MGP Site Closure


The EPRI Nationwide Background PAH Progrma Results - Just the Beginning
Andrew Jay Coleman, Ph.D., Electric Power Research Institute, Palo Alto, CA 

David Mauro, Meta Environmental, Inc., Watertown, MA 

MGP Sediment Management Concerns and Approaches - Observations/Considerations
Raymond D. D'Hollander, PE, ENSR International, Syracuse, NY

Designing and Implementing Perimeter Air Monitoring Programs for MGP Site Remediations
Leo Gendron, ENSR International, Westford, MA
Anthony Sacco, ENSR International, Westford, MA
Ishrat Chaudhuri,
ENSR International, Westford, MA

Risk Based Action Levels for Perimeter Monitoring Programs at MGP Sites
Lisa J.N. Bradley, PhD, DABT, ENSR International, Westford, MA   
Kelly Sullivan, ENSR International, Westford, MA  

Application of State-of-the-Art technology to Contain wastes at a Former Manufactured Gas Plant
Joseph Campisi, ENSR International,  E. Syracuse, NY

Comparison of MGP Regulatory and Enforcement Programs, Northeastern United States
Scott T. Saroff, CPG., ENSR International, Syracuse, NY

MGP Property Real Estate Redevelopment Perspectives
To Be Announced  -  Leading Property Developer Invited

 

The EPRI Nationwide Background PAH Program Results – Just the Beginning

Andrew Jay Coleman, Ph.D., Electric Power Research Institute, 3412 Hillview Avenue, Palo Alto, CA 94304, Tel: 650-855-2249, Fax: 650-855-1069
David Mauro
, Meta Environmental, Inc., 49 Clarendon Ave, Watertown, MA  02472, Tel: 617-923-4662, Fax: 617-923-4610

Polycyclic aromatic hydrocarbons (PAHs) are pandemic in the environment from a number of natural and anthropogenic sources.  Electric Power Research Institute (EPRI) has started national program to collect background PAHs throughout the United States. EPRI has recently completed studies in the States of Illinois and New York, which show that concentrations of PAHs are higher than previously suspected in background samples. Several studies in the U.S. and Europe have indicated that the concentrations of PAHs in urban surface soils can range from the low parts per billion to hundreds of parts per million (EPRI, 2000) depending on the proximity to and contribution from PAH sources.  Literature references concerning the presence of PAHs in environmental media, including surface soils show that there is a lack of consistent data on distributions and concentrations of PAHs in surface soils because of varying sampling and analytical methodologies. EPRI conducted a consistent nationwide assessment of PAHs in urban surface soil from hundreds of sites using a random sampling scheme.  Samples have been collected from two depths, 0 - 2.54 cm and 2.54 – 15.2 cm, and analyzed for 40 PAHs and alkylated PAH groups by gas chromatography with mass spectrometry (GC/MS).  Resulting data is being used to better understand how these concentrations compare to concentrations found in the soils from industrial facilities of interest, including former manufactured gas plants.  The findings from both Illinois and New York were useful for gaining insight into the concentrations that can be expected in urban areas.  The EPA residential risk-based-concentration (RBC) was exceeded for at least one PAH at every site sampled.  In addition, there was no apparent difference in concentrations with depth and the concentrations of PAHs found had a lognormal distribution.  

MGP Sediment Management Concerns and Approaches – Observations and Considerations 

Raymond D. D’Hollander, P.E., ENSR International, 6601 Kirkville Road, East Syracuse, NY 13057 Tel: 315-432-0506, Fax: 315-437-0509, Email: rdhollander@ensr.com

This presentation will focus on some of the practical considerations that need to be addressed in sediment remediation at MGP sites.  In particular, the impacts of non-aqueous phase liquids (NAPLs) that may be present will be discussed.  The significance of hydraulic gradients, both natural and remediation induced, on remediation methods will be presented.

The influence of vertical hydraulic gradients has been underappreciated as a mechanism for redistributing PAHs.  Tidal and other mechanisms that cause rapid lowering of the water surface cause significant upward gradients that disperse NAPLs through the sediments.  The upward gradients can also bring NAPLs directly to the sediment surface and water column.  These mechanisms are critical in designing capping and containment remedies.

