• 文献检索
  • 文档翻译
  • 深度研究
  • 学术资讯
  • Suppr Zotero 插件Zotero 插件
  • 邀请有礼
  • 套餐&价格
  • 历史记录
应用&插件
Suppr Zotero 插件Zotero 插件浏览器插件Mac 客户端Windows 客户端微信小程序
定价
高级版会员购买积分包购买API积分包
服务
文献检索文档翻译深度研究API 文档MCP 服务
关于我们
关于 Suppr公司介绍联系我们用户协议隐私条款
关注我们

Suppr 超能文献

核心技术专利:CN118964589B侵权必究
粤ICP备2023148730 号-1Suppr @ 2026

文献检索

告别复杂PubMed语法,用中文像聊天一样搜索,搜遍4000万医学文献。AI智能推荐,让科研检索更轻松。

立即免费搜索

文件翻译

保留排版,准确专业,支持PDF/Word/PPT等文件格式,支持 12+语言互译。

免费翻译文档

深度研究

AI帮你快速写综述,25分钟生成高质量综述,智能提取关键信息,辅助科研写作。

立即免费体验

在硫酸盐水溶液介质中砷酸盐与铁(III)的共沉淀:时间、作为碱的石灰和共存离子对砷保留的影响。

Coprecipitation of arsenate with iron(III) in aqueous sulfate media: effect of time, lime as base and co-ions on arsenic retention.

作者信息

Jia Yongfeng, Demopoulos George P

机构信息

Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China.

出版信息

Water Res. 2008 Feb;42(3):661-8. doi: 10.1016/j.watres.2007.08.017. Epub 2007 Aug 25.

DOI:10.1016/j.watres.2007.08.017
PMID:17825873
Abstract

The removal and immobilization of arsenic from industrial mineral-processing effluents typically involves lime neutralization and coprecipitation of arsenate with ferric iron. Despite the wide practice and environmental importance of this technique, no laboratory study has focused on the roles of lime as base and third ions like Ca2+, Ni2+ and SO(2)4(-) on the kinetics of arsenic retention by the coprecipitates. In this work, coprecipitation was performed at 22 degrees C by fast (10 min) neutralization of industrially relevant concentrated arsenate-iron(III) (Fe/As=2, 4) acidic sulfate solutions to different pHs (4, 6, 8) in batch reactors, and the concentration of arsenic was monitored up to 1 year. The tests showed that maximum removal of arsenic was achieved upon neutralization to the target pH. Arsenic was found to be released back into solution from the precipitates upon continuing mild agitation at constant pH. Near-equilibrium was attained at different times depending on the applied pH: 10 days at pH 4, 6 months at pH 6 and 9 months at pH 8. An aging treatment at pH 4 significantly enhanced arsenic retention (arsenic release was reduced by at least 50%) after the system was finally stabilized at pH 8. The retention of arsenic at pH 8 was multifold improved (by a factor x 25) when lime was used instead of NaOH. Similarly, the retention of arsenic was enhanced by the presence of calcium and nickel ions in the starting solution. Finally, evidence of Ca(II)-Fe(III)-As(V) association was found, but not sulfate incorporation at pH 8.

摘要

从工业选矿废水中去除并固定砷通常涉及用石灰中和以及砷酸盐与铁离子的共沉淀。尽管该技术应用广泛且具有环境重要性,但尚无实验室研究关注石灰作为碱以及钙离子、镍离子和硫酸根离子等第三类离子对共沉淀物固定砷动力学的作用。在本研究中,通过在间歇式反应器中将工业相关的高浓度砷酸盐 - 铁(III)(铁/砷 = 2、4)酸性硫酸盐溶液在22℃下快速(10分钟)中和至不同pH值(4、6、8)进行共沉淀,并对砷浓度进行长达1年的监测。试验表明,中和至目标pH值时可实现砷的最大去除。发现在恒定pH值下持续温和搅拌时,砷会从沉淀物中重新释放回溶液中。根据所施加的pH值不同,在不同时间达到近平衡状态:pH值为4时10天,pH值为6时6个月,pH值为8时9个月。在系统最终稳定在pH值8后,在pH值4下进行老化处理可显著增强砷的固定(砷释放减少至少50%)。当使用石灰代替氢氧化钠时,在pH值8下砷的固定提高了数倍(提高了25倍)。同样,起始溶液中钙离子和镍离子的存在增强了砷 的固定。最后,发现了Ca(II) - Fe(III) - As(V)缔合的证据,但在pH值8时未发现硫酸根的掺入。

