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Polluted groundwater is one the most prevalent environmental
liabilities rendering water and even soil located on-site
unfit for use. Many contaminants gradually rise up through
the soil from highly concentrated areas deep in the ground
to areas of much lower or zero concentration closer to surface.
This upward diffusion is particularly harmful when it manages
to contaminate buildings on the surface. Another harmful and
costly danger is the tendency of contaminant to migrate off-site
where they contaminate neighboring properties and groundwater.
Industry’s conventional approach to contaminated groundwater
remediation has been to pump the contaminated water located
deep below the surfaces to above ground treatment facilities.
This procedure, referred to as “pump and treat,”
requires years, and sometimes even decades or centuries depending
on the level of contamination and the volume of contaminated
groundwater.
Sorption, the tendency of contaminants to stick to particles
in the soil, retards the remediation process. Pumps do not
extricate contaminants that have stuck to or “sorbed”
to the soil. The pumps are only able to remove contaminants
that the groundwater has dissolved. Once treated in above
ground facility, the clean groundwater returns to the soil
and dissolves some of the sorbed contaminants, but not all
of them. The pump then brings the re-contaminated water to
the surface, treats it, and sends it back to dissolve more
contaminants. The cycle then repeats itself. For this reason,
the pump and treat process is long, expensive, and inefficient.
In recent years, the groundwater remediation industry has
begun to employ ozone as an oxidizing agent with substantial
success. Instead of pumping the contaminants to the above
ground treatment facility, pumps send the ozone to the contaminated
groundwater and sub-surface soil, where it oxidizes organics
by direct oxidation or the generation of free radicals. Sending
the ozone to the contaminated soil allows for the oxidation
of dissolved contaminants as well as those contaminants that
have sorbed to the soil, and is, hence, much more effective
and fast. The oxidation of organic contaminants yields carbon
dioxide and water, or other less toxic organics, which are
later oxidized again, yielding carbon dioxide and water. Other
advantages include:
- Ozone’s ability to move through soil.
- Ozone will not discriminate between sorbed and
dissolved contaminants – it oxidizes them both.
- Ozone is over ten times more soluble in water
than oxygen.
- Oxygenation of the soil
- Ozone is generated on site.
Ozone has successfully treated the following common groundwater
contaminants:
- MTBE
- BTEX
- Aliphatic Hydrocarbons
- Diesel Fuels
- Chlorinated Solvents
- Pesticides
- VOC’s
- And many more
Useful Links
In Situ Chemical Oxidation: An Innovative Groundwater Remediation Technology
National Small Flows Clearinghouse: Ozone Fact Sheet (PDF )
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