颗粒活性炭载纳米零价铁去除水中的Cr(Ⅵ)

以Fe2+溶液为原料、NaBH4为还原剂,采用传统液相还原技术合成了颗粒活性炭(GAC)载纳米零价铁(nZVI)复合材料GAC-nZVI,用扫描电镜对GAC-nZVI进行表征,通过间歇实验考察了其对去除Cr(VI)的影响。结果表明,GAC能阻止nZVI颗粒聚集,合成的GAC-nZVI能有效去除水中的Cr(VI)。在Cr(VI)初始浓度50 mg/L、温度40℃和pH=2.0、投加GAC-nZVI 3.0 g/L的条件下反应5 min,Cr(VI)去除率为99.4%。pH=2.0?4.0时,处理后水中总铬浓度均低于1 mg/L,表明残留少量Cr(III)。随pH值和Cr(VI)浓度增加,Cr(VI)去除率降低;随反应温度和GAC-nZVI投加量增加,Cr(VI)去除率增加。准一级动力学模型可用于描述Cr(VI)的去除过程。相同条件下,GAC-nZVI去除Cr(VI)的反应速率常数达0.19797 min?1,为原颗粒活性炭反应速率常数0.0023 min?1的86倍。随pH值降低或反应温度和GAC-nZVI投加量增加,反应速率常数增加。     

好氧颗粒污泥对高浓度Cr(VI)的抗冲击负荷能力

采用5个并联运行的SBR反应柱培养好氧颗粒污泥,分别用0、1、3、5 mg/L和10 mg/L Cr(VI)对各反应柱中的颗粒污泥长期驯化65 d,此后改变各反应柱中Cr(VI)为30 mg/L进行12天冲击实验。实验结果表明,经10mg/L Cr(VI)驯化后的好氧颗粒抗冲击负荷能力最强,其COD和NH4+-N去除率略有降低,分别由90.46%和85.13%下降到88.53%和82.88%,其污泥浓度仅由4 660 mg/L变为4 460 mg/L,EPS分泌量仅增加39.99%,表面官能团未发生明显变化。总体来看,驯化浓度越高,颗粒污泥污对高浓度Cr(VI)冲击的抵御能力越好。     

胺化Fe3O4@SiO2纳米颗粒的制备及其对水溶液中Cr(VI)的去除

六价铬(Cr(VI))因其高毒性受到人们广泛关注,为提高吸附法去除Cr(VI)的效率,合成了一种新型核壳结构的聚乙烯亚胺(PEI)功能化复合纳米颗粒(Fe3O4@SiO2–NH2),用于去除水中Cr(VI).研究了磁性纳米颗粒的化学结构、形貌和磁性特性.考察了初始浓度、吸附时间、溶液pH值和无机阴离子对Cr(VI)吸附...     

废白土榴莲壳粘土生物炭的制备及对Cr(VI)的吸附

以废白土与榴莲壳为原料制备了粘土生物炭吸附剂(spent bleaching earth biochar,SBEC)、以废白土为原料制备了粘土炭基吸附剂(spent bleaching earth,SBE)吸附废水中的Cr（VI）。用比表面积分析、SEM、XRD、FTIR对吸附剂进行了表征。考察了溶液初始pH、Cr(VI)溶液浓度、吸附剂投加量、吸附时间和吸附温度分别对吸附Cr(VI)的影响。25℃下pH为3时、SBEC 投加量为0.5g/L、Cr(VI)初始浓度为100mg/L、吸附时间120min,SBEC对Cr(VI)去除效率最高为86.1%,SBE则在pH为2去除效率最高为52.5%。SBEC、SBE对Cr(VI)的吸附过程符合准二级动力学模型,SBEC吸附过程符合Freundlich模型,SBE则与Langmuir吸附等温线模型较符合;吸附行为是自发吸热过程。经过5次吸附-脱附后,SBEC对Cr(VI)的去除率达58.8%。     

