Al（Ⅲ）与Fe（Ⅲ）溶液洪聚合研究

以ＡｌＣｌ３．６Ｈ２Ｏ和ＦｅＣｌ３．６Ｈ２Ｏ混合溶液通过滴加ＮａＯＨ溶液的方法制备了不同Ａｌ／Ｆｅ摩尔比，下同）和不同「ＯＨ」／「Ａｌ＋Ｆｅ」值的共聚物，测定了聚合过程和熟化过程中的ＰＨ值变化。并对不同碱化放熟化时间下的聚合物进行了混凝效能实验。     

含磷酸盐的三氯化铁水解溶液的化学特征

通过对含磷酸盐三氯化铁水解溶液的ｐＨ驰豫，电导率，可见光光谱和不同化学反应活性组分的分布等一系列化学物理性质的表征，说明在ＦｅＣｌ３－ＮａＨ２ＰＯ４－ＮａＨＣＯ３溶液体系中，ＰＯ４＾３参与了Ｆｅ（Ⅲ）的水解－聚合反应，形成了Ｆｅ－ＯＨ－Ｆｅ－ＰＯ４－Ｆｅ结构共同控制溶液性质。使溶液性质发生了从量变到质变的过程，证明ＰＯ４＾３对Ｆｅ（Ⅲ）溶液的水解形态有重要影响。     

Fe（Ⅲ）水解过程中无机阴离子的影响作用

本文通过ＰＯ＾３－ ４，Ｆ＾－，ＳＯ＾２－ ４，Ｃｌ＾－，ＮＯ＾－ ３和ＣｌＯ＾－ ４存在时，０．１ｍｏｌ／１ ＦｅＣｌ３溶液的碱中和曲线的分析对比，说明了用曲线斜率区分滴定曲线为三个区域：（Ａ）自发水解反应；（Ｂ）聚合反应；（Ｃ）沉淀反应，以及阴离子对中和曲线的影响及其规律，指出阴子子对Ｆｅ（Ⅲ）浓度中和反应影响为不同程度的竞争配位，参与聚合及电中和脱稳，使沉淀反应提前等。并与ＯＨ＾－共同形成Ｆ     

转化血型用蕃茄α－D－半乳糖苷酶的分离、纯化及理化性质

成熟蕃茄匀浆后，经硫酸铵盐析，ＤＥＡＥ－ＳｅｐｈａｄｅｘＡ－５０离子交换层析，ＳｅｐａｄｅｘＧ－１００凝胶过滤和Ｍｅｌｉｂｉｏｓｅ－Ａｇａｒｏｓｅ亲和层析，获得了α－Ｄ－半乳糖苷酶（Ｃ．Ｅ．３．２．１．１１）。酶制剂经ＰＡＧＥ检测为一条带；ＳＤＳ－Ｇ－ＰＡＧＥ测得酶Ｍｒ为３４０００；比活力５２．９Ｕ／ｍｇ·；提纯倍数为５２９０１产率为４５％．酶专－催化以α－Ｄ－半乳糖为末端ａ－（１，３）连接的糖苷键，以ＰＮＰＧ（对硝基苯－α－Ｄ－半乳糖昔）为废物，酶催化反应的Ｋｍ＝０．１１ｍｍｏｌ／Ｌ，Ｖｍａｘ为６７μｍｏｌ·ｍｇ１－·ｍｉｎ－１．ｔ稳定范是０～３５℃；ＰＨ稳定范围是４．０～７．０．最适ｐＨ为５．１．半乳糖是酶的竞争性抑制剂；Ｃｕ２＋、Ｚｎ２＋、Ｍｎ２＋、Ｆｅ３＋、Ａｇ＋和ＥＤＴＡ对酶活性无影响．纯酶制剂可作为Ｂ型血向Ｏ型血转化的工具酶液．     

流动注射荧光分析法用于土壤及水系沉积物中铈（Ⅲ）含量的测定

研究表明Ｃｅ＾３＋在ｐＨ〈６．２ＫＣｌ介质中以２５４．０ｎｍ紫外光激发时，在３５２．０ｎｍ处发出具有恒定强度的荧光。因而可选择ｐＨ５－６作为测定酸度条件，利用Ａｌ２（ＳＯ４）３消除Ｆｅ＾３＋等离子的干扰，建立起Ｃｅ＾３＋的流动注射荧光分析法。方法的线性范围是２．０×１０＾－７—２．０×１０＾－６ｍｏｌ／ｌ，一元回归方程△Ｆ＝６６３６００Ｃ－０．０４１（ｎ＝１０，ｒ＝０．９９９７），检测限６．０×１     

