Thoma G J, Lam T B, Wolf D C
Department of Chemical Engineering, University of Arkansas, Fayetteville, AR 72701, USA.
Int J Phytoremediation. 2003;5(1):41-55. doi: 10.1080/16226510390856466.
We present a simple model for root length density that combines the generally accepted spatial (exponential decrease with depth) and temporal (sinusoidal) variability of root length. Parameters in this model for root length density can be determined from assumed or measured information regarding the annual biomass turnover, maximum standing biomass, and maximum depth of root penetration. The root length density model, coupled with information regarding the average root lifespan, gives specific root growth and senescence functions that are the forcing functions for the phytoremediation model. We present a screening level mathematical model for phytoremediation that accounts for the growth and senescence of roots in the system. This is an important factor for recalcitrant, immobile compounds found in weathered crude oil contaminated soils. The phytoremediation model is based on variable volume compartments that have individual first-order degradation rate constants; as the roots move through the soil, the soil cycles through the rhizosphere zone, decaying root zone and bulk soil zone. Thus, although the oil is immobile, as the roots penetrate through the soil the oil is brought into contact with the rhizosphere.
我们提出了一个简单的根长密度模型,该模型结合了普遍认可的根长空间(随深度呈指数下降)和时间(正弦)变异性。此根长密度模型中的参数可根据有关年生物量周转、最大现存生物量和最大根穿透深度的假设或测量信息来确定。根长密度模型与平均根寿命信息相结合,给出了特定的根生长和衰老函数,这些函数是植物修复模型的强迫函数。我们提出了一个筛选水平的植物修复数学模型,该模型考虑了系统中根的生长和衰老。对于风化原油污染土壤中难降解、不可移动的化合物而言,这是一个重要因素。植物修复模型基于具有各自一级降解速率常数的可变体积隔室;随着根在土壤中移动,土壤在根际区、根腐区和土体区循环。因此,尽管油是不可移动的,但随着根穿透土壤,油会与根际接触。