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561.
形稳阳极电解处理有机废水机理及动力学的研究   总被引:4,自引:0,他引:4  
采用简便易行的方法对形稳阳极电解催化降解有机废水的机理进行了研究,表明在电解过程中能够产生氧化能力极强的HO@自由基,可以氧化降解废水中的有机污染物,即有机污染物以间接氧化的方式降解,这是电解催化氧化技术的主要机理.用非线性最小二乘法对实验数据的分析表明,其过程基本符合两步一级模型,并得到了水杨酸降解过程中的两步速率常数.  相似文献   
562.
Removing nitrogen from wastewater with low chemical oxygen demand/total nitrogen (COD/TN) ratio is a difficult task due to the insufficient carbon source available for denitrification. Therefore, in the present work, a novel sequencing batch biofilm reactor (NSBBR) was developed to enhance the nitrogen removal from wastewater with low COD/TN ratio. The NSBBR was divided into two units separated by a vertical clapboard. Alternate feeding and aeration was performed in the two units, which created an anoxic unit with rich substrate content and an aeration unit deficient in substrate simultaneously. Therefore, the utilization of the influent carbon source for denitrification was increased, leading to higher TN removal compared to conventional SBBR (CSBBR) operation. The results show that the CSBBR removed up to 76.8%, 44.5% and 10.4% of TN, respectively, at three tested COD/TN ratios (9.0, 4.8 and 2.5). In contrast, the TN removal of the NSBBR could reach 81.9%, 60.5% and 26.6%, respectively, at the corresponding COD/TN ratios. Therefore, better TN removal performance could be achieved in the NSBBR, especially at low COD/TN ratios (4.8 and 2.5). Furthermore, it is easy to upgrade a CSBBR into an NSBBR in practice.  相似文献   
563.
Pb(II)会随工业的应用而残留在各类水体中,对人类和水生态构成潜在风险.以好氧颗粒污泥(Aerobic Granular Sludge, AGS)为接种污泥,在序批式反应器中研究Pb(II)对AGS的生物毒性及其迁移转化特性,同时探讨AGS对Pb(II)的吸附行为与机制.结果表明,Pb(II)会破坏AGS的三维结构,致使污泥生物量下降和沉降性能恶化.同时促进微生物分泌胞外聚合物(Extracellular Polymeric Substances, EPS),但由于污泥内部孔道堵塞使得微生物以EPS为碳源,且Pb(II)的持续毒性超过EPS保护阈值,最终导致EPS含量由对照组的(295.90±6.22) mg·g-1 最低降至(217.23±7.35) mg·g-1.在20 mg·L-1 Pb(II)的长期暴露下,AGS同步硝化反硝化作用明显削弱,导致TN去除率由对照组的97.15%大幅下降至70.04%.高通量结果表明,ExiguobacteriumCandidatus_Competibacter菌属在高浓度Pb(II)的胁迫下成为优势菌属,而与脱氮相关的Pseudomonas菌群相对丰度锐减至6.87%.此外,当Pb(II)进水浓度为1 mg·L-1时,AGS可对其实现99.15%的高效去除.整个过程的吸附动力学可以用准二级模型充分解释,且由多种扩散机制调控.使用Freundlich等温线模型可以较好地描述Pb(II)的吸附,Temkin模型也进一步证实化学吸附可在去除过程中起主导作用.结合扫描电子显微镜、X射线能谱仪和红外光谱表征结果,确定AGS对Pb(II)的吸附机制是以表面络合和沉淀反应为关键途径,并伴有离子交换和静电吸附.  相似文献   
564.
半干半湿法烟气脱硫技术研究   总被引:3,自引:0,他引:3  
在实验的基础上,分析了半干半湿法烟气脱硫技术的优点。根据影响该技术脱硫效率的主要因素,通过实验,较系统地研究了温距与喷嘴布局、入塔烟温、Ca/S 摩尔比、脱硫灰循环利用等对脱硫效率的影响,并对脱硫灰制砖的成分配制也进行了讨论。结果表明,在整体Ca/S 摩尔比为1-5 ~1-7 时,该技术工艺可以达到80 % 以上的脱硫效率  相似文献   
565.
Environmental Science and Pollution Research - This study examines the association among the green energy production (GEP), green technological innovation (GTI), and green international trade (GIT)...  相似文献   
566.
Environmental Science and Pollution Research - Rapid industrialization is deteriorating water quality, and fluoride pollution in water is one of the most serious environmental pollution problems....  相似文献   
567.
Environmental Science and Pollution Research - Owing to rapid socio-economic development in China, trace metal emissions have increased and lakes even in remote areas have experienced marked...  相似文献   
568.

