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20240329122006.0 |
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|a 9781780408484
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|a 178040848X
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|a (OCoLC)963581181
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|b .M535 2016eb
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|a 628.167
|2 23
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|a UAMI
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|a Mickley, Mike.
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|a Database of Permitting Practices for Seawater Concentrate Disposal.
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|a London :
|b IWA Publishing,
|c 2016.
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|a 1 online resource (197 pages)
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|a text
|b txt
|2 rdacontent
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|a computer
|b c
|2 rdamedia
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|a online resource
|b cr
|2 rdacarrier
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|a WERF Research Report Series ;
|v v. Desal-13-07
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|a Print version record.
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|a Cover; Copyright; Abstract & Benefits; Table of Contents; List of Figures; List of Tables; Acronyms; Acknowledgments; Executive Summary; Chapter 1: Project Context and Report Content; 1.1 Chapter Content; 1.2 Report Content; 1.3 The Subject; 1.4 Context of Seawater Concentrate Management and Regulation; 1.4.1 Overview of Global Desalination; 1.4.2 Overview of U.S. Desalination and Concentrate Management; 1.4.3 Seawater Concentrate Discharge Options; 1.4.4 Discharge Permit Issues of Seawater Concentrate and Discharge Regulation; 1.4.5 Concentrate Management as Part of a Desalination Project.
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|a 1.4.6 Summary of Background and Context InformationChapter 2: Desalination Plant Discharge Characterization; 2.1 SWRO Residuals; 2.2 Concentrate; 2.2.1 Quantity; 2.2.2 Quality; 2.3 Backwash Water; 2.3.1 Quantity; 2.3.2 Quality; 2.3.3 Disposal of Spent Backwash Water; 2.4 Disposal of Spent Membrane Flush Water; 2.4.1 Quantity; 2.4.2 Quality; 2.4.3 Disposal; Chapter 3: Seawater Concentrate Discharge Methods; 3.1 Surface Water Discharge of Concentrate; 3.1.1 Impacts of Surface Water Discharge on the Marine Environment; 3.2 Concentrate Treatment Prior to Surface Water Discharge.
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|a 3.3 New Onshore, Near-shore, or Offshore Outfall3.3.1 Description; 3.3.2 Potential Environmental Impacts and Discharge Feasibility; 3.4 Co-disposal with Wastewater Effluent; 3.4.1 Description; 3.4.2 Potential Environmental Impacts; 3.4.3 Feasibility Considerations; 3.5 Co-disposal with Power Plant Cooling Water; 3.5.1 Description; 3.5.2 Potential Environmental Impacts and Discharge Feasibility; Chapter 4: Other Seawater Residual Management Options; 4.1 Introduction; 4.2 Discharge to Sanitary Sewer; 4.2.1 Description; 4.2.2 Potential Environmental Impacts; 4.2.3 Effect on WRRF Operations.
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|a 4.2.4 Effect on Water Reused for Irrigation4.2.5 Application to SWRO Residuals; 4.3 Deep Well Injection and Shallow Coastal Well Disposal; 4.3.1 Description; 4.3.2 Potential Environmental Impacts; 4.3.3 Application to SWRO Residuals; 4.4 Evaporation Ponds; 4.4.1 Description; 4.4.2 Potential Environmental Impacts; 4.4.3 Application to SWRO Residuals; 4.5 High Recovery and Zero Liquid Discharge Concentrate Disposal Systems; 4.5.1 Description; 4.5.2 Potential Environmental Impacts; 4.5.3 Application to SWRO Residuals; 4.6 Beneficial Use of Concentrate.
