Design of an MTBE remediation technology evaluation

被引:3
|
作者
Azadpour-Keeley, Ann
Barcelona, Michael J.
机构
[1] US EPA, Robert S Kerr Environm Res Ctr, Off Res & Dev, Ada, OK 74820 USA
[2] Western Michigan Univ, Dept Chem, Kalamazoo, MI 49008 USA
来源
关键词
D O I
10.1111/j.1745-6592.2006.00078.x
中图分类号
TV21 [水资源调查与水利规划];
学科分类号
081501 ;
摘要
This study examines the intrinsic variability of dissolved methyl tert-butyl ether (MTBE) concentrations in ground water during the course of a pilot-scale bioremedial technology trial in Port Hueneme, California. A pretrial natural gradient tracer experiment using bromide was conducted in an anaerobic test section of the aquifer to characterize hydrogeology. The results showed the presence of a complex velocity field in terms of vertical stratification and preferential flowpaths. The hydraulic conductivity at the test area varied by > 2 orders of magnitude, and the effects of vertical stratification were made apparent by the tracers' detection pattern, which was predominately higher in the lower part of the aquifer. Since historically the lower portion of the aquifer significantly influenced MTBE transport, it was emphasized by increasing the sampling frequency for MTBE and tracers during the pilot test that involved the intermittent addition of oxygen and propane into the aquifer. A second tracer experiment using bromide and deuterated MTBE (H-2(12)-MTBE) was conducted at the onset of the technology trial and after the aquifer was made aerobic. The continuous metering of the tracer solutions into the test area was maintained for 300 d. The results showed that H-2(12)-MTBE behaved as a conservative tracer since (1) its concentrations increased throughout the study approaching its designed injected level and (2) the pattern of its detection resembled that of bromide. On the other hand, H-2(12)-MTBE, which was purposefully introduced into the aquifer, behaved differently from that of the existing dissolved MTBE plume that emanated from a non-aqueous phase liquid (NAPL) source over a decade ago, thereby undergoing years of diffusion. The data imply that a detailed understanding of the complexity of the flow field was not possible by observing the intrinsic MTBE data alone.
引用
收藏
页码:103 / 113
页数:11
相关论文
共 50 条
  • [1] MTBE REMEDIATION
    Kriz, Lubomir
    Danihelka, Pavel
    Wittlingerova, Zdenka
    14TH CONFERENCE ON ENVIRONMENT AND MINERAL PROCESSING, PT III, 2010, : 123 - 128
  • [2] Natural attenuation of MTBE as part of an integrated remediation design
    Moeri, EN
    Salvador, MC
    Coelho, R
    BIOREMEDIATION OF MTBE, ALCOHOLS, AND ETHERS, 2001, 6 (01): : 27 - 34
  • [3] Cost of MTBE remediation
    Wilson, BH
    Shen, H
    Pope, D
    BIOREMEDIATION OF MTBE, ALCOHOLS, AND ETHERS, 2001, 6 (01): : 129 - 136
  • [4] MTBE in groundwater: Status and remediation
    Fiorenza, S
    Suarez, MP
    Rifai, HS
    JOURNAL OF ENVIRONMENTAL ENGINEERING, 2002, 128 (09) : 773 - 781
  • [5] Remediation of water and soil contaminated with MTBE
    Keller, AA
    Sirivithiyapakorn, S
    Kram, ML
    CASE STUDIES IN THE REMEDIATION OF CHLORINATED AND RECALCITRANT COMPOUNDS, 2000, : 73 - 80
  • [6] Regenesis promotes MTBE remediation process
    Industrial Bioprocessing, 2000, 22 (03):
  • [7] Global biosciences MTBE remediation process works
    Perriello, Felix A.
    Industrial Bioprocessing, 2005, 27 (06): : 1 - 2
  • [8] Suitability evaluation of remediation technology for polluted farmland
    Li Yang
    Pan Ligang
    Li An
    Wang Beihong
    INTERNATIONAL JOURNAL OF AGRICULTURAL AND BIOLOGICAL ENGINEERING, 2015, 8 (02) : 39 - 45
  • [9] MBR application for MTBE remediation in contaminated water.
    Morrison, J
    Suidan, M
    Venosa, AT
    ABSTRACTS OF PAPERS OF THE AMERICAN CHEMICAL SOCIETY, 2001, 222 : U420 - U420
  • [10] Simple remediation system reduces MTBE levels in groundwater
    不详
    POLLUTION ENGINEERING, 2001, 33 (05) : 39 - 40