Thematische Bibliographien / Site remediation

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Auswahl der wissenschaftlichen Literatur zum Thema „Site remediation“

Autor: Grafiati

Veröffentlicht am 4. Juni 2021

Zuletzt aktualisiert am 19. Februar 2022

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Zeitschriftenartikel zum Thema "Site remediation"

Vogel, Gregory A., Alan S. Goldfarb, George A. Malone und Dennis E. Lundquist. „A survey of technical aspects of site remediation: Site remediation strategy“. Waste Management 14, Nr. 1 (Januar 1994): 61–66. http://dx.doi.org/10.1016/0956-053x(94)90021-3.

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Bainbridge, Kent L., Greg S. Foote und Grant A. Gartrell. „RANCOUR PROPERTY SITE REMEDIATION“. Proceedings of the Water Environment Federation 2003, Nr. 12 (01.01.2003): 134–56. http://dx.doi.org/10.2175/193864703784755535.

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Otto, Martha, Melissa Floyd und Sankalpa Bajpai. „Nanotechnology for site remediation“. Remediation Journal 19, Nr. 1 (Dezember 2008): 99–108. http://dx.doi.org/10.1002/rem.20194.

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Vogel, Gregory A., George G. Anderson und Dennis E. Lundquist. „Technical aspects of site remediation: Vapor phase thermal oxidation for site remediation“. Waste Management 14, Nr. 2 (Januar 1994): 139–44. http://dx.doi.org/10.1016/0956-053x(94)90006-x.

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Wang, Sih Yu, Zong Han Yang, Jian Li Lin, Tzu Hsin Lee und Chih Ming Kao. „Site Characterization and Optimization of Corrective Actions at a Chlorinated-Solvent Spill Site“. Advanced Materials Research 1030-1032 (September 2014): 174–77. http://dx.doi.org/10.4028/www.scientific.net/amr.1030-1032.174.

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The industrial solvent, trichloroethene (TCE), is among the most ubiquitous chlorinated compounds found in subsurface contamination. Operation of an avionics repair shop at a military base has resulted in past release of solvent chemicals including TCE and other chlorinated aliphatic hydrocarbons. The objectives of this study were to investigate the occurrence of natural remediation process and the feasibility of using natural remediation as the remedial option at this site. The following tasks have been performed: (1) site characterization to delineate the lateral and vertical extent of contaminants in the subsurface; (2) field investigation of natural remediation; and (3) efficiency of TCE removal through natural remediation in the field. Results indicate that TCE biodegradation occurred at this site, and natural remediation is a possible remedial alternative for TCE plume containment. Evidences for the TCE natural remediation included: (1) decreased TCE and other chlorinated compounds concentrations along the transport path; (2) production of the TCE degradation byproducts (including ethane); (3) decreased total organic carbon along the transport path, (4) deceased pH in the spill source area; (5) production of chloride ion and carbon dioxide. Experiences obtained from this study would be helpful in developing a site remedial protocol for other DNAPL sites.

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Fisenne, Isabel M. „USDOE remediation site case study“. Environment International 22 (Januar 1996): 243–49. http://dx.doi.org/10.1016/s0160-4120(96)00114-6.

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Barbour, Richard, Jeffrey M. Smith und Kenneth Wenz. „Millville site multimedia remediation program“. Remediation Journal 5, Nr. 4 (September 1995): 83–103. http://dx.doi.org/10.1002/rem.3440050409.

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Gu, Ji-Dong. „Mining, pollution and site remediation“. International Biodeterioration & Biodegradation 128 (März 2018): 1–2. http://dx.doi.org/10.1016/j.ibiod.2017.11.006.

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Sun, Xiao Song, An Ping Liu, Fang Zhao, Xiao Nan Sun und Jian Ming Sun. „Risk Assessment and Remediation of Cd-Contaminated Site“. Advanced Materials Research 414 (Dezember 2011): 221–25. http://dx.doi.org/10.4028/www.scientific.net/amr.414.221.

