DOCSLIB.ORG

Yak Tunnel/California Gulch Remedial Investigation February 28, 1986

Total Page：16

File Type：pdf, Size：1020Kb

Download full-text PDF Read full-text
Yak Tunnel/California Gulch Remedial Investigation February 28, 1986 ! I *••-.. f"' YAK TUNNEL / CALIFORNIA GULCH REMEDIAL INVESTIGATION DMINISTR RECOR PREPARED FOR STATE OF COLORADO DEPARTMENT OF LAW FEBRUARY 28,1936 PREPARED BY ENGINEERING-SCIENCE, INC, 1100^TOUDENV^t, TCOLORAD STREETO 8020, SUIT4 E 1100 IN COOPERATION Wl THE U.S. ENVIRONMENTAL PROTECTION AGENCY TABLE OF CONTENTS EXECUTIVE SUMMARY Goals of the Remedial Investigation i Site Description and Background Information i Major Findings ii CHAPTER 1 - INTRODUCTION 1-1 CHAPTER 2 - SITE DESCRIPTION AND BACKGROUND INFORMATION Sources, Pathways, and Receptors of Contamination 2-4 Sources 2-4 Pathways and Receptors 2-7 Hazard Evaluation of Selected Hazardous Substances 2-8 Human Health 2-8 Wildlife 2-9 Vegetation 2-9 Aquatic life 2-10 Demographics 2-10 Land Use 2-12 _jP.laiife 2-13 —- Climatology 2-13 CHAPTER 3 - SITE HISTORY AND GEOLOGY History 3-1 Historical Water Quality of Yak Tunnel Drainage 3-9 Historical Water Quality of the Leadville Mine Drainage Tunnel 3-9 Tailings and Mill History 3-12 Mining Activities 3-15 Underground Mining 3-15 Milling Processes 3-17 Smelter Residues and Emissions 3-18 Site Geology 3-19 Surficial Materials 3-19 Bedrock Geology 3-20 Ore Deposits 3-22 Geochemistry Metal Dispersion from Mineralization 3-24 Sulfide Oxidation Processes 3-26 Metal Dispersion in Surface and Ground Waters . 3-27 Metals in Soils 3-31 CHAPTER 4 - MINING WASTE INVESTIGATION Tailings Ponds-.-. 4-rl Waste Piles 4-8 California Gulch 4-8 Stray Horse Gulch 4-11 Contaminated Soils and Sediment 4-12 CHAPTER 5 - GROUND WATER INVESTIGATION Resources and Uses 5-2 Occurrence 5-2 Uses 5-5 Nature and Extent of Contamination 5-10 California Gulch 5-12 Arkansas River Alluvium 5-32 Environmental and Public Health Effects 5-33 CHAPTER 6 - SURFACE WATER INVESTIGATION Resources and Uses 6-1 Description 6-1 Potential for Flood Damage 6-5 Water Use and Supply 6-6 Nature and Extent of Contamination 6-9 Past Studies 6-9 CERCLA Investigations 6-15 EPA CERCLA Investigations 6-15 Engineering-Science CERCLA Investigations 6-42 Enviromental and Public Health Effects 6-81 CHAPTER 7 - AQUATIC BIOTA INVESTIGATION Resources and Use 7-2 Macrohabitat 7-2 Aquatic Biota 7-4 Nature and Extent of Contamination 7-5 Sampling Stations 7-5 Sampling Methods 7-6 Sampling Results " 7-7 Discussion of Contaminants 7-21 Contaminants of Concern and Their Extent in the Arkansas River 7-22 Impacts to the Aquatic Biota Resource 7-41 CHAPTER 8 - SOILS INVESTIGATION Resources and Use 8-1 Nature and Extent of Contamination 8-3 Soil Physical/Chemical Characteristics of Concern 8-3 Toxic Substances of Concern 8-6 Cumulative Geographic Extent of Contamination 8-17 Statistical Analysis of Data 8-26 Metals Concentrations 8-28 Environmental and Public Health Effects 8-36 CHAPTER 9 - VEGETATION INVESTIGATION Resources and Sse 9-1 Nature and Extent of Contamination 9-2 Contaminants of Concern 9-2 Geographic Extent of Contamination in Vegetation 9-9 Results 9-13 Tennessee Creek Valley and Arkansas River Valley Pastures 9-13 Tennessee Creek Valley and Arkansas River Valley Wetlands 9-23 California Gulch and Stray Horse Gulch 