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1.
1,2,4-三氯苯是我国工业污染场地土壤和地下水中典型的有机污染物,具有持久性、生物蓄积性和高毒性特点,对生态环境和人体健康危害巨大。1,2,4-三氯苯密度比水大,容易迁移至深部厌氧区域,因此,开展1,2,4-三氯苯厌氧微生物降解与修复研究具有重要实际应用价值。本文通过长期富集培养,获得一份可以稳定地将1,2,4-三氯苯还原脱氯至1,4-二氯苯,再进一步还原脱氯至氯苯的厌氧菌液。通过16S rRNA基因扩增子测序及引物特异性的定量PCR实验,证明厚壁菌门的脱卤杆菌属细菌(Dehalobacter species)是1,2,4-三氯苯和1,4-二氯苯厌氧还原脱卤的功能菌株,其生长率为(1.68±0.8)×106 copies·μmol-1(释放的氯离子)。通过PCR扩增,获得Dehalobacter菌株的16S rRNA基因序列,构建了系统发育树。本研究可为1,2,4-三氯苯污染场地开展原位厌氧微生物修复提供菌株资源和理论指导。  相似文献   

2.
通过铝盐与蒙脱石(Na-Mt)反应制备了铝柱撑蒙脱石(Al-Mt),同时采用X射线衍射(XRD)、红外光谱(FTIR)对在不同温度(200~600℃)下煅烧获得的铝柱撑蒙脱石产物(At-Mt-X)进行表征。探讨Fe(Ⅱ)与Al-Mt-X所形成的复合系统对邻硝基苯酚(2-NP)的吸附-还原降解行为,包括铝柱撑蒙脱石的煅烧温度、煅烧铝柱撑蒙脱石的表面酸位变化以及溶液pH值等条件对邻硝基苯酚还原转化的影响。结果表明,由于随着煅烧温度的升高,煅烧铝柱撑蒙脱石表面酸性位点会逐渐减少,使得其对Fe(Ⅱ)的还原性能增强;煅烧温度高于500℃时,煅烧改性产物与Fe(Ⅱ)形成的Fe(Ⅱ)/煅烧铝柱撑蒙脱石复合系统显著提高了Fe(Ⅱ)物种的还原活性,因而有效增强对2-NP的还原降解。此外,Fe(Ⅱ)/煅烧铝柱撑蒙脱石复合系统对2-NP的还原降解符合准一级反应动力学方程,表观速率常数(k)随pH值和铝柱撑蒙脱石煅烧温度的升高而增大。作为一种功能性矿物材料,煅烧铝柱撑蒙脱石在缺氧环境下能有效促进吸附态Fe(Ⅱ)物种对污染物的还原降解,煅烧温度与pH值是其中两个重要的制约因素。  相似文献   

3.
系统考查了Fe(Ⅱ)分别与高岭石、蒙脱石结合的界面结合系统对邻硝基苯酚(简称2-NP)的还原转化作用。研究表明,矿物表面结合态Fe(Ⅱ)能够有效提高2-NP的还原转化速率,2-NP的还原反应符合伪一级反应动力学方程,而且速率常数(k)随溶液p H值、亚铁离子初始浓度以及反应温度的升高而显著增大。当温度25℃,p H值6. 7,Fe(Ⅱ)和2-NP初始浓度分别为3. 0 mmol/L、0. 022 mmol/L,以及黏土的投加量为4. 0 g/L时,Fe(Ⅱ)/高岭石系统对2-NP的还原转化率在4. 0 h内可达到100%。同样,p H值从6. 0升高至7. 3时,Fe(Ⅱ)/蒙脱石系统对2-NP的还原转化也显著增强;但在较低p H值和较低初始Fe(Ⅱ)浓度时,蒙脱石对Fe(Ⅱ)的还原催化性能不如高岭石,可归因于蒙脱石具有较高的离子交换性能。因此,Fe(Ⅱ)在上述两种矿物上吸附形态的差异是导致该系统对2-NP还原转化出现不同效应的根本原因。  相似文献   

