Acid Mine Drainage: Innovative Treatment Technologies
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Short Rotation Intensive Culture of Willow, Spent Mushroom Substrate
plants Article Short Rotation Intensive Culture of Willow, Spent Mushroom Substrate and Ramial Chipped Wood for Bioremediation of a Contaminated Site Used for Land Farming Activities of a Former Petrochemical Plant Maxime Fortin Faubert 1 , Mohamed Hijri 1,2 and Michel Labrecque 1,* 1 Institut de Recherche en biologie végétale, Université de Montréal and Jardin Botanique de Montréal, 4101 Sherbrooke East, Montréal, QC H1X 2B2, Canada; [email protected] (M.F.F.); [email protected] (M.H.) 2 African Genome Center, Mohammed VI Polytechnic University (UM6P), Lot 660, Hay Moulay Rachid, Ben Guerir 43150, Morocco * Correspondence: [email protected]; Tel.: +1-514-978-1862 Abstract: The aim of this study was to investigate the bioremediation impacts of willows grown in short rotation intensive culture (SRIC) and supplemented or not with spent mushroom substrate (SMS) and ramial chipped wood (RCW). Results did not show that SMS significantly improved either biomass production or phytoremediation efficiency. After the three growing seasons, RCW- amended S. miyabeana accumulated significantly more Zn in the shoots, and greater increases of some PAHs were found in the soil of RCW-amended plots than in the soil of the two other ground Citation: Fortin Faubert, M.; Hijri, cover treatments’ plots. Significantly higher Cd concentrations were found in the shoots of cultivar M.; Labrecque, M. Short Rotation ‘SX61’. The results suggest that ‘SX61’ have reduced the natural attenuation of C10-C50 that occurred Intensive Culture of Willow, Spent in the unvegetated control plots. The presence of willows also tended to increase the total soil Mushroom Substrate and Ramial concentrations of PCBs. -
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). -
The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils
Final Report FHWA/IN/JTRP-2004/17 The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils by Mark S. McClain Graduate Research Assistant and M. Katherine Banks Professor School of Civil Engineering and A. Paul Schwab Department of Agronomy Purdue University Joint Transportation Research Program Project No. C-36-68T File No. 4-7-20 SPR-2624 Prepared in Cooperation with the Indiana Department of Transportation and the U.S. Department of Transportation Federal Highway Administration The contents of this report reflect the views of the author who is responsible for the facts and the accuracy of the data presented herein. The contents do not necessarily reflect the official views or policies of the Indiana Department of Transportation or the Fedeeral Highway Administration at the time of publication. This report does not constitute a standard, specification, or regulation. Purdue University West Lafayette, Indiana 47907 October 2004 TECHNICAL Summary Technology Transfer and Project Implementation Information INDOT Research TRB Subject Code: 23-8 Ecological Abatement October 2004 Publication No.: FHWA/IN/JTRP-2004/17, SPR-2624 Final Report The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils Introduction Soils can be severely impacted by transportation- Phytoremediation uses plants to degrade, extract, related activities including highway construction, contain, or immobilize contaminants from soil and renovations, maintenance, and accidental spills. water. Phytoremediation is an innovative, cost- Reclamation or remediation of soils contaminated effective alternative to more conventional treatment by salts, solvents, paints, petroleum, and metals methods used in the remediation of hazardous may be necessary to comply with current waste sites. -
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. -
Phytoremediation Potential of Fast-Growing Energy Plants: Challenges and Perspectives – a Review
Pol. J. Environ. Stud. Vol. 29, No. 1 (2020), 505-516 DOI: 10.15244/pjoes/101621 ONLINE PUBLICATION DATE: 2019-09-10 Review Phytoremediation Potential of Fast-Growing Energy Plants: Challenges and Perspectives – a Review Martin Hauptvogl1*, Marián Kotrla2, Martin Prčík1, Žaneta Pauková3, Marián Kováčik4, Tomáš Lošák5 1Department of Environmental Management, Slovak University of Agriculture in Nitra, Slovakia 2Department of Regional Bioenergetics, Slovak University of Agriculture in Nitra, Slovakia 3Department of Regional Bioenergetics , Slovak University of Agriculture in Nitra, Slovakia 4Department of EU Policies, Slovak University of Agriculture in Nitra, Slovakia 5Department of Environmentalistics and Natural Resources, Mendel University in Brno, Czech Republic Received: 23 July 2018 Accepted: 15 December 2018 Abstract Contamination of soil by toxic elements is a global issue of growing importance due to the increased anthropogenic impact on the natural environment. Conventional methods of soil decontamination possess disadvantages in forms of environmental and financial burdens. This fact leads to the search for alternative approaches of remediation of contaminated sites. One such approach includes phytoremediation. Phytoremediation advantages consist of low costs and small environmental impact. Several fast-growing energy plant species are suitable for phytoremediation purposes. Our article focuses on the phytoremediation potential of energy woody crops of Salix and Populus, and energy grasses Miscanthus and Arundo, which are grown primarily for biomass production. This approach links the environmentally friendly and economically less demanding remediation approach with the production of the local sustainable form of energy that decreases dependency on external energy supplies. Energy plants are able to provide high biomass yields in a short period of time, they are resistant against abiotic stress conditions and have the ability to accumulate toxic substances, thus helping to restore the desirable soil properties. -