9-24 Environmental and Public Health Effects 9-24 CHAPTER 10 - AIR QUALITY INVESTIGATION Site Description 10-1 Nature and Extent of Contamination 10-2 Sources 10-3 Receptors 10-3 Transport Mechanism 10-5 Source/Receptor Relationship 10-5 Long-term Impact 10-9 Environmental and Public Health Effects 10-11 CHAPTER 11 - GENERAL RESPONSE ACTIONS AND TECHNOLOGIES Introduction 11-1 Summary of Site Problems 11-2 General Response Actions 11-2 Formation of Remedial Technologies 11-3 References Cited R-l LIST OF TABLES Number Title Page 2.1 Populations of Lake County and Leadville 1900-1983 with Forecasts through 2010 2-11 2.2 Annual and 10-Year Average Precipitation (inches) • 2-15 3.1 Yearly Concentrations of Hazardous Metals in the Yak Tunnel Drainage 3-10 3.2 Yearly Concentrations of Hazardous Metals (Zinc) in the Leadville Drainage Tunnel Discharge 3-11 3.3 Mobility of Some Elements in Surficial Environments 3-32 4.1 Chemical Analysis of Tailings Pond 3 4-4 4.2 Analysis of Tailings Samples from Leadville, Colorado (EPA Data) 4-6 4.3 Soils/Tailing EP-Toxicity Data (EPA Data) 4-7 4.4 Summary of Waste Rock Pile Geochemistry and Other Parameters, California Gulch and Stray Horse Gulch (ES Data) 4-10 4.5 Summary of Geochemistry and other Parameters for Soils and Sediments in California and Stray Horse Gulch (ES Data) 4-14 4.6 Analysis of Soils Samples from Leadville, Colorado (EPA Data) 4-16 5.1 Summary of PEA Monitoring Well Construction Data 5-7 5.2 Summary of Existing Well Construction Data 5-9 5.3 Private Wells Currently in Use 5-11 5.4 Yak Tunnel/California Gulch Summary of Ground Water Sampling Results (mg/1) 5-19 5.5 Federal and State Water Quality Standards 5-24 5.6 Summary of Private Well Sampled by EPA 5-28 5.7 Summary of results from Private Wells Sampled by ES 5-31 6.1 Arkansas River Basin Affected by Metal Mine Drainage 6-10 6.2 Water Quality Data from STORET on the Arkansas River from Leadville to Near Canon City 6-12 6.3 EPA and Es Sampling Location Descriptions for California Gulch and its Tributaries 6-16 6.4 EPA Surface Water Data Summary 6-19 6.5 Federal and State Water Quality Standards 6-28 6.6 EPA Surface Water Data Summary 6-34 6.7 Total Cadmium Loading Values from EPA Data 6-36 6.8 Total Copper Loading Values from EPA Data 6-37 6.9 Total Lead Loading Values from EPA Data 6-38 6.10 Total Zinc Loading Values from EPA Data 6-39 6.11 Total Metals in the Upper Arkansas River 6-70 7.1 Concentrations of Metals (mg/kg) from Invertebrates taken from the Arkansas River and Tributaries during May and October, 1985 7-8 7.2 Concentrations of Metals (mg/kg) from Sediment taken from the Arkansas River and Tributaries during October, 1985 7-9 7.3 Number of Aquatic Macroinvertebrates per Square Meter Collected from the Arkansas River and Associated Tributaries in 1985 (ES Data) 7-12 7.4 Habitat Description of Fish Sampling Stations 7-14 7.5 Fish Collected from the Arkansas River and Tributaries during September, 1985 7-16 7.6 Fish Collected from the Arkansas River and Tributaries during October, 1985 7-17 7.7 Maximum Allowable Concentrations (mg/1) for Specific Metals based on Toxicity Data 7-24 7.8 Acutely and Chronically Toxic Concentrations of Lead to Trout 7-26 7.9 Acutely and Chronically Toxic Concentrations of Copper to Trout 7-28 7.10 Acutely and Chronically Toxic Concentrations