Journal of University of Chinese Academy of Sciences >
Bioavailability of polycyclic aromatic hydrocarbons in soils and its evaluation method
Received date: 2010-03-04
Revised date: 2010-04-20
Online published: 2010-07-15
Supported by
Supported by the National Natural Science Foundation of China (40730740, 20621703) and the National Basic Research Program of China (2009CB421603)
Polycyclic aromatic hydrocarbons (PAHs) are a group of persistant pollutants which are difficult to degrade and metabolize in the environment and exist widely around the world. They can accumulate in organisms and subsequently translocate, transform and be concentrated in food chain due to their lipophilicity. Some PAHs are carcinogenic and pose great risk to human health. In order to predict their potential risk, it is essential to explore the bioavailability of PAHs in soil. The uptake and acropetal translocation of 14 priority PAHs by wheat (Triticum aestivum L.) from field-contaminated soils has been investigated. The results indicate that compounds with intermediate to high hydrophobicity such as PAHs can acropetally translocate in plants. The amount of PAHs translocated from roots to aerial tissues has been quantified. Furthermore, a new type of semipermeable membrane-based passive sampler,triolein embedded cellulose acetate membrane (TECAM), was successfully applied to sample PAHs in soils. PAHs in soil sampled by TECAMs reached apparent equilibrium within 48h, significantly saving time for sampling PAHs in soil. The content of PAHs sampled by TECAMs was related to soil organic matter, dissolved organic carbon and the aging time of PAHs in soil. TECAM-accumulated PAHs correlated well with PAHs accumulated in earthworms (Eisenia andrei) and wheat roots (Triticum aestivum L.). Soil-pore water-TECAM three-compartment model was successfully used to describe the overall pro cess of PAH sampling by TECAM from field-contaminated soils. Additionally, TECAM caused minimal disturbance to soil and was easy to deploy. Therefore, TECAM is believed to be a useful tool to sampling hydrophobic organic carbons in soil and predict their bioavailability to earthworms and plants.
TAO Yu-Qiang , ZHANG Shu-Zhen , XUE Bin . Bioavailability of polycyclic aromatic hydrocarbons in soils and its evaluation method[J]. Journal of University of Chinese Academy of Sciences, 2010 , 27(4) : 568 -576 . DOI: 10.7523/j.issn.2095-6134.2010.4.020
[1] Fismes J, Perrin-Ganier C, Empereur-Bissonnet P, et al. Soil-to-plant transfer and translocation of polycyclic aromatic hydrocarbons by vegetables grown on industrial contaminated soils
[J]. Journal of Environmental Quality, 2002, 31: 1649-1656.
[2] Kipopoulou A M, Manoli E, Samara C. Bioconcentration of polycyclic aromatic hydrocarbons in vegetables grown in an industrial area
[J]. Environmental Pollution, 1999, 106: 369-380.
[3] Gao Y, Zhu L. Plant uptake, accumulation and translocation of phenanthrene and pyrene in soils
[J]. Chemosphere, 2004, 55: 1169-1178.
[4] Kraaij R, Mayer P, Busser F J M, et al. Measured pore-water concentrations make equilibrium partitioning work—A data analysis
[J]. Environmental Science and Technology, 2003, 37: 268-274.
[5] Ramos E U, Meijer S N, Vaes W H J, et al. Using solid-phase microextraction to determine partition coefficients to humic acids and bioavailable concentrations of hydrophobic chemicals
[J]. Environmental Science and Technology, 1998, 32: 3430-3435.
[6] Mayer P, Vaes W H J, Wijnker F, et al. Sensing dissolved sediment porewater concentrations of persistent and bioaccumulative pollutants using disposable solid-phase microextraction fibers
[J]. Environmental Science and Technology, 2000, 34: 5177-5183.
[7] Conder J M, La Point T W, Lotufo G R, et al. Nondestructive, minimal-disturbance, direct-burial soild-phase microextraction fiber technique for measuring TNT in sediment
[J]. Environmental Science and Technology, 2003, 37: 1625-1632.
[8] van Der Wal L, Jager T, Fleuren R H L J, et al. Solid-phase microextraction to predict bioavailability and accumulation of organic micropollutants in terrestrial organisms after exposure to a field-contaminated soil
[J]. Environmental Science and Technology, 2004, 38: 4842-4848.
[9] Yang Z, Zeng E Y, Maruya K A, et al. Predicting organic contaminant concentrations in sediment pore water using solid-microextraction . Chemosphere, 2007, 66: 1408-1414.
[10] Liu J, Hu X, Peng J, et al. Equilibrium sampling of freely dissolved alkylphenols into a thin film of 1-octanol supported on a hollow fiber membrane
[J]. Analytical Chemistry, 2006, 78: 8526-8534.
[11] Rantalainen A L, Passivirta J, Herve S. Uptake of chlorohydrocarbons from soil by lipid-containing semipermeable membrane devices (SPMDs)
[J]. Chemosphere, 1998, 36: 1415-1427.
[12] Wild S R, Jones K C. Polynuclear aromatic hydrocarbon uptake by carrots Grown in sludge-amended soil
[J]. Journal of Environmental Quality, 1992, 21: 217-225.
