Effect of operating parameters on molinate biodegradation

被引:14
作者
Correia, P
Boaventura, RAR
Reis, MAM
Nunes, OC
机构
[1] Univ Porto, Fac Engn, Dept Engn Quim, P-4200465 Oporto, Portugal
[2] Univ Nova Lisboa, Dept Chem, CQFB REQUINTE, Caparica, Portugal
关键词
molinate; 2-oxo-molinate; xenobiotic; herbicide biodegradation; kinetics;
D O I
10.1016/j.watres.2005.11.016
中图分类号
X [环境科学、安全科学];
学科分类号
08 [工学]; 0830 [环境科学与工程];
摘要
The effect of operating conditions during molinate degradation by the defined mixed bacterial culture DC, previously described as able to mineralize molinate, was evaluated in a batch reactor. Parameters such as the rate of molinate degradation, the dissolved organic carbon (DOC) consumption and the accumulation of molinate degradation products were monitored along the culture growth. The effect of conditions such as temperature, pH, aeration rate, salinity, and presence of additional carbon and/or nitrogen sources, was tested independently. Degradation of molinate in river water was also evaluated. Culture DC was able to-grow and to mineralize molinate at all the conditions assayed. Temperature was the factor with the strongest influence on bacterial growth and molinate mineralization. The lowest and the highest rate values of growth (0.010 and 0.110 h(-1)) and of molinate degradation (0.027 and 0.180 g molinate g(-1) cell dry wth(-1)) were obtained at 15 and 35 degrees C, respectively. In cultures with approximately 187 mgl(-1) of molinate, 2-oxo-molinate was the major molinate degradation product accumulated in the medium, in concentrations below 0.133 mg l(-1). Degradation of molinate was also evaluated in a continuous stirred tank reactor (CSTR). Operating the CSTR at a hydraulic retention time (HRT) of 83 h, fed with medium containing molinate concentrations ranging from 1 to 3 mM, culture DC degraded the herbicide with specific degradation rates similar to those obtained in the batch systems. (c) 2005 Elsevier Ltd. All rights reserved.
引用
收藏
页码:331 / 340
页数:10
相关论文
共 24 条
[1]
Monitoring of pesticide residues and their metabolites in surface and underground waters of Imathia (N. Greece) by means of solid-phase extraction disks and gas chromatography [J].
Albanis, TA ;
Hela, DG ;
Sakellarides, T ;
Konstantinou, IK .
JOURNAL OF CHROMATOGRAPHY A, 1998, 823 (1-2) :59-71
[2]
A novel pathway for mineralization of the thiocarbamate herbicide molinate by a defined bacterial mixed culture [J].
Barreiros, L ;
Nogales, B ;
Manaia, CM ;
Ferreira, ACS ;
Pieper, DH ;
Reis, MA ;
Nunes, OC .
ENVIRONMENTAL MICROBIOLOGY, 2003, 5 (10) :944-953
[3]
*CAL EPA, 2000, EV MOL TOX AIR CONT
[4]
MOLINATE DECONTAMINATION PROCESSES IN EFFLUENT WATER FROM RICE FIELDS [J].
CARRASCO, JM ;
SABATER, C ;
ALONSO, JL ;
GONZALEZ, J ;
BOTELLA, S ;
AMOROS, I ;
IBANEZ, MJ ;
BOIRA, H ;
FERRER, J .
SCIENCE OF THE TOTAL ENVIRONMENT, 1992, 123 :219-232
[5]
A case study of molinate application in a Portuguese rice field: herbicide dissipation and proposal of a clean-up methodology [J].
Castro, M ;
Silva-Ferreira, AC ;
Manaia, UM ;
Nunes, OC .
CHEMOSPHERE, 2005, 59 (07) :1059-1065
[6]
Characterization of risks associated with the use of molinate [J].
Cochran, RC ;
Formoli, TA ;
Pfeifer, KF ;
Aldous, CN .
REGULATORY TOXICOLOGY AND PHARMACOLOGY, 1997, 25 (02) :146-157
[7]
DUARTE ACL, 2003, RELATORIOS CIENTIFIC, V8, P10
[8]
GOLOVLEVA LA, 1981, IZV AN SSSR BIOL+, V3, P348
[9]
GRADY CPL, 1999, BIOL WASTE WATER TRE, V43, P420
[10]
IMAI Y, 1986, J PESTIC SCI, V11, P245