Reactive Nitrogen in the Environment
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Riau Natural Gas Power Project ESIA Vol.5 Technical Appendices Part F
DRAFT Environmental and Social Impact Assessment Report Project Number: 50182-001 November 2018 INO: Riau Natural Gas Power Project ESIA Vol.5_Technical Appendices Part F Prepared by ESC for the Asian Development Bank The environmental and social impact assessment is a document of the project sponsor. The views expressed herein do not necessarily represent those of ADB’s Board of Directors, Management, or staff, and may be preliminary in nature. Your attention is directed to the “Terms of Use” section of this website. In preparing any country program or strategy, financing any project, or by making any designation of or reference to a particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of or any territory or area. Volume 5: Technical Appendices Appendix E. KA-ANDAL Approval Letter 6 AM039100-400-GN-RPT-1014 Volume 5: Technical Appendices Appendix F. The Ministry of Agraria and Spatial Planning issued Recommendation Letter 7 AM039100-400-GN-RPT-1014 Volume 5: Technical Appendices Appendix G. Comparison of WBG EHS Guidelines with Indonesian Regulations 8 AM039100-400-GN-RPT-1014 Appendix A. Comparisons of Standards Comparison of World Bank Group IFC Environmental Health and Safety (EHS) Guidelines with Indonesian Environmental Standards Table A1: Gaseous emission for Natural Gas (all turbine types) IFC Guidelines for Thermal Power Plant Indonesian Standard** Parameter Remark Non DA (mg/m3) DA (mg/m3) Limit (mg/Nm3) Particulate Indonesian standards are N/A N/A 30 mg/Nm3 Matter stricter CO NA NA NA - NOx 51* 51* 400 mg/Nm3 IFC guidelines are stricter Indonesian standards are SO2 NA NA 150 mg/Nm3 stricter Opacity NA NA N/A - Note: The figures in red are the more stringent requirements **At dry gas, excess O2 content 15% **Gas volume counted on standard (25 deg C and 1 bar atm) **this is for 95% normal operation in 3 (three) months period ***Source: Ministry of Environmental Regulation No. -
Social and Environmental Impact Assessment for the Proposed Rössing Uranium Desalination Plant Near Swakopmund, Namibia
Rössing Uranium Limited SOCIAL AND ENVIRONMENTAL IMPACT ASSESSMENT FOR THE PROPOSED RÖSSING URANIUM DESALINATION PLANT NEAR SWAKOPMUND, NAMIBIA DRAFT SOCIAL AND ENVIRONMENTAL MANAGEMENT PLAN PROJECT REFERENCE NO: 110914 DATE: NOVEMBER 2014 PREPARED BY ON BEHALF OF Rössing Uranium Desalination Plant: Draft SEMP PROJECT DETAILS PROJECT: Social and Environmental Impact Assessment for the Proposed Rössing Uranium Desalination Plant, near Swakopmund, Namibia AUTHORS: Andries van der Merwe (Aurecon) Patrick Killick (Aurecon) Simon Charter (SLR Namibia) Werner Petrick (SLR Namibia) SEIA SPECIALISTS: Birds –Mike and Ann Scott (African Conservation Services CC) Heritage – Dr John Kinahan (Quaternary Research Services) Marine ecology – Dr Andrea Pulfrich (Pisces Environmental Services (Pty) Ltd) Noise - Nicolette von Reiche (Airshed Planning Professionals) Socio-economic - Auriol Ashby (Ashby Associates CC) - Dr Jonthan Barnes (Design and Development ServicesCC) Visual – Stephen Stead (Visual Resource Management Africa) Wastewater discharge modelling –Christoph Soltau (WSP Group) Shoreline dynamics - Christoph Soltau (WSP Group) PROPONENT: Rio Tinto Rössing Uranium Limited REPORT STATUS: Draft Social and Environmental Management Plan REPORT NUMBER: 9408/110914 STATUS DATE: 28 November 2014 .......................................... .......................................... Patrick Killick Simon Charter Senior Practitioner: Aurecon Environment and Advisory Senior Practitioner: SLR Environmental Consulting ......................................... -
Residential Wood Combustion Technology Review Appendices
EPA-600/R-98-174b December 1998 Residential Wood Combustion Technology Review Volume 2. Appendices Prepared by: James E. Houck and Paul E.Tiegs OMNI Environmental Services, Inc. 5465 SW Western Avenue, Suite G Beaverton, OR 97005 EPA Purchase Order 7C-R285-NASX EPA Project Officer: Robert C. McCrillis U.S. Environmental Protection Agency (MD-61) National Risk Management Research Laboratory Air Pollution Prevention and Control Division Research Triangle Park, NC 27711 Prepared for: U.S. Environmental Protection Agency Office of Research and Development Washington, D.C. 20460 A-i Abstract A review of the current states-of-the-art of residential wood combustion (RWC) was conducted. The key environmental