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		<title>CLU-IN Technology Innovation News Survey</title>
		<link>http://www.clu-in.org/products/tins/</link>
		<language>en-us</language>
		<description>The Technology Innovation News Survey contains market/commercialization information; reports on demonstrations, feasibility studies and research; and other news relevant to the hazardous waste community interested in technology development.    For a complete list of RSS feeds available on CLU-IN, please visit http://www.clu-in.org/rss/about/ .</description>
		<copyright>Information presented is considered public information and may be distributed or copied. The U.S. Government retains a nonexclusive, royalty-free license to publish or reproduce these materials, or allow others to do so, for U.S. Government purposes. These materials may be freely distributed and used for non-commercial, scientific, and educational purposes. Commercial use of the materials available from this server may be protected under U.S. and Foreign Copyright Laws.</copyright>
		
		<lastBuildDate>Sat, 18 May 2013 04:00:43 GMT</lastBuildDate>
		
		
  
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		<title>FEDERAL ACTIONS TO ADDRESS IMPACTS OF URANIUM CONTAMINATION IN THE NAVAJO NATION: FIVE-YEAR PLAN SUMMARY REPORT [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9952</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9952</guid>
		<description>U.S. EPA Region 9, 67 pp, 2013 &lt;br /&gt;&lt;br /&gt; In 2007, five federal agencies developed a five-year plan that outlined a strategy for addressing the most urgent risks posed by legacy uranium contamination on the lands of the Navajo Nation, an area of roughly 27,000 square miles. As the five-year period ended in 2012, U.S. EPA and partner agencies (the Bureau of Indian Affairs, Nuclear Regulatory Commission, Department of Energy, and Indian Health Service) prepared this report to describe the progress made toward cleaning up uranium-contaminated soil and groundwater at specific sites on the reservation between 2008 and 2012. Much remains to be done, and all five agencies have committed to developing another five-year plan to continue the work. &lt;A HREF=&quot;http://epa.gov/region9/superfund/navajo-nation/pdf/NavajoUraniumReport2013.pdf&quot;&gt;http://epa.gov/region9/superfund/navajo-nation/pdf/NavajoUraniumReport2013.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:38:44 GMT</pubDate>
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		<title>PETROLEUM BROWNFIELDS 2013: OPPORTUNITIES FOR ACTION [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9951</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9951</guid>
		<description>U.S. EPA, Offices of Underground Storage Tanks (OUST) and Brownfields and Land Revitalization (OBLR), 9 pp, Feb 2013 &lt;br /&gt;&lt;br /&gt; In 2008, OUST and OBLR jointly developed a petroleum brownfields action plan to identify objectives and resources that specifically targeted petroleum-contaminated properties. This 2013 action plan describes challenges associated with cleaning up and reusing petroleum brownfields, highlights EPA accomplishments achieved since 2008, and proposes petroleum brownfields actions EPA intends to achieve over the next three years. &lt;A HREF=&quot;http://www.epa.gov/oust/pubs/petrobfactionplan.htm&quot;&gt;http://www.epa.gov/oust/pubs/petrobfactionplan.htm&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:38:29 GMT</pubDate>
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		<title>ADVISORY: ACTIVE SOIL GAS INVESTIGATIONS [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9950</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9950</guid>
		<description>California EPA, Department of Toxic Substances Control, 96 pp, Apr 2012 &lt;br /&gt;&lt;br /&gt; This updated Advisory provides technically consistent approaches for collecting and analyzing soil gas samples. Data obtained from soil gas investigations can be used to identify the spatial distribution of volatile contamination at a site and assist in the evaluation of vapor intrusion. This 2012 revision incorporates all key elements from the Los Angeles Regional Water Quality Control Board&apos;s 1997 &lt;i&gt;Interim Guidance for Active Soil Gas Investigation&lt;/i&gt; and is a compilation of available information, knowledge, experience and best practices regarding soil gas sampling. &lt;A HREF=&quot;http://www.dtsc.ca.gov/SiteCleanup/upload/VI_ActiveSoilGasAdvisory_FINAL_043012.pdf&quot;&gt;http://www.dtsc.ca.gov/SiteCleanup/upload/VI_ActiveSoilGasAdvisory_FINAL_043012.pdf&lt;/A&gt;&lt;br&gt;&lt;br /&gt;
See also the 3-page &quot;Summary of Changes Between 2003 Advisory and 2012 Advisory&quot; at &lt;A HREF=&quot;http://www.dtsc.ca.gov/SiteCleanup/upload/VI_ASGI_summary_of_changes_FINAL.pdf&quot;&gt;http://www.dtsc.ca.gov/SiteCleanup/upload/VI_ASGI_summary_of_changes_FINAL.pdf&lt;/A&gt;. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:37:56 GMT</pubDate>
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		<title>TRANSITION ISSUES ANALYSIS [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9949</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9949</guid>
		<description>Association of State and Territorial Solid Waste Management Officials, ASTSWMO Removal Action Focus Group, 22 pp, 2013 &lt;br /&gt;&lt;br /&gt; With assistance from EPA&apos;s Office of Emergency Management, ASTSWMO prepared this document as a quick reference for states to better understand EPA-led removal actions. This guide defines the different types of removal actions and lists milestone phases and typical documents generated. Removal action criteria and general roles are supported by corresponding references. The information highlights the dilemma facing some states as to whether to conduct removal actions to address the more immediate risks posed by sites while potentially jeopardizing the ability to secure funding to address long-term remedial actions. &lt;A HREF=&quot;http://www.astswmo.org/Files/Policies_and_Publications/CERCLA_and_Brownfields/Removals-Transition_Issues_Analysis/2013-03-01-Transitions_Research_Document-3-06-12.pdf&quot;&gt;http://www.astswmo.org/Files/Policies_and_Publications/CERCLA_and_Brownfields/Removals-Transition_Issues_Analysis/2013-03-01-Transitions_Research_Document-3-06-12.pdf&lt;/A&gt;&lt;br&gt;&lt;br /&gt;
Supporting information includes the &quot;Emergency Response Matrix&quot; (.xls), &quot;Non-TCRA Matrix&quot; (.xls), &quot;TCRA Matrix&quot; (.xls), and &quot;Removal Action Process Timeline Schematic&quot; (.ppt), at &lt;A HREF=&quot;http://www.astswmo.org/Pages/Policies_and_Publications/CERCLA_and_Brownfields.htm&quot;&gt;http://www.astswmo.org/Pages/Policies_and_Publications/CERCLA_and_Brownfields.htm&lt;/A&gt;. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:37:27 GMT</pubDate>
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		<title>SUMMARY OF TECHNICAL IMPRACTICABILITY WAIVERS AT NATIONAL PRIORITIES LIST SITES [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9948</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9948</guid>
		<description>U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response.&lt;br /&gt;
OSWER Directive 9230.2-24, 101 pp, Aug 2012 &lt;br /&gt;&lt;br /&gt; Technical impracticability (TI) waivers are one of the means of waiving applicable or relevant and appropriate requirements (ARARs), consistent with CERCLA Section 121(b) and the National Contingency Plan. Through analysis of site data and demonstration of the technical impracticability of achieving those ARARs (e.g., maximum contaminant levels or other federal or state standards), a waiver may be appropriate. This report compiles historical information on 91 TI waivers that were approved for either groundwater or surface water at 85 Superfund sites between 1988 and 2011. Appendix A contains a summary sheet for each TI waiver. &lt;A HREF=&quot;http://www.epa.gov/superfund/health/conmedia/gwdocs/pdfs/TI_waiver_report%2009Aug2012.pdf&quot;&gt;http://www.epa.gov/superfund/health/conmedia/gwdocs/pdfs/TI_waiver_report%2009Aug2012.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:37:04 GMT</pubDate>
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		<title>MERCURY CONTAMINATED SITES: SUMMARY REPORT, NICOLE TECHNICAL MEETING [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9947</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9947</guid>
		<description>Blom, M. (compiler).&lt;br /&gt;
NICOLE Mercury Working Group, 32 pp, 2012 &lt;br /&gt;&lt;br /&gt; Across the European Union, mercury is listed as a priority hazardous substance, and its use is being largely phased out. The technical workshop on mercury-contaminated sites of 4 December 2012, in Brussels, Belgium, was held to identify and disseminate state-of-the-art strategies, techniques, and technologies that support the management of Hg-contaminated sites while minimizing risk and maximizing sustainability. This report summarizes the workshop presentations and discussions. &lt;A HREF=&quot;http://www.nicole.org/uploadedfiles/nicole-brussels-december2012.pdf&quot;&gt;http://www.nicole.org/uploadedfiles/nicole-brussels-december2012.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:36:43 GMT</pubDate>
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		<title>VAPOR INTRUSION PUBLIC PARTICIPATION ADVISORY [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9946</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9946</guid>
		<description>California EPA, Department of Toxic Substances Control, 109 pp, Mar 2012 &lt;br /&gt;&lt;br /&gt; This Advisory describes public participation approaches designed to facilitate effective communication and coordination with communities and stakeholders affected by or concerned with vapor intrusion at sites that have a potentially complete indoor air exposure pathway.&lt;br /&gt;
&lt;A HREF=&quot;http://www.dtsc.ca.gov/SiteCleanup/upload/VIPPA_Final_03_05_12.pdf&quot;&gt;http://www.dtsc.ca.gov/SiteCleanup/upload/VIPPA_Final_03_05_12.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:36:15 GMT</pubDate>
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		<title>VERIFYING FOOD WEB BIOACCUMULATION MODELS BY TRACKING FISH EXPOSURE AND CONTAMINANT UPTAKE [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9945</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9945</guid>
		<description>Gustavson, K. Strategic Environmental Research and Development Program (SERDP), Project ER-1749, 50 pp, 2012 &lt;br /&gt;&lt;br /&gt; The overall project objective was to develop and use innovative technologies that eliminate fundamental uncertainties in food-web modeling by unambiguously documenting contaminant exposure, chemical uptake, and growth over time in individual fish, and to use that information to verify and improve food-web bioaccumulation modeling approaches. An initial prototype was developed to initiate testing and to assess if the device requirements of tracking and surface recovery of implanted fish were met. Substantial progress was made toward developing a reliable and functioning tag design capable of achieving design requirements, but the flotation mechanism requires modification and the coupled flotation/euthanization mechanism needs to be verified in further prototype development and testing. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/15761/180714/file/ER-1749-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/15761/180714/file/ER-1749-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:36:00 GMT</pubDate>
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		<title>USE OF PHYTOREMEDIATION FOR BOTH MANAGING SELENIUM AND PRODUCING BIOFORTIFIED PLANT PRODUCTS AND BIOFUEL UNDER ADVERSE SOIL CONDITIONS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9944</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9944</guid>
		<description>Banuelos, G.S.&lt;br /&gt;
2012 Taipei International Conference on Remediation and Management of Soil and Ground Water Contaminated Sites, October 30-31, 2012, Taipei, Taiwan. 361-366, 2012 &lt;br /&gt;&lt;br /&gt; This paper discusses the production of selenium-biofortified plant products and biofuel from plants grown for the remediation of selenium under field conditions in the San Joaquin Valley, California. [&lt;i&gt;The paper begins on&lt;b&gt; page 361&lt;/b&gt; in the portion of the proceedings (pages 301-422) that opens at the link.&lt;/i&gt;] &lt;A HREF=&quot;http://sgw.epa.gov.tw/resag/Update_Data/Information9055749Oct_30-31_Proceedings_1106_1230_Brief_S5-6.pdf&quot;&gt;http://sgw.epa.gov.tw/resag/Update_Data/Information9055749Oct_30-31_Proceedings_1106_1230_Brief_S5-6.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:35:41 GMT</pubDate>
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		<title>TREATABILITY TEST REPORT: CHARACTERIZATION OF VADOSE ZONE CARBON TETRACHLORIDE SOURCE STRENGTH USING TOMOGRAPHIC METHODS AT THE 216-Z-9 SITE [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9943</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9943</guid>
		<description>Truex, M.J., K.C. Carroll, V.J. Rohay, R.D. Mackley, and K.R. Parker.&lt;br /&gt;
PNNL-21326, 77 pp, Sep 2012 &lt;br /&gt;&lt;br /&gt; A treatability test was conducted in 2011 at the 216-Z-9 Trench to evaluate methods for collecting characterization information that supports refined assessment of soil vapor extraction (SVE) performance goals based on impact to groundwater. The characterization information can also provide input to operational strategies for continued SVE operation and decisions regarding closure of the SVE system or transition to other remedies. &lt;A HREF=&quot;http://0-www.osti.gov.iii-server.ualr.edu/bridge/purl.cover.jsp?purl=/1063738/&quot;&gt;http://0-www.osti.gov.iii-server.ualr.edu/bridge/purl.cover.jsp?purl=/1063738/&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:35:27 GMT</pubDate>
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		<title>COUPLING IN SILICO MICROBIAL MODELS WITH REACTIVE TRANSPORT MODELS TO PREDICT THE FATE OF CONTAMINANTS IN THE SUBSURFACE [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9942</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9942</guid>
		<description>Lovley, D.R.&lt;br /&gt;
DOE/ER/64367-1, 5 pp, Oct 2012 &lt;br /&gt;&lt;br /&gt; This project successfully accomplished its goal of coupling genome-scale metabolic models with hydrological and geochemical models to predict the activity of subsurface microorganisms during uranium bioremediation. The modeling approach can be used to develop new strategies to optimize bioremediation. The approach of coupling genome-scale metabolic models with reactive transport modeling is sufficiently well established that it has been adopted by other investigators studying uranium bioremediation. The basic principles developed during these studies will be applicable to much broader investigations of microbial activities, not only for other types of bioremediation, but for microbial metabolism in a diversity of environments. &lt;A HREF=&quot;http://www.osti.gov/servlets/purl/1053957/&quot;&gt;http://www.osti.gov/servlets/purl/1053957/&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:35:13 GMT</pubDate>
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		<title>HYDROGEL TRACER BEADS: THE DEVELOPMENT, MODIFICATION, AND TESTING OF AN INNOVATIVE TRACER FOR BETTER UNDERSTANDING LNAPL TRANSPORT IN KARST AQUIFERS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9941</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9941</guid>
		<description>Laskoskie, A., H.M. Edenborn, and D.J. Vesper.&lt;br /&gt;
2012 GSA Annual Meeting and Exposition, Charlotte, North Carolina, Poster, 2012 [NETL-462] &lt;br /&gt;&lt;br /&gt; Research is under way to develop proxy tracers that mimic contaminant movement the better to understand and predict contaminant fate and transport in karst aquifers. Hydrogel tracer beads are transported as a separate phase in water and can used as a proxy tracer to mimic the transport of NAPL. The beads can be constructed with different densities, sizes, and chemical attributes. This poster describes the creation and optimization of the beads and the field testing of buoyant beads, including sampling, tracer analysis, and quantitative analysis. The buoyant beads are transported ahead of the dissolved solutes, suggesting that LNAPL transport in karst may occur faster than predicted from traditional tracing techniques. &lt;A HREF=&quot;http://www.osti.gov/bridge/purl.cover.jsp?purl=/1061498/&quot;&gt;http://www.osti.gov/bridge/purl.cover.jsp?purl=/1061498/&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:34:58 GMT</pubDate>
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		<title>A TRACER TEST TO CHARACTERIZE TREATMENT OF TCE IN A PERMEABLE REACTIVE BARRIER [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9940</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9940</guid>
		<description>Shen, H., J.T. Wilson, and X. Lu.&lt;br /&gt;
Groundwater Monitoring &amp; Remediation, Vol 32 No 4, 32-41, 2012 &lt;br /&gt;&lt;br /&gt; A tracer test was conducted to characterize the flow of groundwater across a permeable reactive barrier (PRB) constructed with plant mulch (a biowall) at the OU-1 site on Altus Air Force Base, Oklahoma. Constructed to intercept and treat TCE-contaminated groundwater in a shallow aquifer, the biowall is 139 m long, 7.3 m deep, and 0.5 m wide. Breakthrough of bromide injected from an upgradient well into the groundwater as a conservative tracer was observed subsequently in monitoring wells within and downgradient of the biowall. The bromide breakthrough data demonstrate that groundwater entering the biowall migrated across it, following the slope of the local groundwater surface. The tracer data enabled estimation of the average seepage velocity of groundwater (~0.06 m/d), average residence time of groundwater in the biowall (10 d), and other performance factors. The approach used in this study provides an objective evaluation of the remedial performance of the biowall that can provide a basis for design of other biowalls intended to remediate TCE-contaminated groundwater. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:34:41 GMT</pubDate>
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		<title>EVALUATING TCE ABIOTIC AND BIOTIC DEGRADATION PATHWAYS IN A PERMEABLE REACTIVE BARRIER USING COMPOUND SPECIFIC ISOTOPE ANALYSIS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9939</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9939</guid>
		<description>Lojkasek-Lima, P., R. Aravena, O. Shouakar-Stash, S.K. Frape, M. Marchesi, S. Fiorenza, and J. Vogan. Groundwater Monitoring &amp; Remediation, Vol 32 No 4, 53-62, 2012 &lt;br /&gt;&lt;br /&gt; A pilot-scale zero-valent iron (ZVI) permeable reactive barrier (PRB) was installed using azimuth-controlled vertical hydrofracturing at an industrial facility to treat a plume of chlorinated VOCs. Following ZVI injection, no significant reduction in concentration was observed with the exception of some multilevel monitoring wells, which also showed high levels of total organic carbon. These patterns suggested that the ZVI was not well distributed in the PRB, creating leaky conditions. The geochemical data indicated reducing conditions in the areas where VOC reduction was observed, suggesting that biotic processes associated with the guar used in the ZVI injection could be a major mechanism of VOC degradation. Compound-specific isotope analysis using both carbon and chlorine stable isotopes showed enriched isotope values around the PRB compared to the isotope composition of the VOC source, confirming that VOC degradation is occurring along the PRB. Test results showing differences in isotopic trends combined with changes in VOC concentrations and redox parameters indicated that biotic processes likely are the major pathways involved in the degradation of VOCs near the PRB. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:34:26 GMT</pubDate>
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		<title>VACUUM THERMAL TREATMENT OF PCB CONTAMINATED POLE TRANSFORMERS USING VOLTAGE ADJUSTER [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9938</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9938</guid>
		<description>Ohm, T.I., H.S. An, S.S. Park, K.H. Kim, J.S. Chae, and S.H. Moon.&lt;br /&gt;
Crete 2012: 3rd International Conference on Industrial and Hazardous Waste Management. Technical University of Crete, 6 pp, 2012 &lt;br /&gt;&lt;br /&gt; A vacuum thermal recycling (VTR) process with an adapted voltage adjuster (&quot;improved VTR&quot;) was applied to 50 and 75 kVA pole transformers containing 11.8 and 214.8 mg/L PCBs, respectively. The residual total PCBs were below detection for all sample types&amp;mdash;copper coil, iron core, paper, wood, and porcelain&amp;mdash;results that satisfy the limit concentration standard for the Republic of Korea. To raise the temperature of copper coil from room temperature to between 200-230&amp;deg;C, the original VTR method consumed 292 to 406 kWh, whereas the improved method required 102 to 131 kWh. The voltage adjuster adapted for improved VTR achieved this temperature increase with input energies of ~5 kWh for the 75 kVA transformer and 3 kWh for the 50 kVA transformer. The original VTR method required three to five times longer than the improved VTR method to complete this process. Moreover, no separation of transformer components is required prior to the improved VTR process, which makes it more cost-effective than the original method because it reduces both power consumption and the treatment timeframe. Additional results show that this method was efficient and effective for treating PCB-contaminated transformers and other solid-phase, PCB-contaminated waste. &lt;A HREF=&quot;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16431&quot;&gt;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16431&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:34:13 GMT</pubDate>
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		<title>WHAT ABOUT THE PRACTICAL IMPLEMENTATION OF GEOSTATISTICS FOR CONTAMINATED SITES AND SOILS? [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9937</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9937</guid>
		<description>Demougeot-Renard, H., M. Garcia, and N. Jeannee.&lt;br /&gt;
Ninth International Geostatistics Congress, 11-15 June 2012, Oslo, Norway. 14 pp, 2012 &lt;br /&gt;&lt;br /&gt; The aim of the geostatistical study of a former gasworks located in France, where soils showed high levels of PAHs, was to (1) assess and locate the volume of contaminated soil, (2) compare the estimates with the remediation results, and (3) quantify and position the residual pollution after remediation. The major drawbacks of the available data were a highly heterogeneous support (from 0.1 to 2.3 m in height) and an irregular distribution of samples. The best compromises were obtained by fitting variogram models using all the data set for the range and only the data of small support for the sill, and by conditioning the PAH simulations using the whole data set. Confrontation of the geostatistical model to the remediation results was performed at different scales, and required a discussion on the cumulative effects of data support, heterogeneity of the pollutant phenomenon, and sampling/analytical errors. Most of the residual pollution after remediation appeared to be associated with areas where probabilities of exceeding the regulatory levels were low, which questioned the relevance of the stationarity hypothesis and required explanations to the decision-makers. The key to successful communication seemed to be providing the essential information but not the details, making understandable the different sources of uncertainty, and producing illustrations directly usable by the decision-makers. &lt;A HREF=&quot;http://geostats2012.nr.no/pdfs/1747957.pdf&quot;&gt;http://geostats2012.nr.no/pdfs/1747957.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:33:59 GMT</pubDate>
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		<title>PERMEABLE ADSORBING BARRIER FOR GROUNDWATER PROTECTION FROM SINGLE-COMPOUNDS AND MULTICOMPONENT CONTAMINATION BY CHLORINATED ORGANIC COMPOUNDS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9936</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9936</guid>
		<description>Bortone, I., A. Di Nardo, M. Di Natale, A. Erto, and D. Musmarra.&lt;br /&gt;
Chemical Engineering Transactions, Vol 35, 2013 &lt;br /&gt;&lt;br /&gt; This paper presents a procedure for designing a permeable adsorbing barrier (PAB) for the remediation of an aquifer contaminated by PCE and TCE at a site located near a solid waste landfill in the metropolitan area north of Naples (Italy). Based on hydrological and geotechnical characterization of the entire contaminated aquifer, the design and optimization of the barrier parameters (location, orientation, and dimensions) are defined by an iterative procedure using a computational fluid dynamics approach. Adsorption tests on a commercial activated carbon were carried out to support the PAB design. Model results indicate that the PAB design is effective for the remediation of the contaminated aquifer for both single-compound and binary contamination; effluent flowing out of the barrier is lower than the concentration limits provided for Italian groundwater quality regulations. &lt;A HREF=&quot;http://www.aidic.it/pres13/full/9bortone.docx&quot;&gt;http://www.aidic.it/pres13/full/9bortone.docx&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:33:22 GMT</pubDate>
	</item>