of Zinc to Trout 7-32 7.11 Acutely and Chronically Toxic Concentrations of Cadmium to Trout 7-36 7.12 Means and Ranges of Concentrations (mg/1) of Selected Metals in Water of the Arkansas River with Concentrations above EPA Criteria Levels Noted 7-38 8.1 Ranges of Total Metal Concentrations in Reference Locations, Contaminated Sites, "Normal" Levels, Regulatory Limits, and Known Toxic Levels 8-7 8.2 Arkansas River Valley Total Soil Metals and pH 8-17 8.3 Arkansas River Valley Plant-Available Metals 8-20 8.4 Vertical Distribution of Mean Total and Plant-Available Metal Concentrations in the Soil Profile-Arkansas River Valley 8-33 9.1 Summary of Metals Concentrations in Plant Tissues 9-4 9.2 Summary of Plant Cover Data for Irrigated Pastures 9-14 9.3 Plant Production and Percent Utilization 9-16 9.4 Summary of Plant Tissue, Cover and Production Data 9-17 10.1 Selected Toxic Composition of Tailings Pond and Dust Samples 10-4 10.2 Particle Size Analysis of Mine Tailings in California Gulch 10-6 10.3 Comparison of Dust Constituents (Percent of Metals Analyzed) 10-8 11.1 Mining Wastes 11-4 11.2 Ground Water 11-7 11.3 Surface-Water 11-8 11.4 Aquatic Biota, Soils and Vegetation, and Air Quality 11-11 LIST OF FIGURES Number Title 2.1 Location Map 2.2 Geographical Features and Outline of Productive Area, Leadville District, Colorado 2-3 2.3 Mine Wastes and Slag Piles in and Near the California Gulch Drainage Area 2-5 2.4 Precipitation 2-16 3.1 View of Leadville from Carbonate Hill 3-3 3.2 Carbonate Hill 3-4 3.3 Smelters with Mines Near Leadville Looking West 3-5 3.4 Plan View of Yak Tunnel 3-7 3.5 Location of Tailings Ponds 3-13 3.6 Mining/Process Schematic 3-16 3.7 Principal Faults and Areas of Principal Ore Bodies 3-21 3.8 Bedrock Geology Map 3-22 4.1 Waste Pile and Soil/Sediment Sample Locations- Stray Horse and California Gulches 4-2 5.1 Elevation of Potentiometrie Surface, 1944 5-4 5.2 Monitoring Well Location Map 5-6 5.3 private Wells Location Map 5-8 5.4 Surface Flow and Ground Water Level 5-14 5.5 Dissolved Cadmium Concentration 5-15 5.6 Sulfate Concentration 5-16 6.1 Location Map 6-3 6.2 Fryingpan-Arkansas Project Map 6-7 6.3 EPA Surface Water Sampling Map 6-18 6.4 Dissolved Zinc in California Gulch 6-30 6.5 Dissolved Zinc in California Gulch 6-31 6.6 Total Cadmium in California Gulch 6-32 6.7 Dissolved Cadmium in California Gulch 6-33 6.8 Cadmium Mass Loadings in California Gulch 6-40 6.9 Zinc Mass Loadings in California Gulch 6-41 6.10 Surface Water Sampling Locations along California Gulch 6-43 6.11 Surface Water Sampling Locations along the Arkansas River 6-44 6.12 California Gulch Reaches 6-47 6.13 Arkansas River Reaches 6-48 6.14 Cadmium in California Gulch (May, 1985) 6-49 6.15 Cadmium in California Gulch (June, 1985) 6-50 6.16 Cadmium in California Gulch (August, 1985) 6-51 6.17 Copper in California Gulch (May, 1985) 6-52 6.18 Copper in California Gulch (June, 1985) 6-53 6.19 Copper in California Gulch (August, 1985) 6-54 6.20 Lead in California Gulch (May, 1985) 6-55 6.21 Lead in California Gulch (June, 1985) 6-56 6.22 Lead in California Gulch (August, 1985) 6-57 6.23 Zinc in California
Load more

Recommended publications
  • Explanation of Significant Differences, Residential Populated Areas, OU 9
