Polluting the Future
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Final Treatability Study Technical Memorandum Formosa Mine
Final Treatability Study Technical Memorandum Formosa Mine Superfund Site Douglas County, Oregon Prepared for: U.S. Environmental Protection Agency Region 10 1200 Sixth Avenue, Suite 900 Seattle, Washington 98101 Prepared by: CDM Federal Programs 1218 Third Avenue, Suite 1100 Seattle, Washington 98101 Parametrix 411 108th Avenue NE, Suite 100 Bellevue, Washington 98004 R‐10 AES (SMALL BUSINESS) CONTRACT NO. 68‐S7‐03‐04 June 12, 2014 Task Order No. 047B Final Treatability Study Technical Memorandum Formosa Mine Superfund Site Douglas County, Oregon R‐10 AES (SMALL BUSINESS) CONTRACT NO. 68‐S7‐03‐04 Task Order No. 047B 06/12/14 Prepared by: Date Stephen Dent, Ph.D. CDM Smith Project Scientist1 06/12/14 Reviewed by: Date Roger Olsen, Ph.D. CDM Smith Technical Reviewer 06/12/14 Reviewed by: Date David J. Reisman CDM Smith Technical Consultant 06/12/14 Approved by: Date Michael C. Allen, P.E. CDM Smith Project Manager Distribution List (via email) Chris Cora Remedial Project Manager EPA Region 10 Seattle, WA i This page intentionally left blank ii Table of Contents Section 1 Introduction .................................................................................................................................. 1‐1 1.1 Site Description and Background ........................................................................................................................ 1‐1 1.2 Purpose of Treatability Study ............................................................................................................................... 1‐2 -
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). -
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. -
Pacific Division Meeting Field Trip Guide for the Blue Ledge Mine
Pacific Division Meeting Field Trip Guide for the Blue Ledge Mine, Siskiyou County, California Field Trip Leaders: Bill Elliott (Dept. of Geology), Kathleen Page (Dept. of Biology), and Steve Petrovic (Dept. of Chemistry), Southern Oregon University Field trip guide written by William S. Elliott, Jr. Southern Oregon University June 12, 2005 Medford Jacksonville Phoenix Applegate Ruch Talent 99 Pompadour Bluff Ashland K L A M Mt. A Ashland T H 5 Applegate o Reservoir W 123 00’ OREGON o N 42 00’ M CALIFORNIA Joe Elliott Creek Creek O U BLUE LEDGE MINE Condrey N Mountain T A I N S 96 N Yreka 0 10 20 km Figure 1: Index map to the travel log and location of the Blue Ledge Mine in Siskiyou County, California. 2 Travel Log Below is a brief travel log that summarizes the geological and historical aspects of the route to the Blue Ledge Mine. Refer to Figure 1 for the location of the communities and routes described in the passages and Figure 2 for a regional geologic map of southwestern Oregon and northern California. Historical information is partially derived from the Southern Oregon Historical Society’s Historic Discovery Drives. The mileages provided are cumulative. 0 miles 0 km Leave the parking lot in front of the Science Building at Southern Oregon University. Travel west on Ashland Street to Mountain Avenue, then turn right heading north. At the intersection with Siskiyou Boulevard (Highway 99), turn left and head northwest toward Ashland. A few blocks beyond downtown Ashland, there are views of the southern part of the Bear Creek Valley. -
Blue Ledge Mine D
-- -- -------------------------~- '·,._ -~~~ .. :7\~:.":~-=~-;--'i}{/~::}f·:i~_:~t···· b /i:?;,·~··~;&'~Uc<//?~K .,/(Y !}/It? .Vr.'ct/G" Z),,p,,c-15/U.4,,p~.c /10cf /14,.vk/'v~ 6'/Pr a~,# &~c LEZ?c:;;c-u,"r~$A/c; ( U,c?,J.Ra~v#4~~ 5.c-V~--9~ 7A7);?!:1") • Jacksonville,Nugget ... March 2, 1979 "· ,. , . .. .... ... 11 : · ?'~rtt1llt~,,~1t-:fj/~ creek; the latter in. turn. '.em- ':"'i\'f: i 'sontetimesidescrlbed as il' cob-,,'\;"! f'. ; ,,,. plying into the east forif of the . .'' ''\. tacf vein :1 because, of . the. Copper Mining Applegate. There are eleven ·. · variation of the walls in this claims in the group, and while respect. The vein strikes with not patented, they have· all the formation whose general Continues In The been located by survey. They· dii'ection·is ten degrees east of , are given on the accompanying . 'north and also dips with ,the· map under the names of · . : ... formation, ·. the· · angle being ;' i Malone, Cooper, · L. · F. about,... fity ··:degrees .. from\',. Cooper, McVay and :Adams, · .horizontal and'the dip to the/ . ~!~.~M2f!.!?t?s~=s .. W. H. Hamilton, Brown Bear, west. In other words, the Blue'., ··· Malone, Hamilton,. L. H., Ledge-.;•and aH tlie other veins McVay, Lake, S •. G; Adams, of the district, for that matter, · The Blue Ledge Mine D. Malone,· .and . Adams. ·appear to occupy rifts In the(' ·. There is a new :wagon road up laminations · of the. schist, . the _Applegate arid up the east . which· ~~minatlons .are · like ...... · fork to within four miles off . fissures: ; in :, their · general .: ,, · The month of June wit be unearthed in the next few the Blue Ledge. -
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). -
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. -
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. -
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. -
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. -
What Can EPA Do About Abandoned Mines in California?
