一起液氯泄漏事故的分析及预防对策

针对国内近年来氯气泄漏、爆炸事故频发的现状,选择其中具有典型性的江西某厂氯气泄漏事故,运用因果分析方法对其事故原因进行系统分析,根据分析结果,以降低事故发生概率和严重度为目标,从管理角度提出预防对策.     

石油污染对牡蛎超显微结构毒性效应的研究

采用电子显微镜观察石油污染对牡蛎生殖腺和肝胰腺组织细胞的毒性作用。结果显示,石油污染对牡蛎具有明显的慢性毒害作用,50 mg／L浓度组,实验10 d的牡蛎,其组织细胞受石油污染不明显;当实验时间为30 d时,出现明显的毒性效应,细胞核核膜肿胀,染色质聚集并边际化,细胞核崩解,细胞坏死,组织萎缩,线粒体的变化较其他细胞器对石油污染较敏感,受损坏的程度较重。     

“十四五”时期污染物总量控制的挑战、需求与应对研究

"十四五"时期是进一步巩固和提升环境质量改善成果、切实改善人民群众生存环境的关键时期。展望"十四五",应从发展的视角看总量控制与环境质量控制所面临的问题与困难,在考虑历史因素的基础上兼顾地区间的公平与效率,切实发挥环境管理对高质量发展的推动作用,迈向"环境质量导向的总量控制"。要落实改进总量控制和质量控制效果的新举措,进一步推动建立环境质量与总量控制的量化联动关系,推动城市—单元—行业的精细化总量控制管理,丰富总量控制要素,强化服务于总量控制的能力建设,建立总量控制目标下公平的环境责任划分制度。     

宽滩型河流生态系统服务价值核算——以辽河干流为例

为解决线状河流生态系统服务价值核算长期停留在均一性核算,难以体现空间差异性的问题,整合高精度遥感数据和常规数据,区分源于河槽、滩地和河流整体3种空间的生态系统服务类型,梳理GIS平台运算的方法和参数,构建了宽滩型河流生态系统服务价值空间核算成套方法,并应用于辽河干流。结果表明:2013年辽河干流生态系统服务总价值为537.39亿元,其中洪水调蓄服务占比最高(46.99%),其次是气候调节服务(29.22%);不同土地利用类型单位面积生态系统服务价值存在差异,河槽和坑塘较高,旱地、灌木林、有林地、草地、滩涂和水田较低且数值接近;2013年辽河干流生态系统服务总价值比2009年增长了101.63亿元;辽河干流流经的铁岭、沈阳、鞍山和盘锦4个市中,单位面积生态系统服务价值和生态系统服务总价值均以辽河口的盘锦市为最高。     

天津中东部平原区土壤盐分空间分布特征

土壤盐渍化是滨海地区生态保护修复的重要影响因素。为了解天津平原地区土壤盐渍化程度,沿永定新河、海河干流和独流减河3条入海河流海陆方向开展堤外土壤盐分采样调查,结合地统计学和GIS技术,分析海陆方向土壤盐分的空间梯度和变异特征,以期为天津生态保护修复和陆海统筹提供科学依据。结果表明:土壤水溶性盐含量和碱化度整体呈自东南向西北递减的趋势;重度及以上盐渍化土主要分布在海岸线向陆地纵深15 km的滨海新区,其中盐土、重度碱化土主要分布在大港距海10 km内、塘沽与汉沽距海5 km内;中度盐渍化土主要分布在独流减河沿线距海15~60 km内;轻度盐渍化土主要分布在海河干流沿线距海10~60 km内。土壤阳离子以Na+为主;从海岸线向陆域方向,土壤阴离子从以Cl-、 SO 4 2 - 为主逐步过渡到以 SO 4 2 - 、 CO 3 2 - + HCO 3 - 为主。独流减河一线盐渍土类型以硫酸盐-氯化物和氯化物-硫酸盐为主;海河干流中部平原区盐渍土类型以硫酸盐-苏打为主;永定新河一线盐渍土类型以硫酸盐-氯化物和苏打-硫酸盐为主。     

基于GIS的太原市街道机动车污染物空间分布特征分析

在研究太原市机动车污染现状的基础上,结合太原市机动车排放因子模型Mob ile6和污染物扩散模型OSPM的计算结果,在G IS平台上绘制了太原市冬夏两季道路机动车污染物排放强度分布图和道路交通污染物浓度分布图,并对可视化结果作了科学的分析,研究结果表明：（1）太原市冬季街道污染总体上要高于夏季,这种趋势以CO的表现尤为明显;（2）街道NOX小时浓度超标率比CO小时浓度超标率更高,在研究的56条路段中,CO小时浓度都没有超过国家二级标准,NOX小时浓度超标率达38.9%（夏季）;（3）NOX污染主要集中在中心区,而建成区周边道路某些路段污染也较严重。     