    1118478-RS SDMS <f^',,^^'°«'^^^ ^%:, UNITED STATES ENVIRONMENTAL PROTECTION AGENCY REGIONS 1595 Wynkoop Street » ^^^^^ds'^' DENVER, CO 80202-1129 %'"K., ..„>,.rt.c'-"~PRCi^^ ^ Ptione 800.227.8917 tittp://www.epa.gov/region08 Explanation of Significant Differences Residential Populated Areas, Operable Unit 9 California Gulch Superfund Site Lake County, CO September 2009 Explanation of SigniHcant Differences Residential and Commercial Populated Areas, Operable Unit 9 California Gulch Superfund Site, Lake County, CO September 2009 1. Introduction This Explanation of Significant Differences (ESD) presents the details of an addition to the remedy selected in the September 2, 1999 Record of Decision (ROD) for Residential Populated Areas, Operable Unit 9 (0U9), ofthe California Gulch Superfund Site (Site) in Lake County, CO. Operable Unit 9 includes those portions ofthe Site where the land use is residential or that are currently zoned as residential/populated areas and as low-density residential areas. Future land use of 0U9 is expected to continue to be residential. This ESD, prepared in accordance with Section 117(c) ofthe Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) and with Part 300, Section 435(c)(2)(i) of Title 40 ofthe Code of Federal Regulations, 40 CFR 300.435(c)(2)(i), documents significant differences to the ROD. This ESD documents the decision to require institutional controls for 17 mine waste piles within 0U9. These mine waste piles have soils at the surface that are under the 3500 mg/Kg lead residential action level but may have lead contamination at depth that exceeds the residential lead action level. This ESD does not change or alter any element ofthe Lake County Community Health Program (LCCHP).
    [Show full text]
  • Federal Register/Vol. 66, No. 99/Tuesday, May 22, 2001/Rules
    28106 Federal Register / Vol. 66, No. 99 / Tuesday, May 22, 2001 / Rules and Regulations Authority: 33 U.S.C. 1321(c)(2); 42 U.S.C. DATES: This ‘‘direct final’’ action will be 1. Yak Tunnel/Water Treatment Plant. 9601–9657; E.O. 12777, 56 FR 54757, 3 CFR, effective July 23, 2001 unless EPA 2. Malta Gulch Tailing Impoundments 1991 Comp.; p. 351; E.O. 12580, 52 FR 2923, receives significant adverse or critical and Lower Malta Gulch Fluvial Tailing. 3 CFR, 1987 Comp. p. 193. comments by June 21, 2001. If adverse 3. D&RG Slag piles and Railroad Yard/ Appendix B—[Amended] comments are received, EPA will Easement. publish a timely withdrawal of the 4. Upper California Gulch. 2. Table 1 of Appendix B to part 300 direct final rule in the Federal Register 5. Asarco Smelter sites/Slag/Mill is amended under Salem Acres informing the public that the rule will sites. Superfund Site by removing the ‘‘Salem not take effect. 6. Starr Ditch/Stray Horse Gulch/ Acres Superfund Site, Salem, Lower Evans Gulch/Penrose Mine Waste Massachusetts’’. ADDRESSES: Comments may be mailed to Rebecca Thomas, Remedial Project Pile. [FR Doc. 01–12709 Filed 5–21–01; 8:45 am] Manager, Environmental Protection 7. Apache Tailing Impoundments. BILLING CODE 6560–50–P 8. Lower California Gulch. Agency, Region 8, Mail Code 8EPR-SR, 9. Residential and Commercial 999 18th Street, Suite 300, Denver, CO Populated Areas. ENVIRONMENTAL PROTECTION 80202. Telephone: (303) 312–6552. 10. Oregon Gulch. Information Repositories: AGENCY 11. Arkansas River Valley Floodplain. Comprehensive information on the 12.
