混凝—气浮工艺处理有机物污染地下水现场中试试验

对某农药厂原厂区的有机污染地下水的水质特征进行了分析,采用小试确定了药剂投加量,并采用中试装置考察了混凝—气浮工艺的去除效果。小试结果表明,聚合氯化铝（PAC）的最佳投加量为300 mg/L,聚丙烯酰胺（PAM）的最佳投加量为3 mg/L。中试运行结果表明,当进水流量为0.25 ~1.00 m3/h时,对浊度的去除率为82.66%~90.13%,对悬浮固体的去除率为80.12%~90.11%;碳原子数在10~28范围内的石油烃的平均去除率为38.96%~51.46%;1,2-二氯乙烷、2-甲基萘、苯、萘、甲苯、邻苯二甲酸二甲酯的平均去除率分别为17.76%,67.49%,48.70%,54.56%,37.24%,62.53%。     

一起110 kV变压器高温过热故障综合分析及诊断

讲述了一起110 kV电力变压器内部发生高温过热故障后的分析和诊断过程,文章通过多种溶解气体分析法如特征气体法、三比值法、四比值法、总烃安伏法等对故障进行分析,准确判断了故障类型、严重程度,并准确判断出故障的大概发生部位,从而对设备的运行及检修提出策略参考,并在设备解体中印证了检修前的分析和判断,确保了设备和电网的安全稳定运行。     

全玻璃针筒注射器保存空气中甲烷和总烃的影响因素

采用全玻璃针筒取样/保存、双通道双毛细管柱测定非甲烷总烃分析方法,以甲烷标准气体样品、标准气体样品(TO-14、TO-15),以及3种实际环境空气样品为例,考察了全玻璃针筒注射器取样保存影响检测结果的若干因素。结果表明,样品的保存时间取决于以下因素:(1)样品性质,不同类型样品的保存时间差异大,化学反应活性强的样品,其总烃含量呈现先升高后降低趋势,甲烷则相对稳定;(2)样品浓度水平,相同条件下相同类型样品,浓度高的保存时间短于低浓度样品,如与环境空气浓度相仿的样品保存时间可超过60 h;(3)保存环境的避光程度,对于同一种VOCs标准气体样品,避光、半避光、非避光保存样品回收率迥异,趋势差别极大,对于部分样品即便是避光保存仍发现回收率变化极大;(4)全玻璃材质注射器的气密性,需对照技术规范要求,进行气密性的检查。     

加速溶剂萃取-高效液相色谱法测定土壤中16种多环芳烃

研究了土壤中的16种多环芳烃的提取和测定方法.结果表明,用加速溶剂提取仪在100℃,二氯甲烷和丙酮(1:1)提取5min,再经硅胶柱净化,正己烷和二氯甲烷(3:2)洗脱,25℃氮吹浓缩后用高效液相色谱测定可以得到很好的效果,方法回收率在58%～106%之间,检测限为1.4×10-4～3.6×10-2mg/kg,且重现性好.     

土壤石油烃污染的植物毒性及植物-微生物联合降解

通过盆栽实验研究了土壤石油烃污染对玉米和水稻根伸长的影响,并在土壤中接种经过筛选得到的石油烃降解菌,研究石油烃降解菌对石油烃毒性的影响以及对土壤中石油烃的降解。研究结果表明,石油烃浓度低于1 000 mg/kg时对玉米的根系生长有一定的刺激生长作用,随着石油烃浓度的增加,刺激根长生长的作用逐渐降低,研究结果表明,水稻根长受石油烃影响较小。通过对不同处理土壤中石油烃降解的研究结果表明,土壤中种植水稻对石油烃有一定的降解作用,但是不同处理下土壤中的石油烃降解率不同,其中水稻微生物联合处理下土壤中石油烃的降解速率最快,培养期内的降解效率达到53.3%。     

