离子选择电极法测定水和废水中总氰化物

本文在查阅国内外文献的基础上，对氰化物测定中的前处理方法和干扰消除进行了简要综述。同时对氰离子选择电极法测定氰化物进行了研究，测定的ｐＨ应控制为１２－１３，检测下限为０．０３ｍｇ／ｌ。并用离子交换的方法分离阳离子，以ＰｂＣＯ３为沉淀剂分离Ｓ＾２－后，对废水样进行分析，效果良好。     

气质联用测定甘蓝、韭菜中农药多残留方法研究

建立了甘蓝、韭菜中101种农药残留的快速检测GC—MS—SIM方法，通过考察载气流速、升温程序、离子分组和碎片离子，选择最佳气质分析模式，消除或降低了甘蓝、韭菜等“问题蔬菜”检测时的基质干扰，从而完成对这类“问题蔬菜”的农残检测。本研究优化了实验方案，样品采用乙腈提取、PSA和C18净化的前处理方法，缩短了检测时间，减少了溶剂用量。本实验方案每个样品溶剂用量仅为15mL，一个实验人员每日可以处理35～40个蔬菜样品，每个样品的前处理费用大约为20元，真正实现农残的快速、简便、廉价、有效、灵敏、安全检测。在选择离子监测模式（SIM）下检测，结果表明：最小检出限0．0011～0．0854mg·kg^-1，方法回收率69．2％-122％，相对标准偏差0-9．15％。该方法具干扰目标物检测的杂质少，溶剂用量小，操作简便、快速等特点。在34min内所有农药及其异构体全部出峰完毕，可满足国内及对外出口蔬菜农产品的农残检测分析，将是各实验室常规检测农药多残留物的首选方法。     

废气中硫含量分析方法的试验研究

通过试验研究，建立了高氯酸常压消解-离子色谱法测定工业废气中硫含量的分析方法。滤筒采集污染源废气颗粒物，利用高氯酸常压消解，将元素硫氧化为硫酸根，利用离子色谱法测定，进而得出硫的含量。结果表明：此方法简单、灵敏、检出限低。     

应用多思单元的离子色谱法测定降水中六种阳离子

笔者通过研究建立了应用单标多点校正和英蓝超滤单元的非抑制电导离子色谱法测定降水中Li+、Na+、NH4+-N、K+、Ca2+、Mg2+6种阳离子的方法。该方法操作简单,样品无需过滤即可上机分析测定;检出限低,范围在0.005～0.04 mg/L;重复测定相对标准偏差小于5%,加标回收率稳定在96.7%～104.6%;线性范围广,待测离子之间无明显干扰,可同时快速测定降水中不同浓度的阳离子。同时该方法降低了标准品配制和样品前处理的复杂性。     

离子色谱法测定海产品中NO_2~-、NO_3~-和S~(2-)

建立了海产品中NO2^-、NO3^-和S2^-电导和紫外串联检测离子色谱分析法。优化了样品前处理方法,100mmol/L NaOH溶液浸提测定组分,LC-WCX去除干扰,回收率较好。优化了色谱分离和检测条件,25℃分离共存组分,电导和紫外串联检测,有效消除了高浓度Cl-和SO42-的干扰。电导和紫外检测法的线性范围均为0.05-10mg/L,检出限分别为0.75-6.0mg/kg、0.24-5.8mg/kg,回收率分别为88.5%-101.5%、82.8%-107.8%,RSD分别为1.2%-2.7%、1.7%-3.6%。采用建立的分析方法测定了海鱼和虾仁,结果满意。     

不同前处理方法对活性炭吸附一氧化碳的影响

本文采用颗粒状活性炭（GH-A)作吸附剂，通过不同的前处理方法，以一氧化碳CO与空气的混合物为分离测定对象，用气固色谱法测定被活性炭充分吸附前、后的混合气体中CO的含量，对比评价几种前处理方法。结果表明，对CO的吸附量显著提高的前处理方法分别是研磨筛分至32—38目、酸洗、添加改性剂So而水洗则降低了活性炭吸附CO的能力。     

几种前处理方法对活性炭吸附CO的影响

本文采用颗粒状活性发(代号GH—A)作吸附剂，经过几种不同的访处理方法后，以CO与空气的混合物为分离测定对象，用气固色语法则定被活性发充分吸附前、后的混合气体中CO的含量，对比评价几种访处理方法。实验结果表明，使活性发吸附剂对CO的吸附量显著提高的前处理方法分别是研磨筛分至32-38目、酸洗、添加改性剂So而水洗则降低了活性发吸附加的能力。     

