Mulder H, Breure A M, Van Andel J G, Grotenhuis J T, Rulkens W H
Laboratory of Ecotoxicology, National Institute of Public Health and the Environment, P.O. Box 1, 3720 BA Bilthoven, The Netherlands.
Biotechnol Bioeng. 1998 Jan 20;57(2):145-54. doi: 10.1002/(sici)1097-0290(19980120)57:2<145::aid-bit3>3.0.co;2-n.
The influence of hydrodynamic conditions on the dissolution rate of crystalline naphthalene as a model polycyclic aromatic hydrocarbon (PAH) was studied in stirred batch reactors with varying impeller speeds. Mass transfer from naphthalene melts of different surface areas to the aqueous phase was measured and results were modeled according to the film theory. Results were generalized using dimensionless numbers (Reynolds, Schmidt, and Sherwood). In combined mass transfer and biodegradation experiments, the effect of hydrodynamic conditions on the degradation rate of naphthalene by Pseudomonas 8909N was studied. Experimental results were mathematically described using mass-transfer and microbiological models. The experiments allowed determination of mass-transfer and microbiological parameters separately in a single run. The biomass formation rate under mass transfer limited conditions, which is related to the naphthalene biodegradation rate, was correlated to the dimensionless Reynolds number, indicating increased bioavailability at increased mixing in the reactor liquid. The methodology presented in which mass transfer processes are quantified under sterile conditions followed by a biodegradation experiment can also be adapted to more complex and realistic systems, such as particulate, suspended PAH solids or soils with intrapartically sorbed contaminants when the appropriate mass-transfer equations are incorporated.
在不同搅拌速度的间歇搅拌反应器中,研究了流体动力学条件对作为模型多环芳烃(PAH)的结晶萘溶解速率的影响。测量了不同表面积的萘熔体向水相的传质,并根据膜理论对结果进行了建模。结果使用无量纲数(雷诺数、施密特数和舍伍德数)进行了归纳。在传质与生物降解联合实验中,研究了流体动力学条件对假单胞菌8909N降解萘速率的影响。实验结果使用传质模型和微生物模型进行了数学描述。这些实验允许在一次运行中分别确定传质参数和微生物参数。传质受限条件下的生物质形成速率与萘生物降解速率相关,该速率与无量纲雷诺数相关,表明反应器液体中混合程度增加时生物可利用性提高。所提出的方法,即在无菌条件下对传质过程进行量化,然后进行生物降解实验,当纳入适当的传质方程时,也可适用于更复杂和现实的系统,如颗粒状、悬浮的PAH固体或含有颗粒内吸附污染物的土壤。