diffusion studies at surfaces and interfaces (Kalinichev et al., 2002) show that the
structure and surface composition of LDH control the fluid structure in the inter-
layer space, as well as the effective diffusion coefficients of surface-adsorbed species,
their surface lifetimes, and their rotational and translational dynamics.
Experimental adsorption isotherms, usually interpreted in terms of the classical
Langmuir or Freundlich models (Inacio et al., 2000), can yield adsorption capacity
coefficients. For amphoteric anions such as glyphosate (N-(phosphonome-
thyl)glycine) two different adsorbent/adsorbate interactions are identified: electro-
static adsorption and ligand exchange. Adsorption is limited to the external surface,
and the distribution coefficients (K
d
) depend on the pH of the solution (Sanchez
Martin et al., 1999). In a study of internal versus external uptake of anions, Boclair
et al. (2001) showed ferrocyanide does not displace interlayer carbonate from syn-
thetic hydrotalcite but is adsorbed on the outside of the particles. Anion uptake here
is controlled by specific hydrogen bonding requirements and not by charge density
alone, a feature that can be used to control whether uptake will be both internal and
external, or only external.
H. Synthesis of Polyoxometallate-LDH
Direct methods are not suitable for the preparation of oxoanion- and polyoxomet-
allate (POM)-containing LDH because of their ab ility to incorporate or precipitate
metal cations. Anion-exchange reactions are alternatively employed, requiring tight
control of solution pH (Don Wang et al., 1995; Rives and Ulibarri., 1999). Indeed,
the pH of exchange must be compatible with the domain of stabili ty of the hydroxy
layer and the anion to be intercalated. For example, complete exchange of chloride
by V
10
O
6
28
in [Zn–Al–Cl], [Zn–Cr–Cl], and [Ni–Al–Cl] using ½NH
4
6
½V
10
O
6
28
6H
2
O
must be carried out at pH ¼ 4.5 (Kwon et al., 1988; Doeuff et al., 1989; Malherbe
et al., 1997). At higher pH, carbonate intercalation may occu r preventing complete
exchange. Direct exchange of decavanadate in [Zn
2
–Al] can be facilitated by ultra-
sound treatment (Kooli et al., 1997b ). It is noteworthy that such pH co nditions are
not compatible with the existence of the basic LDH matrix ([Mg–Al], [Ca–Al]).
Silicate species in [Zn–Cr] and [Zn–Al] are intercalated either by anion exchange or
coprecipitation (Schu
¨
tz and Biloen, 1987; Depe
`
ge et al., 1996). The pH of the so-
lution must then be higher than 9.0 in order to prevent precipitation of undesirable
amorphous silicates and metal hydroxides.
Pillaring ions may also be intercalated through a reconstruction process (Miyata
and Hirose, 1978; Drezdon, 1988; Chibwe and Jones, 1989b; Dimotakis and
Pinnavaia, 1990; Ulibarri et al., 1994; Pinnavaia, 1995; Hibino and Tsunashima,
1997; Nijs et al., 1999).
An alternative method involves exchange in expanded, organic anion-containing
LDH (Drezdon, 1988; Dimotakis and Pinnavaia, 1990; Malherbe et al., 1997,
1998). Drezdon et al. (1988) were able to exchange decavanadate in [Mg–Al-ter-
ephtalate]. Terephtalate anions were previously introduced in the structure in order
Chapter 13.1: Layered Double Hydroxides1034