结合WRF/Chem和PMF方法的邯郸市PM_(2.5)源解析

<正>向源模型法和反向受体模型法是进行城市PM_(2.5)源解析的2种方法,两者各有所长。该研究应用三维空气质量模型Weather Research and Forecasting Model with Chemistry(WRF-Chem)模型和受体模型Positive Matrix Factorization(PMF),以2014年10月为研究时段,分别对邯郸市的细微颗粒物(PM_(2.5))进行源解析。PMF模型的解析结果表明,邯郸市PM_(2.5)来源为二次源30.2%,燃煤源25.4%、金属冶炼源15.1%、机动车源14.4%、扬尘源9.8%,生物质燃烧源5.2%。应用WRF-Chem模型,Brute-Force方法解析出的结果为,在本地源贡献中,工业源贡献了49.0%,民用源11.9%、农业源9.6%、交通源3.8%和电厂源-1.5%(负值由于PM_(2.5)前体物之间的非线性反应所致)。应用源模型对二次成分(SO_4~(2-)、NO_3~-和NH_4~+)进行再解析,结果显示,燃煤源源贡献率最大,达到25.7%,其次分别为农业源(24.0%)、工业源(6.5%)、生物质源(1.8%)和机动车(0.03%)。结合2种方法得出,邯郸市的PM_(2.5)中,本地燃煤源贡献了37.1%,其次分别为金属冶炼源(18.4%)、机动车源(15.1%)、扬尘源(13.3%)、生物质燃烧源(6.2%)。     

EDTA增强Cr(VI)共存时Burkholderia cepacia降解孔雀绿的效率

重金属共存严重抑制了微生物降解染料的效率,本研究拟采用EDTA螯合Cr提高Burkholderia cepacia C09G降解复合污染中孔雀绿的效率.实验结果表明,0.1 mmol·L~(-1)孔雀绿单独存在条件下,24 h的生物降解率达到96.2%;然而,在0.5 mmol·L~(-1)Cr(VI)共存条件下,60 h的降解率仅为6.7%.当加入0.5 mmol·L~(-1)EDTA螯合剂后,60 h时孔雀绿的降解率提高到18.8%.当EDTA浓度为0.5 mmol·L~(-1)时,最佳螯合Cr(VI)的浓度为0.7 mmol·L~(-1),此时,60 h后孔雀绿的降解率达到35.3%,对Cr(VI)的吸附率为24.6%.此外,通过EDS、SEM、XPS分析证明,EDTA可以减小Cr(VI)的毒性,Burkholderia cepacia C09G可将吸附的Cr(VI)还原为Cr(III).     

分子生物学技术在水处理中的应用研究进展

利用现代分子生物学技术对微生物进行分析和研究,以解决传统微生物分析成本高、速度慢、准确度较低和灵敏度较差等缺点。介绍分子生物学技术在水处理中的应用现状,并对未来发展方向提出建议。目前分子生物学技术在供水工程中主要用于水中细菌、病毒、原生动物、蠕虫等病原微生物的快速检测以及管网微生物种群的分析,在污水处理中主要用于脱氮除磷过程菌群数量和空间分布的剖析、污泥膨胀成因分析以及监测微生物种群多样性来优化处理工艺。分子生物学技术的深入研究将进一步促进水行业的发展。     

β-环糊精/醋酸纤维素纳米纤维的制备及对染料废水的处理

制备了不同β-环糊精(β-CD)含量的醋酸纤维素(CA)纳米纤维膜,并对纤维膜的结构形貌、尺寸分布、孔隙率、比表面积以及纤维膜的力学性能进行表征分析。随后研究了不同β-CD含量、初始浓度、吸附时间下,纳米纤维膜对甲基红染料的截留性能和吸附性能。结果表明:过量(≥30%)的β-环糊精会使纳米纤维产生珠节,纤维的形貌和力学性能变差;吸附试验表明,β-CD的加入提高了CA纳米纤维膜对染料的吸附,MR吸附率可达93.48%,最大平衡吸附量可达181.74 mg/g,比纯CA纳米纤维膜提高了将近40%;此外,染料的截留实验表明,纳米纤维膜对染料的截留效果较差,最大截留率为50.35%。     

