硫粉投加量与污泥含固率之比对生物淋滤过程的影响

通过接种污泥硫细菌混合菌液,研究了S粉投加量与污泥含固率之比(SA/TS)对城市污泥中重金属生物淋滤效果的影响.结果表明,增大SA/TS值能显著缩短淋滤时间,提高淋滤效果.当SA/TS为2.5,经过8 d生物淋滤,Cu和Zn的淋滤效果可达到最佳,溶出率分别为66.2%和63.9%.淋滤进行16 d后,Pb的溶出率为30.8%.对于Cu,不论淋滤前后有机态都是较强的结合态.Zn的溶出主要是由于结合能力强的铁锰氧化态在淋滤过程中被大量浸出.Pb经过16 d的淋滤,铁锰氧化态所占比例有所下降而有机态比例上升.加大SA/TS有利于提高S粉的利用率,对N的保存影响不大,但增加了P的流失.     

饮用水水源及水厂内分泌干扰物污染分析

对国内的饮用水水源地内分泌干扰物污染现状进行总结,发现我国饮用水水源地很多地区都存在着内分泌干扰物的污染,由于地域的不同,污染物的种类存在差异,但有机氯农药和多氯联苯类化合物的污染尤为严重。同时对水源地内分泌干扰物的种类、来源及生物学效应进行综述,并对内分泌干扰物的毒性作用机制进行了归纳,发现不同来源的内分泌干扰物,毒性作用机制不同,且一种内分泌干扰物可能同时存在多种作用机制。     

农村环境质量影响因素量化分析模型研究

通过对山阴县40个村庄的实际调查,分析影响农村环境质量的主要影响因素,建立多元回归模型,得出了农村居民人均纯收入、国家环保事业的资金投入、中国农村家庭的主要能源结构为主要影响因素,并通过实例验证该模型的可行性。     

铜绿假单胞菌对白腐菌产木质纤维素降解酶的影响

采用固态发酵的方法,考察了两株不同型号的铜绿假单胞菌（AB93066和ATCC9027）对白腐菌（黄孢原毛平革菌）产木质纤维素降解酶（木素过氧化物酶LiP、锰过氧化物酶MnP和羧甲基纤维素酶CMCase）的影响,并对酶提取液的pH值、表面张力及稻草降解残渣中挥发性有机质含量的变化进行了分析.结果表明,添加5.72%的A...     

Feasibility of bioleaching combined with Fenton oxidation to improve sewage sludge dewaterability

A novel joint method of bioleaching with Fenton oxidation was applied to condition sewage sludge. The specific resistance to filtration (SRF) and moisture of sludge cake (MSC) were adopted to evaluate the improvement of sludge dewaterability. After 2-day bioleaching, the sludge pH dropped to about 2.5 which satisfied the acidic condition for Fenton oxidation. Meanwhile, the SRF declined from 6.45 × 10¹⁰ to 2.07 × 10¹⁰ s²/g, and MSC decreased from 91.42% to 87.66%. The bioleached sludge was further conditioned with Fenton oxidation. From an economical point of view, the optimal dosages of H₂O₂ and Fe^2 + were 0.12 and 0.036 mol/L, respectively, and the optimal reaction time was 60 min. Under optimal conditions, SRF, volatile solids reduction, and MSC were 3.43 × 10⁸ s²/g, 36.93%, and 79.58%, respectively. The stability and settleability of sewage sludge were both improved significantly. Besides, the results indicated that bioleaching-Fenton oxidation was more efficient in dewatering the sewage sludge than traditional Fenton oxidation. The sludge conditioning mechanisms by bioleaching-Fenton oxidation might mainly include the flocculation effects and the releases of extracellular polymeric substances–bound water and intercellular water.     

