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1.
A treatment unit packed by granular adsorbent of Fe-Mn binary oxide incorporated into diatomite (FMBO(1:1)-diatomite) was studied to remove arsenic from anaerobic groundwater without any pre-treatment or post-treatment. The raw anaerobic groundwater containing 35-45 μg/L of arsenic was collected from suburb of Beijing. Arsenic(III) constituted roughly 60%-80% of the total arsenic content. Approximately 7,000 bed volumes (ratio of efluent volume to adsorbent volume) treated water with arsenic concentration b...  相似文献   

2.
Fe–Mn binary oxide(FMBO) possesses high efficiency for As(Ⅲ) abatement based on the good adsorption affinity of iron oxide and the oxidizing capacity of Mn(Ⅳ), and the composition and structure of FMBO play important roles in this process.To compare the removal performance and determine the optimum formula for FMBO, magnetic graphene oxide(MRGO)–FMBO and MRGO–MnO_2 were synthesized with MRGO as a carrier to improve the dispersity of the adsorbents in aquifers and achieve magnetic recycling.Results indicated that MRGO–FMBO had higher As(Ⅲ) removal than that of MRGO–MnO_2,although the ratios of Fe and Mn were similar, because the binary oxide of Fe and Mn facilitated electron transfer from Mn(Ⅳ) to As(Ⅲ), while the separation of Mn and Fe on MRGO–MnO_2 restricted the process.The optimal stoichiometry x for MRGO–FMBO(Mn_xFe_(3-x)O_4) was 0.46, and an extraordinary adsorption capacity of 24.38 mg/g for As(Ⅲ) was achieved.MRGO–FMBO showed stable dispersive properties in aquifers, and exhibited excellent practicability and reusability, with a saturation magnetization of 7.6 emu/g and high conservation of magnetic properties after 5 cycles of regeneration and reuse.In addition, the presence of coexisting ions would not restrict the practical application of MRGO–FMBO in groundwater remediation.The redox reactions of As(Ⅲ) and Mn(Ⅳ) on MRGO–FMBO were also described.The deprotonated aqueous As(Ⅲ) on the surface of MRGO–FMBO transferred electrons to Mn(Ⅳ), and the formed As(Ⅴ) oxyanions were bound to ferric oxide as inner-sphere complexes by coordinating their "–OH" groups with Mn(Ⅳ)oxides at the surface of MRGO–FMBO.This work could provide new insights into highperformance removal of As(Ⅲ) in aquifers.  相似文献   

3.
Fe–Mn binary oxide (FMBO) possesses high efficiency for As(III) abatement based on the good adsorption affinity of iron oxide and the oxidizing capacity of Mn(IV), and the composition and structure of FMBO play important roles in this process. To compare the removal performance and determine the optimum formula for FMBO, magnetic graphene oxide (MRGO)–FMBO and MRGO–MnO2 were synthesized with MRGO as a carrier to improve the dispersity of the adsorbents in aquifers and achieve magnetic recycling. Results indicated that MRGO–FMBO had higher As(III) removal than that of MRGO–MnO2, although the ratios of Fe and Mn were similar, because the binary oxide of Fe and Mn facilitated electron transfer from Mn(IV) to As(III), while the separation of Mn and Fe on MRGO–MnO2 restricted the process. The optimal stoichiometry x for MRGO–FMBO (MnxFe3-xO4) was 0.46, and an extraordinary adsorption capacity of 24.38 mg/g for As(III) was achieved. MRGO–FMBO showed stable dispersive properties in aquifers, and exhibited excellent practicability and reusability, with a saturation magnetization of 7.6 emu/g and high conservation of magnetic properties after 5 cycles of regeneration and reuse. In addition, the presence of coexisting ions would not restrict the practical application of MRGO–FMBO in groundwater remediation. The redox reactions of As(III) and Mn(IV) on MRGO–FMBO were also described. The deprotonated aqueous As(III) on the surface of MRGO–FMBO transferred electrons to Mn(IV), and the formed As(V) oxyanions were bound to ferric oxide as inner-sphere complexes by coordinating their “–OH” groups with Mn(IV) oxides at the surface of MRGO–FMBO. This work could provide new insights into high-performance removal of As(III) in aquifers.  相似文献   