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Based on early environmental investigation of the contaminated site, this paper conducts risk assessment for the particular Cd-contaminated site (S-block), acquires the remediation scope of contaminated soils and puts forward a corresponding remediation project accordingly, and then monitors and compares the Cd content before and after remediation. The results indicate that the risk assessment can reflect contamination distribution and contamination level of S-block, which provides a reliable basis for targeted remediation, and the monitoring results show that S-block has been remedied effectively.

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Gruiz, Katalin. „Contaminated-site remediation: role and classification“. Land Contamination & Reclamation 17, Nr. 3 (01.11.2009): 533–42. http://dx.doi.org/10.2462/09670513.974.

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Dissertationen zum Thema "Site remediation"

Tang, Xi Yang John J. Goyne Keith William. „Risk and stability of phosphate-immobilized lead in contaminated urban soil and mining sites in the Jasper County Superfund Site“. Diss., Columbia, Mo. : University of Missouri-Columbia, 2007. http://hdl.handle.net/10355/4911.

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Thesis (M.S.)--University of Missouri-Columbia, 2007.
The entire dissertation/thesis text is included in the research.pdf file; the official abstract appears in the short.pdf file (which also appears in the research.pdf); a non-technical general description, or public abstract, appears in the public.pdf file. Title from title screen of research.pdf file (viewed on November 6, 2007) Includes bibliographical references.

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Tam, Edwin Kwan Lap. „Decision methodology for site owners for the remediation of contaminated sites“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1998. http://www.collectionscanada.ca/obj/s4/f2/dsk1/tape11/PQDD_0012/NQ41514.pdf.

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Journell, Scot. „Site Remediation of Underground Storage Tank Contamination“. Arizona-Nevada Academy of Science, 1990. http://hdl.handle.net/10150/296432.

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From the Proceedings of the 1990 Meetings of the Arizona Section - American Water Resources Association and the Hydrology Section - Arizona-Nevada Academy of Science - April 21, 1990, Arizona State University, Tempe, Arizona
Remedial techniques for sub-surface soil and water contamination are dependent on the lateral and vertical extent of petroleum hydrocarbon contamination and the type of petroleum hydrocarbons which have been released into the sub-surface. Specific remedial technologies are required for diesel fuel and heavy oils compared to the more volatile gasoline compounds. Available remedial technologies for vadose zone contamination include excavation and treatment; soil vapor extraction and possible vapor burning; bioremediation; and chemical treatment. Remedial technologies for ground-water contamination include water recovery, contaminant volatilization, carbon adsorption, bioremediation and water reinjection. Specialized apparatuses are utilized when petroleum hydrocarbon product floating on the water table surface must be separated from the ground water. A number of hydrologic considerations must be evaluated prior to any remediation scenario. These considerations include geologic characterization of the sub-surface soil matrix, and aquifer.

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Han, Liping. „Groundwater remediation at a former oil service site“. Texas A&M University, 2005. http://hdl.handle.net/1969.1/2334.

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As an intern with URS Corporation, I participated in several remediation and wastewater treatment projects during the year 2004. A groundwater remediation project was selected to present in this record of study for my Doctor of Engineering degree not only because I spent more time on it than any other project, but also because it represents the broadness and depth of a typical URS remediation project. In this report, findings from previous environmental investigations were summarized and used for computer modeling and remediation strategy evaluation. Computer models were used to simulate site conditions and assist in remedy design for the site. Current pump-and-treat systems were evaluated by the model under various scenarios. Recommendations were made for the pump-and-treat system to control the contaminant plume. Various remediation technologies were evaluated and compared for their applicability at the site. A combination of on-site remediation and downgradient plume control was chosen as the site remediation strategy. Treatability studies and additional modeling work are needed for the remediation system design and optimization.

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Gallagher, Patricia M. „Passive Site Remediation for Mitigation of Liquefaction Risk“. Diss., Virginia Tech, 2000. http://hdl.handle.net/10919/29610.

