SlideShare a Scribd company logo
www.openness-project.eu
OpenNESS has received funding from the European Union’s
Seventh Programme for research, technological development
and demonstration under grant agreement n° 308428.
Giulio Conte
Milano 25 Settembre 2015
Un caso applicativo di
servizi ecosistemici:
il trattamento naturale delle
acque di sfioro nel progetto
OPENNESS
From concepts to real-world applications
www.openness-project.eu
EU FP7 project OpenNESS (Dec 2012 - May 2017)
Aim:
deliver innovative and practical ways of applying the concepts of
Ecosystem Services in land, water and urban management in Europe, and
examine how these concepts are involved in key EU challenges: well-being,
sustainable development, governance and competitiveness.
2
From concepts to real-world applications
www.openness-project.eu
27 case studies
To achieve these goals, the project will apply the concepts and
methods in 27 case studies. Key to the operationalisation of concepts
is the involvement of local stakeholders and SMEs in the research
3
From concepts to real-world applications
www.openness-project.eu
Il problema: l’inquinamento provocato
dalle reti miste
12.10.201
5
Firstname,Surname,Organization
4
Fognatura Mista
Tubazione dello Scolmatore
Scarico dello scolmatore
Corpo idrico
Strada
Bacino di
Captazione
All’impianto di
depurazione
Scolmatore
(CSO)
Simulazione del funzionamento di un CSO
Agglomerato
Urbano
From concepts to real-world applications
www.openness-project.eu
Il problema: l’inquinamento provocato
dalle reti miste
Le stime dei carichi inquinanti sulle acque in Emilia Romagna
(T/anno BOD)
12.10.201
5
Firstname,Surname,Organization
5
Depurat.
civili
Reti non
depurate
Carico
ecced.
Scaricat.
Reti
miste
Industria diffuso Totale
7.600 4.500 3.070 9.250 3.830 18.300 46.800
From concepts to real-world applications
www.openness-project.eu
Soluzioni possibili
• Intervenire a monte: evitare l’afflusso di acque di pioggia in fogna:
• Separazione reti
• SUDS
• Intervenire a valle: trattare le acque di pioggia in eccesso
• Vasche di prima pioggia
• Sistemi di trattamento in situ
12.10.201
5
Firstname,Surname,Organization
6
From concepts to real-world applications
www.openness-project.eu
The case study of Gorla (Italy)
Key issues from ecosystem service perspective:
1. Quantification and economic evaluation of the
different ecosystem services provided (multi-
criteria analysis, willingness to pay)
2. Comparison of green vs. grey infrastructures
generally used for combined sewer overflow (CSO)
for pollution control and flood prevention (analysis
of scenario and trade-offs)
3. Explore the possibility to integrate the ecosystem
service approach in the decision making process
and in river basin management plans, through the
direct involvement of the stakeholders in the
research
7
The Gorla park is a new ecosystem
including a constructed wetland (green
infrastructure) built on the floodplain
of the Olona River in an area previously
used for poplar plantation
12.10.201
5
8
A map of the case study area
GiulioConte,IRIDRA
From concepts to real-world applications
www.openness-project.eu
Ecosystem services
9
15.1.2015Liqueteetal.,JointResearchCentre
Provisioning services Timber extraction
Regulation and
maintenance services
Water purification
Flood protection
Maintaining populations
and habitats (wildlife)
Cultural services Recreation
CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW
IN GORLA MAGGIORE (VA), ITALY
IRIDRA – STUDIOMAIONE
ALTERNATIVE 0: POPLAR PLANTATION
The area was originally a poplar
plantation. Alternative 0, “doing
nothing” , therefore envisages the use
of the area for productive forestry
m2
Poplar grove 36.000
Reed zones 0
Wetland zones 0
Buffer zones and
trees
0
CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW
IN GORLA MAGGIORE (VA), ITALY
m2
Poplar grove 0
Reed zones 0
Wetland zones 0
Buffer zones and trees 2000
IRIDRA – STUDIOMAIONE
