Characteristics of plankton Hg bioaccumulations based on a global data set and the implications for aquatic systems with aggravating nutrient imbalance

• Hg bioaccumulation by phytoplankton varies among aquatic ecosystems. • Active Hg uptake may exist for the phytoplankton in aquatic ecosystems. • Impacts of nutrient imbalance on food chain Hg transfer should be addressed. The bioaccumulation of mercury (Hg) in aquatic ecosystem poses a potential health risk to human being and aquatic organism. Bioaccumulations by plankton represent a crucial process of Hg transfer from water to aquatic food chain. However, the current understanding of major factors affecting Hg accumulation by plankton is inadequate. In this study, a data set of 89 aquatic ecosystems worldwide, including inland water, nearshore water and open sea, was established. Key factors influencing plankton Hg bioaccumulation (i.e., plankton species, cell sizes and biomasses) were discussed. The results indicated that total Hg (THg) and methylmercury (MeHg) concentrations in plankton in inland waters were significantly higher than those in nearshore waters and open seas. Bioaccumulation factors for the logarithm of THg and MeHg of phytoplankton were 2.4–6.0 and 2.6–6.7 L/kg, respectively, in all aquatic ecosystems. They could be further biomagnified by a factor of 2.1–15.1 and 5.3–28.2 from phytoplankton to zooplankton. Higher MeHg concentrations were observed with the increases of cell size for both phyto- and zooplankton. A contrasting trend was observed between the plankton biomasses and BAF_MeHg, with a positive relationship for zooplankton and a negative relationship for phytoplankton. Plankton physiologic traits impose constraints on the rates of nutrients and contaminants obtaining process from water. Nowadays, many aquatic ecosystems are facing rapid shifts in nutrient compositions. We suggested that these potential influences on the growth and composition of plankton should be incorporated in future aquatic Hg modeling and ecological risk assessments.     

含硝基苯、苯胺废水处理的工程实践

采用固定化微生物-曝气生物滤池与铁-炭微电解法联用的工艺方法处理含硝基苯、苯胺的废水。通过培养驯化微生物阶段、半负荷进水阶段、满负荷进水阶段的调试运行,表明:当进水CODCr<1 000mg/L、硝基苯<120mg/L、苯胺<30mg/L时,出水可达到CODCr<300mg/L、硝基苯<5mg/L、苯胺<5mg/L的设计要求。铁-炭微电解法在pH值为3～4时,对废水有一定的脱色作用,但pH值升高后脱色效果不明显。     

消费电子产品生产过程中挥发性有机物(VOCs)排放特征的研究

选取塑胶零件、印刷线路板及主板3类消费电子产品部件为研究对象,利用活性炭管采样,样品溶剂解吸后采用GC/MS分析,获得了各排气筒及车间内VOCs含量水平与组分特征.通过计算排放量,得出了分物种VOCs排放系数.结果表明,塑胶零件生产线排气筒总挥发性有机物(TVOCs)浓度为48.01~115.05 mg·m-3,印刷线路板为6.08~11.36 mg·m-3,主板为29.81~30.21 mg·m-3.塑胶零件生产车间内TVOCs浓度为4.23~120.58 mg·m-3,印刷线路板为1.50~2.02 mg·m-3,主板为7.01~9.93 mg·m-3.环烷烃类、酯类、苯类为主要排放物质.对于不同产品生产线的排气筒及车间废气,浓度和物种均有很大差异;对于相同产品,浓度有差异但物种基本相同.按产品分类,共计算得出了36个分物种VOCs排放系数,其中,塑胶零件、印刷线路板及主板TVOCs排放系数分别为0.626 kg·kg-1涂料用量、0.123 kg·kg-1油墨用量、0.028 kg·kg-1印刷线路板用量.通过排放量计算结果分析,3种产品中,塑胶零件生产为VOCs主要排放源,车间内无组织排放为主要排放方式.     

低温下生物陶粒反应器去除水源水中氨氮的研究

利用生物陶粒预处理工艺,研究低水温条件下生物陶粒反应器对氨氮的去除效果.进水氨氮浓度为0.5～1.4mg/L,水力停留时间为20～30min.结果表明,低温条件下,生物陶粒反应器对进水中氨氮的去除效果随着水温的下降而降低,但总体上对氨氮仍然有较好的去除效果.当水温从10℃下降到0.4℃时,生物陶粒反应器对氨氮的去除率从90%下降到65%.当水温在3℃以上时,出水中NO₂^--N低于进水NO₂^--N的含量.当水温下降到3℃以下后,出水中NO₂^--N超过了进水中NO₂^--N的含量.在陶粒反应器内部出现了NO₂^--N积累现象,水温越低,出水NO₂^--N的含量越高.     

