MBBR处理猪场废水厌氧消化液的研究

采用移动床生物膜反应器(MBBR)处理猪场废水厌氧消化液,考察了水力停留时间(HRT),进水COD和NH3-N浓度对反应器处理效果的影响.结果表明,在温度为20～30℃,填料填充比为50%,进水COD和NH3-N浓度分别为1016 mg/L和496 mg/L条件下,当HRT为12.5 h时,COD和NH3-N去除率可分别达到62%和77%,猪场废水厌氧消化液中可生物降解性有机物基本得到去除,当HRT增至23.8 h时,COD和NH3-N去除率分别为64%和86%,出水COD和NH3-N浓度分别为368 mg/L和70 ms/L,均达到了<畜禽养殖业污染物排放标准>(GB18596-2001)的要求.     

曝气生物滤池处理生活污水研究

研究了上向流式曝气生物滤池反应器对生活污水COD和NH3-N的启动性能.结果表明,在启动期间,COD和NH3-N的最佳去除率分别达到了94.8%和93.2%;稳定运行期间,在气水比为3:1的条件下,曝气生物滤池对COD和NH3-N的平均去除率分别为95.9%和93.7%;沿程COD和NH3-N的去除率随着滤层高度的增加...     

组合填料生物滤池处理锦纶废水二级出水的性能研究

为解决纺织行业水回用问题,采用陶粒和活性炭组合填料生物滤池对锦纶废水二级生物处理出水进行了深度净化,并考察了气水比和水力负荷对曝气生物滤池处理效果的影响.研究结果表明,曝气生物滤池处理效果良好,平均出水COD、NH4 -N和TN分别为32 mg/L、1.5 mg/L和8.1 mg/L.随着气水比的增加,COD和NH4 -N平均去除率相应提高,TN平均去除率先增大后降低,当气水比为2∶1时,COD、NH4 -N和TN平均去除率分别为48.30%、84.24%和42.18%;随着水力负荷的增加,COD、NH4 -N和TN平均去除率均降低,当水力负荷为0.39 m3/m2·h时,COD、NH4 -N和TN平均去除率分别为48.33%、84.81%和42.54%.     

硅酸钙微粉吸附预处理焦化废水中COD和NH3-N的实验研究

首次将固体废弃物硅酸钙微粉用于焦化废水的预处理,通过静态和动态吸附实验评价了硅酸钙微粉对COD和NH3-N的去除效果。结果表明:对COD和NH3-N产生吸附作用的有效组分为硅酸钙微粉的水解产物H2SiO3电离产生的HSiO3-和SiO23-;pH通过影响硅酸钙微粉水解反应以及水解产物H2SiO3和有机物、NH3的电离反应来影响去除率。在进水pH=7.00、硅酸钙微粉投加量为170g/L、振荡时间为75min的条件下,静态吸附实验中COD和NH3-N的去除率分别达16.1%和27.1%;经直径为10mm、高度为300mm的硅酸钙吸附柱预处理,动态吸附实验中COD和NH3-N的去除率分别可达58.9%和35.9%。     

AS-SMBR工艺处理垃圾渗滤液实验研究

采用AS-SMBR工艺处理城市生活垃圾填埋场渗滤液,选择DO 2～4 mg/L、HRT50～60 h,在常温环境下运行结果表明:AS-SMBR工艺对垃圾渗滤液中COD和氨氮具有高效的去除效果,COD总去除率在50%～60%,NH3-N去除效率在95%以上;COD和NH3-N运行负荷分别为0.2～0.3 kg COD/(kg MLSS.d)和0.06～0.18 g NH3-N/(g MLSS.d);垃圾渗滤液生化系统对大分子物质的降解程度对膜去除效率有重要影响,两者对COD去除效率呈现波浪式交替变化。     

人工湿地对北方城市污水深度处理效果的研究

采用三级串联人工湿地试验装置以及无芦苇的空白对照装置在户外自然条件下进行试验,分阶段考察该组合式人工湿地系统对实际城市污水的深度处理效果.第一阶段为装置初运行阶段,采用较长的停留时间,该阶段装置对COD、TN、NH3-N、NO2--N和TP的去除率分别为75%、75%、95%、75%和50%.芦苇的存在使以上各指标相对于空白对照分别提高了10%、40%,20%、20%和50%;第二阶段采用较短的停留时间,该阶段装置对COD、TN、NH3-N、NO2--N和TP的去除率分别为85%、75%、100%、70%和98%,芦苇的存在使以上各指标相对于空白对照分别提高了10%、20%、35%、25%和63%.试验结果表明,该试验装置对城市污水具有较好的深度处理效果,能够有效降低水中的N和P,对改善水质、恢复生态系统和控制水体富营养化问题具有重要意义.     