4.
To obtain a cost-effective adsorbent for the removal of arsenic in water,a novel nanostructured Fe–Co based metal organic framework(MOF-74)adsorbent was successfully prepared via a simple solvothermal method.The adsorption experiments showed that the optimal molar ratio of Fe/Co in the adsorbent was 2:1.The Fe_2Co_1MOF-74 was characterized by various techniques and the results showed that the nanoparticle diameter ranged from60 to 80 nm and the specific surface area was 147.82 m~2/g.The isotherm and kinetic parameters of arsenic removal on Fe_2Co_1MOF-74 were well-fitted by the Langmuir and pseudo-second-order models.The maximum adsorption capacities toward As(III)and As(V)were 266.52 and 292.29 mg/g,respectively.The presence of sulfate,carbonate and humic acid had no obvious effect on arsenic adsorption.However,coexisting phosphate significantly hindered the removal of arsenic,especially at high concentrations(10 mmol/L).Electrostatic interaction and hydroxyl and metal–oxygen groups played important roles in the adsorption of arsenic.Furthermore,the prepared adsorbent had stable adsorption ability after regeneration and when used in a real-water matrix.The excellent adsorption performance of Fe_2Co_1MOF-74 material makes it a potentially promising adsorbent for the removal of arsenic.  相似文献   

5.
Humic acid-immobilized amine modified polyacrylamide/bentonite composite (HA-Am-PAA-B) was prepared and used as an adsorbent for the adsorption of cationic dyes (Malachite Green (MG), Methylene Blue (MB) and Crystal Violet (CV)) from aqueous solutions. The polyacrylamide/bentonite composite (PAA-B) was prepared by intercalative polymerization of acrylamide with Nabentonite in the presence of N,N0-methylenebisacrylamide as a crosslinking agent and hexamethylenediammine as propagater. PAA-B was subsequently treated with ethylenediammine to increase its loading capacity for HA. The surface characterizations of the adsorbent were investigated. The adsorbent behaved like a cation exchanger and more than 99.0% removal of dyes was detected at pH range 6.0–8.0. The capacity of HA-Am-PAA-B was found to decrease in the following order: MG > MB > CV. The kinetic and isotherm data were interpreted by pseudo-second order rate equation and Freundlich isotherm model, respectively. Experiments were carried out using binary solute systems to assess the competitive adsorption phenomenon. The experimental isotherm data for each binary solute combination of MG, MB and CV were analyzed using Sheindrof-Rebhun-Sheintuch (SRS) (multicomponent Freundlich type) equation.  相似文献   

6.
Because of its significant toxicological effects on the environment and human health,arsenic(As) is a major global issue.In this study,an Fe-based metal-organic framework(MOF)(Materials of Institut Lavoisier:MIL-100(Fe)) which was impregnated with reduced graphene oxide(rGO) by using a simple hydrothermal method and coated with birnessitetype manganese oxide(δ-MnO_2) using the one-pot reaction process(MIL-100(Fe)/rGO/δ-MnO_2 nanocomposites) was synthesized and applied successfully in As removal.The removal efficiency was rapid,the equilibrium was achieved in 40 min and 120 min for As(Ⅲ) and As(Ⅴ),respectively,at a level of 5 mg/L.The maximum adsorption capacities of As(Ⅲ) and As(Ⅴ) at pH 2 were 192.67 mg/g and 162.07 mg/g,respectively.The adsorbent revealed high stability in pH range 2-9 and saturated adsorbent can be fully regenerated at least five runs.The adsorption process can be described by the pseudo-second-order kinetic model and Langmuir monolayer adsorption.The adsorption mechanisms consisted of electrostatic interaction,oxidation and inner sphere surface complexation.  相似文献   