ALTERNATIVE 1: FIRST FLUSH STORAGE TANK AND DRY RETENTION POND FOR SECOND FLUSH VOLUME
CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW
IN GORLA MAGGIORE (VA), ITALY
m2
Poplar grove 0
Reed zones 3800
Wetland zones 3500
Buffer zones and
trees
2000
IRIDRA – STUDIOMAIONE
ALTERNATIVE 2: THE RIVERINE WATER PARK, CSO TREATMENT BY
CONSTRUCTED WETLAND AND WET RETENTION POND
Gorla Maggiore case study: technical
scheme
• CSO discharge repartition
• treatment plant
• 1st flush
• 2nd flush
• Pre-treatment
• 1st stage: French-VF CWs
• 1st flush treatment
• 2nd stage: FWS CW
• 1st flush treatment refinement
• 2nd flush
• Buffer tank
13
Data sampling for OpenNESS project
• CSO wastewater quantity
• CSO event sampling
• every 15 min
during CSO events
14
• CSO wastewater quantity
• Sampling protocol
In VF: since start of CSO event
5 samples in the first hour
Out FWS: after theoretical HRT (36 h)
5 samples every hour
• 3 CSO samples done (COD NH4
+)
• In VF – Out FWS spring
• In VF – Out FWS summer
• In VF – Out FWS winter
Ecological service:
Water quality
Data Sampling: CSO quantity
• 1 year CSO quantity characterization
• From February 2014 to February 2015
• 68 CSO events
• Both singular or consecutive up and down
15
Average values
Volume 2392±3325 m3
Discharge 333±246 m3/h
Duration 7.6±9.7 h
Dry period 11±50 d
Ecological service:
Water quality
Flood protection effect
FWS has been designed to properly works as a buffer tank for the hydrograph with
return time of 10 years
16
IN
OUT
Time (min)
Flowrate
(m3/s)
Ecological service:
Flood protection
Data Sampling: CSO quality – 1
• Satisfactorily low effluent concentrations
• Stochastic events
 when should I sample? Efficiency calculation?
17
COD
N-NH4+
IN OUT
COD
[mg/l]
394.0±218.9 41.1±1.0
N-NH4+
[mg/l]
15.9±12.1 1.0±0.9
Ecological service:
Water quality
Data Sampling: CSO quality - 2
• Removal efficiencies VF+FWS (3 samples)
• COD: 69-91%
• NH4
+ : 70-99%
• Removal efficiencies VF (1 sample)
• COD: 89%
• NH4
+ : 87%
• 1st flush characterization
• Higher concentration in first CSO phase
• Possible higher concentration due to
low flow at the end of CSO event
18
Pollution control: Mass balance
• Black mass load  2017 PE + literature values
• High first flush in Spring and Summer (↑↑ CSO volume)
• Lower but not negligible first flush also in Winter (↓↓ CSO volume)
• Loads to WWTP relevant only for ↓↓ CSO volume
19
Ecological service:
Water quality
From concepts to real-world applications
www.openness-project.eu
Wildlife support
20
15.1.2015Liqueteetal.,JointResearchCentre
Monitoring the pond and the river for macroinvertebrates,
macrophytes, visible fauna and biochemical parameters (July 2014)
From concepts to real-world applications
www.openness-project.eu
Chironomus riparius (non-biting midges)
(Insecta: Diptera)
Naididae
(Annelida, Oligochaeta)
Coenagrionidae
(Insecta: Odonata)
Ditiscidae
(Insecta: Coleoptera)
Gerridae
(Insecta: Heteroptera)
Other Odonata
(dragonflies & damselflies )
Wildlife support
Macroinvertebrates in the pond
• wide tolerance
• important source of food
• contribute to the oxygenation • anoxic sediments
• intermediate water quality
• carnivorous
• adults in the pond
• numerous larvae and adults
• the highest diversity, highest
level of endemism and highest
portion of threatened
dragonflies are found within
the Mediterranean region,
including the Olona (Red List)
• wetlands are crucial
• typical from ponds-macrophytes
• low levels of oxygen
• fierce predator
• typical from ponds
• intermediate-low water quality
• predator
15.1.2015Liqueteetal.,JointResearchCentre
From concepts to real-world applications
www.openness-project.eu
Higher organisms observed in the pond
Rana verde
Rana synklepton esculenta
Airone cenerino (Ardea cinerea)
“Least concern” in the Red List
Gallinella d'acqua (Gallinula chloropus)
“Least concern” in the Red List
Tarabuso (Botaurus stellaris)
(protected by the EU Birds Dir.)
