Pulse cleaning flow models and numerical computation of candle ceramic filters

ＩｎｔｒｏｄｕｃｔｉｏｎＣｌｅａｎｉｎｇｔｈｅｆｉｎｅｐａｒｔｉｃｌｅｓｉｎｈｉｇｈｔｅｍｐｅｒａｔｕｒｅ (450℃ -950℃ )ａｎｄｈｉｇｈｐｒｅｓｓｕｒｅｃｏｎｄｉｔｉｏｎｃａｎｅｎｈａｎｃｅｔｈｅｔｈｅｒｍａｌｅｆｆｉｃｉｅｎｃｙｏｆｃｌｅａｎｃｏａｌｔｅｃｈｎｏｌｏｇｉｅｓｓｕｃｈａｓＩＧＣＣｏｒＰＦＢＣ .Ｒｉｇｉｄｃｅｒａｍｉｃｆｉｌｔｅｒｓｏｆａｖａｒｉｅｔｙｏｆｓｔｒｕｃｔｕｒｅｓａｒｅｕｎｄｅｒｄｅｖｅｌｏｐｍｅｎｔｉｎｐｒｏｇｒａｍｓａｒｏｕｎｄｔｈｅｗｏｒｌｄ ,ｗｈｉｃｈｃａｎｆｉ…     

变光焊接眼护具响应时间定义分析

通过对不同标准的变光焊接眼护具响应时间定义分析，提出各标准定义及计算值的区别，以利于帮助消费者进行产品选择和企业对产品设计的改进。     

自动变光焊接护目镜响应特性测试仪研究

为制定变光焊接护目镜新产品专业标准提供支撑，进行了焊接弧光特性和变光焊接护目镜响应特性研究，解决了焊接弧光模拟、弧光信号检测、时间小信号检测等技术关键，研制了响应特性测试系统，并进行实测分析。便携式测试仪采用暗箱全封闭结构，能产生模拟的交直流弧焊信号，能检测10^-1～10^4lx照度的光信号并保持线性，能检测弧光作用下护目镜可见光透射比的整个变化过程，最大采样频率达30kHz，确保测试精度，能按响应时间定义进行记录和运算，测试接口具有通用性。     

进水有机负荷对三级生物滴滤池脱氮除磷的影响

试验采用三级(好氧/兼氧/好氧)多层组合填料生物滴滤池处理模拟生活污水,探索强化脱氮除磷工艺。考察了在相同水力负荷和布水周期下,改变进水有机负荷对COD、NH_4~+-N、TN和TP去除率的影响,并用扫描电镜和X射线衍射(XRD)对填料进行辅助分析。研究结果表明,三级串联生物滴滤池的组合相比传统的单级或两级生物滴滤池反应器处理效果更好。第1级和第2级生物滴滤池去除COD、NH_4~+-N和TN效果较好,贡献率合计分别为93.0%、91.2%和91.4%。第1级和第3级生物滴滤池除磷效果较好,贡献率合计91.4%。有机负荷为0.328~0.392 kg/(m~3·d)时,系统总体去除效果最好。     

曝气生物滤池的短程硝化特性

通过控制进水pH值实现曝气生物滤池的短程硝化。工艺运行结果表明,对于进水pH值为8.22~8.57,NH4+-N平均容积负荷为0.5 kg/(m3.d),水温为17.5~20.2℃,曝气生物滤池溶解氧质量浓度平均为4.5 mg/L的条件下能够同步实现95%的NH4+-N去除率和80%的NO2--N积累率。通过分析FA和FNA沿滤池高度的变化特征,发现滤池底部(0~5 cm)区域短程硝化反应主要由FA控制,中部(5~15 cm)区域是由FA和FNA共同掌控;而上部区域(15~50 cm)则是由FNA控制,FNA沿滤池高度的快速增加是确保工艺实现稳定亚硝酸盐积累的重要原因。     

