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Published online 19 April 2006
Published in Soil Sci Soc Am J 70:995-1004 (2006)
DOI: 10.2136/sssaj2005.0098
© 2006 Soil Science Society of America
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Nuclear Magnetic Resonance Based Investigations of Contaminant Interactions with Soil Organic Matter

Myrna J. Simpson*

Dep. of Physical and Environmental Sciences, Univ. of Toronto, Scarborough College, 1265 Military Trail, Toronto, ON M1C 1A4, Canada


Figure 1
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Fig. 1. A proposed multitiered approach to studying organic contaminant interactions with soils. Most investigations occur at the landscape or macroscopic-level; however, combining all three approaches will result in a fundamental understanding of contaminant fate in terrestrial environments.

 

Figure 2
Figure 2
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Fig. 2. An illustration of (A) macroscopic-level and (B) molecular-level data. Macroscopic data has yielded a multitude of indirect hypotheses which are now being refined with the application of direct, molecular-level observations. Macroscopic methods commonly employ batch equilibration experiments that produce sorption isotherms (note: not all sorption isotherms are nonlinear; linearity varies with sorbate and sorbent properties and the type of mechanisms that are dominating the attenuation process). Molecular-level studies enable sorption mechanisms, such as those between trifluralin and SOM (adapted from Simpson et al., 2001). Two-dimensional molecular-level data, such as correlation spectroscopy NMR of a soil humic acid, displayed from Simpson et al. (2004), can provide detailed structural information about humic material and can be used to decipher specific SOM interactions with contaminants. Reprinted with permission from Simpson et al. (2004). Copyright (2004) Environmental Toxicology and Chemistry, Alliance Communications Group.

 

Figure 3
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Fig. 3. Solid-state 13C CP/MAS NMR spectra of chemically modified humic acids from Simpson et al. (2003). The selective removal of SOM components suggests that structures such as polymethylene carbon may be blocked by other humic structures. Only through chemical modification do they become more available in contaminant interactions. Reprinted with permission from Simpson et al. (2003).

 

Figure 4
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Fig. 4. (A) Data from (Simpson et al., 2004) displaying the decline in 1H T1 values of 1-naphthol with increasing concentration of soil humic acid (HA). The measurements indicate that all protons are equally interacting and hence, a specific interaction between individual nuclei (1H in this example) and the HA is not observed, suggesting a strong interaction with all protons in the molecule with HA. (B) The aromatic region from the 1H spectrum does not reveal a change in chemical shift, suggesting that this is a strictly noncovalent interaction. The increased line broadening with the addition of 50 mg C L–1 of HA is indicative of a strong, noncovalent association. Reprinted with permission from Simpson et al. (2004). Copyright (2004) Environmental Toxicology and Chemistry, Alliance Communications Group.

 





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