What Can EPA Do About Abandoned Mines in California? Debbie Schechter US EPA Region 9, Superfund Division Presented at Reclaiming the Sierra: Community Summit on Mining Impacts November 8, 2010 What Can EPA Do about Abandoned Mines in California? EPA and federal land managers have cleanup authority under CERCLA, or Superfund EPA’s Brownfields Program can provide funding and technical assistance to eligible grantees Prioritization is critical: there 47,000 abandoned mines in California 2 CERCLA Cleanup Authority CERCLA authorizes the federal government to respond to releases or threats of releases that may endanger human health or the environment Private land: EPA Public land: federal land mgmt. agency CERCLA provides for liability for responsible parties and authorizes the federal government to compel parties to clean up sites CERCLA authorizes two kinds of responses: Removals (short term) Remedial actions (at sites on the National Priorities List) Iron Mountain Mine, Redding, CA 3 Clean Water Act Authority Regulates pollutant discharges from point sources into navigable waters Designed to address industrial facilities Applies to current owners/operators Acid mine drainage is considered a point source Newton Mine, Amador County, CA 4 Bodie State Historic Park Mono County, Eastern Sierra 250,000 visitors per year Elevated levels of lead, arsenic and mercury in soils, mill tailings, indoor dust and indoor air 300,000 cy tailings pile north of town with elevated lead and mercury levels; mercury found off-site in creek and -
26Th Quarterly Literature Update
Measurement & Monitoring: 26th Quarterly Literature Update These references have been added to the literature database developed for the Measurement and Monitoring Technologies for the 21st Century (21M2) website. The searchable archive of abstracts is located at www.clu-in.org/programs/21m2/litsearch.cfm 1,4-Dioxane: The Impact of Analytical Method -- A Case Study Linton, P.J. (Blasland, Bouck, and Lee, Inc., Tampa, FL); T. Armstrong (Lockheed Martin, Bethesda, MD); J. Alonso and B. Foster (Blasland, Bouck, and Lee, Inc.). The 23rd Annual International Conference on Contaminated Soils, Sediments and Water, 15-18 October 2007, University of Massachusetts at Amherst. Northeast Regional Environmental Health Center, Univ. of Massachusetts, Amherst. Abstracts, 2007 Commercial laboratories commonly analyze for 1,4-dioxane (CAS 123-91-1) in groundwater by either EPA Method 8260 or 8270, though 1,4-dioxane is not listed for the latter method. Method 8260 generally does not achieve reporting limits that meet regulatory concentrations. Determination of 1,4-dioxane in water at low detection levels also can be accomplished using a modified approach to Method 8270 with isotope dilution. Because of time and sample volume concerns, many laboratories have begun analyzing for 1,4-dioxane using a modified Method 8260 with specific ion monitoring (SIM) GC-MS to improve the detection limits. During recent characterization sampling at a central Florida site in groundwater affected by chlorinated volatile organic compounds and 1,4-dioxane, split samples of groundwater were collected and analyzed by both Method 8270 and 8260 SIM. The difference in reported concentrations of 1,4-dioxane by the two methods was significant, sometimes by orders of magnitude.