7.
The adsorption of Methyl Violet (MV) cationic dye from aqueous solution was carried out by using crosslinked poly (acrylic acid-co-acrylamide)/attapulgite (Poly(AA-co-AM)/ATP) composite as adsorbent. The factors influencing adsorption capacity of the composite such as pH, concentration of the dye, temperature, contact time, adsorbent dosage, ionic strength and surfactant were systematically investigated. The equilibrium data fitted very well to the Langmuir isotherm and the maximum adsorption capacity reached 1194 mg/g at 30°C. The thermodynamic parameters including G0, △H0 and △S 0 for the adsorption processes of MV on the composite were also calculated, and the negative △H0 and △G0 confirmed that the adsorption process was exothermic and spontaneous. The kinetic studies showed that the adsorption process was consistent with the pseudo second-order kinetic model and the desorption studies revealed that the regeneration of the composite adsorbent can be easily achieved.  相似文献   

8.
Pb adsorption capacities of Fe oxide, Mn oxide and organic materials in natural surface coatings (biofilms and associated minerals) collected in three lakes, two ponds and a river in Jilin Province, China and Cayuga Lake in US were studied. A novel extraction technique was employed to remove one or more component(s) from the surface coatings. Pb adsorption to surface coatings before and after extraction was performed to determine the adsorptive properties of the extracted component(s). The statistical analysis of observed Pb adsorption was carried out using nonlinear least squares fitting (NLSF) to estimate the Pb adsorption capacity of each component of surface coatings. For each body of water, the estimated Pb adsorption capacity of Mn oxide( mol Pb/mol Mn) was significantly higher than that of Fe oxide( mol Pb/ mol Fe). The value of estimated adsorption capacities of organic materials with the unit mol Pb per kg COD was similar to or less than that of Fe oxides with the unit mol Pb per mol Fe. Comparison of components of surface coatings in different waters showed that the estimated Pb adsorption capacities of components in surface coatings developed in different natural waters were different,especially for Mn oxides.  相似文献   

9.
The ubiquitous arsenic in groundwater poses a great risk to human health due to its environmental toxicity and carcinogenicity. In the present work, a new adsorbent, δ-MnO2 modified activated carbon, was prepared, and its performance for the uptake of arsenate and arsenite species from aqueous solutions was investigated by batch experiments. Various techniques, including FESEM-EDX, p-XRD, XPS and BET surface area analysis, were employed to characterize the properties of the adsorbent and the arsenic adsorption mechanisms. The results showed that δ-MnO2 covered on the surface and padded in the pores of the activated carbon. Adsorption kinetic studies revealed that approximately 90.1% and 76.8% of As(III) and As(V), respectively, were removed by the adsorbent in the first 9 hr, and adsorption achieved equilibrium within 48 hr. The maximum adsorption capacities of As(V) and As(III) at pH 4.0 calculated from Langmuir adsorption isotherms were 13.30 and 12.56 mg/g, respectively. The effect of pH on As(V) and As(III) removal was similar, and the removal efficiency significantly reduced with the increase of solution pH. Arsenite oxidation and adsorption kinetics showed that the As(V) concentration in solution due to As(III) oxidation and reductive dissolution of MnO2 increased rapidly during the first 12 min, and then gradually decreased. Based on the XPS analysis, nearly 93.3% of As(III) had been oxidized to As(V) on the adsorbent surface and around 38.9% of Mn(IV) had been reduced to Mn(II) after As(III) adsorption. This approach provides a possible method for the purification of arsenic-contaminated groundwater.  相似文献   

