Am. Scheidegger et al., MECHANISMS OF NICKEL SORPTION ON PYROPHYLLITE - MACROSCOPIC AND MICROSCOPIC APPROACHES, Soil Science Society of America journal, 60(6), 1996, pp. 1763-1772
Retention of heavy metal ions on soil mineral surfaces is a crucial pr
ocess for maintaining environmental quality. A thorough understanding
of the sorption mechanisms of heavy metals on soil mineral surfaces is
therefore of fundamental importance. This study examined Ni(II) sorpt
ion mechanisms on pyrophyllite. The removal of Ni from solution was st
udied as a function of pH (pH = 5-8.5), initial Ni concentration (1 x
10(-4) to 1 x 10(-2) M), and ionic strength (0.01-1 M). The data sugge
st that Ni sorption behavior can be divided into two distinct pH regio
ns. In the lower pH region (i.e., pH <7), relative Ni sorption increas
ed with decreasing ionic strength and initial Ni concentration. The ad
sorption maximum at pH = 6 was significantly higher than the cation-ex
change capacity (CEC) at the same pH. Based on these findings, we prop
ose that both specific and nonspecific adsorption are involved. In the
higher pH region (pH >7), nickel sorption becomes slow and does not s
eem to be affected by the ionic strength and the initial Ni concentrat
ion. We employed high-resolution transmission electron microscopy (HRT
EM) to ascertain whether any alteration in the surface structure of py
rophyllite could be detected after reaction with Ni at pH >7. Surface
deposits, not present on untreated samples, were found. At low Ni sorp
tion densities, surface precipitation seems to occur preferentially al
ong the edges of the particles. Based on the HRTEM findings, and on re
sults from a previous x-ray absorption fine structure spectroscopy (XA
FS) study, we hypothesize that the formation of a mixed Ni-Al hydroxid
e phase on the pyrophyllite surface is responsible for the sorption be
havior above pH 7.