脱氮除磷(NPR)工艺中试研究

NPR工艺是一种活性污泥法和生物膜法相结合的工艺,具有强化脱氮除磷的能力.中试研究采用固定的分段进水比例(厌氧流量∶缺氧流量=7∶3),在污泥龄为10 d的情况下,比较了0.6 m3/h和0.9 m3/h2种流量下对氮磷去除效果,分析了在0.6 m3流量下,工艺是如何对CODCr,NH3-N,PO43-进行去除的.试验发现:在0.6 m3/h流量下:出水稳定达到GB 18918-2002《城镇污水处理厂污染物排放标准》一级A标准,在0.9 m3/h流量下,出水稳定达到GB18918-2002《城镇污水处理厂污染物排放标准》一级B标准.     

氧化沟处理煤矿低浓度生活污水运行控制技术探讨

本文给出了济三煤矿生活污水水量和水质情况,以及采用卡鲁塞尔氧化沟处理该低浓度生活污水的工艺流程和特点。详细描述了实际运行过程中培养和驯化适应低浓度生活污水优势菌种的几个步骤,以及防止和控制污泥膨胀和老化的方法。运行试验结果表明：采用污泥回流比150%、控制氧化沟未端溶解氧（DO）1.5 mg/L,能取得最佳的CODcr去除率和总氮（TN）去除率,分别为76.7%和79.8%。     

浅析脱硫旁路挡板铅封实施后联锁保护逻辑的完善

根据国家环境保护部办公厅文件要求,需要对火电企业脱硫旁路挡板实施铅封。石灰石一石膏湿法脱硫工艺具有脱硫效果好、技术成熟等优点,在目前国内的燃煤发电机组中广为应用。旁路挡板作为连接主机与脱硫系统的关键设备,其正常投用不仅是脱硫系统能否正常投运的关键,更关系到脱硫系统本身甚至发电机组的安全。通过对旁路挡板联锁保护逻辑的分析．提出了实施旁路挡板铅封措施后旁路挡板的联锁保护措施的更改建议,使更改后的联锁保护逻辑更为完善。     

模拟水体硝态氮对黄菖蒲生长及其氮吸收的影响

为了对挺水植物在水环境与水生态修复中的应用提供参考依据,选取黄菖蒲(Iris pseudacorus L.)为对象,通过模拟水培实验,对比研究了6种水体硝态氮质量浓度(10.68、23.88、42.22、63.33、82.92、97.13 mg·L~(-1))下,黄菖蒲地上和地下生物量、根冠比、叶绿素含量、氮累计吸收量以及对硝态氮去除效果的差异,以期明确模拟水体硝态氮质量浓度对黄菖蒲生长及其氮吸收能力的影响.结果显示,首先,不同硝态氮质量浓度对黄菖蒲地上部分(茎叶)生长的影响大于地下部分(根);当硝态氮质量浓度为10.68 mg·L~(-1)时,黄菖蒲的根冠比增加;当硝态氮质量浓度为42.22~97.13 mg·L~(-1)时,黄菖蒲的根冠比减少.其次,黄菖蒲适宜生长的硝态氮质量浓度为23.88~63.33 mg·L~(-1);硝态氮质量浓度低于10.68 mg·L-1或高于82.92mg·L-1时,均会对黄菖蒲的叶绿素合成产生抑制作用.再次,黄菖蒲对氮的累积量随硝态氮质量浓度增加而增加,且地下部分对氮的累积能力优于地上部分;6种浓度下,单株黄菖蒲的氮累计吸收量为10.56~75.43 mg,其地下部分依次为地上部分的7.2、2.3、2.5、2.1、1.6以及1.5倍.此外,黄菖蒲对氮的利用效率与硝态氮质量浓度之间成显著的幂函数关系,且地上部分的氮利用效率高于地下部分.最后,黄菖蒲对硝态氮的去除率随硝态氮质量浓度增加而增加,6种浓度下黄菖蒲对硝态氮的去除率介于94.9%和99.3%之间,且水体中硝态氮质量浓度随时间延续呈指数函数降低.结果表明,黄菖蒲对硝态氮有很好的去除效果,但黄菖蒲的生长及其对氮的吸收与去除效率受水体硝态氮质量浓度影响显著,且地上部分较地下部分更为敏感.     

