Pharmaceutical Active Compounds Removal by Constructed ... · removals •Plant role in the...
Transcript of Pharmaceutical Active Compounds Removal by Constructed ... · removals •Plant role in the...
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AHMED F. HAMADEH1
PIET LENS2 AND GARY AMY1 1KING ABDULLAH UNIVERSITY OF SCIENCE AND
TECHNOLOGY (KAUST), SAUDI ARABIA. 2 UNESCO-IHE INSTITUTE FOR WATER
Pharmaceutical Active Compounds Removal
by Constructed Wetlands
Under Different Redox Conditions
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Outlines
• Objectives and Methodologies
• Set-up preparation
• WW Composition
• Feeding water quality
• Organic matters and nutrients removal
• Organic matters characterization
• OMPs properties and removals
• Plant role in the treatment
• Conclusions
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• Study removal processes of nutrients (C, N & P) through CWs under different Redox conditions.
• Assess the removal efficiency of nutrients and selected group of Organic Micropollutants (OMPs) through CWs.
• Specify the plants role in the wastewater treatment during
horizontal Subsurface flow constructed wetlands.
• Build lab scale subsurface flow CWs
and study the performance for different
nutrients and OMPs present in
wastewaters, planted with Phragmites
australis plant and feed with 2° Eff.
synthetic ww.
Study Objectives
Methodology
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Sand
Gravel
(Non-aeratedControl)
Sand
Gravel
SandGravel
W.Inffl
Air
Sand
Gravel
Sand
Gravel
Sand
Gravel
Sand
Gravel
Sand
Gravel
(AeratedControl)
CW3
CW2
CW1
Hydraulic Loading Rate: 4.6 cm/d Hydraulic Retention Time: 1 d/each
Flow direction
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C Setup Preparation
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Phragmites australis plant harvesting
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Synthetic WW composition
(Source: Jiang, T. (2007) Characterization and modelling of soluble microbial products in membrane bioreactors. PhD thesis, Ghent Un., Belgium.
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Synthetic WW composition
(Source: Jiang, T. (2007) Characterization and modelling of soluble microbial products in membrane bioreactors. PhD thesis, Ghent Un., Belgium.
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Feeding water quality
Parameter Unit Concentration
DOC mg/l 9.61 ± 1.5
TN mg/l 8.35 ± 0.87
NO3- as N mg/l 3.63 ± 0.25
NH4+ as N mg/l 1.98 ± 0.67
Organic N. mg/l 2.83 ± 0.87
SO4-2 mg/l 12.33 ± 2
Specific UV Abs. l/mg.m 0.23± 0.04
COD mg/l 41
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DOC and TN changes in the influents
Aerated influents
Influent DOC (mg/L)
TN (mg/L)
CW1
9.61
8.35
CW2
0.81
1.48
CW3
0.82
0.9
Non-aerated influents
Influent
DOC (mg/L)
TN (mg/L)
Cw1
9.61
8.35
CW2 0.59
2.17
CW3
0.74
1.34
FLOW
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Total % Removal for DOC
78.00
80.00
82.00
84.00
86.00
88.00
90.00
92.00
94.00
96.00
98.00
Non Aerated CW3 Aerated CW3
% R
em
ova
l
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Total % Removal for TN, NO3-, NO2
- and NH3+
-150.00
-100.00
-50.00
0.00
50.00
100.00
TN NO3-N NO2-N NH3-N
% R
em
ova
l
Non Aerated CW3
Aerated CW3
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Organic Nitrogen % Removal
88
90
92
94
96
98
100
NA Control NA CW1 A. Control A. CW1
% R
emo
val
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Total % removal of Phosphate & Sulfate
0.00
10.00
20.00
30.00
40.00
50.00
60.00
70.00
80.00
90.00
NA CW3 A. CW3
% R
emo
val
PO4
SO4
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Fluorescence excitation and emission matrix (FEEM)
FEEM spectra analysis is a tool that helps to investigate which fractions of DOC are available in the water samples
Region Excitation (nm) Emission (nm) Description
1 320-350 400-480 Humic/Fulvic-
like organic
matter
fraction
2 240-280
430-480
Humic-like
organic matter
fractions
3 250-270 320-360 Protein-like
organic matter
fractions
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The organic matters fraction in the influent are proteins like only but the effluents are containing Humic/ Fulvic like organic matter fractions