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Passive site remediation is a new concept proposed for non-disruptive mitigation of liquefaction risk at developed sites susceptible to liquefaction. It is based on the concept of slow injection of stabilizing materials at the edge of a site and delivery of the stabilizer to the target location using the natural groundwater flow. The purpose of this research was to establish the feasibility of passive site remediation through identification of stabilizing materials, a study of how to design or adapt groundwater flow patterns to deliver the stabilizers to the right place at the right time, and an evaluation of potential time requirements and costs. Stabilizer candidates need to have long, controllable gel times and low viscosities so they can flow into a liquefiable formation slowly over a long period of time. Colloidal silica is a potential stabilizer for passive site remediation because at low concentrations it has a low viscosity and a wide range of controllable gel times of up to about 100 days. Loose Monterey No. 0/30 sand samples (Dr = 22%) treated with colloidal silica grout were tested under cyclic triaxial loading to investigate the influence of colloidal silica grout on the deformation properties. Distinctly different deformation properties were observed between grouted and ungrouted samples. Untreated samples developed very little axial strain after only a few cycles and prior to the onset of liquefaction. Once liquefaction was triggered, large strains occurred rapidly and the samples collapsed within a few additional cycles. In contrast, grouted sand samples experienced very little strain during cyclic loading. What strain accumulated did so uniformly throughout loading and the samples remained intact after cyclic loading. In general, samples stabilized with 20 weight percent colloidal silica experienced very little (less than two percent) strain during cyclic loading. Sands stabilized with 10 weight percent colloidal silica tolerated cyclic loading well, but experienced slightly more (up to eight percent) strain. Treatment with colloidal silica grout significantly increased the deformation resistance of loose sand to cyclic loading. Groundwater and solute transport modeling were done using the codes MODFLOW, MODPATH, and MT3DMS. A "numerical experiment" was done to determine the ranges of hydraulic conductivity and hydraulic gradient where passive site remediation might be feasible. For a treatment are of 200 feet by 200 feet, a stabilizer travel time of 100 days, and a single line of low-head (less than three feet) injection wells, it was found that passive site remediation could be feasible in formations with hydraulic conductivity values of 0.05 cm/s or more and hydraulic gradients of 0.005 and above. Extraction wells will increase the speed of delivery and help control the down gradient extent of stabilizer movement. The results of solute transport modeling indicate that dispersion will play a large role in determining the concentration of stabilizer that will be required to deliver an adequate concentration at the down gradient edge. Consequently, thorough characterization of the hydraulic conductivity throughout the formation will be necessary for successful design and implementation of passive site remediation. The cost of passive site remediation is expected to be competitive with other methods of chemical grouting, i.e. in the range of $60 to $180 per cubic meter of treated soil, depending on the concentration of colloidal silica used.
Ph. D.

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Kilback, Andrew H. „Assessment of groundwater remediation at an industrial landfill site“. Thesis, National Library of Canada = Bibliothèque nationale du Canada, 2001. http://www.collectionscanada.ca/obj/s4/f2/dsk3/ftp04/MQ59505.pdf.

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Day, Monica. „A tool for assessing citizen deliberative decisions about contaminated sites“. Diss., Connect to online resource - MSU authorized users, 2008.

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Lukasiak, Anna D. „Internet-enabled integrated presentation system for site remediation preliminary assessment“. Thesis, Massachusetts Institute of Technology, 1997. http://hdl.handle.net/1721.1/43437.

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Gutierrez, Diana, und Diana Gutierrez. „In-Situ Biosequestration for Remediation of Uranium in Groundwater at the Monument Valley UMTRA Site“. Thesis, The University of Arizona, 2016. http://hdl.handle.net/10150/620727.