parameter of concern was the air emission of particles. The technological status of all major RWC categories was reviewed. These were cordwood stoves, fireplaces, masonry heaters, pellet stoves, and wood-fired central heating furnaces. Advances in technology achieved since the mid-1980's were the primary focus. These study objectives were accomplished by reviewing the published literature and by interviewing nationally recognized RWC experts. The key findings of the review included: (1) The NSPS certification procedure only qualitatively predicts the level of emissions from wood heaters under actual use in homes, (2) Wood stove durability varies with model and a method to assess the durability problem is controversial, (3) Nationally the overwhelming majority of RWC air emissions are from non-certified devices (primarily from older non-certified woodstoves), (4) New technology appliances and fuels can reduce emissions significantly, (5) The ISO and EPA NSPS test procedures are quite dissimilar and data generated by the two procedures would not be comparable, and, (6) The effect of wood moisture and wood type on particulate emission appears to be real but to be less than an order of magnitude. -
Annual Report Good Neighbor Environmental Board
Annual Report of the Good Neighbor Environmental Board A Presidential and Congressional Advisory Committee on U.S.-Mexico Border Environmental and Infrastructure Issues April 1997 THE GOOD NEIGHBOR ENVIRONMENTAL BOARD AN ADVISORY COMMITTEE ON U.S.- MEXICO BORDER ENVIRONMENTAL AND INFRASTRUCTURE ISSUES The President The Speaker of the House of Representatives The Vice President The Good Neighbor Environmental Board advisory committee was established by Congress in 1994, to address U.S.-Mexico border environmental and infrastructure issues and needs. The Board is comprised of a broad spectrum of individuals from business, nonprofit organizations, and state and local governments from the four states which border Mexico. The Board also has representation from eight U.S. departments and agencies. The legislation establishing the Board requires it to submit an annual report to the President and the Congress. On behalf of the Good Neighbor Environmental Board, I am happy to present this second annual report. During the past year, the Board has had extensive discussions about critical issues facing the border region, including receiving input from citizens in each of the communities where we met, and has developed a series of recommendations reflected in the enclosed report. The report and recommendations focus on changing the development paradigm along the U.S.-Mexico border--to begin to establish a sustainable development vision for the region. In addition to conventional environmental issues, the Board is also addressing health, transportation, housing, and economic development issues. The current recommendations relate largely to implementation of the new binational Border XXI framework and plan, coordination and leveraging of federal programs in the border region, encouragement of greater private sector participation, and development of needed infrastructure. -
EHS Guidelines for Themal Power Plants
Environmental, Health, and Safety Guidelines THERMAL POWER PLANTS DRAFT FOR SECOND PUBLIC CONSULTATION—MAY/JUNE 2017 WORLD BANK GROUP Environmental, Health, and Safety Guidelines for Thermal Power Plants Introduction 1. The Environmental, Health, and Safety (EHS) Guidelines are technical reference documents with general and industry-specific examples of Good International Industry Practice (GIIP).1 When one or more members of the World Bank Group are involved in a project, these EHS Guidelines are applied as required by their respective policies and standards. These industry sector EHS guidelines are designed to be used together with the General EHS Guidelines document, which provides guidance to users on common EHS issues potentially applicable to all industry sectors. For complex projects, use of multiple industry-sector guidelines may be necessary. A complete list of industry-sector guidelines can be found at: www.ifc.org/ehsguidelines. 2. The EHS Guidelines contain the performance levels and measures that are generally considered to be achievable in new facilities by existing technology at reasonable costs. Application of the EHS Guidelines to existing facilities may involve the establishment of site-specific targets, based on environmental assessments and/or environmental audits as appropriate, with an appropriate timetable for achieving them. 3. The applicability of the EHS Guidelines should be tailored to the hazards and risks established for each project on the basis of the results of an environmental assessment (EA) in which site-specific variables, such as host country context, assimilative capacity of the environment, and other project factors, are taken into account. The applicability of specific technical recommendations should be based on the professional opinion of qualified and experienced persons. -
