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קהילה:
אסיף מאגר המחקר החקלאי
פותח על ידי קלירמאש פתרונות בע"מ -
Bioaugmentation of atrazine and fenamiphos impacted groundwater: Laboratory evaluation
Year:
2000
Source of publication :
Bioremediation Journal
Authors :
מנדלבאום, רפי
;
.
Volume :
4
Co-Authors:
Franzmann, P.D., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Zappia, L.R., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Tilbury, A.L.
Patterson, B.M., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Davis, G.B., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Mandelbaum, R.T., Inst. of Soil and Environ. Sciences, Volcani Research Center, 50250 Beit Dagan, Israel
Facilitators :
From page:
237
To page:
248
(
Total pages:
12
)
Abstract:
After the failure of a three-month pump-and-treat exercise to clean up an aquifer contaminated with the pesticides atrazine and fenamiphos, microcosm experiments using 14C-labeled compounds were undertaken to determine under what conditions bioremediation would be most effective, and to investigate the prospects for the use of bioaugmentation. The calculated half-lives for atrazine and fenamiphos mineralization to carbon dioxide in unamended, anaerobic aquifer material were 730 and 1,000 years, respectively. Oxygenation, coupled with bioaugmentalion with enrichments of atrazine-mineralizing bacteria obtained from the contaminated site or an imported, atrazine-mineralizing pure strain, Pseudomonas sp. strain ADP, decreased the half-life of atrazine mineralization, to <20 days. Although strain ADP does not use atrazine as a source of carbon and energy, amendment of the aquifer material with citrate, which strain ADP uses as a source of carbon and energy, did not appreciably stimulate the mineralization rate of atrazine in the microcosms, suggesting that the aquifer contains enough natural organic carbon for atrazine mineralization. Aerobic enrichments of fenamiphos-degrading bacteria were prepared; however, oxygenation and bioaugmentation of aquifer material with these strains did not enhance mineralization of fenamiphos within the time constraints of the experiments. The shortest calculated half-life of fenamiphos mineralization in the microcosms was 6.8 years, which is exceedingly long compared with the half-life of fenamiphos in most surface soils.
Note:
Related Files :
Aerobic bacteria
aquifers
Bio-augmentation
Clean up
Groundwater resources
herbicides
Time constraints
עוד תגיות
תוכן קשור
More details
DOI :
Article number:
Affiliations:
Database:
סקופוס
Publication Type:
סקירה
;
.
Language:
אנגלית
Editors' remarks:
ID:
31951
Last updated date:
02/03/2022 17:27
Creation date:
17/04/2018 01:06
Scientific Publication
Bioaugmentation of atrazine and fenamiphos impacted groundwater: Laboratory evaluation
4
Franzmann, P.D., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Zappia, L.R., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Tilbury, A.L.
Patterson, B.M., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Davis, G.B., Centre for Groundwater Studies, CSIRO Land and Water, Underwood Ave., Floreat Park, WA 6014, Australia
Mandelbaum, R.T., Inst. of Soil and Environ. Sciences, Volcani Research Center, 50250 Beit Dagan, Israel
Bioaugmentation of atrazine and fenamiphos impacted groundwater: Laboratory evaluation
After the failure of a three-month pump-and-treat exercise to clean up an aquifer contaminated with the pesticides atrazine and fenamiphos, microcosm experiments using 14C-labeled compounds were undertaken to determine under what conditions bioremediation would be most effective, and to investigate the prospects for the use of bioaugmentation. The calculated half-lives for atrazine and fenamiphos mineralization to carbon dioxide in unamended, anaerobic aquifer material were 730 and 1,000 years, respectively. Oxygenation, coupled with bioaugmentalion with enrichments of atrazine-mineralizing bacteria obtained from the contaminated site or an imported, atrazine-mineralizing pure strain, Pseudomonas sp. strain ADP, decreased the half-life of atrazine mineralization, to <20 days. Although strain ADP does not use atrazine as a source of carbon and energy, amendment of the aquifer material with citrate, which strain ADP uses as a source of carbon and energy, did not appreciably stimulate the mineralization rate of atrazine in the microcosms, suggesting that the aquifer contains enough natural organic carbon for atrazine mineralization. Aerobic enrichments of fenamiphos-degrading bacteria were prepared; however, oxygenation and bioaugmentation of aquifer material with these strains did not enhance mineralization of fenamiphos within the time constraints of the experiments. The shortest calculated half-life of fenamiphos mineralization in the microcosms was 6.8 years, which is exceedingly long compared with the half-life of fenamiphos in most surface soils.
Scientific Publication
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