Juvenile fish
(Gambusia?)
Rana agile
Rana dalmatina
Wildlife support
• densely vegetated wetlands
• vulnerable conservation state
• Special Protection Areas
• densely vegetated wetlands
15.1.2015Liqueteetal.,JointResearchCentre
From concepts to real-world applications
www.openness-project.eu
Tifa o stiancia
(Typha angustifolia)
Limnantemio
(Nymphoides peltata)
Ninfea comune
(Nymphaea alba)
Ceratofillo
(Ceratophyllum demersum)
Cannuccia di palude
(Phragmites australis)
Gaggiolo acquatico
(Iris pseudacorus)
Lisca lacustre
(Scirpus lacustris)
Ninfea a fiore giallo (Nymphaea
Marliacea Chromatella)
Macrophytes were planted but their present vigour and distribution depend on the
environmental conditions. Two well-developed plant zones:
• emerged macrophytes covering ca. 10% (dominated by Typha angustifolia)
• floating leaved plants in ca. 15% (dominated by Nymphoides peltata and Nymphaea alba)
No submerged plants (Ceratophyllum was planted but has not survived, most probably due to
low water transparency).
Macrophytes in the pondWildlife support
15.1.2015Liqueteetal.,JointResearchCentre
From concepts to real-world applications
www.openness-project.eu
Wildlife support
Habitats diversity index of the 3 alternatives
Software Fragstats (University of Massachusetts) for landscape metrics
24
15.1.2015Liqueteetal.,JointResearchCentre
2008 2012
From concepts to real-world applications
www.openness-project.eu
Recreation
Relevance for Gorla Maggiore
and surroundings
Questionnaire for local residents
(ongoing):
• Number of visits and people
• Distance from home
• Activities
• Personal opinion
25
15.1.2015Liqueteetal.,JointResearchCentre
Construction costs
26
green infrastructure
constructed wetland - vertical flow systems € 222.459
constructed wetland - free water system € 92.941
pre-treatments (automatic screen, grit
removal) € 111.014
pipelines € 69.361
earthmovings € 54.616
Monitoring equipments € 49.266
Combined sewer overflow structures € 88.307
second flush pipeline € 20.938
Outlet structures € 19.874
outlet protection and river restoration € 38.845
Ancillary works € 25.592
safety plan works € 26.785
Landscaping € 80.000
€ 900.000,00
grey infrastructure
first flush tank 1000 m3 € 500.000
pipelines € 20.000
earthmovings € 45.000
Monitoring equipments € 15.000
Combined sewer overflow structures € 88.307
second flush pipeline € 20.938
Outlet structures € 19.875
outlet protection and river restoration € 38.845
Ancillary works € 20.000
safety plan works € 26.785
Landscaping € 50.000
€ 844.749,24
O&M costs
27
green infrastructure designed Real (1°-3° year) Note
constructed wetland - reeds maintenance € 1.360 € 0 no cutting due to slow grow rate
automatic screen, solids disposal € 200 € 200
grit removal, sand extraction and disposal € 2.800 € 1867
no extraction till now, total emptying scheduled
for this year
power consumption € 50 € 50
monitoring analysis (2 x year) € 600 € 0 analysis funded by Lombardia Region
Landscaping maintenance € 5.600 € 1000 landscaping mainly done by volunteers
manwork for inspection activities € 2.700 € 500 municipal workers + little electrical operations
€ 13.210 €3.617
grey infrastructure
cleaning, sediment extraction and disposal € 1.500
power consumption € 500
elettromechanical equipments maintenance € 200
Landscaping maintenance € 3.600
manwork for inspection activities € 1.350
Main WWTP treatment cost (0,25 €/m3) € 8.250
€ 15.397
28
Alternatives
Objectives Criteria Indicators Poplar
plantation
Grey
infrastruc
Green
infrastruc
People safety Reduce flooding risk Peak flow redution (%), return time of