碱熔－蒸馏－离子选择电极法测定废钻井液中全氟

废钻井液是油气勘探开发的废弃物，目前多采用就地掩埋方式处置。准确测定废钻井液中氟化物的含量，对于评价其对环境可能造成的影响是十分必要的。选用离子选择电极法测定废钻井液中的氟时，对预处理方法进行了试验研究：试验了蒸馏－离子选择电极法、碱熔－离子选择电极法、碱熔－蒸馏－离子选择电极法。结论是：碱熔－蒸馏预处理法综合了碱熔法和蒸馏法各自的优点，能将氟从钻井液中最大程度地蒸馏出来，消除了基体对氟测定的干扰。因此，此法以回收率表示的废钻井液全氟准确度为最高并达到了文献要求，方法可靠。     

分光光度法与离子色谱法测定空气中氯化氢的对比研究

通过对硫氰酸汞分光光度法和离子色谱法测定空气中氯化氢含量的对比发现，两种方法对实验室质控样和实际样品的分析测定均能达到要求，且F检验法分析表明实测结果没有显著性差异。然而，硫氰酸汞分光光度法的测试过程操作繁琐，误差较大，稳定时间较长，且硫氰酸汞具有剧毒，危害操作人员的健康，残液也难以处理。离子色谱法分析操作简单，过程安全可靠，能够有效降低样品受污染的可能性并保证分析质量。     

不同酸消解方法在土壤重金属测定中的比较研究

分别用三种不同的酸消解方法进行土壤标准样品的前处理,用原子吸收分光光度法测定其中铜、铅、锌、镉、镍、锰、总铬元素的含量。结果表明,电热板/硝酸-过氧化氢-氢氟酸消解方法耗酸量少,消解时间短,适用于土壤中铜、铅、锌、镉、镍、锰元素的前处理,相对标准偏差为1.0%～5.0%;而使用电热板/硝酸-硫酸-氢氟酸方法针对土壤中总铬元素进行消解前处理,准确度更高,相对标准偏差为2.7%～5.1%。     

宜宾市酸雨pH值预测的偏最小二乘回归分析

酸雨pH值受酸性离子(有机酸、无机酸)和碱性离子的影响。这些影响因素之间存在多重相关性。用一般最小二乘回归法建模预测pH值,估计参数存在着很大的误差,而且物理意义明显不足。本文以宜宾市区2002-2003年的27组降雨监测数据作为样本数据,应用偏最小二乘回归技术建立pH值预测模型,克服了自变量之间的多重相关性的问题。与最小二乘回归法相比更具有先进性,计算结果更为可靠;在确定了模型可行性后,分析比较了影响宜宾市区酸雨pH值的离子的重要性和离子来源。     

A COLORIMETRIC METHOD FOR THE DETERMINATION OF TRACE COPPER CONCENTRATIONS IN WATER1

Trace quantities of copper (II) ion can be found in natural water as waste products from industrial, mining, and agricultural operations. Because low concentrations of copper can be toxic to plant life, many workers have devised methods of analysis for this metal in water. These methods require expensive equipment and skilled technicians. The described study illustrates a simple method in which copper (II) ion is concentrated by a batch ion exchange technique and estimated colorimetrically after formation of the blue triethylenetetramine complex. Using the visible absorption peak of the complex at 600 nm it was possible to obtain accurate estimations of original copper concentrations in the range 0.5-3 ppm. Using the complex absorption peak at 260 nm in the ultra-violet region of the spectrum increased the sensitivity by a factor of twenty. Because of the dependence of the complex formation reaction on solution acidity it is possible to optimize conditions for the detection of copper (II) in the presence of other metal ions. This type of method, which could be extended to the analysis of other metal ions, could be performed by a relatively unskilled technician under field conditions.     

The potential of cost-effective coconut husk for the removal of toxic metal ions for environmental protection