转化血型用蕃茄α—D—半乳糖苷酶的分离,纯化及理化性质

成熟蕃茄匀浆后，经硫酸铵盐析，ＤＥＡＥ－ＳｅｐｈａｄｅｘＡ－５０离子交换层析，ＳｅｐａｄｅｘＧ－１００凝胶过滤和Ｍｅｌｉｂｉｏｓｅ－Ａｇａｒｏｓｅ亲和层析，获得了α－Ｄ－半乳糖苷酶（Ｃ．Ｅ．３．２．１．１１）。酶制剂经ＰＡＧＥ检测为一条带；ＳＤＳ－Ｇ－ＰＡＧＥ测得酶Ｍ，为３４０００；比活力５２．９Ｕ／ｍｇ．；提纯倍数为５２９０；产率为４５％。酶专一催化以α－Ｄ－半乳糖为末端ａ－（１，３）连接的糖苷     

硫化亚铁处理含砷废水中砷的形态变化

本文对用硫化亚铁处理含砷废水时，在气相、液相和固相中砷的形态进行了研究结果表明，在气相中无ＡａＨ３，但在Ａｓ（Ｖ）废水的液相中有Ａｓ（Ｖ）和Ａｓ（Ⅲ）共同存在，在固相中有Ａｓ（０），ＦｅＡｓＯ４（ＦｅＡｓＯ３），Ａｓ２Ｓ３（Ａｓ２Ｓ５）和吸附砷，砷的形态变化表明，硫化亚铁处理含砷废水能取得良好的效果，是沉淀、沉淀转化、氧化还原、吸附共沉淀和中和五种反应共同作用的结果。     

二甲基硫醚的真空紫外光电子谱

本文测定了二甲基硫醚（ＤＭＳ）的真空紫外光电子能谱（ＵＰＳ），实验测得的ＤＭＳ的各Ｉｖ（ｃＶ）值与Ｋｉｍｕｒａ的结果一致。８．７９，１１．２９ｅＶ峰指认为硫原子孤对电子ｎｇ，ｎｓ的电子电离，１２．６２ｅＶ峰相应于σｃｓ价电子电离，１４．０３－１５．４２ｅＶ的四个峰相应于πＣＨ３－，πＣＨ３＋电子电离，紫外光辐照影响ＤＭＳ的ＵＰＳ，显示在πＣＨ３有变化。微波放电时ＤＭＳ的ＵＰＳ有明显的影响，有许多新     

2℃低温下冬小麦幼苗质膜Ca^2＋—ATPase的活性变化

用氯化铈（ＣｅＣｌ３）沉淀的电镜细胞化学方法，对常温下及２℃低温自理后的冬小麦（Ｔｒｉｔｉｃｕｍ ａｅｓｔｉｖｉｕｍ Ｌ．）幼苗质膜Ｃａ＾２＋＿ＡＴＰａｓｅ活性进行定位。结果显示：（１）常温下生长的冬小麦幼苗，质膜上有部分Ｃａ＾２＿ＡＴＰａｓｅ活性反应。（２）冬小麦幼苗经２℃低温处理１ｈ，质膜上Ｃａ＾２＿ＡＴＰａｓｅ活性增加。处理３ｈ，活性进一步加强。２℃下处理１２ｈ，有强的酶活性反应。处理２４ｈ     

广东不同质地水稻土Q／I特性与钾肥施用技术的关系的研究

钾素Ｑ／Ｉ特性是表征土壤钾素状况的一个重要指标，它能同时度量土壤钾素的强度和容量．本文研究了广东不同质地水稻土Ｑ／Ｉ特性与大田钾肥施用技术的关系．结果表明：（１）不同质地土壤的Ｑ／１曲线差异明显，砂土类曲线较平缓．粘土类曲线较陡。（２）ＰＢＣｋ与土壤粘粒含量呈极显著正相关（ｒ＝０．６５３）．（３）－△Ｋ０与作物相对百分产量呈极显著正相关（ｒ＝０．８７３），可作为预测当季作物需钾量的参数．（４）ＡＲ＿ｅ￣ｋ与土壤粘粒含量呈显著负相关（ｒ＝－０．５２０），ＡＲ＿ｅ￣ｋ的大小可作为钾肥合理分配的依据．     

Enhanced adsorption of phosphate by loading nanosized ferric oxyhydroxide on anion resin

