Dissolved organic matter removal during coal slag additive soil aquifer treatment for secondary effluent recharging: Contribution of aerobic biodegradation

2015 ◽  
Vol 156 ◽  
pp. 158-166 ◽  
Author(s):  
Liangliang Wei ◽  
Siliang Li ◽  
Daniel R. Noguera ◽  
Kena Qin ◽  
Junqiu Jiang ◽  
...  
2007 ◽  
Vol 52 (18) ◽  
pp. 2496-2505 ◽  
Author(s):  
Shuang Xue ◽  
QingLiang Zhao ◽  
Liangliang Wei ◽  
Lina Wang ◽  
Zhigang Liu

Author(s):  
Natália Rodrigues Guimarães ◽  
Fabiane Dörr ◽  
Rodrigo de Oliveira Marques ◽  
Ernani Pinto ◽  
Sidney Seckler Ferreira Filho

2011 ◽  
Vol 25 (4) ◽  
pp. 540-546 ◽  
Author(s):  
Gone Droh Lanciné ◽  
Kamagate Bamory ◽  
Ligban Raymond ◽  
Savane Issiaka ◽  
Biemi Jean

2013 ◽  
Vol 316-317 ◽  
pp. 323-326
Author(s):  
Chao Jie Zhang ◽  
Si Bo Li ◽  
Qian Chen ◽  
Qi Zhou

Dissolved organic matter (DOM) may do harms to human beings. After disinfected by chlorine (amine), DOM can form disinfection by-products (DBPs) which can be mutagenic, teratogenic and carcinogenic. Characterization and source of trihalomethane precursors in the secondary effluent by sequencing batch reactors were investigated. CHCl3 was the primary DBPs. The results showed that the precursors of CHCl3 were mainly strongly hydrophobic DOM, while CHCl2Br and CHClBr2 were mainly formed from hydrophilic DOM. The effects of different powder media (activated carbon, zeolite) on removal of DOM were compared. The results showed that the dosing of powder media can promote the removal of DOM and the DBPs precursors.


2004 ◽  
Vol 50 (2) ◽  
pp. 245-253 ◽  
Author(s):  
T. Rauch ◽  
J.E. Drewes

The fate of effluent organic matter (EfOM) during groundwater recharge was investigated by studying the removal behavior of four bulk organic carbon fractions isolated from a secondary effluent: Hydrophilic organic matter (HPI), hydrophobic acids (HPO-A), colloidal organic matter (OM), and soluble microbial products (SMPs). Short-term removal of the bulk organic fractions during soil infiltration was simulated in biologically active soil columns. Results revealed that the four organic fractions showed a significantly different behavior with respect to biological removal. HPI and colloidal OM were prone to biological removal during initial soil infiltration (0-30 cm) and supported soil microbial biomass growth in the infiltrative surface. Additionally, colloidal OM was partly removed by physical adsorption or filtration. HPO-A and SMPs reacted recalcitrant towards biological degradation as indicated by low soil biomass activity responses. Adsorbability assessment of the biologically refractory portions of the fractions onto powered activated carbon (PAC) indicated that physical removal is not likely to play a significantly role in further diminishing recalcitrant HPO-A, HPI and SMPs during longer travel times in the subsurface.


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