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Arsenic Removal With Iron-Tailored Activated Carbon Plus Zero-Valent Iron PDF

76 Pages·2010·0.94 MB·English
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Arsenic Water Technology Partnership Arsenic Removal With Iron-Tailored Activated Carbon Plus Zero-Valent Iron ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. About the Water Research Foundation The Water Research Foundation is a member-supported, international, nonprofit organization that sponsors research to enable water utilities, public health agencies, and other professionals to provide safe and affordable drinking water to consumers. The Foundation’s mission is to advance the science of water to improve the quality of life. To achieve this mission, the Foundation sponsors studies on all aspects of drinking water, including supply and resources, treatment, monitoring and analysis, distribution, management, and health effects. Funding for research is provided primarily by subscription payments from approximately 1,000 utilities, consulting firms, and manufacturers in North America and abroad. Additional funding comes from collaborative partnerships with other national and international organizations, allowing for resources to be leveraged, expertise to be shared, and broad-based knowledge to be developed and disseminated. Government funding serves as a third source of research dollars. From its headquarters in Denver, Colorado, the Foundation’s staff directs and supports the efforts of more than 800 volunteers who serve on the board of trustees and various committees. These volunteers represent many facets of the water industry, and contribute their expertise to select and monitor research studies that benefit the entire drinking water community. The results of research are disseminated through a number of channels, including reports, the Web site, conferences, and periodicals. For subscribers, the Foundation serves as a cooperative program in which water suppliers unite to pool their resources. By applying Foundation research findings, these water suppliers can save substantial costs and stay on the leading edge of drinking water science and technology. Since its inception, the Foundation has supplied the water community with more than $300 million in applied research. More information about the Foundation and how to become a subscriber is available on the Web at www.WaterRF.org. ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. Arsenic Removal With Iron-Tailored Activated Carbon Plus Zero-Valent Iron Prepared by: Weifang Chen, Robert Parette, Will Sheehan, Fred S. Cannon, Brian A. Dempsey The Pennsylvania State University Department of Civil and Environmental Engineering 212 Sackett Engineering Building University Park, PA 16802 Jointly Sponsored by: Water Research Foundation 6666 West Quincy Avenue, Denver, CO 80235 and U.S. Department of Energy Washington, D.C. 20585-1290 Published by: WERC, a Consortium for Water Research Foundation Environmental Education and Technology Development at New Mexico State University U NM DINÉ U N MS MIM N T SANDIALOSALAMOS A CONSOANRTDIU TMEC FHONRO ELNOVGIRYO DNEVMEELNOTPAML EENDTUCATION ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. DISCLAIMER This study was jointly funded by the Water Research Foundation and the U.S. Department of Energy (DOE) under Grant No. DE-FG02-03ER63619 through the Arsenic Water Technology Partnership. The comments and views detailed herein may not necessarily reflect the views of the Water Research Foundation, its officers, directors, affiliates or agents, or the views of the U.S. Federal Government and the Arsenic Water Technology Partnership. The mention of trade names for commercial products does not represent or imply the approval or endorsement of the Foundation or DOE. This report is presented solely for informational purposes. Copyright © 2010 by Water Research Foundation and Arsenic Water Technology Partnership ALL RIGHTS RESERVED. No part of this publication may be copied, reproduced or otherwise utilized without permission. Printed in the U.S.A. ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. CONTENTS   LIST OF TABLES ........................................................................................................................ vii  LIST OF FIGURES ....................................................................................................................... ix  FOREWORD ............................................................................................................................... xiii  ACKNOWLEDGMENTS ............................................................................................................ xv  EXECUTIVE SUMMARY ........................................................................................................ xvii  CHAPTER 1: INTRODUCTION ................................................................................................... 1  Background ......................................................................................................................... 1  Arsenic Removal Technology............................................................................................. 1  pH Effect on Arsenic Removal by ZVI and Iron (hydr)oxides .......................................... 2  Iron Corrosion and Iron Release ......................................................................................... 2  Iron Corrosion by Electrolytic Cells ................................................................................... 3  Research Objectives ............................................................................................................ 