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Combining methods for wastewater
treatment and proper re-use
www.safir4eu.org
proper re-use by water saving
irrigation
Mathias N AndersenDepartment of AgroecologyUniversity of Aarhus
Contents:
1. The SAFIR Project
2. Water Treatment Methods in SAFIR
3. Irrigation Methods in SAFIR
4. Field Scale Models
www.safir4eu.org
5. Impact Studies and Risk Assessment
6. Results on water saving irrigation
7. Conclusions so far
8. Acknowledgement
The SAFIR project :PNo. Participant name Participant
short name1 Danish Institute of
Agricultural SciencesDIAS
2 Consorzio di Bonifica di Secondo Grado per il Canale Emiliano Romagnolo
CER
3 Royal Veterinary and Agricultural University
KVL
4 Centre for Ecology & Hydrology
NERC, CEH
5 Bureau de Researches Geologique et Minieres
BRGM
6 London School of Hygiene & Tropical Medicine
LSHTM
7 Danish Research Institute of Food Economics
FOI
8 DHI Water and Environment
DHI
9 National Agricultural NAGREF
NEW IRRIGATION
TECHNOLOGIES
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9 National Agricultural Research Foundation
NAGREF
10 Swiss Federal Institute of Food Economics
EAWAG
11 Institute of Plant Physiology, Polish Academy of Sciences
IPP-PAS
12 Faculty of Agriculture, University of Belgrade
UB
13 China Agricultural University
CAU
14 Chinese Academy of Agricultural Sciences
CAAS
15 Netafim, Drip Irrigation Technology
Netafim
16 Stazione Sperimentale per l'Industria delle Conserve Alimentari
SSICA
17 Grundfos Management A/S Grundfos
IMPACT ON FOOD AND
ENVIRONMENT
APPLICATION
FEASIBILITY
Water treatment methods:Membrane Bio-Reactor (MBR) treating primary treated wastewater near Bologna:
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Water treatment methods:Results of Membrane Bio-Reactor (MBR) treatment:
COD
50
100
150
200
250
300
350
400
450
500
PWW
Permeate
Average production: 8.4 m3/d
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0
50
19/3 8/4 28/4 18/5 7/6 27/6 17/7 6/8 26/8 NO3
0
5
10
15
20
25
19-3 8-4 28-4 18-5 7-6 27-6 17-7 6-8 26-8
PWWPermeate
Water treatment methods:
Field Treatment System (FTS) used at 5 field sites for less polluted water:
Heavy Metals Dosing Pump
NETAFIM Gravel Filter
Gravel Filter Backflush
Heavy Metal Removal Device
150 mesh Screen Filter
UV disinfection
Fertigation Dosing Pump
All Sites Crete, CAAS, CAU
All Sites
All Sites
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INLET Proportional Like Device (Integrated Sampling Point)
Proportional Like Device (PE/PVC Storage tank)
OUTLET Proportional Like Device
(Integrated Sampling Point)
Proportional Like Device (PE/PVC Storage tank)
Crete, Serbia,
CAAS, CAUAll Sites
All Sites
All Sites
All Sites
Irrigation methods:
PTWW/MBR
SPRINKLER
SDI
Full Irrigated
Full Irrigated
PRD
PRD
TAP WATER
SPRINKLER
SDI
Full Irrigated
Full Irrigated
PRD
PRD
Dosing
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Partner 2 CER ItalyPotato + Processing Tomato
Tot 9 treatments - 27 plots per crop
STWW/FTS
SPRINKLER
SDI
Full Irrigated
Full Irrigated
PRD
PRD
PRDDosing
Dosing
75 cm
33,3
cm
75 cm
33,3
cm
75 cm
30.0 cm
Experimental Partial Root-zone Drying (PRD) drip system and its placement with respect to potato plants
Irrigation methods
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16,0 m
15,0 m
Irrigation methods:
SECONDARY
WASTE
WATER
PRIMARY
WASTE
WATER
TAP
WATER
POTATO + TOMATO
WATER SAVING IRR.
