长江南京段水质自动监测点位优化

简述了长江南京段监测断面现状,用相关分析与聚类分析方法对水质监测数据进行了统计分析,对长江南京段水质自动监测优化布点提出了相关建议。     

采样条件对固定排放源废气中氯化氢测定的影响

研究了采样条件对固定排放源废气中氯化氢测定的影响。结果发现,采样条件对测定的准确度影响极大,过低的吸收液浓度会导致测定结果严重偏低,进入吸收装置的气体温度过低时也会导致测定结果偏低。目前常用的采样条件(包括有些标准中规定的采样条件)都不合适。推荐合适的Na OH吸收液浓度为2.0 mol/L,合适的进入吸收装置的气体温度为110℃以上。     

顶空-气相色谱法测定地表水中松节油

采用顶空-气相色谱法测定地表水中松节油,并对顶空瓶的平衡温度、平衡时间,盐析效应和取样量等顶空条件进行优化,使方法在0.200 mg/L~4.00 mg/L范围内线性良好,方法检出限为0.037 mg/L。实际样品2个质量浓度水平的加标回收率为89.3%~108%,RSD分别为5.8%和4.8%。     

燃煤电厂烟气中汞的采集与分析方法

汞的测试技术包括采样和分析两部分,其中汞含量的分析方法已经相对比较成熟,限制测试技术发展的诸多问题主要来源于取样过程。根据不同的取样方式,将现有测试技术分为湿式采样分析法、干式采样分析法以及在线分析技术3种,重点介绍了3种方法的采样原理、系统构成、过程的影响因素以及适用范围。最后针对CVAAS、CVAFS、AES 3种汞含量测定技术在Hg CEMS测试系统中的应用进行了对比介绍。     

太湖蓝藻预警采样点位布设与采样层次的研究

蓝藻水华的聚集和分布与气象条件有着密切的关系.根据近几年蓝藻预警监测及科研的实践,分析了风向对蓝藻迁移的影响,以及不同深度的藻密度变化情况.以此为依据,对太湖蓝藻监测时采样点位布设与采样层次选择的方案进行了比较研究,并提出了优化方案,为环太湖地区的相关部门更好地开展蓝藻预警监测工作提供了科学依据.     

污染场地土壤初步调查布点及采样方法探讨

结合我国污染场地的普遍特征以及场地初步调查的基本目标,从布点前期准备、布点原则、布点程序和布点方法等方面详细探讨了污染场地土壤初步调查的点位布设方法;并从采样准备、采集方法、采集程序以及现场记录等环节探讨了现场样品采集的注意事项和要求,以期为污染场地环境调查的土壤监测和采样提供借鉴。     

被动采样监测环境空气中SO2和NO2

用自主研制的采样管开展环境空气中SO2和NO2的被动采样监测.结果表明,被动采样监测结果与自动监测结果高度相关,经回归方程修正后,两者的结果没有显著性差异,被动采样的采样和分析产生的误差得以消除.     

Herbicide promotes the conjugative transfer of multi-resistance genes by facilitating cellular contact and plasmid transfer

The global dissemination of antibiotic resistance genes(ARGs), especially via plasmidmediated horizontal transfer, is becoming a pervasive health threat. While our previous study found that herbicides can accelerate the horizontal gene transfer(HGT) of ARGs in soil bacteria, the underlying mechanisms by which herbicides promote the HGT of ARGs across and within bacterial genera are still unclear. Here, the underlying mechanism associated with herbicide-promoted HGT was analyzed by detecting intr...     

Assessment of polychlorinated dibenzo-p-dioxin and dibenzofuran emissions from a hazardous waste incineration plant using long-term sampling equipment

The aim of this work is to evaluate the performance of a continuous monitoring system for the analysis of the mass concentration of PCDD/Fs from stationary sources. Data was acquired from a modern, state of the art, hazardous waste thermal treatment plant for a period of more than 2 years using a commercial available continuous monitoring system. The study consisted of a total of 16 samples, collected in periods from 1 week to 2 months resulting in an average of 360 m³ sampled flue gas per sample. The study showed the system was able to confirm that for a period of more than 2 years the plant was complying with the limit of 0.1 ng I-TEQ/Nm³. In addition, the data showed the typical fingerprint of such installations which is useful for example in impact studies. Long-term samples were compared to five short-term samples (6 h) collected every 6 months during the study period. Principal component analysis was applied to PCDD/Fs obtained data as useful statistical tool to find out trends and similarities between different samples. Improvement in terms of representativeness of data was achieved through continuous assessment since the starts of the project. The obtained data was further used to determine the emission factor for this activity and the total annual PCDD/Fs release to the atmosphere.     

Determination of deployment specific chemical uptake rates for SDB-RPD Empore disk using a passive flow monitor (PFM)

The use of the adsorbent styrenedivinylbenzene-reverse phase sulfonated (SDB-RPD) Empore disk in a chemcatcher type passive sampler is routinely applied in Australia when monitoring herbicides in aquatic environments. One key challenge in the use of passive samplers is mitigating the potentially confounding effects of varying flow conditions on chemical uptake by the passive sampler. Performance reference compounds (PRCs) may be applied to correct sampling rates (R_s) for site specific changed in flow and temperature however evidence suggests the use of PRCs is unreliable when applied to adsorbent passive samplers. The use of the passive flow monitor (PFM) has been introduced for the assessment of site-specific changes in water flow. In the presented study we have demonstrated that the R_s at which both atrazine and prometryn are accumulated within the SDB-RPD-Empore disk is dependent on the flow conditions. Further, the calibration of the measured R_s for chemical uptake by the SDB-RPD-Empore disk to the mass lost from the PFM has shown that the PFM provides an accurate measure of R_s for flow velocities from 0 to 16 cm s⁻¹. Notably, for flow rates >16 cm s⁻¹, a non linear increase in the R_s of both herbicides was observed which indicates that the key resistance to uptake into the SDB-RPD Empore disk is associated with the diffusion through the overlying diffusion limiting membrane. Overall the greatest uncertainty remains at very low flow conditions, which are unlikely to often occur in surface waters. Validation of the PFM use has also been undertaken in a limited field study.