Mukherji S, Weber W J
Environmental and Water Resources Engineering, Department of Civil and Environmental Engineering, The University of Michigan, Ann Arbor, Michigan 48109-2125, USA.
Biotechnol Bioeng. 1998 Dec 20;60(6):750-60.
The bioavailability of naphthalene present as a component of a complex nonaqueous phase liquid (NAPL) comprised by nine aromatic compounds was investigated. Specifically, the effects of naphthalene mass transfer from the NAPL to the aqueous phase on rates of its microbial degradation were examined. The investigations were conducted using a pure culture, ATCC 17484, and a mixed culture of naphthalene-degrading bacteria, the former having been implicated previously in the direct uptake of sorbed naphthalene. The studies were conducted in mass-transfer-limited, segregated-phase reactors (SPRs) in which both the NAPL and aqueous phases were internally well-mixed. A 30-day active biodegradation period was preceded and followed by a 5-7-day period devoid of bioactivity, during which time the rates and extents of mass transfer of components from the NAPL to the aqueous phase were quantified. The NAPL-phase naphthalene mass depletion profiles during biodegradation were compared to those predicted by assuming maximum mass depletion under mass-transfer-limited conditions using both pre- and post-biodegradation dissolution rate and equilibrium parameters. The observed mass depletion rates were high during the initial stages of biodegradation but decreased significantly in later stages. Throughout biodegradation, even in the initial rapid stage, mass depletion rates never exceeded maximum predicted rates based on pre-biodegradation mass transfer parameters. Reduced depletion rates in the later stages appear to relate to mass transfer hindrance caused by formation of biofilms at the NAPL-water interface.
对由九种芳香族化合物组成的复杂非水相液体(NAPL)中的萘的生物利用度进行了研究。具体而言,考察了萘从NAPL向水相的传质对其微生物降解速率的影响。研究使用了纯培养物ATCC 17484和萘降解细菌的混合培养物,前者先前被认为参与了吸附态萘的直接摄取。研究在传质受限的分离相反应器(SPR)中进行,其中NAPL相和水相在内部均充分混合。在30天的活性生物降解期之前和之后,有一个5至7天的无生物活性期,在此期间对组分从NAPL向水相的传质速率和程度进行了量化。将生物降解过程中NAPL相萘的质量消耗曲线与通过使用生物降解前和生物降解后的溶解速率及平衡参数,在传质受限条件下假设最大质量消耗所预测的曲线进行了比较。观察到的质量消耗速率在生物降解的初始阶段较高,但在后期显著下降。在整个生物降解过程中,即使在初始快速阶段,质量消耗速率也从未超过基于生物降解前传质参数预测的最大速率。后期消耗速率降低似乎与NAPL - 水界面处生物膜形成导致的传质阻碍有关。