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France – Greece – Austria – Poland - HPC AG

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Laboratory test to<br />

improve microbiological<br />

contaminant<br />

degradation<br />

Result of the electric resistance tomography<br />

hydrocarbons and chrome VI was determined.<br />

Due to the historical background<br />

however the result could have been forecast.<br />

Two contamination sources were determined.<br />

In the course of time, the network<br />

of monitoring wells was expanded<br />

and today there exist about 20 groundwater<br />

monitoring wells with construction<br />

depths between 40 m and 120 m in order<br />

to contain VOCs which possess a tendency<br />

to descent through the aquifer due to<br />

their higher density than water. The<br />

groundwater aquifer extends to depths of<br />

300 - 500 m over several occasionally<br />

highly fissured limestone formations.<br />

A crucial factor for the distribution of the<br />

contaminants dissolved in groundwater is<br />

the existence of two deep wells on site<br />

serving for the recovery of groundwater<br />

for cooling processes. Until 2006, about<br />

300,000 m 3 of groundwater were recovered<br />

per year. The pumping cone produced<br />

helped to fix the contaminant plume<br />

more or less on the site. However, contaminant<br />

concentrations in groundwater<br />

could not be significantly decreased.<br />

By reducing by 80 % the pumped water<br />

quantities collected to about 55,000 m 3 per<br />

year, i.e. from averagely 35 m 3 /h to 7 m 3 /h,<br />

the situation slowly began to change and<br />

concentrations in the area of the contaminant<br />

plume increased in the central areas<br />

of the contamination centers, but the<br />

contaminant plume extended only slightly<br />

because of fracture and Karstzones.<br />

The first phase of the investigation program<br />

recommended by <strong>HPC</strong> Envirotec<br />

included a Toxicological Exposure Risk<br />

Quantification (TERQ), as already implemented<br />

by us since several years as standardized<br />

service for human-toxicological<br />

12 www.hpc.ag <strong>HPC</strong>, September 2009<br />

<strong>HPC</strong> Envirotec <strong>France</strong><br />

risk evaluation of environmental contamination<br />

(contaminated sites, etc.). It was<br />

important to obtain a realistic evaluation<br />

of the health risks as impact from the<br />

groundwater contamination to the staff<br />

employed on site and for residents located<br />

in the downgradient area of the site.<br />

Considering the multi-substance aspect<br />

(existing „contaminant cocktail“), acceptable<br />

concentrations for tolerable risks for<br />

human health could be determined for<br />

various, existing and potential exposition<br />

scenarios for the site and its downgradient<br />

area. An additional advantage of TERQ was<br />

that the remediation targets could be<br />

Contaminant plume in limestone aquifer<br />

determined according to the specific site<br />

use, allowing maximum legal and financial<br />

safety for operator, user and authorities.<br />

This approach allows optimum management<br />

of remediation costs with simultaneous<br />

exclusion of non-acceptable, toxic<br />

long-term risks.<br />

The transparency delivered for the health<br />

risks posed by the site (in this case restricted<br />

to the site) enabled us to elaborate a<br />

detailed investigation program in cooperation<br />

with competent authorities and site<br />

operator in order to better evaluate processes<br />

occurring in subsoil and to find alternatives<br />

for the traditional pump & treat<br />

remediation (option considered by the<br />

authorities), which was applied as standard<br />

procedure during the 1980/90ies.<br />

This procedure, however, was in many<br />

cases disappointing (mainly for VOC contamination<br />

by chlorinated solvents) both<br />

from an economic point-of-view and as far<br />

as efficiency was concerned.<br />

Our experience of the last years with innovative<br />

ENA methods has proven that<br />

there exist alternatives to pump & treat.<br />

In October 2008 <strong>HPC</strong> Envirotec started to<br />

implement a feasibility study for the application<br />

of dynamized natural bioattenuation<br />

(DNBA study) or enhanced natural<br />

attenuation (ENA).<br />

The task schedule elaborated by<br />

<strong>HPC</strong> Envirotec comprised the<br />

following Methodology:<br />

1. Site investigations to obtain exact<br />

knowledge of the geological, tectonic<br />

and hydrogeological situation in the<br />

limestone aquifer. Prior to the start of<br />

investigations, diametrically opposed<br />

groundwater flow directions had been<br />

assumed as well as the existence of<br />

underground rivers with jointing and<br />

karstification.<br />

2. TERQ (= QHRA)<br />

3. In-situ and laboratory testing in the<br />

course of the Natural Bio-Attenuation<br />

feasibility study in order to determine<br />

the potential application of various<br />

methods for dechlorination of the<br />

VOC (TCE, PCE, etc.) plume and to<br />

convert chrome VI to inoffensive, precipitable<br />

chrome III.<br />

4. Implementation of in-situ pilot tests<br />

with the two most efficient treatment<br />

methods of pre-testing.<br />

In detail, implementation of the four<br />

investigation phases was ensured as<br />

follows: The first in-situ investigation<br />

included implementation of traditional<br />

gamma-ray logs in all boreholes. The<br />

results were correlated with the first<br />

existing boring profiles and indicated that<br />

a tectonic disturbance ran diagonally<br />

across the entire site. The horizontal<br />

stowage amounts to about 20 m. Now it<br />

was possible to interpret more precisely<br />

the slightly irritating map of the groundwater<br />

flow situation dominating the site<br />

and its surroundings.<br />

Understanding by combining. Acting by<br />

purpose.<br />

continued on page 15 ...

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