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		<title>EVALUATION OF ZEROVALENT ZINC FOR TREATMENT OF 1,2,3-TRICHLOROPROPANE-CONTAMINATED GROUNDWATER: LABORATORY AND FIELD ASSESSMENT [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9935</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9935</guid>
		<description>Salter-Blanc, A.J., E.J. Suchomel, J.H. Fortuna, J.T. Nurmi, C. Walker, T. Krug, S. O&apos;Hara, N. Ruiz, T. Morley, and P.G. Tratnyek.&lt;br /&gt;
Groundwater Monitoring &amp; Remediation, Vol 32 No 4, 42-52, 2012 &lt;br /&gt;&lt;br /&gt; The efficacy and feasibility of using zero-valent zinc (ZVZ) to treat 1,2,3-trichloropropane (TCP)-contaminated groundwater was assessed in lab and field experiments. The reactivity of commercially available granular ZVZ toward TCP was measured in bench-scale batch-reactor and column experiments, and the results were used to design columns for on-site pilot-scale treatment of contaminated groundwater at a site in Southern California. Two of the ZVZ materials tested were found to produce relatively high rates of TCP degradation as well as predictable behavior when scaling from bench-scale to field testing. Little decrease in TCP degradation rate was observed over the duration of field testing, and no secondary impacts to water quality were identified. [&lt;i&gt;Additional information on this work is available at &lt;A HREF=&quot;http://www.ebs.ogi.edu/tratnyek/resources/docs/Salter10-TCPvsZVZ-Chlorcon525.pdf&quot;&gt;http://www.ebs.ogi.edu/tratnyek/resources/docs/Salter10-TCPvsZVZ-Chlorcon525.pdf&lt;/A&gt;.&lt;/i&gt;] &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:32:52 GMT</pubDate>
	</item>

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		<title>APPLICATION OF MICROWAVE-ASSISTED TECHNOLOGIES FOR THE ANALYSIS OF CHLORINATED SOLVENTS IN ROCK SAMPLES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9934</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9934</guid>
		<description>Kusinski, Matthew, Master&apos;s thesis, University of Waterloo, ON, Canada. 95 pp, 2012 &lt;br /&gt;&lt;br /&gt; Rock cores used in the study of microwave-assisted technologies to analyze chlorinated solvents present in rock samples were collected from a dolostone aquifer in Guelph, Ontario, Canada. The cores possessed low permeability for analyte extraction while containing significant moisture internally in micropores. A technique that combines microwave heating, purge-and-trap concentration, and cryotrap focusing achieved results comparable to the established MAE-GC-&amp;micro;ECD method while avoiding extraction solvent costs, sample cross-contamination from aliquot removal, or analyte loss. The method allows the operator to monitor relevant ion fragments via the use of a mass selective detector, which is particularly useful when performing extractions of environmental samples contaminated with numerous pollutants. &lt;A HREF=&quot;http://uwspace.uwaterloo.ca/handle/10012/6535&quot;&gt;http://uwspace.uwaterloo.ca/handle/10012/6535&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:32:30 GMT</pubDate>
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		<title>REMOTE SENSING TECHNIQUES FOR PREDICTING EVAPOTRANSPIRATION FROM MIXED VEGETATED SURFACES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9933</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9933</guid>
		<description>Nouri, H., S. Beecham, F. Kazemi, A.M. Hassanli, and S. Anderson.&lt;br /&gt;
Hydrology and Earth System Sciences Discussions, Vol 10, 3897-3925, 2013 &lt;br /&gt;&lt;br /&gt; Quantifying evapotranspiration (ET) from mixed landscape vegetation environs, such as innovative ET covers, is complicated and challenging due to the heterogeneity of plant species, canopy covers, and microclimates, as well as the potentially costly methodological requirements. This review discusses the strengths and weaknesses of general remote sensing-based approaches to estimate ET. Because most of them are expensive and need extensive time investment and a medium to high level of skill, the simplest approach is recommended for application to mixed vegetation, and the vegetation indices-based approach is discussed for two categories of agricultural and non-agricultural environs.&lt;br /&gt;
&lt;A HREF=&quot;http://www.hydrol-earth-syst-sci-discuss.net/10/3897/2013/hessd-10-3897-2013-print.pdf&quot;&gt;http://www.hydrol-earth-syst-sci-discuss.net/10/3897/2013/hessd-10-3897-2013-print.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:32:07 GMT</pubDate>
	</item>

<item>

		<title>REMOVAL OF ARSENIC AND HEAVY METALS FROM POTABLE WATER BY BAUXSOL IMMOBILIZED ONTO WOOL FIBERS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9932</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9932</guid>
		<description>Hassan, M.M. and J.F. Davies-McConchie.&lt;br /&gt;
Industrial &amp; Engineering Chemistry Research, Vol 51 No 28, 9634-9641, 2012 &lt;br /&gt;&lt;br /&gt; Filters made from Bauxsol immobilized onto wool were investigated for removal of arsenite and heavy metals from water. The exhaustion technique was found most effective for immobilizing Bauxsol onto wool. Of the two types of Bauxsol investigated&amp;mdash;unneutralized (Bauxsol-A) and acid-neutralized (Bauxsol-B)&amp;mdash;the removal efficiency of arsenite by Bauxsol-B was considerably higher (53.3%) than that of Bauxsol-A (34.4%). A pilot-scale trial of a Bauxsol-B-bonded wool fiber filtration system showed that it successfully removed arsenite, lead, copper, and zinc from water. The best results were obtained for the removal of lead and copper, as their removal reached 100% and 96%, respectively. Increased contact time had a significant effect on removal efficiency; e.g., removal of copper increased from 10.2% to 96% when the contact time was extended from 5.4 min to 86.4 min. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:31:49 GMT</pubDate>
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<item>

		<title>LONG-TERM PAH MONITORING RESULTS FROM THE ANACOSTIA RIVER ACTIVE CAPPING DEMONSTRATION USING POLYDIMETHYLSILOXANE (PDMS) FIBERS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9931</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9931</guid>
		<description>Lampert, D.J., X. Lu, and D.D. Reible.&lt;br /&gt;
Environmental Science: Processes &amp; Impacts, Vol 15 No 3, 554-562, 2013 &lt;br /&gt;&lt;br /&gt; Passive PDMS measurements of high-resolution vertical pore water concentration profiles were used to infer fate and transport of PAHs at a field demonstration of active caps on contaminated sediments at the Anacostia River in Washington, DC. The pore water concentration profiles were used to assess chemical migration through the capping materials. Solid-phase concentration could not be used for comparison due to the limited sorption capacity of sand. Because of surface re-contamination, low sorption capacity in the demonstration caps, and strong tidal pumping effects, steady-state contaminant profiles were reached in the caps several years after placement. The measurements indicated lower contamination levels in the capped areas relative to the control area. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:31:34 GMT</pubDate>
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<item>