STRATEGIES
SPRINKLER
IRRIGATION
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FTS
FINISSAGGIO IN
CAMPO
FTS
FIELD TREATMENT
SYSTEM
MBR
HIGH EFFICIENCY
TREATMENT
POTATO + TOMATO POTATO + TOMATO
WATER SAVING IRR.
STRATEGIES
WATER SAVING IRR.
STRATEGIES
SUBSURFACE DRIP
IRRIGATION
RDI
SUBSURFACE DRIP
IRRIGATION
PRD
SUBSURFACE DRIP
IRRIGATION
RDI
SUBSURFACE DRIP
IRRIGATION
PRD
SPRINKLER
IRRIGATION
SUBSURFACE DRIP
IRRIGATION
RDI
SUBSURFACE DRIP
IRRIGATION
PRD
Field scale models
Two dynamic crop-soil-water-atmosphere simulation models:
-SALTMED
-Daisy
Strong features of the two models will be shared and extended with: (salt)
8 meristem
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-2D-simulation of soil processes
-Abscisic acid in plants as a function of PRD soil drying
-Stomatal regulation as a function of abscisic acid
-Transpiration as a function of stomatal opening (Penman-Monteith)
ABA root
ABA soil
ABA root
ABA soil
drying soilpHsaltcompaction
irrigated soilpHsaltcompaction
Impact studies and risk assessment
Safety of Food and Environment – Pathogens and Heavy Metals
Thermotolerantcoliforms
”Presumptive” indicators of pollution
E. coli, Enterobacter, Citrobacter
Helminth eggs
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Total coliforms95% is E. coli
Citrobacter, Enterobacter, Escherichia, Arizona, Hafnia and Klebsiella
Unpolluted soils and waters
May be of non-faecal origin and multiply in the environment
Helminth eggs
Cryptosporidiumand Giardia
Impact studies and risk assessment
Safety of Food and Environment – Pathogens and Heavy Metals
Concentration of E. coli in STWW, STWW with sand filtration, PTWW and PTWW with MBR
1.E+01
1.E+02
1.E+03
1.E+04
1.E+05
CF
U/m
l
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1.E-01
1.E+00
14-17 May2007
4-7 June 2007 18-21 June2007
16-19 July2007
6-9 August2007
Secondary treated waste water before SAFIR treatment Secondary treated waste water after SAFIR treatment
Primary treated waste water before SAFIR treatment Primary treated waste water after SAFIR treatment
Bologna, Italy: Sand filtration has no effect on E. coli. MBR reduces number of E. coli (-3-log). Soil from surface of potatoes all negative for E. coli whereas some soil samples (tomatoes) positive for E. coli. Potatoes and tomatoes all negative.
Impact studies and risk assessment
Quality of ±Processed Food
Evaluation of fresh matter food quality
Physical and chemical characteristics assessment
Industrial processing of the harvested vegetables into stabilizes commercial products (tomato puree and potato flakes)
Physical-Chemical analyses done in food samples:
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Physical-Chemical analyses done in food samples:
Analyses of Minerals
