实施污染物总量控制中的环境监测

随着经济的发展,由发展带来的污染问题也愈发的严重,如何治理和监测环境问题显得十分重要。文章旨在研究环境监测在对污染物总量控制上的作用做出分析,指出目前环境监测上存在的不足,提出建议和解决方案,更好的发挥环境监测的作用。     

亚甲蓝分光光度法测定水体阴离子表面活性剂方法的探讨

LAS是地表水和地下水水质的必测项目,国标（GB7494—87）方法操作复杂,要重复萃取四次后再洗涤,有机溶剂消耗量大,而且相当的耗时,本文通过同步实验对比与分析,得出：一次性加入20mL氯仿萃取加洗涤的方法其测定结果较好,而且极大地减轻了氯仿对分析人员身体的损害程度。测定结果有较好的精密度和准确度。本方法具有可观的经济性、安全性和可操作性。     

DELtatox便携式毒性测试仪在Q—TOX和B—TOX两种模式下应用与探讨

随着经济社会的发展,突发性水质污染事故日趋增多。因此能够快速、准确测定水质状况是环境应急监测的一项重要工作。在一起水厂取水口有人投药打鱼事故中,采用DELtatox便携式毒性测试仪在Q—TOX和B—TOX两种模式下快速检测事发地水质,结果表明快速、高效的检测为此次污染事故的成功处置提供了技术支持,为以后类似突发污染事故的应急监测提供了参考。     

皇甫川流域不同水土治理方式下土壤钾含量的变化

本文采用NaOH熔融法,原子吸收分光光度法和NH4OAc浸提,原子吸收分光光度法,分别测定了皇甫川流域五分地沟试验区不同植被治理措施下土壤的全K和速效K含量,对测定结果的分析表明：①不同治理措施下,土壤中全K含量的大小次序是：人工草地〉农田〉人工灌木〉退化草地〉次生草地〉人工林地〉百里香草原,土壤中速效K含量的大小次序是：人工林地〉百里香草原〉人工灌木〉退化草地〉农田〉次生草地〉人工草地。②不同治理方式对土壤钾含量提高的差异明显,灌草类植被对土壤钾的提高效果较好,杨树林对土壤钾的恢复效果稍差。     

室内污染物污染与控制

室内空气质量问题已经成为社会各界广泛关注的问题,如何有效地控制室内污染、改善室内空气质量是目前急待解决的问题.文章介绍了室内空气污染的特点、种类和来源,以及对人体的危害,并对传统方法如污染源控制、加强通风透气、植物净化等方法进行了探讨,另外还介绍了目前几种先进的室内环境净化处理技术及各技术的优缺点,进而对室内空气净化技术的发展趋势进行了展望.     

应用加载磁絮凝技术处理垃圾渗滤液试验研究

垃圾渗滤液是一种成分复杂多变的高浓度难处理有机废水。本研究采用加载磁絮凝技术对垃圾渗滤液进行预处理,并讨论了适宜的磁载体、凝聚剂和絮凝剂的加入量。     

基于功率法的结构⁃TMD减震控制分析∗

建立了结构-TMD振动方程,推导了无控结构和带TMD受控结构基于功率表达的运动方程,分别解释并给出了各种功率表达参数的物理意义,推导了随机激励下结构耗能功率流均值的随机表达式,对比分析了基于功率法的结构-TMD优化方法与其他优化方法的优化分析结果,并对其减震控制效果进行了对比分析。结果表明,结构-TMD系统的参数可以通过耗能功率流随机分析方法所得均值进行优化,且通过功率法优化后,结构在减震效果上优于其他传统方法得到的结果,从耗能功率均值的随机分析和时程功率分析角度证明了TMD控制的有效性;TMD做功功率为负时对结构有控制效果,起吸收转移能量的作用,且功率幅值越大控制效果越好,做功功率为正时则相反。     

