Fixed-bed column
adsorption studies are performed with metal-complexed
polyvinyl alcohol (PVA) hydrogel beads to remove fluoride from groundwater.
The fixed-bed column (bed height = 8 ± 0.2 cm) of copper–zirconium–PVA
(PCZH), zirconium–PVA (PZH), and iron–zirconium–PVA
(PFZH) hydrogel beads have equilibrium fluoride removal capacities
of 17.26 ± 0.05, 31.67 ± 0.05, and 11.84 ± 0.05 mg
g
–1
from a 10 ± 0.20 mg L
–1
fluoride solution of pH 6.5 maintained at a flow rate of 1 ±
0.01 mL min
–1
. The breakthrough curves for fluoride
adsorption are analyzed by non-linear empirical models of Thomas,
Bohart–Adams, Yoon–Nelson, and semi-empirical bed depth
service time models. The maximum fluoride adsorption capacities obtained
from the Thomas model are 25.66 ± 0.05, 38.17 ± 0.05, and
13.75 ± 0.05 mg g
–1
for PCZH, PZH, and PFZH.
Moreover, the column of PZH (bed height = 4 ± 0.2 cm) removes
about 1.67 ± 0.05 mg g
–1
of fluoride from the
alkaline groundwater sample with high total dissolved solids containing
2.84 ± 0.20 mg L
–1
fluoride maintained at a
flow rate of 0.5 ± 0.01 mL min
–1
. The fluoride
removal efficiency decreases marginally (<1 ± 0.02%) in the
presence of interfering ions such as chlorides, sulfates, phosphates,
bicarbonates, and nitrates. Furthermore, the fixed-bed column (bed
height = 4 ± 0.2 cm) of PCZH, PZH, and PFZH remove 7.40 ±
0.05, 14.85 ± 0.05, and 6.53 ± 0.05 mg g
–1
fluoride, respectively, even after the third regeneration cycle.
Additionally, the hydrogel beads are effective in the removal of arsenate
(≤90 ± 0.02%) and chromate ions (≤96 ± 0.02%)
from 100 ± 0.20 mg L
–1
solution in batch adsorption
studies. Therefore, the hydrogel beads could be used as potent filters
for the removal of fluoride, chromate, and arsenate ions from water.