(Cd, Cr, Pb, Fe, Cu, As, Ni, Zn, Hg,
Sn, P, Mg, K, Na, Na, K, P, B )
Analysis of microelements
(Se, Li, B)
Analysis of quality markers
(Total Solids, pH, Hunter Colour, Sugars,
Tot.Acidity, Consistency, NO3- N tot)
Impact studies and risk assessmentPollution of the Environment - Inorganic compounds
LOQ
I2-in
teg-
Tap
Wat
er
I2-in
teg-
I°Bef
ore
I2-in
teg-
I°Afte
r
I2-in
teg-
II°B
efor
e
I2-in
teg-
II°A
fter
I2-W
W-T
ap
I2-W
W-I
°-Bef
ore
I2-W
W-I
I°-B
efor
e
I2-W
W-I
I°-A
fter
I2-in
teg-
Tap
wat
er
I2-in
teg-
II°B
efor
e
I2-in
teg-
II°A
fter
02/0
8/06
02/0
8/06
02/0
8/06
02/0
8/06
02/0
8/06
19/0
9/06
19/0
9/06
19/0
9/06
19/0
9/06
19/0
9/06
19/0
9/06
19/0
9/06
COT 0,5 1,2 15,7 12,2 4,9 4,6 1,1 44,8 5,9 1,9 0,8 5,6 6,2Ca 0,5 36,8 89,5 70,2 96,7 88,1 115,4 147,2 111,6 116,1 115,4 109,2 109,3Mg 0,5 23,5 27,7 18,6 21,6 23,5 22,2 30,7 25 22,7 24,8 24,3 24,4Na 0,5 29,1 138,3 72,5 109,2 118,8 31,8 281,8 38,6 31,8 30,8 133,1 115,7K 0,5 14,1 7 16,5 17,7 2,7 15,9 7,8 2,9 2,8 15,4 13,7HCO3 5 354 595 466 367
No or uncertain effect
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HCO3 5 354 595 466 367Cl 0,5 19,4 203 95 132,2 136,3 28,4 491,7 25,7 25,6 25,6 154,1 134SO4 0,5 78,5 93,3 50 89,4 93,7 98,8 111,6 54 93 134,2 120,1 168,7PO4 0,1 < LQ 8,2 12 35,2 32,1 < LQ 9,8 12 0,8 < LQ 9,7 8,5F 0,1 0,2 0,2 0,2 0,2As 1 < LQ 3,7 2,2 3,5 3,9 < LQ < LQ < LQ < LQ < LQ 3,2 3B 10 134 338 189 393 422 131 240 139 127 145 518 492Cu 1 < LQ 5 < LQ 12 8 12 4 < LQ 46 16 20 16Li 1 15 21 13 16 16 16 21 15 15 17 19 20Mn 5 < LQ 26 95 < LQ < LQ 11 89 150 17 < LQ 18 16SiO2 0,5 16,9 18,7 18,3 20,3 22,1 14,5 16,7 25,3 15,4 15,6 17,4 16,4Sr 10 823 898 650 740 692 882 1157 1025 880 998 923 937Zn 5 < LQ 11 < LQ 10 9 546 30 < LQ 690 58 377 269RSEC 0,1COD 0,5 1,1 27,2 2,6 1,2
NH4 0,1 < LQ 69,3 1,5 < LQ CO3 5 < LQ < LQ < LQ < LQ NO3 0,5 15,2 < LQ < LQ 12,3NO2 0,01 < LQ 0,17 < LQ < LQ Al 10 < LQ < LQ < LQ < LQ < LQ < LQ 17 < LQ < LQ 15 49 19Cd 0,5 < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ Co 1 < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ Cr 5 5,6 10,8 9,4 7,5 7,4 0,7 1,9 0,7 0,6 < LQ < LQ < LQ Fe 0,02 < LQ < LQ < LQ 0,04 < LQ < LQ 0,03 < LQ < LQ < LQ 0,07 0,05Ni 1 < LQ 3,1 4,5 4 4,6 74,2 3,8 3,5 61,4 5,5 4,8 7,5Pb 1 < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ Se 1 < LQ < LQ < LQ < LQ < LQ < LQ < LQ < LQ
Most values < LOQItaly 2006-season
Impact studies and risk assessmentRisk assessment according to WHO, 2006The revised guidelines do no longer only focus on wastewater treatment and croprestriction but offer a wider range of risk reduction measures such as localised (drip)irrigation techniques, food preparation measures like washing or peeling of produce
and also takes natural die-off of pathogens on produce into consideration.