BTF Incident Objectives and Requirements 2011
Bridger-Teton National Forest WFDSS Incident Objectives and Requirements 2011 Incident Objectives and Requirements This list was compiled from objectives included in old WFSAs (Blind Trail, Boulder, Cow Camp, East Table) and requirements in the FMP. CONTENTS INCIDENT OBJECTIVES ............................................................................................................... 2 General ....................................................................................................................................... 2 Economic .................................................................................................................................... 2 Local business/outfitters and guides ................................................................................. 2 Range ..................................................................................................................................... 2 Recreation .............................................................................................................................. 2 Special uses and private property ...................................................................................... 2 Environmental ........................................................................................................................... 3 Air quality ............................................................................................................................... 3 Cultural resources ................................................................................................................ -
Nitrogen Pollution and the European Environment Implications for Air Quality Policy
Science for Environment Policy IN-DEPTH REPORT Nitrogen Pollution and the European Environment Implications for Air Quality Policy September 2013 Environment Science for Environment Policy This In-depth Report is written and edited by the Science Nitrogen Pollution and the European Environment Communication Unit, University of the West of England Implications for Air Quality Policy (UWE), Bristol Email: [email protected] Acknowledgements Contents We wish to thank Prof Mark Sutton of the Centre for Ecology and Hydrology for his input to this report. Final responsibility Executive summary 3 for the content and accuracy of the report, however, lies solely with the author. Introduction 5 1. The economic cost of the ecological Images impacts of nitrogen pollution 9 Page 3: ©istockphoto.com/chukov 2. The relative importance of reduced Page 6, Figure 1: Rockström et al., 2009a Page 6, Figure 2: INI, 2010 and oxidised nitrogen pollutants 12 Page 7, Figure 3: Erisman et al., 2011 3. Nitrogen and climate change 15 Page 8, Figure 4: Sutton and Billen, 2010 4. Potential co-benefits from improved Page 9, Figure 5: Brink et al. 2011 Page 14, Figure 6: Stevens et al., 2011 nitrogen efficiency in agriculture 18 Page 9, Table 1: Brink et al. 2011 5. The potential for new air quality Page 9, Table 2: Brink et al. 2011 limits on ammonia to help achieve objectives of the Habitats Directive 24 In conclusion 26 About Science for Environment Policy Science for Environment Policy is a free news and information service published by the European Commission’s Directorate-General Environment, which provides the latest environmental policy- relevant research findings. -
Provincial Framework for AIRSHED PLANNING