    [Show full text]
  • Restoration Plan and Environmental Assessment for the Upper Arkansas
    Chapter 2 Upper Arkansas River Watershed Restoration Plan and Environmental Purpose and Need for Restoration Assessment Th is chapter describes the purpose and need for restoration to address losses to natural resources caused by the releases of hazardous substances at and from the Site. Th e Trustees determined in their preliminary estimate of damages that groundwater, aquatic, and terrestrial resources have been injured; that the locations of injury include California Gulch, and aquatic resources of the upper Arkansas River and terrestrial resources associated with the 500-year fl oodplain of the upper Arkansas River; and that restoration is required to compensate the public for these injuries (Industrial Economics, 2006). Th is RP focuses on projects that will address injuries to natural resources through the restoration of similar resources in locations within the upper Arkansas River Basin (Figure 2.1). 2.1 Summary of Release History and Resulting Public Losses Th e Site extends over a large area including more than 15 square miles in and around the town of Leadville, Colorado. Extensive historic mining activities in and around Leadville generated more than 2,000 on-site waste rock piles and resulted in past and ongoing releases of heavy metals and acid mine drainage into California Gulch and, subsequently, to the upper Arkansas River Basin. In particular, the Yak Tunnel, which was constructed to dewater mines in the area, was a signifi cant source of contamination to California Gulch from the time of its construction in 1895 until the Yak Tunnel Water Treatment Plant began operation in 1992. Before construction of the treatment plant, more than 200 tons of metals were discharged into California Gulch each year by the Yak Tunnel (Industrial Economics, 2006).
    [Show full text]
  • Toxicological Profile for Lead
    TOXICOLOGICAL PROFILE FOR LEAD U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry August 2007 LEAD ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. LEAD iii UPDATE STATEMENT A Toxicological Profile for Lead, Draft for Public Comment was released in September 2005. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology and Environmental Medicine/Applied Toxicology Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 LEAD iv This page is intentionally blank. v FOREWORD This toxicological profile is prepared in accordance with guidelines developed by the Agency for Toxic Substances and Disease Registry (ATSDR) and the Environmental Protection Agency (EPA). The original guidelines were published in the Federal Register on April 17, 1987. Each profile will be revised and republished as necessary. The ATSDR toxicological profile succinctly characterizes the toxicologic and adverse health effects information for the hazardous substance described therein. Each peer-reviewed profile identifies and reviews the key literature that describes a hazardous substance's toxicologic properties. Other pertinent literature is also presented, but is described in less detail than the key studies. The profile is not intended to be an exhaustive document; however, more comprehensive sources of specialty information are referenced. The focus of the profiles is on health and toxicologic information; therefore, each toxicological profile begins with a public health statement that describes, in nontechnical language, a substance's relevant toxicological properties.
    [Show full text]
  • Mapping Acid-Generating Minerals at the California Gulch Supcrfund Site in L.Cadvillc, Colorado Using Imaging Spectroscopy
    Mapping Acid-Generating Minerals at the California Gulch Supcrfund Site in l.cadvillc, Colorado using Imaging Spectroscopy Gregg A, Swayze, Roger N. Clark, Ronald M. Pearson*, and K. Eric 1.ivo lJ.S. Geological Survey, Box 25046 MS964 DFC Denver, CO 80225 *U.S. Bureau of Reclamation, P.O. Box 25007 D-8321 DFC, Denver, CO 80225 Introduction The Leadville mining district, located at an elevation of 3000 m in the Central Colorado Rockies, has been mined for gold, silver, lead and zinc for over 100 years. ‘l’his activity has resulted in waste rock and tailings, rich in pyrite and other sulfides, being dispersed over a 30 kn~2 area including the city of I,eadville. Oxidation of these sulfides releases lead, arsenic, cadmium, silver, and zinc into snowmelt and thunderstorm runoff, which drains into the Arkansas River, a main source of water for Front Range urban centers and agricultural communities. The U.S. Environmental Protection Agency (WA), U.S. Bureau of Reclamation (US13R), contractors, and responsible parties are remediating the mined areas to curtail further releases of heavy metals into various drainage tributaries of the Arkansas River. The USBRS’ current work is directed toward characterizing and pinpointing localized sources of acid mine drainage and contamination from waste rock piles found throughout an area of 900 hectares. Method The sulfide oxidation process is biologically driven along complex chemical pathways with feedback reactions that enhance the speed and magnitude of oxidation (Nordstron~, 1982). Release of heavy metals is facilitated by sulfide oxidation, since many of the sulfides contain the heavy metals (e.g.
