Fate of chemical warfare agents and toxic industrial chemicals in landfills

被引:38
作者
Bartelt-Hunt, Shannon L.
Barlaz, Morton A.
Knappe, Detlef R. U.
Kjeldsen, Peter
机构
[1] N Carolina State Univ, Dept Civil Construct & Environm Engn, Raleigh, NC 27695 USA
[2] Univ Nebraska, Dept Civil Engn, Omaha, NE 68182 USA
[3] Tech Univ Denmark, Inst Environm & Resources, DK-2800 Lyngby, Denmark
关键词
D O I
10.1021/es052400y
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
One component of preparedness for a chemical attack is planning for the disposal of contaminated debris. To assess the feasibility of contaminated debris disposal in municipal solid waste (MSW) landfills, the fate of selected chemical warfare agents (CWAs) and toxic industrial chemicals (TICs) in MSW landfills was predicted with a mathematical model. Five blister agents [sulfur mustard (HD), nitrogen mustard (HN-2), lewisite (L), ethyldichloroarsine (ED), and phosgene oxime (CX)], eight nerve agents [tabun (GA), sarin (GB), soman (GD), GE, GF, VX, VG, and VM], one riot-control agent [CS], and two TICs [furan and carbon disulfide] were studied. The effects of both infiltration ( climate) and contaminant biodegradability on fate predictions were assessed. Model results showed that hydrolysis and gas-phase advection were the principal fate pathways for CWAs and TICs, respectively. Apart from CX and the TICs, none of the investigated compounds was predicted to persist in a landfill for more than 5 years. Climate had little impact on CWA/TIC fate, and biodegradability was only important for compounds with long hydrolysis half-lives. Monte Carlo simulations were performed to assess the influence of uncertainty in model input parameters on CWA/TIC fate predictions. Correlation analyses showed that uncertainty in hydrolysis rate constants was the primary contributor to variance of CWA fate predictions, while uncertainty in the Henry's Law constant and landfill gas-production rate accounted for most of the variance of TIC fate predictions. CWA hydrolysates were more persistent than the parent CWAs, but limited information is available on abiotic or biotic transformation rates for these chemicals.
引用
收藏
页码:4219 / 4225
页数:7
相关论文
共 38 条
[1]   Carbon storage during biodegradation of municipal solid waste components in laboratory-scale landfills [J].
Barlaz, MA .
GLOBAL BIOGEOCHEMICAL CYCLES, 1998, 12 (02) :373-380
[2]   Kinematic wave model for water movement in municipal solid waste [J].
Bendz, D ;
Singh, VP ;
Rosqvist, H ;
Bengtsson, L .
WATER RESOURCES RESEARCH, 1998, 34 (11) :2963-2970
[3]   PHARMACOKINETICS OF THE SOMAN SIMULANT 1,2,2-TRIMETHYLPROPYL DIMETHYLPHOSPHINATE (PDP) IN RATS [J].
BENSCHOP, HP ;
WESSELMAN, HC .
ARCHIVES OF TOXICOLOGY, 1989, 63 (03) :238-243
[4]   Field performance of compacted clay liners [J].
Benson, CH ;
Daniel, DE ;
Boutwell, GP .
JOURNAL OF GEOTECHNICAL AND GEOENVIRONMENTAL ENGINEERING, 1999, 125 (05) :390-403
[5]  
CAMOBRECO V, 2000, LIFE CYCLE INVENTORY
[6]  
*CDCP, 2005, CHEM AG
[7]  
CLARK DN, 1989, REV REACTIONS CHEM A
[8]  
COHEN B, 1946, CHEM WARFARE AGENT 3
[9]  
*DEP ARM, 2005, P467 NAVFAC DEP ARM
[10]   Anaerobic degradation of phthalic acid esters during digestion of municipal solid waste under landfilling conditions [J].
Ejlertsson, J ;
Meyerson, U ;
Svensson, BH .
BIODEGRADATION, 1996, 7 (04) :345-352