烟气脱汞技术研究进展

基于现阶段烟气汞的排放情况,介绍当前燃煤电站的几种烟气脱汞技术。主要是先将零价汞氧化为二价汞,再进行脱除。其中利用现有烟气控制设备,活性炭吸附及添加改性物质,有比较好的脱汞效率,电催化、光催化以及等离子体脱汞等新技术处于研发阶段,而烟气中多种污染物协同脱除有较好的应用前景。     

我国燃煤锅炉汞减排工艺措施探讨

面对当前汞污染日益严峻的趋势,分析了燃煤锅炉烟气其它污染物（如二氧化硫、氮氧化物、颗粒物）控制设施及其运行情况,结合所燃用的煤质情况,介绍了燃煤锅炉烟气汞减排各种经济实用的方法,以及选择汞排放控制措施的“抉择树”。根据燃煤锅炉烟气实际情况,确定可采用的汞减排控制技术,必要时采取活性炭喷射脱汞技术（ACI）,最大限度地提高协同除汞效果。同时提出了应注重燃煤残留物中汞的二次污染问题。     

超低排放燃煤火电机组汞排放特性研究

针对燃煤火电机组汞排放特性,开展了汞测试技术研究,完成了3台典型超低排放机组汞排放特性现场测试,揭示了烟气汞排放特性及现有污染物控制装置对汞的协同脱除效果,对后续燃煤电厂汞污染物治理技术选择具有重要意义。     

炭法烟气脱硫机理的研究现状

炭法烟气脱硫技术是一种污染治理与资源回收利用相结合的脱硫技术，本文在对活性炭吸附催化转化SO2过程、H2O和O2的存在对脱硫过程的影响，以及改性活性炭脱硫性能提高影响因素等方面分析基础上，论述了炭法脱硫机理研究现状，并提出了以后的发展方向。     

燃煤电厂烟气多污染物协同治理技术

从我国大气环保的严峻形势出发,论述并分析了燃煤电厂现有常规除尘、脱硫、脱硝设备之间的相互影响及多污染物协同治理的潜力,讨论了燃煤烟气污染控制设备对烟气汞、三氧化硫和细颗粒物的协同脱除技术,提出了燃煤烟气多污染物协同治理技术是应对未来我国环保形势的较佳选择。     

燃煤电厂烟气中Hg的采样及测定方法研究

对国内煤种Hg含量分析及燃煤电厂控制现状进行了阐述,对燃煤电厂烟气中Hg的采样及测定方法进行了分析研究,分别研制出ZR-3701型烟气总汞采样器和RA-915M型汞分析仪进行燃煤烟气中Hg的采样及测定,并与同类测试仪器进行对比,为燃煤电厂烟气中Hg测定标准的研制提供了借鉴。     

钢铁厂烧结烟气SCR脱硝技术应用探讨

目前烧结烟气脱硝主要采用活性炭(焦)吸附技术,投资及运行费用极高。SCR(选择性催化还原)烟气脱硝技术广泛应用于燃煤锅炉,技术成熟可靠。针对钢铁厂烧结烟气的特点,探讨了将SCR烟气脱硝技术应用于烧结烟气脱硝;通过适当的工艺优化和技术创新,烧结烟气采用SCR脱硝技术完全可行,经济适用。     

改性椰壳活性炭对工业废水中氨氮的吸附行为研究

为高效去除工业废水中的氨氮化合物,采用椰壳活性炭为原材料,通过碱性溶液改性制备高性能吸附剂。通过表面特征分析发现2 mol/L氢氧化钠改性后的椰壳活性炭孔体积和吸附平均孔径最小,比表面积最大;分析不同体系温度对改性活性炭吸附性能的影响,结果表明：温度对于氨氮的吸附效率影响较大,在35℃时的吸附效果最优,利用等温吸附模型Langmuir方程拟合得到计算理论吸附量为38.8 mg/g;改性椰壳活性炭的吸附行为符合准二级动力学模型,进一步表明椰壳活性炭对废水中氨氮化合物的吸附是易于发生的化学吸附过程。由此可见,改性椰壳活性炭作为一种高性能吸附材料,在去除水中的氨氮化合物方面具有良好的应用价值。     

水处理用活性炭改性研究

研究了锆（Zr）和十六烷基三甲基氯化铵（CTAC）联合改性活性炭的制备，并考察Zr-CTAC改性活性炭对水中硝酸盐和磷酸盐的吸附作用及相关吸附机制，着重论述了锆（Zr）和十六烷基三甲基氯化铵联合改性活性炭（Zr-CTAC-AC）对水中硝酸盐和磷酸盐的吸附去除作用，结果表明Zr-CTAC-AC对水中硝酸盐和磷酸盐均具备较好的吸附去除能力。     