废白土榴莲壳粘土生物炭的制备及对Cr(VI)的吸附

以废白土与榴莲壳为原料制备了粘土生物炭吸附剂(spent bleaching earth biochar,SBEC)、以废白土为原料制备了粘土炭基吸附剂(spent bleaching earth,SBE)吸附废水中的Cr（VI）。用比表面积分析、SEM、XRD、FTIR对吸附剂进行了表征。考察了溶液初始pH、Cr(VI)溶液浓度、吸附剂投加量、吸附时间和吸附温度分别对吸附Cr(VI)的影响。25℃下pH为3时、SBEC 投加量为0.5g/L、Cr(VI)初始浓度为100mg/L、吸附时间120min,SBEC对Cr(VI)去除效率最高为86.1%,SBE则在pH为2去除效率最高为52.5%。SBEC、SBE对Cr(VI)的吸附过程符合准二级动力学模型，SBEC吸附过程符合Freundlich模型，SBE则与Langmuir吸附等温线模型较符合；吸附行为是自发吸热过程。经过5次吸附-脱附后,SBEC对Cr(VI)的去除率达58.8%。     

高浓度FeO(OH)溶胶制备及对苯酚的吸附特性

对高浓度FeO(OH)溶胶直接用作苯酚吸附剂的制备和吸附性能做了试验研究和机理分析。试验结果表明,FeO(OH)胶溶化受温度和FeCl3胶溶剂浓度的影响,并有一稳定区间。高浓度FeO(OH)溶胶吸附水中苯酚,特别是对苯酚低浓度(苯酚质量浓度<5mg/L)时的吸附量比FeO(OH)沉淀高8～10倍,而经高温处理的FeO(OH)纳米粒子在此浓度则基本没有吸附作用。     

啤酒酵母吸附Cr（VI）的动力学及热力学研究

研究啤酒酵母对溶液中铬(VI)的吸附效果和机理,通过红外对吸附前后菌体表面特征分析,表明Cr (VI)与菌体表面基团发生配位络合反应.结果表明,在温度为35 ℃,pH=2,Cr(VI)初始浓度为20 mg/L时达到最大吸附量,最大吸附量为4.19 mg/g.酵母菌对Cr(VI)的吸附行为基本符合Langmuir方程,并且在 25,30和35 ℃条件下的理论最大吸附量qmax分别为4.472,4.533,4.702 mg/g.动力学研究表明,反应在240 min吸附基本达到平衡状态,准二级动力学模型能够更好的描述吸附过程.不同温度下的吸附热力学显示,该吸附过程为自发的吸热反应.     

天然FeS矿处理含Cr(Ⅵ)废水研究

采用天然硫化亚铁矿处理含Cr(VI)模拟废水,系统探讨了初始pH、投加量、矿粉粒径、Cr(VI)含量、DO含量等因素对Cr(VI)去除率的影响,并采用X射线光电子能谱仪对反应前后矿物表面的铁与铬元素形态进行分析,初步探讨了Cr(VI)的去除机制。结果表明,FeS矿粉对Cr(VI)的去除主要依靠吸附与表面还原作用;Cr(VI)去除率随pH的升高而降低,当pH≥4时,其去除率明显减小;随矿粉投加量增加和矿粉粒径减小,Cr(VI)去除率升高但逐渐趋于平衡;溶解氧对反应影响很小。在pH=3、投加量为2 g/L、矿粉粒径筛孔0.25 mm的优化条件下,对于初始质量浓度为25 mg/L的Cr(VI),其在1 h之内的去除率可达到近100%。研究发现一次回收矿粉的去除率仍可达80%,具有很高的再利用价值。     

201×4强碱性阴离子交换树脂吸附Cr(Ⅵ)的机理研究

实验研究了201×4强碱性阴离子交换树脂去除溶液中Cr(VI)的影响因素以及该树脂吸附Cr(VI)的动力学和热力学特性。结果表明,吸附平衡过程符合Frendilch等温吸附方程,吸附动力学数据表明化学反应过程为控速步骤,树脂对Cr(VI)的吸附量随pH的降低而增加,随着温度的升高而增加,表观吸附活化能Ea(10mg/L)=30.851kJ-mol-1,Ea(400mg/L)=16.074kJ·mol-1。当pH=2.0时,反应温度为323K,吸附量存在最大值为13.74mg/g。树脂的再生能力比较强,经过3次再生,树脂的平衡吸附量下降8.3%。     

膨胀石墨负载氧化锌吸附废水中的Cr(Ⅵ)