The quantitative assessment of landfill gas emissions is essential to assess the performance of the landfill cover and gas collection system. The relative error of the measured surface emission of landfill gas may be induced by the static flux chamber technique. This study aims to quantify effects of the size of the chamber, the insertion depth, pressure differential on the relative errors by using an integrated approach of in situ tests, and numerical modeling. A field experiment study of landfill gas emission is conducted by using a static chamber at one landfill site in Xi’an, Northwest China. Additionally, a two-dimensional axisymmetric numerical model for multi-component gas transport in the soil and the static chamber is developed based on the dusty-gas model (DGM). The proposed model is validated by the field data obtained in this study and a set of experimental data in the literature. The results show that DGM model has a better capacity to predict gas transport under a wider range of permeability compared to Blanc’s method. This is due to the fact that DGM model can explain the interaction among gases (e.g., CH4, CO2, O2, and N2) and the Knudsen diffusion process while these mechanisms are not included in Blanc’s model. Increasing the size and the insertion depth of static chambers can reduce the relative error for the flux of CH4 and CO2. For example, increasing the height of chambers from 0.55 to 1.1 m can decrease relative errors of CH4 and CO2 flux by 17% and 18%, respectively. Moreover, we find that gas emission fluxes for the case with positive pressure differential (?Pin-out) are greater than that of the case without considering pressure fluctuations. The Monte Carlo method was adopted to carry out the statistical analysis for quantifying the range of relative errors. The agreement of the measured field data and predicted results demonstrated that the proposed model has the capacity to quantify the emission of landfill gas from the landfill cover systems.

  相似文献   
569.
Environmental Science and Pollution Research - Environment-friendly algaecides based on allelopathy have been widely used to control harmful algal blooms. In this research, micro and nano scale...  相似文献   
570.

Coastal rivers contributed the majority of anthropogenic nitrogen (N) loads to coastal waters, often resulting in eutrophication and hypoxia zones. Accurate N source identification is critical for optimizing coastal river N pollution control strategies. Based on a 2-year seasonal record of dual stable isotopes (\({\updelta}^{15}\mathrm{N}-{\mathrm{NO}}_3^{\hbox{-} }\) and \({\updelta}^{18}\mathrm{O}-{\mathrm{NO}}_3^{\hbox{-} }\)) and water quality parameters, this study combined the dual stable isotope-based MixSIAR model and the absolute principal component score-multiple linear regression (APCS-MLR) model to elucidate N dynamics and sources in two coastal rivers of Hangzhou Bay. Water quality/trophic level indices indicated light-to-moderate eutrophication status for the studied rivers. Spatio-temporal variability of water quality was associated with seasonal agricultural, aquaculture, and domestic activities, as well as the seasonal precipitation pattern. The APCS-MLR model identified soil + domestic wastewater (69.5%) and aquaculture tailwater (22.2%) as the major nitrogen pollution sources. The dual stable isotope-based MixSIAR model identified soil N, aquaculture tailwater, domestic wastewater, and atmospheric deposition N contributions of 35.3 ±21.1%, 29.7 ±17.2%, 27.9 ±14.5%, and 7.2 ±11.4% to riverine \({\mathrm{NO}}_3^{\hbox{-} }\) in the Cao’e River (CER) and 34.4 ±21.3%, 29.5 ±17.2%, 27.4 ±14.7%, and 8.7 ±12.8% in the Jiantang River (JTR), respectively. The APCS-MLR model and the dual stable isotope-based MixSIAR model showed consistent results for riverine N source identification. Combining these two methods for riverine N source identifications effectively distinguished the mix-source components from the APCS-MLR method and alleviated the high cost of stable isotope analysis, thereby providing reliable N source apportionment results with low requirements for water quality sampling and isotope analysis costs. This study highlights the importance of soil N management and aquaculture tailwater treatment in coastal river N pollution control.

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