		<title>MATERIAL FLOW ANALYSIS: AN EFFECTIVENESS ASSESSMENT TOOL FOR IN SITU THERMAL REMEDIATION [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9930</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9930</guid>
		<description>Laumann, S., V. Micic, J. Fellner, D. Clement, and T. Hofmann.&lt;br /&gt;
Vadose Zone Journal, Vol 12 No 1, 2013 &lt;br /&gt;&lt;br /&gt; The effectiveness of in situ thermal desorption (ISTD) in the vadose zone was assessed by applying material flow analysis (MFA). The simultaneous application of heat and vacuum via ISTD was used to remove a chlorinated solvent source from unsaturated soil beneath an existing aboveground infrastructure. The remediation target value in soil vapor was achieved after nine months of remediation, demonstrating the time efficiency of ISTD for this particular site. The principle of matter conservation used in MFA enabled the quantification of chlorinated solvent flows in soil, groundwater, and soil vapor and also provided an overview of the processes and contaminant transformations occurring in these compartments during the course of remediation. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:31:19 GMT</pubDate>
	</item>

<item>

		<title>BEHAVIOR AND FATE OF PFOA AND PFOS IN SANDY AQUIFER SEDIMENT [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9929</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9929</guid>
		<description>Ferrey, M.L., J.T. Wilson, C. Adair, C. Su, D.D. Fine, X. Liu, and J.W. Washington.&lt;br /&gt;
Groundwater Monitoring &amp; Remediation, Vol 32 No 4, 63-71, 2012 &lt;br /&gt;&lt;br /&gt; Microcosms were constructed with sediment from beneath a landfill that received waste containing PFOA (perfluorooctanoic acid) and PFOS (perfluorooctane sulfonate). Observation suggests that the sorption of PFOA and PFOS at near-neutral pH was controlled by electrostatic sorption on ferric oxide minerals and not by sorption to organic carbon. Results indicate that accurate predictions of PFOA and PFOS mobility in groundwater should be based on empirical estimates of sorption using affected aquifer sediment. This paper is Open Access at &lt;A HREF=&quot;http://onlinelibrary.wiley.com/doi/10.1111/j.1745-6592.2012.01395.x/full&quot;&gt;http://onlinelibrary.wiley.com/doi/10.1111/j.1745-6592.2012.01395.x/full&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:31:05 GMT</pubDate>
	</item>

<item>

		<title>FIELD-SCALE ASSESSMENT OF DESICCATION IMPLEMENTATION FOR DEEP VADOSE ZONE CONTAMINANTS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9928</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9928</guid>
		<description>Truex, M.J., M. Oostrom, C.E. Strickland, G.B. Chronister, M.W. Benecke, and C.D. Johnson.&lt;br /&gt;
Vadose Zone Journal, Vol 11 No 4, 2012 &lt;br /&gt;&lt;br /&gt; Desiccation of the vadose zone has the potential to reduce the flux of contaminants to underlying groundwater by removing moisture and decreasing the water-relative permeability of the desiccated zone. Implementation of desiccation was field-tested by injecting dry nitrogen gas to a target treatment zone and monitoring the spatial and temporal progress of the drying process. The test was conducted adjacent to one of the former disposal cribs in a contaminated (primarily technetium-99 and nitrate) portion of the vadose zone dominated by fine sands with lenses of loamy sand. Desiccation removed over 18,000 kg of water from the test zone within the 151-day active desiccation period. The lateral and vertical distribution of drying from the injection well was influenced by the subsurface heterogeneity, with initial drying in higher permeability zones. Over time, desiccation also occurred in the wetter, lower permeability lenses. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:30:50 GMT</pubDate>
	</item>

<item>

		<title>ASSESSING PERFORMANCE AND CLOSURE FOR SOIL VAPOR EXTRACTION: INTEGRATING VAPOR DISCHARGE AND IMPACT TO GROUNDWATER QUALITY [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9927</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9927</guid>
		<description>Carroll, K.C., M. Oostrom, M.J. Truex, V.J. Rohay, and M.L. Brusseau.&lt;br /&gt;
Journal of Contaminant Hydrology, Vol 128 Nos 1-4, 71-82, 2012 &lt;br /&gt;&lt;br /&gt; After soil vapor extraction (SVE) has been operated for a period of time and the remaining contamination is located primarily in low-permeability zones, the remedy performance needs to be evaluated to determine whether the SVE system should be optimized, terminated, or transitioned to another technology to replace or augment SVE. Mathematical-model simulations can be used to characterize the relationship between the short-term source vapor mass discharge rate, measurable using SVE system operational data, and predicted groundwater contaminant concentration as a function of vadose zone source size and strength. The method enables consideration of alternative conceptual site models to evaluate how uncertainty in site parameters affects the predicted impact to groundwater. [&lt;i&gt;See slide 9 in &quot;DOE Case Studies: End States for Vadose Zone Environments&quot; at &lt;A HREF=&quot;http://cluin.org/meetings/frtr/presentations/truex-presentation.pdf&quot;&gt;http://cluin.org/meetings/frtr/presentations/truex-presentation.pdf&lt;/A&gt; for an illustration of the SVE guidance and calculation tool.&lt;/i&gt;] &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:30:35 GMT</pubDate>
	</item>

<item>

		<title>AN INNOVATIVE TECHNIQUE FOR REMEDIATION OF GROUNDWATERS: DISCONTINUOUS PERMEABLE REACTIVE BARRIERS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9926</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9926</guid>
		<description>Bortone, I., A. Di Nardo, M. Di Natale, D. Musmarra, and G.F. Santonastaso.&lt;br /&gt;
Crete 2012: Third International Conference on Industrial and Hazardous Waste Management, Technical University of Crete, 8 pp, 2012 &lt;br /&gt;&lt;br /&gt; In this work, an innovative solution for a permeable reactive barrier (PRB) is based on the proposed design for a discontinuous PRB (PRB-D), using absorbing materials and configured as a grid of deep passive wells. This solution would allow the application of PRB technology to deep aquifers and make its realization more flexible and less costly. A well-characterized PCE-contaminated aquifer close to Naples (Italy) provides the setting for the modeled design, and the results are compared with those obtained for a continuous PRB on the same site. &lt;A HREF=&quot;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16571&quot;&gt;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16571&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:30:15 GMT</pubDate>
	</item>

<item>

		<title>SULFATE REDUCTION IN GROUNDWATER: CHARACTERIZATION AND APPLICATIONS FOR REMEDIATION [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9925</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9925</guid>
		<description>Miao, Z., M.L. Brusseau, K.C. Carroll, C. Carreon-Diazconti, and B. Johnson.&lt;br /&gt;
Environmental Geochemistry &amp; Health, Vol 34 No 4, 539-550, Aug 2012 &lt;br /&gt;&lt;br /&gt; Sulfate reduction reactions play a significant role in mediating redox conditions and biogeochemical processes for subsurface systems. They also serve as the basis for innovative in-situ methods for groundwater remediation. This paper provides an overview of sulfate reduction in subsurface environments with a specific focus on implications for groundwater remediation resulting from acid mine drainage. A case study presenting the results of a pilot-scale ethanol injection illustrates the advantages and difficulties associated with the use of electron-donor amendments for sulfate remediation. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:29:45 GMT</pubDate>
	</item>

<item>

		<title>IN SITU SODIUM PERSULFATE OXIDATION OF BENZENE UNDER AMBIENT ACTIVATION [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9924</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9924</guid>
		<description>Shepherd, C., E. Reece, M. Klemmer, K. Brantingham, and S. Rhodes.&lt;br /&gt;
2012 AHS Annual Water Symposium, September 18-21, 2012, Phoenix, AZ. 21 slides, 2012 &lt;br /&gt;&lt;br /&gt; A pilot study was conducted in Tempe, Arizona, to optimize an in situ chemical oxidation (ISCO) remedial design for gasoline-affected groundwater. Sodium persulfate (under ambient activation, with no activator compound) and deuterated water (as a conservative tracer) were used to support the design of a prospective full-scale ISCO remedy. The injection of an 8,600-gallon solution of 40 g/L sodium persulfate and 900 per mil deuterium (~0.25 g/L) showed relatively even vertical and lateral distribution of solution around the injection well, with sodium persulfate concentrations as high as 25 mg/L up to 13 ft from the injection well. The kinetic reaction rate was found to be relatively rapid, given the ambient activation method. Following the pilot injection, dissolved benzene concentrations in the area of influence declined 50% on average from initial conditions.&lt;br&gt;&lt;br /&gt;
&lt;b&gt;Longer abstract:&lt;/b&gt; &lt;A HREF=&quot;http://azhydrosoc.org/2012Symposium/docs/abstracts/1f_Shepherd_et%20al.pdf&quot;&gt;http://azhydrosoc.org/2012Symposium/docs/abstracts/1f_Shepherd_et%20al.pdf&lt;/A&gt; &lt;br&gt;&lt;br /&gt;
&lt;b&gt;Slides:&lt;/b&gt; &lt;A HREF=&quot;http://azhydrosoc.org/2012Symposium/docs/presentations/1f_Shepherd_ISCO_Ambient_Pilot.pdf&quot;&gt;http://azhydrosoc.org/2012Symposium/docs/presentations/1f_Shepherd_ISCO_Ambient_Pilot.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:29:16 GMT</pubDate>
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<item>

		<title>ENGINEERED PHYTOREMEDIATION PILOT STUDY FOR PETROLEUM HYDROCARBONS IN A DEEP CONFINED AQUIFER [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9923</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9923</guid>
		<description>Gatliff, E. and B. Snow.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 43 slides, 2012 &lt;br /&gt;&lt;br /&gt; The groundwater at a former petroleum refinery in Oklahoma is contaminated with benzene within an area exceeding 350 acres. An engineered phytoremediation feasibility study was installed to achieve hydraulic control of contaminant migration. Mobile- and residual-phase LNAPL is trapped within the confined aquifer beneath a 15-25 ft thick confining aquitard unit that overlies portions of the site. A plantation of 96 trees was installed using the TreeWell&amp;reg; system in five test plots: a background control group, two areas with LNAPL, a main test plot in an area with high dissolved benzene concentrations, and a closed tree lysimeter plot that measures water consumption rates. Preliminary data from the pilot study are presented. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Gatliff_EngineeredPhytoremediation_102.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Gatliff_EngineeredPhytoremediation_102.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:28:58 GMT</pubDate>
	</item>

<item>

		<title>TRIP REPORT: PRODUCED-WATER FIELD TESTING [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9922</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9922</guid>
		<description>Sullivan, E.J.&lt;br /&gt;
LA-UR-12-21661, 11 pp, 2012 &lt;br /&gt;&lt;br /&gt; Los Alamos National Laboratory conducted field testing of a produced-water pretreatment apparatus with assistance from faculty at Texas A&amp;M University. The purpose of the test was to use a new, commercially available filter media housing containing a modified zeolite (surfactant-modified zeolite, or SMZ) porous medium for use in pretreatment of oil and gas produced water (PW) and fracturing flowback waters. In lab tests, the SMZ performed well in removing BTEX from produced water. A pilot-scale test conducted in a treatment trailer demonstrated the use of a commercial filter housing packed with SMZ combined with a simple flow modification for removing BTEX from a produced water source in College Station, Texas. &lt;A HREF=&quot;http://permalink.lanl.gov/object/tr?what=info:lanl-repo/lareport/LA-UR-12-21661&quot;&gt;http://permalink.lanl.gov/object/tr?what=info:lanl-repo/lareport/LA-UR-12-21661&lt;/A&gt;&lt;br&gt; &lt;br /&gt;
Additional information is available in a slide presentation at &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Goltz.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Goltz.pdf&lt;/A&gt;. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:28:28 GMT</pubDate>
	</item>

<item>

		<title>COMBINING LOW-ENERGY ELECTRICAL RESISTANCE HEATING WITH BIOTIC AND ABIOTIC REACTIONS FOR TREATMENT OF CHLORINATED SOLVENT DNAPL SOURCE AREAS [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9921</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9921</guid>
		<description>Macbeth, T., M.J. Truex, T. Powell, and M. Michalsen.&lt;br /&gt;
ESTCP Project ER-200719, 383 pp, Dec 2012 &lt;br /&gt;&lt;br /&gt; Project ER-0719 demonstrated the combination of low-temperature subsurface heating with in situ remedies to enhance remediation performance through both increased degradation reaction rates and contaminant dissolution. Dechlorination was induced in two test cells for zero-valent iron (ZVI) and in situ bioremediation (ISB) using emulsified oil and whey powder. For the ZVI test, temperature elevated from 10&amp;deg;C to between 35-45&amp;deg;C increased dechlorination by a factor of 4 to 8. For the ISB test, a similar temperature increase accelerated overall contaminant dechlorination by a factor of 2-4 at hotspot locations close to residual contaminant mass. Field test results demonstrated that moderate heating and minor operational costs enhanced efficiency and effectiveness of in situ treatment of TCE. Capture and treatment of contaminated vapor&amp;mdash;a major cost element of standard thermal treatment&amp;mdash;was not needed as treatment maintained low aqueous TCE concentrations. The heating infrastructure was limited to subsurface electrodes and a power control unit. Results indicate the combined methods may be cost-effective in source zones with moderate contaminant mass. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18254/202725/file/ER-200719-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18254/202725/file/ER-200719-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:28:07 GMT</pubDate>
	</item>