600 MW机组加装增压风机旁路系统的探索

应环保政策要求,火电厂烟气旁路系统必须在2014年底前取消,如何解决取消烟气旁路后锅炉的安全运行问题呢?漳山电厂提出加装增压风机旁路系统的方案,并通过检测风烟系统阻力,进行可行性研究。该方案实施后,完全达到预期效果,当增压风机故障时,烟气经旁路烟道进入吸收塔,保障了锅炉正常运行,实现了增压风机在线检修。     

镁法脱硫副产物亚硫酸镁处理现状

简单论述了镁法烟气脱硫技术在国内外的应用现状,镁法烟气脱硫技术具有脱硫效果好、投资小、运行维护费低、副产品可回收等优点;同时介绍了镁法脱硫技术在我国的应用优势,重点是镁法脱硫副产物综合利用的几种方法,如亚硫酸镁煅烧回收氧化镁,该技术是镁法脱硫副产物循环利用的关键。     

等离子体法脱硫脱硝一体化试验研究

对等离子体法烟气脱硫脱硝一体化技术进行了中试研究。在不同温度下,烟气中NOx及SO2的脱除量随温度升高而升高,其中脱硝效率最大化的温度区间约为210℃;在还原剂存在的条件下,温度提高40℃,脱硫脱硝效率平均上升70%和50%,氮氧化物的脱除效率对温度变化更加敏感,应予以更多考虑。     

Debromination of decabromodiphenyl ether by organo-montmorillonite-supported nanoscale zero-valent iron：Preparation, characterization and influence factors

An organo-montmorillonite-supported nanoscale zero-valent iron material(M-NZVI) was synthesized to degrade decabromodiphenyl ether(BDE-209). The results showed that nanoscale zero-valent iron had good dispersion on organo-montmorillonite and was present as a core-shell structure with a particle size range of nanoscale iron between 30–90 nm, characterized by XRD, SEM, TEM, XRF, ICP-AES, and XPS. The results of the degradation of BDE-209 by M-NZVI showed that the efficiency of M-NZVI in removing BDE-209 was much higher than that of NZVI. The efficiency of M-NZVI in removing BDE-209 decreased as the pH and the initial dissolved oxygen content of the reaction solution increased, but increased as the proportion of water in the reaction solution increased.     

改良UNITANK工艺在东鄱污水处理厂的应用分析

介绍了改良UNTIANK工艺在东鄱污水处理厂的应用情况,对比传统UNITANK工艺与改良UNTIANK工艺在除磷脱氮方面的去除效果,并讨论改良UNITANK工艺的结构、运行方式、工艺特点及存在问题,得出相关结论。     

Arsenic removal from groundwater by acclimated sludge under autohydrogenotrophic conditions

Arsenic in the environment is attracting increasing attention due to its chronic health effects. Although arsenite(As(III)) is generally more mobile and more toxic than arsenate(As(V)), reducing As(V) to As(III) may still be a means for decontamination, because As(III) can be removed from solution by precipitation with sulfide or by adsorption or complexation with other metal sulfides. The performance of As(V) bio-reduction under autohydrogenotrophic conditions was investigated with batch experiments. The results showed that As(V) reduction was a biochemical process while both acclimated sludge and hydrogen were essential. Most of the reduced arsenic remained in a soluble form, although 20% was removed with no addition of sulfate, while 82% was removed when sulfate was reduced to sulfide. The results demonstrated that the reduced arsenic was re-sequestered in the precipitates, probably as arsenic sulfides. Kinetic analysis showed that pseudo first-order kinetics described the bio-reduction process better than pseudo second-order. In particular, the influences of pH and temperature on As(V) reduction by acclimated sludge under autohydrogenotrophic conditions and total soluble As removal were examined. The reduction process was highly sensitive to both pH and temperature, with the optimum ranges of pH 6.5–7.0 and 30–40°C respectively. Furthermore, Arrhenius modeling results for the temperature effect indicated that the As(V) reduction trend was systematic. Total soluble As removal was consistent with the trend of As(V) reduction.