Biological treatment of TNT contaminated soil. 2. Biologically induced immobilization of the contaminants and full-scale application

被引:76
作者
Lenke, H
Warrelmann, J
Daun, G
Hund, K
Sieglen, U
Walter, U
Knackmuss, HJ
机构
[1] Fraunhofer Inst Grenzflachen & Bioverfahrenstech, D-70569 Stuttgart, Germany
[2] Umweltschutz Nord GMBH & Co, D-27767 Ganderkesee, Germany
[3] Fraunhofer Inst Umweltchem & Okotoxikol, D-57392 Schmallenberg, Germany
关键词
D O I
10.1021/es970950t
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Anaerobic treatment of originally contaminated soil from a former ammunition plant was carried out in a laboratory slurry reactor. While fermenting glucose to ethanol, acetate, and propionate, the anaerobic bacteria completely reduced the nitro groups of 2,4,6-trinitrotoluene (TNT) and aminodinitrotoluenes, which led to a complete and irreversible binding of the reduced products to the soil. 2,4-Dinitrotoluene and hexahydro-1,3,5-trinitro-l,3,5-triazine were also reduced in the soil slurry and were no longer detectable after the anaerobic treatment. To mineralize the fermentation products, a subsequent aerobic treatment was necessary to complete the bioremediation process. This bioremediation process was tested in a technical scale at Hessisch Lichtenau-Hirschhagen, Germany. A sludge reactor (Terranox system) was filled with 18 m(3) of contaminated soil (main contaminants were TNT, 2,4-dinitrotoluene, hexahydro-1,3,5-trinitro-l,3,5-triazine)and 10 m(3) of water. The anaerobic stage was carried out by periodical feeding of sucrose. The sludge was subsequently dewatered and treated aerobically. Chemical analysis revealed an overall reduction of more than 99% of the contaminants. Ecotoxicological tests performed with various aquatic systems (luminescent bacteria, daphnids, algae) and terrestrial systems (respiring bacteria, nitrifying bacteria, cress plants, earth worms) showed that residual toxicity could not be detected after the anaerohic/aerobic treatment.
引用
收藏
页码:1964 / 1971
页数:8
相关论文
共 47 条
[1]  
[Anonymous], 1985, 38414S2 DIN
[2]  
[Anonymous], 1991, 38412 DIN 34
[3]  
[Anonymous], 1991, 38412 DIN 33
[4]  
*BDK, 1994, METH AN KOMP, P57
[5]   AMMONIUM OXIDIZER NUMBERS, POTENTIAL AND ACTUAL OXIDATION RATES IN 2 SWEDISH ARABLE SOILS [J].
BERG, P ;
ROSSWALL, T .
BIOLOGY AND FERTILITY OF SOILS, 1985, 1 (03) :131-140
[6]  
BOOPATHY R, 1993, APPL MICROBIOL BIOT, V39, P270, DOI 10.1007/BF00228618
[7]   NITROAROMATIC COMPOUNDS SERVE AS NITROGEN-SOURCE FOR DESULFOVIBRIO SP (B-STRAIN) [J].
BOOPATHY, R ;
KULPA, CF .
CANADIAN JOURNAL OF MICROBIOLOGY, 1993, 39 (04) :430-433
[8]  
Breitung J, 1996, APPL MICROBIOL BIOT, V44, P795, DOI 10.1007/BF00178621
[9]   BIODEGRADATION OF 2,4,6-TRINITROTOLUENE BY PHANEROCHAETE-CHRYSOSPORIUM - IDENTIFICATION OF INITIAL DEGRADATION PRODUCTS AND THE DISCOVERY OF A TNT METABOLITE THAT INHIBITS LIGNIN PEROXIDASES [J].
BUMPUS, JA ;
TATARKO, M .
CURRENT MICROBIOLOGY, 1994, 28 (03) :185-190
[10]   Biological treatment of TNT-contaminated soil. 1. Anaerobic cometabolic reduction and interaction of TNT and metabolites with soil components [J].
Daun, G ;
Lenke, H ;
Reuss, M ;
Knackmuss, HJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1998, 32 (13) :1956-1963