<item>

		<title>COMPARATIVE DEMONSTRATION OF ACTIVE AND SEMI-PASSIVE IN SITU BIOREMEDIATION APPROACHES FOR PERCHLORATE IMPACTED GROUNDWATER: ACTIVE IN SITU BIOREMEDIATION DEMONSTRATION (AEROJET FACILITY) [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9920</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9920</guid>
		<description>Cox, E. and T. Krug.&lt;br /&gt;
ESTCP Project ER-200219, 848 pp, Dec 2012 &lt;br /&gt;&lt;br /&gt; During the demonstration of active enhanced in situ bioremediation at the inactive Rancho Cordova test site in California, groundwater containing perchlorate and TCE was extracted from the shallow aquifer, amended with ethanol, and recharged to the shallow aquifer to promote in situ biodegradation of the contaminants. The active biobarrier provided treatment and containment of a 600-ft wide section of the plume in the shallow aquifer using two groundwater extraction wells and a single groundwater recharge well. Results demonstrate that the site&apos;s indigenous bacteria are capable of biodegrading perchlorate using ethanol as an electron donor. Perchlorate concentrations as high as 4,300 &amp;micro;g/L were reduced to less than 4 &amp;micro;g/L within 50 ft of the recharge well. TCE dechlorination was observed at the downgradient monitor well following bioaugmentation of the shallow aquifer with KB-1 to introduce dehalorespiring bacteria. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/17440/194744/file/ER-200219-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/17440/194744/file/ER-200219-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:27:52 GMT</pubDate>
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		<title>INTEGRATED FORENSICS APPROACH TO FINGERPRINT PCB SOURCES IN SEDIMENTS USING RAPID SEDIMENT CHARACTERIZATION (RSC) AND ADVANCED CHEMICAL FINGERPRINTING (ACF) [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9919</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9919</guid>
		<description>Leather, J., G. Durell, G. Johnson, and M. Mills.&lt;br /&gt;
ESTCP Project ER-200826, SPAWAR Technical Document 3262, 228 pp, June 2012 &lt;br /&gt;&lt;br /&gt; To identify PCB sources to sediments, this project demonstrated an integrated approach to fingerprinting PCB contamination that combines sediment screening technologies on a large number of field samples followed by detailed PCB congener analysis in conjunction with advanced chemical fingerprinting data interpretation on a subset of selected laboratory samples. Sites with extensive preexisting data sets were selected for the demonstration: the South Basin at Hunters Point Shipyard, located south of San Francisco, and the Ashtabula River Dredge site, located east of Cleveland. All the techniques discussed in this report are commercially available from multiple sources. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18183/202326/file/ER-200826-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18183/202326/file/ER-200826-FR.pdf&lt;/A&gt; &lt;i&gt;See also the ESTCP Cost and Performance Report&lt;/i&gt;: &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18182/202316/file/ER-200826-C&amp;P.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18182/202316/file/ER-200826-C&amp;&lt;wbr&gt;P.pdf&lt;/A&gt;. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:27:22 GMT</pubDate>
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		<title>COMPARISON OF APPROACHES TO ENGINEERED IN SITU BIOGEOCHEMICAL TRANSFORMATION OF CHLORINATED SOLVENTS [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9918</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9918</guid>
		<description>Henry, B.M.&lt;br /&gt;
REMTECH 2012: The Remediation Technologies Symposium, Banff, AB, Canada, 17-19 Oct 2012. Environmental Services Association of Alberta, Edmonton, AB (Canada), 37 slides, 2012 &lt;br /&gt;&lt;br /&gt; The U.S. Air Force has funded demonstrations to stimulate biogeochemical transformation of chlorinated solvents by addition of iron and sulfate into the subsurface at Air Force facilities in Alaska, Utah, Oklahoma, and Hawaii. Two demonstrations involved injection of various forms of sulfate, iron, and emulsified vegetable oil directly into the subsurface. Another demonstration involved the injection of ferrous sulfate into a solar-powered recirculating bioreactor. The fourth demonstration involved emplacement of a high-iron basalt sand in a mulch bioreactor within a high-sulfate groundwater plume. Stimulating biogeochemical transformation of PCE and TCE was most effective where a source of sulfate was sustained and organic substrate was limited to &lt;100-200 mg/L. Under these conditions, iron and sulfate reduction produce sufficient quantities of FeS minerals to enhance abiotic dechlorination of PCE and TCE before a microbial population capable of sequential halorespiration of PCE and TCE to DCE and vinyl chloride fully acclimates. &lt;A HREF=&quot;http://www.esaa-events.com/remtech/2012/pdf/12-Henry.pdf&quot;&gt;http://www.esaa-events.com/remtech/2012/pdf/12-Henry.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:26:50 GMT</pubDate>
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		<title>OCCURRENCE AND REMEDIATION OF PCE AND OTHER CHLORINATED SOLVENTS IN SYDNEY URBAN GROUNDWATER SYSTEMS [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9917</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9917</guid>
		<description>Nash, J.M., L. Rockett, and K. Plambeck.&lt;br /&gt;
Crete 2012: 3rd International Conference on Industrial and Hazardous Waste Management. Technical University of Crete, 7 pp, 2012 &lt;br /&gt;&lt;br /&gt; This paper examines the investigation and remediation strategies adopted for two PCE-contaminated sites in the Sydney (Australia) metropolitan area and looks at the similarities and differences in terms of the contaminant transport mechanisms, lithological conditions, effects on neighboring properties, and the remedial strategies adopted (i.e., monitored natural attenuation and a biostimulation pilot study, respectively). The lessons learned can be applied to the investigation and remediation of similar sites. &lt;A HREF=&quot;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16575&quot;&gt;http://www.srcosmos.gr/srcosmos/showpub.aspx?aa=16575&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:26:36 GMT</pubDate>
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		<title>ENGINEERED PHYTOREMEDIATION OF BENZENE, GROS, DROS AND OTHER VOCS IN GROUNDWATER [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9916</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9916</guid>
		<description>Gatliff, E.G., F. Manale, S. Lucas, and M. Siegman.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 43 slides, 2012 &lt;br /&gt;&lt;br /&gt; Two phytoremediation pilots were installed in 2007 at sites in central Michigan to assess the potential for engineered phytoremediation to (1) gain hydraulic control of the local groundwater units and (2) remediate groundwater containing elevated concentrations of dichloropropane, benzene, gasoline range organics (GROs), diesel range organics (DROs), and other VOCs. The Root_Sleeve&amp;trade; liner of the TreeWell&amp;reg; engineered phytoremediation system is designed to treat the groundwater via a bioreactor effect before the groundwater contacts the root system. This bioreactor effect is demonstrated in the sampling data as well as by the absence of phytotoxic effects of the elevated contaminant concentrations on the trees, most of which realized aggressive and healthy growth. The few occurrences of phytotoxicity were attributed to elevated chloride levels. Hydraulic data show increasing hydraulic effects with each growing season. Groundwater in the pilot study area has shown progressive reductions in contaminant concentrations (~20% cumulatively) over the 5-year term of the study. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Gatliff.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Gatliff.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:26:20 GMT</pubDate>
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		<title>REMEDIATION OF A FORMER GASWORKS USING IN-SITU SOLIDIFICATION TECHNOLOGY [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9915</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9915</guid>
		<description>von Schwerin, B., P. Carstairs, and C. Cowper.&lt;br /&gt;
2012 Taipei International Conference on Remediation and Management of Soil and Ground Water Contaminated Sites, October 30-31, 2012, Taipei, Taiwan. 549-561 (paper &amp; slides), 2012 &lt;br /&gt;&lt;br /&gt; The proposed upgrade of an existing car park on a former gasworks site in Australia led to the identification of significant residual gasworks contamination in the form of coal tar DNAPL despite remediation activities conducted 16 years earlier. Proof-of-performance bench-scale and field pilot trials of in situ solidification enabled the selection of a cost-effective remediation approach to address future site needs and meet performance requirements. The adopted remediation strategy incorporates a holistic approach to managing site issues by addressing the impacted shallow soil with ex situ solidification; tarry soil below the water table with in situ solidification; impacts in groundwater with pump and treat; and community engagement throughout the project. [&lt;i&gt;The paper begins on &lt;b&gt;page 549&lt;/b&gt; in the portion of the proceedings (pages 423-610) that opens at the link.&lt;/i&gt;] &lt;A HREF=&quot;http://sgw.epa.gov.tw/resag/Update_Data/Information9053129Oct_30-31_Proceedings_1106_1230_Brief_S7-9.pdf&quot;&gt;http://sgw.epa.gov.tw/resag/Update_Data/Information9053129Oct_30-31_Proceedings_1106_1230_Brief_S7-9.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:25:51 GMT</pubDate>
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		<title>IN SITU &apos;DELIVERABILITY&apos; TRIALS USING CALCIUM POLYSULPHIDE TO TREAT CHROMIUM CONTAMINATION AT SHAWFIELD, GLASGOW [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9914</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9914</guid>
		<description>Bewley, R. and G. Sojka.&lt;br /&gt;
CL:AIRE (Contaminated Land: Applications in Real Environments), Technology Demonstration Project Bulletin TDP30, 8 pp, Feb 2013 &lt;br /&gt;&lt;br /&gt; Calcium polysulfide (CaSx) reduces highly soluble Cr(VI) compounds to much less soluble and comparatively harmless Cr(III) compounds. Following earlier field trials that indicated the effectiveness of CaSx application in reducing Cr(VI) associated with chromite ore processing residue, another field trial was conducted in 2009 to identify the most effective mechanism for delivering CaSx into the subsurface. The CaSx delivery methods investigated were (1) a groundwater recirculation system (which also achieved in situ flushing of contaminated soil); (2) direct-push injection using close grid spacing; and (3) soil mixing. All three trials provided evidence of total Cr mobilization as a combination of chemical-physical action. [NOTE: &lt;i&gt;The bulletin is available without charge on the CL:AIRE website to registered users (also free) at &lt;A HREF=&quot;http://www.claire.co.uk/&quot;&gt;http://www.claire.co.uk/&lt;/A&gt;. An online read-only copy is available at &lt;A HREF=&quot;http://www.slideshare.net/slideshow/embed_code/20401310&quot;&gt;http://www.slideshare.net/slideshow/embed_code/20401310&lt;/A&gt;.&lt;/i&gt;] &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:24:34 GMT</pubDate>
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		<title>CONSTRUCTION AND OPERATION OF A GRAVEL BED REACTOR: BIODEGRADATION OF NITRATE [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9913</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9913</guid>
		<description>Fricke, R.&lt;br /&gt;
Symposium: Salt and Nitrate in Groundwater: Finding Solutions for a Widespread Problem, June 13-14, 2012, Fresno, CA. Groundwater Resources Association of California, Abstract only, 2012 &lt;br /&gt;&lt;br /&gt; Several bioremediation methods have been tested and implemented at Aerojet&apos;s inactive Rancho Cordova test site. The current system consists of a gravel bed reactor (GBR) for treating nitrate and perchlorate. Citric acid is the electron donor, and indigenous bacteria utilize the oxygen from nitrate and perchlorate during the respiration of the citric acid. The GBR was constructed using a 40-foot shipping container, PVC liner, and 3/4-inch crushed rock. It has a pore volume of about 7,200 gallons. With a probable hydraulic capacity of 100 gallons per minute (gpm), the GBR currently operates at about 30 gpm. Influent nitrate concentrations varied from 10-13 mg/L during 2012; effluent concentrations have ranged from non-detect to 0.2 mg/L. Perchlorate concentrations varied from 0.1-0.3 mg/L in the influent but were non-detect in effluent during 2012. The GBR could treat much higher perchlorate concentrations. Sulfate can be reduced in the GBR if the oxidation-reduction potential (ORP) is too low. Iron and manganese are mobilized by the low ORP but generally have declined in concentration. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:24:07 GMT</pubDate>
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		<title>EVAPORATIVE DESORPTION TECHNOLOGY (EDT): AN ADVANCEMENT IN FLAMELESS THERMAL REMEDIATION [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9912</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9912</guid>
		<description>Sutton, M.C., P.D. Horton, P.R. Brady, and D.W. Moore.&lt;br /&gt;
RemTEC Summit, 4-6 March 2013, Westminster, Colorado. Poster, 2013 &lt;br /&gt;&lt;br /&gt; Elevated concentrations of PCE &gt;50,000 &amp;micro;g/kg and degradation compounds remained in tight, Bay mud soil at a former industrial dry cleaning facility located near the margin of the San Francisco Bay. Following excavation and off-site disposal of the more accessible contaminated soil, implementation of evaporative desorption technology (EDT) reduced PCE concentrations to below 20 &amp;micro;g/kg, and in most cases below 5 &amp;micro;g/kg. EDT is differentiated from other thermal technologies by the lower treatment temperature, limited air emissions, regulatory acceptance and permitting (similar to soil vapor extraction), and the remedial certainty of ex situ treatment by excavation and on-site treatment and reuse.&lt;br&gt; &lt;b&gt;Poster:&lt;/b&gt; &lt;A HREF=&quot;http://www.reterro.com/edt-advancement.pdf&quot;&gt;http://www.reterro.com/edt-advancement.pdf&lt;/A&gt; &lt;br&gt;&lt;b&gt;Longer abstract:&lt;/b&gt; &lt;A HREF=&quot;http://www.remtecsummit.com/index.php/component/content/article?id=498:amin-bio&amp;catid=232&quot;&gt;http://www.remtecsummit.com/index.php/component/content/article?id=498:amin-bio&amp;&lt;wbr&gt;catid=232&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:23:45 GMT</pubDate>
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<item>

