焙烧温度对N掺杂TiO2催化剂催化性能的影响

以Ti（SO4）2为钛源、碳酸氢铵为氮源,采用均匀沉淀法制得水合沉淀物,在N2保护下对水合沉淀物进行程序升温处理,制得了不同焙烧温度的N掺杂TiO2可见光响应催化剂.以三硝基间苯二酚为目标降解物,研究了所制备微粒在可见光区及紫外光区的光催化活性.对所制备的催化剂采用X射线衍射、热重-差热分析、傅立叶变换红外光谱和紫外-可见漫反射光谱对催化剂进行表征,研究改性催化剂的晶相结构、热稳定性、表面结构和光谱特征.结果表明：N-掺杂TiO2的可见光催化活性显著提高,焙烧温度为300℃时可见光催化活性最为优异,在不降低紫外段催化能力的同时,催化剂的吸收带边红移至468nm.     

煤矸石中硫铁矿在处理含铬(Ⅵ)废水中的应用

在此用煤矸石中硫铁矿对含铬废 (Ⅵ )水处理进行了实验研究 ,确定了有关工艺参数 ,并进行了工业化应用实验 ,煤矸石中硫铁矿处理含铬废 (Ⅵ )水工艺简单、操作方便、成本低 ,具有较好的推广应用价值 ,实现了以废治废 ,开辟了煤矸石中硫铁矿资源化利用的新途径     

Prenatal diagnosis of morquio's disease type a (n-acetylgalactosamine 6-sulphate sulphatase deficiency)

Prenatal monitoring of three pregnancies at risk of Morquio's disease type A by determination of N-acetylgalactosamine 6-sulphate sulphatase activity in cultured amniotic cells is reported. In one pregnancy prenatal diagnosis of one affected fetus was made. Enzyme determinations in tissues of the aborted fetus confirmed the prenatal diagnosis.     

产碱菌株F-3-4降解2,6-二叔丁基苯酚机理研究

研究有毒化合物的生物降解途径．以鉴定有毒化合物在微生物作用下的降解中间产物．以及是否最终成为无害的产物（CO2和H2O），对人们认识有毒化合物在环境中的迁移规律及生物去除的办法．途径具有重要的启示作用。通过色质联机测试中间产物以及降解过程体系酶的变化，对产碱菌株F-3-4降解2,6-二叔丁基苯酚（2,6-DTBP）的途径和机理进行了研究。GC—MS测试结果表明。中间降解产物为乙酸、丙酮酸和异丁酸等化合物。降解过程体系酶测定结果显示．儿茶酚2，3-双加氧酶变化比较明显。表明在菌种生物降解底物过程中。主要以2，3位开裂为主。即主要以间位开裂途径进行开环反应，从而推测了F-3-4对2,6-DTBP的降解途径和机理。     

Summer air quality over an artificial lake

In the summer of 1998, the air quality (indicators: CO, NO, NO₂, O₃) above the water surface of the Lake Balderey (Essen, Ruhr area, North Rhine-Westphalia, Germany), an artificial lake used for recreation purposes, was measured using the Fourier transform infrared spectroscopy (FTIR) and differential optical absorption spectroscopy (DOAS) remote measurement methods. The lake, with an area of 3 km² was created by damming the Ruhr and is surrounded by higher ground. In calm, bright weather conditions, this location results in a low-exchange situation (formation of temperature inversions, cold air dynamics) with a sustained impact on pollutant concentrations over the lake. The results of trace substance measurements (1/2 h mean values) were compared with values from comparison stations (suburban, high traffic and forest) located outside the area of the lake. In general, it was found that mean CO and NO concentrations over the lake were very low (0.3 ppm and 7.5 ppb, respectively). NO₂ values (15 ppb) were some 3.5 times higher than those recorded at the forest station and O₃ values, at 27 ppb, almost reached the same level as at the forest station (30 ppb). Mass flow densities as a function of wind direction, diurnal courses, differences between weekdays and weekends and comparisons with air quality standards are presented for the lake station.     

SO2-4/TiO2对SO2-C7H16-TiO2复相光化学反应的影响

研究了TiO2与SO2,C7H16复相光化学反应的光催化活性.在SO2-C7H16-O2-TiO2光催化反应过程中,TiO2表面可形成SO2-4/TiO2结构,它的存在可提高庚烷的光催化氧化速率,利用IR和XPS研究了反应过程中TiO2表面形成的SO2-4/TiO2结构.     

一种新去整合素Adinbitor的表达、序列分析及其对C6神经胶质瘤细胞凋亡的诱导

Adinbitor为一通过基因工程方法获得的来自于中国白眉蝮蛇毒腺的去整合素家族的新成员 .从蝮蛇毒腺中提取总RNA进行RT -PCR扩增 ,获得了 2 19bp的白眉蝮蛇去整合素基因 .cDNA测序及由此推导的氨基酸序列结果显示 ,Adinbitor为含有 73个氨基酸的多肽 ,其中包括 12个半胱氨酸 ,并具有去整合素的特征模序 -RGD .对此去整合素基因进行克隆、转化与诱导后 ,得到了该蛋白的可溶性高效表达 .经组氨酸亲和层析纯化 ,获得了分子量Mr为 9×10 3 的均质融合蛋白 ,并将其命名为adinbitor.序列分析表明 ,adinbitor与已发表于GENBANK上的整合素序列有很高的同源性 ,其中同源性最高的是南韩的saxatilin ,二者的蛋白质同源性高达 91.78% .活性测定结果表明 ,Adinbitor能有效地诱导神经胶质瘤细胞C6的细胞凋亡 ,有希望成为一种抗癌新药 .图 5参 15     

地衣芽孢杆菌(Bacillus licheniformis)对 Cr6+的吸附动力学研究

从污染土壤中分离出地衣芽孢杆菌(Bacilluslicheniformis),利用其死菌体对Cr6 溶液进行吸附动力学研究.在Ci=300mg/L、pH=2.5和θ=50℃条件下,吸附120min获得最大吸附量60.5mg/g.应用Langmuir和Freundlich吸附等温线研究,结果表明,Langmuir吸附等温线更为适合.动力学研究显示,地衣芽孢杆菌对Cr6 的吸附动力学可以用拟二级速度方程进行描叙.图3表4参14     

碘化物-罗丹明6G体系共振瑞利散射法测定痕量铅

在稀磷酸介质中 ,铅 (Ⅱ )与过量的I-离子形成 [PbI4]2 -配阴离子 ,并进一步与罗丹明 6G(Rh6G )形成离子缔合配合物 ,产生强烈的共振瑞利散射 (RRS )光谱 ,最大RRS波长位于 315nm 对共振瑞利散射光谱特性、主要影响因素和反应的最佳条件进行了研究 ,在 4 0× 10 -5%D 2 0× 10 -4μg·ml-1范围内 ,共振瑞利散射强度与铅的浓度成线性关系 ,实验结果表明 ,铅的检出限为 3 5× 10 -5μg·ml-1,可用于自来水中痕量铅的测定     

Degradation of the herbicide imazapyr by Fenton reactions

The degradation of the herbicide imazapyr has been carried out by three advanced oxidation processes involving iron ions as catalysts: Fentons reagent, photo-Fenton and electro-Fenton. We show that all processes are rapid and efficient. The kinetic rate constant was found to be k=5.4×10⁹ M^–1 s^–1. The mineralization of imazapyr is almost complete using the photo-Fenton and electro-Fenton processes.