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Статті в журналах з теми "Site remediation"

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Автор: Grafiati

Опубліковано: 4 червня 2021

Оновлено: 19 лютого 2022

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1

Vogel, Gregory A., Alan S. Goldfarb, George A. Malone, and Dennis E. Lundquist. "A survey of technical aspects of site remediation: Site remediation strategy." Waste Management 14, no. 1 (January 1994): 61–66. http://dx.doi.org/10.1016/0956-053x(94)90021-3.

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2

Bainbridge, Kent L., Greg S. Foote, and Grant A. Gartrell. "RANCOUR PROPERTY SITE REMEDIATION." Proceedings of the Water Environment Federation 2003, no. 12 (January 1, 2003): 134–56. http://dx.doi.org/10.2175/193864703784755535.

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3

Otto, Martha, Melissa Floyd, and Sankalpa Bajpai. "Nanotechnology for site remediation." Remediation Journal 19, no. 1 (December 2008): 99–108. http://dx.doi.org/10.1002/rem.20194.

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4

Vogel, Gregory A., George G. Anderson, and Dennis E. Lundquist. "Technical aspects of site remediation: Vapor phase thermal oxidation for site remediation." Waste Management 14, no. 2 (January 1994): 139–44. http://dx.doi.org/10.1016/0956-053x(94)90006-x.

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5

Wang, Sih Yu, Zong Han Yang, Jian Li Lin, Tzu Hsin Lee, and 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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6

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

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7

Barbour, Richard, Jeffrey M. Smith, and Kenneth Wenz. "Millville site multimedia remediation program." Remediation Journal 5, no. 4 (September 1995): 83–103. http://dx.doi.org/10.1002/rem.3440050409.

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8

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

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9

Sun, Xiao Song, An Ping Liu, Fang Zhao, Xiao Nan Sun, and Jian Ming Sun. "Risk Assessment and Remediation of Cd-Contaminated Site." Advanced Materials Research 414 (December 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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10

Gruiz, Katalin. "Contaminated-site remediation: role and classification." Land Contamination & Reclamation 17, no. 3 (November 1, 2009): 533–42. http://dx.doi.org/10.2462/09670513.974.

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11

Abbott, John C. "Remediation efforts at DOE's hanford site." Federal Facilities Environmental Journal 7, no. 1 (1996): 27–36. http://dx.doi.org/10.1002/ffej.3330070104.

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12

Hogland, William. "Remediation of an old landsfill site." Environmental Science and Pollution Research 9, S1 (January 2002): 49–54. http://dx.doi.org/10.1007/bf02987426.

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13

Panagiotakis, I., and D. Dermatas. "Contaminated Site Management and Remediation Technologies." Bulletin of Environmental Contamination and Toxicology 101, no. 6 (November 1, 2018): 691. http://dx.doi.org/10.1007/s00128-018-2483-5.

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14

Bennett, GaryF. "Innovative site remediation technology: Thermal desorption." Journal of Hazardous Materials 39, no. 1 (October 1994): 121–22. http://dx.doi.org/10.1016/0304-3894(94)80065-0.

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15

Huang, Yao Xuan, and Li Liu. "Financing and Operation for Contaminated Site Remediation." Advanced Materials Research 361-363 (October 2011): 1411–15. http://dx.doi.org/10.4028/www.scientific.net/amr.361-363.1411.

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Анотація:

Based on the financing and capital operation of the U.S. Superfund, the soil remediation funds of EU countries and Soil and Groundwater Pollution Remediation Fund in Taiwan, the concept of a contaminated-site-fund managed by government is proposed, followed by further illustration of its purpose, raising, application and return.

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16

Marques, Ana P. G. C., António O. S. S. Rangel, and Paula M. L. Castro. "Remediation of Heavy Metal Contaminated Soils: An Overview of Site Remediation Techniques." Critical Reviews in Environmental Science and Technology 41, no. 10 (April 14, 2011): 879–914. http://dx.doi.org/10.1080/10643380903299517.

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17

Plant, Roel, Spike Boydell, Jason Prior, Joanne Chong, and Aleta Lederwasch. "From liability to opportunity: An institutional approach towards value-based land remediation." Environment and Planning C: Politics and Space 35, no. 2 (July 26, 2016): 197–220. http://dx.doi.org/10.1177/0263774x16646772.