城市再生水生产工艺中典型紫外防晒剂的去除

随着紫外防晒剂在个人护理用品中的大量使用,其环境及健康风险效应开始得到人们的关注.采用固相萃取-气相色谱-质谱联用(SPE-GC-MS)技术对天津某再生水厂不同处理单元中4种典型紫外防晒剂4-甲氧基肉桂酸-2-乙基己基酯(ethylhexylmethoxycinnamate,EHMC),羟苯甲酮(benzophenone-3,BP-3),3-(4-甲苯基亚甲基)-d-1-樟脑(4-methylbenzylidene,4-MBC),2-氰基-3,3-二苯基丙酸-(2-乙基)己基酸(octocylene,OC)的分布及去除情况进行了检测.结果表明,污水处理厂二级出水中4种目标化合物的浓度范围在34ng·L-1￣2128ng·L-1之间;4种物质在夏秋季(7月和9月)的浓度普遍高于冬季(2月).污水处理厂二级出水中的这4种紫外防晒剂在经过混凝-絮凝处理、连续膜过滤和臭氧氧化处理后出水中的浓度呈下降趋势,总去除率为28.3%￣43.1%,其中臭氧氧化阶段对目标物的去除率最大(16%￣29%),而连续膜过滤阶段去除率最小(3.6%￣8.5%),混凝-絮凝阶段去除率介于2者之间(8%￣21%).由此可见,紫外防晒剂在再生水处理过程中并未得到完全去除,因此再生水的使用需经周密规划,以免对人体健康和生态环境造成威胁.     

大气颗粒物手工比对监测体系滤膜称量质控技术探讨

健全大气颗粒物手工比对监测体系是"十三五"环境空气自动监测质量管理的一项重点任务,其中颗粒物滤膜的称量直接影响手工监测数据质量。研究调研了国内各级环保部门所属环境监测机构颗粒物滤膜称量工作情况,结合国内外方法标准、技术规范等,重点探讨了称量实验室环境、称量设备、称量影响因素等滤膜称量质控要点,并针对环境管理与监测需求对大气颗粒物手工比对监测滤膜称量质控提出建议。     

Investigation of a filter explosion

At about 10 o'clock on a summer morning in 1987, an industrial filter used to purify an electrolytic plating solution exploded at a printed wiring board manufacturing plant. An investigation team used the failure modes and effects analysis technique to identify potential failures that could have caused the explosion and to reconstruct the most probable sequence of events that led to the accident. This paper describes the investigation and its results.     

疾病预防控制中心废水处理技术工程实例

疾病预防控制机构废水具有重金属种类繁多、含病原体数量大、间断性排放等特点,通过运用混凝沉淀＋曝气生物滤池（BIOFOR）＋ClO2消毒工艺对其废水进行处理,处理后废水达到《医疗机构水污染物排放标准（》GB18466-2005）排放标准。     

Particle properties in granular activated carbon filter during drinking water treatment

The elemental composition and bacteria attached in particles were investigated during granular activated carbon (GAC) filtration.The experimental results showed that trapped influent particles could form new,larger particles on GAC surface.The sloughing of individuals off GAC surface caused an increase in effluent particles in the size range from 5 to 25 μm.The selectivity for element removal in GAC filters caused an increasing proportion of metallic elements in the effluent particles.The distribution of molar ratio indicated a complicated composition for large particles,involving organic and inorganic substances.The organic proportion accounted for 40% of total carbon attached to the particles.Compared with dissolved carbon,there was potential for the formation of trihalomethanes by organic carbon attached to particles,especially for those with size larger than 10 μm.The pure carbon energy spectrum was found only in the GAC effluent and the size distribution of carbon fines was mainly above 10 μm.The larger carbon fines provided more space for bacterial colonization and stronger protection for attached bacteria against disinfection.The residual attached bacteria after chorine disinfection was increased to 10 2-10 3 CFU/mL within 24 hours at 25°C.