Coconut (Cocos nucifera) husk, an agricultural waste, has been thoroughly investigated for the removal of toxic Cd(II), Cr(III) and Hg(II) ions from aqueous media. The parameters like nature and composition of electrolyte, concentration of toxic ions, dosage of coconut husk, and equilibration time between the two phases were optimized for their maximum accumulation onto the solid surface. The effect of common ions on the uptake of metal ions has been monitored under optimal conditions. The variation of retention of each metal ion with temperature was used to compute the thermodynamic quantities DeltaH, DeltaS and DeltaG. The values 18.1+/-0.6 kJmol(-1), 74+/-2 Jmol(-1)K(-1), and -3.8+/-0.04 kJmol(-1) at 298 K; 10.8+/-0.8 kJmol(-1), 48.8+/-2.7 Jmol(-1)K(-1), and -4.6+/-0.3 kJmol(-1) at 298 K; and -37.4+/-2k Jmol(-1), 105+/-7 Jmol(-1)K(-1) and -2.58+/-0.5 kJmol(-1) at 298 K were obtained for Cd(II), Cr(III) and Hg(II) ions, respectively. The sorption data were analysed by applying different sorption isotherms. The sorption capacity and energy were evaluated for each metal ion. The values of the Freundlich constants 1/n and C(m) were 0.92+/-0.04 and 52.6+/-22.2 mmolg(-1); 0.85+/-0.05 and 56.0+/-0.03 mmolg(-1); and 0.88+/-0.03 and 6.84+/-0.45 mmolg(-1) for Cd(II) Cr(III) and Hg(II) ions, respectively. Similarly, the Dubinin-Radushkevich (D-R) constants beta, X(m,) and E were evaluated for the three metal ions. To check the selectivity of the sorbent, sorption of a number of elements was measured under similar conditions. Separation of Zn(II) from Cd(II); Cr(III) from I(I), Zr(IV), Se(IV), and Hg(II) from Se(IV) and Zn(II) can be achieved using this sorbent. This cheap material has potential applications in analytical chemistry, water decontamination, industrial effluent treatment and in pollution abatement.     

Removal of Cr(VI) from Cr-contaminated groundwater through electrochemical addition of Fe(II)

The conventional chemical reduction-precipitation technique in the removal of Cr(VI) from contaminated groundwater involves a two-step process whereby Cr(VI) is first reduced to Cr(III) at an acidic pH by a reducing agent and in a subsequent step, Cr(III) is precipitated as insoluble hydroxide at an alkaline pH. In a variation of this method, Fe(II) is added electrochemically to the Cr(VI) containing water. From a pure iron electrode, Fe(2+) ions are released into the solution and bring forth the reduction of Cr(VI). At the cathode, H(2)O is reduced whereby the OH(-) ions entering the solution keep the pH of the solution in the alkaline range. This latter fact greatly facilitates simultaneous reduction of Cr(VI) to Cr(III) and co-precipitation of hydroxides of trivalent Cr and Fe. On the basis of a set of experimental data, it is shown that this process is both thermodynamically and kinetically efficient, meaning, with the electrochemical method, rapid and nearly complete removal of Cr(VI) from a groundwater source with both high and low levels of Cr-contamination can be achieved. These factors make the electrochemical process superior to the conventional chemical process in remediation of Cr-contaminated groundwater.     

灭活性产黄青霉菌对铅的吸附研究

本文通过某制约厂青霉素车间排放手大量灭活性产黄青霉菌对溶液中铅的吸附研究，发现该菌体对金属离子吸附有较强的选择性，尤其对铅离子高于其它金属离子。而且被吸附的铅离子能被重新洗脱回收。     

Equilibrium and kinetic studies on biosorption of Hg(II), Cd(II) and Pb(II) ions onto microalgae Chlamydomonas reinhardtii

The microalgae Chlamydomonas reinhardtii was used for the biosorption of Hg(II), Cd(II) and Pb(II) ions. The maximum adsorption of Hg(II) and Cd(II) ions on Chlamydomonas reinhardtii biomass was observed at pH 6.0 and the corresponding value for Pb(II) ions was 5.0. The biosorption of Hg(II), Cd(II) and Pb(II) ions by microalgae biomass increased as the initial concentration of Hg(II), Cd(II) and Pb(II) ions increased in the biosorption medium. The maximum biosorption capacities of microalgae for Hg(II), Cd(II) and Pb(II) ions were 72.2+/-0.67, 42.6+/-0.54 and 96.3+/-0.86 mg/g dry biomass, respectively. The affinity order for algal biomass was Pb(II)>Hg(II)>Cd(II). FT-IR analysis of algal biomass revealed the presence of amino, carboxyl, hydroxyl and carbonyl groups, which were responsible for biosorption of metal ions. Biosorption equilibrium was established in about 60 min and the equilibrium was well described by the Freundlich biosorption isotherms. Temperature change in the range of 5-35 degrees C did not affect the biosorption capacity. The microalgae could be regenerated using 0.1 M HCl, with up to 98% recovery, which allowed the reuse of the biomass in six biosorption-desorption cycles without any considerable loss of biosorption capacity.     