10 years
0 80 86
Reduction of flooding downstream
(m3), return time of 10 years
0 8 100 8 900
Water quality Reduce pollution load Load reduction of dissolved organic
carbon (t/yr)
0 9.5 11.7
Load reduction of nitrogen (t/yr) 0 0.2 0.4
Wildlife support Provide a healthy natural
habitat
Expert judgment about biodiversity low low high
Landscape diversity (Shannon’s
diversity index)
1.89 1.85 2
People recreation and
health
Provide green space for
recreation
No. of visitors/users 0 moderate-
high*
high*
Frequency of visits 0 moderate-
high*
high*
Market goods Timber exploitation Value of timber production (profit
from harvest in EUR)
ca. 21 420 0 0
Public costs Reduce public costs Total construction costs (EUR) 0 844 750 900 000
Total management costs (EUR/yr) 0 15 396 13 210
Expected lifespan (yr) 17 20 20
Area occupied (ha) 36 000 2 000 9 300
Indicators and alternatives
Conclusions
• Green option gives better performance for most of criteria
• Comparable construction costs between Green and Grey
• Green option shows lower cost per m3 of treated water (higher volume treated)
Further possible studies
• Evaluate alternatives considering other criteria (e.g. LCA)
• Expand analysis at basin scale to support decision-maker (can CSO-CWs contribute to flood
protection?)
29

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Valle Olona: Un caso applicativo di servizi ecosistemici

  • 1. www.openness-project.eu OpenNESS has received funding from the European Union’s Seventh Programme for research, technological development and demonstration under grant agreement n° 308428. Giulio Conte Milano 25 Settembre 2015 Un caso applicativo di servizi ecosistemici: il trattamento naturale delle acque di sfioro nel progetto OPENNESS
  • 2. From concepts to real-world applications www.openness-project.eu EU FP7 project OpenNESS (Dec 2012 - May 2017) Aim: deliver innovative and practical ways of applying the concepts of Ecosystem Services in land, water and urban management in Europe, and examine how these concepts are involved in key EU challenges: well-being, sustainable development, governance and competitiveness. 2
  • 3. From concepts to real-world applications www.openness-project.eu 27 case studies To achieve these goals, the project will apply the concepts and methods in 27 case studies. Key to the operationalisation of concepts is the involvement of local stakeholders and SMEs in the research 3
  • 4. From concepts to real-world applications www.openness-project.eu Il problema: l’inquinamento provocato dalle reti miste 12.10.201 5 Firstname,Surname,Organization 4 Fognatura Mista Tubazione dello Scolmatore Scarico dello scolmatore Corpo idrico Strada Bacino di Captazione All’impianto di depurazione Scolmatore (CSO) Simulazione del funzionamento di un CSO Agglomerato Urbano
  • 5. From concepts to real-world applications www.openness-project.eu Il problema: l’inquinamento provocato dalle reti miste Le stime dei carichi inquinanti sulle acque in Emilia Romagna (T/anno BOD) 12.10.201 5 Firstname,Surname,Organization 5 Depurat. civili Reti non depurate Carico ecced. Scaricat. Reti miste Industria diffuso Totale 7.600 4.500 3.070 9.250 3.830 18.300 46.800
  • 6. From concepts to real-world applications www.openness-project.eu Soluzioni possibili • Intervenire a monte: evitare l’afflusso di acque di pioggia in fogna: • Separazione reti • SUDS • Intervenire a valle: trattare le acque di pioggia in eccesso • Vasche di prima pioggia • Sistemi di trattamento in situ 12.10.201 5 Firstname,Surname,Organization 6
