2014年河北中南部两次重霾天气成因分析

利用河北省环保局环境监测站提供的污染物浓度数据及常规气象观测数据、NCEP再分析资料,结合HYSPLIT4.9后向轨迹模式,对2014年10月上旬发生在河北省的2次大范围的重霾天气特征和成因进行综合分析.结果表明,这2次重污染天气过程PM_2.5地面浓度最大值出现在邢台,为507μg/m³,水平能见度不足1km.均压场的分布和较为平稳的高空形势为2次霾天气提供了有利的气象背景.高湿,静小风以及较低的混合层高度不利于污染物扩散,是导致这两次重污染天气持续的主要原因.结合卫星火点及污染物来源分析表明,河北南部及周边省份的秸秆燃烧加重了第2次过程的污染,污染气团的输送对区域性重霾天气产生重要影响.     

通风速率对厌氧残余物沼渣堆肥的影响

以牛粪发酵残余物沼渣为原料,设置不同的通风速率进行堆肥,堆体的通风速率分别是0.2,0.5,0.8L/（min·kg OM）,分析堆肥20d过程中物理、化学和腐熟变化的特征,探讨不同通风速率对堆肥特性的影响.结果表明,通风速率为0.2,0.5L/（min·kg OM）的堆体维持高温阶段的时间为5d,而通风速率为0.8L/（min·kg OM）堆体维持高温阶段时间为4d;各堆体OM分解率分别是28.2%,32.9%,30.5%;通风速率对终产品pH值、电导率（EC）影响不大,pH值均能满足堆肥最优pH值,EC均未超过4mS/cm;通风速率为0.2L/（min·kg OM）的堆体终产品的NH₄⁺-N含量超过400mg/kg,各堆体终产品NO₃^--N的含量分别是2545,3146,2735mg/kg;各堆体终产品C/N分别是16.5,14.1,15.6;各堆体终产品GI值分别是92.2%,96.6%,82.7%.通风速率为0.5L/（min·kg OM）堆体E465/E665（E₄/E₆）最小,其腐殖化程度最高.综合分析,0.5L/（min·kg OM）是沼渣堆肥最为合适的通风速率.     

南京市蔬菜中滴滴涕和六六六的残留及摄食暴露分析

为研究有机氯农药在食物中的残留及人群的摄食暴露,在2015年5月采集了南京市居民普遍食用的10种蔬菜,利用气相色谱-质谱联用仪(GC-MS)进行检测。研究表明滴滴涕(DDTs)和六六六(HCHs)在蔬菜中均有检出,∑DDTs的残留量为1.78~5.29 ng·g~(-1),∑HCHs的残留量为0.21~4.77 ng·g~(-1),其中∑10OCPs(有机氯农药)含量最高的蔬菜是藕(10.07 ng·g~(-1)),含量最低的是青菜(2.32 ng·g~(-1))。通过来源分析发现,蔬菜中DDTs可能有新的输入,而HCHs则主要源于历史残留。通过对不同人群的每日摄取量(EDI)进行摄食暴露分析发现,儿童的摄食暴露量要高于同性别其他年龄段人群,在儿童和未成年阶段,男性的暴露量普遍高于女性,而在成年和老年阶段,男性的暴露量低于女性。平均而言,各年龄段人群对γ-HCH和DDTs的日均口摄暴露量(EDI)值远低于联合国粮农组织和世界卫生组织(FAO/WHO)所规定的ADI值,表明在目前蔬菜消费量下,南京市居民通过摄入蔬菜引起的健康风险水平较低。     

