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    Gowanus Canal Superfund Site. VII: Rapid Verification of Organoclay–Sand Capping Blends

    Source: Journal of Hazardous, Toxic, and Radioactive Waste:;2024:;Volume ( 028 ):;issue: 004::page 04024019-1
    Author:
    Alyssa B. Lampi
    ,
    Dennis G. Grubb
    ,
    Nasser Hamdan
    ,
    Dusty R. V. Berggren
    DOI: 10.1061/JHTRBP.HZENG-1375
    Publisher: American Society of Civil Engineers
    Abstract: At the Gowanus Canal Superfund site in Brooklyn, New York, a multilayer reactive capping system is required as part of the approved remedy. The base reactive layer is an organoclay (OC)–sand layer containing a minimum of 25% by dry weight OC that is intended to block any upwelling mobile nonaqueous phase liquids (NAPLs). The construction quality assurance (CQA) method for verifying the OC content of the OC–sand stockpiles prior to placement in the canal consists of Loss on Ignition (LOI) testing performed at an offsite laboratory with a turnaround time of 3 days. To mitigate construction delays, rapid field testing methods to verify the OC content of the OC–sand blends were sought. Interestingly, electrical conductivity (EC) measurements on the as-is (not sieved or pulverized) OC, sand, and their blends provided several correlations with goodness of fit (R2) values >0.95 for a variety of sand-sized materials including: a commercial playground sand, beach sand, a limestone quarry sourced sand, and the sediment capping sand from the first Remedial Target Area (RTA-1) at the Gowanus Canal. The correlation curves and R2 values were relatively insensitive to change in the sand borrow source (silicate or karst geology or salinity). EC measurements were available in as little as 30 min and up to approximately 24 h using a tabletop pH/EC probe, distilled water, beaker, and magnetic stirrer. The EC approach and preliminary correlations presented here can greatly reduce CQA testing turnaround times to within hours (not days) in field settings. Lastly, similar findings were made when another commercially modified bentonite clay known as Fluorosorb-400™ was blended with playground sand.
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      Gowanus Canal Superfund Site. VII: Rapid Verification of Organoclay–Sand Capping Blends

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    http://yetl.yabesh.ir/yetl1/handle/yetl/4299038
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    • Journal of Hazardous, Toxic, and Radioactive Waste

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    contributor authorAlyssa B. Lampi
    contributor authorDennis G. Grubb
    contributor authorNasser Hamdan
    contributor authorDusty R. V. Berggren
    date accessioned2024-12-24T10:30:08Z
    date available2024-12-24T10:30:08Z
    date copyright10/1/2024 12:00:00 AM
    date issued2024
    identifier otherJHTRBP.HZENG-1375.pdf
    identifier urihttp://yetl.yabesh.ir/yetl1/handle/yetl/4299038
    description abstractAt the Gowanus Canal Superfund site in Brooklyn, New York, a multilayer reactive capping system is required as part of the approved remedy. The base reactive layer is an organoclay (OC)–sand layer containing a minimum of 25% by dry weight OC that is intended to block any upwelling mobile nonaqueous phase liquids (NAPLs). The construction quality assurance (CQA) method for verifying the OC content of the OC–sand stockpiles prior to placement in the canal consists of Loss on Ignition (LOI) testing performed at an offsite laboratory with a turnaround time of 3 days. To mitigate construction delays, rapid field testing methods to verify the OC content of the OC–sand blends were sought. Interestingly, electrical conductivity (EC) measurements on the as-is (not sieved or pulverized) OC, sand, and their blends provided several correlations with goodness of fit (R2) values >0.95 for a variety of sand-sized materials including: a commercial playground sand, beach sand, a limestone quarry sourced sand, and the sediment capping sand from the first Remedial Target Area (RTA-1) at the Gowanus Canal. The correlation curves and R2 values were relatively insensitive to change in the sand borrow source (silicate or karst geology or salinity). EC measurements were available in as little as 30 min and up to approximately 24 h using a tabletop pH/EC probe, distilled water, beaker, and magnetic stirrer. The EC approach and preliminary correlations presented here can greatly reduce CQA testing turnaround times to within hours (not days) in field settings. Lastly, similar findings were made when another commercially modified bentonite clay known as Fluorosorb-400™ was blended with playground sand.
    publisherAmerican Society of Civil Engineers
    titleGowanus Canal Superfund Site. VII: Rapid Verification of Organoclay–Sand Capping Blends
    typeJournal Article
    journal volume28
    journal issue4
    journal titleJournal of Hazardous, Toxic, and Radioactive Waste
    identifier doi10.1061/JHTRBP.HZENG-1375
    journal fristpage04024019-1
    journal lastpage04024019-8
    page8
    treeJournal of Hazardous, Toxic, and Radioactive Waste:;2024:;Volume ( 028 ):;issue: 004
    contenttypeFulltext
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