采用化学氧化法将氧化锌负载在膨胀石墨表面,制备了膨胀石墨氧化锌复合材料。以废水中的Cr(VI)为去除对象,采用静态吸附法,研究了Cr(VI)在膨胀石墨氧化锌表面的吸附行为,探讨了Cr(VI)初始浓度、溶液pH等因素对吸附效果的影响;并从吸附热力学和动力学角度讨论了吸附机理。结果表明,吸附量可达99.46 mg/g,吸附焓变为11.64 kJ/mol;拟二级动力学模型和Langmuir等温方程式能较好的拟合吸附过程,证明Cr(VI)主要以单分子层形式被吸附于吸附剂表面且整个吸附过程放热反应占主导地位。     

改性镍铁渣吸附剂对Cr(VI)吸附性能的影响及机理分析

以镍铁渣为原料,加入硝酸和表面活性剂对其矿物相改性,制备改性镍铁渣吸附剂,考察表面活性剂种类、十六烷基三甲基溴化铵(CTAB)掺量、吸附剂掺量、溶液初始pH值、Cr(VI)浓度对Cr(VI)吸附效果的影响。结果表明:镍铁渣经改性后可制得结构疏松、比表面积高达180.6 m²/g的无定形SiO₂;改性镍铁渣对Cr(VI)的吸附率在10 min内可达到90%,吸附等温线符合Langmuir模型,最大理论吸附容量为42.55 mg/g,吸附动力学符合拟二级动力学模型。改性镍铁渣吸附剂对Cr(VI)的吸附机理主要是物理吸附和氧化还原,即吸附剂表面范德华力将HCrO ^-₄吸附至吸附剂表面,CTAB提供的电子对将Cr(VI)还原为Cr(III)。对镍铁渣改性获得的高比表面积无定形SiO₂不仅可以有效吸附净化Cr(VI),同时可以实现镍铁渣资源化利用,达到以废治污的目的,具有良好的环境效应和经济效益。     

单宁基酚胺型螯合树脂的制备及对Cr(VI)的吸附

杨梅单宁先与氯化亚砜反应制得氯代单宁,再与聚乙烯亚胺交联合成单宁基酚胺型螯合树脂。通过FTIR、SEM、EDS和XPS对单宁基酚胺型螯合树脂的结构进行表征,并考察了螯合树脂对Cr(VI)的吸附性能。在单宁的分子结构侧链引入氨基,能有效改善单宁基螯合树脂对Cr(VI)的吸附性能,螯合树脂对Cr(VI)的吸附主要为还原吸附,铬主要以Cr(III)的形式吸附到树脂上;在温度为318 K、pH为2.0、Cr(VI)初始质量浓度为500 mg/L时,单宁基酚胺型螯合树脂对Cr(VI)的最大吸附量达到364.46 mg/g;当Cr(VI)初始质量浓度低于20 mg/L时,树脂对铬的吸附率达到95%以上;单宁基酚胺型螯合树脂对Cr(VI)的吸附过程符合Langmuir等温吸附模型和准二级吸附动力学方程。该树脂在含铬废水处理方面具有潜在的应用前景。     

Boron-Doped Diamond Electrode Performance in Cr(VI) Reduction Using Synthetic and Plating Wastewater

The goal of this work was to evaluate the effectiveness of iron and boron-doped-diamond (BDD) as cathodic electrodes on the reduction of Cr(VI) in synthetic and wastewater samples. The pH and electrolyte composition were varied, and the effect on the Cr(VI) reduction rate was measured. The optimized conditions from the synthetic water Cr(VI) reduction experimental data, were tasted on electroplating wastewater. The results indicated that both a pH of 2 and the use of NaCl as an electrolyte significantly increase the Cr(VI) reduction rate for all synthetic systems, especially the iron-BDD system. The Cr(VI) reduction rate in Fe-BDD systems was also affected by nitrate and sulfate ions. In the case of electroplating wastewater, Cr(VI) reduction by BDD cathodes was faster than with iron cathodes, achieving a complete reduction of 180 mg Cr(VI)/L in 25 min, with 40% less sludge produced. The elemental composition of sludge was analyzed using SEM/EDS and X-ray spectroscopy to confirm that iron and chromium precipitated out of the solution. The sludge had a chemical composition of (31.9%) Fe₂O₃, (29.6%) FeOOH, (21%) FeO, and (17.4%) FeSO₄. Therefore, BDD as an electrode material effectively reduces Cr(VI) in electroplating wastewater, and can be effectively scaled up to industrial applications.     