Provincial Framework for AIRSHED PLANNING CONTENTS ii PREFACE iii EXECUTIVE SUMMARY 1 INTRODUCTION 7 THE PLANNING FRAMEWORK 9 Stage 1: Evaluate the need for a plan 12 Stage 2: Identify and engage stakeholders 14 Stage 3: Investigate planning synergies 16 Stage 4: Determine priority sources 18 Stage 5: Develop the plan 20 Stage 6: Implement, monitor, and report 22 CONCLUSION 23 REFERENCES 26 GLOSSARY OF TERMS AND ACRONYMS 29 Appendix 1: Background to the framework 33 Appendix 2: Air quality planning and information 35 Appendix 3: Examples of related planning processes 36 Appendix 4: Examples of best practices and local bylaws i PREFACE This document describes a framework for preparing air quality management plans, or "airshed plans," in British Columbia. As such, it should be of interest to a broad range of local stakeholders in air quality, including local and regional governments, health professionals, industry, businesses, environmental and community interest groups, and private citizens. The framework is designed to help those considering or undertaking a planning process to better understand what the Province of British Columbia (the Province) expects from an airshed plan in terms of approach and content. The intent is to encourage greater consistency and efficiency in planning efforts, towards implementation of the Canada-Wide Standards for particulate matter and ozone – key pollutants of concern due to their health and environmental impacts. The Draft Provincial Framework for Airshed Planning represents the culmination of a development process that started in 2005 and included two rounds of stakeholder consultation (see Appendix 1). More than 60 participants contributed to these consultations, drawn from local and regional government, industry, academia, health authorities, and environmental and community organizations. -
Impact of Reactive Surfaces on the Abiotic Reaction Between Nitrite and 2 Ferrous Iron and Associated Nitrogen and Oxygen Isotope Dynamics
https://doi.org/10.5194/bg-2020-73 Preprint. Discussion started: 17 March 2020 c Author(s) 2020. CC BY 4.0 License. 1 Impact of reactive surfaces on the abiotic reaction between nitrite and 2 ferrous iron and associated nitrogen and oxygen isotope dynamics 3 Anna-Neva Visser1,4, Scott D. Wankel2, Pascal A. Niklaus3, James M. Byrne4, Andreas A. Kappler4, 4 Moritz F. Lehmann1 5 1Department of Environmental Sciences, Basel University, Bernoullistrasse 30, 4056 Basel, Switzerland 6 2Woods Hole Oceanographic Institution, Woods Hole, 360 Woods Hole Rd, MA 02543, USA 7 3Department of Evolutionary Biology and Environmental Studies, University of Zürich, Winterthurerstrasse 190, 8057 Zürich, 8 Switzerland 9 4Department of Geosciences, Tübingen University, Hölderlinstrasse 12, 72074 Tübingen, Germany 10 Correspondence to: Anna-Neva Visser ([email protected]) 11 Abstract. Anaerobic nitrate-dependent Fe(II) oxidation (NDFeO) is widespread in various aquatic environments, and plays a 12 major role in iron and nitrogen redox dynamics. However, evidence for truly enzymatic, autotrophic NDFeO remains limited, 13 with alternative explanations involving coupling of heterotrophic denitrification with abiotic oxidation of structurally-bound 14 or aqueous Fe(II) by reactive intermediate N species (chemodenitrification). The extent to which chemodenitrification is 15 caused, or enhanced, by ex vivo surface catalytic effects has, so far, not been directly tested. To determine whether the presence 16 of either a Fe(II)-bearing mineral or dead biomass (DB) catalyses chemodenitrification, two different sets of anoxic batch 17 experiment were conducted: 2 mM Fe(II) was added to a low-phosphate medium, resulting in the precipitation of vivianite - 8 - 18 (Fe3(PO4)2), to which later 2 mM nitrite (NO2 ) was added, with or without an autoclaved cell suspension (~1.96×10 cells ml 1 2+ 19 ) of Shewanella oneidensis MR-1. -
Species and Habitats Most at Risk in Greater Yellowstone by Andrew J
Species and Habitats Most at Risk in Greater Yellowstone By Andrew J. Hansen The broad-scale ecological and human patterns of the Greater Yellowstone Ecosystem (GYE) (Fig. 1) are relatively well understood. Keiter and Boyce (1991) placed ecological processes and organisms in Yellowstone National Park in the context of the broader GYE. Glick et al. (1991) focused on the interplay between natural resources and local economics. Clark and Minta (1994) explored how government and social institutions influence management of the GYE. Hansen et al. (2002) quantified change in land cover and use in the GYE during 1975–1995 and examined the consequences for bio- diversity and socioeconomics of local communities. Noss et Figure 1. Map of the Greater Yellowstone Ecosystem as al. (2002) rated the ecological importance of 43 “megasites” defined by Hansen et al. (2002). outside of protected areas based on ecological and land use factors. Gude et al. (2007) evaluated the consequences of past, present, and possible future land use on several indices from expanding backcountry recreation and climate-induced of biodiversity. changes in habitat and water. These assessments and other studies have identified This article is drawn largely from a report that was several successes and challenges in maintaining viable species, prepared for the U.S. Forest Service (USFS) (Hansen 2006) communities, and ecosystems across the GYE. Management to assess the major factors that influence species and ecosys- of elk populations, recovery of the threatened grizzly bear, tem viability across the GYE as a context for the analysis and and reintroduction of wolves have involved both large, management of biodiversity. -