ICP—OES法在测定降水中金属离子的研究

本文主要研究了应用电感耦合等离子体发射光谱法（ICP—OES法）同时测定降水中钾、钠、钙、镁金属离子的应用。通过多次测试待测标准物质，确定各待测元素的最佳分析谱线和仪器的工作参数。根据ICP-OES法测定模拟降水混合标准样品、降水样品及其加标样品的结果，与AAS法（原子吸收分光光度法）进行实验室间比对测定，得出ICP—OES法测定降水中钾、钠、钙、镁各离子的检出限、线性范围、标准偏差、准确度等均比AAS法得到的结果要好。ICP-OES法与国家标准方法——原子吸收分光光度法（GB13580．12—92，GB13580．13—92）相比，具有操作简单、多种元素同时测定、方便快捷、检出限低、线性范围宽、干扰少等优点；有良好的准确度和精密度，相对标准偏差在0．3％～1．5％之间，加标回收率在97％～105％之间；该方法明显优于国家标准方法。     

A method to quantitatively trap volatilized organoselenides for stable selenium isotope analysis

If volatile organoselenides are to be analyzed for their stable Se isotope composition to elucidate sources and formation processes, organoselenides need to be trapped quantitatively to avoid artificial Se isotope fractionation. We developed an efficient trap of organoselenides to be used in microcosms designed to determine the Se isotope fractionation by microbial transformation of inorganic Se to volatile organoselenides. The recoveries of volatilized dimethyldiselenide (DMDSe) from aqueous standard solutions by activated charcoal and alkaline peroxide solution with subsequent freeze-drying and purification via a cation exchange resin were tested. Microcosm experiments with the Se-methylating fungus in a growth medium were conducted, and tightness of the microcosm was assessed by comparing mass balances of total Se of the fungus, medium, and trapped organoselenides with the supplied Se mass. At the end of the experiment, we calculated δSe values of the whole microcosm and compared them with the δSe value of supplied Se(IV) and Se(VI). Our results demonstrated that activated charcoal cannot be used for quantitative trapping of organoselenides because generally <64% of the outgassed DMDSe were recovered. The mean recovery of Se volatilized from an aqueous DMDSe standard trapped in alkaline peroxide, in contrast, was 96 ± 11% (SD) after 2 h ( = 4). The mass balances of total Se in microcosm experiments with alkaline peroxide traps run for 11 to 15 d were 96 ± 15 and 102 ± 2.4% for Se(IV) and Se(VI) ( = 3), respectively. The mass-weighted mean δSe values for the Se(IV) and Se(VI) batch experiments were -0.31 ± 0.05‰ ( = 3) and -0.76 ± 0.07‰ ( = 3), compared with -0.20 ± 0.10‰ and -0.69 ± 0.10‰ in the supplied Se oxyanions, respectively. We conclude that the alkaline peroxide trap can reliably be used to determine the Se isotope composition of organoselenides.     

Binding of heavy metal contaminants onto chitosans--an evaluation for remediation of metal contaminated soil and water

The binding efficiency of chitosan samples for Ag(+), Cd(2+), Cu(2+), Pb(2+) and Zn(2+) has been evaluated in order to consider their application to remediate metal contaminated soil and water. The sorption behaviour of metal ions was assessed using a batch technique at different contact time and initial metal concentration with different background electrolytes. The kinetics followed a pseudo-second-order model, while the equilibrium data correlated well with the Freundlich and Langmuir isotherm models. For example, the maximum sorption capacity (Q) for chitosan was estimated as 1.93 mmol/g for Ag(+), 1.61 mmol/g for Cu(2+), 0.94 mmol/g for Zn(2+), 0.72 mmol/g for Cd(2+) and 0.64 mmol/g for Pb(2+). Covalent interaction between metal ions and functional groups (amino and hydroxyl) of the chitosans was the main binding mechanism. Ion exchange is not an important process. Chitosan and cross-linked chitosans were able to bind metal ions in the presence of K(+), Cl(-) and NO(3)(-). The nature of Cl(-) and NO(3)(-) ions did not affect Zn(2+) binding by the chitosans. Even at 11x dilution, the chitosans were able to retain metal ions on their surfaces.     

基于环境一号卫星的四川盆地气溶胶光学厚度精细化反演

四川盆地为中国灰霾形势较为严重的区域之一,对四川盆地大气灰霾的监测具有十分重要的意义。利用环境一号卫星数据,对能表征大气污染程度的气溶胶光学厚度进行了反演。提出了用EVI植被指数判定暗像元精细化反演气溶胶光学厚度的方法,该方法能较好地去除部分大气影响,气溶胶光学厚度反演结果与CE318的气溶胶光学厚度结果相关性较高,误差较小,具有较高的精度,反演结果满足精细化要求。反演结果表明,四川盆地内有德阳、成都、眉山和乐山4个气溶胶光学厚度高值区,该高值区呈带状分布且与四川盆地的地形密切相关。