铬渣-煤矸石砖中Cr(Ⅵ)解毒机理研究

铬渣因所含Cr(Ⅵ)具有强氧化性而会对环境造成严重污染.本文采用自养煤矸石砖焙烧技术对铬渣进行无害化治理,对不同铬渣掺量的铬渣-煤矸石砖,进行铬的浸出毒性分析.通过试验得出,除铬渣掺量为15%的砖中六价铬浸出浓度超标外,其余铬的浸出浓度均小于国标规定,铬的解毒率都在95%以上.此技术对Cr的还原解毒为,在高温熔融条件下,煤矸石中的碳及随后产生的CO、H2、CH4等还原性物质与Cr(Ⅵ)化合物发生反应.铬渣、煤矸石及砖的X-粉晶衍射物相分析表明,砖中Cr(Ⅵ)被还原为Cr(Ⅲ)后,以类质同相方式进入辉石、尖晶石、铝硅酸盐等稳定物相,得以固化解毒.因此,还原后Cr的存在形式稳定,可以经受恶劣自然环境而不会重新溶出和造成二次污染,作为建材,可以安全利用.     

秸秆焚烧影响南京空气质量的成因探讨

综合利用卫星遥感的火点和云覆盖信息,结合气团后向轨迹分析,探讨了由秸秆焚烧造成的空气污染物的区域尺度输送和本地源对城市空气质量的影响.结果表明,在一定气象条件下,污染物可以发生区域尺度的输送,上风火点与下风城市的污染有明显的相关,将空气污染分为局地型(如,2006年5月31日、2009年11月8日)、区域型(如,2008年10月28日),以及局地区域相结合型(如,2006年6月14日、2007年6月5日、2008年6月2日)3种.应用本文的方法,在有云时,可以通过部分火点和气团后向轨迹分析推测污染物源地.空气污染气象条件分析表明,秸秆焚烧若伴随高空(500hPa)有槽(或位于槽前),低空存在弱切变,气流由周边向中心辐合;同时,若在均压场控制下,等压线稀疏,风速较小或静风,污染物则易积聚而不易输送;逆温层的形成将污染物禁锢在混合层以下,不利于垂直扩散;再加上较大的相对湿度,有利于霾的形成,造成严重空气污染.     

Thermal cracking of waste printed wiring boards for mechanical recycling by using residual steam preprocessing

Mechanical waste-processing methods, which combine crushing and separation processes for the recovery of valuable materials, have been widely applied in waste printed wiring board (PWB) treatment. However, both the high impact toughness and the tensile and flexural strengths of whole PWB with a laminated structure result in great energy consumption and severe abrasion of the cutters during multi-level crushing. In addition, the high temperatures occurring in continual crushing probably cause the decomposition of the polymer matrix. A thermal-crack method using residual steam as the heating medium has been developed to pre-treat waste PWBs. This treatment reduces the mechanical strength in order to improve the recovery rate of valuable materials in subsequent mechanical recycling. The changes of the PWBs’ macro-mechanical properties were studied to evaluate thermal expansion impacts associated with changes in temperature, and the dynamic dislocation micro-structures were observed to identify the fracture mechanism. The results showed that thermal cracking with steam at the temperature of 500 K can effectively attenuate the mechanical properties of waste PWBs, by reducing the impact, tensile and flexural strengths respectively, by 59.2%, 49.3% and 51.4%, compared to untreated PWB. Thermal expansion can also facilitate the separation of copper from glass fiber by reducing peel resistance by 95.4% at 500 K. It was revealed that the flexural fracture was a transverse cracking caused by concentrated stress when the heating temperature was less than 500 K, and shifted to a vertical cracking after exceeding 500 K.     

Effect of pH on the fate of fenazaquin in soil and water under laboratory-simulated condition

The persistence of fenazaquin (4-t-butylphenylethyl quinazolin-4-yl ether) was studied in three different soils, namely, Gangetic alluvial (pH 6.9), laterite (pH 5.3), and terai (pH 5.1) soil and in water at three different pH values (4.0, 7.0, and 9.2) under laboratory-simulated condition and samples were analyzed upto 60 days at regular intervals. Fenazaquin was applied at 5 and 10 µg g^?1 for each soil and at 0.2 and 0.4 µg mL^?1 to each water sample. Dissipation of fenazaquin in soil and water followed first-order kinetics irrespective of any treatments. The half-life of fenazaquin was found in the range of 47–64 days in soils and 3.49–37.6 days in water irrespective of dose. The persistence of fenazaquin in soil significantly increased in the order of Gangetic alluvial soil (pH 6.9) > laterite soil (pH 5.3) > terai soil (pH 5.1), whereas in water the trend of persistence was pH 9.2 ≥ pH 7.0 > pH 4.0. The dissipation of fenazaquin in soil and water was found to be dependent on pH irrespective of doses.     