4  CHAPTER 2: MATERIALS AND METHODS ............................................................................ 5  Materials ............................................................................................................................. 5  Water Sources for Pilot Columns and rapid small-scale column test (RSSCT) ..... 5  Activated Carbons ................................................................................................... 5  Methods............................................................................................................................... 6  Iron Tailoring by Iron-salt Evaporation .................................................................. 6  Rapid Small-Scale Column Tests (RSSCTs) .......................................................... 6  Zero-Valent Iron (ZVI) and Iron-Loaded GAC for As Removal in RSSCTs ........ 7  Iron Pre-Corrosion, Aging, and Idling in RSSCTs ................................................. 7  Pilot Columns.......................................................................................................... 7  Sampling Protocol and Chemical Analysis ........................................................... 12  CHAPTER 3: RESULTS AND DISCUSSIONS ......................................................................... 13  Effect of Temperature on Iron Tailoring by Evaporation ................................................. 13  RSSCT vs. Pilot-scale Columns ....................................................................................... 14  Pilot-scale Studies with Zero-valent Iron Rod and GAC .................................................. 16  Pilot-Scale Studies With Electrolytic Solubilization And Iron-Tailored GAC ................ 22  Pilot-Scale Studies with Electrolytic Solubilization Achieved with 0.01 or 0.02A, Plus Iron-Tailored GAC ................................................................ 23  Pilot-Scale Studies with Electrolytic Solubilization Achieved with 0.1 A, Plus Iron-Tailored GAC .................................................................................... 28  Zero-Valent Iron With Iron-Tailored GAC In RSSCTs ................................................... 31  RSSCTs: Arsenic Removal with Pre-corroded Galvanized Steel Fittings Coupled with Iron-tailored GAC .............................................................. 32  Performance of Perforated Steel Chamber Preceding Iron-tailored GAC ............ 34  v ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. vi | Arsenic Removal With Iron-Tailored Activated Carbon Plus Zero-Valent Iron CHAPTER 4: CONCLUSIONS ................................................................................................... 47  CHAPTER 5: SIGNIFICANCE TO UTILITIES ......................................................................... 49  REFERENCES ............................................................................................................................. 51  ABBREVIATIONS ...................................................................................................................... 55  ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. TABLES 2.1 Water quality characteristics of the groundwater used in this study ...................................5  2.2 Pilot-scale columns operational conditions .........................................................................9  2.3 Composition of zero-valent iron sources (percent %) .......................................................12  3.1 Iron content and BVs to breakthrough for carbons that were iron-preloaded by the evaporation method, with curing at 50−100°C ..................................................................14  3.2 Bed volumes to 10 µg/L As breakthrough in RSSCT versus pilot columns with iron tailored carbons ..................................................................................................................16  3.3 Bed volumes to 10 µg/L As breakthrough in pilot columns with zero-valent iron rods and either iron-tailored GAC or virgin GAC. For Column 5, the rods reached all the way to the column’s bottom. For all others, the rods remained in the top two-thirds of the media ............................................................................................................................21  3.4 Theoretical and measured iron dose for electrolytic cells* ...............................................32  3.5 Arsenic distribution in GS #1 (iron-tailored GAC coupled with corrosion of galvanized steel fittings) after 250,000 BVs ......................................................................34  3.6 Column operating parameters and BVs to 10 µg/L breakthrough* ...................................44  vii ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. FIGURES 2.1 Photograph of pilot-scale columns .......................................................................................8  2.2 Electrolytic solubilization cells ..........................................................................................10  2.3 Branched rod configuration used in Columns #11 to 15. ..................................................11  3.1 RSSCT using arsenic-containing groundwater, for iron-loaded GAC, with preloaded iron curing at temperatures of 50−100°C. Y-axis µg/L As. ..............................................13  3.2 Arsenic breakthrough for iron-tailored (60oC) carbon in RSSCTs and Pilot Column #3........................................................................................................................................15  3.3 Arsenic breakthrough for iron-tailored (100oC) carbon in RSSCTs and Pilot Column #4........................................................................................................................................15  