交联薯渣黄原酸酯对废水中Cr(Ⅵ)的吸附研究

交联薯渣黄原酸酯(CCX)废水中Cr(Ⅵ)离子的吸附,探讨了pH值、温度、吸附时间、CCX含硫量、Cr(Ⅵ)初始浓度等因素对其吸附效果的影响。结果表明,当CCX加入量为理论加入量的3.0倍时,pH为2.5,在45℃下搅拌反应50 min,对Cr(Ⅵ)的吸附容量为37.76 mg/g,去除率达到99.69%,处理后的废水中Cr(Ⅵ)浓度为0.15 mg/L,低于国标排放标准(0.5 mg/L)。并通过红外光谱和热重分析,对CCX吸附Cr(Ⅵ)的机理进行了探讨。     

Removal of Chromium(VI) and Chromium(III) from Aqueous Solution by Grainless Stalk of Corn

Abstract

Grainless stalk of corn (GLSC) was tested for removal of Cr(VI) and Cr(III) from aqueous solution at different pH, contact time, temperature, and chromium/adsorbent ratio. The results show that the optimum pH for removal of Cr(VI) is 0.84, while the optimum pH for removal of Cr(III) is 4.6. The adsorption processes of both Cr(VI) and Cr(III) onto GLSC were found to follow first-order kinetics. Values of k _ads of 0.037 and 0.018 min^?1 were obtained for Cr(VI) and Cr(III), respectively. The adsorption capacity of GLSC was calculated from the Langmuir isotherm as 7.1 mg g^?1 at pH 0.84 for Cr(VI), and as 7.3 mg g^?1 at pH 4.6 for Cr(III), at 20°C. At the optimum pH for Cr(VI) removal, Cr(VI) reduces to Cr(III). EPR spectroscopy shows the presence of Cr(V) + Cr(III)-bound-GLSC at short contact times and adsorbed Cr(III) as the final oxidation state of Cr(VI)-treated GLSC. The results indicate that, at pH ≈ 1, GLSC can completely remove Cr(VI) from aqueous solution through an adsorption-coupled reduction mechanism to yield adsorbed Cr(III) and the less toxic aqueous Cr(III), which can be further removed at pH 4.6.     

Sonochemical assisted preparation of ZnS–ZnO/MCM-41 based on blast furnace slag and electric arc furnace dust for Cr (VI) photoreduction

Iron/steel making industry is a weed that produces large quantities of slag and dust. The objective of the present study was to develop a procedure for obtaining and characterizing photocatalysts derived from this waste for chromium remediation. The MCM-41 was synthesized via sodium silicate (Na₂SiO₃) derived from Blast Furnace Slag (BFS), and ZnO and ZnS were synthesized based on zinc extracted from Electric Arc Furnace Dust (EAFD). Subsequently, ZnO/ZnS were sono-chemically loaded on the MCM-41 and were tested for the Cr (IV) photoreduction. The resultant ZnO, ZnS, MCM-41, and composites were characterized by X-ray diffraction (XRD), Energy-dispersive X-ray spectroscopy (EDX), N2adsorption–desorption isotherms, Fourier-transform infrared (FT-IR) spectrometry, Dynamic Light scattering, and Transmission electron microscopy (TEM), and X-ray photoelectron spectroscopy (XPS). A regular hexagonal structure of typical mesoporous MCM-41 had been proven by small-angle XRD, HRTEM, and N2 adsorption–desorption. The photoreduction activity of ZnS–ZnO/MCM-41 nanocomposite has obvious efficiency compared to ZnO and ZnO/MCM-41, achieving a 94% photoreduction of Cr (VI) in 180 min under UV irradiation. The slight activity loss after 4 cycles (84.7%) reveals the good photoreduction properties of catalysts. Based on these results, ZnS–ZnO/MCM-41 composite material seems to be high efficiency, green, stable, environment, and economical alternative to be used as a photocatalyst for the reduction of Cr (VI).     