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Impact studies and risk assessmentRisk assessment according to WHO, 2006
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The Disability Adjusted Life Years (DALY) indicator adds years of life expectancy lost dueto premature death and duration of illness A widely used limit of tolerable risk, is 10-5
lifetime risk, or 1 excess case of cancer over a lifetime per 100,000 of the populationingesting water with a given chemical. In terms of DALYs rounded to a simple figure thisdisease burden is equivalent to 1 x 10-6DALY per person per year (pppy) (WHO, 2003)
Impact studies and risk assessmentRisk assessment according to WHO, 2006
Involuntary ingestion of soil, subsurface irrigated by MBR treated primary wastewater
Soil quality: 360 E. coli per 100 gram of soil
SAFE
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Soil quality: 360 E. coli per 100 gram of soilMechanised agriculture: 1-10 mg of soil per day ingestedWorking Days: 100 days
Risk (DALY per person per year)Rota Virus Mean 7.0 * 10-4, SD 0.0006Campylobacter Mean 3.0 * 10-5, SD 0.00003Cryptosporodium Mean 0.000, SD 0.00000
SAFE
Impact studies and risk assessmentRisk assessment according to WHO, 2006
Consumption of tomatoes, surface irrigated by MBR t reated primary wastewater
Produce quality: 2,000 E. coli per 100 gram of tomatoes
UNSAFE
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Produce quality: 2,000 E. coli per 100 gram of tomatoes Consumption pattern: 100 grams every three days
Risk (DALY per person per year)Rota Virus Mean 2.0 * 10-2, SD 0.03 Campylobacter Mean 1.0 *10-3, SD 0.001 Cryptosporodium Mean 0.0001, SD 0.0002
UNSAFE
Results on water saving irrigation
Semifield-facility, where all components in the water balance: irrigation/precipitation – drainage – soil water content – evapotranspiration, can be controlled or measured
I ET
ET =
I - ∆θgain - D
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Coarse sand
Coarse sand
Sand loamLoam
D
∆θgain =WCe-WCs
Results on water saving irrigation
Experimental Design:
3 soil types
+
Irrigation treatments:
•FI: Drip irrigated daily to
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•FI: Drip irrigated daily to 25% deficit
•PRD1: PRD 70% in phase 1
•PRD2: PRD 70% in phase 2
Results on water saving irrigation
15
20
25Middel af Water
Right drip
Plant (middle)
2006-season Soil water content in PRD2:Automatic horizontal TDR (sand loam in ridge z:0.08)
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0
5
10
03/0
6/20
0604
/06/
2006
05/0
6/20
0606
/06/
2006
07/0
6/20
0608
/06/
2006
09/0
6/20
0610
/06/
2006
11/0
6/20
0612
/06/
2006
13/0
6/20
0614
/06/
2006
15/0
6/20
0616
/06/
2006
17/0
6/20
0618
/06/
2006
19/0
6/20
0620
/06/
2006
21/0
6/20
0622
/06/
2006
23/0
6/20
0624
/06/
2006
25/0
6/20
0626
/06/
2006
27/0
6/20
0628
/06/
2006
29/0
6/20
0630
/06/
2006
01/0
7/20
0602
/07/
2006
03/0
7/20
0604
/07/
2006
05/0
7/20
0606
/07/
2006
07/0
7/20
0608
/07/
2006
09/0
7/20
0610
/07/
2006
11/0
7/20
0612
/07/
2006
13/0
7/20
0614
/07/
2006
15/0
7/20
0616
/07/
2006
17/0
7/20
0618
/07/
2006
19/0
7/20
0620
/07/
2006
21/0
7/20
0622
/07/
2006
23/0
7/20
0624
/07/
2006
25/0
7/20
0626
/07/
2006
27/0
7/20
0628
/07/
2006
29/0
7/20
0630
/07/
2006
31/0
7/20
0601
/08/
2006
02/0
8/20
0603
/08/
2006
04/0
8/20
0605
/08/
2006
06/0
8/20
0607
/08/
2006
08/0
8/20
0609
/08/
2006
10/0
8/20
0611
/08/
2006
12/0
8/20
0613
/08/
2006
14/0
8/20
0615
/08/
2006
Left drip
Results on water saving irrigation
Soil Treatment Irrigation
(mm)
∆Soil water
(mm)
Drainage
(mm)
Total evapotranspiration
(mm)FI 285 13 36±8.0 262PRD1 245 0 40±5.6 205
Coarse sand
PRD2 243 24 37±6.5 230
Water balance 2006:
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PRD2 243 24 37±6.5 230FI 217 25 1±0.2 241PRD1 209 30 2±0.1 237
Sand loam
PRD2 172 35 2±0.2 205FI 253 25 26±0.3 252PRD1 213 35 4±1.3 244