焙烧温度对CeO_2(ZrO_2)/TiO_2选择性催化脱硝性能的影响

采用溶胶-凝胶法并以不同温度焙烧制备一系列CeO_2(ZrO_2)/TiO_2(CZT)催化剂,考察了CZT催化剂固相结构、酸量、比表面积等性能与催化活性的关系。采用XRD、BET、NH3-TPD、H2-TPR以及XPS等表征技术对催化剂进行表征。结果表明:焙烧温度为450℃时CZT催化剂具有最高的催化活性,其在240~400℃的温度窗口内活性均高于90%,且具有较好的抗水和抗硫中毒能力。随着焙烧温度的提高,催化剂表面的Ce和Zr原子进入体相晶格且Ce0.5Zr0.5O2向Ce0.75Zr0.25O2转变,导致催化剂的储释氧能力和氧化还原性能降低。另外,锐钛矿和金红石型TiO_2晶粒尺寸的增加,催化剂的有效比表面积和总酸量降低,因此CZT催化活性随着焙烧温度的提高而有所降低。换言之,大的比表面积、良好的氧化还原性能、表面Ce4+的富集以及酸性位的增多均有利于NH3-SCR活性的提高。     

地下水循环井技术处理土壤和地下水中甲基叔丁基醚研究

研究了MTBE在砂土中的静态吸附以及采用地下水循环井技术(GCW)去除砂土和地下水中MTBE的衰减规律。结果表明:MTBE在砂土中的吸附动力学符合准二级动力学方程,相关系数R2为0.99618,在砂土中的吸附平衡时间为24 h;吸附热力学符合Linear平衡吸附,吸附系数为0.00306 m3/kg。GCW运行30 h后,地下水饱和含水层中MTBE浓度由500 mg/L降至72.5 mg/L,去除率为85.5%;砂土中MTBE的吸附量由0.93 mg/g降至0.03 mg/g,去除率达96.4%。水平方向距GCW越近,MTBE的去除效率越快,垂直方向位于GCW上部的MTBE优先会被去除,最佳修复时间为运行15 h。GCW对砂土和地下水中高浓度MTBE具有良好的修复效果。     

Effects of sludge retention time, carbon and initial biomass concentrations on selection process: From activated sludge to polyhydroxyalkanoate accumulating cultures

Four sequence batch reactors (SBRs) fed by fermented sugar cane wastewater were continuously operated under the aerobic dynamic feeding (ADF) mode with different configurations of sludge retention time (SRT), carbon and initial biomass concentrations to enrich polyhydroxyalkanoate (PHA) accumulating mixed microbial cultures (MMCs) from municipal activated sludge. The stability of SBRs was investigated besides the enrichment performance. The microbial community structures of the enriched MMCs were analyzed using terminal restriction fragment length polymorphism (T-RFLP). The optimum operating conditions for the enrichment process were: SRT of 5 days, carbon concentration of 2.52 g COD/L and initial biomass concentration of 3.65 g/L. The best enrichment performance in terms of both operating stability and PHA storage ability of enriched cultures (with the maximum PHA content and PHA storage yield (Y_PHA/S) of 61.26% and 0.68 mg COD/mg COD, respectively) was achieved under this condition. Effects of the SRT, carbon concentration and initial biomass concentration on the PHA accumulating MMCs selection process were discussed respectively. A new model including the segmentation of the enrichment process and the effects of SRT on each phase was proposed.     