Good Practice Guidance for Mining and Biodiversity
sity er or Mining and Biodiv e f e Guidanc actic Good Pr Good Practice for Guidance Mining and Biodiversity Good Practice Guidance for Mining and Biodiversity ICMM e d Plac [email protected] or atf +44 (0) 20 7290 4921 ax: www.icmm.com ICMM 19 Str London W1C 1BQ Kingdom United Telephone: +44 (0) 20 7290 4920 F Email: inf ur library at www.goodpracticemining.com has case studies and other studies has case at www.goodpracticemining.com ur library he International Council on Mining and Metals (ICMM) is a CEO-led organisation (ICMM) is a CEO-led Council on Mining and Metals he International CMM – Council on Mining and Metals International I T as as well companies mining and metals leading many of the world’s comprising to committed all of which are associations, national and commodity regional, the responsible and to performance development their sustainable improving society needs. resources and metal of the mineral production that is widely industry and metals mining, minerals vision is a viable ICMM’s sustainable to contributor modern living and a key for as essential recognised development. O practices. of leading examples sity er or Mining and Biodiv e f e Guidanc actic Good Pr Good Practice Guidance for Mining and Biodiversity Good Practice Guidance for Mining and Biodiversity Good Practice Guidance for Mining and Biodiversity Good Practice Guidance for Mining and Biodiversity Contents 1 Contents 1 Acknowledgements 4 Foreword 5 SECTION A: BACKGROUND AND OVERVIEW 1. Introduction 8 1.1 Background 9 1.2 Biodiversity and why it is valuable 10 1.2.1 What is biodiversity? 10 1.2.2 Why is biodiversity valuable? 10 1.2.3 Relevance to mining operations 12 1.3 Why mining companies should consider biodiversity 13 1.4 The importance of stakeholder engagement 15 1.5 Scope and structure of the Good Practice Guidance 16 1.51 Scope 16 1.5.2 Structure 16 SECTION B: MANAGING BIODIVERSITY AT DIFFERENT OPERATIONAL STAGES 2. -
Nitric Oxide-Induced Cytotoxicity: Involvement of Cellular Resistance to Oxidative Stress and the Role of Glutathione in Protection
0031-3998195/3701-0041$03.0010 PEDIATRIC RESEARCH Vol. 37, No. 1, 1995 Copyright O 1994 International Pediatric Research Foundation, Inc Printed in U.S.A. Nitric Oxide-Induced Cytotoxicity: Involvement of Cellular Resistance to Oxidative Stress and the Role of Glutathione in Protection M. WHIT WALKER, MICHAEL T. KINTER, ROBERT J. ROBERTS, AND DOUGLAS R. SPITZ University of Virginia Health Sciences Center, Division of Neonatology, Departments of Pediatrics and Pathology, University of Virginia Hospital, Charlottesville, Virginia 22908 [M.W.W., M.T.K., R.J.R.], and Mallinckrodt Institute of Radiology, Radiation Oncology Center, Section of Cancer Biology, Washington University Medical Center, St. Louis, Missouri 63108 [D.R.S.] A series of experiments were designed to examine the poten- NO exposure. Other experiments demonstrated that nitrate and tial cytotoxicity of nitric oxide (NO), or reactive species derived nitrite exposure produced no cytotoxicity in glutathione-depleted from NO, in HA1 fibroblasts and H202-resistant variants of this HA1 cells and that coincubation of NO-saturated medium with cell line, designated OC14 cells. A 1-h exposure at 37OC to a 1.7 oxyhemoglobin inhibited NO-induced cytotoxicity in glutathio- mM bolus dose of NO, prepared in N2-gassed medium, signifi- ne-depleted HA1 cells. These results demonstrate that 1) nitric cantly reduced clonogenic survival in the HA1 fibroblasts line to oxide, or an NO-derived reactive nitrogen species other than 60% of control cells treated with N2-gassed medium alone. The nitrites or nitrates, is responsible for reduction in clonogenic OC14 cells were found to be completely resistant (100% sur- survival and trypan blue dye exclusion capabilities in vitro; 2) vival) to NO-mediated injury in comparable experiments.