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Анотація:

The remediation of contaminated sites impacts on stakeholders in potentially beneficial ways, yet stakeholder dialogue has historically been focussed on costs, risk, liability, stigma, and other negatives. Shedding light on stakeholders’ remediation values can help reform remediation policy towards more positive outcomes of site clean-up. We adopt institutional theory to elicit plural motivations and cognitive assumptions as embedded in stakeholders’ expressions of remediation values, objectives, and outcomes. We explore in four case studies with varying size, complexity, cultural diversity, and geographical location (three in Australia, one in Fiji) how remediation values operate within remediation decisions. Our findings suggest that more than economic costs, liability, and risks are at play in decision-making on contaminated land. Our research confirmed that different socio-ethical, environmental and sustainability values are evaluated differently by different types of actors (site owners, regulators, auditors, residents, local government, consultants). We found that remediation values often shift in the course of a remediation decision-making process, suggesting learning and improved understanding. Remediation policy that better facilitates and aligns stakeholders’ articulations of initial and emergent outcomes sought from site clean-up is likely to enhance both economic and social value outcomes of remediation. Further research is needed on how remediation policy could better incorporate remediation value dynamics in stakeholder consultation and engagement.

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18

Huysegoms, Lies, Sandra Rousseau, and Valérie Cappuyns. "Chemical or Natural? Including LCA in Social CBA to Compare Remediation Alternatives for a Dry-Cleaning Facility." Sustainability 11, no. 7 (April 3, 2019): 1975. http://dx.doi.org/10.3390/su11071975.

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The choice between remediation alternatives for contaminated sites is complicated by different elements, e.g., the occurrence of multiple contaminants, the extent of the contamination, or the urban location, complicate the choice between remediation alternatives. This paper addresses this challenging choice by analyzing a case study of an extensive soil and groundwater contamination by a dry-cleaning company. For remediating this site, two alternatives were proposed. The first remediation alternative combines several techniques with in-situ chemical oxidization being the most important one. Due to the potential negative impact of this alternative on local residents a second remediation alternative was drawn up, in which the focus lies on the use of stimulated biological degradation. A Life Cycle Assessment (LCA) was performed on both alternatives and showed that the second alternative had a lower environmental impact. The inclusion of monetized LCA results in the calculation of a social Cost-Benefit Analysis (CBA) provided a more extensive view of the secondary environmental costs and benefits of the remediation alternatives. The results of the social CBA allow to conclude that both alternatives are not socially desirable, the chemical alternative however is socially less disadvantageous than the more natural remediation alternative.

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19

Karlsson, Haraldur. "Horizontal Systems Technology for Shallow Site Remediation." Journal of Petroleum Technology 45, no. 02 (February 1, 1993): 160–65. http://dx.doi.org/10.2118/24600-pa.

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20

Ladd, Beth, and Curtis C. Travis. "In situ thermal technologies for site remediation." Journal of Hazardous Materials 42, no. 1 (June 1995): 107. http://dx.doi.org/10.1016/s0304-3894(95)90044-6.

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21

Freeman, Natalie C. G., Paul J. Lioy, and Alan H. Stern. "Reduction in Residential Chromium Following Site Remediation." Journal of the Air & Waste Management Association 50, no. 6 (June 2000): 948–53. http://dx.doi.org/10.1080/10473289.2000.10464132.

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22

Barkley, N. P., C. W. Farrell, and T. W. Gardner-Clayson. "Alternating Current Electrocoagulation for Superfund Site Remediation." Air & Waste 43, no. 5 (May 1993): 784–89. http://dx.doi.org/10.1080/1073161x.1993.10467161.

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23

寇, 婷. "Summary of Cadmium Contaminated Site Remediation Technology." Advances in Environmental Protection 09, no. 02 (2019): 158–63. http://dx.doi.org/10.12677/aep.2019.92024.

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24

Devinny, Joseph S., John April, Daniel F. Buss, Charlie Johnson, Khalique Khan, Kenneth H. Lister, Julio A. Nuno, Patrick S. Sullivan, M'balia Tagoe, and David P. Williams. "The ASCE Draft Environmental Site Remediation Manual." Practice Periodical of Hazardous, Toxic, and Radioactive Waste Management 1, no. 3 (July 1997): 97–104. http://dx.doi.org/10.1061/(asce)1090-025x(1997)1:3(97).

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25

Kavanaugh, Michael C. "Contaminant site remediation: Technology vs. public policy." Water Environment Research 68, no. 6 (September 1996): 963–64. http://dx.doi.org/10.1002/j.1554-7531.1996.tb00171.x.

