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2024-06-07_PERMIT FILE - M2024026 (23)
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2024-06-07_PERMIT FILE - M2024026 (23)
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Last modified
6/11/2024 7:22:14 AM
Creation date
6/10/2024 10:43:12 AM
Metadata
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Template:
DRMS Permit Index
Permit No
M2024026
IBM Index Class Name
Permit File
Doc Date
6/7/2024
Doc Name Note
Exhibit D - Mining Plan
Doc Name
Application
From
Colorado Sand Company II, LLC
To
DRMS
Email Name
NCG
JLE
EL1
Media Type
D
Archive
No
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Environmental Impacts of Water Treatment Chemicals at Industrial Sand Mines <br /> BARR <br /> fate of PoIyDADMAC in the soil and groundwater beneath them. <br /> PoIyDADMAC cationic coagulants are commonly used <br /> to enhance the performance of the belt press associ Because DADMAC carries no known human health con- <br /> ated with wash plants. This compound is also widely cerns,there is less published data and little risk analysis <br /> used in the United States to treat public drinking water. concerning its fate in the environment. We have not <br /> DAD MAC is a monomer used in the production of the been able to locate sufficient information on DADMAC <br /> cationic polyDADMAC coagulant. A small amount of to derive steady-state concentrations of the compound <br /> residual, unreacted DADMAC monomer remains in the as we were for acrylamide. However, given the evidence <br /> polyDADMAC coagulant when it is added to the process. that it is highly biodegradable, it is assumed that if acryl <br /> The differences between the DADMAC and acrylamide amide degrades rapidly than the same conditions would <br /> monomers and the fate of residual DADMAC monomer result in similar performance from DADMAC monomer. <br /> in the environment are discussed later in this document. analytical methods and <br /> The DADMAC monomer is soluble in water, biodegrad monitoring requirements <br /> There are no practical, EPA-approved laboratory meth- <br /> able under aerobic conditions, and has poor adsorption ods for monitoring of acrylamide or DAD MAC.The EPA, <br /> to minerals and organic matter.1°Because of its solubil through a treatment technology standard, limits the <br /> ity and its inability to adsorb to solids,the water phase amount of anionic polyacrylamide used at water treat- <br /> concentration of the DADMAC monomer in the filtrate ment plants by limiting the amount of the monomer <br /> produced by the belt press will equal the concentration <br /> in flocculants to less than 500 parts per million (ppm) <br /> within the process water that overflows the clarifier and acrylamide, used at a concentration of 1.0 ppm or less. <br /> is recycled in the wash loop. <br /> This gives a de facto safe drinking water limit of 0.5 ug/L. <br /> Like acrylamide, the DADMAC monomer is considered The EPA has established no treatment standards for DAD- <br /> readily biodegradable. The acrylamide monomer has a MAC. NSF 60 has established an allowable concentration <br /> shorter half-life than DADMAC(approximately one day in drinking water of 50 ug/L,or 100 times higher than <br /> vs. 15 days for DADMAC). Neither monomer is consid- the de facto standard for acrylamide. <br /> ered bioacculmative. Both monomers are considered to ALS-Columbia Laboratory in Kelso, Washington, has de- <br /> have low environmental toxicity. veloped a practical, non-EPA-approved analysis method <br /> Because the DADMAC monomer is readily biodegradable for acrylamide. It uses liquid chromatography tandem <br /> in water, it will achieve a steady-state concentration in mass spectrometry (LC-MS/MS)technology and has a <br /> the clarifier/sand wash loop. Due to its higher monomer minimum detection limit at or below the EPA's limit of <br /> concentration and longer half-life, it is expected to have 0.5/ug/L. <br /> a higher steady state concentration than acrylamide. It ATSDR study <br /> is important to note that there are no published recom- In 2008,The U.S. Department of Health and Human <br /> mended or regulatory standard for DAD MAC. Given the Services' Agency for Toxic Substances and Disease Reg- <br /> relatively small volume of polyDADMAC used at most istry(ATSDR) published a Health Consultation regarding <br /> facilities(in comparison to polyacrylamide) and the potential environmental exposures to acylamide from <br /> relatively small concentration of DADMAC monomer,the the on-site disposal of sand fine sludge and wash water <br /> expected steady-state concentration is expected to be from the Belvidere Sand &Gravel (BS&G) site in Warren <br /> relatively low (less than 1mg/L). County, New Jersey. BS&G uses a polyacrylamide floc- <br /> Since DADMAC readily breaks down in soil and water, culant in their closed loop aggregate washing process, <br /> biodegradation should occur in the sand piles as well as similar to those used by the Industrial Sand industry. <br /> 10 EPA.2004.Test Plan for DADMAC.http://www.epa. Petitioners expressed concern about potential con- <br /> gov/hpv/pubs/summaries/dialdime/c15208t12.pdf tamination of potable wells by acrylamide and resulting <br /> Page 5 <br />
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