Bisphenol S induces oxidative stress and DNA damage in rat spermatozoa in vitro and disrupts daily sperm production in vivo

Bisphenol S has been introduced into some industrial applications and it may act as a xeno-estrogen that can alter endocrine functions and reproduction. The present study was carried out to examine the effect of bisphenol S exposure on oxidative stress, generation of reactive oxygen species, and DNA integrity in rat spermatozoa in vitro and daily sperm production and sperm DNA damage in vivo. Sperm were incubated with bisphenol S at concentrations of 0.5, 1, 10, and 100 µg/L. At the highest concentration, bisphenol S induced formation of reactive oxygen species, caused lipid peroxidation, affected superoxide dismutase levels, and increased DNA fragmentation. Adult rats were exposed to doses of 0.5, 5, 25, and 50 µg/kg/d for 28 days. Decrease in daily sperm production and an increase in sperm DNA damage was observed at the highest dose in the 50 µg/kg/d treated group, but sperm motility was not reduced.     

压裂返排液生物处理实验研究

从油田压裂返排液中筛选出EB系列菌种,可高效降解压裂返排液中的高分子和有机污染物。考察了振荡时间、温度、接种量、菌种混合比例等对压裂返排液COD去除率的影响。结果表明:48h振荡、25℃、10%接种量、菌种EB1和EB2按1∶1比例混合是较佳应用条件。EB复合菌种的应用范围较广,其pH值适用范围为6～9,矿化度适用范围为3 000～20 000mg/L。该研究提高了压裂返排液生物处理技术规模化应用的可行性。     

A/O生化池和BAF生物滤池的组合应用

较为全面地介绍了A/O生化池和BAF生物滤池两级生化合并的应用原理和效果,对两级生化的进出水水质进行了分析,并对系统运行中存在的问题进行了阐述。     

生物活性炭曝气滤池处理油田废水的应用

为实现DB 12/356-2008《天津市污水综合排放标准》(CODCr≤60mg/L)要求,大港油田对原有的废水生化处理工艺进行技术升级改造,优选生物活性炭曝气滤池工艺作为工程改造的主体技术方案。现场实施后,各项水质指标均达到了天津市标准的要求,对大港油田工业废水深度处理工作具有实践指导意义。     

活性焦吸附—曝气生物滤池处理煤气化废水生化出水

采用活性焦吸附—曝气生物滤池（BAF）工艺对煤气化废水生化出水进行深度处理。在活性焦投加量2 g/L、吸附时间2 h、BAF生化停留时间4 h的条件下,总COD去除率为85.4%,最终出水平均COD为45.2 mg/L,满足后续双膜法回用工艺要求（COD≤50 mg/L）。活性焦对致色的大分子有机物具有较好的吸附效果,吸附后废水的色度从300倍降至60倍,同时耗氧速率加快,可生化性提高。活性焦的吸附以物理吸附为主,吸附出水没有急性毒性。三维荧光光谱显示：各单元对于酚类的去除均有贡献,小分子组分中的酚类几乎全被去除。     

气水比对曝气生物活性炭处理原水的影响

针对从臭氧-活性炭工艺中开发出来的预臭氧-曝气生物活性炭,在不同气水比工况下进行实验,分析了不同气水比对曝气生物活性炭处理微污染原水的影响与作用。结果表明:在滤速为8～12 m/h,空床接触时间为11.5～15.4 min,装填密度为510 g/L条件下,不同气水比对去除氨氮的影响大于对CODMn的影响。气水比为0.3∶1时,对氨氮浓度为1.65～2.10 mg/L范围的进水平均去除率为81.9%,亚硝酸盐氮平均积累率为1.4%,CODMn去除率为70.6%。当气水比逐渐增加时,氨氮平均去除率有所提高,亚硝酸盐氮积累率则有所下降,对较低浓度的CODMn影响不大。     

MBR处理低浓度稠油废水

为解决稠油废水达标排放问题,构建了一套中试实验装置,以经过除油、浮选和过滤预处理的富含溶解性有机化合物、氮磷缺乏的低浓度难生化稠油废水为原水,进行了187 d的连续运行,结果表明,经过厌氧和好氧生物处理后,出水COD可降至80~100 mg/L以下,再经膜过滤后COD降至60~80 mg/L,加入少量的粉末活性炭进行吸附处理后,出水COD可稳定在50 mg/L以下;水力停留时间从72 h降至30 h时,出水COD基本无变化;气相色谱-质谱分析表明该系统容易去除的有机物为酮类、醇类等物质,而烷烃(C17~C25)和芳烃等为本工艺难降解物质,通过膜生物反应器工艺优化或选择专门降解菌如Acinetobacter spp.进行处理可进一步降低出水COD的浓度。     

What is the acceptable margin of error for the oxygen uptake method in evaluating the reactivity of organic waste?

The acceptable margin of error for the organic waste reactivity measured by the oxygen uptake method was assessed. Oxygen uptake was determined by the Dynamic Respiration Index (DRI) (mgO₂/kgVS h). The composed uncertainty (uC) of the experimental set up used for the DRI test was evaluated and the uncertainty (u) of all the components of the apparatus was evaluated. A procedure for calculating the uC of the apparatus is proposed. The components affecting the uC of the DRI to a more significant extent were the one of the oxygen mass rate and the u of the amount of VS in the sample analyzed. For a confidence level of 99.73%, the extended uC (UC) interval for a DRI = 1024 mgO₂/kgVS h was ±440 mgO₂/kgVS h, whereas for a DRI = 3489 mgO₂/kgVS h, the UC interval was ±1288 mgO₂/kgVS h. When oxygen consumption and VS content become lower than 600 mgO₂/h and 0.9 kg, respectively, the UC interval is similar to the measured DRI.     

颗粒计数法在高锰酸钾强化常规工艺运行优化中的应用

以引黄水库水为实验原水,通过颗粒计数和浊度的联用检测优化评估了高锰酸钾强化常规处理工艺中的各制水环节的处理效果。结果表明,絮凝出水10μm颗粒数和过滤出水2~7μm颗粒数的可作为水厂运行管理的依据,滤后水的颗粒物数量变化比浊度更灵敏准确地反映滤池运行状况;在高锰酸钾强化预处理的最佳投加量为0.8 mg/L时,原常规工艺沉淀对颗粒总数的去除率提高20.55%,滤后颗粒总数减少56.40%,显著降低了"两虫"穿透滤池的风险。     

预缺氧池配水比对Johannesburg工艺脱氮除磷效果的影响

以处理城市污水的中试规模Johannesburg工艺为对象,探讨不同配水比对预缺氧池的反硝化及Johannesburg工艺脱氮除磷效果的影响。在总HRT为12.86 h,预缺氧池HRT为0.6 h的条件下,当配水比分别为0%、10%、20%和30%时,预缺氧池硝酸盐去除率分别为37.67%、78.95%、87.62%和94.95%,对应的厌氧池磷酸盐浓度分别为8.72、19.37、16.1和12.99 mg/L。预缺氧池最佳配水比为10%,此时厌氧段释磷速率、好氧吸磷速率和缺氧吸磷速率分别为6.94、3.17和2.12 mg/(g MLSS·h),厌氧池中磷的最大浓度和污泥中的磷最大含量可达到19.37 mg/L和25.7 mg TP/g MLSS。出水COD、NH3-N、TN和TP等各项水质指标有80%以上的概率达到《城镇污水处理厂污染物排放标准(GB18918-2002)》一级A标准。