Sorption of the neutral and charged forms of pentachlorophenol on soil: Evidence for different mechanisms

被引:74
作者
DiVincenzo J.P. [1 ]
Sparks D.L. [2 ]
机构
[1] Department of Chemistry, Middle Tennessee State University, Murfreesboro, TN 37132
[2] Dept. of Plant and Soil Sciences, University of Delaware, Newark
关键词
Isotherm Model; Langmuir Model; Sorption Experiment; Neutral Form; Neutral Species;
D O I
10.1007/s002440010196
中图分类号
学科分类号
摘要
Laboratory soil sorption experiments have been conducted on pentachlorophenol (PCP) at different pH values in an attempt to elucidate differences in sorption mechanisms between the charged and neutral species. Sorption of PCP on soil was investigated by maintaining pH 4 or 8 in batch sorption experiments. Pre-equilibration of the soil was necessary to maintain a constant pH over the course of the experiments. Additionally, a CaCO3-CO2/N2 buffered solution was necessary to maintain a pH of 8. Sorption of the neutral pCP species conformed to a linear isotherm model, while a Langmuir model provided the best fit for the charged species. Desorption of the neutral form was completely reversible over the sorption times studied but the charged species exhibited some resistance to desorption. Temperature effects on the distribution coefficients (Kd) were investigated and thermodynamic parameters were calculated. The ionized species showed a clear decrease in Kd with increasing temperature while the protonated species showed no apparent trend. Enthalpies (ΔH°), entropies (ΔS°), and free energies (ΔG°), support the conclusions that the neutral form of PCP partitions by hydrophobically binding to the soil while the charged form sorbs by a more specific exothermic adsorption reaction.
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页码:445 / 450
页数:5
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共 34 条
  • [1] Ball W.P., Roberts P.V., Long-term sorption of halogenated organic chemicals by aquifer material. 2. Intraparticle diffusion, Environ Sci Technol, 25, 7, pp. 1223-1236, (1991)
  • [2] Banerji K.S., Piontek K., O'Connor J.T., Pentachlorophenol adsorption on soils and its potential for migration into ground water, Hazardous and Industrial Solid Waste Testing and Disposal, 6, pp. 120-139, (1986)
  • [3] Brucher J., Bergstrom L., Temperature dependence of linuron sorption to three different agricultural soils, J Environ Qual, 26, 5, pp. 1327-1335, (1997)
  • [4] Brusseau M.L., Jessup R.E., Rao P.S.C., Nonequilibrium sorption of organic chemicals: Elucidation of rate-limiting processes, Environ Sci Technol, 25, 1, pp. 134-142, (1991)
  • [5] Cancela G.D., Taboada E.R., Sanchez-Rasero F., Carbendazim adsorption on montmorillonite, peat and soil, J Soil Sci, pp. 4399-5111, (1992)
  • [6] Christodoulatos C., Mahiuddin M., Generalized models for prediction of pentachlorophenol adsorption by natural soils, Water Environ Res, 68, 3, pp. 370-378, (1996)
  • [7] Curl R.L., Keolelan G.A., Implicit-adsorbate model for apparent anomalies with organic adsorption on natural adsorbents, Environ Sci Technol, 18, 2, pp. 916-922, (1984)
  • [8] Di Toro D.M., Horzempa L.M., Reversible and resistant components of PCB adsorption-desorption: Isotherms, Environ Sci Technol, 16, 9, pp. 594-602, (1982)
  • [9] DiVincenzo J.P., Slow Sorption Kinetics of Pentachlorophenol on Soil, (1996)
  • [10] DiVincenzo J.P., Sparks D.L., Slow sorption kinetics of pentachlorophenol on soil: Concentration effects, Environ Sci Technol, 31, 4, pp. 977-983, (1997)