南充市郊蔬菜基地土壤重金属污染状况调查与评价

分析了南充市郊蔬菜地土壤中的pH、有机质、N、P、K及重金属（Pb、Cd、As、Ag、Cr）含量，并用单项污染指数和综合污染指数评价方法，对土壤重金属污染状况进行评价。结果表明该地区多数蔬菜地未受到污染，属于清洁安全，但是仍然有一部分地区受到污染，从综合污染指数看，部分超过了3级水平，处于轻污染。     

当代河流系统研究中稳定性同位素的应用

对天然存在的稳定碳、氮同位素在河流系统中的有机物质（POM和DOM）来源、转换、运移规律、与沿岸生态系统的关系、河口区不同来源颗粒有机质的混合过程、河流系统中富营养的污染来源和土壤中的微生物过程、系统中的营养行为和食物来源途径以及河流有机物质在陆架上的分配、积累和运移规律的应用研究作了较为系统的论述。     

川西北高寒草地沙化土壤特征及治理模式探讨——以阿坝州红原县为例

通过对川西北高寒草地不同类型的沙化样地0—10cm,10～20cm和20～30cm土壤有机质、pH和含水量进行分析。结果表明：（1）随着沙化程度加重,土壤有机质含量和土壤含水量明显降低;（2）随着土层深度增加,土壤有机质含量降低;未沙化、轻度沙化样地的土壤含水量随土层深度增加而降低,重度沙化样地则相反;（3）中度和重度沙化样地土壤pH约7．0,未沙化和轻度沙化pH值在6．5左右;沙地土壤有机质与pH值呈显著负相关关系,沙化土壤有机碳与水分损失是一个正反馈。鉴于川西高寒草地特殊环境,探讨了选用适宜的多年生高原药用植物或者其他高价值资源植物作为固沙材料,将治沙与经济发展相结合,建立高寒沙化草地治理模式。     

土壤对钻井废水中有机污染物吸附作用研究

分析了钻井废水中有机污染物在土壤中吸附的机理,对吸附量和有机负荷的关系进行了阐述;针对钻井废水有机污染物在土壤中的吸附和解吸过程进行了实验研究。实验表明:钻井废水中有机污染物在土壤中的吸附量与土壤有机负荷的关系符合初始质量等温线;土壤中天然有机质含量越高,对钻井废水中有机污染物吸附能力越强;土壤对钻井废水中有机污染物具有一定的持久吸附作用;天然有机质含量越高的土壤对钻井废水中有机污染物的持久吸附能力越强。     

高氯低COD废水中COD的测定

以某污水厂的高氯低COD生化出水为研究对象,探讨了硫酸汞加入量、K2Cr2O7溶液浓度、反应酸度、取水样量等参数对COD测定的影响,探讨消除该厂Cl-干扰最简单有效方法,结果表明:控制硫酸汞与氯离子比为15∶1(质量比)、K2Cr2O7浓度为0.18 mol/L、水样稀释0.75倍、Ag2SO4-H2SO4加入量为28mL,皆可有效减少氯离子的干扰。该方法相对氯气校正法,操作简单、准确可靠。     

不同经营措施对杉木人工林土壤碳库的影响

森林土壤有机碳在陆地生态系统碳循环中发挥着关键作用。以我国亚热带杉木人工林为研究对象,以常绿阔叶林为对照,分析比较了不同经营措施对土壤碳矿化、微生物特征、碳库管理指数的影响。结果表明,与连栽杉木纯林相比,杉木火力楠混交模式和轮栽模式均显著增加了土壤微生物量碳含量、土壤微生物熵、易氧化有机碳和碳库管理指数,提高了土壤微生物对底物的利用效率,土壤易氧化有机碳可作为反映土壤碳库质量的有效指标。     

氮磷养分配施对土壤碳氮特征及叶用枸杞生长的影响

通过田间定位试验,探讨水肥一体化技术下不同养分配施措施对土壤碳氮特征及叶用枸杞生长的影响,筛选出适合该区域叶用枸杞高效可持续生产管理模式。结果表明,随着养分浓度的增大,各层次土壤中有机碳含量整体呈现增加趋势,土壤中易氧化态有机碳及土壤碳库管理指数(CPMI)变化趋势与土壤有机碳类似。与对照相比,水肥一体化施肥增加了0～20cm和20～40cm土层硝态氮含量;但随着土层深入,土壤剖面硝态氮含量整体呈现出逐渐降低的趋势,而对照处理硝态氮呈现增加趋势,40～60cm土层硝态氮含量达最大。在水肥一体化N2P3处理下,叶用枸杞叶芽产量最高。研究确定,N2P3处理的"少量多次"水肥一体化灌溉模式,是叶用枸杞生产区最佳的农业高效高产的水肥生产管理模式。     