Removal remedies often use “dry excavation” techniques.  These removal actions often put significant hydraulic stresses on the sediment system.  These hydraulic conditions are often ignored during the remedial design causing delays and additional expenditures in the removal action.  Measures to reduce these impacts are discussed.

Various remedial approaches to sediments impacted by coal tar and other MGP related constituents will be presented.

Designing and Implementing Perimeter Air Monitoring Programs for MGP Site Remediations

Leo J. Gendron, Anthony Sacco, and Ishrat Chaudhuri, ENSR International, 2 Technology Park Drive, Westford, MA  01886, Tel: 978-589-3000, Fax: 978-589-3100

ENSR International has been designing, installing and operating perimeter/fenceline ambient air quality and meteorological programs for over 30 years.  ENSR’s more recent experience includes numerous perimeter and fenceline monitoring programs around hazardous waste sites, landfill excavation projects and MGP site remediation projects.  The paper focuses on and presents general guidance on the development and implementation of perimeter air monitoring programs for MGP site remediation projects.  Topics include: site-specific perimeter monitoring and data quality objectives; parameters to be measured; determination of action levels for the various parameters; types of instrumentation available; number and placement of fenceline monitoring locations; frequency of sampling; data telemetry and reporting alternatives; routine field operations and equipment QC protocols; perimeter monitoring program conceptual design and regulatory review; and monitoring plan generation.

Risk-Based Action Levels for Perimeter Monitoring Programs at MGP Sites

Lisa J.N. Bradley, Ph.D., DABT, ENSR International, 2 Technology Park Drive, Westford, MA 01886, Tel: 978-589-3059, Fax: 978-589-3282
Kelly Sullivan, ENSR International, 2 Technology Park Drive, Westford, MA 01886, Tel: 978-589-3061, Fax: 978-589-3282

ENSR International. Fenceline air monitoring programs increasingly are required at MGP remediation sites.  Risk-based action levels (RBAL) for the fenceline monitoring program should adequately address both project needs and the protection of human health.  Issues to be considered and addressed in the development of risk-based action levels include the following.  1)  Receptors.  Off-site receptors should be identified, and appropriate receptors should serve as the basis for the fenceline air standard.  2)  Timeframe of remediation.  RBALs for a fenceline program should be developed within the context of potential human exposure periods.  In toxicology, appropriate exposure periods to consider are:  Acute – less than 24 hours up to 3 months; Subchronic – 3 months up to 7 years; and Chronic – greater than 7 years.  RBALs should be developed to address each of these exposure durations, depending on the intended length of the remediation.  Potential noncarcinogenic health effects should be considered for each exposure duration, however, chronic exposure durations are generally not anticipated for a remediation project.  Potential carcinogenic effects are most appropriately considered for the chronic exposure duration, however, they can also be considered for the subchronic exposure duration.  3)  Toxicity values.  Appropriate chemical-specific toxicity values from the USEPA should be employed in the RBAL calculations.  This includes the use of subchronic toxicity values.  For benzene, the range of toxicity values provided by USEPA for addressing the potential carcinogenic effects at a given target risk level should be used in developing the RBALs; ideally a range of standards should be developed for benzene where any air monitoring data within that range would be considered to have not exceeded the RBAL.  4)  Point of Exposure.  Where potential receptors are not at the fenceline, air modeling should be used to calculate an RBAL to be protective of the receptors at the point of exposure.  

Application of State-of-the-Art technology to Contain wastes at a Former Manufactured Gas Plant

Joseph Campisi, ENSR International, 6601 Kirkville Road, E. Syracuse, NY 13078

Today, hazardous waste containment systems play a very important role in our efforts to clean up soil and groundwater pollution.  With thousands of former manufactured gas plants (MGPs) undergoing investigation and remediation, containment is becoming a preferred alternative at many of these sites.  This choice is preferred due to the persistence of many of the MGP-derived containments, the difficulty in effecting significant mass reduction in soil and groundwater, and the significant expense associated with more aggressive methods of clean-up.  This case study examines the application of a state-of-the-art technology to one of the components of a containment system.  Specifically, this case study elaborates on the barrier wall selection process and presents the results of a treatability study on the sealant material.  The steel sheet pile wall with synthetic water-stop was installed in the fall of 1994 at a former MGP site in Central Wisconsin.  More recent performance data has been assessed to evaluate the long term effectiveness of this containment approach.

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