Arsenic removal by discontinuous ZVI two steps system for drinking water production at household scale

被引:42
作者
Casentini, Barbara [1 ]
Falcione, Fabiano Teo [1 ]
Amalfitano, Stefano [1 ]
Fazi, Stefano [1 ]
Rossetti, Simona [1 ]
机构
[1] Natl Res Council Italy IRSA CNR, Water Res Inst, Via Solaria Km 29-300, I-00015 Rome, Italy
关键词
Arsenic; Zero valent iron; Iron precipitation; Flow cytometry; Drinking water; Adsorption; ZERO-VALENT IRON; PERMEABLE REACTIVE BARRIERS; PARTICLE-ASSOCIATED BACTERIA; FERRIC HYDROXIDE GFH; ACID-MINE DRAINAGE; METALLIC IRON; ZEROVALENT IRON; GROUNDWATER REMEDIATION; WELL WATER; OXIDATION;
D O I
10.1016/j.watres.2016.09.057
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Different countries in Europe still suffer of elevated arsenic (As) concentration in groundwaters used for human consumption. In the case of households not connected to the distribution system, decentralized water supply systems, such as Point of Use (POU) and Point of Entry (POE), offer a direct benefit for the consumers. Field scale ex-situ treatment systems based on metallic iron (ZVI) are already available for the production of reduced volumes of drinking water in remote areas (village scale). To address drinking water needs at larger scale, we designed a pilot unit able to produce an elevated daily volume of water for human consumption. We tested the long-term As removal efficiency of a two steps ZVI treatment unit for the production of 400 L/day clean water based on the combination of ZVI corrosion process with sedimentation and retention of freshly formed Fe precipitates. The system treated 100 mu g/L As(V)-contaminated oxic groundwater in a discontinuous operation mode at a flow rate of 1 L/min for 31 days. Final removal was 77-96% and the most performing step was aeration/sedimentation (A/S) tank with a 60-94% efficiency. Arsenic in the outflow slightly exceeded the drinking water limit of 10 mu g/L only after 6000 L treated and Fe concentration was always below 0.2 mg/L. Under proposed operating conditions ZVI passivation readily occurred and, as a consequence, Fe production sharply decreased. Arsenic mobility attached to particulate was 13-60% after ZVI column and 37-100% after A/S tank. Uniform amorphous cluster of Fe nanoparticles (100 nm) formed during aeration drove As removal process with an adsorption capacity corresponding to 20.5 mgAs/gFe. Research studies often focus only on chemico-physical aspects disregarding the importance of biological processes that may co-occur and interfere with ZVI corrosion, As removal and safe water production. We explored the microbial transport dynamics by flow cytometry, proved as a suitable tool to monitor the fate of both single cells and bioactive particles along the treatment train of the pilot unit. A net release of bioactive particles, representing on average 26.5% of flow cytometric events, was promoted by the ZVI filter, with densities 10 times higher than those found in the inflow. In conclusion, the proposed system was efficient to treat large daily volumes of As contaminated groundwater. However, filter design and operating conditions should be carefully adapted to specific situation, since several key factors affect As removal efficiency. An effort in the optimization of ZVI filter design should be made to reduce fast observed ZVI passivation and low As adsorption capacity of the whole filter: More attention to biomass retention and bioactive particles travelling within the unit should be given in order to elucidate bacteria influences on As removal efficiency and related sanitary risks on long term basis. (C) 2016 Elsevier Ltd. All rights reserved.
引用
收藏
页码:135 / 145
页数:11
相关论文
共 64 条
[1]   Intraparticle diffusion and adsorption of arsenate onto granular ferric hydroxide (GFH) [J].
Badruzzaman, M ;
Westerhoff, P ;
Knappe, DRU .
WATER RESEARCH, 2004, 38 (18) :4002-4012
[2]   Removal of arsenic from water by zero-valent iron [J].
Bang, S ;
Korfiatis, GP ;
Meng, XG .
JOURNAL OF HAZARDOUS MATERIALS, 2005, 121 (1-3) :61-67
[3]   Arsenic accumulation in irrigated agricultural soils in Northern Greece [J].
Casentini, B. ;
Hug, S. J. ;
Nikolaidis, N. P. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2011, 409 (22) :4802-4810
[4]  
Chiu PC, 2013, ACS SYM SER, V1123, P237
[5]   SPECTROPHOTOMETRIC DETERMINATION OF HYDROGEN SULFIDE IN NATURAL WATERS [J].
CLINE, JD .
LIMNOLOGY AND OCEANOGRAPHY, 1969, 14 (03) :454-&
[6]   A Comparison Between Field Applications of Nano-, Micro-, and Millimetric Zero-Valent Iron for the Remediation of Contaminated Aquifers [J].
Comba, Silvia ;
Di Molfetta, Antonio ;
Sethi, Rajandrea .
WATER AIR AND SOIL POLLUTION, 2011, 215 (1-4) :595-607
[7]   Use of iron-based technologies in contaminated land and groundwater remediation: A review [J].
Cundy, Andrew B. ;
Hopkinson, Laurence ;
Whitby, Raymond L. D. .
SCIENCE OF THE TOTAL ENVIRONMENT, 2008, 400 (1-3) :42-51
[8]   Comparison of arsenic(V) and arsenic(III) sorption onto iron oxide minerals: Implications for arsenic mobility [J].
Dixit, S ;
Hering, JG .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2003, 37 (18) :4182-4189
[9]   Discussing porosity loss of Fe0 packed water filters at ground level [J].
Domga, Richard ;
Togue-Kamga, Fulbert ;
Noubactep, Chicgoua ;
Tchatchueng, Jean-Bosco .
CHEMICAL ENGINEERING JOURNAL, 2015, 263 :127-134
[10]   Microbial Transport, Retention, and Inactivation in Streams: A Combined Experimental and Stochastic Modeling Approach [J].
Drummond, Jennifer D. ;
Davies-Colley, Robert J. ;
Stott, Rebecca ;
Sukias, James P. ;
Nagels, John W. ;
Sharp, Alice ;
Packman, Aaron I. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2015, 49 (13) :7825-7833