		<title>TAMING THE &quot;TOWER PLUME&quot; [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9911</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9911</guid>
		<description>Zaney, R.&lt;br /&gt;
The Military Engineer, Vol 105 No 681, Nov-Dec 2012 &lt;br /&gt;&lt;br /&gt; Reese Air Force Base was recommended for closure in 1991, but property transfer was stalled by contamination issues: petroleum products and chlorinated solvents contaminated the soil and groundwater, with one of the solvent plumes extending more than two miles off base, affecting more than two dozen residential water systems. Enhanced in situ biodegradation was implemented using molasses as the electron donor. Coupled with an innovative directed groundwater recirculation system, pump-and-treat technology was used to decrease the size of the plume. The elevated dissolved oxygen levels in the treated water helped restore the portions of the aquifer that had undergone reductive dechlorination. Groundwater monitoring results were used to adjust the extraction and injection patterns on at least a quarterly basis to target the plume reduction. The Tower Plume has been shrinking by 2-3 acres per week since 2006. From the original 800 acres of contaminated groundwater, today less than one acre of contamination remains. Environmental regulators require three annual clean sample results before the Air Force can officially complete remediation of the plume at Reese, estimated for 2014.&lt;br /&gt;
&lt;A HREF=&quot;http://themilitaryengineer.com/index.php/component/k2/item/192-taming-the-%E2%80%9Ctower-plume%E2%80%9D&quot;&gt;http://themilitaryengineer.com/index.php/component/k2/item/192-taming-the-%E2%80%9Ctower-plume%E2%80%9D&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:23:30 GMT</pubDate>
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		<title>LESSONS LEARNED FROM IMPLEMENTATION OF IN-SITU CHEMICAL OXIDATION REMEDIATION [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9910</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9910</guid>
		<description>Pickens, W.E., R.P. Hultgren, and J. TeGrotenhuis.&lt;br /&gt;
2012 Taipei International Conference on Remediation and Management of Soil and Ground Water Contaminated Sites, October 30-31, 2012, Taipei, Taiwan. 677-703 (paper &amp; slides), 2012 &lt;br /&gt;&lt;br /&gt; A well-studied site located in Denver, Colorado, is contaminated with chlorinated solvents, pesticides, and herbicides from its former use as a chemical distribution facility. A PCE plume in the groundwater extends about 0.7 kilometers downgradient from the facility, and PCE concentrations in groundwater were detected at levels up to 6,700 &amp;micro;g/L. A combination of shallow impacted soil excavation, soil vapor extraction, and in situ chemical oxidation (ISCO) using sodium permanganate was identified as the most viable remedial approach. ISCO injections were performed in December 2007 and August-September 2010. Groundwater samples collected 20 months after the second round of injections showed 70-100% (by weight) decreases in PCE concentration in monitoring wells within 22 meters of the injection locations, as well as significant reductions in PCE concentrations in the majority of the monitoring wells within 91 meters downgradient of the injection wells. [&lt;i&gt;The paper begins on&lt;b&gt; page 677&lt;/b&gt; in the portion of the proceedings (pages 611-768) that opens at the link.&lt;/i&gt;] &lt;A HREF=&quot;http://sgw.epa.gov.tw/resag/Update_Data/Information9051423Oct_30-31_Proceedings_1106_1230_Brief_S10-11.pdf&quot;&gt;http://sgw.epa.gov.tw/resag/Update_Data/Information9051423Oct_30-31_Proceedings_1106_1230_Brief_S10-11.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:23:14 GMT</pubDate>
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		<title>GEOCHEMICAL CHARACTERIZATION AND LONGEVITY ESTIMATES OF A PERMEABLE REACTIVE BARRIER SYSTEM REMEDIATING A 90SR PLUME [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9909</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9909</guid>
		<description>Hoppe, Jutta, Master&apos;s thesis, University of Waterloo, Waterloo, ON, Canada, 144 pp, 2012 &lt;br /&gt;&lt;br /&gt; In 1998, a &quot;wall and curtain&quot; permeable reactive barrier (PRB) containing clinoptilolite as a reactive material was installed at the Chalk River Laboratories in Chalk River, Ontario, to prevent discharge of a strontium-90 plume into a nearby swamp. After nearly 14 years of operation, refined estimates of the PRB&apos;s efficiency and longevity indicate the system is highly efficient in treating an average mass flux of &gt;17,000 Bq/m&lt;sup&gt;2&lt;/sup&gt;/day and could continue to function for 80 to 100 years. &lt;A HREF=&quot;http://uwspace.uwaterloo.ca/handle/10012/7293&quot;&gt;http://uwspace.uwaterloo.ca/handle/10012/7293&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:22:44 GMT</pubDate>
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		<title>DUS II SOIL GAS SAMPLING AND AIR INJECTION TEST RESULTS [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9908</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9908</guid>
		<description>Noonkester, J., D. Jackson, W. Jones, W. Hyde, J. Kohn, and R. Walker.&lt;br /&gt;
SRNL-STI-2012-00449, 32 pp, 2012 &lt;br /&gt;&lt;br /&gt; Soil vapor extraction (SVE) and air injection well testing was performed at the dynamic underground stripping (DUS) site located near the M-Area Settling Basin. The objective of the DUS II tests was to determine the effectiveness of continued system operation in removing PCE and TCE from the subsurface. The SVE operations have utilized residual heat present in the subsurface since steam injection ended on September 19, 2009. While traditional air sparging (AS) is not a primary component of the DUS process (although AS often is coupled with SVE when contaminant recovery is necessary), eight of the 63 steam injection wells were used to inject air after steam injection ended. The test results will be used to determine the wells that should continue in active SVE operation and to identify wells that can be transitioned from active to passive treatment systems. The test data also will be used to provide a technical basis to determine which components of the well infrastructure should remain for future corrective action activities. &lt;A HREF=&quot;http://sti.srs.gov/fulltext/SRNL-STI-2012-00449.pdf&quot;&gt;http://sti.srs.gov/fulltext/SRNL-STI-2012-00449.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:22:29 GMT</pubDate>
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		<title>ANAEROBIC TREATMENT AND HYDROCARBON SEEPAGE CONTOL USING MODIFICATIONS TO NATURAL STREAM MORPHOLOGY [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9907</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9907</guid>
		<description>Binder, J.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 28 slides, 2012 &lt;br /&gt;&lt;br /&gt; Hydrocarbon seeps were entering an oxbow along a creek adjacent to a former refinery at a site in north-central Oklahoma. As an interim remedial measure, the site contractor rerouted the creek and constructed a biologically active interceptor trench in the former oxbow. Varying proportions and mixtures of gravel, limestone sand, wood chips, cow manure, and gypsum were emplaced in different zones with the trench, which collects any free-phase hydrocarbon and treats the impacted waters via anaerobic biological processes prior to discharge to the creek channel. The system is sampled regularly and monitored to assess water quality at the discharge outfall and in groundwater near the treatment trench. &lt;br /&gt;
&lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Binder.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Binder.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:22:14 GMT</pubDate>
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		<title>IN SITU THERMAL DESORPTION OF LNAPL-CONTAMINATED SOIL WITH HIGH-ENERGY EFFICIENCY [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9906</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9906</guid>
		<description>Geckeler, G., H. Saadaoui, and J. Haemers.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 13 slides, 2012 &lt;br /&gt;&lt;br /&gt; A 2011/2012 in situ thermal desorption (ISTD) remediation of hydrocarbon-contaminated soils was conducted at an active refinery in France. The propane-fueled ISTD system remediated contaminated soils from &gt;10,000 mg/kg to less than 10 mg/kg during 25 days of operation. Gaseous-phase hydrocarbons removed via soil vapor extraction were directed to the ISTD device and used as supplemental fuel, which reduced ISTD propane consumption by over 50%. This technique also destroyed off-gas vapors, removing the need for traditional thermal oxidation equipment to meet local air emissions. The large-scale project used new modular grid arrangements to prevent disruption of refinery operations. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Geckeler.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Geckeler.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:21:59 GMT</pubDate>
	</item>

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		<title>FIRST STATE-FUNDED CLEANUP USING ELECTRICAL RESISTIVITY HEATING TECHNOLOGY [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9905</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9905</guid>
		<description>Van Riper, E.&lt;br /&gt;
The DEQbicle, Fall 2012 &lt;br /&gt;&lt;br /&gt; The Remediation and Redevelopment Division of the Michigan Department of Environmental Quality completed remediation of PCE in the soil and groundwater under a former dry cleaning facility in the city of Owosso using electrical resistivity heating (ERH). An operating medical center and restaurant currently occupy the site of the former Launderama Dry Cleaner in Owosso&apos;s downtown business district. The restaurant was closed for two weeks while the ERH system was installed below grade. The system comprised 83 borings drilled to a depth of 14 ft, electrodes installed in each boring, and a vapor extraction well at each electrode location. ERH operation began on January 9, 2012, reached the goal temperature of 88&amp;deg;C on March 9, and continued until its decommissioning on June 7, having removed 821 lbs of VOCs. Initial verification sampling conducted in July 2012 indicated &gt;90% reduction in site soil concentrations. Additional soil gas monitoring and verification sampling will continue until the end of 2013. &lt;A HREF=&quot;http://www.deq.state.mi.us/eforms/deqbicle/Fall2012/ThermalRemediation.htm&quot;&gt;http://www.deq.state.mi.us/eforms/deqbicle/Fall2012/ThermalRemediation.htm&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:21:39 GMT</pubDate>
	</item>

<item>

		<title>EMERGENCY RESPONSE [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9904</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9904</guid>
		<description>Department of the Air Force, Air Combat Command, Tyndall AFB, FL.&lt;br /&gt;
Federal Business Opportunities, FBO-4158, Solicitation FA4819-12-T-0054, 2013 &lt;br /&gt;&lt;br /&gt; Air Combat Command is seeking a contractor to provide all manpower, equipment, supplies, oversight and management, recordkeeping, and administration for the services necessary to support emergency and non-emergency response and cleanup activities at Tyndall Air Force Base related to spills and accidental discharges of hazardous and non-hazardous materials. Proposals are due no later than May 17, 2013, 1:00 PM CT. &lt;A HREF=&quot;https://www.fbo.gov/notices/46b1612d246cd238bad0487f0ebb530f&quot;&gt;https://www.fbo.gov/notices/46b1612d246cd238bad0487f0ebb530f&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:21:17 GMT</pubDate>
	</item>

<item>

		<title>DOD SBIR 2013.2 [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9903</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9903</guid>
		<description>Department of Defense, Washington Headquarters Services, WHS, Acquisition Directorate.&lt;br /&gt;
Federal Business Opportunities, FBO-4171, Solicitation DoDSBIR13-2, 2013 &lt;br /&gt;&lt;br /&gt; Small high-technology firms are encouraged to submit proposals to DoD for its Small Business Innovation Research (SBIR) Program 2013.12 for projects with both military and commercial applications. This SBIR opportunity will be publicly released on May 24, 2013, on the DoD SBIR website at &lt;A HREF=&quot;http://www.dodsbir.net/solicitation/&quot;&gt;http://www.dodsbir.net/solicitation/&lt;/A&gt;. The window for receipt of proposals will close at 6:00 AM ET on June 26, 2013. The solicitation lists all of the R&amp;D topics under which DoD is seeking proposals, and also contains detailed information on the parameters of the SBIR program and how to submit a proposal. [NOTE: The few DoD needs areas for this SBIR opportunity with potential environmental application include A13-079: Convergence of sensor technologies into a tool for assessing environmental contaminants, and DHP13-005: Rapid ID of microbial pathogens from food, water, and environmental samples.] &lt;A HREF=&quot;https://www.fbo.gov/spg/ODA/WHS/REF/DoDSBIR13-2/listing.html&quot;&gt;https://www.fbo.gov/spg/ODA/WHS/REF/DoDSBIR13-2/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:20:47 GMT</pubDate>
	</item>

<item>

		<title>SOURCES SOUGHT ANNOUNCEMENT FOR RISK ASSESSMENT SUPPORT [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9902</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9902</guid>
		<description>U.S. Environmental Protection Agency, Office of Acquisition Management, Washington, DC.&lt;br /&gt;
Federal Business Opportunities, FBO-4169, Solicitation SSA-ORCR-2013, 2013 &lt;br /&gt;&lt;br /&gt; U.S. EPA is conducting market research for the Office of Resource Conservation and Recovery (ORCR) to gain knowledge of potential qualified sources and their size classifications relative to NAICS code 541620, Environmental Consulting Services, for the performance of risk assessment support services (size standard of $14M). ORCR is responsible for the assessment of potential risks and other impacts associated with the generation and management of materials originating in households and businesses, industrial process materials, and residues, and in the management of municipal and industrial solid wastes. Services will require the assessment of potential risks, benefits, costs, economic impacts, and other effects associated with the generation and management of hazardous and non-hazardous waste and hazardous substances. The Government anticipates a single contract award to fulfill this requirement for up to 5 years. Interested small business firms are asked to add their company information to an &quot;Interested Vendors List&quot; and/or to submit a capability statement as a searchable PDF file via email by 3:00 PM ET, May 13, 2013. &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/HQ/SSA-ORCR-2013/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/HQ/SSA-ORCR-2013/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:20:16 GMT</pubDate>
	</item>

<item>

		<title>A-E SERVICES: HAZARDOUS WASTE AND CERCLA CLEANUP [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9901</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9901</guid>
		<description>U.S. Department of Agriculture, Forest Service, Atlanta, GA.&lt;br /&gt;
Federal Business Opportunities, FBO-4179, Solicitation AG-43ZP-S-13-0006, 2013 &lt;br /&gt;&lt;br /&gt; The USDA-Forest Service Southern Regional Office has an ongoing need for Architect-Engineer services, including environmental engineering services, for planning and documentation, compliance, advisory assistance, and waste management consulting. The majority of work will occur within the boundaries of the Southern Region (AL, AR, FL, GA, KY, LA, MS, NC, OK, SC, TN, TX, and VA) as well as Puerto Rico and the U.S. Virgin Islands. This procurement is set aside for service-disabled, veteran-owned small business, NAICS code 541330, with a size standard of $14M. The government expects to award a single indefinite-delivery, indefinite-quantity contract for one base year with four option-year periods. The full solicitation will be posted on or about May 28, 2013. &lt;A HREF=&quot;https://www.fbo.gov/spg/USDA/FS/43ZP/AG-43ZP-S-13-0006/listing.html&quot;&gt;https://www.fbo.gov/spg/USDA/FS/43ZP/AG-43ZP-S-13-0006/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:20:01 GMT</pubDate>
	</item>

<item>

		<title>HELENA NATIONAL FOREST WARM SPRINGS CREEK TAILINGS PROJECT [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9900</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9900</guid>
		<description>U.S. Department of Agriculture, Forest Service.&lt;br /&gt;
Federal Business Opportunities, FBO-4179, Solicitation AG-03H6-S-13-0003, 2013 &lt;br /&gt;&lt;br /&gt; The Helena National Forest desires to conduct a CERCLA removal action for ~40,000 cubic yards of heavy metal laden mill tailings from the Warm Springs Creek drainage and placement of the tailings into a nearby constructed repository. The site is located near Clancy, Montana. The solicitation will be published around July 1 as a total small business set-aside. Estimated magnitude of construction is between $500,000 and $1,000,000, subject to availability of funds. &lt;A HREF=&quot;https://www.fbo.gov/spg/USDA/FS/398/AG-03H6-S-13-0003/listing.html&quot;&gt;https://www.fbo.gov/spg/USDA/FS/398/AG-03H6-S-13-0003/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:19:48 GMT</pubDate>
	</item>

<item>

		<title>BAXTER SPRINGS OU3 &amp;mdash; PHASE III [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9899</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9899</guid>
		<description>U.S. Environmental Protection Agency, Region 7, Lenexa, KS.&lt;br /&gt;
Federal Business Opportunities, FBO-4165, Solicitation SOL-R7-13-00012, 2013 &lt;br /&gt;&lt;br /&gt; U.S. EPA plans to solicit services for performance of a remedial action for a portion of the mine waste located at the Baxter Springs subsite, Operable Unit #03 (OU-3), of the Cherokee County Superfund site. The selected remedy consists of excavation, consolidation, and disposal of approximately 206,500 cubic yards of mine waste and associated soils contaminated with heavy metals. Remediation will be conducted pursuant to CERCLA and National Contingency Plan requirements. This procurement will be set aside for service-disabled, veteran-owned small businesses under NAICS code 562910. EPA anticipates issuing a fixed-price contract with a contract period of 24 months and an estimated dollar value between $2M to $3M. The solicitation/RFP and more detailed information should be released on or about May 20, 2013, via EPA&apos;s acquisition management website (&lt;A HREF=&quot;http://www.epa.gov/oam/regions/index.htm&quot;&gt;www.epa.gov/oam/regions/index.htm&lt;/A&gt;) and &lt;A HREF=&quot;https://www.FedConnect.net&quot;&gt;https://www.FedConnect.net&lt;/A&gt;. &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00012/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00012/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:19:25 GMT</pubDate>
	</item>

<item>

		<title>SOIL REMEDIATION [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9898</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9898</guid>
		<description>Department of the Air Force, Air Force Materiel Command, Tinker AFB, OK.&lt;br /&gt;
Federal Business Opportunities, FBO-4170, Solicitation FA8101-13-Q-0028, 2013 &lt;br /&gt;&lt;br /&gt; Tinker Air Force Base (TAFB) intends to issue a request for quotes for the procurement of services to remediate 4,000 cubic yards of soil where a fuel transfer line released about 8,000 gallons of jet fuel (JP-8) on TAFB (Oklahoma City, Oklahoma) on 9 June 2011. The acquisition is 100% set aside for small businesses under NAICS code 562910. Award of a single firm, fixed-price contract is anticipated. Offers are due no later than May 24, 2013, 12:00 PM CT. &lt;A HREF=&quot;https://www.fbo.gov/spg/USAF/AFMC/OCALCBC/FA8101-13-Q-0028/listing.html&quot;&gt;https://www.fbo.gov/spg/USAF/AFMC/OCALCBC/FA8101-13-Q-0028/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:19:09 GMT</pubDate>
	</item>

