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Relationship between cyclodextrin extraction and biodegradation of phenanthrene in soil
Angela H Rhodes1, Nadia M Dew, Kirk T Semple
1Department of Environmental Science and the Lancaster Environment Centre, Lancaster University, Lancaster LA1 4YQ, United Kingdom.
Hydroxypropyl-beta-cyclodextrin (HPCD) extraction accurately predicts microbial degradation of phenanthrene in soil. A single HPCD extraction correlates well with the total amount of phenanthrene available for microbial breakdown.
Area of Science:
- Environmental Chemistry
- Soil Science
- Microbiology
Background:
- Assessing microbial degradability of soil contaminants is crucial for environmental remediation.
- Traditional exhaustive extraction methods using organic solvents lack relevance to bioavailable contaminant fractions.
- Hydroxypropyl-beta-cyclodextrin (HPCD) offers a potential alternative for estimating bioavailable contaminants.
Purpose of the Study:
- To investigate the relationship between sequential HPCD extractions and microbial mineralization of phenanthrene in soil.
- To determine if HPCD extraction can predict the fraction of phenanthrene available for microbial degradation over time.
Main Methods:
- Four different soils were used to assess phenanthrene desorption via sequential HPCD extractions over 10 days.
- Phenanthrene mineralization was measured using a [14C]-labeled compound and an enriched pseudomonad inoculum.
- Desorption and mineralization data were compared to establish correlations.
Main Results:
- Cumulative HPCD extraction of phenanthrene exceeded mineralization by over 20%.
- Total phenanthrene mineralized after single or multiple inoculations was statistically similar to that extracted after the first 24 hours by HPCD.
- A strong linear correlation was observed between mineralized and extracted phenanthrene (r2 > 0.95).
Conclusions:
- A single HPCD extraction accurately predicts the total fraction of phenanthrene available for microbial mineralization in diverse soil types.
- HPCD extraction serves as a reliable and reproducible method for assessing the bioavailable fraction of organic contaminants in soil.
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