Passive Treatment Systems for Acid Mine Drainage
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln U.S. Bureau of Land Management Papers U.S. Department of the Interior 2003 Passive Treatment Systems for Acid Mine Drainage K. L. Ford National Science and Technology Center Follow this and additional works at: https://digitalcommons.unl.edu/usblmpub Part of the Environmental Sciences Commons Ford, K. L., "Passive Treatment Systems for Acid Mine Drainage" (2003). U.S. Bureau of Land Management Papers. 19. https://digitalcommons.unl.edu/usblmpub/19 This Article is brought to you for free and open access by the U.S. Department of the Interior at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in U.S. Bureau of Land Management Papers by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Technical Note 409 April 2003 U.S. Department of the Interior • Bureau of Land Management Production services provided by: Information and Communications Staff Publishing Staff (303-236-6547) Janine Koselak: Layout and Design Linda Hill: Editing Lee Barkow, Director National Science & Technology Center P.O. Box 25047 Denver, Colorado 80225-0047 The Bureau of Land Management’s National Science and Technology Center supports other BLM offices by providing a broad spectrum of services in areas such as physical, biological, and social science assessments; architecture and engineering support; library assistance; mapping science; photo imaging; geographic information systems applications; and publications support. Available at: www.blm.gov/nstc/library/techno2.htm Technical Note 409 BLM/ST/ST-02/001+3596 Technical Note 409 April 2003 by: K.L. Ford Bureau of Land Management National Science and Technology Center PASSIVE TREATMENT SYSTEMS FOR ACID MINE DRAINAGE SUGGESTED CITATION: Ford, K.L. -
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). -
Acid Mine Drainage: the Case of the Lafayette Mine, Rapu Rapu (Philippines)
Acid Mine Drainage: the case of the Lafayette mine, Rapu Rapu (Philippines) Janet Cotter & Kevin Brigden Greenpeace Research Laboratories Technical Note 09/2006 October 2006 Summary Acid streams resulting from mining activities from certain types of mineral deposits such as those at Rapu Rapu in the Philippines are highly toxic to the aquatic environment. The extreme acidity is harmful to most aquatic life and, even after neutralisation, the precipitate formed continues to affect aquatic organisms. Toxic elements, such as copper, cadmium and zinc are often associated with acidic mine drainage (AMD), contributing substantially to its devastating ecological effects. An outflow of acid mine drainage from the Lafayette mines in Rapu Rapu into the sea would undoubtedly affect local marine life. It could silt up corals causing coral mortality and cause the depletion of bottom dwelling organisms, which would have domino effects up the ecosystem, reducing the food sources available for animals at the top of the marine food chain, e.g. sharks. The toxic elements could also be taken up into the marine food chain, causing long term health effects to marine life, and some may bioaccumulate up the food chain. Although AMD can be treated at the mine to some degree, e.g. by neutralisation at source, this process is never fully effective. Furthermore, accidents with the treatment system are inevitable. Earthquakes, tropical storms and typhoons occur regularly in the Philippines. These could cause tailings dams to break or cause flooding, sending a large pulse of either acid mine drainage or the precipitate downstream, which could have devastating effects on corals and marine life. -
Interest Increases in Using Plants for Environmental Remediation
Specialty Plant Products Interest Increases in Using Plants For Environmental Remediation In an effort to meet environmental regulations of the last three decades, environmental remediation has developed into a multibillion dollar industry. The high cost of many traditional methods is causing many organizations to look to lower cost alternatives. Bioremediation is a commercial remediation technology with a growing market and continuing research. Phytoremediation is another potential low-cost technology that is currently being investigated for many remediation applications. Health and environmental risks of pollution have become Table 14--Soil remediation technologies more apparent throughout the world over the past several Method In situ Ex situ decades. Air, water, and soil contaminants can include nu- merous organic and inorganic substances, such as munici- Physical Soil vapor extraction Landfilling pal waste and sewage, various gaseous emissions, fertiliz- Thermally enhanced Incineration ers, pesticides, chemicals, heavy metals, and radionuclides soil vapor extraction Thermal desorption (radioactive substances). Contaminants can cause land and Containment systems Soil vapor extraction groundwater to be unusable. In addition, animals and in- and barriers sects may come in contact with a contaminant, thus intro- ducing a toxic substance into the food chain. Because of in- Chemical Soil flushing Soil washing creased public awareness and concern, environmental Solidification Solidification regulations have been created to not only prevent -