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26

Knights, B. "Book Review: Hazardous waste site soil remediation." Journal of Chemical Technology & Biotechnology 65, no. 2 (February 1996): 208. http://dx.doi.org/10.1002/(sici)1097-4660(199602)65:2<208::aid-jctb2409>3.0.co;2-v.

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27

Suèr, Pascal, Sören Nilsson-Påledal, and Jenny Norrman. "LCA for Site Remediation: A Literature Review." Soil and Sediment Contamination: An International Journal 13, no. 4 (July 2004): 415–25. http://dx.doi.org/10.1080/10588330490471304.

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28

Suthersan, Suthan S., Scott T. Potter, Matthew Schnobrich, Jennifer Wahlberg, Joseph Quinnan, Nicklaus Welty, and Tom Fewless. "Rethinking Conceptual Site Models in Groundwater Remediation." Groundwater Monitoring & Remediation 36, no. 4 (November 2016): 22–30. http://dx.doi.org/10.1111/gwmr.12192.

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29

Laha, Shonali, Sumitra Mukherjee, and Sarita R. Nebhrajani. "Information Management System for Site Remediation Efforts." Environmental Management 25, no. 5 (May 1, 2000): 513–23. http://dx.doi.org/10.1007/s002679910040.

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30

Goldfarb, Alan S., Gregory A. Vogel, and Dennis E. Lundquist. "Technical aspects of site remediation: Carbon adsorption." Waste Management 14, no. 2 (January 1994): 145–52. http://dx.doi.org/10.1016/0956-053x(94)90007-8.

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31

Dhir, V. K. "In situ thermal technologies for site remediation." Waste Management 14, no. 2 (January 1994): 175–76. http://dx.doi.org/10.1016/0956-053x(94)90013-2.

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32

Bennett, Gary F. "Site Assessment and Remediation Handbook, 2nd ed." Journal of Hazardous Materials 105, no. 1-3 (December 2003): 202–4. http://dx.doi.org/10.1016/j.jhazmat.2003.08.011.

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33

Huang, Jun Ying, Cheng Haw Lee, and Kao Hung Lin. "ELISA Applied on Survey and Remediation of Dioxin Contaminated Site - A Case Study in Southern Taiwan." Advanced Materials Research 788 (September 2013): 444–49. http://dx.doi.org/10.4028/www.scientific.net/amr.788.444.

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Анотація:

Once the pollution was found in a preliminary survey, the related information about the pollution site should be collected to confirm polluted range and quantity. Appropriate remediation technology is implemented until the pollution is completely remove. The more precise survey could lower the risk of uncertainty and improve the site remediation process. However, numerous of sampling and analysis should be done during whole process, including pollution survey, evaluation of remediation effectiveness, and verification after remediation. Time and budget needed for the remediation will be huge loads because of the widely range of site, and characteristics of the complicated pollutants, which may affect the remediation process. This study utilities Enzyme-Linked ImmunoSorbant Assay (ELISA) as the screening tool for dioxin pollutants by means of immuno-biological assay, which can complete the detailed investigation quickly and effectively, and also the pollution reclamation in a short time with the independent quality control. An appropriate screening method plays an important role for a successful and effective remediation.

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34

Xie, Bin, Xiangwei Zhao, Jun Yang, Qingzhong Wang, and Shun Pan. "Research on Intelligent Supervision Method and System Developing of Soil Remediation Project Based on 3D Mobile GIS." E3S Web of Conferences 131 (2019): 01085. http://dx.doi.org/10.1051/e3sconf/201913101085.

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At present, some problems such as inconvenient manual supervision, lack of real-time online supervision and poor online interaction during the implementation of soil remediation project. In order to solve the problems, the supervision method and system development of soil remediation project are studied based on sensing online and 3D mobile GIS technologies. The remediation environment are monitored with fixed sensors online and the heavy metal content are sampled with the mobile sensors. The status of soil remediation site is supervised in real time with video online. All the real-time sensing data are integrated and stored in the comprehensive database. The information of soil pollution and remediation environment is visualized with maps and charts in 3D geographic scenes in the system. In addition, the pollution degree evaluation and remediation effect analysis functions are implemented in system. It is proved with the project practice that the method and system are convenient for managers to monitor the environment on-site and supervise the status of soil remediation site in real time. The informationization and intelligence level of soil remediation project can be effectively improved.

