Difference between revisions of "Transport parameters and contaminant data"

From Limestone
Jump to: navigation, search
m (Contaminant data)
m
Line 14: Line 14:
 
Important transport parameters that influence the migration of a substance are
 
Important transport parameters that influence the migration of a substance are
 
* diffusion coefficient of the substance in the limestone (often estimated as molecular diffusion coefficient times the tortuosity or porosity of the limestone)
 
* diffusion coefficient of the substance in the limestone (often estimated as molecular diffusion coefficient times the tortuosity or porosity of the limestone)
* dispersivities
+
* dispersivities (may be less important, if fracture flow dominates)
* sorption coefficient
+
* sorption coefficient (organic carbon is usually low in limestone)
 
* limestone porosity
 
* limestone porosity
* degradation rate
+
* degradation rates
  
 
'''Tracer tests''' are very useful to analyze the transport behavior in a limestone aquifer.
 
'''Tracer tests''' are very useful to analyze the transport behavior in a limestone aquifer.
Line 30: Line 30:
  
 
Furthermore, measurements from core material can be used to determine the porosity and hydraulic conductivity of a limestone sample, for example using gas permeameter and porosimeter (Poroperm test).
 
Furthermore, measurements from core material can be used to determine the porosity and hydraulic conductivity of a limestone sample, for example using gas permeameter and porosimeter (Poroperm test).
 +
At the Akacievej site, this yielded porosity values between 7 adn 46 %, with a strong variation with depth.
 +
The determined hydraulic conductivity values were correlated to the porosity (and limestone hardness) and were in the range of between 5x10-11 and 10-6 m/s, see
 +
<ref name="Broholm2016"> Broholm et al. (2016), ''Sammenligning af niveauspecifikke prøvetagningsmetoder for vurdering af knocentrationsfordeling i kalkmagasin: Akacievej, Hedehusene.'' Technical University of Denmark, DTU Environment.</ref>
  
 
== Contaminant data ==
 
== Contaminant data ==

Revision as of 22:00, 5 February 2018

Highlights
  • Determination of transport parameters
  • Contaminant sampling techniques

Transport parameters

Advective transport happens due to the groundwater flow. However, to describe the transport of a substance in a fractured limestone aquifer properly, additional parameters are required. Important transport parameters that influence the migration of a substance are

  • diffusion coefficient of the substance in the limestone (often estimated as molecular diffusion coefficient times the tortuosity or porosity of the limestone)
  • dispersivities (may be less important, if fracture flow dominates)
  • sorption coefficient (organic carbon is usually low in limestone)
  • limestone porosity
  • degradation rates

Tracer tests are very useful to analyze the transport behavior in a limestone aquifer. Different types of tracer tests can be distinguished:

  • push-pull tracer tests, where a tracer is injected and monitored in the same borehole
  • tracer tests with an injection well and one or several observation wells
  • forced-gradient (with pumping) or natural gradient tracer tests

In the limestone project, a forced-gradient tracer test with several injection wells and a central pumping well for tracer monitoring was conducted. Details are described in the following report:

Furthermore, measurements from core material can be used to determine the porosity and hydraulic conductivity of a limestone sample, for example using gas permeameter and porosimeter (Poroperm test). At the Akacievej site, this yielded porosity values between 7 adn 46 %, with a strong variation with depth. The determined hydraulic conductivity values were correlated to the porosity (and limestone hardness) and were in the range of between 5x10-11 and 10-6 m/s, see [1]

Contaminant data

Fig.1: Extraction of samples from a borehole core for the lab analysis of PCE and TCE.

Different sampling and monitoring techniques to determine the depth-discrete contaminant distribution in boreholes have been developed. Depth-discrete sampling is important, since due to a very heterogeneous nature of the aquifer, the concentration can vary strongly over depth. For the planning of a site remediation it is important to know the vertical extent and the location of the contamination, so the remediation system can be planned most effectively.

One way to obtain depth-discrete concentrations is to analyze small samples from borehole cores for the sorbed contaminant concentration. An example is shown in Figure 1. However, limestone has a very varying hardness and may be unstable. Soft limestone material is often lost when taking a borehole core. As a consequence, the core analysis is difficult and may lead to wrong results.

The following list gives an overview of some other useful sampling methods in wells in limestone aquifers:

  • Snap samplers
  • Diffusion cells
  • Bladder pump
  • Separation pumping with a heat pulse probe

The following ones require open (unscreened) boreholes:

  • NAPL-FLUTe (detection of DNAPL)
  • FACT-FLUTe (dissolved concentrations) [2]
  • Passive flux meters for fractured aquifers
  • etc.

The following report gives a comparison of some of these sampling methods.


Return to Content

  1. Broholm et al. (2016), Sammenligning af niveauspecifikke prøvetagningsmetoder for vurdering af knocentrationsfordeling i kalkmagasin: Akacievej, Hedehusene. Technical University of Denmark, DTU Environment.
  2. Broholm et al. (2016), Characterization of chlorinated solvent contamination in limestone using innovative FLUTe technologies in combination with other methods in a line of evidence approach, Journal of Contaminant Hydrogeology