    [Show full text]
  • Hydrologic Characterization and Remediation of the Leadville Mine Dr
    HYDROGEOLOGIC CHARACTERIZATION OF GROUND WATERS, MINE POOLS AND THE LEADVILLE MINE DRAINAGE TUNNEL, LEADVILLE, COLORADO1 Michael Wireman2 Jord Gertson2 Dr. Mark Williams2 Abstract. The 3385 meter long Leadville Mine Drain Tunnel (LMDT) was completed in 1952 to create a free-draining tunnel to dewater existing and future mine workings in the Leadville Mining District in the Sawatch Mountains of central Colorado. Since 1952 mining has been mostly discontinued in the Leadville district and the physical condition of the LMDT, which discharges approximately 82 l/s, has deteriorated. Roof falls have resulted in blockages which can cause water to pool up, increasing the hydraulic head and presenting a potential blowout problem. Using its’ authority under CERCLA, the US EPA is planning to implement a number of hydraulic and source control elements which are designed to contain and control mine pool water. To support this work the US EPA has completed a rigorous hydrogeologic characterization aimed at developing a sound conceptual understanding of the hydrologic, geologic and geochemical conditions that control inflow of ground water to the underground workings associated with the LMDT and the outflow of mine water from these workings. The investigations discussed here included hydrogeologic mapping, interpretation of water chemistry data and isotopic tracer analysis. The results of this investigation indicate that the LMDT drains only a small volume of mine pool water and a very large volume of regional bedrock and adjacent alluvial ground water. These understandings have been used to design a containment system will be used to control and manage the ground water intercepted by the LMDT and the mine pool(s) that are connected to the LMDT.
    [Show full text]
  • Monitoring the Extent of Contamination from Acid Mine Drainage in the Iberian Pyrite Belt (SW Spain) Using Hyperspectral Imagery
    Remote Sens. 2011, 3, 2166-2186; doi:10.3390/rs3102166 OPEN ACCESS Remote Sensing ISSN 2072-4292 www.mdpi.com/journal/remotesensing Article Monitoring the Extent of Contamination from Acid Mine Drainage in the Iberian Pyrite Belt (SW Spain) Using Hyperspectral Imagery Asuncion Riaza 1,*, Jorge Buzzi 1, Eduardo García-Meléndez 2, Veronique Carrère 3 and Andreas Müller 4 1 Geological Survey of Spain (IGME), La Calera 1, 28760 Tres Cantos, E-28003 Madrid, Spain; E-Mail: [email protected] 2 Facultad de Ciencias Ambientales, Universidad de León, Campus de Vegazana s/n, E-24071 León, Spain; E-Mail: [email protected] 3 Laboratoire de Planétologie et Géodynamique de Nantes, 2 rue de la Houssinière BP 92208, 44322 Nantes Cedex 3, France; E-Mail: [email protected] 4 Remote Sensing Data Centre, German Aerospace Research (DLR), P.O. Box 1116, D-82234 Wessling, Germany; E-Mail: [email protected] * Author to whom correspondence should be addressed; E-Mail: [email protected]; Tel.: +34-91-728-7249; Fax: +34-91-728-7202. Received: 25 July 2011; in revised form: 6 September 2011 / Accepted: 2 October 2011 / Published: 14 October 2011 Abstract: Monitoring mine waste from sulfide deposits by hyperspectral remote sensing can be used to predict surface water quality by quantitatively estimating acid drainage and metal contamination on a yearly basis. In addition, analysis of the mineralogy of surface crusts rich in soluble salts can provide a record of annual humidity and temperature. In fact, temporal monitoring of salt efflorescence from mine wastes at a mine site in the Iberian Pyrite Belt (Huelva, Spain) has been achieved using hyperspectral airborne Hymap data.