新疆小城镇生活污水生态利用技术模式研究——以鄯善县生活污水生态利用为例

本研究以吐鲁番地区鄯善县氧化塘处理后出水灌溉生态林为案例,分析新疆小城镇生活污水生态利用可行性。选择3个示范点,分别对0.2 m、0.4 m、0.6 m、0.8 m、1.0 m五个深度生态利用前后土壤中有机碳、氨氮、硝酸盐氮、亚硝酸盐氮、盐分等污染物浓度进行监测,研究土壤生态系统对生活污水处理效果。研究结果表明土壤的p H、全盐量、钠离子、氯离子灌溉区较对照区有均有降低,降幅分别为1.9%~6.0%、71.43%~95.71%、97.70%~99.53%、95.76%~98.99%。土壤中的有机质、全氮、全磷含量均较非灌区有所增加,且随土层深度的增加其含量增加量逐渐减少,并呈现稳定趋势。研究区从2008-11月投入使用至今,区域地下水水质无明显变化。     

土壤样品中TOC的测定浅析

环境土壤中的TOC(总有机碳)含量是反应土壤有机污染的一个重要指标。文章描述了应用总有机碳测定仪和固体进样装置对土壤中TOC含量的测定方法,建立TC(总碳)和IC(无机碳)测定标准曲线,利用差减法计算出TOC含量。实验结果表明,利用该方法建立的标准曲线线性良好,多次测定样品的相对标准偏差较小,该方法精密度、准确度较高。     

水淬渣处理废水的研究进展

水淬渣的微观结构特殊,比表面积大,表面能高。国内外研究表明,水淬渣吸附去除废水中的Cu2+、Zn2+、Ni2+、Pb2+、Cr6+、As3+及磷等效果良好,而且对废水中的COD、大分子有机物、油类、苯酚等也有比较好的去除率;并研究了吸附去除的机理,对水淬渣在水处理领域的应用起到了推动作用。     

混凝沉淀SBR活性炭过滤处理垃圾渗滤液

采用沉淀-SBR-活性炭过滤复合工艺对城市垃圾渗滤液进行处理，确定混凝、SBR和活性炭过滤的最佳参数。结果表明，当进水CODcr 2500mg／L、氨氮在900mg／L的条件下，经该系统处理后，出水CODcr均在300mg/L以下，氨氮在20mg/L以下。CODcr去除率达90％以上，氨氮去除率达98％以上，达到去除有机物和氨氮的较好效果。     

In situ reduction of chromium(VI) in heavily contaminated soils through organic carbon amendment

Chromium has become an important soil contaminant at many sites, and facilitating in situ reduction of toxic Cr(VI) to nontoxic Cr(III) is becoming an attractive remediation strategy. Acceleration of Cr(VI) reduction in soils by addition of organic carbon was tested in columns pretreated with solutions containing 1000 and 10 000 mg L(-1) Cr(VI) to evaluate potential in situ remediation of highly contaminated soils. Solutions containing 0,800, or 4000 mg L(-1) organic carbon in the form of tryptic soy broth or lactate were diffused into the Cr(VI)-contaminated soils. Changes in Cr oxidation state were monitored through periodic micro-XANES analyses of soil columns. Effective first-order reduction rate constants ranged from 1.4 x 10(-8) to 1.5 x 10(-7) s(-1), with higher values obtained for lower levels of initial Cr(VI) and higher levels of organic carbon. Comparisons with sterile soils showed that microbially dependent processes were largely responsible for Cr(VI) reduction, except in the soils initially exposed to 10 000 mg L(-1) Cr(VI) solutions that receive little (800 mg L(-1)) or no organic carbon. However, the microbial populations (< or = 2.1 x 10(5) g(-1)) in the viable soils are probably too low for direct enzymatic Cr(VI) reduction to be important. Thus, synergistic effects sustained in whole soil systems may have accounted for most of the observed reduction. These results show that acceleration of in situ Cr(VI) reduction with addition of organic carbon is possible in even heavily contaminated soils and suggest that microbially dependent reduction pathways can be dominant.     