Extracellular polymeric substance induces biogenesis of vivianite under inorganic phosphate-free conditions

Vivianite is often found in reducing environments rich in iron and phosphorus from organic debris degradation or phosphorus mineral dissolution. The formation of vivianite is essential to the geochemical cycling of phosphorus and iron elements in natural environments. In this study, extracellular polymeric substances (EPS) were selected as the source of phosphorus. Microcosm experiments were conducted to test the evolution of mineralogy during the reduction of polyferric sulfate flocs (PFS) by Shewanella oneidensis MR-1 (S. oneidensis MR-1) at EPS concentrations of 0, 0.03, and 0.3 g/L. Vivianite was found to be the secondary mineral in EPS treatment when there was no phosphate in the media. The EPS DNA served as the phosphorus source and DNA-supplied phosphate could induce the formation of vivianite. EPS impedes PFS aggregation, contains redox proteins and stores electron shuttle, and thus greatly promotes the formation of minerals and enhances the reduction of Fe(III). At EPS concentration of 0, 0.03, and 0.3 g/L, the produced HCl-extractable Fe(II) was 107.9, 111.0, and 115.2 mg/L, respectively. However, when the microcosms remained unstirred, vivianite can be formed without the addition of EPS. In unstirred systems, the EPS secreted by S. oneidensis MR-1 could agglomerate at some areas, resulting in the formation of vivianite in the proximity of microbial cells. It was found that vivianite can be generated biogenetically by S. oneidensis MR-1 strain and EPS may play a key role in iron reduction and concentrating phosphorus in the oligotrophic ecosystems where quiescent conditions prevail.     

Dosing low-level ferrous iron in coagulation enhances the removal of micropollutants, chlorite and chlorate during advanced water treatment

Drinking water utilities are interested in upgrading their treatment facilities to enhance micropollutant removal and byproduct control. Pre-oxidation by chlorine dioxide (ClO₂) followed by coagulation-flocculation-sedimentation and advanced oxidation processes (AOPs) is one of the promising solutions. However, the chlorite (ClO₂^–) formed from the ClO₂ pre-oxidation stage cannot be removed by the conventional coagulation process using aluminum sulfate. ClO₂^– negatively affects the post-UV/chlorine process due to its strong radical scavenging effect, and it also enhances the formation of chlorate (ClO₃^–). In this study, dosing micromolar-level ferrous iron (Fe(II)) into aluminum-based coagulants was proposed to eliminate the ClO₂^– generated from ClO₂ pre-oxidation and benefit the post-UV/chlorine process in radical production and ClO₃^– reduction. Results showed that the addition of 52.1-µmol/L FeSO₄ effectively eliminated the ClO₂^– generated from the pre-oxidation using 1.0 mg/L (14.8 µmol/L) of ClO₂. Reduction of ClO₂^– increased the degradation rate constant of a model micropollutant (carbamazepine) by 55.0% in the post-UV/chlorine process. The enhanced degradation was verified to be attributed to the increased steady-state concentrations of HO^· and ClO^· by Fe(II) addition. Moreover, Fe(II) addition also decreased the ClO₃^– formation by 53.8% in the UV/chlorine process and its impact on the formation of chloro-organic byproducts was rather minor. The findings demonstrated a promising strategy to improve the drinking water quality and safety by adding low-level Fe(II) in coagulation in an advanced drinking water treatment train.     

Identification and characterization of Fe3O4/peroxodisulfate advanced oxidation products from sulfameter

Sulfonamides (SAs) are one of the most widely used antibiotics and their residuals in the environment could cause some negative environmental issues. Advanced oxidation such as Fenton-like reaction has been widely applied in the treatment of SAs polluted water. Degradation rates of 95%-99.7% were achieved in this work for the tested 8 SAs, including sulfisomidine, sulfameter (SME), phthalylsulfathiazole, sulfamethoxypyridazine, sulfamonomethoxine, sulfisoxazole, sulfachloropyridazine, and sulfadimethoxine, in the Fe₃O₄/peroxodisulfate (PDS) oxidation system after the optimization of PDS concentration and pH. Meanwhile, it was found that a lot of unknown oxidation products were formed, which brought up the uncertainty of health risks to the environment, and the identification of these unknown products was critical. Therefore, SME was selected as the model compound, from which the oxidation products were never elucidated, to identify these intermediates/products. With liquid chromatography-high resolution tandem mass spectrometry (LC-HRMS/MS), 10 new products were identified, in which 2-amino-5-methoxypyrimidine (AMP) was confirmed by its standard. The investigation of the oxidation process of SME indicated that most of the products were not stable and the degradation pathways were very complicated as multiple reactions, such as oxidation of the amino group, SO₂ extrusion, and potential cross-reaction occurred simultaneously. Though most of the products were not verified due to the lack of standards, our results could be helpful in the evaluation of the treatment performance of SAs containing wastewater.