SLIDE 1
Removal of organic matter and micro- pollutants using the ozone/BAC process for recycled water production Dr Julien Reungoat
M.J. Farré, M. Rattier, F.X. Argaud, W. Gernjak, J. Keller - AWMC B.I. Escher, M. Macova - Entox
Enhanced Treatment Project
Science Forum, 19-20 June 2012
Urban Water Security Research Alliance
SLIDE 2 Effluent organic matter in secondary effluent
Nutrient Removal WWTP Effluent
Effluent
Micropollutants DBPs precursors AOC Taste Odour Colour NOM
SLIDE 3 Effluent organic matter in secondary effluent
Nutrient Removal WWTP Non-potable reuse Indirect potable reuse Irrigation Membrane filtration Oxidation Adsorption Riverbank filtration Aquifer recharge Effluent
Effluent
Micropollutants DBPs precursors AOC Taste Odour Colour NOM
SLIDE 4 Ozone/BAC
O3
Effluent
matter
O3 BAC
SLIDE 5
The plants studied
Dissolved air flotation and sand filtration Pre-ozonation (~0.10 mgO3 /mgDOC ) Ozonation (0.6-0.8 mgO3 /mgDOC ) BAC (18 min) Ozone disinfection (~0.30 mgO3 /mgDOC ) BNR WWTP 40,000 EP - 8,000 m3/day
Plant A
Rapid sand filtration Ozonation (0.2-0.3 mgO3 /mgDOC ) BAC (9 min) UV disinfection BNR WWTP 10,000 EP - 2,000 m3/day Rapid sand filtration Ozonation (0.4-0.5 mgO3 /mgDOC ) BAC (45 min) MF membranes (0.2 µm) BNR WWTP 11,000 EP - 900m3/day UV disinfection
Plant B Plant C
Commissioned in 1999 Replaced in March 2008 ≈ 50,000 bed volumes Commissioned in 2003 ≈ 300,000 bed volumes Commissioned in 2002 Half replaced in 2009 ½ ≈ 95,000 bed volumes ½ ≈ 13,000 bed volumes
SLIDE 6 Water quality before ozonation
Plant A Plant B Plant C T (°C) 22.0 22.6 ‐ 28.5 ‐ pH 6.6 ‐ 6.7 6.7 ‐ 7.1 6.7‐ 6.9 Conductivity (µS) 879 ‐ 910 392 ‐ 507 519 ‐563 DOC (mg L‐1) 6.5 ‐ 8.1 5.8 ‐ 6.6 4.2 ‐ 5.8 PO4
3‐‐P (mg L‐1)
≤ 0.02 0.22 ‐ 2.00 < 0.02 NH4 ‐N (mg L‐1) < 0.03 0.22 ‐ 0.45 0.18 ‐ 1.36 NO2 ‐N (mg L‐1) < 0.02 0.03 ‐ 0.06 <0.02 ‐ 0.04 NO3 ‐N (mg L‐1) < 0.02 ‐ 0.95 0.18 ‐ 0.47 0.39 ‐ 1.14
SLIDE 7 Removal of DOC
Plant A Plant B Plant C T (°C) 22.0 22.6 ‐ 28.5 ‐ pH 6.6 ‐ 6.7 6.7 ‐ 7.1 6.7‐ 6.9 Conductivity (µS) 879 ‐ 910 392 ‐ 507 519 ‐563 DOC (mg L‐1) 6.5 ‐ 8.1 5.8 ‐ 6.6 4.2 ‐ 5.8 PO4
3‐‐P (mg L‐1)
≤ 0.02 0.22 ‐ 2.00 < 0.02 NH4 ‐N (mg L‐1) < 0.03 0.22 ‐ 0.45 0.18 ‐ 1.36 NO2 ‐N (mg L‐1) < 0.02 0.03 ‐ 0.06 <0.02 ‐ 0.04 NO3 ‐N (mg L‐1) < 0.02 ‐ 0.95 0.18 ‐ 0.47 0.39 ‐ 1.14
SLIDE 8 Micropollutants
41 targeted compounds:
- Mainly PPCPs and a few pesticides.
- Wide range of physico-chemical properties.
- Some known to be easily removed in WWTP, others not.
SLIDE 9 Micropollutants
Plant A Plant B Plant C Quantified 35 38 36 < LOQ 3 1 5 Not quantifiable 3 2
Concentrations ranged from a few ng/L to more than 1 µg/L. For a given compound, the concentration remained in the same
- rder of magnitude regardless of sampling date and plant sampled.