Light-catalyzed chromium(VI) reduction by organic compounds and soil minerals

Detoxification of Cr(VI) through reduction has been considered an effective method for reclaiming Cr-contaminated soil, sediment, and waste water. Organic matter is widely distributed in soil and aquatic systems; however, low Cr(VI) reduction rates inhibit the adoption of Cr reduction technologies by industry. Scientists have been aware of Cr(VI) reduction catalyzed by soil minerals; however, most of the studies focused on using semiconductors as catalysts with UV irradiation to accelerate the redox reactions. The objective of this study was to evaluate the rates of Cr(VI) reduction by fluorescence light in the presence of organic materials with or without specific soil minerals. Experimental results showed that dissolved organic compounds reduced Cr(VI) slowly under laboratory light; however, Cr(VI) reduction was greatly enhanced when growth chamber light was applied. Low photon flux (i.e., laboratory light) only enhanced Cr(VI) reduction by organics when Fe(III) was also present, because the Fe(II)-Fe(III) redox couple accelerated electron transfer and decreased electrostatic repulsion between reactants. Laboratory light was required to initiate Cr(VI) reduction catalyzed by TiO2; nonetheless, light-catalyzed Cr(VI) reduction by smectite and ferrihydrite could occur only when greater light energy was provided with a growth chamber light. Our results suggest a potential pathway for Cr(VI) reduction using naturally occurring organic compounds and colloids in acidic water systems or in surface soils when light is available.     

The influence of biochar and black carbon on reduction and bioavailability of chromate in soils

The widespread use of chromium (Cr) has a deleterious impact on the environment. A number of pathways, both biotic and abiotic in character, determine the fate and speciation of Cr in soils. Chromium exists in two predominant species in the environment: trivalent [(Cr(III)] and hexavalent [Cr(VI)]. Of these two forms, Cr(III) is nontoxic and is strongly bound to soil particles, whereas Cr(VI) is more toxic and soluble and readily leaches into groundwater. The toxicity of Cr(VI) can be mitigated by reducing it to Cr(III) species. The objective of this study was to examine the effect of organic carbon sources on the reduction, microbial respiration, and phytoavailability of Cr(VI) in soils. Organic carbon sources, such as black carbon (BC) and biochar, were tested for their potential in reducing Cr(VI) in acidic and alkaline contaminated soils. An alkaline soil was selected to monitor the phytotoxicity of Cr(VI) in sunflower plant. Our results showed that using BC resulted in greater reduction of Cr(VI) in soils compared with biochar. This is attributed to the differences in dissolved organic carbon and functional groups that provide electrons for the reduction of Cr(VI). When increasing levels of Cr were added to soils, both microbial respiration and plant growth decreased. The application of BC was more effective than biochar in increasing the microbial population and in mitigating the phytotoxicity of Cr(VI). The net benefit of BC emerged as an increase in plant biomass and a decrease in Cr concentration in plant tissue. Consequently, it was concluded that BC is a potential reducing amendment in mitigating Cr(VI) toxicity in soil and plants.     

Combination effect of light and toxicity in algal tests

The sensitivity of Scenedesmus subspicatus against potassium dichromate is positively correlated to the photon flux density during the algal growth inhibition test. Low photon flux densities led to significantly reduced maximum effects and higher EC50 levels. To improve the testing of colored substances, we distinguished between the toxic effect (chemical part, represented by potassium dichromate) and the shading effect (physical part, simulated by reduced light intensities during the test) of a hypothetical light absorbing substance. The contribution of these single effects to the total inhibition varied greatly. At high concentrations of potassium dichromate (1.6 and 3.2 mg L(-1)) the physical part never exceeded 25% of the total inhibition, not even at strongest light reduction, while at low concentrations (0.2 and 0.4 mg L(-1)) the physical effect became more prominent when halving the amount of available light. Further, the combination effect of the chemical and the physical effect could be calculated well only by using the concept of independent action. Thus, if chemical and physical effects are measured in combination, as is the case in tests with dye-stuffs, the current test protocol for the algal growth inhibition test may lead to incorrect estimations of the toxic potential.     

Urban soil quality of Raipur,Chhattisgarh, India

Soil quality in urban areas in India is degraded due to multiple anthropogenic activities. The objectives of this work are to determine the concentration variations, toxicity, and sources of carbons, metals, and ions in the surface soil of Raipur, the industrialized capital city of Chhattisgarh state, India. High concentrations of Al, K, Ca, Ti, Fe, and elemental carbon (EC) were registered. Relatively lower concentrations of V, Cr, Mn, Ni, Cu, Zn, Sr, Ba, Pb, organic carbon (OC), and carbonate carbon (CC), as well as ions (viz. F^–, Cl^–, NO₃^–, SO₄^2–, Na⁺, K⁺, Mg²⁺, and Ca²⁺), were also recorded. EC was found to be one of the major pollutants, although enrichment factors pointed to high contamination with SO₄^2–, K⁺, Mg²⁺_, Cr, Mn, and Pb; and extreme contamination with NO₃^– and Ca²⁺. The spatial and temporal variations, enrichment factors, toxicity, and sources of the chemical species detected in the soil are discussed.     

