The role of humic non-exchangeable binding in the promotion of metal ion transport in groundwaters in the environment.
Metal ions form strong complexes with humic substances. When the metal ion is first complexed by humic material, it is bound in an 'exchangeable' mode. The metal ion in this fraction is strongly bound, however, if the metal-humic complex encounters a stronger binding site on a surface, then the metal ion may dissociate from the humic substance and be immobilised. However, over time, exchangeably-bound metal may transfer to a 'non-exchangeable' mode. Transfer into this mode and dissociation from it are slow, regardless of the strength of the competing sink, and so immobilisation may be hindered. A series of coupled chemical transport calculations has been performed to investigate the likely effects of non-exchangeable binding upon the transport of metal ions in the environment. The calculations show that metal in the non-exchangeable mode will have a significantly higher mobility than that in the exchangeable mode. The critical factor is the ratio of the non-exchangeable first-order dissociation rate constant and the residence time in the groundwater column, metal ion mobility increasing with decreasing rate constant. A second series of calculations has investigated the effect of the sorption to surfaces of humic/metal complexes on the transport of the non-exchangeably bound metal. It was found that such sorption may reduce mobility, depending upon the humic fraction to which the metal ion is bound. For the more weakly sorbing humic fractions, under ambient conditions (humic concentration etc.) the non-exchangeable fraction may still transport significantly. However, for the more strongly sorbed fractions, the non-exchangeable fraction has little effect upon mobility. In addition to direct retardation, sorption also increases the residence time of the non-exchangeable fraction, giving more time for dissociation and immobilisation. The non-exchangeable dissociation reaction, and the sorption reaction have been classified in terms of two Damkohler numbers, which can be used to determine the importance of chemical kinetics during transport calculations. These numbers have been used to develop a set of rules that determine when full chemical kinetic calculations are required for a reliable prediction, and when equilibrium may be assumed, or when the reactions are sufficiently slow that they may be ignored completely.
Bryan
Nick D
ND
Centre for Radiochemistry Research, School of Chemistry, University of Manchester, Oxford Road, Manchester, UKM13 9PL. nick.bryan@manchester.ac.uk
Jones
Dominic L M
DL
Keepax
Rose E
RE
Farrelly
Dean H
DH
Abrahamsen
Liam G
LG
Pitois
Aurelien
A
Ivanov
Peter
P
Warwick
Peter
P
Evans
Nick
N
D006812:Humic Substances; D007700:Kinetics; D008670:Metals / Q000737:chemistry*; D008956:Models, Chemical; D009716:Numerical Analysis, Computer-Assisted; D014875:Water Pollutants, Radioactive / Q000737:chemistry*
D006812:Humic Substances; D008670:Metals; D014875:Water Pollutants, Radioactive