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    Application and modeling of aniline sorption

    Author
    Roggenkamp, Susan E.
    View/Open
    177145_Roggenkamp_rpi_0185N_10776.pdf (2.362Mb)
    Other Contributors
    Nyman, Marianne; Kilduff, James; Gorby, Yuri;
    Date Issued
    2015-12
    Subject
    Environmental engineering
    Degree
    MS;
    Terms of Use
    This electronic version is a licensed copy owned by Rensselaer Polytechnic Institute, Troy, NY. Copyright of original work retained by author.;
    Metadata
    Show full item record
    URI
    https://hdl.handle.net/20.500.13015/1641
    Abstract
    Passive and active vegetative systems, and building integrated systems, were studied as viable aniline treatment options. The research of aqueous aniline sorption was executed to understand the best way to treat aniline, and possibly other volatile organic compounds (VOCs), with a building integrated system using growing media.; The sorption of aniline to four different growing media (e.g., expanded clay, growstone, activated carbon (AC) sheets, and granular activated carbon (GAC)) was studied after 1- and 7-day equilibration. The GAC was found to have the greatest sorption capacity for aniline with an average 7-d sorption value of 196.0 mg/g. Expanded clay and growstone did not adsorb much aniline with average 7-d sorption values of 0.16 and 0.01 mg/g, respectively. The AC sheets were tested with the idea that this material would provide even air treatment in a building integrated active phytoremediation system, but did not perform as well as GAC with a 7-d average sorption value of 5.1 mg/g.; A mathematical model that estimates the throughput parameter and subsequent time for a C/Co aniline concentration ratio, was developed. This model predicted a breakthrough curve of aniline through a GAC packed bed system. A laboratory study of a GAC packed column was studied to compare experimental results to the model output. The model was used in three different ways: [1] at equilibrium (7-d Freundlich coefficients of 16.6 (KF) and 0.37 (N)), [2] at non-equilibrium (1-d Freundlich coefficients of 24.5 (KF) and 0.45 (N)), and [3] in expected gas phase. The equilibrium model matched the laboratory breakthrough curve well with both curves having C/Co values of 0.5 occurring at about 9 days.;
    Description
    December 2015; School of Engineering
    Department
    Dept. of Civil and Environmental Engineering;
    Publisher
    Rensselaer Polytechnic Institute, Troy, NY
    Relationships
    Rensselaer Theses and Dissertations Online Collection;
    Access
    Restricted to current Rensselaer faculty, staff and students. Access inquiries may be directed to the Rensselaer Libraries.;
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