<item>

		<title>SMALL BUSINESS TECHNOLOGY TRANSFER PROGRAM PHASE I, FY 2014 [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9897</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9897</guid>
		<description>National Science Foundation, Funding Opportunity 13-547, 2013 &lt;br /&gt;&lt;br /&gt; NSF&apos;s Small Business Technology Transfer (STTR) program stimulates technological innovation in the private sector by requiring small business concerns to partner with researchers at universities and other non-profit research institutions. This STTR Phase I solicitation aims to encourage the commercialization of research previously funded by NSF. The proposals submitted should fall into one of four broad topic areas: (1) Biological and Chemical Technologies; (2) Education Applications; (3) Electronics, Information, and Communication Technologies; and (4) Nanotechnology, Advanced Materials, and Manufacturing. The window for submitting proposals is open from May 13, 2013, to June 13, 2013. Estimated Total Program Funding: $11,250,000. Expected Number of Awards: 50. Award Ceiling: $225,000. &lt;A HREF=&quot;http://www.grants.gov/search/search.do?mode=VIEW&amp;oppId=225797&quot;&gt;http://www.grants.gov/search/search.do?mode=VIEW&amp;&lt;wbr&gt;oppId=225797&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:17:50 GMT</pubDate>
	</item>

<item>

		<title>SMALL BUSINESS INNOVATION RESEARCH PROGRAM PHASE I, FY 2014 [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9896</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9896</guid>
		<description>National Science Foundation, Funding Opportunity 13-546, 2013 &lt;br /&gt;&lt;br /&gt; NSF has formulated the following broad solicitation topics for its Small Business Innovation Research (SBIR) Program: (1) Biological and Chemical Technologies; (2) Education Applications; (3) Electronics, Information, and Communication Technologies; and (4) Nanotechnology, Advanced Materials, and Manufacturing. The window for submitting proposals is open from May 11, 2013, to June 11, 2013. Estimated Total Program Funding: $30,000,000. Expected Number of Awards: 200. Award Ceiling: $150,000. NOTE: The submission of the same project idea to both this SBIR Phase I solicitation and the concurrent STTR Phase I solicitation is strongly discouraged. &lt;A HREF=&quot;http://www.grants.gov/search/search.do?mode=VIEW&amp;oppId=225796&quot;&gt;http://www.grants.gov/search/search.do?mode=VIEW&amp;&lt;wbr&gt;oppId=225796&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:17:29 GMT</pubDate>
	</item>

<item>

		<title>ENVIRONMENTAL SERVICES TO SUPPORT THE ARMY IN ENVIRONMENTAL MONITORING, RESTORATION, COMPLIANCE, AND REMEDIATION AT A SUPERFUND SITE [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9895</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9895</guid>
		<description>U.S. Army Corps of Engineers, USACE District, Sacramento, CA.&lt;br /&gt;
Federal Business Opportunities, FBO-4158, Solicitation W91238-13-S-0025, 2013 &lt;br /&gt;&lt;br /&gt; The U.S. Army Corps of Engineers is conducting market research to determine the availability of firms to perform environmental services and support at the former Fort Ord. All responses will be used to determine the appropriate strategy for a potential future acquisition. The services sought will support environmental monitoring, restoration, compliance, and remediation at a Superfund site that includes endangered species habitats. Responses are due by 3 PM PST, June 3, 2013. &lt;A HREF=&quot;https://www.fbo.gov/spg/USA/COE/DACA05/W91238-13-S-0025/listing.html&quot;&gt;https://www.fbo.gov/spg/USA/COE/DACA05/W91238-13-S-0025/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:17:08 GMT</pubDate>
	</item>

<item>

		<title>AMERICAN DAM SOIL REMEDIATION [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9894</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9894</guid>
		<description>International Boundary and Water Commission, El Paso, TX.&lt;br /&gt;
Federal Business Opportunities, FBO-4159, Solicitation IBM13R0002, 2013 &lt;br /&gt;&lt;br /&gt; The United States section of the International Boundary and Water Commission (USIBWC) intends to issue a solicitation for environmental cleanup services. The cleanup is part of the settlement of the bankruptcy case for ASARCO, a former smelter located next to the USIBWC&apos;s American Dam/Carlos Marin Field Office in El Paso, Texas. USIBWC is using settlement funds to clean up soil contaminated with arsenic, cadmium, and lead at the office complex. Existing buildings and utilities, a rock wall, and a Customs and Border Patrol tower must be protected in place during construction as government operations at the field office will continue throughout the construction period. The work will be performed under NAICS Code 562910, Remediation Services, with an associated small business size standard of $14 million. The contract will be firm fixed-price for construction. Approximate date of solicitation issuance is May 1, 2013. &lt;A HREF=&quot;https://www.fbo.gov/spg/IBWC/IMD/ElPasoTX/IBM13R0002/listing.html&quot;&gt;https://www.fbo.gov/spg/IBWC/IMD/ElPasoTX/IBM13R0002/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:14:41 GMT</pubDate>
	</item>

<item>

		<title>ARCHITECT/ENGINEERING INDEFINITE QUANTITY CONTRACT FOR ENVIRONMENTAL CONSULTING SERVICES FOR THE NORTHEAST AREA [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9893</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9893</guid>
		<description>U.S. Postal Service, Northern Facilities Construction CMT, Windsor, CT.&lt;br /&gt;
Federal Business Opportunities, FBO-4158, Solicitation 089495-13-A-0039, 2013 &lt;br /&gt;&lt;br /&gt; The U.S. Postal Service seeks the following environmental services for its Northeast Area (i.e., CT, MA, ME, NH, RI, VT, NY, and NJ): (1) underground and aboveground storage tank services; (2) surveys, monitoring, mitigation plans, and remediation oversight for asbestos-containing materials, lead-based paint, radon, mold, lead in drinking water, and indoor air; (3) general site health and safety; (4) site remediation services provided by state-certified staff; (5) site evaluations for property transactions; (6) emergency response and remedial services and hazardous materials management; (7) permitting (e.g., air and water quality, stormwater management); and (8) plan preparation (e.g., spill prevention control and countermeasures). The contract will be for one base year with four 1-year renewal options, not to exceed a total of $9.5 million. A completed SF 330 should be submitted by May 29, 2013, 3:00 PM EST. Consideration will be given to local firms. &lt;A HREF=&quot;https://www.fbo.gov/notices/93b8977c46dafddb47fa33daa4987557&quot;&gt;https://www.fbo.gov/notices/93b8977c46dafddb47fa33daa4987557&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Tue, 7 May 2013 14:12:41 GMT</pubDate>
	</item>

<item>

		<title>SCIENCE FOR ENVIRONMENTAL PROTECTION: THE ROAD AHEAD [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9892</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9892</guid>
		<description>National Research Council.&lt;br /&gt;
National Academies Press, Washington, DC. ISBN-10: 0-309-26489-8, 233 pp, 2012 &lt;br /&gt;&lt;br /&gt; In anticipation of future environmental science and engineering challenges and technologic advances, EPA asked the National Research Council (NRC) to assess the overall capabilities of the agency to develop, obtain, and use the best available scientific and technologic information and tools to meet persistent, emerging, and future mission challenges and opportunities. Although the NRC committee responsible for this report cannot predict with certainty what new environmental problems EPA will face in the next 10 years or more, it worked to identify some of the common drivers and common characteristics of problems that are likely to occur. This text outlines a framework for building science for environmental protection in the 21st century and identifies key areas where enhanced leadership and capacity can strengthen the EPA&apos;s abilities to address current and emerging environmental challenges and take advantage of new tools and technologies to address them. &lt;A HREF=&quot;http://www.nap.edu/catalog.php?record_id=13510&quot;&gt;http://www.nap.edu/catalog.php?record_id=13510&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:10:27 GMT</pubDate>
	</item>

<item>

		<title>ENVIRONMENTAL DECISIONS IN THE FACE OF UNCERTAINTY [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9891</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9891</guid>
		<description>Institute of Medicine, Board on Population Health and Public Health Practice.&lt;br /&gt;
National Academies Press, Washington, DC. ISBN-10: 0-309-13034-4, 260 pp, 2013 &lt;br /&gt;&lt;br /&gt; U.S. EPA is one of several federal agencies responsible for protecting U.S. citizens against significant risks to human health and the environment. As part of that mission, EPA estimates the nature, magnitude, and likelihood of risks to human health and the environment; identifies the potential regulatory actions that will mitigate those risks and protect public health and the environment; and uses that information to decide on appropriate regulatory action. Uncertainties, both qualitative and quantitative, in the data and analyses on which these decisions are based enter into the process at each step. Given that uncertainty is inherent in science, including the science that informs EPA decision-making, this summary presents discussions and recommendations for managing risks, considerations in the decision-making process, and approaches to analyzing and communicating uncertainty about human health risks as well as other areas of environmental concern. &lt;A HREF=&quot;http://www.nap.edu/catalog.php?record_id=12568&quot;&gt;http://www.nap.edu/catalog.php?record_id=12568&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:10:13 GMT</pubDate>
	</item>

<item>

		<title>PHYTOTECHNOLOGIES: REMEDIATION OF ENVIRONMENTAL CONTAMINANTS [General News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9890</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9890</guid>
		<description>Anjum, N.A., M.E. Pereira, I. Ahmad, A.C. Duarte, S. Umar, and N.A. Khan&lt;br /&gt;
CRC Press, Boca Raton, FL. ISBN: 9781439875186, 617 pp, 2012 &lt;br /&gt;&lt;br /&gt; This book provides a conceptual overview of ecosystems approaches and phytotechnologies and their cumulative significance in relation to various environmental problems and potential solutions. Phytoremediation case studies accompany discussions of the tolerance of plant types to different contaminants. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:09:53 GMT</pubDate>
	</item>

<item>

		<title>RADIAL FILTRATION IN PERMEABLE REACTIVE BARRIERS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9889</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9889</guid>
		<description>Courcelles, B.&lt;br /&gt;
International Journal of Environmental Pollution and Remediation, Vol 1 No 1, 104-110, 2012 &lt;br /&gt;&lt;br /&gt; An innovative radial filter for permeable reactive barriers (PRBs) has been designed to reduce the head loss of groundwater flow bypassing the barrier compared to classical filters with axial flow. The design also improves the water/reactive media contact time. The new cylindrical filter is composed of a core of coarse material surrounded by a reactive material and a final ring of coarse material. The radial flow can be centripetal or centrifugal depending on the hydraulic heads applied to the filter. Based on numerical simulations and analytical solutions, the new configuration could improve the lifetime of a PRB, and in a centripetal configuration, improve the contact time where the groundwater is most contaminated. &lt;A HREF=&quot;http://ijepr.avestia.com/2012/PDF/015.pdf&quot;&gt;http://ijepr.avestia.com/2012/PDF/015.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:09:38 GMT</pubDate>
	</item>

<item>

		<title>EVALUATION OF THE EFFECTIVENESS OF DIFFERENT METHODS FOR THE REMEDIATION OF CONTAMINATED GROUNDWATER BY DETERMINING THE PETROLEUM HYDROCARBON CONTENT [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9888</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9888</guid>
		<description>Voyevoda, M., W. Geyer, P. Mosig, E.M. Seeger, and S. Mothes.&lt;br /&gt;
CLEAN: Soil, Air, Water, Vol 40 No 8, 817-822, Aug 2012 &lt;br /&gt;&lt;br /&gt; The effectiveness of different remediation approaches in a constructed wetland for decreasing the amount of TPH (total petroleum hydrocarbons) in contaminated groundwater was evaluated at the site of a former refinery. The most effective hydrocarbon removal approach tested was a planted horizontal subsurface flow gravel filter with 0.1% activated carbon addition. This remediation method allowed the reduction of petroleum hydrocarbon content independently of seasonal conditions. The correlation between the reduction of TPH and BTEX was found to be &lt;i&gt;R&lt;/i&gt;=0.8824. Using this correlation coefficient, the time-consuming determination of the BTEX content was no longer necessary. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:09:24 GMT</pubDate>
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<item>

		<title>STATISTICAL TECHNIQUES FOR ANALYZING OF SOIL VAPOR INTRUSION DATA: A CASE STUDY OF MANUFACTURED GAS PLANT SITES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9887</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9887</guid>
		<description>Singh, A., E.F. Neuhauser, N.A. Azzolina, M. Distler, K.M. Anders, M.A. Doroski, and A.J. Rabideau. &lt;br /&gt;
Journal of the Air &amp; Waste Management Association, Vol 63 No 2, 219-229, 2013 &lt;br /&gt;&lt;br /&gt; As part of an ongoing study of soil vapor intrusion (SVI), concentration data for ~2,000 air and vapor samples were assembled from remedial site investigations and stand-alone assessments conducted at manufactured gas plant (MGP) sites in New York state. Vapor samples were collected from ambient outdoor air, indoor air, beneath building slabs, and just outside buildings. Despite the large sample size, the considerable variability in compound and sample-specific censoring limits inhibited the use of conventional tools for statistical interpretation. In addition to methods for calculating population percentiles and associated confidence intervals, methods for comparing the population of MGP-SVI data with a reference population were developed and evaluated via illustrative comparisons with EPA&apos;s Building Assessment Survey and Evaluation Study of industrial buildings. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:09:10 GMT</pubDate>
	</item>