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|a 4.6.1 Land Application of Concentrate -- Description4.6.1.1 Potential Environmental Impacts; 4.6.1.2 Applicability to SWRO Residuals; 4.6.2 Other Beneficial Uses of Concentrate; 4.6.2.1 Potential Environmental Impacts; 4.6.2.2. Applicability to SWRO Residuals; 4.6.3 Salt Recovery from Concentrate; 4.6.3.1 Potential Environmental Impacts; 4.6.3.2 Application to SWRO Residuals; Chapter 5: Regulations and Permitting Practices in the United States; 5.1 Introduction; 5.2 General Overview of U.S. Federal Regulatory Framework; 5.2.1 Federal Regulatory Programs Affecting SWRO Concentrate Disposal.
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|a 5.2.2 Federal Framework for Ocean Discharge.
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|b Permitting the disposal of concentrate and other waste streams is often one of the most challenging tasks associated with the development and implementation of desalination projects. This study focuses on the review of key regulatory requirements, support studies, and permitting practices for medium and large seawater reverse osmosis (SWRO) desalination plants in the United States and abroad. The size range (from 2.5 to 110 MGD or 9.5 to 440 ML/d) covers most plants built since 2005. The study is based on permitting experience with recent SWRO projects and is focused on the regulatory issues and considerations associated with the most commonly used concentrate management method: discharge to surface water bodies. Issues specific to the permitting of thermal desalination plants are not addressed in the report because, although popular in the Middle East, thermal desalination has not found significant application in seawater desalination in the United States and most other developed countries. The formal project objective was to identify the discharge information that permitting agencies need and the decision-making process they go through to permit discharge methods in order to help desalination project proponents focus and expedite their permitting efforts. The project involved documenting SWRO discharge regulatory information and facility information for the United States and selected countries. In the United States, the National Pollutant Discharge Elimination System (NPDES) permit is the primary permit required for discharge to surface waters. Discussion focused on events, information, and issues associated with obtaining an NPDES-type permit. One of the key limiting factors in the construction of new seawater desalination plants is the availability of suitable conditions and locations for disposal of the high-salinity sidestream commonly referred to as concentrate or brine. Concentrate is generated as a by-product of the separation of the minerals from the source water used for desalination. This liquid stream contains in concentrated form most of the source water's dissolved solids as well as some pretreatment additives (i.e., residual amounts of coagulants, flocculants, and antiscalants) and other chemicals, as well as microbial contaminants and particulates rejected by the reverse osmosis (RO) membranes. If chemical pretreatment is used, such as coagulants, antiscalants, polymers, or disinfectants, some or all of these chemicals may reach or may be disposed of along with the plant discharge concentrate. Chapter 1 of the report provides background and contextual information for the study including the relatively new interest and recent challenges associated with the permitting complexity of medium and large SWRO desalination plants in the United States.
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| 590 |
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|a ProQuest Ebook Central
|b Ebook Central Academic Complete
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| 650 |
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|a Saline water conversion.
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| 650 |
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|a Saline waters.
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| 650 |
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6 |
|a Eau salée
|x Dessalement.
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| 650 |
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6 |
|a Eau salée.
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| 650 |
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|a salt water.
|2 aat
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| 650 |
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|a Water supply & treatment.
|2 bicssc
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| 650 |
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|a Saline water conversion
|2 fast
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| 650 |
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7 |
|a Saline waters
|2 fast
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| 650 |
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|a Environmental science, engineering & technology.
|2 thema
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| 650 |
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|a Industrial applications of scientific research & technological innovation.
|2 thema
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| 650 |
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|a Mining technology & engineering.
|2 thema
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| 650 |
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|a Water supply & treatment.
|2 thema
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| 650 |
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|a Environment and Ecology.
|2 ukslc
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| 700 |
1 |
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|a Voutchkov, Nikolay.
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| 776 |
0 |
8 |
|i Print version:
|a Mickley, Mike.
|t Database of Permitting Practices for Seawater Concentrate Disposal.
|d London : IWA Publishing, ©2016
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| 830 |
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|a WERF Research Report Series.
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| 856 |
4 |
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|u https://ebookcentral.uam.elogim.com/lib/uam-ebooks/detail.action?docID=4742400
|z Texto completo
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|a Askews and Holts Library Services
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