环境矿物材料在微污染水处理中的应用前景

自来水厂传统工艺对水中微量有机物没有明显的去除效果，常规净化工艺也很难去除重金属离子和氨氮等涪染物。环境矿物材料具有来源广泛和良好的使用性能、无生态副作用等特点，对微污染水具有较好的处理效果。本文论述了沸石和磷灰石对污染物的去除机理，探讨了基于环境矿物材料的人工快滤系统在净化微污染水中的应用前景。     

SAF-化学絮凝-微滤膜组合工艺处理高浓度生活污水的试验研究

采用SAF-化学絮凝-微滤分离膜组合工艺对高浓度生活污水进行处理.SAF处理系统对污染物的去除效果良好,CODCr,BOD5,SS和NH4 -N的去除率分别为92%,93%,90%和98%.SAF生物处理系统的出水再经化学絮凝和微滤分离膜深度处理后,CODCr,BOD5,NH4 -N,PO43--P的浓度分别低于40 mg/L,10mg/L,4mg/L,0.3mg/L;浊度小于0.5NTU,色度小于10度.试验结果表明该组合工艺处理后的污水水质优良,可满足生活杂用和市政杂用.     

温州临江垃圾焚烧发电厂飞灰的性质研究

研究了温州临江垃圾焚烧发电厂生活垃圾焚烧产生飞灰的物理和化学性质。飞灰为含水率低、颗粒尺寸集中在43~175μm之间的灰色粉末,主要由Si、Al、Ca、Mg、Fe、Na、K、C和S元素组成。飞灰中Pb、Cd的浸出浓度在酸性条件下都不同程度地高于我国危险废物鉴别标准的允许浓度,其中Pb的浸出浓度在pH值1.06~13.69条件下远远超标,碱性条件下浸出毒性比酸性条件下小。矿物组成主要为石英(SiO2)、赤铁矿αFe2O3、钙长石CaO.Al2O3.2SiO2、钙铝黄长石2CaO.Al2O3.SiO2、KCl、NaCl、CaCO、PbO、TiO2、ZnCO3等,溶解盐含量高达19.5%,化学反应活性较强,热稳定性较差。     

伊洛河流域河水来源及水化学组成控制因素

伊洛河是黄河中游南岸重要支流,由伊河和洛河在洛阳偃师汇合而成.流域上游矿产资源开采活动较多,下游城镇密集,工农业活动分布广泛.为探究不同类型人为活动对伊洛河流域河水水化学组成的影响,分别在丰水期(8月)和平水期(12月)采集伊洛河流域干流和支流河水样品,借助水体氢氧同位素组成和阴阳离子组成的时空分布特征,阐明水体来源以及水化学组成控制因素,说明人为活动的影响途径和方式.结果表明:①洛河干流河水丰水期和平水期δD和δ¹⁸O均值分别为-56‰和-7.9‰以及-55‰和-8.1‰,伊河干流河水丰水期和平水期δD和δ¹⁸O均值分别为-49‰和-6.9‰以及-53‰和-7.8‰,丰水期和平水期河水主要接受当地大气降水补给;②洛河及伊河干流河水水化学类型均为HCO₃-SO₄-Ca-Mg型,丰水期干流河水Ca²⁺和HCO^-₃当量浓度占比低于平水期,而丰水期SO₄^2-当量浓度占比则高于平水期,显示丰水期较多...     

Determination of particulate polycyclic aromatic hydrocarbons in ambient air by gas chromatography-mass spectrometry after molecularly imprinted polymer extraction

A solid phase extraction procedure (SPE) is described for the quantitative analysis of polycyclic aromatic hydrocarbons (PAHs) in atmospheric particulate matter (PM), as ubiquitous environmental pollutants routinely measured in air quality monitoring. A SPE cartridge was used based on a molecular imprinted polymer (MIP-SPE) properly tailored for selective retention of PAHs with 4 and more benzene fused rings. The performance of the clean-up procedure was evaluated with the specific concern of selective purification towards saturated hydrocarbons, which are the PM components mostly interfering GC analysis of target PAHs. Under optimized operative conditions, the MIP-SPE provided analyte recovery close to 95% for heavier PAHs, from benzo(α)pyrene to benzo(ghi)perylene, and close to 90% for four benzene rings PAHs, with good reproducibility (RSDs: 2.5%-5.9%). Otherwise, C₁₇-C₃₂ n-alkanes were nearly completely removed. The proposed method was critically compared with Solid Phase Micro Extraction (SPME) using a polyacrylate fiber. Both methods were successfully applied to the analysis of ambient PM_2.5 samples collected at an urban polluted site. Between the two procedures, the MIP-SPE provided the highest recovery (R% ≥ 93%) for PAHs with 5 and more benzene rings, but lower for lighter PAHs. In contrast, SPME showed a mean acceptable R% value (∼ 80%) for all the investigated PAHs, except for the heaviest PAHs in the most polluted samples (R%: 110%-138%), suggesting an incomplete purification from the interfering n-hydrocarbons.     

镁渣配料煅烧硅酸盐水泥熟料的研究

研究了镁渣矿物组成和镁渣配料煅烧硅酸盐水泥熟料的反应动力在数和物理性能。结果表明：镁渣的主要矿物组成为γ－Ｃ２Ｓ、β－Ｃ２Ｓ、ＭｇＯ、ＣＦ、Ｃ２Ｆ、ＦｅＯ、ＣａＦ２等，并且镁渣可降低熟料形成反应表观活化能，加速熟料矿物的形成，提高熟料的强度。