Effects of different sludge disintegration methods on sludge moisture distribution and dewatering performance

A key step in sludge treatment is sludge dewatering. However, activated sludge is generally very difficult to be dewatered. Sludge dewatering performance is largely affected by the sludge moisture distribution. Sludge disintegration can destroy the sludge structure and cell wall, so as change the sludge floc structure and moisture distribution, thus affecting the dewatering performance of sludge. In this article, the disintegration methods were ultrasound treatment, K2 Fe O4oxidation and KMn O4 oxidation. The degree of disintegration(DDCOD), sludge moisture distribution and the final water content of sludge cake after centrifuging were measured. Results showed that three disintegration methods were all effective, and K2 Fe O4oxidation was more efficient than KMn O4 oxidation. The content of free water increased obviously with K2 Fe O4and KMn O4 oxidations, while it decreased with ultrasound treatment. The changes of free water and interstitial water were in the opposite trend. The content of bounding water decreased with K2 Fe O4oxidation, and increased slightly with KMn O4 oxidation, while it increased obviously with ultrasound treatment. The water content of sludge cake after centrifuging decreased with K2 Fe O4oxidation, and did not changed with KMn O4 oxidation, but increased obviously with ultrasound treatment. In summary, ultrasound treatment deteriorated the sludge dewaterability, while K2 Fe O4and KMn O4 oxidation improved the sludge dewaterability.     

Interaction between Cu and different types of surface-modified nanoscale zero-valent iron during their transport in porous media

This study investigated the interaction between Cu^2 + and nano zero-valent iron (NZVI) coated with three types of stabilizers (i.e., polyacrylic acid [PAA], Tween-20 and starch) by examining the Cu^2 + uptake, colloidal stability and mobility of surface-modified NZVI (SM-NZVI) in the presence of Cu^2 +. The uptake of Cu^2 + by SM-NZVI and the colloidal stability of the Cu-bearing SM-NZVI were examined in batch tests. The results showed that NZVI coated with different modifiers exhibited different affinities for Cu^2 +, which resulted in varying colloidal stability of different SM-NZVI in the presence of Cu^2 +. The presence of Cu^2 + exerted a slight influence on the aggregation and settling of NZVI modified with PAA or Tween-20. However, the presence of Cu^2 + caused significant aggregation and sedimentation of starch-modified NZVI, which is due to Cu^2 + complexation with the starch molecules coated on the surface of the particles. Column experiments were conducted to investigate the co-transport of Cu^2 + in association with SM-NZVI in water-saturated quartz sand. It was presumed that a physical straining mechanism accounted for the retention of Cu-bearing SM-NZVI in the porous media. Moreover, the enhanced aggregation of SM-NZVI in the presence of Cu^2 + may be contributing to this straining effect.     

SBR系统中同步硝化反硝化好氧颗粒污泥的培养

采用人工配制的模拟生活污水,研究序批式反应器(SBR)中好氧颗粒污泥的培养.实验结果表明:通过对进水碳源进行调控,反应器中形成了高活性具有同步硝化反硝化能力的好氧颗粒污泥,反应器中COD和NH₃-N的去除率分别为74.0%～92.8%和82.3%～98.5%.颗粒污泥的粒径一般为0.5～1.0mm,MLSS达到4.5g·L^-1以上,SVI值约为32.5,其有效生物量及脱氮性能远远高于一般的好氧活性污泥.     

Recent advances in research on cyclic volatile methylsiloxanes in sediment,soil and biosolid: a review

Three cyclic volatile methylsiloxanes (cVMS) were widely used in various processes of production and industrials and frequently added to consumer products. cVMS are continuously released into the environment, causing increasing environmental and human exposing risks. cVMS were investigated in air, water, biogas, soil, sediment, biosolid and organism. Many scholars focused on the occurrence, behaviours, fate and effects of cVMS in environmental matrices all over the world. However, few studies paid attention to the environmental behaviour of cVMS in the solid phase. We assessed their environmental behaviour and fate in soil, biosolid and sediment. High concentrations of cVMS were detected in biosolids. Volatilisation, adsorption and degradation were the major environmental behaviours for cVMS in the solid phase. Although some aquatic organisms showed an appropriate level of bioaccumulation and bioconcentration, there were no obvious evidence of trophic biomagnification in aquatic food webs for octamethylcyclotetrasiloxane (D4) and decamethylcyclopentasiloxane (D5). In addition, cVMS in the environment have not impacted for natural organisms because the concentrations in soil and sediment have not exceeded the maximum no-observed-effect-concentration threshold. Finally, regarding the major environmental behaviour in soil and sediment, suggestions for further study are proposed.