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The Monument Valley UMTRA Site is a former uranium mining site that is located in Cane Valley, Arizona. The mining that occurred there from 1943 to 1968 created a groundwater contaminant plume that consists of nitrate, sulfate, and uranium. There are only a few viable methods for remediation of these types of contaminants occurring in large, deep plumes. Monitored natural attenuation is a popular approach because it is a green and low-cost alternative. However, it is often ineffective without some form of supplemental enhancement. In-situ biosequestration is one method of enhanced attenuation, which involves injecting an electron- donating substrate that will promote microbial activity and sequester contaminants by bioprecipitation, biomineralization, and enhanced adsorption. Prior tests conducted at the Monument Valley site in the center of the plume using ethanol as the electron donor proved effective in the treatment of nitrate, sulfate, and uranium. Subsequent pilot scale tests are being conducted in the source zone of the Monument Valley Site to further investigate the feasibility and effectiveness of using in-situ biosequestration for treatment of uranium contaminated groundwater. The preliminary results of these tests are discussed.

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Andrade, Marc-David. „Development of an on-site ex-situ unsaturated-flow remediation process for trace metal contaminated soils“. Thesis, McGill University, 2005. http://digitool.Library.McGill.CA:80/R/?func=dbin-jump-full&object_id=85117.

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Innovative means and methods were tested to develop an economical, pragmatic and environmentally sustainable soil remediation process for heavy metal contaminated soils. An unsaturated-flow soil washing procedure was devised to dissolve the soil-bound toxic heavy metals; the latter were extracted by a chemical washing solution that percolated through the soil matrix. Subsequently, the leached toxic heavy metals were selectively concentrated, by a chemical precipitation process, into a solid waste. Thereby, a fraction of the spent ethylenediaminetetraacetic acid (EDTA), within the washing and rinsing leachate, was theoretically regenerated and recycle-ready.
The unsaturated-flow washing procedure was perfected by applying different treatments to a soil from a secure landfill. This soil was contaminated with Cd, Co, Cr, Cu, Fe, Mn, Ni, Pb, S and Zn. The major contaminants were Fe, Pb, Zn, S, Cu and Mn, making up 25, 1.9, 1.0, 0.4, 0.4 and 0.2%wt of the soil. The extraction responses of the contaminants and those of Al, Ca, Mg and P were established for citric acid (0.5 M) and different molarities of diammonium EDTA ((NH4)2EDTA). The DOW Chemical Company supplied the (NH4)2EDTA (i.e. VERSENE), a 1.37M industrial cleaner, which roughly costs $1.85kg-1 in bulk. The affordability of VERSENE was a pre-condition for hoping to satisfy the economical feasibility of remediating trace metal contaminated soils.
Ultimately, the developed unsaturated-flow washing procedure was tested in a pilot-scale experiment, for its ability to remediate a soil from an abandoned car battery recycling facility. The latter soil was severely contaminated with Pb (3.9%wt). Drip irrigation was used to apply (NH4) 2EDTA and water-rinsing solutions to the surface of soil heaps that rested atop an impermeable barrier, which permitted the retrieval of the leachate. A cumulative EDTA input to the soil of 10.6% wt extracted 49.4% of the total Pb content of the soil. Alternatively, readily biodegradable citric acid barely extracted 2.2% of the total Pb content of the soil, for a cumulative input of 18.1% weight of soil. Different treatments were tested for their effectiveness in concentrating the leached toxic heavy metals into a solid waste. The Pb was best precipitated with Na2S alone, as it provided the most concentrated solid toxic waste.
The environmental sustainability of remediating trace metal contaminated soils was thoroughly examined, as per the amounts of chemical entrants and toxic waste by-products, and per the post-treatment leaching of toxic levels of the remaining and potentially toxic trace metals. (Abstract shortened by UMI.)

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Bücher zum Thema "Site remediation"

Eller, P. Gary, und William R. Heineman, Hrsg. Nuclear Site Remediation. Washington, DC: American Chemical Society, 2000. http://dx.doi.org/10.1021/bk-2001-0778.