微波辅助絮凝处理养猪场废水实验研究

通过在养猪场废水中加入絮凝剂和助凝剂,并采用微波辐射的方法,研究了微波辅助絮凝对养猪场废水的前处理效果,考察了单一絮凝、单一微波和絮凝微波联用3种条件下对COD和NH+4-N的去除效果。结果表明,硫酸亚铁是较为合适的絮凝剂,当投加量为50mg/L时,COD和NH+4-N的去除率分别为23.5%和25.1%;投加助凝剂对提高絮凝效果有一定的作用,但并不明显;敏化剂投加量为5g/L、微波辐射时间为30s的条件下,COD和NH+4-N的去除率分别可达到48.4%和25.2%;和单一絮凝、单一微波相比,絮凝微波联用对养猪场废水COD和NH+4-N的去除率提高不是很明显,建议工程中不必联用。     

超声波-膜生物法联合处理垃圾焚烧厂渗滤液

采用超声波-膜生物法(MBR)联合处理垃圾渗滤液,探讨了超声波辐射时间和MBR的水力负荷对COD、NH3-N和TP去除的影响。结果表明,(1)超声波单独处理时,超声波辐射时间在30～90 s时,COD、NH3-N最大增加率分别34.31%、3.36%,而对TP的去除没有影响;(2)超声波-膜生物(MBR)联合处理时,超声波辐射时间为300 s,MBR的水力负荷为6.4 L/(m2.d)时,COD、NH3-N和TP的最佳去除率分别为92.20%、80.10%和91.12%;MBR的水力负荷为12.8 L/(m2.d),超声波辐射时间在5～20 min时,COD、NH3-N的最佳去除率分别为92.34%、79.93%,TP的浓度低于0.2 mg/L;MBR反应时间为7 h,超声波辐射时间为5～20 min,与未进行超声波辐射处理(超声波辐射时间为0 min)相比,COD、NH3-N的去除率增加了11.37%、15.26%;超声波预处理有助于提高后续MBR对COD、NH3-N的去除作用。     

平板膜-生物反应器净化微污染水源水的研究

利用平板膜-生物反应器恒流运行处理微污染水源水,考察通量为18、25及30 L/m2·h时其运行特性及有机物和氨氮的去除效果.结果表明:3个工况对COD的去除率分别为78.7%、76.9%和80.4%,出水COD低于15 mg/L;3个工况对NH4 -N的去除率分别为90.4%、87.4%和92.8%,出水NH4 -N低于0.5 mg/L;3个工况对UV254的去除率分别为27.5%、28.2%和48.1%.胞外聚合物(EPS)的研究结果表明,其与膜污染之间并没有显著关系,运行通量的选择是影响膜污染和操作运行的一个重要原因.     

包埋法处理抗生素废水的试验研究

采用包埋活性污泥对抗生素废水进行了试验研究,以COD、BOD5、NH3-N和TN去除率为指标,考察包埋活性污泥处理抗生素废水的可行性,结果表明,COD、BOD5、NH3-N和TN去除率分别为68.02%、78.80%、45.00%和49.11%.说明包埋法处理抗生素废水是可行的,尤其是去除TN上具有一定的优势.     