[13] Collins C, Fryer M, Grosso A. Plant uptake of non-ionic organic chemicals
[J]. Environmental Science and Technology, 2006, 40: 45-52.
[14] Simonich S T, Hites R A. Organic pollutant accumulation in vegetation
[J]. Environmental Science and Technology, 1995, 29: 2905-2913.
[15] Briggs G G, Bromilow R H, Evans A A. Relations between lipophilicity and root uptake and translocation of non-ionised chemicals by barley
[J]. Pesticide Science, 1982, 13: 495-504.
[16] Lin D H, Zhu L Z, He W, et al. Tea plant uptake and translocation of polycyclic aromatic hydrocarbons from water and around air
[J]. Journal of Agricultral and Food Chemistry, 2006, 54: 3658-3662.
[17] Tao Y Q, Zhang S Z, Zhu Y, et al. Uptake and acropetal translocation of polycyclic aromatic hydrocarbons by wheats (Triticum aestivum L.) . Environmental Science and Technology, 2009, 43, 3556-3560.
[18] Semple K T, Morriss A W J, Paton G I. Bioavailability of hydrophobic organic contaminants in soils: fundamental concepts and techniques for analysis
[J]. European Journal of Soil Science, 2003, 54: 809-818.
[19] Liste H, Alexander M. Butanol extraction to predict bioavailability of PAHs in soil
[J]. Chemosphere, 2002, 46: 1011-1017.
[20] Tang J X, Alexander M. Mild extraction and bioavailability of polycyclic aromatic carbons in soils
[J]. Environment Toxicology Chemistry, 1999, 18: 2711-2714.
[21] Reid B J, Jones K C, Semple K T. Bioavailability of persistent organic pollutants in soils and sediments-a perspective on mechanisms, consequences and assessment
[J]. Environmental Pollution, 2000, 108: 103-112.
[22] Alexander M. Aging, bioavailability, and overestimation of risk from environmental pollutants
[J]. Environmental Science and Technology, 2000, 34: 4259-4265.
[23] Verweij F, Booij K, Satumalay K, et al. Assessment of bioavailable PAH, PCB and OCP concentrations in water, using semipermeable membrane devices (SPMDs), sediments and caged carp
[J]. Chemosphere, 2004, 54: 1675-1689.
[24] Rantalainen A L, Passivirta J, Herve S. Uptake of chlorohydrocarbons from soil by lipid-containing semipermeable membrane devices (SPMDs)
[J]. Chemosphere, 1998, 36: 1415-1427.
[25] Hernandez F, Beltran J, Lopez F J, et al. Use of solid-phase microextraction for the quantitative determination of herbicides in soil and water samples
[J]. Analytical Chemistry, 2000, 72: 2313-2322.
[26] Awata H, Cobb G P, Anderson T A. A chemical test for determining biological availability of aged chemicals in soil
[J]. International Journal of Environmental Analytical Chemistry, 2000, 78, 41-49.
[27] Krauss M, Wilcke W G. Biomimetic extraction of PAHs and PCBs from soil with octadecyl-modified silica disks to predict their availability to earthworms
[J]. Environmental Science and Technology, 2001, 35: 3931-3935.
[28] Tao Y, Zhang S, Wang Z, et al. Biomimetic accumulation of PAHs from soils by triolein embedded cellulose acetate membranes (TECAMs) to estimate their bioavailability
[J]. Water Research, 2008, 42: 754-762.
[29] Tao Y, Zhang S, Wang Z, et al. Predicting bioavailability of PAHs in field-contaminated soils by passive sampling with triolein embedded cellulose acetate membranes
[J]. Environmental Pollution, 2009, 157: 545-551.
[30] Tao S, Xu F, Liu W, et al. A chemical extraction method for mimicking bioavailability of polycyclic aromatic hydrocarbons to wheat grown in soils containing various amounts of organic matter
[J]. Environmental Science and Technology, 2006, 40: 2219-2224.
[31] Bogolte B J, Ehlers G A C, Braun R, et al. Estimation of PAH bioavailability to Lepidium sativum using sequential supercritical fluid extraction-a case study with industrial contaminated soils
[J]. European Journal of Soil Biology, 2007, 43: 242-250.
[32] Huckins J N, Tubergen M W, Manuweera G K. Semipermeable membrane devices containing model lipid: A new approach to monitoring the bioavailability of lipophilic contaminants and estimating their bioconcentration potential
[J]. Chemosphere, 1990, 20: 533-552.
[33] Gourlay C, Miege C, Noir A, et al. How accurately do semi-permeable membrane devices measure the bioavailability of polycyclic aromatic hydrocarbons to Daphnia magna?
[J] Chemosphere, 2005, 61: 1734-1739.
[34] Tao Y, Zhang S Z, Wang Z, et al. Predicting bioavailability of PAHs to wheat roots grown in field-contaminated soils with triolein embedded cellulose acetate membranes and comparison with chemical extraction
[J]. Journal of Agricultural and Food Chemistry, 2008, 56, 10817-10823.
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