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		<title>EFFICIENT DEGRADATION OF TCE IN GROUNDWATER USING PD AND ELECTRO-GENERATED H&lt;sub&gt;2&lt;/sub&gt; AND O&lt;sub&gt;2&lt;/sub&gt;: A SHIFT IN PATHWAY FROM HYDRODECHLORINATION TO OXIDATION IN THE PRESENCE OF FERROUS IONS [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9886</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9886</guid>
		<description>Yuan, S., X. Mao, and A.N. Alshawabkeh.&lt;br /&gt;
Environmental Science &amp; Technology, Vol 46, 3398-3405, 2012 &lt;br /&gt;&lt;br /&gt; This paper outlines the use of iron ions (Fe(II)) with a palladium (Pd) catalyst to enhance oxidative degradation of TCE, which typically occurs as a side reaction during traditional TCE hydrodechlorination. The authors applied mixed-metal oxide electrodes to simulated TCE-contaminated groundwater to generate H&lt;sub&gt;2&lt;/sub&gt;. They added Pd powder to catalyze the reaction, which degraded TCE into ethane and other by-products. Application of Pd alone degraded 40% of the TCE within 80 minutes, but the addition of Fe(II) degraded 95% of the TCE within the same amount of time, shifting the TCE decontamination process from hydrodechlorination (a reduction process) to a more rapid oxidative reaction. This shift was most effective when high concentrations of iron (about 10 mg/L) were present and the pH of the water was low. For sustained treatment, the researchers are developing an in-well solar-powered system. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:08:50 GMT</pubDate>
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		<title>ARSENIC ENCAPSULATION USING PORTLAND CEMENT WITH FERROUS SULFATE/LIME AND TERRA-BOND&amp;trade; TECHNOLOGIES: MICROCHARACTERIZATION AND LEACHING STUDIES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9885</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9885</guid>
		<description>Randall, P.M., U.S. EPA, Cincinnati, OH.&lt;br /&gt;
Science of the Total Environment, Vol 420, 300-312, 2012 &lt;br /&gt;&lt;br /&gt; An investigation on the treatment and encapsulation of arsenic-containing materials by Portland cement with ferrous sulfate and lime (PFL) and Terra-Bond&amp;trade; was conducted on chromated copper arsenate (CCA)-containing wood materials; scorodite-rich mine tailings from the La Trinidad Mine in California; and a soil/smelter dust mixture from the Anaconda Superfund site. The smelter dust mixture was spiked with monosodium methyl arsenate (MSMA) to simulate an organoarsenic soil material. In the CCA-containing samples, arsenic has a predominant pentavalent form (As +5), and PFL treatment did not alter the arsenic oxidation state. In the untreated and PFL-treated scorodite-rich mine tailings, however, the arsenic coordination structure changed from a mixture of As (+3/+5) to exclusively As (+5). In most cases, Terra-Bond&amp;trade; treatment decreased the amount of arsenic released from wastes over that achieved using PFL. Cost analysis indicates that the PFL process is in the $200-400/ton range, and the Terra-Bond&amp;trade; process is in the $325-525/ton range. Refinement of technology recipes will be needed to ensure long-term containment of the arsenic. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:08:35 GMT</pubDate>
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		<title>COMBINED USE OF A TRANSFORMED RED MUD REACTIVE BARRIER AND ELECTROKINETICS FOR REMEDIATION OF CR/AS CONTAMINATED SOIL [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9884</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9884</guid>
		<description>Cappai, G., G. De Gioannis, A. Muntoni, D. Spiga, and J.J.P. Zijlstra.&lt;br /&gt;
Chemosphere, Vol 86 No 4, 400-408, 2012 &lt;br /&gt;&lt;br /&gt; A reactive barrier (RB) of transformed red mud (TRM), a by-product of the refinement of bauxite in alumina production, was placed adjacent to the anode of an electrokinetic (EK) system with the aim of enhancing removal of chromium or arsenic added singly to a low-permeability clayey soil, and favoring entrapment. The study focused on evaluation of the synergic interaction between the EK system and the RB, as well as the efficiency of the pairing compared to EK remediation alone. Results indicated successful treatment of the Cr(VI)-contaminated soil, while the combined treatment was much less effective on As-contaminated soil, at least under the operative conditions applied. Low initial As concentration and interference from iron oxides in the soil likely were the reasons underlying the low As decontamination efficiency. Details are available in D. Spiga&apos;s Ph.D. thesis (&lt;A HREF=&quot;http://veprints.unica.it/621/1/PhD_Thesis_D.Spiga.pdf&quot;&gt;http://veprints.unica.it/621/1/PhD_Thesis_D.Spiga.pdf&lt;/A&gt;) and in &quot;Re-use Options for Mineral Processing Waste: A Case Study,&quot; a presentation from the Workshop 2012 Sardegna, which was held to discuss remediation, operating procedures, and potential redevelopment of abandoned mine sites. &lt;i&gt;Please note that the compiled Sardegna presentations are graphics-heavy and may load very slowly.&lt;/i&gt; The case study is &lt;b&gt;available on PDF pages 22-66&lt;/b&gt; at &lt;A HREF=&quot;http://www.sardegnaambiente.it/documenti/18_330_20120503101048.pdf&quot;&gt;http://www.sardegnaambiente.it/documenti/18_330_20120503101048.pdf&lt;/A&gt;. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:07:55 GMT</pubDate>
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		<title>IDENTIFICATION OF MICROBIAL GENE BIOMARKERS FOR IN SITU RDX BIODEGRADATION [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9883</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9883</guid>
		<description>Crocker, F.H., K.J. Indest, C.M. Jung, et al.&lt;br /&gt;
ERDC/EL TR-12-33, SERDP Project ER-1609, 175 pp, 2012 &lt;br /&gt;&lt;br /&gt; Genome annotation and functional characterization of the plasmid pGKT2 in KTR9 revealed that xplA gene is both necessary and sufficient for RDX degradation. &lt;i&gt;Shewanella oneidensis&lt;/i&gt; MR-1 was shown to degrade RDX efficiently and anaerobically via two initial routes: (a) sequential N-NO&lt;sub&gt;2&lt;/sub&gt; reduction to the corresponding nitroso (N-NO) derivatives; and (b) monodenitration followed by ring cleavage. The qPCR molecular tools described in this report have the potential to be used by remediation specialists for site characterization, treatment recommendations, and evaluation/optimization of treatment processes for RDX constituents.&lt;br /&gt;
&lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18082/201628/file/ER-1609-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18082/201628/file/ER-1609-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:07:34 GMT</pubDate>
	</item>

<item>

		<title>DEVELOPMENT OF TOXICITY BENCHMARKS AND BIOACCUMULATION DATA FOR N-BASED ORGANIC EXPLOSIVES FOR TERRESTRIAL PLANTS AND SOIL INVERTEBRATES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9882</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9882</guid>
		<description>Sunahara, G.&lt;br /&gt;
Strategic Environmental Research and Development Program, Project ER-1416, 289 pp, 2012 &lt;br /&gt;&lt;br /&gt; Studies using three plant and three soil invertebrate test species exposed in sandy loam soils established new ecotoxicological data for 2,4-DNT, 2-ADNT, 4-ADNT, HMX, and nitroglycerin under conditions of very high relative bioavailability for organic chemicals in soil. The data were used to derive draft ecological soil screening level concentrations for each energetic material. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/17859/197874/file/ER-1416-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/17859/197874/file/ER-1416-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:07:21 GMT</pubDate>
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<item>

		<title>DEFINING MUNITION CONSTITUENT (MC) SOURCE TERMS IN AQUATIC ENVIRONMENTS ON DOD RANGES [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9881</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9881</guid>
		<description>Wang, P.F., R.D. George, W.J. Wild, and Q. Liao.&lt;br /&gt;
SPAWAR Technical Report 1999, SERDP ER-1453, 130 pp, 2013 &lt;br /&gt;&lt;br /&gt; The objectives of this study were to develop a basic understanding of the release rate and subsequent fate and transport of MCs in water and sediment. With the ability to characterize, assess, and predict potential MC source loading and distribution, DoD will gain critical information for making scientifically defensible risk management decisions about underwater ordnance leave-in-place mitigation and blow-in-place versus removal options. In addition to explosive blast (safety) considerations, future regulatory emphasis likely will require an assessment of potential underwater ordnance contamination and mitigation efforts that could include water and sediment quality issues. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18166/202199/file/ER-1453-%20FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18166/202199/file/ER-1453-%20FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:07:07 GMT</pubDate>
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<item>

		<title>APPLICATION OF MICROARRAYS AND QPCR TO IDENTIFY PHYLOGENETIC AND FUNCTIONAL BIOMARKERS DIAGNOSTIC OF MICROBIAL COMMUNITIES THAT BIODEGRADE CHLORINATED SOLVENTS TO ETHENE [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9880</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9880</guid>
		<description>Alvarez-Cohen, L.&lt;br /&gt;
Strategic Environmental Research and Development Program, Project ER-1587, 85 pp, 2012 &lt;br /&gt;&lt;br /&gt; Project ER-1587 applied 16S rRNA- and mRNA-based microarray and quantitative PCR tools to monitor &lt;i&gt;Dehalococcoides&lt;/i&gt; (Dhc)-containing microbial communities capable of reductive dechlorination of chlorinated solvents. The work focused on the following areas:&lt;br /&gt;
&lt;ul&gt;&lt;br /&gt;
&lt;li&gt;Application of 16S rRNA based molecular tools (e.g., clone libraries, qPCR, and PhyloChip, to different TCE dechlorinating communities. &lt;/li&gt;&lt;br /&gt;
&lt;li&gt;Construction of a robust consortium of &lt;i&gt;D. mccartyi&lt;/i&gt; strain 195 with other bacteria. &lt;/li&gt;&lt;br /&gt;
&lt;li&gt;Design, validation, and application of a genus-wide microarray targeting all four known Dhc genomes (strain CBDB1, BAV1, 195 and VS). &lt;/li&gt;&lt;br /&gt;
&lt;li&gt;Investigation of the correlation among certain biomarkers, growth phases, dechlorination performance, and corrinoid availability. &lt;/li&gt;&lt;br /&gt;
&lt;/ul&gt;&lt;br /&gt;
The combination of microarray (i.e., GeneChip and PhyloChip) analyses of DNA and RNA with clone library construction provided insights into the in situ microbial ecology and population dynamics during biostimulation-bioaugmentation at a TCE-contaminated site. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/17860/197884/file/ER-1587-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/17860/197884/file/ER-1587-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:06:48 GMT</pubDate>
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		<title>MICRO ION MOBILITY SENSOR FOR IN SITU MONITORING OF CONTAMINATED GROUNDWATER [Research]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9879</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9879</guid>
		<description>Xu, J.&lt;br /&gt;
Strategic Environmental Research and Development Program, Project ER-1603, 45 pp, 2012 &lt;br /&gt;&lt;br /&gt; The objective of project ER-1603 was to develop a prototype sensor based on membrane extraction-ion mobility spectrometry (ME-IMS) for in situ or ex situ use, e.g., for characterizing the extent of groundwater plumes, conducting compliance monitoring around waste facilities or at the leading edge of a plume, and monitoring remedial actions. A preliminary field test of the ME-IMS groundwater monitor was conducted on high and low concentrations of TCE at NASA&apos;s Stennis Space Center. The instrument also could be used to monitor chlorinated hydrocarbons in the vapor phase. &lt;A HREF=&quot;http://www.serdp-estcp.org/content/download/18081/201618/file/ER-1603-FR.pdf&quot;&gt;http://www.serdp-estcp.org/content/download/18081/201618/file/ER-1603-FR.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:06:27 GMT</pubDate>
	</item>

<item>

		<title>PILOT STUDY TO EVALUATE TOLUENE SOURCE AREA BIOREMEDIATION USING AN AEROBIC IN-SITU BIOREACTOR (ISBR) [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9878</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9878</guid>
		<description>Key, K., K. Sublette, E. Sullivan, J. Duba, G. Davis, D. Ogles, B. Baldwin, and A. Biernacki.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 35 slides, 2012 &lt;br /&gt;&lt;br /&gt; Six aerobic in situ bioreactor (ISBR) units were installed into treatment wells within the contaminant source area in a pilot study conducted in northern New Jersey at a former industrial site contaminated with significant concentrations of toluene and benzene in groundwater, as well as free-product toluene. The ISBR unit is designed to enhance the natural attenuation process by stimulating microbial growth and enhancing contaminant degradation to achieve cleanup goals. This approach builds on existing Bio-Sep&amp;reg; bead technology, which provides a substrate that can be colonized rapidly by the active members of the microbial community, serving to concentrate indigenous degraders. Oxygen and nutrients are also delivered to the bioreactor to maintain conditions favorable for growth and reproduction. Not only is the contaminated groundwater treated as it circulates through the bed of beads, groundwater leaving the system also transports degraders released from the beads away from the bioreactor, thus increasing biodegradation rates in the aquifer. Bio-Trap&amp;reg; samplers and molecular biological tools were used to assess system performance. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Key_IPEC_2012.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Key_IPEC_2012.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:06:12 GMT</pubDate>
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		<title>PERMEABLE REACTIVE BARRIER (PRB) TECHNOLOGY: AN INNOVATIVE SOLUTION FOR THE REMEDIATION OF ACIDIC GROUNDWATER FROM ACID SULPHATE SOIL (ASS) TERRAIN [Demonstrations]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9877</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9877</guid>
		<description>Banasiak, L. and B. Indraratna, University of Wollongong.&lt;br /&gt;
GeoCongress 2012: State of the Art and Practice in Geotechnical Engineering. American Society of Civil Engineers, ISBN (print): 978-0-7844-1212-1, 3523-3432, 2012 &lt;br /&gt;&lt;br /&gt; In 2006, the first pilot permeable reactive barrier (PRB) using recycled concrete for the remediation of acidic groundwater (~pH 3) was deployed in acid sulfate soil (ASS) terrain in southeast New South Wales, Australia. While monitoring has confirmed the PRB is successfully neutralizing the acidic groundwater to ~pH 7.3 and removing ~95% of Al and Fe, technology challenges remain. This paper presents details on the process of screening for reactive materials; PRB installation; experiments to simulate the flow of acidic groundwater through the PRB to study the predominant neutralization reactions; PRB long-term performance (including the potential for chemical armoring and possible clogging of the recycled concrete by Al and Fe oxy/hydroxide precipitates); and the current research strategy for investigating the PRB&apos;s longevity. &lt;A HREF=&quot;http://ro.uow.edu.au/cgi/viewcontent.cgi?article=7522&amp;context=engpapers&quot;&gt;http://ro.uow.edu.au/cgi/viewcontent.cgi?article=7522&amp;&lt;wbr&gt;context=engpapers&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:05:44 GMT</pubDate>
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		<title>SOLVENT RELEASE AREA (SRA), OPERABLE UNIT 14, FORMER NAVAL AIR STATION SOUTH WEYMOUTH, WEYMOUTH, MASSACHUSETTS: PROPOSED PLAN [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9876</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9876</guid>
		<description>U.S. Navy, 16 pp, Feb 2013 &lt;br /&gt;&lt;br /&gt; The Navy&apos;s preferred alternative for cleaning up contaminants (PCE, TCE, cis-1,2-DCE, vinyl chloride, pentachlorophenol, arsenic, 3,3-dichlorobenzidine, and barium) at OU-14 consists of enhanced bioremediation of the overburden and bedrock source zone, installation of two overburden permeable reactive barriers (PRBs), monitoring, engineering controls, and land-use controls. For the bioremediation option, a soluble electron donor, such as sodium lactate, would be injected in both the overburden and bedrock target treatment zones through grids of injection points. Mulch PRBs would provide an organic source for microorganisms to stimulate anaerobic degradation of chlorinated VOCs. Pilot treatability studies will be performed prior to design to determine the details of remedy construction. &lt;A HREF=&quot;http://www.bracpmo.navy.mil/base_docs/south_weymouth/documents/enviro_docs/SRA_ProposedPlan_final.pdf&quot;&gt;http://www.bracpmo.navy.mil/base_docs/south_weymouth/documents/enviro_docs/SRA_ProposedPlan_final.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:05:28 GMT</pubDate>
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		<title>RAPID SITE CLOSURE OF A LARGE GAS PLANT USING INNOVATIVE IN-SITU BIOREMEDIATION TECHNOLOGY [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9875</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9875</guid>
		<description>Harp, T.A.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 25 slides, 2012 &lt;br /&gt;&lt;br /&gt; Rapid in situ remediation of on- and off-site petroleum hydrocarbon impacts associated with a gas plant located in central Texas was accomplished using BOS 200&amp;reg;. The compound is a granular activated carbon injectant inoculated with consortia of facultative microorganisms, electron acceptors (nitrate and sulfate), and nutrients (phosphorus and nitrogen) designed to biodegrade BTEX compounds. During pre-design delineation of the vertical and horizontal distribution of BTEX, impacts were found within 8 to 9 feet of stiff clay and the underlying weathered limestone. The site was subdivided into six regions, based on BTEX concentrations. Treatment was implemented in three phases over a 15-month period in which ~4,800 injections were completed at 1,230 locations throughout the 66,000 ft&lt;sup&gt;2&lt;/sup&gt; plume. The remedy consisted of 185,875 lbs of carbon slurry, 5,650 lbs of supplemental sulfate (gypsum), and 352 gals of microbes. The primary petroleum constituent, benzene, was reduced from concentrations of &gt;50,000 &amp;micro;g/L (i.e., free-phase product) to &lt;1 &amp;micro;g/L. Following 24 months of post-treatment groundwater monitoring, the Railroad Commission of Texas issued a No Further Action determination for the site. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Harp.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Harp.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:04:54 GMT</pubDate>
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		<title>THERMALLY ENHANCED REMEDIATION IN SANTA FE, NEW MEXICO [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9874</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9874</guid>
		<description>Golden, T., M. McVey, G. Peterson, and J. Doesburg.&lt;br /&gt;
IPEC 2012: Proceedings of the 19th International Petroleum &amp; BioFuels Environmental Conference, October 29 - November 1, 2012, San Antonio, Texas. 23 slides, 2012 &lt;br /&gt;&lt;br /&gt; During dewatering activities for construction of an underground parking structure, the contractor encountered groundwater contaminated with petroleum hydrocarbons. Remediation was challenged by tight quarters at the site&apos;s downtown location, other ongoing construction activities, input from multiple stakeholders, and an accelerated timeline for achieving remedial goals. The remedial strategy consisted of completing a grout barrier around the site and implementing thermally enhanced soil vapor extraction to remove the hydrocarbon LNAPL. The grout barrier (22 ft high) consisted of 600 linear ft of high-pressure jet-grouted elements that overlapped with the ends of a 185-ft slurry wall. Key features of the extraction system included vertical wells, horizontal wells beneath existing buildings, natural-gas-fired thermal oxidizers, and a hot-air injection system. Subsurface temperature increases of 10 to 30&amp;deg;F accelerated the removal and treatment of more than 22,000 gal of gasoline. &lt;A HREF=&quot;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Golden.pdf&quot;&gt;http://ipec.utulsa.edu/Conf2012/Papers_Presentations/Golden.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:04:40 GMT</pubDate>
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		<title>EPA ISSUES AMENDMENT TO RECORD OF DECISION FOR THE 10TH STREET SUPERFUND SITE IN COLUMBUS, NEB. [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9873</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9873</guid>
		<description>U.S. EPA Region 7 News Release, 4 Jan 2013 &lt;br /&gt;&lt;br /&gt; The 2005 ROD for the 10th Street Superfund Site in Columbus, Nebraska, selected the following remedies for PCE and TCE contamination: (1) continued operation of the air sparge-soil vapor extraction and groundwater extraction and treatment (GET) systems, (2) in situ chemical oxidation (ISCO) in the upgradient portion of the groundwater contaminant plume, and (3) institutional controls in all three source areas: the former One Hour Martinizing dry cleaner, the former Jackson Services, and the former Liberty Cleaners. EPA&apos;s amendment to the 2005 ROD for all three contaminated source area soils calls for building demolition, soil excavation, and off-site disposal. The excavated area will be backfilled with non-contaminated soil. The amended remedy to address contaminated groundwater at the former Jackson Services and former Liberty Cleaners source areas includes continued operation of the GET system and limited ISCO. The remedy for contaminated groundwater at the former One Hour Martinizing dry cleaner is ISCO and/or biological remediation. &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:04:24 GMT</pubDate>
	</item>