苏南水库硅藻群落结构特征及其控制因素

为了解我国东南湿润区丘陵山地型水库硅藻的群落结构特征和控制因素,于2015年6月硅藻水华敏感期对苏南地区18座水库的浮游植物群落结构和水质进行调查,分析了营养盐、水深、库容等因素与硅藻及其它浮游生物的关系.结果表明,硅藻达到轻度水华水平(硅藻细胞含量介于100~1 000万cells·L~(-1))的水库有10座,对供水和景观功能产生明显影响;苏南地区水库普遍处于中营养和富营养水平,总氮浓度普遍偏高,磷及营养状态指数与硅藻生物量的关系密切;苏南地区水库中的浮游植物在数量上以蓝藻门中的席藻为主,在生物量上则以硅藻门、绿藻门和蓝藻门为主,其中硅藻门浮游植物平均占总浮游植物生物量的46.8%,是浮游植物异常增殖的主要门类;硅藻门中,主要是针杆藻、小环藻、曲壳藻和直链藻这4个种属占优,特别是针杆藻和小环藻,平均占硅藻总生物量的51.6%和21.4%;较深的水体,利于硅藻成为主要优势藻门;较大的水库流域库容比和较高总磷水平会导致水库营养水平和叶绿素浓度增加,促进浮游植物从硅藻门向绿藻门、蓝藻门演替,增加藻类危害的风险.因此,对于该地区水库,需要加强流域管理,并且针对水库自身的特点,包括水深、流域库容比等,确定其特定的富营养化控制策略,从而减少硅藻等藻类水华发生的风险,提升水源地水质安全保障能力.     

Expression of sulfur uptake assimilation-related genes in response to cadmium, bensulfuron-methyl and their co-contamination in rice roots

The responses of sulfur （S） uptake assimilation-related genes＇ expression in roots of two rice cultivars to cadmium （Cd）, bensulfuron-methyl （BSM） and their co-contamination （Cd＋BSM） were investigated by gene-chip microarray analysis and quantitative real-time PCR （QRT-PCR） technology. Treatments of Cd and Cd＋BSM induced expression of sulfate transporter and permease genes, and promoted sulfate uptake in rice roots. Cd＋BSM could alleviate Cd toxicity to cv. Fengmeizhan seedlings, probably due to Cd＋BSM promoting greater S absorption by seedlings. Cd and Cd＋BSM induced expression of sulfate assimilation-related genes, and thus activated the sulfur assimilation pathway. Cd and Cd＋BSM induced expression of phytochelatin synthase and metallothionein genes, and induced expression of glutathione S-transferases （GSTs）, glutathione synthase （GS） and S- containing antioxidation enzyme genes, which detoxified Cd2＋. It is suggested that （to cope with the toxicity of Cd, BSM and their co-contamination） the S uptake and assimilation pathway was activated in rice roots by increased expression of related genes, thus enhancing the supply of organic S for synthesis of Cd or BSM resistance-related substances.     

Removal of phosphate from wastewater using alkaline residue

Alkaline residue(AR) was found to be an efficient adsorbent for phosphate removal from wastewater. The kinetic and equilibrium of phosphate removal were investigated to evaluate the performance of modified alkaline residue. After treatment by NaOH(AR-NaOH), removal performance was significantly improved, while removal performance was almost completely lost after treatment by HCl(AR-HCl). The kinetics of the removal process by all adsorbents was well characterized by the pseudo second-order model. The Langmuir model exhibited the best correlation for AR-HCl, while AR was effectively described by Freundlich model. Both models were well fitted to AR-NaOH. The maximum adsorption capacities calculated from Langmuir equation were in following manner: AR-NaOH AR AR-HCl. Phosphate removal by alkaline residue was pH dependent process. Mechanisms for phosphate removal mainly involved adsorption and precipitation, varied with equilibrium pH of solution. For AR-HCl, the acid equilibrium pH( 6.0) was unfavorable for the formation of Ca-P precipitate, with adsorption as the key mechanism for phosphate removal. In contrast, for AR and ARNaOH, precipitation was the dominant mechanism for phosphate removal, due to the incrase on pH( 8.0) after phosphate removal. The results of both XRD and SEM analysis confirmed CaHPO4·2H2O formation after phosphate removal by AR and AR-NaOH.