NOM removal in artificial waters From batch experiments to model April – July 2009 Leonard Galais...
-
date post
19-Dec-2015 -
Category
Documents
-
view
214 -
download
0
Transcript of NOM removal in artificial waters From batch experiments to model April – July 2009 Leonard Galais...
NOM removal in artificial watersFrom batch experiments to model
April – July 2009
Leonard Galais
Supervisor : Anke Grefte
1/11
What is NOM ?
assimilable organic carbon over the treatment plant
0
20
40
60
80
100
120
140
influentozone
influentsoftening
influentactivatedcarbon
influentslow sandfiltration
clear water
AOC (ug/L)
•The Orange – brown color of water is mainly due to NOM
•NOM is everywhere from the treatment plant to the sewerage
network
•NOM is a complex and highly heterogeneous mixture of organic
compounds
•Humic and Fulvic acids stand for the major part of NOM
•NOM is entirely due to chemical and biological degradation organics
compounds
•NOM is negatively charged
09-07-2009
2/11
What is IEX ?
•The most efficient way to remove dissolved ionic constituents
•LEWATIT® and MIEX®
•strong base activity
•macro porous structure
•pre-treatment of raw water with efficient IEX resins may increase by a factor 10 the life time of downstream
GAC filters (A. Grefte, 2007) Zoom on IEX particules
09-07-2009
Aims
3/1109-07-2009
•Is it possible to measure and identify the different humic substances with S::can and DOC?
•How are they removed by IEX?
4/11
S::canMeasuring UV254 absorbance
UV254
0
2
4
6
8
10
12
14
16
solutions
ad
s (
1/c
m)
09-07-2009
5/11
DOC measurementsA different point of view
0
2
4
6
8
10
12
14
16
SRHA-5
SRFA-5
NAHAR-5
NAFAR-5
OA-0,5
AA-0,5
FA-0,5
SRHA-3
SRFA-3
NAHAR-3
NAFAR-3OA-1
AA-1FA-1
0
0,5
1
1,5
2
2,5
UV254
DOC
09-07-2009
0
2
4
6
8
10
12
14
16
0
0,5
1
1,5
2
2,5
UV254
DOC
ads acids
0
2
4
6
8
10
12
14
16
18
20
200 300 400 500 600 700 800
NAHAR-3 AV
OA-10 AV
FA-10 AV
FA-5 AV
AA-10 AV
AA-5 AV
NAHAR-4 AV
NAHAR-2 AV
NAFAR-4 AV
NAFAR-2 AV
SRHA-4 AV
SRHA-2 AV
SRFA-4 AV
SRFA-2 AV
6/11
Untreated solutions - 1 ADS
-1
0
1
2
3
4
5
6
255 322,5 447,5 572,5 697,5
UV lenght
Ad
s
OA - 1
OA - 5
DEMIW
OA - 0,5
ADS fulvic acids / humic acids
0
10
20
30
40
50
60
70
80
200 325 450 575 700
UV lenght
Ad
s
NAFAR 5 AV
NAHAR 5 AV
SRFA 5 AV
SRHA 5 AV
Comparing artificial solutions of acids
09-07-2009
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
0 1 2 3 4 5 6 7 8 9 10 11
concentration (mg/ L)
ad
s (
1/c
m)
SRHA
SRFA
NAHAR
NAFAR
7/11
Untreated solutions - 2 Comparing curves and Looking for relations
09-07-2009
Is it possible to predict the UV spectrum of an unknown concentration solution by combination ?
0
1
2
3
4
5
6
7
8
9
10
200 300 400 500 600 700 800
wavelenght (nm)
ad
s (
cm
-1)
NAHAR 5-3
NAHAR-2 AV
Error : 22%
8/11
Batch experiments - 1UV254 absorbance over the time
09-07-2009
Adsorbance over the time for 10 mg/L solutions of humic and fulvic acids
8
10
12
14
16
18
20
22
24
26
28
30
0,00 10,00 20,00 30,00 40,00 50,00 60,00
time (hours)
ad
s (
1/c
m)
SRHA SRFA NAHAR NAFAR
67%
37%
26%
60%
NAFAR A series
05
1015202530
samples
UV
(1/c
m)
0123456
DOC (mg/L)
UV AV
DOC value
9/11
Batch experiments - 2Influence of the resin amount
resin efficiency
0
5
10
15
20
25
30
35
40
0 100 200 300 400 500 600 700
amount of resin (mg) in 1/2L
UV
ad
s (1
/cm
) SRHA
SRFA
NAHAR
NAFAR
09-07-2009
10/11
ModelingAre we able to predict breakthrough curves ?
09-07-2009
SRHA predicted breakthrough curve
Conclusions
11/11
• Acids are not measurable with UV, neither with DOC.
• DOC and UV measurements are different for Humic and Fulvic substances.
• Fulvic substances are better removed by IEX.• To remove 50% of NOM, you may regenerate IEX
every 3 weeks at least.
09-07-2009
NOM removal in artificial watersFrom batch experiments to model
April – July 2009
Leonard Galais
Supervisor : Anke Grefte