scholarly journals Identification of TCE and PCE sorption and biodegradation parameters in a sandy aquifer for fate and transport modelling: batch and column studies

2015 ◽  
Vol 22 (13) ◽  
pp. 9877-9888 ◽  
Author(s):  
E. Kret ◽  
A. Kiecak ◽  
G. Malina ◽  
I. Nijenhuis ◽  
A. Postawa
2014 ◽  
Vol 23 (7) ◽  
pp. 736-750 ◽  
Author(s):  
Gloria Teijón ◽  
Lucila Candela ◽  
Jirka Šimůnek ◽  
Karim Tamoh ◽  
Javier Valdes-Abellán

1998 ◽  
Vol 38 (11) ◽  
pp. 193-199
Author(s):  
Byung-Gi Hwang ◽  
Kwan-Soo Jun ◽  
Young-Dae Lee ◽  
Wu-Seng Lung

Contaminants in the interstitial waters are not only dissolved but also associated with a filterable colloidal phase such as DOC. The DOC plays an important role regulating the distribution of chemicals between particulate and dissolved phases since it binds chemicals and makes them unavailable for vertical diffusive exchange. A three-phase partitioning model that consists of free-dissolved, DOC-bound, particulate-bound components of the chemicals involved is used for the contaminant transport model in order to include the effect of DOC on the partition coefficient. The contaminant model is linked to WASP modeling framework to predict remobilization of PCBs in sediments and the fate and transport of the contaminant in overlying waters of the New Bedford Harbor where the harbor has been contaminated with PCBs and heavy metals released from electronic capacitor manufacturers. Simulation of remedial controls indicates that if no action is taken, PCB concentrations will continue to be at elevated levels. Several scenarios for the removal of contaminated sediments have been performed to reduce the elevated PCB concentrations to background levels.


2019 ◽  
Vol 221 ◽  
pp. 35-49 ◽  
Author(s):  
Luca Locatelli ◽  
Philip J. Binning ◽  
Xavier Sanchez-Vila ◽  
Gitte Lemming Søndergaard ◽  
Louise Rosenberg ◽  
...  

2008 ◽  
Vol 22 (19) ◽  
pp. 4011-4021 ◽  
Author(s):  
B. S. Caruso ◽  
T. J. Cox ◽  
R. L. Runkel ◽  
M. L. Velleux ◽  
K. E. Bencala ◽  
...  

1986 ◽  
Vol 21 (3) ◽  
pp. 398-410 ◽  
Author(s):  
John A. McCorquodale ◽  
Kamal Ibrahim ◽  
Yousry Hamdy

Abstract The response of the St. Clair River system (water column and bed sediments) to a spill of perchloroethylene (PERC) is predicted by application of the U.S. Environmental Protection Agency (EPA) TOXIWASP fate transport model. The spill occurred from August 13 to 16, 1986 at the Dow Chemical of Canada Inc. site. The estimated quantity of the spill was 18000 kg of which approximately 10,000 kg initially settled out In the vicinity of the Dow Chemical outfalls. At the end of 30 days the model indicated that about 12600 kg had been discharged to Lake St. Clair while 4500 kg and 90 kg remained on the river bed and in temporary storage in the water column respectively. Approximately 5% of the original spill was volatilized in the river during the 30 days after the spill.


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