Thermal
stress during heat waves in urban areas is
recognized for its strong devastating effect on
human health. A lot of effort to mitigate urban
heat was put into planting more vegetation and
removing sealed surfaces. However, many green
roofs and green areas are not irrigated, which
in turn leads – during eventually longer or more
extreme future summer heat periods without
precipitation – to drought stress of the plants.
As a result, evapotranspiration from vegetation
surfaces is reduced. Therefore, many
non-irrigated green roofs may not reach the
expected cooling effect.
During
droughts, agricultural surroundings cannot
provide full daytime cooling effects as well.
Further, simulations show that the conversion of
solar energy into electricity by photovoltaic
panels may reduce the urban heat island since
less energy is available for heating the air.
Local energy production by PV also reduces the
anthropogenic heat generated because of
importing energy to the city. Taking this factor
into account, the cooling effect of PV might be
even higher.
The project aims to investigate open
questions regarding urban overheating and to
incorporate them into a holistic analysis.
Questions that this project adresses are therefore
the quantification of the cooling potential of
green areas within and around Vienna via
evapotranspiration, the future irrigation needs,
further the cooling effect of PV panels and the
quantification of potential anthropogenic heat
reductions mainly by electrification of local
energy production and transport.
Four measurement sites were set up
on green roofs in different local climate zones
of Vienna (compact-midrise rooftop,
compact-midrise below rooftop, open mid-rise and
large low-rise). For
microclimatic measurements, automatic pot
lysimeters were installed at these four
different green roof sites over the city of
Vienna with a setup for a shallow and a deep
soil substrate (25 cm and 10 cm,
respectively). Besides the local microclimate
(especially wind, temperature, air humidity as
well as soil wetness within the pots), the
mini lysimeters measured quantitatively water
loss through evapotranspiration by weighing
the pots. The measurement period was starting
in June 2022 and completed by end of 2023,
including 2 years of different weather
conditions.
This data was used to calibrate the
FAO model according to Allen et al. 1998, which
simulates the soil moisture for selected drought
periods on green roofs. ARIS (Drought monitoring
system) data were used to simulate the soil
moisture of the surrounding agricultural areas
of Vienna.
To estimate the anthropogenic heat
flux of Vienna energy use data (oil, gas,
electricity, and others) were compiled for
different spatial and temporal scales to derive
the fluxes stemming from Viennese traffic,
services, private households, and industry. The
anthropogenic heat data were adjusted for the
defined simulation periods and developed as
time series functions based on the standard
load profiles. This was done for the three
categories (low residential, high residential,
industry). These scenarios included energy use
in buildings and traffic.
Further, the properties and climate
effects caused by using photovoltaics on roofs
were investigated. Literature research and
communication with stakeholders were used to
update and refine the prospective changes of
Viennese building parameters used in the
different urban categories of models.
All collected data were used to
initialize, run, and validate the coupled
WRF-TEB model and simulate the atmospheric
condition for present and future summer drought
episodes to estimate the expected thermal strain
on inhabitants in Vienna. The offline TEB model
was used to calculate the indoor temperature,
urban canyon microclimate and the microclimatic
contribution to the urban climate and to compare
scenarios.