4.
零价铜作为一种廉价金属很少应用于促进氯代有机物脱氯研究,其原因是零价铜的催化还原脱氯活性差,且反应机制复杂。本文采用机械球磨技术制备了Cu-Fe和Cu-Ni合金,研究零价铜在不同微观环境下对对氯苯酚(4-CP)的脱氯行为,旨在考察有机氯分子结构对零价铜脱氯机制的影响。应用扫描电镜-能谱(SEM-EDS)及色相色谱-质谱(GC-MS)分析发现,铜原子的微环境及有机氯分子结构均影响铜的脱氯机制。在Cu-Fe体系中,Cu遵循经典的催化加氢脱氯机制,4-CP的降解产物为苯酚;Cu-Ni体系的还原作用来源于零价铜,其中的镍金属并未起到催化加氢作用,Cu-Ni合金及单独零价铜对4-CP的降解产物是环己酮。零价铜对4-CP的降解率可达70%以上,而Cu-Fe体系的降解率仅为34%,两者对芳香族氯代物的降解效率差距显著。零价铜能够降解化学稳定性高的4-CP和苯酚,但不能降解化学稳定性相对较差的脂肪族氯代有机物(如一氯乙酸和二氯乙酸),因此认为零价铜脱氯机制并非传统的催化加氢机制,而是遵循直接电子传递还原机制,且有机氯分子的苯环结构是零价铜直接电子传递还原的诱因。  相似文献   

5.
本文以阳离子表面活性剂(十六烷基三甲基溴化铵,HDTMAB)为柱撑剂,在不同浓度条件下(0.5～2.5CEC)制备了层间季铵盐离子呈单层平卧、双层平卧和倾斜双层排列的HDTMA 柱撑蒙脱石,并研究了具有不同层间结构的HDTMA 柱撑蒙脱石对对硝基苯酚的吸附能力以及溶液pH值、温度、对硝基苯酚初始浓度等因素对HDTMA 柱撑蒙脱石吸附性能的影响。实验结果表明,HDTMA 柱撑蒙脱石对对硝基苯酚的吸附能力随着介质溶液pH值的升高而升高,这主要受对硝基苯酚在不同pH条件下的离子化程度影响;HDTMA 柱撑蒙脱石对对硝基苯酚的吸附能力随着介质溶液温度的升高而降低,说明吸附反应是一个放热过程。同时,从单层平卧→双层平卧→倾斜双层,HDTMA 柱撑蒙脱石对对硝基苯酚的吸附能力明显提高。钠基蒙脱石和低堆垛密度(单层平卧、双层平卧)的HDTMA 柱撑蒙脱石对对硝基苯酚的吸附等温线呈S型,而高堆垛密度(倾斜双层)的HDTMA 柱撑蒙脱石对对硝基苯酚的吸附等温线呈Linear型,表明前者以表面吸附为主,后者以分配作用为主。  相似文献   

6.
四氯乙烯的生物吸附和厌氧生物降解研究   总被引：2，自引：2，他引：0  
四氯乙烯(PCE)的广泛使用和不合理的处置已经使其成为地下水中普遍存在的有毒有害的有机污染物。PCE在厌氧条件下通过还原脱氯发生生物降解,按照非水溶性生物降解模型,有机物先吸附到厌氧活性污泥中,解吸后再进行生物降解。利用间歇试验进行厌养污泥对PCE的吸附降解实验研究。试验结果表明：厌氧污泥对PCE的吸附在0.5 h达到吸附平衡,在1.0 h达到解吸平衡。对实验结果的回归分析表明：PCE的吸附和解吸均符合Freundlich等温吸附方程。厌氧污泥在微生物的作用下将PCE还原脱氯为TCE和DCEs。  相似文献   

