
Soil and Groundwater Contamination Survey and Countermeasure Technologies
| Category of Tchnology | Survey | Soil Gas Survey Method | |
| Media | Soil Gas | ||
| Contaminants |
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| Applied (Demonstrated) Substances | Volatile Chlorinated Organic Compounds | ||
| Scope | Concentration Range | Detective sensibility will be 10 ppbv if 100 ml of soil gas is poured into 1 ml of hexane. | |
| Hydrogeological Conditions |
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| Chemical Soil Properties | |||
| Other Remarks | Contaminants are absorbed by hexane on-site for gas chromatographic analysis. This is a relatively sensitive survey method available for analysis by ordinary research institutions, allowing identification of individual substances. | ||
| Technology Description | Classification | ||
| Status |
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| Outline of Technology | Soil gas is taken by a gas-tight cylinder from the bottom of small holes dug for the purpose, and volatile substances in the gas is absorbed by hexane contained in a mini vial on-site, then to be taken to laboratory for gas chromatographic analysis. Generally, some deciliters of gas is taken and absorbed to some milliliters of hexane, although the volume depends on the concentrations in the gas. | ||
| Required Pre- and Post-treatment | |||
| Enhance Effectiveness through Combination | Linear survey method, to which the soil-gas method is applied, for surveying the plume containing contaminated groundwater and for searching the contaminant source. | ||
| Case History | Work time at the site is mostly used for pouring the gas into hexane. The time can be saved by using a large number of gas sampling devices. The soil gas test surveys in two areas, where the contaminant sources were identified in advance, have proven that it is possible to detect the contaminated gas at spots 22 m to 29 m away from the contaminant source. This method ranks between the gas detection tube method and high sensitivity methods, such as “Mobilabomethod, in terms of the analysis sensitivity. | ||
| Application Examples | This soil-gas survey technology is widely used to locate the contaminant source and to measure the concentrations, ranging from low to high, in areas where the gas is highly contaminated within a plant site, etc. | ||
| Limitations | Fixing the gas contents to hexane is the most time-consuming part of the work. It also takes time to get results of the laboratory analysis of the sampled materials. | ||
| Properties of Treated Soil |
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| Schematic Flow Process |
Sampling of Soil Gas and Absorption of Volatile Components to Hexane |
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| Applicability | In Situ Applicability | Possible | |
| Ground Structures | Applicable even if Ground Structures are Present * | ||
| Required Excavation | Sampling holes should be about 2 cm to 3 cm in diameter and about one meter deep. | ||
| Groundwater Extraction | None | ||
| Required Space | Space for soil gas sampling work. | ||
| Operational Time |
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| Installation Time | On-site work time is comparable to that of the gas detection tube method. Laboratory analysis takes time. | ||
| Maintenance and Control Requirements |
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| Additional Remarks | * Concrete floors must be dug separately by cutters. | ||
| Secondary Impacts to Environment | Secondary Treatment Required? |
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| Effects on Living Environment | |||
| Additives |
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| Possibility of Contaminant Spreading | None | ||
| Secondary By-products |
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Soil Environment Management Division, Water Environment Department, Environmental Management Bureau, Ministry of Environment
Tel: +81-3-5521-8319
E-mail: MOE@env.go.jp