Patterns of volatile metabolites and nonvolatile trichothecenes produced by isolates of <Emphasis Type="Italic">Stachybotrys,Fusarium, Trichoderma,Trichothecium</Emphasis> and <Emphasis Type="Italic">Memnoniella</Emphasis>

We reported previously that trichodiene, a volatile trichothecene derivative, was produced by a Stachybotrys isolate, also known to produce highly cytotoxic, non-volatile, macrocyclic trichothecenes (satrotoxins). We investigated the relationship between the production of trichodiene and various non-volatile trichothecenes for several molds. Volatile metabolites were concentrated by adsorption on Tenax TA and analyzed by GC/MS, while non-volatile metabolites were separated by HPLC, derivatized and analyzed by GC/MS. Stachybotrys chartarum isolates producing macrocyclic trichothecenes secreted significantly larger amounts of trichodiene and other sesquiterpenes than isolates which only produced simple trichothecenes. The amounts of secreted trichodiene were relatively small in all cases. With the exception of Memnoniella, which excreted small amounts of sesquiterpenes, the other isolates produced varying amounts of sesquiterpenes, including trichodiene, as well as simple tricothecenes, no detectable trichodiene, but large amounts of griseofulvin derivatives. In Stachybotrys there is apparently a correlation between trichodiene and macrocyclic trichothecene production. In the remaining isolates, there was no simple relationship between trichodiene and non-volatile trichothecene synthesis. Trichodiene is produced in larger amounts by Stachybotrys isolates, which also produce satratoxins, but it will be difficult to utilize this metabolite to detect toxic isolates in buildings due to the relatively small amounts excreted.     

Effects of Mn(II) and Fe(II) on microbial removal of arsenic (III)

Goal, scope, and background  Arsenic contamination in groundwater creates severe health problems in the world. There are many physiochemical and biological methods available for remediation of arsenic from groundwater. Among them, microbial remediation could be taken as one of the least expensive methods, though it takes longer treatment time. The main objective of this research was to study the improvement on remediation by addition of some essential ion salts such as Mn and Fe. Materials and methods   Staphylococcus aureus, Bacillus subtilis, Klebsiella oxytoca, and Escherichia coli were taken as model microbes from Dhulikhel, 30 km east from Kathmandu, Nepal. Results and discussion  Microbes used in this study showed different abilities in their removal of As(III) with and without addition of Mn and Fe salts. The trend of remediation increased with time. S. aureus was found to be the best among the microbes used. It showed almost 100% removal after 48-h culture, both with and without Fe and Mn salts. Rate of removal of As increased with addition of Fe and Mn for all microbes. Removal efficiency was found to increase by about 32% on average after addition of salts in 24-h cultures of S. aureus.     

Bioindicators for toxicity assesment of effluents from a wastewater treatment plant

The discharge of effluents and toxic compounds into aquatic systems represents a growing environmental problem involving an impact on water ecology and potential effect on human health. Most municipal wastewaters are complex mixtures; their complexity led as to carry out a hazard assessment using chemical analyses and biological tests.This study investigates biochemical alteratiobns in two sentinel organisms, the Anodonta cygnea mussel and the Xenopus laevis frog exposed for different lengths of time to various concentrartion of wastewater of the S. Antonino Ticino treatment plant. The results point out the long-life of toxic compounds.     

利用发光菌和大型蚤对北方某城市再生水急性毒性的调查

利用发光菌和大型蚤作为受试生物测定了北方某城市5个再生水原水(城市污水厂二级出水)和2个再生水处理系统的各工艺出水的急性毒性.结果表明,各再生水原水对大型蚤和发光菌具有不同程度的毒性效应,其中工业废水占较大比例的K和B厂再生水原水的大型蚤48 h总抑制率分别高达90%和100%,发光菌发光抑制率分别达到74.2%和46...     

污泥堆肥施用于草坪草栽培:Zn和Cu的分布特征简

为了探索污泥堆肥中重金属在土壤-植物系统中的积累与转移特性，通过温室盆栽实验，分析了污泥堆肥对草坪草高羊茅、黑麦草和白三叶生物量积累的情况，研究了污泥堆肥中Zn和Cu在植物和土壤中的分布特征。结果表明，污泥堆肥施用可以有效促进3种草坪草的积累生物量，在0~6 kg/m²的污泥堆肥施用量范围内，草坪草的生物量积累随着施用量的增加而提高。土壤中Zn和Cu的含量随污泥堆肥施加量的增加而增大，85%以上的Zn和Cu残留在土壤中。污泥堆肥中的Zn和Cu均可以被植物吸收，随着污泥堆肥施用量的增加，草坪草对Zn和Cu的吸收量增大，但当污泥堆肥施用量超过一定阈值时，草坪草吸收Zn和Cu不再增加，甚至减少；对于不同的草坪草，这一阈值有所不同。植物对Zn和Cu的吸收量只占土壤中Zn和Cu减少量的5%左右。根据生物富集系数（BCF）的计算结果推测，污泥堆肥的施用对土壤环境的影响大于对植物体内累积Zn和Cu的影响。     