41 targeted compounds:
- Mainly PPCPs and a few pesticides.
- Wide range of physico-chemical properties.
- Some known to be easily removed in WWTP, others not.
SLIDE 10
Removal of micropollutants: ozonation
O3 reactive compounds Low reactivity compounds
SLIDE 11
Removal of micropollutants: BAC
>80% >80% 20 - 80% 20 - 80% <20% <20%
Onesios et al., 2009 in Biodegradation, 20(4), 441-466
SLIDE 12 2 , 4
A c e t a m i n
h e n A t e n
C a f f e i n e C a r b a m a z e p i n e C i t a l
r a m D i a z i n
D i c l
e n a c D i u r
D
y l a m i n e E r y t h r
y c i n F u r
e m i d e G e m f i b r
i l H y d r
h l
h i a z i d e I b u p r
e n M e t
r
N a p r
e n P e r i n d
r i l P h e n y t
n P r
r a n
R a n i t i d i n e R
i t h r
y c i n S e r t r a l i n e S u l p h a m e t h
a z
e T r a m a d
T r i c l
y r T r i m e t h
r i m V e n l a f a x i n e W a r f a r i n
Removal (%) 20 40 60 80 100 Plant A Plant C Plant B
Removal of micropollutants: O3 +BAC
SLIDE 13 Bioanalytical tools
Microtox:
- non-specific toxicity
- takes into account all micropollutants, by-products,…
- expressed as baseline-TEQ (mg/L)
E-screen:
- estrogenicity
- expressed as estradiol equivalent concentration (EEQ)
- limit of quantification = 0.01 ng/L
Plant A Plant B Plant C Baseline-TEQ (mg/L) 1.83 - 2.72 1.50 - 2.01 1.10 - 1.84 EEQ (ng/L) 0.98 - 1.73 1.13 - 1.44 0.57 - 1.53
SLIDE 14 Toxicity removal
- Effect of ozonation similar in the three plants
- Effectiveness of BAC increased from 9 to 18 minutes EBCT
but not further
SLIDE 15 Toxicity removal
- Ozonation very effective (estrogenic moieties are very
reactive with molecular ozone)
- Effectiveness of BAC difficult to assess due to low levels
SLIDE 16
Disinfection by-products precursors
Formation potential (µg/L)
Chloroform 224±21 Bromodichloromethane 53±6 Dibromochloromethane 11±2 Bromoform < 1 Total THMs 289±26 Monochloroacetic acid < 10 Dichloroacetic acid 154±32 Trichloroacetic acid 143±17 Bromochloroacetic acid 30±6 Monobromoacetic acetic < 5 Dibromoacetic acid < 5 Total HAAs 327±53 NDMA (ng/L) 327±22 THMs HAAs
THMs HAAs NDMA
FP reduction (%)
20 40 60 80 O3
SLIDE 17
Disinfection by-products precursors
Formation potential (µg/L)
Chloroform 224±21 Bromodichloromethane 53±6 Dibromochloromethane 11±2 Bromoform < 1 Total THMs 289±26 Monochloroacetic acid < 10 Dichloroacetic acid 154±32 Trichloroacetic acid 143±17 Bromochloroacetic acid 30±6 Monobromoacetic acetic < 5 Dibromoacetic acid < 5 Total HAAs 327±53 NDMA 327±22 THMs HAAs
THMs HAAs NDMA
FP reduction (%)
20 40 60 80 O3+BAC O3
SLIDE 18 Take home messages
- Ozonation:
- removal of OMPs depends on compound and ozone dose
- reduction of non-specific toxicity
- > 90% reduction of estrogenicity
- removal of NDMA precursors
- Biological activated carbon:
- removes OMPs
- reduces non-specific toxicity / removes O3 by-products
- removal of THMs and HAAs precursors
- Combination:
- > 90% removal of OMPs
- up to 70% reduction of non-specific toxicity
- > 90% reduction of estrogenicty (<0.01 ng/L EEQ)
- removal of DBPs precursors
SLIDE 19
Acknowledgements
Wolfgang Gernjak François Xavier Argaud Maria Jose Farré Maxime Rattier Jurg Keller Jelena Radjenovic Beatrice Keller Beate Escher Miroslava Macova Yvan Poussade
SLIDE 20
Urban Water Security Research Alliance THANK YOU www.urbanwateralliance.org.au