Thesis Acid Mine Drainage Impacts in the Upper

Thesis Acid Mine Drainage Impacts in the Upper

THESIS ACID MINE DRAINAGE IMPACTS IN THE UPPER ARKANSAS RIVER BASIN: A STUDY OF WATER QUALITY, TREATMENT EFFICIENCY, AND PREDICTED LONGEVITY Submitted by Megan Moore Department of Ecosystem Science and Sustainability In partial fulfillment of the requirements For the Degree of Master of Science Colorado State University Fort Collins, Colorado Spring 2019 Master’s Committee: Advisor: Tim Covino Matthew Ross Mike Wilkins Charles Rhoades Copyright by Megan Moore 2019 All Rights Reserved ABSTRACT ACID MINE DRAINAGE IMPACTS IN THE UPPER ARKANSAS RIVER BASIN: A STUDY OF WATER QUALITY, TREATMENT EFFICIENCY, AND PREDICTED LONGEVITY Mining activity in the Sugarloaf and Leadville mining districts of Leadville, Colorado has impaired water quality in the Upper Arkansas River Basin. Tributary and main channel waters are often out of compliance with state water quality standards, and stream flora and fauna as well as human use of these waterways is threatened by acid mine drainage. This study aims to describe the impact historical mining activity has had on the waters of the Upper Arkansas River Basin by characterizing water quality, analyzing metal removal efficiency from both active and passive treatment sites in the area, and estimating the time it will take for drainage from mining tunnels to naturally comply with state water quality standards. A comparison of instream dissolved concentrations of cadmium, copper, iron, lead, manganese, and zinc to state water quality standards shows waters of the Upper Arkansas River Basin are often out of compliance with chronic and/or acute standards. This is seen more frequently upstream from treatment sites and higher up in the tributary system than at tributary mouths or in the main channel of the Arkansas River. An examination of metal removal from the Leadville Mine Drainage Tunnel and Yak Tunnel water treatment plants along East Fork and California Gulch shows dissolved metal reduction between 33 and 100 percent compared with 0 to 84 percent at the passive Dinero Wetland Complex along Lake Fork. Finally, an analysis of projected longevity highlights the importance of clean-up plans for future mining projects with estimated impaired water quality continuing upwards of 2000 years at Yak Tunnel. i ACKNOWLEDGEMENTS This project has taken more than I ever might have imagined it could and I could not have done it alone. I would like to thank John Stednick for helping me find the resources I needed to pursue the project closest to me, and Tim Covino for taking me on the majority of the way through my graduate career, allowing me to join his lab after John’s retirement, and for helping me to complete my project. Without help from John and Tim, this project never would have gotten off of the ground or landed in one piece, I am grateful for everything you have both done for me. To my committee members, Matt Ross, Mike Wilkins, and Chuck Rhoades, I would like to thank you for hopping onto my project in the most unconventional of ways and for helping me see it through. The help from my advisors and committee members has helped me along through my long graduate career and hurtled me on to whatever may be next in my future. Outside of the academic realm, I also found a great support network in my amazing family and wonderful partner. Mom, Lindsey, Matthew, and Aaron, I can’t thank you enough for the loving support you’ve given me and the incredible patience you’ve shown me as tackled graduate school, sometimes more successfully than others. I know it wasn’t always easy to watch my struggles or offer advice in my field of study, but you still stood by my side and held me up. It hasn’t been easy dealing with the distance between us as I’ve been finishing my degree, but soon you will finally get me back! I’m excited to share this project with you, to show you what I’ve done and what your support has helped me accomplish, and to finally be able to give more back to each of you. ii TABLE OF CONTENTS ABSTRACT ..................................................................................................................................... i ACKNOWLEDGEMENTS ............................................................................................................ ii 1. INTRODUCTION ......................................................................................................................1 1.1. Acid Rock Drainage/Acid Mine Drainage Chemistry ........................................................1 1.2. Mining in Leadville and Water Quality Standards .............................................................3 1.3. Remediation Efforts ............................................................................................................5 1.4. Purpose Statement ...............................................................................................................9 1.5. Hypothesis/Objectives ........................................................................................................9 2. METHODS ...............................................................................................................................11 2.1. Site Description .................................................................................................................11 2.2. Data Source and Assumptions ..........................................................................................13 2.3. Water Quality Characterization ........................................................................................16 2.4. Treatment Removal Efficiency .........................................................................................18 2.5. Mine Drainage Longevity .................................................................................................19 3. RESULTS .................................................................................................................................22 3.1. Water Quality Characterization ........................................................................................22 3.2. Metal Concentrations and Water Quality Standards .........................................................24 3.3. Treatment Removal Efficiency .........................................................................................25 3.4. Mine Drainage Longevity .................................................................................................28 4. DISUSSION ..............................................................................................................................29 4.1. Water Quality Characterization ........................................................................................29 iii 4.2. Metal Concentrations ........................................................................................................32 4.3. Treatment Removal Efficiency .........................................................................................34 4.4. Mine Drainage Longevity .................................................................................................37 5. CONCLUSIONS.......................................................................................................................39 5.1. Water Quality Characterization ........................................................................................39 5.2. Metal Concentrations ........................................................................................................39 5.3. Treatment Removal Efficiency .........................................................................................40 5.4. Mine Drainage Longevity .................................................................................................40 5.5. Recommendations .............................................................................................................41 6. FIGURES ..................................................................................................................................43 7. TABLES ...................................................................................................................................52 REFERENCES ..............................................................................................................................60 iv 1. INTRODUCTION Contamination from mining waste is a part of hard rock mining’s legacy and dates back to the Roman Empire (Robb and Robinson, 1995). Mine waste contamination is most commonly associated with water quality degradation as a result of acid rock drainage from flooded mine voids and from tailings and spoil heaps that are hydrologically connected to surface water. Contamination may persist for many decades or centuries and occurs at both active and abandoned mines (Younger, 1997; Wood, et al., 1999; Younger, 2000; Demchak et al. 2004). In the United States there are over 557,650 abandoned mines (Garavan et al., 2008 as cited by Cidu, 2011) and approximately 20,000 kilometers of streams and rivers are impacted by acid mine drainage—the majority of which receive effluent directly from abandoned mines (Skousen, 1995). In the Rocky Mountain region of Colorado, 18,382 abandoned mines and related features are identified on National Forest System lands (Sares et al., 2000). Total Colorado stream length impacted by abandoned mine lands in 2010 has been estimated at 908 kilometers (Colorado Water Quality Assessment Report) including at least 102 kilometers in the Upper Arkansas River Basin (Watershed Quality Assessment Report). 1.1. Acid Rock Drainage/Acid

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