10.
Graphene oxide is a very high capacity adsorbent due to its functional groups and π?π interactions with other compounds. Adsorption capacity of graphene oxide, however, can be further enhanced by having synergistic effects through the use of mixed-matrix composite. In this study, silica-decorated graphene oxide (SGO) was used as a high-efficiency adsorbent to remove Congo red (CR) and Cadmium (II) from aqueous solutions. The effects of solution initial concentration (20 to 120 mg/l), solution pH (pH 2 to 7), adsorption duration (0 to 140 min) and temperature (298 to 323 K) were measured in order to optimize the adsorption conditions using the SGO adsorbent. Morphological analysis indicated that the silica nanoparticles could be dispersed uniformly on the graphene oxide surfaces. The maximum capacities of adsorbent for effective removal of Cd (II) and CR were 43.45 and 333.33 mg/g based on Freundlich and Langmuir isotherms, respectively. Langmuir and Freundlich isotherms displayed the highest values of Qmax for CR and Cd (II) adsorption in this study, which indicated monolayer adsorption of CR and multilayer adsorption of Cd (II) onto the SGO, respectively. Thermodynamic study showed that the enthalpy (ΔH) and Gibbs free energy(ΔG) values of the adsorption process for both pollutants were negative, suggesting that the process was spontaneous and exothermic in nature. This study showed active sites of SGO (π-π, hydroxyl, carboxyl, ketone, silane-based functional groups) contributed to an enormous enhancement in simultaneous removal of CR and Cd (II) from an aqueous solution, Therefore, SGO can be considered as a promising adsorbent for future water pollution control and removal of hazardous materials from aqueous solutions.  相似文献   

11.
铁锰复合氧化物吸附去除五价锑性能研究   总被引:11,自引:2,他引:9       下载免费PDF全文
对比研究了铁锰复合氧化物(FMBO)、羟基氧化铁(FeOOH)和二氧化锰(MnO2)吸附去除五价锑(Sb(V))的性能.结果表明FMBO对Sb(V)具有很好的吸附性能,在pH=5.0的条件下,最大吸附容量达到1.05 mmol·g-1,略高于FeOOH (0.82 mmol·g-1)及远高于MnO2 (0.43 mmol·g-1);采用Freundlich模型可以很好地描述Sb(V)在FMBO的吸附行为(R2 = 0.98).就吸附动力学而言,假二级动力学可很好地描述Sb(V)在FMBO (R2 = 0.93)和MnO2表面的吸附过程(R2 = 0.96),而Sb(V)在FeOOH表面的吸附过程可用Elovich模型拟合 (R2 = 0.94).Sb(V)的吸附量随着pH值的升高而降低;磷酸盐显著抑制了Sb(V)的吸附,而硫酸盐和碳酸盐影响不大.提高体系离子强度可促进Sb(V)在FMBO表面的吸附,推断Sb(V)在FMBO表面形成内层络合物后被吸附去除.  相似文献   

12.
载铁(β-FeOOH)球形棉纤维素吸附剂去除地下水As(Ⅴ)的研究   总被引:2,自引:2,他引:2  
制备了一种载铁(β- FeOOH)球形棉纤维素吸附剂,球珠孔隙度大,强度好,活性成分铁的载入量可高达360mg/mL ,(质量分数达50%) ,活性好.研究表明,当铁含量为220mg/mL时,该吸附剂对As(V)的最大吸附量为15.6mg/mL(33.2mg/g) ,Langmuir和Freundlich方程能很好地描述吸附等温线.吸附速度较快,10h可达到吸附平衡,吸附动力学符合Lagergren二级方程.SiO32- ,SO42-,Cl-干扰离子均不影响砷的去除.柱吸附实验表明,空床停留时间为5.9min ,进水As(V)浓度为500μg/L时,As(V)的穿透体积为5000BV .吸附剂可以用1.5mol·L-1 NaOH再生,洗脱和再生效率可达90%以上.活性成分β-FeOOH形态稳定,柱操作和再生时铁无溶出.吸附剂制备方法简单,新颖,对地下水和饮用水砷去除具有较好的应用前景.  相似文献   