Effects of organic amendments on the reduction and phytoavailability of chromate in mineral soil

In this study, seven organic amendments (biosolid compost, farm yard manure, fish manure, horse manure, spent mushroom, pig manure, and poultry manure) were investigated for their effects on the reduction of hexavalent chromium [chromate, Cr(VI)] in a mineral soil (Manawatu sandy soil) low in organic matter content. Addition of organic amendments enhanced the rate of reduction of Cr(VI) to Cr(III) in the soil. At the same level of total organic carbon addition, there was a significant difference in the extent of Cr(VI) reduction among the soils treated with organic amendments. There was, however, a significant positive linear relationship between the extent of Cr(VI) reduction and the amount of dissolved organic carbon in the soil. The effect of biosolid compost on the uptake of Cr(VI) from the soil, treated with various levels of Cr(VI) (0-1200 mg Cr kg(-1) soil), was examined with mustard (Brassica juncea L.) plants. Increasing addition of Cr(VI) increased Cr concentration in plants, resulting in decreased plant growth (i.e., phytotoxicity). Addition of the biosolid compost was effective in reducing the phytotoxicity of Cr(VI). The redistribution of Cr(VI) in various soil components was evaluated by a sequential fractionation scheme. In the unamended soil, the concentration of Cr was higher in the organic-bound, oxide-bound, and residual fractions than in the soluble and exchangeable fractions. Addition of organic amendments also decreased the concentration of the soluble and exchangeable fractions but especially increased the organic-bound fraction in soil.     

利用造纸黑液回收电镀废液中铬的研究

本文报道了利用造纸黑液回收电镀废液中铬的方法，阐明了造纸黑液中所含有还原性物质与Ｃｒ＾６＋的反应机理；讨论了进行反应的最佳条件以及采用这一方法对废液的治理效果。     

人工沸石对Cr(Ⅲ)的吸脱附的实验研究

采用单变量法研究了人工沸石对Cr3+的最佳吸附粒径、最佳吸附反应条件和吸附动力学。结果表明,在Cr3+初始浓度为20mg/L、沸石投放量为10g/L时,最佳粒径为80目;在Cr3+初始浓度为50mg/L、沸石投放量为10g/L时,最佳振荡时间为70min;Cr3+浓度在20～70mg/L范围内时,人工沸石饱和吸附量随Cr3+的初始浓度增加而增加,二者近似于指数关系;人工沸石吸附Cr3+的过程主要为化学吸附,受表面扩散和颗粒内扩散过程控制。脱附实验表明洗脱性价比最佳的洗脱剂(NaCl)浓度为10g/L,洗脱微振荡-静置沉降最佳时间分布为:微振荡10min,静置沉降50min,洗脱两次后吸附效率下降25%～30%。     

Low-temperature chromium(VI) biotransformation in soil with varying electron acceptors

Effective and low-cost strategies for remediating chromium (Cr)-contaminated soil are needed. Chromium(VI) leaching from contaminated soil into ground water and surface water threatens water supplies and the environment. This study tested indigenous Cr(VI) microbial transformation in batch systems at 10 degrees C in the presence of various electron acceptors. The effects of carbon addition, spiked Cr(VI), and mixing highly contaminated soil with less contaminated soil were investigated. The results indicated that Cr(VI) can be biotransformed in the presence of different electron acceptors including oxygen, nitrate, sulfate, and iron. Sugar addition had the greatest effect on enhancing Cr(VI) removal. Less dissolved organic carbon (DOC) was consumed per amount of Cr(VI) transformed under anaerobic conditions [0.8-93 mg DOC/mg Cr(VI)] compared with aerobic conditions [1.4-265 mg DOC/mg Cr(VI)]. Toxicity of high concentrations (< 160 mg/L) of spiked Cr(VI) were not evident. At Cr(VI) concentrations > 40 mg/L, aerobic conditions promoted faster Cr(VI) reduction than anaerobic conditions with nitrate or sulfate present. Biotransformation of Cr(VI) in highly contaminated soil (22,000 mg Cr/kg) was facilitated by mixing with less-contaminated soil. The study results provide a framework for evaluating indigenous Cr(VI) microbial transformation and enhance the ability to develop strategies for soil treatment.