    [Show full text]
  • Restoration Plan and Environmental Assessment for the Upper Arkansas Ri Ve R Watershed Dated January 7, 2010
    Restoration Plan and Environmental Assessment for the April 14, 2010 Upper Arkansas River Watershed PREPARED FOR PREPARED BY U.S. Department of the Interior State of Colorado Stratus Consulting Inc. U.S. Fish and Wildlife Service Department of Natural Resources PO Box 4059 U.S. Bureau of Land Management Department of Public Health and Environment Boulder, CO 80306-4059 U.S. Bureau of Reclamation Department of Law 303-381-8000 Contact: Diana R. Lane, PhD or Allison Ebbets, MS List of Authorities and Responsible Agency Point of Contact Natural Resource Trustees: • U.S. Department of the Interior - U.S. Fish and Wildlife Service - U.S. Bureau of Land Management - U.S. Bureau of Reclamation • State of Colorado - Department of Natural Resources - Department of Public Health and Environment - Department of Law Legal Authority: • Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (as amended), 42 U.S.C. § 9601, et. seq. • Federal Water Pollution Control Act (Clean Water Act) (as amended), 33 U.S.C. § 1251, et. seq. • Natural Resource Damage Assessment Regulation, 43 C.F.R. Part 11 Lead Federal Agency for Restoration Plan: • U.S. Department of the Interior (Region 6, U.S. Fish and Wildlife Service) Lead Federal Agency for Environmental Assessment: • U.S. Department of the Interior (Region 6, U.S. Fish and Wildlife Service) Participating State Agencies: • Colorado Department of Natural Resources - Division of Wildlife, Division of Reclamation Mining and Safety • Colorado Department of Public Health and Environment • Colorado Department of Law Point of Contact: Laura Archuleta U.S. Fish and Wildlife Service, Saguache Field Offi ce 46525 Highway 114 Saguache, CO 81149 719-655-6121 SC11902 Upper Arkansas River Watershed Restoration Plan and Environmental Contents Assessment Executive Summary .......................................................................................................................................................
    [Show full text]
  • Associating Soil Lead with Adverse Effects on Songbirds in the Southeast Missouri Mining District
    Associating Soil Lead with Adverse Effects on Songbirds in the Southeast Missouri Mining District Prepared for: David Mosby U.S. Fish and Wildlife Service 101 Park DeVille Drive, Suite A Columbia, MO 65203 Associating Soil Lead with Adverse Effects on Songbirds in the Southeast Missouri Mining District Prepared for: David Mosby U.S. Fish and Wildlife Service 101 Park DeVille Drive, Suite A Columbia, MO 65203 Prepared by: Stratus Consulting Inc. PO Box 4059 Boulder, CO 80306-4059 303-381-8000 1920 L St. NW, Suite 420 Washington, DC 20036 Contacts: Jamie Holmes Joshua Lipton July 28, 2014 SC13255 Contents List of Figures .............................................................................................................................. vii List of Tables ................................................................................................................................ ix List of Acronyms and Abbreviations ......................................................................................... xi Chapter 1 Introduction ........................................................................................................ 1-1 Chapter 2 Effects of Lead on Birds .................................................................................... 2-1 Chapter 3 Relating Soil Lead to Avian Toxicity ............................................................... 3-1 3.1 Coeur d’Alene Basin, Idaho ................................................................................. 3-1 3.2 SEMO .................................................................................................................
    [Show full text]
  • Efficacy of Heavy-Metal Capture by Clinoptilolite-Rich Rocks from Heavy-Metal-Polluted Water in Five Drainages in Colorado
    U.S. DEPARTMENT OF THE INTERIOR U.S. GEOLOGICAL SURVEY Efficacy of heavy-metal capture by clinoptilolite-rich rocks from heavy-metal-polluted water in five drainages in Colorado by George A. Desborougb1 Open-File Report 94-140 This report is preliminary and has not been reviewed for conformity with U.S. Geological Survey editorial standards or with the North American Stratigraphic Code. Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. 'Denver, Colorado 1994 CONTENTS Page Abstract .................................................. 1 Introduction ................................................ 1 Characteristics of clinoptilolite-rich rocks .............................. 2 Methods of study ............................................ 2 Argo tunnel, Idaho Springs ...................................... 2 California Gulch, Leadville ...................................... 6 Mineral Creek, San Juan County ................................... 6 Rawley tunnel, Bonanza ....................................... 10 Wellington mine drain, Breckenridge ............................... 10 Related field studies and significance of calcium in stream water ............... 13 Cobalt .............................................. 13 Calcium and the "Class 1 Aquatic Life" standards ................... 14 Summary ................................................ 14 Acknowledgments ........................................... 15 References cited ...........................................