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R, Wilson Stephanie, Hrsg. Site remediation planning and management. Boca Raton: CRC Press, 1997.

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Site assessment and remediation handbook. 2. Aufl. Boca Raton, Fla: Lewis Publishers, 2003.

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Fundamentals of hazardous waste site remediation. Boca Raton: Lewis Publishers, 1999.

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Hazardous waste site remediation: Source control. Boca Raton: Lewis Publishers, 1993.

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Sibul, U. Site remediation technologies used in Ontario. [Toronto]: Ministry of Environment and Energy, 1996.

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E, Hinchee Robert, Hrsg. In situ thermal technologies for site remediation. Boca Raton, Fla: Lewis Publishers, 1993.

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Asante-Duah, D. Kofi. Managing contaminated sites: Problem diagnosis and development of site restoration. Chichester: Wiley, 1996.

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United States. Environmental Protection Agency. Office of Solid Waste and Emergency Response. Technical support services for Superfund site remediation. 2. Aufl. Washington, DC: U.S. Environmental Protection Agency, Office of Solid Waste and Emergency Response, 1990.

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Rong, Yue. Fundamentals of Environmental Site Assessment and Remediation. Boca Raton : Taylor & Francis, a CRC title, part of the Taylor & Francis imprint, a member of the Taylor & Francis Group, the academic division of T&F Informa, plc, 2018.: CRC Press, 2018. http://dx.doi.org/10.1201/b22330.

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Buchteile zum Thema "Site remediation"

Milkey, Nancy E. „Site Assessment“. In MTBE Remediation Handbook, 73–92. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-1-4615-0021-6_5.

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Dutta, Subijoy. „Site remediation process“. In Environmental Treatment Technologies for Municipal, Industrial and Medical Wastes, 7–17. 2. Aufl. London: CRC Press, 2021. http://dx.doi.org/10.1201/9781003004066-2.

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Surbeck, Cristiane Q., und Jeff Kuo. „Groundwater Remediation“. In Site Assessment and Remediation for Environmental Engineers, 173–228. First edition. | Boca Raton, FL : CRC Press/Taylor & Francis Group, LLC, 2021. |: CRC Press, 2021. http://dx.doi.org/10.1201/9780429427107-6.

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Mariano, Christopher G. „Physical Treatment at a Massachusetts Site“. In MTBE Remediation Handbook, 435–44. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-1-4615-0021-6_23.

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Mercer, James W., Robert M. Cohen und Michael R. Noel. „DNAPL Site Characterization Issues at Chlorinated Solvent Sites“. In SERDP/ESTCP Environmental Remediation Technology, 217–80. New York, NY: Springer New York, 2010. http://dx.doi.org/10.1007/978-1-4419-1401-9_8.

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Espy, David L. „Physical Treatment at a New Hampshire Site“. In MTBE Remediation Handbook, 419–33. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-1-4615-0021-6_22.

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Kerfoot, William B., und Paul LeCheminant. „Ozone Microbubble Sparging at a California Site“. In MTBE Remediation Handbook, 455–72. Boston, MA: Springer US, 2003. http://dx.doi.org/10.1007/978-1-4615-0021-6_25.

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Zhang, Wei-xian, Jiasheng Cao und Daniel Elliott. „Iron Nanoparticles for Site Remediation“. In Nanotechnology and the Environment, 248–55. Washington, DC: American Chemical Society, 2004. http://dx.doi.org/10.1021/bk-2005-0890.ch033.

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Körbitzer, B., H. Witte und E. Schramm. „Combined Technologies for Site Remediation“. In Contaminated Soil ’90, 1445–46. Dordrecht: Springer Netherlands, 1990. http://dx.doi.org/10.1007/978-94-011-3270-1_332.

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Surbeck, Cristiane Q., und Jeff Kuo. „Vadose Zone Soil Remediation“. In Site Assessment and Remediation for Environmental Engineers, 121–72. First edition. | Boca Raton, FL : CRC Press/Taylor & Francis Group, LLC, 2021. |: CRC Press, 2021. http://dx.doi.org/10.1201/9780429427107-5.