  • 7. From concepts to real-world applications www.openness-project.eu The case study of Gorla (Italy) Key issues from ecosystem service perspective: 1. Quantification and economic evaluation of the different ecosystem services provided (multi- criteria analysis, willingness to pay) 2. Comparison of green vs. grey infrastructures generally used for combined sewer overflow (CSO) for pollution control and flood prevention (analysis of scenario and trade-offs) 3. Explore the possibility to integrate the ecosystem service approach in the decision making process and in river basin management plans, through the direct involvement of the stakeholders in the research 7 The Gorla park is a new ecosystem including a constructed wetland (green infrastructure) built on the floodplain of the Olona River in an area previously used for poplar plantation
  • 8. 12.10.201 5 8 A map of the case study area GiulioConte,IRIDRA
  • 9. From concepts to real-world applications www.openness-project.eu Ecosystem services 9 15.1.2015Liqueteetal.,JointResearchCentre Provisioning services Timber extraction Regulation and maintenance services Water purification Flood protection Maintaining populations and habitats (wildlife) Cultural services Recreation
  • 10. CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW IN GORLA MAGGIORE (VA), ITALY IRIDRA – STUDIOMAIONE ALTERNATIVE 0: POPLAR PLANTATION The area was originally a poplar plantation. Alternative 0, “doing nothing” , therefore envisages the use of the area for productive forestry m2 Poplar grove 36.000 Reed zones 0 Wetland zones 0 Buffer zones and trees 0
  • 11. CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW IN GORLA MAGGIORE (VA), ITALY m2 Poplar grove 0 Reed zones 0 Wetland zones 0 Buffer zones and trees 2000 IRIDRA – STUDIOMAIONE ALTERNATIVE 1: FIRST FLUSH STORAGE TANK AND DRY RETENTION POND FOR SECOND FLUSH VOLUME
  • 12. CONSTRUCTED WETLAND FOR THE TREATMENT OF COMBINED SEWER OVERFLOW IN GORLA MAGGIORE (VA), ITALY m2 Poplar grove 0 Reed zones 3800 Wetland zones 3500 Buffer zones and trees 2000 IRIDRA – STUDIOMAIONE ALTERNATIVE 2: THE RIVERINE WATER PARK, CSO TREATMENT BY CONSTRUCTED WETLAND AND WET RETENTION POND
  • 13. Gorla Maggiore case study: technical scheme • CSO discharge repartition • treatment plant • 1st flush • 2nd flush • Pre-treatment • 1st stage: French-VF CWs • 1st flush treatment • 2nd stage: FWS CW • 1st flush treatment refinement • 2nd flush • Buffer tank 13
  • 14. Data sampling for OpenNESS project • CSO wastewater quantity • CSO event sampling • every 15 min during CSO events 14 • CSO wastewater quantity • Sampling protocol In VF: since start of CSO event 5 samples in the first hour Out FWS: after theoretical HRT (36 h) 5 samples every hour • 3 CSO samples done (COD NH4 +) • In VF – Out FWS spring • In VF – Out FWS summer • In VF – Out FWS winter Ecological service: Water quality
  • 15. Data Sampling: CSO quantity • 1 year CSO quantity characterization • From February 2014 to February 2015 • 68 CSO events • Both singular or consecutive up and down 15 Average values Volume 2392±3325 m3 Discharge 333±246 m3/h Duration 7.6±9.7 h Dry period 11±50 d Ecological service: Water quality
  • 16. Flood protection effect FWS has been designed to properly works as a buffer tank for the hydrograph with return time of 10 years 16 IN OUT Time (min) Flowrate (m3/s) Ecological service: Flood protection
  • 17. Data Sampling: CSO quality – 1 • Satisfactorily low effluent concentrations • Stochastic events  when should I sample? Efficiency calculation? 17 COD N-NH4+ IN OUT COD [mg/l] 394.0±218.9 41.1±1.0 N-NH4+ [mg/l] 15.9±12.1 1.0±0.9 Ecological service: Water quality