相似文献

1
Coprecipitation of arsenate with iron(III) in aqueous sulfate media: effect of time, lime as base and co-ions on arsenic retention.在硫酸盐水溶液介质中砷酸盐与铁(III)的共沉淀:时间、作为碱的石灰和共存离子对砷保留的影响。
Water Res. 2008 Feb;42(3):661-8. doi: 10.1016/j.watres.2007.08.017. Epub 2007 Aug 25.
2
A novel two-step coprecipitation process using Fe(III) and Al(III) for the removal and immobilization of arsenate from acidic aqueous solution.一种新型两步共沉淀法,使用 Fe(III) 和 Al(III) 从酸性水溶液中去除和固定砷酸盐。
Water Res. 2012 Feb 1;46(2):500-8. doi: 10.1016/j.watres.2011.11.045. Epub 2011 Nov 25.
3
Removal of arsenic from water: effect of calcium ions on As(III) removal in the KMnO(4)-Fe(II) process.水中砷的去除:钙离子对 KMnO4-Fe(II)工艺中去除 As(III)的影响。
Water Res. 2009 Dec;43(20):5119-28. doi: 10.1016/j.watres.2008.12.054. Epub 2009 Jan 20.
4
Adsorption of As(V) from water using Mg-Fe-based hydrotalcite (FeHT).使用镁铁基水滑石(FeHT)从水中吸附 As(V)。
J Hazard Mater. 2009 Nov 15;171(1-3):665-70. doi: 10.1016/j.jhazmat.2009.06.052. Epub 2009 Jun 18.
5
Arsenic recovery from water containing arsenite and arsenate ions by hydrothermal mineralization.通过水热矿化从含亚砷酸根离子和砷酸根离子的水中回收砷。
J Hazard Mater. 2007 Jul 19;146(1-2):328-33. doi: 10.1016/j.jhazmat.2006.12.025. Epub 2006 Dec 15.
6
Role of Fe(II), phosphate, silicate, sulfate, and carbonate in arsenic uptake by coprecipitation in synthetic and natural groundwater.亚铁离子、磷酸盐、硅酸盐、硫酸盐和碳酸盐在合成及天然地下水中通过共沉淀作用对砷吸收的作用。
Water Res. 2008 Feb;42(3):615-24. doi: 10.1016/j.watres.2007.08.011. Epub 2007 Aug 17.
7
Determination of arsenic removal efficiency by ferric ions using response surface methodology.采用响应面法测定铁离子去除砷的效率。
J Hazard Mater. 2009 Jul 30;166(2-3):796-801. doi: 10.1016/j.jhazmat.2008.11.131. Epub 2008 Dec 11.
8
Effect of ferrous iron on arsenate sorption to amorphous ferric hydroxide.亚铁对砷酸盐吸附于无定形氢氧化铁的影响。
Ann N Y Acad Sci. 2008 Oct;1140:335-45. doi: 10.1196/annals.1454.024.
9
Chemical reactions between arsenic and zero-valent iron in water.水中砷与零价铁之间的化学反应。
Water Res. 2005 Mar;39(5):763-70. doi: 10.1016/j.watres.2004.12.022.
10
Determination of surface properties of iron hydroxide-coated alumina adsorbent prepared for removal of arsenic from drinking water.用于去除饮用水中砷的氢氧化铁包覆氧化铝吸附剂的表面性质测定。
J Colloid Interface Sci. 2005 Apr 1;284(1):71-7. doi: 10.1016/j.jcis.2004.10.032.

引用本文的文献

1
Utilization of Lead Slag as In Situ Iron Source for Arsenic Removal by Forming Iron Arsenate.利用铅渣作为原位铁源通过形成砷酸铁去除砷。
Materials (Basel). 2022 Oct 25;15(21):7471. doi: 10.3390/ma15217471.
2
Novel strategy for reusing agricultural mulch film residual by iron modification for arsenic removal in gold-smelting wastewater.铁改性再利用农业地膜残渣去除黄金冶炼废水中砷的新策略。
Front Chem. 2022 Oct 24;10:1036726. doi: 10.3389/fchem.2022.1036726. eCollection 2022.
3
Insight into mineralizer modified and tailored scorodite crystal characteristics and leachability for arsenic-rich smelter wastewater stabilization.
深入了解用于富含砷冶炼废水稳定化的矿化剂改性和定制臭葱石晶体特性及浸出性。
RSC Adv. 2018 May 29;8(35):19560-19569. doi: 10.1039/c8ra01721b. eCollection 2018 May 25.
4
Enhanced arsenate removal from aqueous solution by Mn-doped MgAl-layered double hydroxides.锰掺杂镁铝层状双氢氧化物增强水溶液中砷酸盐的去除。
Environ Sci Pollut Res Int. 2019 Apr;26(12):12014-12024. doi: 10.1007/s11356-019-04667-4. Epub 2019 Mar 2.
5
Interpreting competitive adsorption of arsenate and phosphate on nanosized iron (hydr)oxides: effects of pH and surface loading.解析砷酸盐和磷酸盐在纳米铁(氢)氧化物上的竞争吸附:pH 值和表面负载的影响。
Environ Sci Pollut Res Int. 2018 Oct;25(28):28572-28582. doi: 10.1007/s11356-018-2897-y. Epub 2018 Aug 8.
6
Mobility and natural attenuation of metals and arsenic in acidic waters of the drainage system of Timok River from Bor copper mines (Serbia) to Danube River.蒂莫克河(塞尔维亚博尔铜矿)排水系统酸性水中金属和砷的迁移性和自然衰减及其对多瑙河的影响。
Environ Sci Pollut Res Int. 2018 Sep;25(25):25005-25019. doi: 10.1007/s11356-018-2541-x. Epub 2018 Jun 22.
7
Effect of iron reduction by enolic hydroxyl groups on the stability of scorodite in hydrometallurgical industries and arsenic mobilization.偕-OH 基团还原铁对水冶工业中铁矾稳定性及砷释放的影响。
Environ Sci Pollut Res Int. 2017 Dec;24(34):26534-26544. doi: 10.1007/s11356-017-0016-0. Epub 2017 Sep 26.
8
Fluxes of nutrients and trace metals across the sediment-water interface controlled by sediment-capping agents: bentonite and sand.由沉积物覆盖剂(膨润土和沙子)控制的营养物质和痕量金属在沉积物-水界面的通量。
Environ Monit Assess. 2016 Oct;188(10):566. doi: 10.1007/s10661-016-5583-x. Epub 2016 Sep 16.
9
The effect of microbial sulfidogenesis on the stability of As-Fe coprecipitate with low Fe/As molar ratio under anaerobic conditions.在厌氧条件下,微生物硫化作用对低 Fe/As 摩尔比的 As-Fe 共沉淀稳定性的影响。
Environ Sci Pollut Res Int. 2016 Apr;23(8):7267-77. doi: 10.1007/s11356-015-5927-z. Epub 2015 Dec 17.