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35

Vanheusden, Bernard. "The Relation between Spatial Planning Law and Soil Remediation Law." Journal for European Environmental & Planning Law 7, no. 1 (2010): 25–36. http://dx.doi.org/10.1163/161372710x12676263561755.

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AbstractThis contribution looks at the relation between spatial planning law and soil remediation law when a contaminated site is being developed. The relation between both legal fields clearly emerges when the land use of the site must be modified in function of the future land use in view. This will have an impact on the remediation criterion as well as on the remediation objective. Another point of contact is the link between a soil remediation and a town planning permit. A good harmony between the spatial planning law and the soil remediation law is essential for the development of a contaminated site. After a brief European perspective, the contribution mainly focuses as a case study on the situation in the Flemish Region (Belgium).

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36

Liao, Shi Guo, and Dong Wei Li. "Review of Contaminated Sites Remediation Technology." Advanced Materials Research 414 (December 2011): 1–4. http://dx.doi.org/10.4028/www.scientific.net/amr.414.1.

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Анотація:

The contaminated site remediation is an important content of site management. Plans for the introduction of measures and requirements to prevent and remediate soil contamination, particularly through the development of inventories of contaminated sites and the definition of targets for prioritization of remediation actions, are expected to have important consequences for site management practice and national site policies. Nowadays contaminated soil and groundwater treatment technologies can be sorted as three categories, that is bioremediation, chemical treatment and physical treatment. Biodegradation generally refers to the breakdown of organic compounds by living organism eventually resulting in the formation of carbon dioxide and water or methane. Chemical remediation is a kind of method that chemical reagent, chemical reaction and chemistry principles are used to reduce the mobility, organisms use ratio of heavy metals and decrease the heavy metals in the soil so as to remediate and repair the soil. Physical treatments in the remediation of contaminated site contains revising methods, capping methods, stabilization methods, electrokinetic methods and so on.

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37

Liu, An Ping, Xiao Nan Sun, Fang Zhao, Xiao Song Sun, Wei Ren, and Jian Ming Sun. "Determination of Pb-Contamination and Remediation Boundary Based on a Specific Site." Advanced Materials Research 414 (December 2011): 27–31. http://dx.doi.org/10.4028/www.scientific.net/amr.414.27.

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Анотація:

In the remediation of heavy metal contaminated site, determining the remediation boundary of contaminated site and amount of contaminated soil are important link of the entire work. This paper uses surfer software to draw out a picture of Pb-contamination distribution in different soil layers, determines a remediation boundary, and provides a reliable basis and brings great convenience for later repair work.

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38

Lien, Bo Ren, Wei Hsiang Huang, Yih Terng Sheu, Sun Long Lin, and Chih Ming Kao. "Risk-Based Approaches for the Remediation of a UST Site: A Case Study." Applied Mechanics and Materials 496-500 (January 2014): 2959–62. http://dx.doi.org/10.4028/www.scientific.net/amm.496-500.2959.

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Risk-based corrective action (RBCA) is a scientifically-accepted approach to remediate polluted sites. Under the RBCA approach, the risks to human health associated with polluted sites are assessed and appropriate remedial measures are taken to reduce risks. RBCA evaluations involve the use of risk models to assess health risks to different receptors. In Taiwan, the Soil and Groundwater Remediation Act was enforced in 2000. The government of Taiwan also use risk assessment protocols to obtain acceptable remediation goals for polluted sites with low risks. In this study, the application of risk assessment to derive remediation goals and develop remedial strategies at a fuel-oil spill site were performed. After the risk evaluation, the soil and groundwater remediation goals for total petroleum hydrocarbon (TPH), benzene, toluene, ethylbenzene, and xylenes (BTEX) were determined. The remediation levels meet with the requirements for minimum target risk levels (cancer risk = 1×10-6 and hazard quotient = 1). The developed risk-based cleanup goals are calculated based on actual land use and exposure pathways rather than on assumed maximum exposure. After the completion of RBCA process, the remediation cost can be significantly reduced. Based on the risk assessment results, source zone remediation, natural attenuation, and long term monitoring were recommended as the remediation strategies of the studied site to reduce risks to human health. Results from this study provide a streamlined process for future risk assessment work at petroleum-hydrocarbon polluted sites in Taiwan. RBCA is a sound and defensible basis for site closure, and it offers a more logical framework for making site closure decisions.

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39

Shrader-Frechette, Kristin, and Andrew M. Biondo. "Protecting Children from Toxic Waste: Data-Usability Evaluation Can Deter Flawed Cleanup." International Journal of Environmental Research and Public Health 17, no. 2 (January 8, 2020): 424. http://dx.doi.org/10.3390/ijerph17020424.