  • 18. Data Sampling: CSO quality - 2 • Removal efficiencies VF+FWS (3 samples) • COD: 69-91% • NH4 + : 70-99% • Removal efficiencies VF (1 sample) • COD: 89% • NH4 + : 87% • 1st flush characterization • Higher concentration in first CSO phase • Possible higher concentration due to low flow at the end of CSO event 18
  • 19. Pollution control: Mass balance • Black mass load  2017 PE + literature values • High first flush in Spring and Summer (↑↑ CSO volume) • Lower but not negligible first flush also in Winter (↓↓ CSO volume) • Loads to WWTP relevant only for ↓↓ CSO volume 19 Ecological service: Water quality
  • 20. From concepts to real-world applications www.openness-project.eu Wildlife support 20 15.1.2015Liqueteetal.,JointResearchCentre Monitoring the pond and the river for macroinvertebrates, macrophytes, visible fauna and biochemical parameters (July 2014)
  • 21. From concepts to real-world applications www.openness-project.eu Chironomus riparius (non-biting midges) (Insecta: Diptera) Naididae (Annelida, Oligochaeta) Coenagrionidae (Insecta: Odonata) Ditiscidae (Insecta: Coleoptera) Gerridae (Insecta: Heteroptera) Other Odonata (dragonflies & damselflies ) Wildlife support Macroinvertebrates in the pond • wide tolerance • important source of food • contribute to the oxygenation • anoxic sediments • intermediate water quality • carnivorous • adults in the pond • numerous larvae and adults • the highest diversity, highest level of endemism and highest portion of threatened dragonflies are found within the Mediterranean region, including the Olona (Red List) • wetlands are crucial • typical from ponds-macrophytes • low levels of oxygen • fierce predator • typical from ponds • intermediate-low water quality • predator 15.1.2015Liqueteetal.,JointResearchCentre
  • 22. From concepts to real-world applications www.openness-project.eu Higher organisms observed in the pond Rana verde Rana synklepton esculenta Airone cenerino (Ardea cinerea) “Least concern” in the Red List Gallinella d'acqua (Gallinula chloropus) “Least concern” in the Red List Tarabuso (Botaurus stellaris) (protected by the EU Birds Dir.) Juvenile fish (Gambusia?) Rana agile Rana dalmatina Wildlife support • densely vegetated wetlands • vulnerable conservation state • Special Protection Areas • densely vegetated wetlands 15.1.2015Liqueteetal.,JointResearchCentre
  • 23. From concepts to real-world applications www.openness-project.eu Tifa o stiancia (Typha angustifolia) Limnantemio (Nymphoides peltata) Ninfea comune (Nymphaea alba) Ceratofillo (Ceratophyllum demersum) Cannuccia di palude (Phragmites australis) Gaggiolo acquatico (Iris pseudacorus) Lisca lacustre (Scirpus lacustris) Ninfea a fiore giallo (Nymphaea Marliacea Chromatella) Macrophytes were planted but their present vigour and distribution depend on the environmental conditions. Two well-developed plant zones: • emerged macrophytes covering ca. 10% (dominated by Typha angustifolia) • floating leaved plants in ca. 15% (dominated by Nymphoides peltata and Nymphaea alba) No submerged plants (Ceratophyllum was planted but has not survived, most probably due to low water transparency). Macrophytes in the pondWildlife support 15.1.2015Liqueteetal.,JointResearchCentre
  • 24. From concepts to real-world applications www.openness-project.eu Wildlife support Habitats diversity index of the 3 alternatives Software Fragstats (University of Massachusetts) for landscape metrics 24 15.1.2015Liqueteetal.,JointResearchCentre 2008 2012