磁性活性炭吸附苯酚的初步研究

本文研究了磁性活性炭对苯酚的吸附性能;探讨了Cd2＋对苯酚在磁性活性炭上吸附的影响。目的是对磁性活性炭进行研究,以及为在实际废水中吸附处理苯酚提供参考。结果表明,磁性活性炭对苯酚的吸附过程符合拟二级动力学模型,R2为0.9935;与Freundlich吸附模型相比,Langmuir吸附模型能更好地描述磁性活性炭对苯酚的吸附行为;在不影响去除率的情况下,Cd2＋的存在使苯酚吸附处理最佳浓度由30 mg/L增大至50 mg/L;同时,Cd2＋对磁性活性炭和活性炭吸附苯酚分别具有促进和抑制作用。针对苯酚的吸附去除率,当无Cd2＋时,磁性活性炭的比活性炭的低10.65%～20.2%;当有Cd2＋时,磁性活性炭的比活性炭的高0.3%～7.71%。     

PRESERVATION OF SAMPLES FOR DISSOLVED MERCURY1

ABSTRACT: Water samples for dissolved mercury require special treatment because of the high chemical mobility and volatility of this element. Widespread use of mercury and its compounds has provided many avenues for contamination of water. Two laboratory tests were done to determine the relative permeabilities of glass and plastic sample bottles to mercury vapor. Plastic containers were confirmed to be quite permeable to airborne mercury, glass containers were virtually impermeable. Methods of preservation include the use of various combinations of acids, oxidants, and complexing agents. The combination of nitric acid and potassium dichromate successfully preserved mercury in a large variety of concentrations and dissolved forms. Because this acid-oxidant preservative acts as a sink for airborne mercury and plastic containers are permeable to mercury vapor, glass bottles are preferred for sample collection. To maintain a healthy work environment and minimize the potential for contamination of water samples, mercury and its compounds are isolated from the atmosphere while in storage. Concurrently, a program to monitor environmental levels of mercury vapor in areas of potential contamination is needed to define the extent of mercury contamination and to assess the effectiveness of mercury clean-up procedures.     

MA-2000型测汞仪直接测定环境水体中的汞

介绍了MA-2000型测汞仪测定环境水体中的汞，以氯化亚锡为还原剂，0．001％半胱氨酸为汞固定剂，在一定浓度范围内被测汞蒸汽在波长253．7nm紫外光下的吸收值与汞蒸汽浓度成正比。方法检出限0．006ng，精密度和准确度均满足水质监测实验室质量控制的要求。     

Application of the analytic hierarchy process to compare alternatives for the long-term management of surplus mercury

This paper describes a systematic method for comparing options for the long-term management of surplus elemental mercury in the US, using the analytic hierarchy process as embodied in commercially available Expert Choice software. A limited scope multi-criteria decision analysis was performed. Two (2) general types of treatment technologies were evaluated (stabilization/amalgamation and selenide), combined with four (4) disposal options: (a) hazardous waste landfill; (b) hazardous waste monofill; (c) engineered below-ground structure; and (d) mined cavity. In addition, three storage options for elemental mercury were considered: (a) aboveground structure; (b) hardened structure; and (c) mined cavity. Alternatives were evaluated against criteria that included costs, environmental performance, compliance with current regulations, implementation considerations, technology maturity, potential risks to the public and workers, and public perception. Considering non-cost criteria only, the three storage options rank most favorably. If both cost and other criteria are considered, then landfill options are preferred, because they are the least expensive ones. Storage options ranked unfavorably on cost because: (a) even relatively small per annum costs will add up over time; and (b) storage is a temporary solution and, sooner or later, a treatment and disposal technology will be adopted, which adds to the cost. However, the analysis supports continued storage for a short period (up to a few decades) followed by permanent retirement when treatment technologies have matured. Suggestions for future work include: (a) involving additional stakeholders in the process, (b) evaluating alternatives for mercury-containing wastes rather than for elemental mercury only, (c) revisiting the analysis periodically to determine if changes are required, (d) conducting uncertainty analyses utilizing Monte Carlo-based techniques.     

