Bedoukian   RussellIPM   RussellIPM   Piezoelectric Micro-Sprayer


Home
Animal Taxa
Plant Taxa
Semiochemicals
Floral Compounds
Semiochemical Detail
Semiochemicals & Taxa
Synthesis
Control
Invasive spp.
References

Abstract

Guide

Alphascents
Pherobio
InsectScience
E-Econex
Counterpart-Semiochemicals
Print
Email to a Friend
Kindly Donate for The Pherobase

« Previous AbstractGrape and Wine Composition in Vitis vinifera L. cv. Cannonau Explored by GC-MS and Sensory Analysis    Next AbstractMetabolite profiling of non-sterile rhizosphere soil »

Ground Water


Title:Effect of NAPL Source Morphology on Mass Transfer in the Vadose Zone
Author(s):Petri BG; Fucik R; Illangasekare TH; Smits KM; Christ JA; Sakaki T; Sauck CC;
Address:"Faculty of Nuclear Sciences and Physical Engineering, Czech Technical University in Prague, Prague, Czech Republic. Department of Civil and Environmental Engineering, Colorado School of Mines, 1500 Illinois St, Golden, CO 80401. Department of Civil and Environmental Engineering, U. S. Air Force Academy, Colorado Springs, CO"
Journal Title:Ground Water
Year:2015
Volume:20141223
Issue:5
Page Number:685 - 698
DOI: 10.1111/gwat.12284
ISSN/ISBN:1745-6584 (Electronic) 0017-467X (Linking)
Abstract:"The generation of vapor-phase contaminant plumes within the vadose zone is of interest for contaminated site management. Therefore, it is important to understand vapor sources such as non-aqueous-phase liquids (NAPLs) and processes that govern their volatilization. The distribution of NAPL, gas, and water phases within a source zone is expected to influence the rate of volatilization. However, the effect of this distribution morphology on volatilization has not been thoroughly quantified. Because field quantification of NAPL volatilization is often infeasible, a controlled laboratory experiment was conducted in a two-dimensional tank (28 cm x 15.5 cm x 2.5 cm) with water-wet sandy media and an emplaced trichloroethylene (TCE) source. The source was emplaced in two configurations to represent morphologies encountered in field settings: (1) NAPL pools directly exposed to the air phase and (2) NAPLs trapped in water-saturated zones that were occluded from the air phase. Airflow was passed through the tank and effluent concentrations of TCE were quantified. Models were used to analyze results, which indicated that mass transfer from directly exposed NAPL was fast and controlled by advective-dispersive-diffusive transport in the gas phase. However, sources occluded by pore water showed strong rate limitations and slower effective mass transfer. This difference is explained by diffusional resistance within the aqueous phase. Results demonstrate that vapor generation rates from a NAPL source will be influenced by the soil water content distribution within the source. The implications of the NAPL morphology on volatilization in the context of a dynamic water table or climate are discussed"
Keywords:"Diffusion Gases *Models, Theoretical Porosity Soil Pollutants/*analysis Trichloroethylene/*analysis Volatilization Water Movements Water Pollutants, Chemical/*analysis;"
Notes:"MedlinePetri, Benjamin G Fucik, Radek Illangasekare, Tissa H Smits, Kathleen M Christ, John A Sakaki, Toshihiro Sauck, Carolyn C eng Research Support, Non-U.S. Gov't 2014/12/24 Ground Water. 2015 Sep-Oct; 53(5):685-98. doi: 10.1111/gwat.12284. Epub 2014 Dec 23"

 
Back to top
 
Citation: El-Sayed AM 2024. The Pherobase: Database of Pheromones and Semiochemicals. <http://www.pherobase.com>.
© 2003-2024 The Pherobase - Extensive Database of Pheromones and Semiochemicals. Ashraf M. El-Sayed.
Page created on 23-11-2024