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Анотація:

Nearly 25 percent of US children live within 2 km of toxic-waste sites, most of which are in urban areas. They face higher rates of cancer than adults, partly because the dominant contaminants at most US hazardous-waste sites include genotoxic carcinogens, like trichloroethylene, that are much more harmful to children. The purpose of this article is to help protect the public, especially children, from these threats and to improve toxics-remediation by beginning to test our hypothesis: If site-remediation assessments fail data-usability evaluation (DUE), they likely compromise later cleanups and public health, especially children’s health. To begin hypothesis-testing, we perform a focused DUE for an unremediated, Pasadena, California toxic site. Our DUE methods are (a) comparing project-specific, remediation-assessment data with the remediation-assessment conceptual site model (CSM), in order to identify data gaps, and (b) using data-gap directionality to assess possible determinate bias (whether reported toxics risks are lower/higher than true values). Our results reveal (1) major CSM data gaps, particularly regarding Pasadena-toxic-site risks to children; (2) determinate bias, namely, risk underestimation; thus (3) likely inadequate remediation. Our discussion shows that if these results are generalizable, requiring routine, independent, DUEs might deter flawed toxic-site assessment/cleanup and resulting health threats, especially to children.

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40

Wei, Wen Xia, Teng Quan, Yan Wang, Hai Jian Wang, and Pei Zhong Li. "Application of Three-Dimensional Interpolation Methods in Contaminated Site Evaluation." Advanced Materials Research 878 (January 2014): 782–90. http://dx.doi.org/10.4028/www.scientific.net/amr.878.782.

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Анотація:

Contaminated sites remediation is one of the hot points in environmental protection fields. Therefore, an important research project is how to expediently determine the bound and level of pollution of contaminated sites. This may help to decide on a timely and accurate rescue plan so as to minimize the costs and to improve the effect of restoration. This is also the basis of contaminated sites remediation acceptance. There are many influencing factors to confirm the remediation areas on contaminated sites. Studies show that three-dimensional interpolation method is effective tool to delimit the pollution scope. Different three-dimensional interpolation methods have different results in contaminate distribution prediction and directly affect the boundary of contamination. This paper selects one specific case with heavy metal lead contamination to study three-dimensional interpolation methods. The three-dimensional stratigraphic model is established for uncertainty analysis and error analysis in the grid through KrigingIDW(Shepard) and nearest neighbor interpolation method. Results show that 40m*40m grids have the highest accuracy of stratigraphic simulation. Nearest neighbor interpolation method is most suitable for stratigraphic model building. Kriging interpolation method is more suitable for constructing three-dimensional pollutant prediction model. On the basis of above, this text established one distribution prediction model of soil lead contamination, and calculated the contaminated earthwork quantity under different remediation goals. Finally, the paper achieved three-dimensional visualization of the site soil contamination. This study can be directly applied to the actual site remediation decision process, and is helpful for the contaminated sites evaluation and restoration in the future.

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41

Palma, Valerio, Federico Accorsi, Alessandro Casasso, Carlo Bianco, Sarah Cutrì, Matteo Robiglio, and Tiziana Tosco. "AdRem: An Integrated Approach for Adaptive Remediation." Sustainability 13, no. 1 (December 22, 2020): 28. http://dx.doi.org/10.3390/su13010028.

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Abandoned industrial sites are generally characterized by soil and subsoil contamination. The paradigm currently employed for their remediation is “tabula rasa”, i.e., remediation of the entire site before its repurpose. However, this method is not economically, socially, or technologically sustainable: it delays the reuse of large areas, often well-connected to infrastructures, whose reuse may prevent further soil consumption. A possible solution to this problem is the application of adaptive reuse principles. This study, conducted at FULL (Future Urban Legacy Lab) in Politecnico di Torino, presents an interdisciplinary approach to spatialize, visualize, and manage interactions between reclamation and urban design for the transformation of contaminated urban areas. The core is based on a decision support parametric toolkit, named AdRem, developed to compare available remediation techniques and schematic urban design solutions. AdRem uses a 3D modeling interface and VPL scripting. Required input data are a geometric description of the site, data on the contamination status, viable remediation techniques, and associated features, and schematic urban design recommendations. A filtering process selects the techniques compatible with the site use foreseen. The output is an optimized remediation and reuse plan that can support an interdisciplinary discussion on possible site regeneration options.