REFERENCE GUIDE to Treatment Technologies for Mining-Influenced Water
REFERENCE GUIDE to Treatment Technologies for Mining-Influenced Water March 2014 U.S. Environmental Protection Agency Office of Superfund Remediation and Technology Innovation EPA 542-R-14-001 Contents Contents .......................................................................................................................................... 2 Acronyms and Abbreviations ......................................................................................................... 5 Notice and Disclaimer..................................................................................................................... 7 Introduction ..................................................................................................................................... 8 Methodology ................................................................................................................................... 9 Passive Technologies Technology: Anoxic Limestone Drains ........................................................................................ 11 Technology: Successive Alkalinity Producing Systems (SAPS).................................................. 16 Technology: Aluminator© ............................................................................................................ 19 Technology: Constructed Wetlands .............................................................................................. 23 Technology: Biochemical Reactors ............................................................................................. -
Alkalinity and Acidity in Mine Drainage
Proceedings America Society of Mining and Reclamation, 2004 ACIDITY AND ALKALINITY IN MINE DRAINAGE: PRACTICAL CONSIDERATIONS1 Charles A. Cravotta III2 and Carl S. Kirby2 Abstract. In this paper, we emphasize that the Standard Method hot peroxide treatment procedure for acidity determination (hot acidity) directly measures net acidity or net alkalinity, but that more than one water-quality measure can be useful as a measure of the severity of acid mine drainage. We demonstrate that the hot acidity is related to the pH, alkalinity, and dissolved concentrations of Fe, Mn, and Al in fresh mine drainage. We show that the hot acidity accurately indicates the potential for pH to decrease to acidic values after complete oxidation of Fe and Mn, and it indicates the excess alkalinity or that required for neutralization of the sample. We show that the hot acidity method gives consistent, interpretable results on fresh or aged samples. Regional data for mine-drainage quality in Pennsylvania indicated the pH of fresh samples was predominantly acidic (pH 2.5 to 4) or near neutral (pH 6 to 7); approximately 25 percent of the samples had intermediate pH values. This bimodal frequency distribution of pH was distinctive for fully oxidized samples; oxidized samples had acidic or near-neutral pH, only. Samples that had near- neutral pH after oxidation had negative hot acidity; samples that had acidic pH after oxidation had positive hot acidity. Samples with comparable pH values had variable hot acidities owing to variations in their alkalinities and dissolved Fe, Mn, and Al concentrations. The hot acidity was comparable to net acidity computed on the basis of initial pH and concentrations of Fe, Mn, and Al minus the initial alkalinity. -
Treatment of Acid Mine Drainage: a General Review
IARJSET ISSN (Online) 2393-8021 ISSN (Print) 2394-1588 International Advanced Research Journal in Science, Engineering and Technology ISO 3297:2007 Certified Vol. 3, Issue 11, November 2016 Treatment of Acid Mine Drainage: A General Review H. L. Yadav1, A. Jamal2 Research Scholar, Department of Mining Engineering, Indian Institute of Technology, (BHU) Varanasi, India1 Faculty Member, Department of Civil Engineering, G.B.Pant Engineering College Pauri, Garhwal, UK, India1 Professor, Department of Mining Engineering, Indian Institute of Technology, (BHU) Varanasi, India2 Abstract: Acid mine drainage has severe environmental effects. These environmental effects can be devastating for living organism. The acidity of acid mine drainage destroys plants, vegetations, human and animals health, corrosion of pipes, building and building materials, Increasing degradation and contamination of aquatic resources and make water quality unsuitable for human and biota utilization. Presently treatment of mine influence water has significant challenges because of its persistent nature. The generation of acid mine drainage once initiated, can continue for decades and often long after active mining operations have ceased. Traditional treatment methods are not suitable for treatment of mining effluents. Recently, passive treatment systems have been proposed and implemented as low-cost, effective, efficient and long-term management options. This review summarizes the applications of active and passive treatment system for treatment of acid mine drainages. Keywords: Acid mine drainage, effect, active and passive treatment technology. INTRODUCTION The generation of Acidic wastewater is a natural process Sources of mine influence water that becomes accelerated and intensified by different The primary sources of mine impact water during different mining operation for coal and metals mines.