    [Show full text]
  • 6560-50-P Environmental Protection
    This document is scheduled to be published in the Federal Register on 10/24/2014 and available online at http://federalregister.gov/a/2014-25286, and on FDsys.gov Rio Grande Western Railroad Company Slag Piles/Railroad Easement/Railroad Yard; Operable Unit 6, Starr Ditch/Penrose Dump/Stray Horse Gulch/Evans Gulch; Operable Unit 11, the Arkansas River Floodplain; and Operable Unit 12 (OU12), Site-wide Water Quality will remain on the NPL and is/are not being considered for deletion as part of this action. The EPA and the State of Colorado, through the Colorado Department of Public Health and the Environment, have determined that all appropriate response actions under CERCLA, other than operation, maintenance, and five-year reviews, have been completed. However, the deletion of these parcels does not preclude future actions under Superfund. DATES: This action is effective [Insert date of publication in the Federal Register]. ADDRESSES: EPA has established a docket for this action under Docket Identification No. EPA-HQ-SFUND-1983-0002. All documents in the docket are listed on the http://www.regulations.gov Web site. Although listed in the index, some information is not publicly available, i.e., Confidential Business Information or other information whose disclosure is restricted by statute. Certain other material, such as copyrighted material, is not placed on the Internet and will be publicly available only in hard copy form. Publicly available docket materials are available either electronically in http://www.regulations.gov or in hard copy: o By calling EPA Region 8 at (303) 312-7279 and leaving a message, or o At the Lake County Public Library, 1115 Harrison Avenue, Leadville, CO 80461, (719) 486-0569, Monday and Wednesday from 10:00 am – 8:00 pm, Tuesday and Thursday from 10:00 am – 5:00 pm, and Friday and Saturday 1:00 pm – 5:00 pm.
    [Show full text]
  • Simulation of Metals Transport and Toxicity at a Mine-Impacted Watershed: California Gulch, Colorado
    Environ. Sci. Technol. 2006, 40, 6996-7004 cadmium (Cd), copper (Cu), and zinc (Zn) (11). In response Simulation of Metals Transport and to rainfall, surface erosion, and subsequent transport, metals Toxicity at a Mine-Impacted are exported from the gulch and harm water quality and habitat in downstream areas, particularly at the confluence Watershed: California Gulch, with the Arkansas River (2, 12). Efforts to remediate the gulch began in 1983 when the U.S. Environmental Protection Colorado Agency (USEPA) placed the site on the National Priority List for the Comprehensive Environmental Response, Compen- MARK L. VELLEUX,*,² PIERRE Y. JULIEN,² sation, and Liability Act (CERCLA) (Superfund) (2). ROSALIA ROJAS-SANCHEZ,² The objectives of this research were to (1) calibrate and WILLIAM H. CLEMENTS,³ AND validate a watershed model to simulate the transport and JOHN F. ENGLAND, JR.§ fate of metals at California Gulch, and (2) demonstrate how Department of Civil Engineering and Department of Fishery the model can be used to assess the extent that individual and Wildlife Biology, Colorado State University, Fort Collins, contaminated areas contribute to overall impairments. To Colorado, 80523, and Bureau of Reclamation, Denver, meet these objectives, the Two-dimensional, Runoff, Erosion, Colorado, 80225 and Export (TREX) watershed model (13) was applied to California Gulch. Runoff, sediment transport, and metals transport were simulated using TREX for a June, 2003 calibration event and a September, 2003 validation event. The transport and toxicity of metals at the California Once calibrated and validated, the model was used to Gulch, Colorado mine-impacted watershed were simulated simulate metals transport and toxicity, and the contributions with a spatially distributed watershed model.
    [Show full text]