FIELD INVESTIGATION OF IN SITU LIME NEUTRALIZATION OF ACIDIC SEDIMENT

Slides:



Advertisements
Similar presentations
By: Frank Filas, P.E. Environmental Manager Energy Fuels Resources Corporation 44 Union Blvd., Suite 600 Lakewood, Colorado Uranium Development in.
Advertisements

FE Review for Environmental Engineering Problems, problems, problems Presented by L.R. Chevalier, Ph.D., P.E. Department of Civil and Environmental Engineering.
By Hung Nguyen Lime Treatment of Acid Mine Drainage at Leviathan Mine, California.
Clean-up of Lincoln Park, Colorado Introduction The Source of the problem The area effected.
Chilled Water, Hot Water, Heat Pump and Glycol Loops
Surface Water Treatment Plant
Acid Mine Drainage. Terms Acid Mine Drainage (AMD) –Water that is polluted from contact with mining activity Acid Rock Drainage (ARD) –Natural rock drainage.
Dale T Littlejohn Senior Geologist. What is fate and transport in the vadose zone? Vadose Zone Hydrocarbon release from buried pipeline Aquifer Surface.
Sustained Treatment of AMD Containing Al and Fe 3+ with Limestone Aggregate Neil Wolfe and Robert Hedin Hedin Environmental West Virginia Mine Drainage.
Presented to: The Society of Wetland Scientists Mid-Atlantic Chapter 2014 Conference State College, Pennsylvania April 5 th, 2014 By: Kevin L. Hoover,
I1i1 i2i2 r p r = runoff from upslope areas i 1 = inflow from Upper Carbonate aquifer i 2 = inflow from Decorah area infiltration p = precipitation (direct)
Passive Remediation of High Metal Loading, Net Acidic Mine Impacted Water Using Crab Shell Chitin as a Substrate Amendment Amanda K. Brown and Dr. Rachel.
2010 Long-Term Surveillance and Maintenance Conference Old Rifle Title I Processing Site, Rifle, Colorado What Are They Doing on My Site? Richard Bush,
Aeration Approaches and Activated Iron Solids (AIS) for AMD Treatment By Jon Dietz, Ph.D. Environmental Engineering & Science Iron Oxide Technologies,
Wetlands for Acid Mine and Livestock Drainage Treatment By: Gabe Jenkins April 18 th 2005.
WASTE WATER TREATMENT FOR RITONAVIR PRODUCTION PLANT Presented by Wang Dong Mei July 8, 2000.
AQUATEST a.s. TECHNICAL SUPPORT DIVISION Modular units for mine water disposal A set of technical equipment designed for mine water disposal is.
PHOSPHORUS REMOVAL ON DAIRIES IN THE PACIFIC NORTHWEST Applying a Cone Shaped Fluidized Bed Phosphorus Crystallizer Ron Sheffield – U of Idaho Keith Bowers.
Acid Mine Drainage. Terms Acid Mine Drainage (AMD) –Water that is polluted from contact with mining activity Acid Rock Drainage (ARD) –Natural rock drainage.
Water Treatment for NYC Croton Schematic. NYC Filtration Plant for Delaware and Catskill Systems  Filtration avoidance criteria  Alternatives to Filtration.
Water Treatment for NYC Croton Schematic. NYC Filtration Plant for Delaware and Catskill Systems ä Filtration avoidance criteria ä Alternatives to Filtration.
1 Abandoned Coal Mines: In-Situ Treatment of AMD with CCPs Jess W. Everett, Ph.D., P.E. Associate Professor Civil Engineering Rowan University.
Kavita Mahulikar and Taylor Reiss Cornell University 10 December 2005
Waupun Utilities Water Treatment Facility. Treatment Processes Source Water Pretreatment System Reverse Osmosis System Post Treatment System Distribution.
Acid Lakes from Lignite Mines Dan Henderson. Lignite  Brown/soft coal.  Used for steam electric power generation.  Mined in open pits.  Production.
PHOSPHORUS REMOVAL FOR LAGOON OPERATORS WHY THE CONCERN OVER P.
Larnaca Desalination Plant, Cyprus
Converting a supply well into an ASR well: Case Histories Roger Dittus PG – United Water Idaho Inc.
FSA Groundwater Flow and Solute Transport Model Presentation to Scottsdale Citizens Group March 19, 1999.
Formation and Treatment
Selenium Removal from Mine Waters
Seasonal Changes in Biogeochemistry of a Natural Wetland Receiving Drainage from an Abandoned Mine Diane McKnight and Eric August – University of Colorado.
Pre-Lab 19B: Acids, Bases and pH
The Drinking Water Treatment Process
Chemical Treatment Precipitation and Reduction/Oxidation (Section 9-4)
Water Treatment CE 326 Principles of Environmental Engineering
History and Cleanup at Chemical Commodities, Inc. Jeff Field US EPA Region 7 1.
Water Quality Considerations for Non-Hazardous Disposal Wells Injecting Under Pressure Chad Milligan, P.G. Nicole Franken, E.I.T.
Decommissioned BCR Organic Media Characterization Standard Mine Superfund Site, Crested Butte, CO Neal Gallagher, Eric Blumenstein, Tom Rutkowski, John.
Two Union Square Union Street, Suite 601 Seattle, WA (206) Field testing and modeling of in situ groundwater.
SOME RECENT ADVANCES IN PASSIVE TREATMENT OF MINED DRAINAGE Arthur W. Rose Pennsylvania State University.
Considerations for Brackish Groundwater Use as a Water Supply for Small Water Systems and Municipalities Eddie C. Livingston, MSCE, P.E. Livingston Associates,
Sustainable development and the environment Remediation.
By: Pimluck Kijjanapanich. I Introduction O Objectives S Scope of Study L Literature Review マスタ タイトルの書式設定 M Methodology マスタ タイトルの書式設定 R1R1 Results and.
Reactions of Carbonate Minerals with Acid Mine Drainage: Is Dolostone or Limestone Better?
SUDS Research Dr Martin Mansell School of Engineering and Science University of Paisley.
1.  Residual Solids Management Plan – RSMP (2014)  Pilot-Scale Screw Press Evaluation  Residual Disposal Options  Recommendations 2.
Timothy K. Tsukamoto, Ph.D.
Groundwater Chapter 10 Notes.
Topic 9 ReactionsofAcids. Neutralisation Neutralisation is the reaction of acids with neutralisers. A neutraliser is a substance which neutralises an.
Petroleum engineers use a variety of flooding agents (seawater, hot water, acids, CO 2, and alkali solutions) to displace fluids and increase production.
CE 3354 Engineering Hydrology Lecture 2: Surface and Groundwater Hydrologic Systems.
 Greater flexibility in application of fertilizers does not depend on the climatic conditions such as rain and soil condition.  Frequent and small applications.
1 Groundwater Pollution GW 10 Monitored Natural Attenuation.
Acid mine drainage Mateo Transueo. What causes it……... ► Acid mine drainage (AMD) is the drainage produced from mines containing sulfide minerals which.
Paul Eger, Global Minerals /Sovereign Consulting Peggy Jones, Doug Green, American Peat Technology Igor Kolomitsyn, Natural Resources Research Institute.
Conventional Sewage Treatment Plants:
Groundwater Pilot Treatment System Update May 2017
Lecture (8): liquid wastes treatment (primary, vital, advanced).
Date of download: 10/29/2017 Copyright © ASME. All rights reserved.
Chapter 11 Preview Section 1 The Active River
Jesse Taylor: Remington Technologies
ASSESSMENT OF CORRECTIVE MEASURES PUBLIC MEETING
European Metallurgical Conference
System Monitoring/Regulatory Evaluation
Diagram the pH scale Seconds Left:
Diagram the pH scale Seconds Left:
MRU: Metal Removal Units
MRU: Metal Removal Units
Modeling Water Treatment Using the Contaminant Transport Module
Presentation transcript:

FIELD INVESTIGATION OF IN SITU LIME NEUTRALIZATION OF ACIDIC SEDIMENT John Villinski SME 2017 Annual Conference Denver, Colorado February 22, 2016

Problem Alluvial aquifers impacted by past mining operations Majority of the acidity and metals stored in the sediment Estimates of pump & treat cleanup times can many decades This is pretty well known, just to set the stage Unlined tailings, pond upsets, improper storage of process solutions

Program Objectives Evaluate treatment alternatives to enhance remediation and shorten duration Effectiveness Implementability Cost Proposed Technology – in situ neutralization with alkali This talk will focus on effectiveness and implementability Other treatment options – oxidation, sulfate reduction/sulfide precipitation, etc.

Field Testing Infiltrate lime solution via basin to acidic sediment at base of vadose zone Implementability mix and infiltrate near-saturated lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH (target pH 8) reduce metals concentrations

Field Testing Alkali treatment is a two-step process Targets Alkali application Neutral water flush Targets Deliver alkali dose over 5 days Transport alkalinity through treatment volume

Acidic Vadose Zone Test Schematic MWVZ01 Treatment Volume Circum-neutral Vadose Zone CNVZ pH > 6.5 Acidic Vadose Zone AVZ pH < 6.5 Bedrock

Pretest Sediment pH Cross Section Looking Upgradient CNVZ Review of the acidity in Live Oak AVZ ASZ Water Level Bedrock Contact

Site Layout Weir Tank Groundwater Flow Mix Tank Legend X Gravity Basin MW MWVZ01 Still Well Neutral Water Mix Tank Weir Tank (solids retention) A Pump Totalizer A – Mix Tank B – Weir Tank C – Basin Well Flow Direction Legend *Diagram not to scale N B C X Milk of Lime Basin Gravity Feed Groundwater Flow

Weir Tank Schematic FLOW In Solids trapped behind weir Out

Test Results Implementability Effectiveness mix near-solubility lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH reduce metals concentrations

Test Results Implementability Effectiveness mix near-solubility lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH reduce metals concentrations

Alkalinity Average 1,857 mg/l as CaCO3 NWF Field NWF Lab

Test Results Implementability Effectiveness mix near-solubility lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH reduce metals concentrations

SOLIDS CONTROL – WEIR TANK During Lime Application Post Neutral Flush

SOLIDS CONTROL – BASIN DURING ALKALI APPLICATION

SOLIDS CONTROL – BASIN DURING NEUTRAL WATER FLUSH

Test Results Implementability Effectiveness mix near-solubility lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH reduce metals concentrations

Infiltration Rate Average 11.5 gpm

Test Results Implementability Effectiveness mix near-solubility lime solution control solids avoid application facility/aquifer formation damage Effectiveness raise pH reduce metals concentrations

Metals concentrations drop by > 90% Groundwater Quality Metals concentrations drop by > 90% pH > 5.3 for 30 days

Test Summary Implementability Lime solutions near 90% solubility were efficiently mixed with a readily available rental mix tank Calcite precipitates were effectively controlled using a readily available rental weir tank Lime applied continuously at a rate of 11.5 gpm for 5.14 days No clogging of the infiltration basin No formation damage Basin alkalinity was 98.2% of mix tank alkalinity

Test Summary Effectiveness Raised aqueous pH at base of treatment volume for >30 days maximum pH of 6.58 Aqueous Al, Cu, and Mn concentrations decreased by >90% remained at low levels through end of test (45 days)