Residues and dissipation of the pesticide emamectin benzoate under Egyptian field condition: a case study

A simple, rapid analytical procedure for the quantification of emamectin benzoate in tomato was developed using high performance liquid chromatography with fluorescence detector (HPLC-FLD). Emamectin benzoate residues were extracted from tomato samples with n-hexane:ethyl acetate (1:1, v/v). The method involved derivatization using trifluoroacetic anhydride and 1-methylimidazole, prior to analysis by HPLC-FLD. Limit of quantification of this method was found to be 0.01 mg/kg, while limit of detection was 0.005 mg/kg. The dissipation of emamectin benzoate on tomato was studied, and half-life (t_1/2) was estimated in a field study carried out at three different locations. Emamectin benzoate was sprayed on tomato at recommended dosage. Samples of tomato were collected at 0, 1, 3, 7, 10, and 15 days after treatment. The t_1/2 of emamectin benzoate when applied at the recommended doses in tomato was approximately 2.5 days. The residue of emamectin benzoate reached below the maximal residue limit (MRL) 10 days after spraying at the tested dosage. Hence, a safe pre-harvest interval of 10 days is suggested before harvesting of tomato. This study would also be helpful for the Egypt government to establish the MRL of emamectin benzoate in tomatoes and provide guidance on the proper and safe use of this insecticide.     

Assessment of hydrocarbon emissions from diesel invert mud residues treated in a bioreactor

Hydrocarbon emissions from a diesel invert mud residue (DIMR) were monitored while the hydrocarbons were being biodegraded in a solid‐phase bioreactor. Five to twenty percent of the reduction in diesel hydrocarbons was attributed to evaporation depending on the treatment, i.e. homogenization, cultivation, and aeration. Most of these volatile hydrocarbons were linear C₈ — C₁₂ alkanes and one‐ring aromatics. Of the treatments aeration had the largest effect on emissions; forced air through the bottom of the bioreactor cells increased emissions by three times over that of the non‐aerated cells. Cultivation increased hydrocarbon emission concentration as much as twofold over the pre‐cultivation value, however, emissions returned to the original levels within 12 hours. Homogenization had the least effect of all treatments. Diurnally, the emission rate was 40% higher in late afternoon than at midnight; the cause of which was probably atmospheric fluctuations such as temperature and solar radiation. The effects of daily atmospheric fluctuations were empirically modeled and taken into account for determining the total volume of emissions.     

多孔水化硅酸钙的制备及其磷回收特性

为实现磷资源的可持续利用,以环境废弃物电石渣为钙质材料,以白碳黑为硅质材料合成CSH(水化硅酸钙),以该材料为晶种,以结晶形成羟基磷灰石的形式从含磷废水中回收磷,重点研究了不同钙硅比〔c(CaO)/c(SiO₂)〕条件下制备的CSH对含磷废水中磷的回收特性. 结果表明,钙硅比为1.8∶1时所得的CSH结构更疏松、表面分布有较多的孔隙, 较大的比表面积使其具有较好的溶钙能力. 钙硅比为1.8∶1的CSH最佳磷回收工艺条件:反应时间为60min,CSH投加量为4g/L,搅拌强度为40r/min. 在该条件下重复除磷15次以后,回收产物中w(P)达到17.56%,说明CSH具有良好的磷回收性能. 对回收磷前后的CSH进行了XRD图谱分析和FTIR分析发现,溶液中的磷主要生成了羟基磷灰石并嵌入到CSH中. 基于回收磷的目的,CSH可以用于处理ρ(P)较高的工业废水,或者是生物除磷系统中的污泥厌氧释磷液中,回收磷后的产品可作为含磷矿石或者磷肥加以利用.