氧化亚铁硫杆菌浸铜作用研究

为研究氧化亚铁硫杆菌(Acidithiobacillus ferrooxidans,简称A.f)对铜浸出的作用,从某煤堆积水中分离得到A.f菌,利用该菌对铜进行浸出实验,设置3个处理,3个处理的浸出液分别为9 K培养基(简称S),成熟菌液(简称MS)和过滤除菌液(简称FS)。结果表明,3个处理中铜都得到了浸出,浸出铜浓度按S、FS和MS依次递增分别为4 433、5 377和6 296 mg/L;浸出初期,MS中的铜,浸出速度最快,过滤除菌液中次之,而培养基中的速度比较稳定,比前两者均慢,24 h后三者浸铜速度趋近一致;三者中pH、Eh变化相似,pH均先升高至3.4左右保持相对稳定,Eh均先迅速下降至280 mV后保持稳定。由实验可知,氧化亚铁硫杆菌主要在浸出初期促进了铜的浸出,且菌液中溶解氧氧化Fe2+以及酸性条件下氧化Cu0对铜的浸出作用不容忽视。     

Marine macroalgal community structure, metal content and reproductive function near an acid mine drainage outflow

Marine macroalgal communities were examined near the outflow of acid mine drainage (AMD) from the Britannia Mine, British Columbia, Canada. No marine algae were present within 100 m of the mouth of Britannia Creek, which carries the AMD into the marine environment. At greater distances (300-700 m) from this Creek, mean summer cover of filamentous green algae, mostly Enteromorpha intestinalis, was >60%, which was significantly higher than at nearby reference stations. At still greater distances (600-1000 m) from Britannia Creek, Fucus gardneri dominated algal communities that were similar to those at reference stations. No consistent differences were detected in mean plant length, mean per cent cover or mean oocyte production between F. gardneri near Britannia Creek and those at reference stations. Cu body burden in F. gardneri near Britannia Creek was five to 17 times higher than in reference plants.     

不同质量浓度黄菖蒲和狭叶香蒲对铜绿微囊藻的化感作用简

分别采用黄菖蒲（Iris pseudacorus L.）、狭叶香蒲（Typha angustifolia L.）和铜绿微囊藻（Microcystis aeruginosa）共生培养的实验方法研究了不同质量浓度黄菖蒲、狭叶香蒲对铜绿微囊藻的化感作用。结果表明，黄菖蒲在质量浓度大于10 g/L时对初始密度为1.0×10⁷ ind/mL的铜绿微囊藻具有较好的抑制作用，表现为黄菖蒲质量浓度为10、20和40 g/L时，第15天对铜绿微囊藻的抑制率分别为30.1%、51.8%和84.0%；狭叶香蒲在质量浓度大于20 g/L时对铜绿微囊藻有明显的抑制作用，表现为狭叶香蒲质量浓度为20 g/L和40 g/L时，第15天对铜绿微囊藻的抑制率分别为34.2%和77.7%，实验过程中，铜绿微囊藻叶绿素a含量逐渐减少，而藻密度、SOD活性及MDA含量先增加后逐渐降低，表明经过一段时间持续地化感胁迫，黄菖蒲和狭叶香蒲可以诱导铜绿微囊藻产生氧化胁迫，导致细胞结构严重损伤和叶绿素大量分解，从而强烈抑制铜绿微囊藻的生长。     

Physical-chemical and ecotoxicological evaluation of water based drilling fluids used in Italian off-shore

In order to evaluate the effects on the marine ecosystem caused by an eventual discharge into sea of water based drilling fluids, as current legislation allows, chemical and ecotoxicological analyses were performed on the most common drilling muds and products used in Italian off-shore activities. The chemical analysis on drilling fluids involved the leaching test and the measurement of total content of heavy metals, whereas biodegradation tests were performed on the products used in mud's formulations. As for ecotoxicological evaluation, two marine organisms, the crustacean Artemia salina and the diatom Phaeodactylum tricornutum, were selected to determine the LC₅₀ and the EC₅₀ respectively.