥石流形成机制——以称多县拉隆沟泥石流为例

[目的]对青海省玉树州高原暴雨型泥石流形成机制进行研究,旨在为此类泥石流灾害防治及风险减缓提供依据。[方法]以青海省玉树州称多县拉隆沟暴雨型泥石流为例,通过实地调查对其形成因素及形成机制进行研究。[结果]该泥石流主沟道长约3km,流域面积5.25km~2,纵坡比降212‰,高差约600m。物源区发育滑坡方量约为6.50×104 m~3,流域内冲出泥石流物质共约8.5×104 m~3,沟道内物源补给量2.0×104 m~3。[结论]青海省玉树州高原暴雨型泥石流的启动模式可总结为:滑坡—物源形成—固体物质起动—沟道侵蚀—泥石流形成。