Techniques of mathematical analysis by Tranter C.J.

By Tranter C.J.

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G. 2004, Overview and comparison of lipid-containing semipermeable membrane devices (SPMDs) and oysters (Crassostrea gigas) for assessing chemical exposure. Environ. Toxicol. Chem. 23: 1617–1628. D. S. 1992, Viability of glochida of two species of Anodonta exposed to low pH and selected metals. Can. J. Zool. 70: 2348–2354. Hwang, S-T. and Kammermeyer, K. 1984, Membranes in Separations. Krieger Publishing: Malabar, FL. P. 1995, Passive sampling devices for rapid determination of soil contaminant distributions.

Sci. Technol. 35: 1425–1431. N. 1992, Rapid characterization of pesticide residues in contaminated soils by passive sampling devices. Environ. Toxicol. Chem. 11: 765–770. Zabik, M. 1988, Michigan State University, East Lansing, MI. Personal communication. 1. SPMD DESCRIPTION AND RATIONALE From the discussions thus far, the reader can infer that SPMDs are designed to mimic the passive diffusional and partitioning steps of bioconcentration while providing semi-quantitative to quantitative estimates of hydrophobic organic chemicals (HOC) concentrations in the ambient exposure medium.

1997, Field-portable solid-phase microextraction/fast GC system for trace analysis. Field Anal. Chem. Tech. 1: 227–284. Harner, T. F. 1996, Measurements of octanol-water partition coefficients for polychlorinated biphenyls. J. Chem. Eng. Data. 41: 895–899. C. 2003, Characterization of polymercoated glass as a passive air sampler for persistent organic pollutants. Environ. Sci. Technol. 37: 2486–2493. ; Song, H. 1989, A Passive In situ Sampler for Organic Compounds in Water. Extended Abstracts of the 198th National Meeting of American Chemical Society; Miami Beach, FL; 5: 496–397.

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