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2019-05-24_PERMIT FILE - M2019027 (2)
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2019-05-24_PERMIT FILE - M2019027 (2)
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Last modified
1/5/2025 6:38:51 AM
Creation date
5/28/2019 9:34:10 AM
Metadata
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Template:
DRMS Permit Index
Permit No
M2019027
IBM Index Class Name
PERMIT FILE
Doc Date
5/24/2019
Doc Name
Application
From
Colorado Sand Company
To
DRMS
Email Name
PSH
MAC
Media Type
D
Archive
No
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Environmental Impacts of Water Treatment Chemicals at Industrial Sand Mines C-39 <br /> BARR <br /> This compound has been safely used for decades in the is classified by the U.S. Environmental Protection Agency <br /> United States to treat public drinking water. Polyacryl- (EPA) as a B2, a probable human carcinogen.'There are <br /> amide also is widely used in a variety of industries and no negative health effects associated with the actual <br /> can be found at food processing facilities, used as blast- polyacrylamide flocculant itself; only the acrylamide <br /> ing agents, used for drilling mud and grout products, and monomer <br /> used as a soil-stabilization agent. <br /> Because of this classification and its common use as a <br /> Acrylamide is a monomer used in the production of the settling agent, or flocculant, at municipal drinking water <br /> anionic polyacrylamide flocculant. It is not a breakdown treatment plants,the EPA has established a National <br /> or daughter product of polyacrylamide. A small amount Primary Drinking Water Regulation (NPDWR)for acryl- <br /> of residual, unreacted acrylamide monomer remains in amide. This NPDWR established the de facto limit of <br /> the polyacrylamide flocculant as an impurity when it is 0.5 micrograms per liter(ug/L)for acrylamide through a <br /> added to the wash process. treatment technology standard.This standard is based <br /> PolyDADMAC cationic coagulants are commonly used to on a maximum concentration of acrylamide monomer in <br /> enhance the performance of the belt press associated commercial polyacrylamide flocculant (500 ppm) and a <br /> with wash plants. This compound is also widely used in maximum dosing concentration of flocculants (1.0 ppm) <br /> the United States to treat public drinking water. DADMAC directly to potable water. While the EPA has approved <br /> is a monomer used in the production of the cationic laboratory methods for acrylamide, Barr has found no <br /> polyDADMAC coagulant. laboratory able and willing to perform the procedure <br /> on process wastewater. Barr has identified at least one <br /> These products serve a significant benefit to the op- laboratory that can measure acrylamide monomer con- <br /> eration of a mine site because they reduce the overall centrations near these low concentrations (less than 1 <br /> footprint of the mine,which would otherwise require ug/L) using a non-EPA approved method. <br /> extensive settling basins. In some cases, these settling <br /> b This paper addresses uses typical of polyacrylamide at <br /> basins can result in additional costs related to water <br /> management and berm construction. mine sites and related processing facilities. However, it <br /> is appropriate to note that polyacrylamide can be highly <br /> Both of these compounds are readily biodegradable and toxic to aquatic life if discharged directly into surface wa- <br /> monitoring at frac sand mines in the Midwest indicate ter habitats. Although this type of discharge is not typi- <br /> that there is no evidence of groundwater contamina- cal of the mine site processing, any potential discharge <br /> lion associated with either of these compounds.This involving unreacted polyacrylamide entering surface <br /> paper provides additional background on each of these water should be avoided. <br /> chemicals and a detailed analysis of the fate of these <br /> compounds using a kinetic model that includes biodegra- Unlike the acrylamide monomer, the DADMAC monomer <br /> dation and other chemical processes. has not been linked to adverse health effects. DADMAC <br /> has no NPDWR and no secondary standards, nor has it <br /> regulatory background been designated by the EPA as a Contaminate of Concern <br /> Although no adverse human health effects are associ- in CCL1 (Contaminate of Concern List 1), CCL2 or CCL3.' <br /> ated with the polyacrylamide polymer, adverse human Furthermore,there are no EPA or MPCA surface water <br /> health effects have been linked to an impurity called standards for DADMAC, nor has the Minnesota Depart- <br /> acrylamide, which is a monomer, or part of the poly- ment of Health or the Wisconsin Department of Natu- <br /> acrylamide molecule used in the production of the ral Resources established health-risk limits.The water <br /> anionic polyacrylamide flocculant. A very small amount <br /> of the monomer molecule is present in the raw chemical <br /> feedstock that remains unreacted in the polyacrylamidewww.epa.gov/chemfact/s—acryla.txt <br /> flocculant when it is mixed in the wash process used in <br /> the mine's wet plant. 2 EPA. 2012.Basic Information on CCL and Regulatory <br /> Determinations. http://water.epa.gov/scitech/drinkingwater/ <br /> It is this acrylamide monomer(not polyacrylamide) that dws/ccl/basicinformation.cfm <br /> Page 2 © Barr Engineering Co.2013 <br /> Keenesburg Project—Limited Impact 110 Application_May 24,2019 <br />
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