多氯二苯并-对-二噁英(PCDDs)半定量标准的制备

以热聚法合成,柱色谱纯化,配制了几种PCDDs的半定量标准,并对其进行了评价。     

微波法制取锯末活性炭及其吸附Cr~(6 )性能的研究

介绍了微波照射—氯化锌法(ZCMR)制取锯末活性炭的方法。用该法所制锯末活性炭处理含铬废水的结果表明,该锯末活性炭具有吸附容量大、过滤速度快、操作控制方便等优点,活性炭对铬的吸附容量是市售一级粉末活性炭的1.72倍,极限吸附量达21.5mg/g,过滤速度为市售活性炭的1.64倍。     

稻壳吸附剂净化水中有机污染物的研究

以酸处理稻壳为原料，研究了稻壳吸附剂的活化工艺，所制备的吸附剂对水中芳香化合物和杂环染料均有较大的吸附能力。通过试验得出了吸附剂净化水中芳香化合物及染料的最佳条件     

电磁屏蔽织物的制备及应用

本文介绍了电磁屏蔽织物的制备技术和国外电磁屏蔽织物的产品开发概况。     

云南省土壤污染状况调查中土壤样品制备

主要介绍了土壤采集后的混合样品和单独样品制备过程，并根据不同的分析项目采用不同粒径的过筛样品。统一规范操作，确保数据的准确性和可比性。     

用生产草酸产生的废草酸泥渣制备铬酸铅的工艺研究

用生产草酸产生的废草酸泥渣,通过采用以加热转化,硝酸溶解提取,重铬酸钠合成为主要步骤的制备新工艺,用草酸泥渣制得了铬酸铅.对用草酸泥渣制备铬酸铅的工艺原理进行了分析.本文着重研究了原料粒度、反应温度、反应时间和硝酸用量等因素对产品产量和铬酸铅含量的影响.     

用三聚氰胺生产中排放的固体废物制备三聚氰酸

对三聚氰胺生产企业产生的固体废物利用进行了研究。研究发现 ,在自生压力下可以由三聚氰胺生产过程中排放出的固体废弃物酸解制备三聚氰酸 ;添加酸式硫酸盐在低硫酸浓度下水解几乎能达到高硫酸浓度下水解的效果 ;固体废弃物酸解时 ,反应温度升高、反应时间延长和NaHSO4用量增加都会提高三聚氰酸的收率 ;酸解过程中 ,反应温度对收率有显著影响 ,而反应时间、硫酸氢钠的用量对收率影响不显著 ;在 160℃、NaHSO4用量为 10 0g时反应 4h ,三聚氰酸的收率可达 67%     

铝质固体废料制取聚合氯化铝及絮凝脱色性能

采用酸溶一步法利用三种铝质固体废料制取了聚合氯化铝。实验表明 :该法生产聚合氯化铝 ,工艺可行 ,产品主要指标满足国家标准 (GB1 5892 95)的要求 ,所制的PAC对模拟染料废水的絮凝效果与用AlCl3.6H2 O制成的聚合氯化铝的相当。     

制备条件对硅胶负载氧化锆吸附除氟的影响

应用浸渍法制备了硅胶负载氧化锆除氟吸附剂,研究了焙烧温度、硅胶粒度、浸渍时间、浸渍温度、浸渍液浓度、浸渍固液比和浸渍次数等制备参数对吸附剂吸附容量的影响.实验发现焙烧温度有较大影响,450℃焙烧有最大的吸附量,再升高温度吸附量迅速下降.浸渍可在2h内达到平衡.浸渍温度越高,浸渍液浓度越高,则吸附容量越大.采用较高浓度一次浸渍优于低浓度多次浸渍.硅胶粒度和浸渍固液比也影响吸附量,粒度越大吸附量越小,粒度小于0.25mm后吸附量趋于稳定.     

Behavior of PAHs during cold storage of historically contaminated soil samples

The stability of historically polycyclic aromatic hydrocarbon (PAH)-contaminated soils during cold storage was investigated. Samples from two former manufactured gas plants exhibited quantitative recoveries of PAHs over the whole period of sample holding at 4 °C in the dark (8–10 months), whereas significant losses of PAHs were observed for soils received from a former railroad sleeper preservation plant with low molecular weight compounds being notably more affected compared to heavier PAHs. Already after 2 weeks of holding time, 3-ring PAHs in one of theses samples were down to 29–73% of the initial concentration and significant losses were observed for up to 5-ring compounds. Dissipation of PAHs was found to be predominantly due to aerobic microbial metabolism since sodium azide poisoned samples showed quantitative recoveries for all PAHs over the entire storage time of 3 months. A similar stabilizing effect was observed for freezing at −20 °C as means of preservation. Except for acenaphthene, no significant loss for any of the PAHs was observed over 6 weeks of holding time. Eventually, selected chemical, physical, and biological parameters of two soils were investigated and identified as potential indicators for the stability of PAH-contaminated soil samples.