Marjol Battery Site
Spring site maintenance activities to begin end of week of April 29, 2013.
 
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Site Background

Summary of Corrective Measures Implementation (CMI) Process

Post-Construction  Maintenance and Monitoring

Construction  Information (May 2008 to August 2010)

Final (100%) Remedial Design

Air Monitoring

Stormwater Management System

Photo Gallery

Quarterly Progress Reports - CMI Completion Report - Biennial Report 

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Frequently Asked Questions (FAQs)
Q What is the Final Remedy for the Site?
A The Final Remedy is a containment remedy which means that the contaminated materials will remain on the site in a central location under a specially designed cap. The containment area will be maintained so that the cap continues to be effective at containing the lead-contaminated materials safely. More information on the selected remedy can be found at Final Decision and Response to Comments on Selection of Corrective Measure.
 
 

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Q How long will the remedy take?
A

Implementation of the final remedy (construction activities) began on May 12, 2008.  On August 27, 2010, punch list items required for “Substantial Completion” of the project were completed.  The “Final Inspection” (required in the 100 % Design Plan) took place on Tuesday, August 31, 2010. 
 

 

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Q What about lead blowing from the site?
A The design plans call for precautions to control the amount of dust in the air during the final remedy.   Understandably, no one (including and perhaps, especially Gould) wants to have any recontamination in the off-site area as a result of implementation of the Final Remedy.  Off-site verification sampling was performed the week of November 16, 2009. This sampling program was designed to confirm that remedial activities did not cause off-site contamination.  As per the USEPA/PADEP approved Final (100%) Remedial Design Plan, analytical results from the post-remediation sampling event were compared to the results from the pre-remediation sampling event to see if there was a statistically significant increase of more than 100 mg/kg between the pre-construction and post-construction sample results. For all five properties, the comparison showed that soil lead concentrations before and after construction were essentially the same with the largest change in mean soil lead concentration being less than 20 mg/kg. Statistically, there was not an increase in soil lead of more than 100 mg/kg at a 95% confidence level. This means that there is less than a 5% chance that there actually was an increase of more than 100 mg/kg when the sample results indicate that there was not. Therefore, as per the Final (100%) Design Plan, no additional off-site sampling is required. A report on the Off-Site Verification Sampling was submitted to USEPA and PADEP on February 15, 2010, as part of Quarterly Report #14. (Click here to review the text from the Off-Site Verification Sampling Report.)  The full report may be viewed at the Marjol Community Relations Office at 502 George Street in Throop, PA or at the repository in the Throop Borough Building, located at 436 Sanderson Street in Throop, PA. 

 

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Q What does the ambient air data mean?
A One way lead in air is measured is by using high-volume air samplers that run every six days for a 24-hour period. The site was monitored this way from 1989 until December 2010.  The sampler draws in air across a filter that collects the dust. This filter is sent to the lab and the amount of lead in the dust is measured. The results are in micrograms (1/1,000,000th of a gram) of lead per cubic meter of air. For comparison, a speck of dust weighs about 10 micrograms, and the average person breathes a cubic meter of air in about 2 hours. The typical results for lead in air in Throop are in fractions of micrograms per cubic meter, equivalent to breathing a dust particle every 3.4 months.

There were four high volume air samplers located at the site, one sampler at the Mid-Valley Secondary Center on Underwood Road in Throop, and one sampler located across the river in Dickson City. The predominant wind direction at the site is from the west and northwest. One sampler at the site was located in the predominant upwind direction (HV-4), and the other three samplers at the Site were located in the predominant downwind direction (HV-1, HV-2, and HV-3). The Dickson City air monitor provided background air data. Click here to review the December 9, 2010, 24-hour ambient air lead data.  (Click here to review additional information on air monitoring during construction activities.)
 
 

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Q Where can I get information about the Site or about the clean up?
A There are many ways you can obtain information. This web site is hosted by Gould, owner of the Marjol Site. If you would like to contact Gould’s Community Relations Representative, Lisa Ayers, you may do so by e-mail at layers@advancedgeoservices.com  or by telephone 570.383.9313.  You may also contact the EPA or PADEP project managers for the Marjol Site. For their information, click here.
 
 

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Q What is considered “background lead” in yards for this area?
A Lead is found naturally in soil; therefore, there will always be some lead in the soil in our yards. “Background” is a level that varies based on many things, such as the area you live in, the age of the houses, and proximity to roadways. “Background” for the Throop area would be in the range of 300 to 350 ppm. This is what would be expected for an average soil lead level for a yard with an older home with the samples being taken outside of the drip zone (the area closest to the house). It will be less for the properties that had soil removed in 1988 to 1992 since the replacement soils had lead concentrations below 50 ppm.
 
 

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Q What impact has Marjol had on the groundwater at the site?
A In the vicinity of the Marjol site, groundwater is found in a mine pool, about 200 feet below the ground surface.  During the Mine Subsidence Investigation in 1998, samples from the Mine Pool were collected and tested for lead.  Both the total and dissolved lead concentrations in groundwater samples from four of the five sample locations were below the laboratory detection limit of 0,8 µg/l.  The total lead sample result for the fifth sample location was 0.99 µg/l, which is well below the USEPA Action Level for Lead of 15 µg/l; the dissolved lead result for this fifth sample location was below the detection limit.  These results show that lead from the Site is not dissolving and migrating downward at measurable levels.  There is no groundwater remediation required under the Final Decision.
 

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If your question is not listed on this page, please contact us so we can get an answer for you. 

Page Last Modified Sunday July 29, 2012 09:05:59 PM

 

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