轻烃回收装置大检修动火风险管控措施探讨

针对轻烃回收装置火灾爆炸事故大部分发生在维检修阶段的现象,通过结合生产实际,提出采用动火前施工工序确认制度,严控高风险点位,避免"立体交叉"动火作业等措施,杜绝经验主义和侥幸心理,最大限度避免动火作业着火爆炸事故的发生。文章介绍了轻烃回收装置的介质特点及主要工艺,分析了轻烃回收装置大检修基本流程及动火风险,提出控制动火施工安全风险的管理实践。     

ASE萃取-SPE净化-HPLC法测定土壤中多环芳烃

建立了加速溶剂萃取-固相萃取净化-高效液相色谱测定土壤中16种多环芳烃的方法,优化了试验条件.方法线性关系良好,16种多环芳烃的检出限在0.412 ng/g～3.974 ng/g之间,空白加标试验的相对标准偏差在1.2%～12.7%之间,基质加标回收率在60.4%～126%之间.实际样品的测定结果表明该方法分离效果好,能够满足土壤分析的要求.     

加油站的烃类VOCs污染及其治理技术

加油站因储运轻质油品而产生的烃类VOCs对健康、环境、安全以及油品质量等带来了一系列负面影响.发达国家的常规治理措施主要是进行密闭卸油和密闭发油,对加油站的设备安装、管线布置、运营管理等都有一些具体要求;进入21世纪后美国又提出了强化加油站油气回收处理的观点,相应的技术、设备及法规也都日益健全.国内目前对加油站烃类VOCs污染的治理工作与发达国家相比差距很大,应该尽快从烃类VOCs回收处理的专用膜分离装置入手进行相关研究和产品开发.     

Variation in indoor levels of polycyclic aromatic hydrocarbons from burning various biomass types in the traditional grass-roofed households in Western Kenya

Biomass burning as fuel in the traditional grass-roofed rural households of Western Province of Kenya in open fire places, in poorly ventilated conditions, lead to accumulation of soot under the roofs. This study characterized and quantified the polycyclic aromatic hydrocarbons (PAHs) in accumulated soot in these households and determined the variation in PAHs concentrations with fuel biomass type. Soot samples collected from the households were extracted, cleaned and analysed by gas chromatography. The PAHs were identified using retention times, verified by gas chromatographic mass spectral analysis and quantified from peak area responses using the internal standard method. The PAHs levels significantly varied (P ≤ 0.05) with biomass type in the order: dung ≥ indigenous trees ≥ exotic trees ≥ shrubs and crop residues. Use of dung and wood from indigenous trees as fuel should be discouraged since they are higher emitters (P ≤ 0.05) of carcinogenic PAHs.     

Sorption of polycyclic aromatic hydrocarbons (PAHs) on glass surfaces

Sorption of polycyclic aromatic hydrocarbons (PAHs) to glass commonly used in laboratories was studied. Sorption coefficients (K_d) of five selected PAHs to borosilicate glass surfaces were measured using column chromatography. A linear relationship between log K_d and the corresponding water solubility of the subcooled liquid (log S_w) of the investigated PAHs was observed. Based on the determined sorption coefficients our data revealed that mass loss caused by sorption on glass walls strongly depends on the ratio of solution volume to contacted surface area (V/S). The influence of solution chemistry such as ionic strength, solution pH, presence of cosolvent, and the influence of temperature on the sorption process were investigated. In the presence of ionic strength, sorption coefficients concurrently increased but less than a factor of 2 up to 0.005 M calcium chloride concentration. However, further increasing ionic strength had no influence on K_d. The cosolvent reduced sorption at a concentration of methanol in water above 0.5% (v/v); however, for benzo[a]pyrene even with 10% (v/v) methanol the mass loss would be still higher than 10% (with a V/S ratio less than 0.25). Significant effects of the solution pH and temperature were not observed. These results suggest that van der Waal’s forces dominate the sorption process. In the analysis of highly hydrophobic PAHs in aqueous samples, mass loss due to sorption on glass walls should be accounted for in the final result if untreated glass is used. The presented relationship between log K_d and log S_w may help to decide if such a correction is necessary. Furthermore, the frequently used silanization of glass surfaces may not be sufficient to suppress sorption for large PAHs.