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L’impermeabilizzazione del suolo: effetti sull’ecosistema urbano e possibili soluzioni per mitigarli

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L’impermeabilizzazione del suolo: effetti sull’ecosistema urbano e possibili soluzioni per mitigarli

Alessio Fini*, Piero Frangi, Irene Vigevani, Sebastien Comin, Francesco Ferrini

* Presenting author – Dipartimento di Scienze Agrarie e Ambientali – Produzione, Territorio, Agroenergia

(2)

Soil sealing, “the covering of soil by buildings, constructions, and

layers of completely or partly impermeable artificial materials” is the most pervasive form of land take and it is essentially an irreversible process (Alberti, 2005)

Effects of soil sealing include disruption of the water and carbon

cycles; higher soil and air temperature; drought stress on trees

(3)

To mitigate the effects of soil sealing, the use of pervious pavements is now advokated

Wikipedia.org

livinglandscapes.uk.com

POROUS PAVEMENTS:

The pavements itself is

permeable to water across its entire structure

PERMEABLE PAVEMENTS:

Pavements made by impervious modular elements, but voids between elements allow water infiltration

These pavements have infiltration

coefficients = 0.5-0.7, compared to

0.15 of asphalt

(4)

The aim of this work is to understand the effects of soil sealing and pervious pavements on tree growth, health and physiology.

To achieve this goal, in 2011, an experimental field was built in Vertemate con Minoprio to compare different pavement treatments, using a randomized block design with six blocks

Fraxinus ornus

Celtis australis

(5)

Permeable desing: curb on

a crushedrock sub-grade

Four soil treatments were imposed

Impermeable design:

asphalt on a concrete sub- grade

Control: unpaved soil (chemical weeding used for weed control) Porous desing:

epoxy resin + even-graded inert

on a crushed rock sub-grade

(6)

Research conducted from 2011 to 2015 revealed minor effects of pavement treatments on tree growth and physiology during establishment.

Pavements reduced evaporation, resulting in higher moisture availability compared to bare soil

Variation in

moisture through the year:

Asphalt: 8%

Permeable: 7%

Porous: 18%

Control: 29%

(7)

Limitations (2011-2015 research)

?

(8)

2011 2012 2013 2014 2015 Exp 1: establishing trees

Building

Planting

Start of measurements

Establishment

2016 2017 2018 2019 2020 Exp. 2: established trees

Start of measurements Root measurements

(9)

Net photosynthesis was measured using an infra-red gas analyzer, at 400 ppm CO2, 1300 mmol irradiance, and ambient temperature, from May 2016 to

September 2020

Net photosynthesis

Pavements had no effect on Asat in Celtis.

Fraxinus growing in permeable pavements had higher Asat than other treatments, but Asat did not differ between sealed soils and control

(10)

Water relations

No evidence that soil sealing triggers less favorable water relations in any species.

Permeable pavements, which allow rainfall infiltration but hasten evaporation, induced more favorable water relations in Fraxinus.

Water relations were measured in July from 2016 to 2020 using a pressure bomb.

Measurements were done at pre-dawn, at midday, and at midday on wrapped leaves (xylem water potential)

(11)

Chlorophyll fluorescence Fv/Fm was measured using a Handy-Pea after a dark acclimation of 40’, from May 2016 to September 2020

Pavements had little impact on Fv/Fm

Overall, we found no evidence that soil sealing triggered drought stress in established trees

n.s.

(12)

Volumetric soil moisture

Field capacity

Punto di appassimento Wilting point

• Transpiration of established trees depleted shallow moisture under asphalt, but moisture never

reached WP.

• Larger differences in winter and spring than in summer and fall.

• Deeper in the soil, moisture was

similar under asphalt and in bare

soil.

(13)

Root measurements (2020)

Size of the root system and root density for coarse roots, assessed in 2020 on 24 plants (3 x treatment) using Ground Penetrating Radar (900 MHz antenna). Measurements in 2020 were conducted using TreeRadarUnit (TRU) in cooperation with Studio Planta (Turin, Italy)

Roots were then dug with a suction

excavator, and fine and coarse root dry biomass were

quantified on individual roots.

(14)

Growth – roots (GPR, preliminary results)

Celtis control Fraxinus control

Celtis impermeable Fraxinus impermeable

Root density

Celtis porous Celtis permeable

total 0-30 cm 30-60 cm 60-90 cm total 0-30 cm 30-60 cm 60-90 cm

Fraxinus permeable

Fraxinus porous

(15)

Fine roots concentrated in the unpaved planting pit

Fine roots everywhere

impermeable permeable

porous

control

(16)

Soil sealing reduced root number, increased root thickening and

reduced fine roots biomass per unit dry root biomass

(17)

Soil CO 2

Low diffusivity of impermeable pavements to CO

2

resulted in elevated soil CO

2

beneath asphalt.

Elevated soil CO2 is known to

depress root activity and growth

(18)

Above-gound growth

• Minor effects of pavements on DBH growth, canopy growth and leaf area were detected

• Growth-rate was about 3.5

times higher in Celtis than in

Fraxinus

(19)

• Despite pavements affected moisture availability and root characteristics, trees

(Celtis in particular) were extremely plastic to

pavement type and showed little change in above-ground growth and physiology.

• From the tree’s

perspective, growing in a high-quality soil probably matters more than the pavement itself.

Conclusions

PERM IMP POR

CONPERM

IMP CON

POR IMP

CON POR

PERM PERMIMP CON POR

CON IMP PORPERM IMPPERM

POR CON

UAV with thermal and multispectral camera flying on the pavements

• Impermeable pavements affect water and

carbon cycling, which can be effectively

mitigated by the use of porous pavements

(20)

Thank you for your attention

This research was funded by the TREE Fund Research

Fellowship Grant Program

“Long-term assessment of the effects of impervious,

permeable, and porous

pavements on the underlying soil and on established trees”,

Funding:

100’000 USD

(21)

Concentrazione di CO2 in suoli

pavimentati (pre-establishment)

Riferimenti

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