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2014-104A
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2014-104A
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Last modified
4/23/2018 1:20:08 PM
Creation date
1/5/2017 1:53:26 PM
Metadata
Fields
Template:
Official Documents
Official Document Type
Contract
Approved Date
08/19/2014
Control Number
2014-104A
Agenda Item Number
8.Z.
Entity Name
Langham Consulting Services
Subject
Automatic Meter Reading
Advanced Metering Infrastructure
AMI Consulting Services Contract
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Brownfields Site Assessment <br />June 2014 <br />South Gifford Road Landfill, Vero Beach, Florida <br />4.3 Landfill Cover Evaluation Results <br />Typical soil cover required for redevelopment of a landfill, such as Gifford Road Landfill, is two <br />ft; however, alternative cover systems have been approved by FDEP (e.g., a geonet or geotextile <br />overlain by one ft of cover soil). Approximate landfill cover thickness observed in the <br />assessment area is presented on Figure 6. Data collected during the 2008 test pit excavation <br />activities were used to supplement the data collected from TP -101 through TP -110. Two ft of <br />landfill cover was observed at all but three test pit locations (TP -101, TP -102, and TP -103). In <br />addition, less than two ft of landfill cover was observed at soil boring locations between TP -106 <br />and TP -107 and near TP -102. Selected photographs from the cover thickness evaluation <br />fieldwork are included in Appendix E. Improvements to the existing cap can easily be <br />completed during grading operations when construction is underway for site development. The <br />design of the final cover system for the landfill will need to be approved by FDEP prior to <br />construction. <br />4.4 Soil Gas Results <br />Field screening results from the soil gas probes are presented on Figure 7. The results indicated <br />that methane, which is found in LFG, is present in soil gas in the subsurface within the <br />assessment area. <br />LFG is created when organic materials decompose under anaerobic conditions. LFG is typically <br />composed of methane (50 to 55%), carbon dioxide (45 to 50%), and trace amounts of other gases <br />(e.g., oxygen, nitrogen, and hydrogen sulfide). Field screening results were found to generally <br />be within the typical ranges for landfills, with observed carbon dioxide concentrations being <br />slightly less and methane being slightly higher. In addition to waste decomposition, naturally - <br />occurring organic material in the subsurface and natural attenuation of VOCs present in <br />groundwater at the Site (through ongoing bioremediation activities) may also contribute to <br />methane soil gas concentrations. <br />PID measurements ranged from non -detect in LFG06 to 18.5 parts per million (ppm) in LFG04. <br />Soil gas samples were collected from LFGO1, LFG04, and LFG06 on 11 April 2014. The soil <br />gas results are tabulated in Table 2. Soil gas results were compared to Default Concentrations <br />for LFG Constituents found in Table 2.4-1 of the 1998 USEPA AP 42, Fifth Edition, <br />Compilation of Air Pollutant Emission Factors, Volume 1: Stationary Point and Area Sources. <br />Of the 67 constituents analyzed, 33 were detected in one or more soil gas probes. None were <br />above the USEPA default concentrations, suggesting that the soil gas concentrations measured as <br />part of this effort are indicative of conditions at typical closed/former landfills. There are <br />currently no state regulatory drivers in Florida to evaluate the chemical composition of soil gas; <br />however, any construction projects should consider potential impacts from combustible gas. <br />FR0766H 10 7/8/2014 <br />
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