<item>

		<title>SUCCESSFUL REMEDY FOR COMPLEX REMEDIATION [Cleanup News]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9872</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9872</guid>
		<description>Kleiser, H.&lt;br /&gt;
Military Engineer, Vol 104 No 675, 49-50, 2012 &lt;br /&gt;&lt;br /&gt; The site investigation of the Lake City Army Ammunition Plant in Independence, Missouri, revealed about 1 million pounds of soil, groundwater, and sediments contaminated with chlorinated solvents, metals, petroleum hydrocarbons, and explosive chemicals. The remediation approach incorporated up to 12 different remediation technologies, ranging from sustainable, state-of-the-art in situ approaches to conventional remedial technologies. Innovative techniques included bioremediation employing a patented in situ reactive zone groundwater remediation technology; a combination of enhanced reductive dechlorination, monitored natural attenuation, and zero-valent iron-clay soil mixing; mobile, solar-powered recovery of free-phase liquids; and a phytoremediation plantation of &gt;1,000 trees. This paper provides a brief overview of the performance-based remediation effort. &lt;A HREF=&quot;http://themilitaryengineer.com/2012toulmin/jan-feb/SuccessfulRemedyforComplexRemediation.pdf&quot;&gt;http://themilitaryengineer.com/2012toulmin/jan-feb/SuccessfulRemedyforComplexRemediation.pdf&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:04:02 GMT</pubDate>
	</item>

<item>

		<title>ENVIRONMENTAL REMEDIATION SERVICES MATOC [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9871</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9871</guid>
		<description>Department of the Army, U.S. Army Corps of Engineers, USACE District, Alaska.&lt;br /&gt;
Federal Business Opportunities, FBO-4136, Solicitation W911KB-13-R-0014, 2013 &lt;br /&gt;&lt;br /&gt; This acquisition is a total small business set-aside under NAICS code 562910, Remediation Services, which has a size standard of 500 employees. A solicitation is anticipated to be available in electronic format only at FBO.gov on or about April 5, 2013. The Government intends to award three small-business indefinite-delivery, indefinite-quantity, multiple-award task-order contracts (MATOC), consisting of a 3-year base period and 2-year option period. The overall capacity of this small business MATOC will be $180 million shared among all MATOC awardees. The objective of this MATOC for environmental remediation services is to provide the U.S. Army Corps of Engineers (USACE) with the capability to execute a full range of environmental remediation services for the Alaska District, USACE. &lt;A HREF=&quot;https://www.fbo.gov/spg/USA/COE/DACA85/W911KB-13-R-0014/listing.html&quot;&gt;https://www.fbo.gov/spg/USA/COE/DACA85/W911KB-13-R-0014/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:03:45 GMT</pubDate>
	</item>

<item>

		<title>MIXED WASTE TRANSPORTATION, TREATMENT AND DISPOSAL [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9870</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9870</guid>
		<description>NAVSUP Fleet Logistics Center Norfolk, Portsmouth, VA.&lt;br /&gt;
Federal Business Opportunities, FBO-4127, Solicitation N0018913RE037, 2013 &lt;br /&gt;&lt;br /&gt; The NAVSUP Fleet Logistics Center Norfolk intends to negotiate an indefinite-delivery, firm fixed-price, requirements-type contract on an unrestricted basis in support of the Naval Nuclear Propulsion Programs (NNPP) requirement for contractor services for the transportation, treatment, and disposal of NNPP mixed-waste materials. The waste materials may have both a hazardous component and a radioactive component. In addition, some waste material may contain TSCA-regulated PCBs, asbestos, or state-identified hazardous waste. The period of performance for the resulting contract will be for one 12-month base period and two 12-month option periods under NAICS code 562211, with a small business standard of $35.5 million. Requests for quote will be available for download some time after March 2013 at &lt;A HREF=&quot;https://www.neco.navy.mil&quot;&gt;https://www.neco.navy.mil&lt;/A&gt; under solicitation number N00189-13-R-E037. &lt;A HREF=&quot;https://www.fbo.gov/spg/DON/NAVSUP/N00189/N0018913RE037/listing.html&quot;&gt;https://www.fbo.gov/spg/DON/NAVSUP/N00189/N0018913RE037/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:03:29 GMT</pubDate>
	</item>

<item>

		<title>REGION 7 START IV [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9869</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9869</guid>
		<description>U.S. EPA, Office of Acquisition Management, Region VII, Kansas City.&lt;br /&gt;
Federal Business Opportunities, FBO-4127, Solicitation SOL-R7-13-00008, 2013 &lt;br /&gt;&lt;br /&gt; The purpose of the Superfund Technical Assessment and Response Team (START) contract is to provide nationally consistent advisory and assistance services to EPA On-Scene Coordinators and other federal officials implementing EPA&apos;s responsibilities under the National Response System. The contractor will fulfill these responsibilities within and outside the region on a backup regional response, cross-regional response, national response, and international response. The technical requirements under this unrestricted procurement include response, preparedness and prevention, assessment and inspection, technical support, data management and training. The contract will consist of a 3-year base period and two 1-year option periods. The total estimated ceiling for the contract is over $40 million if all options (both quantity and term) are exercised. EPA is issuing this presolicitation notice to advise that the RFP should be posted some time after March 27, 2013 at both epa.gov and fbo.gov. &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00008/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00008/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:03:15 GMT</pubDate>
	</item>

<item>

		<title>SUPERFUND TECHNICAL ASSESSMENT AND RESPONSE TEAM (START) IV, REGION 9 [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9868</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9868</guid>
		<description>U.S. EPA Region 5, Chicago, IL.&lt;br /&gt;
Federal Business Opportunities, FBO-4138, Solicitation SOL-R5-12-00006, 2013 &lt;br /&gt;&lt;br /&gt; U.S. EPA&apos;s Region 5 contracting office intends to issue an RFP on or about April 6, 2013, to obtain technical support services for the Superfund Technical Assessment and Response Team (START) IV in EPA Region 9 (i.e., Arizona, California, Hawaii, Nevada, American Samoa, Guam, and U.S. Trust Territories). Support services will include emergency response, removal, site assessment, training, data management, and related technical and administrative services. The Government intends to award one fixed-rate, indefinite-delivery, indefinite-quantity contract, with work assigned through the issuance of task orders. The solicitation anticipates a 24-month base period with two 18-month award-term option periods for a total contract length of 60 months. The acquisition will be conducted on the basis of full and open competition. Additional information, including a draft SOW, can be located at &lt;A HREF=&quot;http://www.FedConnect.net&quot;&gt;www.FedConnect.net&lt;/A&gt; using the search interface. &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/MMC-10J/SOL-R5-12-00006/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/MMC-10J/SOL-R5-12-00006/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:02:58 GMT</pubDate>
	</item>

<item>

		<title>REMEDIAL ACTION CONTRACT III (RAC III) [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9867</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9867</guid>
		<description>U.S. EPA, Office of Acquisition Management, Region VII, Kansas City, KS.&lt;br /&gt;
Federal Business Opportunities, FBO-4143, Solicitation SOL-R7-13-00011 &lt;br /&gt;&lt;br /&gt; EPA requires professional architect and engineering services to support RAC III remedial planning and oversight activities at Superfund Sites in Region 10, which covers Alaska, Idaho, Oregon, and Washington. This procurement envisions the award of up to two fixed-rate, indefinite-delivery, indefinite-quantity, award-term RACs under a small business set-aside. The base period of performance will be three years, with two award terms of four years and three years, for a potential total period of 10 years. Work will be issued by task orders. The RFP for SOL-R7-13-00011 is expected to be released on or about May 1, 2013. NAICS code 562910 applies. The solicitation, amendments, and other information related to this procurement will be posted at &lt;A HREF=&quot;http://www.epa.gov/oam/regions/index.htm#solam&quot;&gt;http://www.epa.gov/oam/regions/index.htm#solam&lt;/A&gt;. FBO notice: &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00011/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/RegVII/SOL-R7-13-00011/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:02:23 GMT</pubDate>
	</item>

<item>

		<title>ESG - NEW MEXICO-ARIZONA (NM-AZ) PERFORMANCE-BASED REMEDIATION (PBR) [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9866</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9866</guid>
		<description>Air Force Materiel Command, ESG - Enterprise Sourcing Group, Wright Patterson AFB, OH.&lt;br /&gt;
Federal Business Opportunities, FBO-4144, Solicitation FA8903-12-R-0050, 2013 &lt;br /&gt;&lt;br /&gt; The 772 ESS/PKJ, Base Realignment and Closure Branch, is issuing an RFP for the NM-AZ PBR requirement. This is a major source selection for PBR in support of DoD installations in New Mexico (Cannon AFB, Holloman AFB, and Kirtland AFB) and Arizona (Luke AFB). The intent of this PBR effort is to maximize the number of site closeouts (SCs) or advance sites as close to SC as practicable during the period of performance (POP) in a cost-effective manner for 88 Installation Restoration Program sites and 21 Military Munitions Response Program sites at the above installations. This procurement is solicited as a total small business set-aside envisioned as a single stand-alone &quot;C&quot; contract with a firm-fixed-price arrangement at a range of $35 to $42 million and a POP of 120 months. The NAICS code for this acquisition is 562910. Proposals are due by 1600 hrs CDT on April 29, 2013.&lt;br /&gt;
&lt;A HREF=&quot;https://www.fbo.gov/notices/7f18f634d29cee9fd87d8cd62a786aee&quot;&gt;https://www.fbo.gov/notices/7f18f634d29cee9fd87d8cd62a786aee&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:02:09 GMT</pubDate>
	</item>

<item>

		<title>HAZARDOUS WASTE REMOVAL AND EMERGENCY RESPONSE SERVICES FOR THE U.S. EPA REGION 3 ESC [Market/Commercialization]</title>
		<link>http://www.clu-in.org/products/tins/tinsone.cfm?num=9865</link>
				<guid isPermaLink="false">http://www.clu-in.org/products/tins/tinsone.cfm?num=9865</guid>
		<description>U.S. EPA, Office of Acquisition Management, Region III, Contracts Branch (3PM10).&lt;br /&gt;
Federal Business Opportunities, FBO-4151, Solicitation RFQ-PA-13-00016, 2013 &lt;br /&gt;&lt;br /&gt; The Government intends to award a fixed-unit-price, indefinite-delivery, indefinite-quantity contract, including one 12-month base period and four 1-year option periods, for hazardous waste removal and emergency response services for the U.S. EPA Environmental Science Center, located at Fort Meade, Maryland. This procurement is a 100% woman-owned small business set-aside, NAICS code 562112, with a size standard of $35.5M. The quotation due date (closing date) is April 24, 2013, by 5:00 pm ET, via e-mail. &lt;A HREF=&quot;https://www.fbo.gov/spg/EPA/OAM/3PM10/RFQ-PA-13-00016/listing.html&quot;&gt;https://www.fbo.gov/spg/EPA/OAM/3PM10/RFQ-PA-13-00016/listing.html&lt;/A&gt; &lt;br /&gt;&lt;br /&gt; </description>
		<pubDate>Thu, 11 Apr 2013 19:01:12 GMT</pubDate>
	</item>

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