Impacts of wastewater sludge amendments in restoring nitrogen cycle in p-nitrophenol contaminated soil

The possible impacts on nitrogen-cycle in a p-nitrophenol (PNP) polluted soil and the e ectiveness of wastewater sludge amendments in restoring nitrification potential and urease activity were evaluated by an incubation study. The results indicated that PNP at 250 mg/kg soil inhibited urease activity, nitrification potential, arginine ammonification rate and heterotrophic bacteria counts to some extents. After exposure to PNP, the nitrification potential of the tested soil was dramatically reduced to zero over a period of 30 days. Based on the findings, nitrification potential was postulated as a simple biochemical indicator for PNP pollution in soils. Nitrogen-cycling processes in soils responded positively to the applications of wastewater sludges. A sludge application rate of 200 tons/ha was su cient for successful biostimulation of these nitrogen processes. The microbial activities in sludge-amended, heavy PNP-polluted soils seemed to recover after 30–45 days, indicating the e ectiveness of sludge as a useful soil amendment.     

Modeling assessment for ammonium nitrogen recovery from wastewater by chemical precipitation

Chemical precipitation to form magnesium ammonium phosphate (MAP) is an effective technology for recovering ammonium nitrogen (NH4 +-N). In the present research, we investigated the thermodynamic modeling of the PHREEQC program for NH4 +-N recovery to evaluate the effect of reaction factors on MAP precipitation. The case study of NH4 +-N recovery from coking wastewater was conducted to provide a comparison. Response surface methodology (RSM) was applied to assist in understanding the relative significance of reaction factors and the interactive effects of solution conditions. Thermodynamic modeling indicated that the saturation index (SI) of MAP followed a polynomial function of pH. The SI of MAP increased logarithmically with the Mg2+/NH4 + molar ratio (Mg/N) and the initial NH4 +-N concentration (CN), respectively, while it decreased with an increase in Ca2+/NH4 + and CO3 2??/NH4 + molar ratios (Ca/N and CO3 2??/N), respectively. The trends for NH4 +-N removal at different pH and Mg/N levels were similar to the thermodynamic modeling predictions. The RSM analysis indicated that the factors including pH, Mg/N, CN, Ca/N, (Mg/N) (CO3 2??/N), (pH)2, (Mg/N)2, and (CN)2 were significant. Response surface plots were useful for understanding the interaction effects on NH4 +-N recovery.     

Effect of anaerobic digestion on the high rate of nitritation, treating piggery wastewater

Laboratory reactors were operated by using piggery wastewater and the effluent of anaerobic digester from piggery wastewater plants to study the effect of anaerobic digestion on nitritation rate.     

铅酸电池的回收处理工艺

本文阐述了铅酸电池的资源化回收利用的工艺技术,通过分析废铅合金板的回收再利用技术及电解液、含铅废水、废气处理工艺的优、缺点探索铅酸电池回收利用技术的发展趋势。     

废弃线路板热解油中酚类物质的提取与分离

将FR-4型废弃线路板热解,并对热解油中含量最多的组分-酚类物质进行分离提取.比较研究线路板热解油的分离提取方法,探索出"碱液处理-酸化-萃取-减压蒸馏"的新方法,对分离出的组分进行GCMS(气质联用)测试.结果显示运用该方法对FR-4型线路板的热解油进行提取分离,得到的总酚占热解油的62.0%,其中苯酚的最高纯度可达...     

酸析+臭氧+MBR工艺处理手机显示屏厂废水

哈威特光电技术有限公司是一家生产手机显示屏强化玻璃的企业,主要生产废水为油墨废水、研磨废水、清洗废水,其中油墨废水COD浓度高达8 000～12 000 mg/L,废水呈碱性且可生化性差;污水处理采用酸析+臭氧+MBR工艺,其中酸析法主要对油墨废水进行预处理,臭氧氧化提高综合废水的B/C比,最后进入膜生化装置MBR处理,出水能达到污水综合排放标准(GB8978-1996)的一级标准。     

磁性膨润土材料吸附处理印染废水研究

针对目前膨润土在应用中的一些问题,对膨润土进行磁性能改性,通过共沉淀法制备磁性膨润土颗粒,并对其进行了X射线衍射和磁性能表征分析.以阴离子染料OrangeⅡ为目标化合物,研究了磁性膨润土材料对OrangeⅡ废水的吸附效果,并探讨了主要工艺参数如阳离子表面活性剂的质量浓度、pH、温度等对染料去除率的影响.结果表明:阳离子...     

稀土磁盘水处理方案技术经济比较

文章针对日照钢铁集团公司2150热轧水处理工程浊环水处理方案选择,对传统沉淀过滤法和先进的稀土磁盘法进行了对比和分析,稀土磁盘法在效果、占地、投资和运行维护费用上有较多优势,最终选用该工艺。     

工业废水中钡的排放限值研究

在查阅大量文献资料基础上,总结了环境中钡的来源和特性,采用电感耦合等离子原子发射光谱方法测定地表水及稀土废水中的钡元素含量.对仪器的工作参数和被测元素的分析谱线进行了优化和选择,结合钡的化学毒性,提出了废水中钡的标准是5mg/L的建议.     

高压脉冲电凝-Fenton-生化法处理制药废水

通过高压脉冲电凝-Fenton对制药废水进行预处理,出水进入UASB-AO生化处理系统.研究表明:高压脉冲电凝-Fenton氧化法的最佳工况条件为进水pH值为4.0左右,高压脉冲电凝反应时间为45 min,H2O2投加量为4mL/L,Fenton氧化时间为60min.高压脉冲电凝-Fenton对CODCr去除率为36.5%～39.2%,ρ(BOD5)/ρ(CODCr)从0.13提高到0.32-0.34,废水的可生化性大大提高,UASB厌氧反应器去除率为81.4%～82.1%,AO系统去除率为88.0%～88.5%,而整个生化处理系统对CODCr去除率为95.4%～97.9%,最终出水各项指标可达到GB 8978-1996<污水综合排放标准>中一级标准.