高压实新疆阿尔泰膨润土微观结构随吸力变化特征

采用压汞法(MIP)和扫描电镜(SEM)法,在自由和侧限状态下,试验研究了高压实新疆阿尔泰膨润土在不同吸力条件下的微观结构变化特征。吸力的控制采用了气相法和渗析(液相)法。研究结果表明:(1)低吸力范围内,自由膨胀和侧限条件下的高压实膨润土土水特征存在明显差异;(2)膨润土在自由和侧限状态下的水化过程中呈现出了截然不同的微结构变化特征。自由膨胀条件下,土的吸水膨胀量主要来自土中大孔隙的逐渐膨胀。侧限状态下,随着控制吸力的降低,膨润土的大孔隙逐渐被压缩,较小孔隙的数量不断增加,土中孔隙分布变得更加均匀。     

分光光度法测定氯化氢的实验条件改进

硫氰酸汞分光光度法测定大气中的氯化氢,所使用的硫氰酸汞-乙醇溶液配置时间长,浓度低,曲线线性不好,不适用于环境现场监测。通过对氯化氢测定过程中遇到的问题进行分析,对硫氰酸汞-乙醇溶液的配置方法进行改进,提高该溶液的浓度。实验证明,使用定性滤纸过滤后的0.40%硫氰酸汞-乙醇溶液,曲线线性关系好,标样准确度高,适用于现场监测分析。     

Clonal differences in mercury tolerance, accumulation, and distribution in willow

This study was performed to investigate mercury (Hg) tolerance, accumulation, and translocation within the genus Salix for the potential use of this plant to remediate Hg-contaminated sites. Six clones of willow (Salix spp.) were tested on tolerance to Hg by treating plants grown in solution culture with 0 to 15 microM HgCl(2). Results showed that willow had a large variation in its sensitivity to Hg. However, the accumulation and translocation of Hg to shoots was similar in the eight tested willow clones as shown by cold vapor atomic absorption spectrometry analysis when plants were treated with 0.5 microM HgCl(2) in a nutrient solution. The majority of total Hg accumulated was localized to the roots, whereas only 0.45 to 0.62% of the total Hg accumulated via roots was translocated to the shoots. Thus, the root system is the main tissue of willow that accumulates Hg and the majority of the Hg in the root system (80%) was bound in the cell wall.     

Potential anthropogenic mobilisation of mercury and arsenic from soils on mineralised rocks, Northland, New Zealand

Eroded roots of hot spring systems in Northland, New Zealand consist of mineralised rocks containing sulfide minerals. Marcasite and cinnabar are the dominant sulfides with subordinate pyrite. Deep weathering and leached soil formation has occurred in a warm temperate to subtropical climate with up to 3 m/year rainfall. Decomposition of the iron sulfides in natural and anthropogenic rock exposures yields acid rock drainage with pH typically between 2 and 4, and locally down to pH 1. Soils and weathered rocks developed on basement greywacke have negligible acid neutralisation capacity. Natural rainforest soils have pH between 4 and 5 on unmineralised greywacke, and pH is as low as 3.5 in soils on mineralised rocks. Roads with aggregate made from mineralised rocks have pH near 3, and quarries from which the rock was extracted can have pH down to 1. Mineralised rocks are enriched in arsenic and mercury, both of which are environmentally available as solid solution impurities in iron sulfides and phosphate minerals. Base metals (Cu, Pb, Zn) are present at low levels in soils, at or below typical basement rock background. Decomposition of the iron sulfides releases the solid solution arsenic and mercury into the acid rock drainage solutions. Phosphate minerals release their impurities only under strongly acid conditions (pH<1). Arsenic and mercury are adsorbed on to iron oxyhydroxides in soils, concentrated in the C horizon, with up to 4000 ppm arsenic and 100 ppm mercury. Waters emanating from acid rock drainage areas have arsenic and mercury below drinking water limits. Leaching experiments and theoretical predictions indicate that both arsenic and mercury are least mobile in acid soils, at pH of c. 3-4. This optimum pH range for fixation of arsenic and mercury on iron oxyhydroxides in soils is similar to natural pH at the field site of this study. However, neutralisation of acid soils developed on mineralised rocks is likely to decrease adsorption and enhance mobility of arsenic and mercury. Hence, development of farmland by clearing forest and adding agricultural lime may mobilise arsenic and mercury from underlying soils on mineralised rocks. In addition, arsenic and mercury release into runoff water will be enhanced where sediment is washed off mineralised road aggregate (pH 3) on to farm land (pH>6). The naturally acid forest soils, or even lower pH of natural acid rock drainage, are the most desirable environmental conditions to restrict dissolution of arsenic and mercury from soils. This approach is only valid where mineralised soils have low base metal concentrations.     

正交试验-硝酸微波消解-冷原子吸收法测定土壤中汞

应用硝酸微波消解土壤样品-冷原子吸收法测定土壤中的汞。通过正交试验，优化了土壤中汞的微波消解条件。并对干扰消除、方法精密度、加标回收、检出限进行了试验研究。在0～10μg／L范围内线性关系良好，方法测定下限为0．20μg／L，土壤中汞的检出限为0．005μg／g。该优化条件对汞含量为0．02—0．46μg／g的土壤样品，汞提取完全。建立了一种简便、成本低、干扰少、灵敏度高的方法。