7.
制备了不同阳离子掺杂改性的针铁矿,并采用XRD、红外、热重差热分析以及TEM等手段对其进行了表征,结果显示,掺入Mn~(2+)、Cr~(3+)、Al~(3+)后并未明显改变α-FeOOH的晶体结构类型,说明部分阳离子掺杂进入α-FeOOH晶格,从而分别形成因Fe~(3+)被Mn~(2+)、Cr~(3+)、Al~(3+)部分取代的固溶体;红外分析也得到类似结果;热重和差热分析以及TEM观察结果均表明几种金属阳离子没有形成氧化物相,可以确定这些离子已经进入针铁矿的晶格;紫外-可见漫反射光谱分析发现Mn~(2+)、Cr~(3+)掺杂者的能带隙较之纯相针铁矿的稍小,依次为2.18 e V和2.24 e V;而Al~(3+)掺杂者的能带隙与纯相针铁矿相比有所提高,增加至2.34 e V。此外还考查了不同阳离子掺杂及纯相针铁矿与Fe(Ⅱ)构成的复合系统对邻硝基苯酚(2-NP)的还原效果,研究表明,在溶液pH=6和25℃等的条件下,上述还原转化反应符合准一级动力学方程。其中,Fe(Ⅱ)/Al~(3+)掺杂针铁矿复合系统对2-NP的降解效果最好,在120 min时就达到了100%去除率,在一定浓度范围内,随着2-NP浓度的升高,2-NP的还原速率降低。而且,Fe(Ⅱ)/Al~(3+)-针铁矿复合系统速率常数(k)随着溶液的pH值增大而升高。  相似文献   

8.
研究了山西代县天然金红石在紫外光和日光照射条件下对苯酚的光催化降解性能,考察了光照时间、pH值、苯酚初始浓度以及H2O2添加量对降解过程的影响。在紫外光照射下,酸性条件(pH=3.5)利于光催化降解,中性和碱性条件下降解效率较低;当初始浓度为60mg/L时,降解速率可达1.922mg/(L.h);H2O2作为电子捕获剂可提高苯酚降解速率,最佳投加量为2mL/L。在日光条件下,天然金红石对苯酚表现出良好的降解性能,照射7h后,降解率达87.68%,仅略低于P25型TiO2(99.72%),可在14h内完全降解。根据电子探针和X射线衍射分析结果,认为天然金红石晶格中的V、Fe等杂质可能是提高其可见光响应效果和光催化活性的主要原因。  相似文献   

9.
建立了离子对色谱法同时测定水中DCPA二元酸、4-硝基苯酚、麦草畏、苯达松、2,4-二氯苯乙酸、2-甲基-4-氯苯氧乙酸(MCPA)、2-(4-氯苯氧基-2甲基)丙酸(MCPP)、3,5-二氯苯甲酸、2,4-滴丙酸9种氯代酸性除草剂。通过加入离子对试剂使多种极性强、保留弱的酸性除草剂在普通的反相色谱柱上同时分离。采用Shim-pack VP-ODS色谱柱,流动相为V(1-辛烷三乙磷酸铵溶液)∶V(乙腈)∶V(甲醇)=6∶3∶1,流速1.8 mL/min,不同组分全流程方法检出限范围为0.03~0.15μg/L,相对标准偏差在10%以下。建立的方法可将9种除草剂完全分离,与高效液相色谱法和气相色谱-质谱法相比,具有操作简单、分离效果好、回收率高、干扰少的优点,能够满足不同水质的检测要求。  相似文献   

10.
谭皓月  文章  朱棋  杨舒婷  蔡其正  刘慧 《地球科学》2022,47(11):4184-4195
在室内砂槽实验尺度,建立了潜水-微承压含水层中电化学-水动力循环系统下混合氯代烃生物降解的反应迁移模型,求取了混合氯代烃体系中各组分的反应动力学参数,并基于模型探究了含水层性质及工艺参数对该修复过程的影响机制.研究结果表明:（1）增大抽水流量可加快反应速率常数大的污染物降解,同时也会抑制反应速率常数较小的污染物去除.（2）增大电流强度和井内电极对氯代烃的好氧降解和厌氧脱氯过程分别具有促进和抑制作用.（3）含水层非均质性越强,氯代烃降解速率越小,这尤其体现在低渗区,且含水层非均质性对易降解污染物修复效果的影响较小.   相似文献   