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Konferenzberichte zum Thema "Site remediation"

Armstrong, J. E., M. K. Burkholder und K. W. Biggar. „Applying Decision Analysis to Site Remediation“. In Canadian International Petroleum Conference. Petroleum Society of Canada, 2004. http://dx.doi.org/10.2118/2004-137.

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AKINYEMI, Lukman, Shamsudeen Kunle Alausa, Ralph Pollister Soule, Ryan Franklin, Anthony Bartruff, Cas F. Bridge, Karson R. Bizzell et al. „Geophysics for Contaminant and Site Remediation“. In Symposium on the Application of Geophysics to Engineering and Environmental Problems 2015. Society of Exploration Geophysicists and Environment and Engineering Geophysical Society, 2015. http://dx.doi.org/10.4133/sageep.28-037.

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Babcock, Esther, John Bradford, Benjamin Petersen, Jeremy Strohmeyer, Douglas Lambert, Boston Fodor, Colin Zelt, Jianxiong Chen und Alan Levander. „Geophysics for Contaminant and Site Remediation“. In Symposium on the Application of Geophysics to Engineering and Environmental Problems 2015. Society of Exploration Geophysicists and Environment and Engineering Geophysical Society, 2016. http://dx.doi.org/10.4133/sageep.29-038.

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Nzewi, Emmanuel, und Demola Onafuye. „An Investigative Approach to Site Remediation“. In World Water and Environmental Resources Congress 2001. Reston, VA: American Society of Civil Engineers, 2001. http://dx.doi.org/10.1061/40569(2001)81.

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Bethel, E. W., Janet Jacobsen und Preston Holland. „Site remediation in a virtual environment“. In IS&T/SPIE 1994 International Symposium on Electronic Imaging: Science and Technology, herausgegeben von Robert J. Moorhead II, Deborah E. Silver und Samuel P. Uselton. SPIE, 1994. http://dx.doi.org/10.1117/12.172079.

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Banerjee, Anomitra, und Miller Jothi. „Site Remediation Techniques in India: A Review“. In ASME 2013 15th International Conference on Environmental Remediation and Radioactive Waste Management. American Society of Mechanical Engineers, 2013. http://dx.doi.org/10.1115/icem2013-96215.

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India is one of the developing countries operating site remediation techniques for the entire nuclear fuel cycle waste for the last three decades. In this paper we intend to provide an overview of remediation methods currently utilized at various hazardous waste sites in India, their advantages and disadvantages. Over the years the site remediation techniques have been well characterized and different processes for treatment, conditioning and disposal are being practiced. Remediation Methods categorized as biological, chemical or physical are summarized for contaminated soils and environmental waters. This paper covers the site remediation techniques implemented for treatment and conditioning of wastelands arising from the operation of nuclear power plant, research reactors and fuel reprocessing units.

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Rude, Peter D. „The Cascade Pole Site Sediment Remediation: Part 1 - The Road to Remediation“. In Third Specialty Conference on Dredging and Dredged Material Disposal. Reston, VA: American Society of Civil Engineers, 2003. http://dx.doi.org/10.1061/40680(2003)131.

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Scott, L. Max. „A Successful Remediation Project“. In ASME 2009 12th International Conference on Environmental Remediation and Radioactive Waste Management. ASMEDC, 2009. http://dx.doi.org/10.1115/icem2009-16400.