A. CW3
Influent
NA CW3
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Peak 3
Protein-like
organic
matter
fractions
Source Excitation
(nm) Emission
(nm) Intensity
Reduction in intensity
(%)
A CW1 275 355 8250 85
NA CW1 275 355 8250 85
A Control 275 355 6250 89
NA Control 275 355 17250 69
A CW3 275 355 11250 80
NA CW3 275 355 7500 86
Fluorescence EEM analysis of influent and effluent
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Specific UV Abs. Changes
0.00
0.50
1.00
1.50
2.00
2.50
3.00
3.50
4.00
Inffl1 NA CW1 NA CW2 NA CW3 A CW1 A CW2 A CW3
SUV
A (
L/m
g.m
)
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Chloride concentrations changes through CWs
0
0.2
0.4
0.6
0.8
1
1.2
1.4
1.6
1.8
2
NA CW3 NA CW2 NA CW1 Inffluent A.CW1 A.CW2 A.CW3
Effl
ue
nt/
Inff
lue
nt
Because of 1. Plant water uptake
2. Evaporation
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Physical-chemical properties of OMPs
No OMPs Name Conc (ng/l) M. Wt (g/mol) Kow pka
1 Acetaminophen 268 151.2 0.46 9.38
2 Atenolol 1927 266.34 0.16 9.6
3 Caffeine 831 194.1 -0.07 10.4
4 Fluoxetine 225 309.1 4.05 10.3
5 Sulfamethoxazole 322 253.3 0.89 5.5
6 Trimethoprim 651 290.1 0.91 7.12
7 Atrazine 546 215.7 2.61 1.7
8 Carbamazepine 649 236.1 2.45 13.9
9 DEET 387 191.1 2.18 0.67
10 Dilantin
248 252.3 2.47 8.33
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% Removal of OMPs through CW1 (1)
40.00
50.00
60.00
70.00
80.00
90.00
100.00
% R
emo
val
A. CW1 (d1)
NA. CW1 (d1)
A. CW1
NA. CW1
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% Removal of OMPs through CW1 (2)
-10.00
0.00
10.00
20.00
30.00
40.00
50.00
60.00
Atrazine Carbamazepine DEET Dilantin
% R
emo
val
A. CW1 (d1)
NA. CW1 (d1)
A. CW1
NA. CW1
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Total % Removal of OMPs (1)
60.00
65.00
70.00
75.00
80.00
85.00
90.00
95.00
100.00
% R
emo
val
Aereated (d1)
Non- Aereated (d1)
Aereated
Non- Aereated
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Total % Removal of OMPs (2)
-10.00
10.00
30.00
50.00
70.00
90.00
110.00
% R
emo
val
Aereated (d1)
Non- Aereated (d1)
Aereated
Non- Aereated
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% Removal of OMPs in Un-Planted CWs (1)
-20.00
0.00
20.00
40.00
60.00
80.00
100.00
Acetaminophen Atenolol Caffeine Sulfamethoxazole Trimethoprim
% R
emo
val
NA Control (d1)
A. Control (d1)
NA Control
A. Control
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% Removal of OMPs in Un-Planted CWs (2)
0.00
10.00
20.00
30.00
40.00
50.00
60.00
70.00
80.00
Atrazine Carbamazepine DEET Dilantin Fluoxetine
% R
emo
val
NA Control (d1)
A. Control (d1)
NA Control
A. Control
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What is the plant role Phragmites australis in CWs???
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Nutrients reduction by the plant
0
10
20
30
40
50
60
70
80
90
100
NO3 TN Org. N PO4 SO4
% R
emo
val
NA Control
NA CW1
Reduction by plant
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Ammonia reduction by the plant
-180
-130
-80
-30
20
70
120
170
220
270
NA Control NA CW1 Reduction by plant
% R
emo
val
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OMPs reduction by the plant
-20
0
20
40
60
80
100
120
% R
emo
val
NA. CW1
NA Control
Reduction by plant
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Conclusions (1) Achievable Removals are: DOC (95%), TN (75%),
NH3+(99%), org N.(98%), and PO4
-3 (73%).
Plants “e.g. phragmites australis” in CWs play an essential role in the treatment especially for nitrogen and phosphates removals during secondary wastewater treatment. It removes; 15% (TN), 55% (Org. N.), 38% (NO3
-), and phosphate (22%).
The Plant also contributes effectively in removals of some OMPs such as: Acetaminophen, Caffeine, Fluoxetine, Sulfamethoxazole, and Trimethoprim.
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Conclusions (2) Caffeine, Atrazine, Carbamazepine and Dilantin
showed better removals under Non Aerated conditions.
Humics and fulvic like organic matter where found in the effluents (especially in aerated row because of plant degradation.
Providing air gas to CWs systems enhances phosphate removal.
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Thank You
and
Any
Question?