Table 10.3
(continued)
References
Target compound/initial
concentration
Water
matrix
Process conditions
parameters
Scale
Measure of degradability
Summary results
He et al.
(2016)
IBP, CBZ and DCF at
5 mg/L
Real
wastewater
Immobilized TiO
2 on quartz
sand by sol-gel
Irradiation source:
Xe-lamps (55 W)
Irradiation time: 96 h
Bench
Target compounds, DOC,
DBO and toxicity
Chronic toxicity of compounds decreased for the
green algae and bluegreen algae. In addition,
the biodegradability of
wastewater spiked with
pharmaceuticals compounds was slightly
improved
Carbajo et al.
(2016)
IBP and CBZ at 100
μg/L Natural
ground
water
Solar photocatalysis: TiO
2
P25 (200 mg/L) and homemade TiO
2 catalyst TiEt-450
(500 mg/L)
Organic pollutants: Phenol, dichloroacetic acid and
pyrimethanil
Pilot
plant
Target compounds, TOC
and ions
Pharmaceutical
microcontaminants were
efficiently treated with
very short irradiation
times (t
30w < 35 min)
with both titania catalysts
Homogeneous processes
Heberer
(2007)
CBZ and DCF at 1
μg/L
Real
waterworks
Ozone doses in the range of
0.5–3.0 mg/L
DOC
¼ 1.3 mg/L
pH
¼7.8
T
¼ 23
C
Bench
Target compounds
In lab scale experiments,
0.5 mg/L ozone was
shown to reduce the concentrations of DCF and
CBZ by more than 90%
Huber et al.
(2003)
IBP and DCF at 0.5 to
5
μg/L
Real
municipal
wastewater
Ozonation
O
3 doses ranging from 0.5 to
5 mg/L
Gas
flow rate:
200
Æ 10 L h
À1
Pilot
plant
Target compounds and
DOC
Pharmaceuticals presents
in wastewater can be
efficiently oxidized with
O
3 and that suspended
solids have only a minor
influence on the
oxidation
322
E. M. Saggioro
(continued)
References
Target compound/initial
concentration
Water
matrix
Process conditions
parameters
Scale
Measure of degradability
Summary results
He et al.
(2016)
IBP, CBZ and DCF at
5 mg/L
Real
wastewater
Immobilized TiO
2 on quartz
sand by sol-gel
Irradiation source:
Xe-lamps (55 W)
Irradiation time: 96 h
Bench
Target compounds, DOC,
DBO and toxicity
Chronic toxicity of compounds decreased for the
green algae and bluegreen algae. In addition,
the biodegradability of
wastewater spiked with
pharmaceuticals compounds was slightly
improved
Carbajo et al.
(2016)
IBP and CBZ at 100
μg/L Natural
ground
water
Solar photocatalysis: TiO
2
P25 (200 mg/L) and homemade TiO
2 catalyst TiEt-450
(500 mg/L)
Organic pollutants: Phenol, dichloroacetic acid and
pyrimethanil
Pilot
plant
Target compounds, TOC
and ions
Pharmaceutical
microcontaminants were
efficiently treated with
very short irradiation
times (t
30w < 35 min)
with both titania catalysts
Homogeneous processes
Heberer
(2007)
CBZ and DCF at 1
μg/L
Real
waterworks
Ozone doses in the range of
0.5–3.0 mg/L
DOC
¼ 1.3 mg/L
pH
¼7.8
T
¼ 23
C
Bench
Target compounds
In lab scale experiments,
0.5 mg/L ozone was
shown to reduce the concentrations of DCF and
CBZ by more than 90%
Huber et al.
(2003)
IBP and DCF at 0.5 to
5
μg/L
Real
municipal
wastewater
Ozonation
O
3 doses ranging from 0.5 to
5 mg/L
Gas
flow rate:
200
Æ 10 L h
À1
Pilot
plant
Target compounds and
DOC
Pharmaceuticals presents
in wastewater can be
efficiently oxidized with
O
3 and that suspended
solids have only a minor
influence on the
oxidation
322
E. M. Saggioro