Abstracts
IAH_CNC_WEB2
IAH_CNC_WEB2
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Geological and geochemical conditions commonly found in Canada that should be considered<br />
when implementing a bioremediation approach include: low groundwater temperatures,<br />
low permeability matrices and fractured rock. Recent experience implementing<br />
bioremediation remedies under these conditions have provided insights and lessons<br />
learned for optimizing bioremediation of chlorinated solvents in Canada.<br />
Groundwater temperatures defined as cold (i.e., below 10 º C) are commonly found north<br />
of 45 degrees latitude. Understanding the feasibility of bioremediation of chlorinated solvents<br />
and the practical limits of bioremediation under cold conditions is important in<br />
remedy selection and expectation management for high latitude bioremediation projects.<br />
Examples of successful bioremediation at sites in Alaska, Denmark and Canada, will be<br />
presented with a focus on degradation half-lives, concentrations of dechlorinating bacteria<br />
(Dehalococcoides [Dhc]) and remediation outcomes.<br />
Low permeability strata are common in some of the most highly industrialized areas of<br />
Canada; notably in Southern Ontario and Quebec. Originally conceived as an oil and<br />
gas extraction technology, hydraulic fracturing can also be used to improve distribution of<br />
bioremediation amendments thereby improving bioremediation outcomes. Examples of<br />
successful implementation of hydraulic fracturing and other approaches for bioremediation<br />
in clay strata and fractured rock environments will be discussed. One such site, in the<br />
Toronto area, with groundwater concentrations of PCE, TCE and cis-1,2-dichloroethene<br />
(cDCE) above regulatory limits will be presented. A high pressure grout pump was used<br />
to inject EHCTM electron donor and KB-1 ® . After KB-1 ® application, a 10,000-fold<br />
increase in Dhc abundance was observed from pre to post bioaugmentation in less than<br />
one year. cDCE concentrations declined concurrently to below detection limits, reaching<br />
Ontario regulatory standards (Table 3) and site remedial objectives in the target monitoring<br />
wells for all chlorinated compounds within 1.5 years of bioaugmentation.<br />
Groundwater Aspects of Deep Geological<br />
Repositories<br />
Wednesday, October 28, 10:10 – 11:50<br />
Chair: Mark Jensen<br />
Room: Heritage<br />
228 - Deep Geologic Repositories: Developing a Geoscientific<br />
Basis for Long-Term Safety<br />
M.R. Jensen & M. Hobbs<br />
Nuclear Waste Management Organization, Toronto, Ontario, Canada<br />
The Nuclear Waste Management Organization (NWMO) is responsible for implementing<br />
the Adaptive Phased Management (APM) Program, Canada’s approach for the longterm<br />
management of its nuclear used fuel. The APM program, approved by the federal<br />
government in June 2007, envisions that nuclear used fuel would be placed within a<br />
46 IAH-CNC 2015 WATERLOO CONFERENCE