Ferric oxyhydroxide loaded anion exchanger （FOAE） hybrid adsorbent was prepared by loading nanosized ferric oxyhydroxide （FO） on anion exchanger resin for the removal of phosphate from wastewater. TEM and XRD analysis confirmed the existence of FO on FOAE. After FO loading, the adsorption capacity of the hybrid adsorbent increased from 38.70 to 51.52mg.g-1. Adsorption processes for both FOAE and anion resin were better fit to the pseudo first order model. Batch adsorption experiments revealed that higher temperature （313K）, higher initial phosphate concentration （50 mg.L-1） and lower solution pH （pH value of 2） would be more propitious to phosphate adsorption. Competition effect of coexisting anions on phosphate removal can be concluded as sulfate 〉 nitrate 〉 chloride. Freundlich isotherm model can describe the adsorption of phosphate on FOAE more accurately, which indicated the heterogeneous adsorption occurred on the inner-surface of FOAE.     

铁盐和铝盐混凝剂对消毒副产物的控制作用及机制研究

以三氯化铁和硫酸铝为研究对象,探讨了两种混凝剂对三氯甲烷生成量的控制作用及控制机制．结果表明,与硫酸铝相比,三氯化铁可以更好地控制三氯甲烷的生成量,对有机物的去除方面,也具有良好的效果．E4／E6变化表明,三氯化铁和硫酸铝对水中有机物的去除机制不同,硫酸铝主要去除水中大分子的有机物,三氯化铁更倾向于去除水中小分子有机物,而这些小分子有机物通常是消毒副产物的前体物,从而使三氯化铁对消毒副产物的控制作用较硫酸铝明显．     

Arsenic adsorption on lignocellulosic substrate loaded with ferric ion

We loaded a lignocellulosic substrate extracted from wheat bran with ferric ions. This new low-cost adsorbent was prepared for the adsorption and removal of arsenate and arsenite ions from aqueous systems. The loading process of Fe in this biomaterial was done by hydrolization of a ferric salt while an alkaline solution was added dropwise. The new material obtained has a high sensivity to arsenite and arsenate species. Here, we investigated the effect of contact time, pH, and Fe content on the adsorption of both arsenic ions on the new material. This adsorption was found to be highly pH-dependent, which can be explained on the basis of electrostatic interactions between ionic species in solution and the ≡FeOH surface groups. The maximum adsorption capacity of arsenite and arsenate species vary linearly with the amount of Fe loaded on the lignocellulosic substrate.     

Applying chemical sedimentation process in drinking water treatment plant to address the emergent arsenic spills in water sources

Arsenic (As) spills occurred more frequently and sometimes polluted water sources in recent years in China. It is as urgent need to develop emergency treatment technologies to address the arsenic threat for large-scale water treatment plants. In response, we developed a chemical sedimentation technology to remove arsenic contaminants for water treatment plants. Bench-scale experiments were conducted to investigate the efficiency of arsenic removal and the influencing factors of the chemical sedimentation treatment process. The influencing factors included the choice and dosage of coagulants, the valence of arsenic and pH value of solution. The As(V) contaminants can be almost completely removed by ferric or alum coagulants. The As(III) contaminants are more recalcitrant to chemical sedimentation, 75% for ferric coagulant and 40% for alum coagulant. The quantitative results of arsenic removal load by different ferric or alum coagulants were presented to help determine the parameters for arsenic treatment technology. The dominant mechanism for arsenic removal is static combination, or adsorption of negative arsenic species onto positive ferric hydroxide or alum hydroxide flocs. The efficiency of this treatment technology has also been demonstrated by a real production test in one water treatment plant with arsenic-rich source water and one emergency response. This technology was verified to be quick to set-up, easy to operate and highly efficient even for high concentration of arsenic.     

石英砂负载氧化铁吸附除锑的研究

考察了石英砂负载氧化铁(IOCS)在不同的实验条件下(无机阴离子种类及其离子强度、 pH值、IOCS投加量、温度等)对水溶液中锑的去除效果.结果表明:三种无机阴离子(NO-3,Cl-,SO2-4)对IOCS吸附锑的去除率、吸附容量以及反应速率几乎没有影响;在pH3-9范围内,锑的去除率达到90%.二级反应动力学模型及Langmuir等温吸附模型可分别较好地描述锑的吸附动力学及吸附等温线实验结果.随着温度的增加,反应速率以及吸附容量也随之增加.     