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42

Nordstrom, D. Kirk. "Geochemical modelling for mine site characterization and remediation." E3S Web of Conferences 98 (2019): 05013. http://dx.doi.org/10.1051/e3sconf/20199805013.

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Although substantial advances in geochemical modelling have improved our ability to understand and improve mine site characterization and remediation, the limitations of modelling are often underappreciated. Modelers must have expertise in chemistry, geology, hydrology, geochemistry, and microbiology. Those who use codes must understand inorganic chemistry, thermodynamics, and kinetics for water-rock interactions. They must understand that code output is only useful insofar as they understand the limitations of the database and the built-in assumptions. A brief overview of geochemical code development in this paper reveals strengths and weaknesses in modelling capability. Because early predictions of water quality after mine closure often bear little resemblance to actual conditions, this approach should not be relied upon for permitting. Complex large-scale mine sites are not readily amenable to future predictions of hydrogeochemical conditions through modelling, however, modelling can constrain the possible and probable processes that give rise to specific water compositions. Modelling can also help guide remediation planning to find the most cost-effective alternative. Examples are provided for the Questa, New Mexico natural background study, the Summitville Mine, Colorado, and the Pinal Creek Basin, Arizona acid-contaminated aquifer.

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Clement, William P., Steve Cardimona, Anthony L. Endres, and Katharine Kadinsky‐Cade. "Site characterization at the Groundwater Remediation Field Laboratory." Leading Edge 16, no. 11 (November 1997): 1617–21. http://dx.doi.org/10.1190/1.1437538.

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Pennock, Kelly A., Shawn J. Bohn, and Michael K. White. "Expert software that matches remediation site and strategy." Remediation Journal 2, no. 2 (March 1992): 183–98. http://dx.doi.org/10.1002/rem.3440020209.

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45

Regens, James L., Donald G. Hodges, Patrick L. Wilkey, R. Eric Zimmerman, Anthony Q. Armstrong, Linda Kelley, Timothy A. Hall, and Eugene A. Hughes. "Integrated framework for assessment of site remediation options." Federal Facilities Environmental Journal 10, no. 1 (1999): 81–93. http://dx.doi.org/10.1002/ffej.3330100109.

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46

Robitaille, George E. "Groundbreaking technologies for site characterization and remediation monitoring." Field Analytical Chemistry & Technology 2, no. 2 (1998): 61. http://dx.doi.org/10.1002/(sici)1520-6521(1998)2:2<61::aid-fact1>3.0.co;2-h.

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47

Desnoyers, Yvon, Claire Faucheux, and Nadia Pérot. "Use case 3: post accidental site remediation − CEA." EPJ Nuclear Sciences & Technologies 6 (2020): 13. http://dx.doi.org/10.1051/epjn/2019060.

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Within the H2020 INSIDER project, the main objective of work package 3 (WP3) is to draft a sampling guide for initial nuclear site characterization in constraint environments, before decommissioning, based on a statistical approach. This paper is dedicated to the sampling strategy for use case 3 (UC3) about contaminated soils, in the context of post-incidental remediation of a site. For this use case, the constraint environment comes from the difficulty to collect samples beneath a building on the one hand and the fact that samples were collected in the past with no possibility for additional samples. This task has been initiated by gathering prior knowledge for the contaminated site and analysing the available dataset (historical assessment + available data from non-destructive and destructive analyses).

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48

Parker, Jack, Ungtae Kim, Peter K. Kitanidis, Michael Cardiff, and Xiaoyi Liu. "Stochastic Cost Optimization of Multistrategy DNAPL Site Remediation." Ground Water Monitoring & Remediation 30, no. 3 (April 20, 2010): 65–78. http://dx.doi.org/10.1111/j.1745-6592.2010.01287.x.

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49

Ruff, Cynthia M., David A. Dzombak, and Chris T. Hendrickson. "Owner-Contractor Relationships on Contaminated Site Remediation Projects." Journal of Construction Engineering and Management 122, no. 4 (December 1996): 348–53. http://dx.doi.org/10.1061/(asce)0733-9364(1996)122:4(348).

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50

Showalter, W. Eric, and Daniel W. Halpin. "Dynamic Programming Approach to Optimization of Site Remediation." Journal of Construction Engineering and Management 134, no. 10 (October 2008): 820–27. http://dx.doi.org/10.1061/(asce)0733-9364(2008)134:10(820).

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