Loam
PRD2 208 40 3±1.0 245
Results on water saving irrigationSize-grading of tubers:
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40
50
60
70T
otal
yie
ld (t
/ha)
6
9
12
15
Yie
ld d
iffer
ence
(t/h
a)
PRD
FI
PRD-FI
A
+L
Meta-analysis
Yield 2005-2006 sand: PRD2 v. FI
2
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0
10
20
30
Tot
al y
ield
(t/h
a)
-6
-3
0
3
Yie
ld d
iffer
ence
(t/h
a)
+L
-L
2005 2006 Both years
30
40
50
60
Mar
keta
ble
yiel
d (t/
ha)
6
8
10
12
Yie
ld d
iffer
ence
(t/h
a)
****
B
Marketable yield 2005-2006: PRD2 v. FI
PRD FI PRD-FI
2
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0
10
20
30
Mar
keta
ble
yiel
d (t/
ha)
0
2
4
6
Yie
ld d
iffer
ence
(t/h
a)
2005 2006 Both years
200
250
300
350
IrrW
UE
(kg/
ha m
m)
40
50
60
70
IrrW
UE
diff
. (kg
/ha
mm
)
* ******C
Irr.WUE 2005-2006: PRD2 v. FI
PRD FI PRD-FI
2
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0
50
100
150
2005 2006 Both years
IrrW
UE
(kg/
ha m
m)
0
10
20
30
IrrW
UE
diff
. (kg
/ha
mm
)
Jyndevad, Foulum and Rønhave Soils
10
12
14
16
18
20
Sca
b in
dex
and
pct.
mal
shap
ed tu
bers
Scab
Deform
Results on water saving irrigation
Tuber quality 2006:
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0
2
4
6
8
J J J F F F R R R
S2M1 S3M3 S3M4 S2M1 S3M3 S3M4 S2M1 S3M3 S3M4
Sca
b in
dex
and
pct.
mal
shap
ed tu
bers
Deform
FI PRD1 PRD2 FI PRD1 PRD2 FI PRD1 PRD2
Sand Sand loam Loam
After 2 years of SAFIR experiments:
� The treatment systems combined with subsurface drip irrigation have worked well, i.e. the water quality produced is suitable for SDI.
� PRD 70% during the tuber filling stage produced yield and quality equivalent to a fully irrigated treatment and had 20% higher irrigation water use efficiency and a marketable yield that was 15% higher than FI. Management models for PRD
Conclusions so far:
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that was 15% higher than FI. Management models for PRD irrigation will be developed for tomato and potato.
� The first lesson of SAFIR is that low quality water can be used. European and Chinese field experiments with potatoes and tomatoes grown on treated wastewater (vs. drinking water) indicate that contaminants and pathogens are very low in both the irrigation water delivered to the crops and the final product, and that food quality is good.
� The SAFIR project will in addition provide data for risk assessment in general of various irrigation practices. This will help in setting standards and be used in defining good agricultural practice for re-use of water when developing product certification schemes.
Conclusions so far:
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Sven-Erik Jacobsen2, Seyed Hamid Ahmadi1, Finn Plauborg1, Fulai Liu2, Adriano Battilani3, Martin Andersen4, Michele Steiner5, Georgios Psarras6, Radmila Stikic7, Guitong Li8, Xuebin Qi9, Anita Forslund2, Wolfram Klopmann10, Luca Sandei11, Jeroen Ensink12
1Faculty of Agricultural Sciences, University of Århus, Denmark 2Faculty of Life Sciences, University of Copenhagen, 3Consorzio di Bonifica di secondo grado per il Canale Emilliano Romagnolo, Bologna,
Acknowledgement
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Bonifica di secondo grado per il Canale Emilliano Romagnolo, Bologna, Italy, 4Grundfos BioBooster A/S, Bjerringbro, Denmark, 5Swiss Federal Institute of Environmental Science and Technology, Zürich, Switzerland, 6National Agricultural Research Foundation, Chania, Crete, Greece, 7Faculty of Agriculture, Belgrade University, Serbia, 8College of Resource and Environment, China Agricultural University, 9Chinese Academy of Agricultural Sciences, Xinxiang, China, 10Bureau de Researches Geologique et Minieres, Orleans, France, 11Stazione Sperimentale Industria Conserve Alimentari, Parma, Italy, 12London School of Hygiene and Tropical Medicine, United Kingdom