Comparing the efficacy of a novel waste-based adsorbent with PAC for the simultaneous removal of chromium (VI) and cyanide from electroplating wastewater

The potential of powdered pistachio hull (PHP) for the co-adsorption of Cr(VI) and cyanide from electroplating wastewater was compared to that of powdered activated carbon (PAC). The results of dynamic adsorption experiments indicated that the complete and simultaneous removal of Cr(VI) and cyanide from wastewater was achieved with 2 g/L of PHP after 60 min of contact. Alternatively, with PAC, 69.2 and 77.8% of Cr(VI) and cyanide, respectively, were removed under the same conditions. Adsorption of Cr(VI) and cyanide by PHP and PAC followed pseudo-second order kinetics, and the equilibrium adsorption data best fit the Langmuir isotherm. The maximum capacity of PHP for the co-adsorption of Cr(VI) and cyanide was 117.6 and 151.5 mg/g, respectively, and the maximum capacity of PAC for the adsorption of Cr(VI) and cyanide was 47.6 and 39.4 mg/g, respectively. It was found that which intraparticle diffusion controlled the adsorption of Cr(VI) and cyanide onto PHP and PAC under the selected conditions. Overall, PHP efficiently adsorbed Cr(VI) and cyanide from industrial effluents; thus, PHP is an affordable and cost-effective system for the treatment of wastewater.     

Metal ion adsorption behavior of lignocellulosic fiber–ethylene vinyl acetate composites

This study describes the applicability of lignocellulosic fiber dispersed in ethylene vinyl acetate (EVA) to adsorb Pb(II), Cr(III), and Cr(VI) ions in aqueous solutions. Water absorption studies revealed that metal‐ion uptake does not only take place on the surface of the adsorbent but ions can also diffuse into the composite. The adsorption of the metal ions under different experimental conditions was studied. Solute concentration, pH, and contact time were used to assess the adsorption capacity and efficiency. The amount of metal adsorbed increased to 7 mg/g with an increase in solute concentration but compromising the efficiency. Adsorption equilibrium was reached after 3 h, when the maximum lead adsorption was above 80%. The optimum pH for the adsorption of Pb(II) and Cr(III) was 6.5, and pH 2.5 was used for the adsorption of Cr(VI). Competitive adsorption revealed the order of adsorption to be: Pb(II) > Cr(VI) > Cr(III). POLYM. ENG. SCI., 2011. © 2011 Society of Plastics Engineers     

Red mud (aluminum industrial waste): An eco-friendly treatment of electroplating effluent

In this work, aluminum industrial waste, red mud (RM), was activated to verify its potential in the management of electroplating wastewater containing hexavalent chromium (Cr(VI)). A comparison between the adsorption capabilities of RM and activated red mud (ARM) towards Cr(VI) from aqueous solutions was made. The effects of several parameters were evaluated. The adsorbents were characterized by field emission scanning electron microscopy (FESEM), Fourier transmission infrared spectroscopy (FTIR), x-ray diffraction (XRD), zeta potential, and thermogravimetric analysis (TGA). The particle size was observed as 23.59 nm. The ARM demonstrated an acceptable adsorption capacity of 25.641 mg/g at a pH of 2, adsorbent dosage of 2 g/L, initial Cr(VI) concentration of 100 mg/L, at 25°C. The experimental data is in good agreement with Langmuir adsorption isotherm. The kinetic study was performed to verify that the adsorption follows pseudo-second-order kinetics. In addition, the ARM showed decent recyclability for adsorbing Cr(VI) as even after three adsorption cycles, and the adsorption capacity was reduced by ~30%. The results recommend ARM to be an efficient and cost-effective adsorbent for Cr(VI) removal from industrial wastewater.     

Equilibrium kinetic and thermodynamic studies of Cr(VI) adsorption onto a novel adsorbent of <Emphasis Type="Italic">Eucalyptus camaldulensis</Emphasis> waste: Batch and column reactors

Cr(VI) adsorption onto Eucalyptus camaldulensis sawdust (ECS) waste was investigated in batch and column reactors. Various parameters, including the adsorbent dose, pH, initial concentration, particle size, contact time and temperature were optimized. The maximum adsorption capacity (35.58mg g^-1, 71.16%) was achieved at pH 2.0. Data fitted well to Freundlich and Halsey’s models (R²=0.992), indicating the multilayer adsorption of Cr(VI). It obeys the pseudo-second order kinetics. Endothermic and non-spontaneous nature of Cr(VI) adsorption was observed with positive values of changes in enthalpy (9.83 kJ mol^-1), and Gibbs-free energy (1.52, 1.38, 1.24, 1.10 and 0.97 kJ mol^-1), respectively. In this column study, the breakthrough curve time increased from 670 to 1,270min by increasing the bed height from 5 to 15 cm, respectively. Column data was found well fitted to bed depth service time model. Adsorption capacity at 60% breakthrough was 2,443.636mg L^-1. The study indicates that ECS waste can be a promising adsorbent for Cr(VI) remediation from industrial effluents.