3.4 As breakthrough for pilot columns with virgin AquaCarb and plain steel mesh + virgin AquaCarb.................................................................................................................17  3.5 Back pressure buildup for Columns #1 and 2 ....................................................................18  3.6 Iron concentration in effluent from Column #2 .................................................................18  3.7 As breakthrough for pilot columns with straight and branched rods (rod diameters ¼ inch) ...................................................................................................................................19  3.8 As for pilot columns, while comparing the effect of pH, EBCT, iron-tailored carbon and smaller branched rod (rod diameters ¼ inch, unless otherwise listed) .......................20  3.9 Iron concentration in effluent for Column #5, with straight rods that extended through the full media depth ...........................................................................................................22  3.10 Electrolytic solubilization chamber ...................................................................................23  3.11 Effluent arsenic concentration in Column #17: 0.02 A electrolytic solubilization, virgin GAC.........................................................................................................................24  3.12 Back pressure and voltage vs. BVs in Column #17: 0.02 A electrolytic solubilization, virgin GAC.........................................................................................................................25  3.13 Effluent arsenic concentration vs. BVs for Column #18, 19 and 20 .................................26  3.14 Backpressure vs. BVs for Column #18, 19 and 20 ............................................................27  3.15 Electrolytic cell voltages vs. BVs for Column #18, 19 and 20 ..........................................27  ix ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED. x | Arsenic Removal With Iron-Tailored Activated Carbon Plus Zero-Valent Iron 3.16 Uneven iron loading in Column #6 when 0.1 A was applied across the ZVI electrolytic cell ...................................................................................................................29  3.17 Effluent Arsenic Concentration from Pilot Columns #7−10. Influent Concentration 50−60 ppb, targeted EBCTs as listed, and these EBCTs were maintained for the first 1,000−1,500 BVs ...............................................................................................................29  3.18 Release of Iron from Electrolytic Pilot Columns Operated at 0.1A, targeted EBCTs as listed, and these EBCTs were maintained for the first 1,000−1,500 BVs .........................30  3.19 Pressure Build-up during Operation of Electrolytic Pilot Columns Operated at 0.1 A, targeted EBCTs as listed, and these EBCTs were maintained for the first 1,000−1,500 BVs ....................................................................................................................................30  3.20 Operational Voltage of Electrolytic Pilot Columns Operated at 0.1 A, targeted EBCTs as listed, and these EBCTs were maintained for the first 1,000−1,500 BVs .....................31  3.21 RSSCT of iron tailored GAC coupled with galvanized steel (GS#1) and without (#1); both systems operated at pH 6±0.3 using the arsenic-containing groundwater as influent (As 47−55 µg/L). Dashed line indicated where the GS#1 system was idled for 6 days............................................................................................................................33  3.22 pH effect on Mini column performance (A) Arsenic effluent from GAC column. (B) Arsenic removed by steel chamber. (C) Filterable arsenic after steel chamber. Lines indicate where the columns were idled for 7 days (Dotted line: pH 7.5; dashed: pH 6; Solid line: pH 6−6.5) .........................................................................................................35  3.23 Arsenic removal with no idle (PS #3), one idle (PS #1) and 3 idles (PS #2). (A) As effluent from GAC column. (B) As removal in steel chamber. (C) Filterable arsenic leaving steel chamber. Solid line indicates where PS #2 idled for 7 days, dashed line indicates where PS #1 idled for 7 days. All columns were operated at pH 6±0.3 .............38  3.24 Idling effect on Fe release. (A) Total Fe released from steel chamber. (B) Filterable Fe released from steel chamber. (C) Fe effluent from GAC column. Solid line is where PS#2 idled for 7 days on 3 occasions. D) Ferrous iron in filtered water released from steel chamber. Dashed line is where PS#1 idled once for 7 days. ............................40  3.25 Scanning electron microscopy of: (A) Fresh precorroded steel sheets, (B) Aged precorroded steel sheets, and (C) Steel sheets employed in PS#2, after use. (D) Steel sheets employed in PS#4, after use. ...................................................................................41  3.26 Effect of pH, pre-corrosion, aging, and idling on: (A) Total Fe released from steel chamber, (B) Filterable Fe released from steel chamber, (C) Fe accumulated in GAC column (including preloaded iron). ....................................................................................43  ©2010 Water Research Foundation and Arsenic Water Technology Partnership. ALL RIGHTS RESERVED.

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arsenic-sorbing propensity and low costs of iron. Our overall approach has been to couple iron- impregnated GAC with zero-valent iron sources to
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