Ni2+对2-氯酚厌氧降解系统的影响

针对重金属对难降解有毒有机物厌氧降解的影响问题,采用间歇试验法研究Ni2 对2-氯酚(2-CP)厌氧降解系统的影响规律.结果表明,当ρ(Ni2 )＜5 mg/L时,Ni2 对2-CP厌氧降解表现出轻度促进,当ρ(Ni2 )为5～500 mg/L,Ni2 以抑制作用为主,抑制作用随ρ(Ni2 )的增加而增强.Ni2 对原基质及关键中间产物苯酚和苯甲酸的抑制程度表现为:苯酚＞苯甲酸＞2-CP;ρ(Ni2 )低时的驯化能有效提高厌氧污泥对Ni2 毒性的耐受性能,300 mg/L Ni2 对2-CP降解的抑制从驯化前的65%降至驯化后的21%.Ni2 对2-CP厌氧降解的抑制作用与污泥中Ni的截留量之间存在正相关关系.抑制浓度CIP值和方程αC=[1-(I/I*)m]/[1 (I/I*)n)]能较好地表征厌氧生物处理过程受抑制程度.     

抗生素制药废水的处理

锦州九泰制药废水属于不易生化类废水，废水量1000m^3/d，污水站总投资140万元。本文阐述了该工程的水质、预处理、生化处理工艺、活性污泥的培养与驯化及运行效果与设计特点。     

驯化菌种降解油制气废水的影响因素研究

利用筛选的3种微生物,在初步研究其对某些化合物降解能力的基础上,考察其降解油制气废水过程中一般因素如温度、pH值、供氧条件、废水浓度以及营养因素如磷源、碳源对微生物降解能力的影响。研究表明,各菌种可在自然环境条件范围内,保持对废水CODCr降解效果的稳定性。葡萄糖、乙醇的加入,可将各菌种对CODCr的去除率分别提高16.9%~26.5%、17.6%~25.6%。     

贵州木本食用油料资源及其开发利用

对贵州野生特有和稀有的大宗木本食用油料的种类、分布、现状等进行了分析，提出了提高大宗食用木本油料经营水平，选择利用野生木本油料植物资源，加强特有和稀有资源的保护、驯化和繁殖等开发利用建议。     

稠油污水生化性处理技术研究

为了探讨稠油污水能否使用生物法处理,以生活污水和农药厂生化池原菌种经过诱导驯化,分别培养了可以在稠油污水中生长的好氧菌种革兰氏阴性菌G-1和厌氧菌种革兰氏阴性菌G-2.以G-2和G-1对稠油污水进行顺序处理,可使其BOD5/CODCr达到0.26;采用SBR法对新疆稠油污水放大处理试验的结果：COD降至150 mg/L以下,各项指标达到GB8978-1998二级排放标准.     

复合膜生物反应器处理环氧氯丙烷废水

实验利用复合膜生物反应器处理以甘油为原料制备环氧氯丙烷产生的废水,考察了不同进水COD、水力停留时间以及盐度对处理能力的影响,并进行盐度冲击实验。生物处理后出水进行了深度处理的研究。结果表明:进水COD对处理能力影响较小;适当延长水力停留时间能优化出水水质;废水盐度高于22g/L时会对微生物产生抑制作用;深度处理能进一步降低出水COD;微生物通过一定时间的驯化期能适应并处理高盐度废水。     

浅谈厌氧生物处理工艺在污水处理工程实践中的应用

对厌氧生物处理工艺的进展进行较全面的叙述,分析厌氧生物处理技术可行性及影响因素,重点剖析厌氧设备的启动中厌氧污泥的培养和驯化、厌氧反应器运行中的欠平衡现象及原因分析.提出了污水处理厂应建立健全的日常安全管理制度和完善的突发事件应急机制.     

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.