敌敌畏在颗粒物上吸附的支配因素

研究了敌敌畏在颗粒物(呼和浩特土壤和黄河水体沉积物)上的吸附行为,探讨了颗粒物性质如有机质含量、粘粒含量、阳离子交换量(CEC)、pH值和离子强度等因素对吸附的影响。结果表明:敌敌畏在2种颗粒物上的吸附过程均符合一级动力学规律,可用Freundlich等温式描述,吸附常数Kd为5. 822 0和11. 738 8;颗粒物性质与吸附常数的相关分析发现:支配敌敌畏在颗粒物上吸附的主要因素是有机质含量、pH值和离子强度,随着pH值的增加和离子强度的降低,敌敌畏在2种颗粒物上的吸附量增大。     

磷酸活化活性炭对Cu2+的吸附特征研究

寻求廉价而高效的吸附材料为目的,研究向日葵秸杆基活性炭对铜离子的吸附性能。以向日葵秸秆为原料,经H3PO4活化制备活性炭,通过静态实验研究了其对水溶液中Cu2+的吸附特性,考察了溶液pH值、吸附温度和离子强度对吸附的影响,探讨了吸附热力学、动力学和吸附机理。结果表明:溶液pH值为5～6时活性炭对Cu2+的去除效果最好;向50 mL 170 mg·L-1的溶液中加入0.5 g活性炭,温度为45℃、吸附时间为1 h时,对Cu2+的去除率可达98.3%;Langmuir方程能更好地描述Cu2+在活性炭上的等温吸附特征,静态吸附容量可达41.03 mg·g-1;吸附过程符合拟二级动力学过程,且为吸热的化学吸附过程,膜扩散为速率控制步骤,离子交换可能在吸附过程中起了重要作用。     

磷酸活化活性炭对Cu~（2＋）的吸附特征研究

寻求廉价而高效的吸附材料为目的,研究向日葵秸杆基活性炭对铜离子的吸附性能。以向日葵秸秆为原料,经H3PO4活化制备活性炭,通过静态实验研究了其对水溶液中Cu2＋的吸附特性,考察了溶液pH值、吸附温度和离子强度对吸附的影响,探讨了吸附热力学、动力学和吸附机理。结果表明：溶液pH值为5～6时活性炭对Cu2＋的去除效果最好;向50 mL 170 mg·L-1的溶液中加入0.5 g活性炭,温度为45℃、吸附时间为1 h时,对Cu2＋的去除率可达98.3%;Langmuir方程能更好地描述Cu2＋在活性炭上的等温吸附特征,静态吸附容量可达41.03 mg·g-1;吸附过程符合拟二级动力学过程,且为吸热的化学吸附过程,膜扩散为速率控制步骤,离子交换可能在吸附过程中起了重要作用。     

中南地区几种地带性土壤中的氧化铁类型与钼吸附特性

应用X射线衍射和化学分析等手段研究了中南地区几种地带性土壤中的氧化铁类型与钼吸附的关系，结果表明：供试土壤粘粒的氧化铁以晶质氧化铁为主，非晶质氧化铁含量低；砖红壤和赤红壤中的晶质氧化铁以赤铁矿为主．其次为针铁矿；红壤、棕红壤中针铁矿含量比赤铁矿含量稍高，黄棕壤中的晶质氧化铁全为针铁矿；针铁矿的平均晶粒大小（MCD）一般比赤铁矿的小，而比表面积却比赤铁矿的大；针铁矿型氧化铁的钼吸附量比针－赤混合型氧化铁的高，从砖红壤到黄棕壤．单位重量的晶质氧化铁的钼吸附量随G／（G＋H）比值的升高而增大．     

Role of water chemistry on estrone removal by nanofiltration with the presence of hydrophobic acids

Hydrophobic acid organic matter (HpoA) extracted from treated effluent has been known to improve the rejection of steroid hormone estrone by reverse osmosis (RO) and nanofiltration (NF) membranes. In this study, the effects of solution chemistry (solution pH and ionic strength) on the estrone rejection by NF membrane with the presence of HpoA were systematically investigated. Crossflow nanofiltration experiments show that the presence of HpoA significantly improved estrone rejection at all pH and ionic strength levels investigated. It is consistently shown that the “enhancement effect” of HpoA on estrone rejection at neutral and alkaline pH is attributed to the binding of estrone by HpoA macromolecules via hydrogen bonding between phenolic functional groups in feed solutions, which leads to an increase in molecular weight and appearance of negative charge. The membrane exhibited the best performance in terms of estrone rejection at pH 10.4 (compared to pH 4 and pH 7) as a result of strengthening the electrostatic repulsion between estrone and membrane with the presence of HpoA. At neutral pH level, the ability of HpoA macromolecules to promote estrone rejection became stronger with increasing ionic strength due to their more extended conformation, which created more chances for the association between estrone and HpoA. The important conclusion of this study is that increasing solution pH and salinity can greatly intensify the “enhancement effect” of HpoA. These results can be important for NF application in direct/indirect potable water reuse.