13.
由于矿产资源的共生、伴生现象及历史上采选冶技术的相对落后,我国矿区附近的重金属污染场地多存在复合污染的情况,而稳定化技术是解决该问题的有效措施.本文通过室内模拟培养实验和静态吸附试验,研究了人工合成的铁锰双金属材料(FMBO)对矿区复合污染土壤中As、Pb、Cd等重金属的稳定化作用和机制.毒性浸出实验结果表明,在3种不同的As和重金属复合污染土壤中,FMBO材料能够对As和Pb等重金属起到较好的稳定化作用,在5%的最大添加量下,FMBO对As、Pb的稳定化效率分别能够达到95.2%~100%和95.5%~97.5%,同时不会引起Cd、Zn和Cu等重金属的活化.由连续提取实验结果可知,FMBO能够使土壤中As和Pb由酸可提取态向可还原态转变,稳定性增强.微观特征分析结果表明,FMBO材料对As的稳定化主要通过表面羟基(—OH)基团的吸附作用,而对Pb、Cd等金属离子则通过吸附、沉淀等多种方式起作用.总体看来,FMBO材料适用于As、Pb等重金属复合污染土壤的治理.  相似文献   

14.
费杨  阎秀兰  李永华 《环境科学》2018,39(3):1430-1437
pH是影响土壤As和重金属赋存形态及稳定化过程的重要因素,本文以人工合成的铁锰双金属材料(FMBO)为研究对象,研究了其在不同pH条件下对3种As和重金属复合污染土壤的稳定化作用,同时探讨了材料添加对土壤pH和酸碱缓冲性的影响.结果表明,As、Pb元素分别在土壤pH 3~9的中性偏酸性条件、pH 5~10的中性偏碱性条件下较为稳定,Cd、Zn、Cu在pH为7~11的碱性条件下浸出浓度较低.在碱性条件下,FMBO材料自身稳定性及稳定化作用均优于酸性条件,在As和重金属稳定的最适pH范围内,随着材料添加量增加,稳定化效率逐渐升高,其对As、Pb、Cd、Zn、Cu的稳定化效率最高分别能达到92.7%、100%、97.0%、88.7%、82.7%.添加FMBO材料可使土壤pH值升高,并能够提高土壤的酸缓冲能力,对As和重金属的长期稳定性有促进作用,而对土壤碱缓冲作用影响较小.从浸出元素的相关关系可以看出,Fe元素对土壤中As的稳定性有重要作用,Pb、Cd、Zn、Cu的稳定性受土壤pH影响较大.  相似文献   

15.
采用浸渍焙烧法制备了活性炭负载氧化锰的除镉(Cd(Ⅱ))吸附剂,通过L_9(3~4)正交试验确定最优制备条件如下:浸渍时间7 h,KMnO_4质量分数2.7%,焙烧温度470℃,焙烧时间2.5 h。通过BET、SEM、FTIR、XRD对改性活性炭(MOAC)进行表征,研究了pH值、吸附时间、初始浓度、吸附温度等对Cd(Ⅱ)吸附效果的影响。结果表明:MOAC表面烃基含氧官能团增多,氧化锰以MnO_2的形式负载到其表面;当MOAC的投加量为0.5 g/L,Cd(Ⅱ)的初始浓度为50 mg/L,溶液pH值为6.0,温度为298 K,吸附时间为12 h时,MOAC对Cd(Ⅱ)的吸附量高达84.15 mg/g,吸附过程符合准二级动力学方程和Langmuir等温吸附方程,热力学参数表明该吸附过程为放热、自发的过程。  相似文献   