11.
Chloroaromatics in groundwater: chances of bioremediation   总被引：1，自引：0，他引：1  
. The potential for biodegrading of mono-, di- and trichlorobenzenes in a contaminated aquifer in Bitterfeld (Saxony-Anhalt) was tested both in the laboratory and using on-site column experiments. Under the prevailing anaerobic conditions, the reductive dechlorination of 1,4-dichlorobenzene (1,4-DCB) takes place very slowly. Under aerobic conditions the indigenous micro-organisms are able to mineralize monochlorobenzene (MCB) and 1,4-DCB. The degradation rates for the other two isomeric dichlorobenzenes and for 1,2,4-trichlorobenzene (1,2,4-TCB) under aerobic conditions are significantly lower. Indications were found that once the oxygen has been consumed, Fe(III) species can be used as alternative electron acceptors.  相似文献   

12.
1,2,4-trichlorobenzene (1,2,4-TCB) is one of the most common pollutants in landfill leachate that impacts shallow drinking groundwater quality; accordingly, the transport mechanism and capacity for remediation of this compound are important to the management of local water resource. In this study, a series of indoor experiments and analytical predictions revealed that the transportation of 1,2,4-TCB in groundwater is similar in medium sand and fine sand. Specifically, the peak time increases with distance between monitoring points and the source point, but the peak relative concentrations decrease with distance, indicating that the concentration of 1,2,4-TCB in groundwater is controlled by adsorption and biodegradation. In addition, transportation of water in a fine sand column was lower than that in a medium sand column; therefore, the adsorption and biodegradation of 1,2,4-TCB in groundwater was lower in the medium sand column. These findings demonstrate that 1,2,4-TCB in groundwater could be removed by natural degradation after about 5 years, but that other methods (permeable reactive barriers, air sparging or biosparging) should be applied in the field to shorten the remediation period and enhance water supply safety around landfill.  相似文献   

13.
The Luhuagang landfill site (LLS) in Kaifeng, China, lacks liner and leachate collection systems. Thus, leachate generated from the waste dump has contaminated the surrounding subsoil and shallow aquifer with various chemicals, including 1,2,4-Trichlorobenzene (1,2,4-TCB). This paper is a part of a series of studies on adsorption, transport and biodegradation and fate of 1,2,4-TCB in the shallow aquifer beneath LLS. Here, adsorption of 1,2,4-TCB onto silt, fine sand and medium sand aquifer deposits collected at LLS was conducted by performing batch experiments involving four common adsorption kinetic models. The results of the analyses showed that the pseudo-second-order adsorption kinetic model provided the best fit for the equilibrium data with a coefficient of determination (R 2) greater than 0.99. Least squares analysis of Henry, Freundlich and Langmuir linearly transformed isotherm models was used to establish the best isotherm for 1,2,4-TCB adsorption onto the three aquifer materials. The Freundlich isotherm provided the best fit for experimental data with R 2 > 0.99. The results further suggested that the highest adsorption rate of 1,2,4-TCB (27.55 μg/g) was onto silt deposit, followed by fine sand (21.65 μg/g) and medium sand (14.88 μg/g). This showed that silt layer beneath the LLS was critical for retarding the downward percolation and migration of 1,2,4-TCB into the shallow aquifer systems under the landfill. The findings of the study were adopted as basis for designing the slated transport and biodegradation study of 1,2,4-TCB in aquifer system at LLS.  相似文献   