磁性PEI功能化秸秆的制备及对Pb (Ⅱ)的吸附

为获得同时具有优良的吸附性能和磁分离特性的生物吸附材料,以汽爆秸秆为基质,采用戊二醛交联剂法制备了磁性聚乙烯亚胺功能化秸秆吸附剂（Fe₃O₄-PEI-RS）,通过SEM、XRD、FTIR、XPS和VSM等手段表征了材料的结构和性质,测定了Pb（Ⅱ）在Fe₃O₄-PEI-RS上的吸附性能,考察了pH、吸附时间、吸附剂投加量、Pb（Ⅱ）初始浓度、温度等因素对吸附的影响.结果表明,Fe₃O₄-PEI-RS对Pb（Ⅱ）的吸附具有强烈的pH依赖性;吸附时间对Pb（Ⅱ）的吸附效率有明显的影响,在180 min时吸附达到平衡,吸附过程符合准二级动力学模型;Langmuir和Freundlich模型都能很好地描述Pb（Ⅱ）在Fe₃O₄-PEI-RS上的吸附行为,20、30和40℃时最大吸附量分别为192.31、200.00和212.77 mg/g;热力学参数△G < 0,而焓变△H>0、△S>0,说明该吸附属于熵增加的自发吸热反应过程,升温有利于吸附.重复试验表明,EDTA作解吸剂,经5次吸附/解吸附循环后吸附剂仍能保持较高的吸附容量.研究显示,所制Fe₃O₄-PEI-RS对Pb（Ⅱ）具有较高的吸附容量,稳定性好、可循环利用,能在磁场下实现快速分离.      

Biodegradation of polycyclic aromatic hydrocarbons (PAHs) by fungal enzymes: A review

Polycyclic aromatic hydrocarbons (PAHs) are a large group of chemicals. They represent an important concern due to their widespread distribution in the environment, their resistance to biodegradation, their potential to bioaccumulate and their harmful effects. Several pilot treatments have been implemented to prevent economic consequences and deterioration of soil and water quality. As a promising option, fungal enzymes are regarded as a powerful choice for degradation of PAHs. Phanerochaete chrysosporium, Pleurotus ostreatus and Bjerkandera adusta are most commonly used for the degradation of such compounds due to their production of ligninolytic enzymes such as lignin peroxidase, manganese peroxidase and laccase. The rate of biodegradation depends on many culture conditions, such as temperature, oxygen, accessibility of nutrients and agitated or shallow culture. Moreover, the addition of biosurfactants can strongly modify the enzyme activity. The removal of PAHs is dependent on the ionization potential. The study of the kinetics is not completely comprehended, and it becomes morem hallenging when fungi are applied for bioremediation. Degradation studies in soil are much more complicated than liquid cultures because of the heterogeneity of soil, thus, many factors should be considered when studying soil bioremediation, such as desorption and bioavailability of PAHs. Different degradation pathways can be suggested. The peroxidases are heme-containing enzymes having common catalytic cycles. One molecule of hydrogen peroxide oxidizes the resting enzyme withdrawing two electrons. Subsequently, the peroxidase is reduced back in two steps of one electron oxidation. Laccases are copper-containing oxidases. They reduce molecular oxygen to water and oxidize phenolic compounds.     

Amoxicillin effects on functional microbial community and spread of antibiotic resistance genes in amoxicillin manufacture wastewater treatment system

This study aimed to reveal how amoxicillin(AMX) affected the microbial community and the spread mechanism of antibiotic resistance genes(ARGs) in the AMX manufacture wastewater treatment system. For this purpose, a 1.47 L expanded granular sludge bed(EGSB) reactor was designed and run for 241 days treating artificial AMX manufacture wastewater. 454 pyrosequencing was applied to analyze functional microorganisms in the system. The antibiotic genes OXA_(-1), OXA_(-2), OXA_(-10), TEM_(-1), CTX-M_(-1), class I integrons(intI1) and 16 SrRNA genes were also examined in sludge samples. The results showed that the genera Ignavibacterium, Phocoenobacter,Spirochaeta, Aminobacterium and Cloacibacillus contributed to the degradation of different organic compounds(such as various sugars and amines). And the relative quantification of eachβ-lactam resistance gene in the study was changed with the increasing of AMX concentration.Furthermore the vertical gene transfer was the main driver for the spread of ARGs rather than horizontal transfer pathways in the system.