16.
三种氧化铁吸附水环境中砷的试验研究   总被引:6,自引:1,他引:5  
采用两种人工合成的氧化铁(针铁矿、水铁矿)和赤铁矿作为吸附剂,对含砷(三价砷及三价五价砷混合液)水进行了吸附试验。结果表明,在初始浓度为1200μg/L的As(Ⅲ)溶液中,水铁矿的吸附效果最好,针铁矿和赤铁矿吸附效果较差;在初始pH为7,As(Ⅲ)和As(Ⅴ)摩尔比为1:1的混合液中时,三种铁矿对总砷的吸附效果均随着As/Fe摩尔比的增大而减小;在A(sⅢ)和As(Ⅴ)摩尔比为1:1的混合液中,吸附总砷效果最好的是针铁矿,水铁矿次之,赤铁矿的吸附效果最差;A(sⅤ)的存在对除砷效果有一定的影响,三价砷和五价砷共存时,三种铁矿对其吸附具有一定的选择性。  相似文献   

17.
水固液微界面氧化还原反应过程与污染物控制研究   总被引:1,自引:1,他引:0  
本文介绍了3个反应体系,包括铁锰复合氧化物氧化吸附除砷体系、铁氧化物包覆零价铁光芬顿催化和负载型多价态锰氧化物臭氧催化体系,通过固液微界面不同的氧化还原反应,实现了对水中砷和难降解有机污染物的高效去除.重点介绍了不同氧化还原反应对污染物转移转化的作用机制,说明了水体中固液微界面氧化还原反应,对污染物的转移转化起着重要作用.  相似文献   

18.
Fe-Mn binary oxide incorporated into porous diatomite (FMBO-diatomite) was prepared in situ and regenerated in a fixed-bed column for arsenite [As(III)] and arsenate [As(V)] removal. Four consecutive adsorption cycles were operated under the following conditions: Initial arsenic concentration of 0.1 mg·L−1, empty bed contact time of 5 min, and pH 7.0. About 3000, 3300, 3800, and 4500 bed volumes of eligible effluent (arsenic concentration ⩽ 0.01 mg·L−1) were obtained in four As (III) adsorption cycles; while about 2000, 2300, 2500, and 3100 bed volumes of eligible effluent were obtained in four As(V) adsorption cycles. The dissection results of FMBO-diatomite fixed-bed exhibited that small amounts of manganese and iron were transferred from the top of the fixed-bed to the bottom of the fixed-bed during As(III) removal process. Compared to the extremely low concentration of iron (<0.01 mg·L−1), the fluctuation concentration of Mn2+ in effluent of the As(III) removal column was in a range of 0.01–0.08 mg·L−1. The release of manganese suggested that manganese oxides played an important role in As(III) oxidation. Determined with the US EPA toxicity characteristic leaching procedure (TCLP), the leaching risk of As(III) on exhausted FMBO-diatomite was lower than that of As(V).  相似文献   

19.
磁性吸附材料CuFe2O4吸附砷的性能   总被引:6,自引:1,他引:6  
根据Cu(Ⅱ)和Fe(Ⅲ)都对砷有较强的亲和性,制备了同时含有Cu(Ⅱ)和Fe(Ⅲ)的、可用磁分离方法进行分离回收的磁性吸附材料CuFe2O4,并对其进行了表征及吸附砷的性能研究.结果表明,该吸附剂对砷的吸附能力与溶液pH有关,在弱酸性及中性条件下,吸附砷的能力最强,而对As(V)的吸附能力比对As(Ⅲ)更强些,在平衡浓度为10μg/L时,其吸附容量可达10mg/g左右,可以很容易地将水中浓度为1~20mg/L的As(V)降到10μg/L以下.实验考察了几种无机阴离子对吸附砷的影响,表明较高浓度(砷浓度的20倍)的硫酸盐对As(Ⅲ)和As(V)的吸附均有一定影响,盐酸盐及磷酸盐则影响不明显;负载的As(V)可较容易地用0.1mol/L NaOH洗脱下来,使吸附剂再生,而As(Ⅲ)则难以洗脱,这与2种价态砷的吸附机理不同有关.  相似文献   

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