The solubility and
bioavailability of arsenic in the environment
are to a large extent governed by adsorption reactions with iron (hydr)oxides,
the extent of which is affected by competitive interactions with other
ions, for example, phosphate. Here, batch experiments were performed
with ferrihydrite suspensions to determine the adsorption of arsenate
[As(V)] and phosphate (PO4) at different As(V)–PO4 ratios. A surface complexation model based on the Charge
Distribution MUltisite Ion Complexation (CD-MUSIC) concept (the “Ferrihydrite
CD-MUSIC model”) was developed to describe these interactions
in a way consistent with results from spectroscopic studies. For this
purpose, several previously published data sets on As(V) and PO4 adsorption in ferrihydrite suspensions were reviewed, including
a number of systems containing other major ions (CO3
2– and Ca2+), and new surface complexation
constants were derived. During model development, it was found that
the inclusion of ternary complexes was not needed to describe the
observed Ca2+–PO4 interactions. For both
As(V) and PO4, the resulting model predicts the presence
of corner-sharing bidentate complexes as well as monodentate complexes,
with the latter being important particularly at low pH. The experimental
results showed that As(V) and PO4 displayed similar adsorption
patterns in the single-ion systems studied, which were conducted using
a constant anion-to-Fe ratio of 0.2. Even so, As(V) was preferentially
adsorbed over PO4 in competitive systems, particularly
at low As(V)-to-PO4 ratios when the K
d values for As(V) were up to 2.1 times as high as those for
PO4. The model, which described these patterns very well,
suggests that adsorbed As(V) consists of a larger fraction of bidentate
complexes than in the case of PO4. This causes a flatter
adsorption isotherm for As(V), which leads to a stronger As(V) adsorption
as the As(V)-to-Fe ratio decreases, compared to that for PO4.