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Simulation of Phytoremediation of a TNT‐Contaminated Soil Using the CTSPAC Model
Author(s) -
Ouyang Y.,
Shinde D.,
Ma L. Q.
Publication year - 2005
Publication title -
journal of environmental quality
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.888
H-Index - 171
eISSN - 1537-2537
pISSN - 0047-2425
DOI - 10.2134/jeq2004.0471
Subject(s) - xylem , phytoremediation , bioavailability , environmental chemistry , biodegradation , soil water , bioremediation , chemistry , rhizosphere , soil contamination , environmental science , transpiration , contamination , botany , soil science , biology , photosynthesis , ecology , bioinformatics , biochemistry , genetics , organic chemistry , bacteria
ABSTRACT Knowledge of water movement in the plant‐xylem system and contaminant bioavailability in the soil environment is crucial to evaluate the success of phytoremediation practices. This study investigated the removal of 2,4,6‐trinitrotoluene (TNT) from a contaminated sandy soil by a single poplar ( Populus fastigiata ) tree through the examinations of temporal variations of xylem water potential, root water uptake, and soil TNT bioavailability. A mathematical model, CTSPAC (Coupled Transport of water, heat, and solutes in the Soil–Plant–Atmosphere Continuum), was modified for the purpose of this study. The model was calibrated using laboratory measurements before its application. Our simulations show that the xylem water potential was high in the roots and low in the leaves with a potential head difference of 3.55 cm H 2 O, which created a driving force for water flow and chemical transport upward from the roots through the stem to the leaves. The daily average root water uptake rate was 25 cm 3 h −1 when an equilibrium condition was reached after 24 h. Our simulations further reveal that no TNT was found in the stem and leaves and only about 1% of total TNT mass was observed in the roots due to the rapid biodegradation and transformation of TNT into its daughter products. About 13% of the soil TNT was removed by the poplar tree, resulting mainly from root uptake since TNT is a recalcitrant compound. In general, the soil TNT bioavailability decreased with time due to the depletion of soil solution TNT by the poplar tree. A constant bioavailability (i.e., 3.1 × 10 −6 ) was obtained in 14 d in which the soil TNT concentration was about 10 mg L −1 Our study suggests that CTSPAC is a useful model to simulate phytoremediation of TNT‐contaminated sites.