  • 25. From concepts to real-world applications www.openness-project.eu Recreation Relevance for Gorla Maggiore and surroundings Questionnaire for local residents (ongoing): • Number of visits and people • Distance from home • Activities • Personal opinion 25 15.1.2015Liqueteetal.,JointResearchCentre
  • 26. Construction costs 26 green infrastructure constructed wetland - vertical flow systems € 222.459 constructed wetland - free water system € 92.941 pre-treatments (automatic screen, grit removal) € 111.014 pipelines € 69.361 earthmovings € 54.616 Monitoring equipments € 49.266 Combined sewer overflow structures € 88.307 second flush pipeline € 20.938 Outlet structures € 19.874 outlet protection and river restoration € 38.845 Ancillary works € 25.592 safety plan works € 26.785 Landscaping € 80.000 € 900.000,00 grey infrastructure first flush tank 1000 m3 € 500.000 pipelines € 20.000 earthmovings € 45.000 Monitoring equipments € 15.000 Combined sewer overflow structures € 88.307 second flush pipeline € 20.938 Outlet structures € 19.875 outlet protection and river restoration € 38.845 Ancillary works € 20.000 safety plan works € 26.785 Landscaping € 50.000 € 844.749,24
  • 27. O&M costs 27 green infrastructure designed Real (1°-3° year) Note constructed wetland - reeds maintenance € 1.360 € 0 no cutting due to slow grow rate automatic screen, solids disposal € 200 € 200 grit removal, sand extraction and disposal € 2.800 € 1867 no extraction till now, total emptying scheduled for this year power consumption € 50 € 50 monitoring analysis (2 x year) € 600 € 0 analysis funded by Lombardia Region Landscaping maintenance € 5.600 € 1000 landscaping mainly done by volunteers manwork for inspection activities € 2.700 € 500 municipal workers + little electrical operations € 13.210 €3.617 grey infrastructure cleaning, sediment extraction and disposal € 1.500 power consumption € 500 elettromechanical equipments maintenance € 200 Landscaping maintenance € 3.600 manwork for inspection activities € 1.350 Main WWTP treatment cost (0,25 €/m3) € 8.250 € 15.397
  • 28. 28 Alternatives Objectives Criteria Indicators Poplar plantation Grey infrastruc Green infrastruc People safety Reduce flooding risk Peak flow redution (%), return time of 10 years 0 80 86 Reduction of flooding downstream (m3), return time of 10 years 0 8 100 8 900 Water quality Reduce pollution load Load reduction of dissolved organic carbon (t/yr) 0 9.5 11.7 Load reduction of nitrogen (t/yr) 0 0.2 0.4 Wildlife support Provide a healthy natural habitat Expert judgment about biodiversity low low high Landscape diversity (Shannon’s diversity index) 1.89 1.85 2 People recreation and health Provide green space for recreation No. of visitors/users 0 moderate- high* high* Frequency of visits 0 moderate- high* high* Market goods Timber exploitation Value of timber production (profit from harvest in EUR) ca. 21 420 0 0 Public costs Reduce public costs Total construction costs (EUR) 0 844 750 900 000 Total management costs (EUR/yr) 0 15 396 13 210 Expected lifespan (yr) 17 20 20 Area occupied (ha) 36 000 2 000 9 300 Indicators and alternatives
  • 29. Conclusions • Green option gives better performance for most of criteria • Comparable construction costs between Green and Grey • Green option shows lower cost per m3 of treated water (higher volume treated) Further possible studies • Evaluate alternatives considering other criteria (e.g. LCA) • Expand analysis at basin scale to support decision-maker (can CSO-CWs contribute to flood protection?) 29