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Lorenzo Galbiati

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Title: Lorenzo Galbiati


1
Integrated modeling approach for diffuse
pollution management The Burana-Po di Volano
watershed
  • Lorenzo Galbiati
  • JRC-Institute for Environment and Sustainability
  • Rural, Water and Ecosystem Resources
  • lorenzo.galbiati_at_jrc.it

2
BURANA-PO DI VOLANO and SACCA DI GORO
  • Particularly important because
  • Intensively cultivated,
  • The nutrients applied within the watershed
    quickly move from the basin to the coastal zone,
  • The Sacca di Goro lagoon is of a great importance
    both for ecological and economical reasons,
  • This watershed allows the evaluation and
    application of tool for the Integrated River
    Basin Management Plan.

3
  • Burana-Po di Volano (BP-V) watershed is covering
    an area of around 3000 km2.
  • It is a complex system, especially for what
    concerning the river network
  • Artificial channels
  • Water is moved using pumps
  • Direction of water in many channels is opposite
    respect with to the slope.

4
Objectives of the application
  • Evaluate the interaction between the agricultural
    activities and the watershed,
  • Evaluate how the channels outflow from the
    watershed affects the water quality in the Sacca
    di Goro,
  • Apply the model for
  • climate scenarios,
  • Variation of the water quality derived in the
    system for irrigational purposes,
  • Link the model with multi-objectives optimization
    criteria in order to make evaluation, both on
    economical and ecological aspects.

5
DEFINITON OF THE MODEL TOOL ISSm (Integrated
Surface and Subsurface model).
  • SWAT 2000 (Soil and Water Assessment Tool, Arnold
    J., et al., Blackland Research Centre, 2000)
  • ModFlow 2000 (Harbaugh, A.W., et al., U.S.
    Geological Survey, 2000)
  • Mt3Dms (Zheng and Wang, et al., U.S. Geological
    Survey, 1999)
  • Qual2E (Lienfield, C., et al, U.S., Environmental
    Protection Agency, 1987)

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Water percolation and nutrients leaching
STEP 2
Bi-directional water and nutrients exchange
between aquifer and river network
STEP 3
9
INPUT for ISSm (Integrated Surface and Subsurface
model).
  • Daily precipitation and max/min temperature,
  • grids maps about soil, landuse and digital
    elevation model,
  • Data about the management of water within the
    basin, description of the channels and water
    pumps, amount of water derived for irrigational
    purposes,
  • Description of the soil types,
  • Time series of water flow and measured data about
    the water quality along the channel network to be
    used in the calibration of the model,
  • Soil water content and diluted nutrients,
  • Crop rotation, crop management operation
    schedules,
  • Time series about the groundwater table trends.

10
APPLICATION of ISSm to the B-PV
11
The Consorzio di Bonifica I Circondario (CB-1C),
  • Il CB-1C covers an area of around 900 km2,
  • Intensively drained by rivers and artificial
    channels (around 1500 Km of channels extension),
  • Parts of the channels (400 Km) have draining
    purposes, another part have irrigational purposes
    (350 Km), the remaining part have a mixed use
    (800 Km).

12
Hydraulic boundaries condition
13
Digital Elevation Model
14
Soil distribution and characteristics
15
Landuse and management practices
16
Channels network description and location of
measured station
17
  • Each of the sub-basin in the CB-1C has been
    divided in areas characterized by
  • unique soil/landuse combinations,
  • Water pumps to whom the channels discharge.

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The groundwater table has been characterized
using a 90 m cell size grid. The boundaries
condition and the hydrogeological properties have
been then defined on this base.
22
Water percolation to the shallow aquifer
1992-1999
23
Groundwater trends 1999-2001
E0.713
E0.668
E0.693
24
Water flow at the system outlets Collettore
Acque alte Collettore Acque Basse 1991-2001
E 0.813
25
Water flow at the system outlets Romanina
1991-2001
E 0.707
26
Water flow at the system outlets Bonello
1991-2001
E 0.799
27
Exchange flow between channels and groundwater,
Romanina sub-watershed 1991-2001.
28
Nutrients loads to the Sacca di Goro lagoon,
1991-1998
29
Conclusion on the application of ISSm and some
example of its use for RBMP
  • ISSm allows an evaluation, both for quantity and
    quality, of the nutrients loads draining into the
    Sacca di Goro,

The 10 years simulations for the 1991-2001 period
gave good results, therefore
  • ISSm could be used to evaluate scenarios on
    climate change / crop change / nutrients loads
    from the Po River,
  • Use the OUTPUT produced by ISSm as INPUT for the
    3D hydrodynamics model applied in the Sacca di
    Goro, with the aims to have an integrated tool
    for watershed management,
  • Use ISSm coupled with multi-objectives
    optimization tools in the context of River Basin
    Management Plan.

30
Example 1 Crop change scenarios fertilizer
application rate 15 decreased
Decreasing the application of fertilizer by 15,
the average percolation in 10 year decreases
about 16-20, while the crop production decreases
by about 7.
31
Example 2. Use of ISSm as a tool to take decision
at watershed level
1. We know the crop types distribution in the
area.
2. We have information on the management
practices for the different crop types.
3. We have statistical information on the
cultivation costs and the market prices of the
different crop types.
We can apply ISSm coupled with multi-objectives
optimization tools to built a PARETO-FRONT of
optimal decisions.
32
Example 2. Use of ISSm as a tool to take decision
at watershed level
1. The crop types widely common in the area
DURUM WHEAT, SPRING WHAET, MAIS, SUGAR BEAT,
SUNFLOWERS, SOYBEAN, ROTATION GRASS, ALFA-ALFA,
ORCHARD and FRUITS.
2. ISSm is coupled with a crop DB which allows to
estimate the fertilizer and irrigation
application as affected by meteorological
characteristics.
3. ISSm is able to run a set of 10-years
simulation calculating the crop production in the
area, and the nutrients percolation from through
the soil profile.
The model can evaluate all the combination of
CROP PRODUCTION, PROFIT, NITRATE AND PHOSPHORUS
PERCOLATION, giving as results a PARETO FRONT
where the PRODUCTION and PROFIT are Maximized,
while the NUTRIENTS PERCOLATION is Minimized.
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