14.
Sediments from the Aquia aquifer in coastal Maryland were collected as part of a larger study of As in the Aquia groundwater flow system where As concentration are reported to reach levels as high as 1072 nmol kg−1, (i.e., ∼80 μg/L). To test whether As release is microbially mediated by reductive dissolution of Fe(III) oxides/oxyhydroxides within the aquifer sediments, the Aquia aquifer sediment samples were employed in a series of microcosm experiments. The microcosm experiments consisted of sterilized serum bottles prepared with aquifer sediments and sterilized (i.e., autoclaved), artificial groundwater using four experimental conditions and one control condition. The four experimental conditions included the following scenarios: (1) aerobic; (2) anaerobic; (3) anaerobic + acetate; and (4) anaerobic + acetate + AQDS (anthraquinone-2,6-disulfonic acid). AQDS acts as an electron shuttle. The control condition contained sterilized aquifer sediments kept under anaerobic conditions with an addition of AQDS. Over the course of the 27 day microcosm experiments, dissolved As in the unamended (aerobic and anaerobic) microcosms remained constant at around ∼28 nmol kg−1 (2 μg/L). With the addition of acetate, the amount of As released to the solution approximately doubled reaching ∼51 nmol kg−1 (3.8 μg/L). For microcosm experiments amended with acetate and AQDS, the dissolved As concentrations exceeded 75 nmol kg−1 (5.6 μg/L). The As concentrations in the acetate and acetate + AQDS amended microcosms are of similar orders of magnitude to As concentrations in groundwaters from the aquifer sediment sampling site (127-170 nmol kg−1). Arsenic concentrations in the sterilized control experiments were generally less than 15 nmol kg−1 (1.1 μg/L), which is interpreted to be the amount of As released from Aquia aquifer sediments owing to abiotic, surface exchange processes. Iron concentrations released to solution in each of the microcosm experiments were higher and more variable than the As concentrations, but generally exhibited similar trends to the As concentrations. Specifically, the acetate and acetate + AQDS amended microcosm typically exhibited the highest Fe concentrations (up to 1725 and 6566 nmol kg−1, respectively). The increase in both As and Fe in the artificial groundwater solutions in these amended microcosm experiments strongly suggests that microbes within the Aquia aquifer sediments mobilize As from the sediment substrate to the groundwaters via Fe(III) reduction.  相似文献   

15.
We have conducted acid–base potentiometric titrations and U(VI) sorption experiments using the Gram negative, facultatively anaerobic bacterium Shewanella putrefaciens. Results of reversed titration studies on live, inactive bacteria indicate that their pH-buffering properties result from the equilibrium ionization of three discrete populations of functional groups. Carboxyl (pKa=5.16±0.04), phosphoryl (pKa=7.22±0.15) and amine (pKa=10.04±0.67) groups most likely represent these three resolvable functionalities, based on their pKa values. Site densities for carboxyl, phosphoryl and amine groups on the bacterial surface were approximately 31.7 μmol sites/g bacteria (0.35±0.02 sites/nm2), 8.95 μmol/g (0.11±0.007 sites/nm2) and 38.0 μmol/g (0.42±0.008 sites/nm2), respectively, based on an estimated bacterial specific surface area of 55 m2/g. Sorption experiments showed that U(VI) can reversibly complex with the bacterial surface in the pH 2–8 interval, with maximum adsorption occurring at a pH of 5. Sorption is not strongly sensitive to ionic strength (NaCl) in the range 0.02–0.10 M. The pH and ionic strength dependence of U(VI) sorption onto S. putrefaciens is similar to that measured for metal-oxide surfaces and Gram positive bacteria, and appears to be similarly governed by competitive speciation constraints. Measured U(VI) sorption is accounted for by using two separate adsorption reactions forming the surface complexes >COO–UO2+ and >PO4H–UO2(OH)2. Using S. putrefaciens as a model organism for dissimilatory metal-reducing Gram negative anaerobes, our results extend the applicability of geochemical speciation models to include bacteria that are capable of reductively solubilizing or precipitating a wide variety of environmentally and geologically important metals and metallic species.  相似文献   

16.
已知在无氧条件下天然矿物菱铁矿能成功水解微囊藻毒素-LR(MC-LR),然而实际应用过程中难以避免水中溶解氧(O2)的存在,因此有必要深入研究不同溶氧量(DOC)条件下菱铁矿对MC-LR降解的影响。本文通过在无氧和有氧条件下菱铁矿对MC-LR的降解实验,发现在有氧条件下(溶氧量1.62～21.87 mg/L), MC-LR的降解速率均比无氧条件(k0=0.030 16 mg·L-1·h-1)高且其降解速率随O2含量增加而依次增加,当O2加入量为1.0 mL(溶氧量21.87 mg/L)时,菱铁矿对MC-LR降解速率最大(0.083 34 mg·L-1·h-1),为无氧条件下的2.76倍。通过外加腐殖酸(humic acid, HA)和自由基进行捕获实验,发现FeCO3能直接活化O2产生超氧自由基(·O~-2),以实现对MC-LR的氧化,但外加HA抑...  相似文献   