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As part of a program to visit formerly licensed sites to determine if they meet current uncontrolled release conditions, a United States Nuclear Regulatory Commission (USNRC) inspection was conducted in the fall of 1993 at a site that had possessed a radioactive material license from about 1955 to 1970. While the license was in force, the plant processed magnesium scrap containing up to 4 percent thorium. The source of the scrap is believed to be the aircraft manufacturing industry. The scrap was placed in furnaces and heated to the melting point of magnesium, and the molten magnesium was drawn off, leaving the thorium with the residue (dross). Under the regulation in existence at that time, the thorium dross was buried on site in an approximate 14 acre field. In 1993 the inspector found readings up to 900uR/h. Early in 1994 an informal grid survey of most of the 14 acre site was conducted. Based on that survey, it was concluded that the thorium was widespread and extended beyond the property lines. The preliminary findings were reported to the USNRC, and in 1994 the site was designated as a Site Decommissioning Management Plan (SMPD) site. A remediation team was formed which included the following disciplines: remediation health physics, geology, hydrology, engineering, law, public relations, and project management. This remediation team planned, participated in selecting vendors, and provided project over site for all activities from site characterization through the final status survey. In 2006 the site was released for uncontrolled access. A chronology of activities with lessons learned will be presented.

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Cowart, James B., Mark Levin, Keith Bowers, Julie E. Ash und Warren C. Rider. „Burlington Mine Site Voluntary Cleanup: Innovative Design for Mine Site Remediation“. In Biennial Geotechnical Symposium 2004. Reston, VA: American Society of Civil Engineers, 2004. http://dx.doi.org/10.1061/40758(151)11.

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Devinny, Joseph S. „Environmental Site Characterization and Remediation Design Guidance: Introduction“. In National Conference on Environmental and Pipeline Engineering. Reston, VA: American Society of Civil Engineers, 2000. http://dx.doi.org/10.1061/40507(282)26.

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Berichte der Organisationen zum Thema "Site remediation"

Craig, J. R. Jr, J. A. Saric, T. Schneider und M. K. Yates. Status report: Fernald site remediation. Office of Scientific and Technical Information (OSTI), Januar 1995. http://dx.doi.org/10.2172/10119898.

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US DOE. Salmon Site Remediation Investigation Report, Appendix A. Office of Scientific and Technical Information (OSTI), September 1999. http://dx.doi.org/10.2172/14967.

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Kamboj, Sunita, und Lisa Durham. Post-Remediation Radiological Dose Assessment, Painesville Site, Painesville, Ohio. Office of Scientific and Technical Information (OSTI), November 2013. http://dx.doi.org/10.2172/1177889.

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Waters, L. C., A. Palausky, R. W. Counts und R. A. Jenkins. Performance of immunoassay kits for site characterization and remediation. Office of Scientific and Technical Information (OSTI), Dezember 1995. http://dx.doi.org/10.2172/204201.

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COLORADO SCHOOL OF MINES GOLDEN. In Situ Chemical Oxidation for Groundwater Remediation: Site-Specific Engineering & Technology Application. Fort Belvoir, VA: Defense Technical Information Center, Oktober 2010. http://dx.doi.org/10.21236/ada571919.

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Haass, C. C. Hanford site tank waste remediation system programmatic environmental review report. Office of Scientific and Technical Information (OSTI), September 1998. http://dx.doi.org/10.2172/362426.

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PARSONS ENGINEERING SCIENCE INC DENVER CO. Intrinsic Remediation Engineering Evaluation/Cost Analysis for UST Site 870. Fort Belvoir, VA: Defense Technical Information Center, Juni 1995. http://dx.doi.org/10.21236/ada384520.

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Kamboj, Sunita, und Lisa A. Durham. Post-Remediation Radiological Dose Assessment, Linde Site, Tonawanda, New York. Office of Scientific and Technical Information (OSTI), Juni 2014. http://dx.doi.org/10.2172/1177293.

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Ringland, J. T. Risk-based analyses in support of California hazardous site remediation. Office of Scientific and Technical Information (OSTI), August 1995. http://dx.doi.org/10.2172/104451.

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Boothe, G. F. Remediation and cleanout levels for Hanford site single-shell tanks. Office of Scientific and Technical Information (OSTI), Dezember 1995. http://dx.doi.org/10.2172/274893.

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