17.
高效实用的预处理方式对提高甲烷产量具有重要的作用,但单一的预处理方式往往较难获得满意效果,尤其是针对组成成分复杂的褐煤而言,对其后续产甲烷性能的影响更是存在不确定性。为探讨不同联合预处理对褐煤厌氧发酵产甲烷的影响,以1.00%HCl+5.00%H2O2(1号)、6.00%NaOH+5.00%H2O2(2号)、1.00%HCl+10.00 g木质素酶(3号)、6.00%NaOH+10.00 g木质素酶(4号)、5.00%H2O2+10.00 g木质素酶(5号)等不同联合预处理褐煤为实验组,未经预处理煤样为对照组(6号),在适宜菌种来源和环境条件下进行厌氧发酵产甲烷实验。利用比色法、气质联用法、扫描电镜等对联合预处理产甲烷过程中的糖类、挥发性脂肪酸含量及煤降解特征进行分析,以揭示其影响机理。结果表明:①不同联合预处理均可以增加褐煤发酵产甲烷量。4与5号联合预处理效果较好,累积甲烷产量分别是20.36 mL/g与8.83 mL/g,相比6号对照样分别提高了24.24倍与10.51倍。②各实验组COD(化学需氧量)去除率均高于对照组,且反应前后菌液pH波动值小。③反应初期3号实验组多糖含量最低(0.37 μg/mL),6号多糖含量最高(2.15 μg/mL),且均呈现出先下降后上升的总体趋势。④ 2、3与5号实验组还原糖含量在整个反应过程中保持较高值,且反应末期各产气组糖类含量均不为零。⑤不同联合预处理均可以促进乙酸、丁酸的降解并提高产气率。不同条件下的褐煤产甲烷量与转化率变化特征,证实了联合预处理煤增产生物甲烷的有效性,可为煤制生物气技术的产业化应用提供借鉴。   相似文献   

18.
The low-temperature thermal treatment to degrade PCDD/Fs contained in fly ash was promoted by alcohol amines in a closed system. Three types of fly ash collected separately from municipal solid waste incinerator, medical waste incinerator and hazardous waste incinerator, were compared. Experimental design was used to investigate the homologue patterns of PCDD/Fs and distribution of the toxic congeners in fly ash from incinerator after thermal treatment promoted by alcohol amines. The effect of ethanolamine (MEA) on the hydrodechlorination reaction of polychlorinated aromatics pollutants on fly ash from solid waste incinerator was carried out, and the three ashes clearly showed different degradation potentials for PCDD/F during thermal treatment. Results from the present study indicate that (1) the concentration of alkaline species and metals strongly influenced the degradation of PCDD/F; (2) after addition of 8% MEA, the toxicity equivalent (TEQ) values of PCDD/Fs in fly ash were significantly lower than those obtained without MEA. 49%–71% of PCDD/Fs in TEQ was removed from different types of ash at 250℃ with 8% MEA; (3) the destruction and dechlorination are major mechanism for PCDD/Fs degradation.  相似文献   

19.
Microcosm experiments were conducted to understand the mechanism of microbially mediated mobilization of Fe and As from high arsenic aquifer sediments. Arsenic-resistant strains isolated from aquifer sediments of a borehole specifically drilled for this study at Datong basin were used as inoculated strains, and glucose and sodium acetate as carbon sources for the experiments. In abiotic control experiments, the maximum concentrations of Fe and As were only 0.47 mg/L and 0.9 μg/L, respectively. By contrast, the maximum contents of Fe and As in anaerobic microcosm experiments were much higher (up to 1.82 mg/L and 12.91 μg/L, respectively), indicating the crucial roles of microbial activities in Fe and As mobilization. The observed difference in Fe and As release with different carbon sources may be related to the difference in growth pattern and composition of microbial communities that develop in response to the type of carbon sources.  相似文献   

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