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ORIGINAL ARTICLE
Assessment of bioclimatic conditions on Crete Island, Greece
Anastasia Bleta • Panagiotis T. Nastos •
Andreas Matzarakis
Received: 3 May 2012 / Accepted: 30 August 2013 / Published online: 13 September 2013
� Springer-Verlag Berlin Heidelberg 2013
Abstract The objective of this study was to assess and
analyze the human bioclimatic conditions of Crete Island,
by applying two human thermal indices: physiological
equivalent temperature (PET), derived from the Munich
Energy-balance Model for Individuals human energy bal-
ance model, and Universal Thermal Climate Index (UTCI),
based on the Fiala multi-node model of human thermo-
regulation. Human bioclimatic studies provide a frame-
work for considering the effects of climatic conditions on
human beings and highlighting the social/economic factors
that mitigate or amplify the consequences of environmental
changes. In order to estimate the thermal effect of the
environment on the human body, it has been considered
that the total effects of all thermal components, not only of
individual parameters, should be taken into account. The
climatic data (air temperature, relative humidity, cloudi-
ness, wind speed) used in this study were acquired from the
archives of the Hellenic National Meteorological Service,
regarding ten meteorological stations in Crete Island. These
data, covering the 30-year period 1975–2004, were used for
the calculation of PET and UTCI in order to assess thermo-
physiological stress levels. The findings of this analysis,
such as bioclimatic diagrams, temporal and spatial distri-
butions of PET and UTCI as well as trends and variability,
will help stake holders to understand and interpret the
island’s current bioclimate, in order to make any necessary
adaptations and become more resilient to the foreseen
climate change.
Keywords Bioclimatic conditions � PET � UTCI �Crete Island
Introduction
The quality of life in an urban or rural environment is
influenced significantly by bioclimatic conditions, both
short and long terms. Bioclimatic conditions are modified
due to environmental factors and the complex structure and
development of urban agglomerations as well. There has
been extended human biometeorological research indicat-
ing the impact of urban bioclimate on human morbidity
(Schwartz et al. 2004; Nastos and Matzarakis 2006; Mi-
chelozzi et al. 2007), mortality (Curriero et al. 2002; An-
alitis et al. 2008; Baccini et al. 2008; Hajat and Kosatky
2010; Almeida et al. 2010; Nastos and Matzarakis 2012),
tourism potential and decision making (de Freitas 2003;
Didaskalou and Nastos 2003; Hamilton and Lau 2005; Lin
et al. 2006; Matzarakis and Nastos 2011), and urban
planning (Carmona et al. 2003; Nikolopoulou and Steemers
2003; Nikolopoulou and Lykoudis 2006; Thorsson et al.
2004; 2007). Over the last years, many attempts have been
made to formulate a reliable and user-friendly index for the
assessment of the physiological thermal response of the
human body to climatic conditions (d’Ambrosio Alfano
et al. 2011), but only physiological equivalent temperature
(PET) and Universal Thermal Climate Index (UTCI) seem
to meet these requirements. PET is recommended for the
evaluation of the thermal component of different climates
by VDI Guideline 3787 (VDI 1998). PET is based on the
A. Bleta � P. T. Nastos (&)
Laboratory of Climatology and Atmospheric Environment,
Department of Geography and Climatology, Faculty of Geology
and Geoenviroment, National and Kapodistrian University of
Athens, Panepistimiopolis, 15784 Athens, Greece
e-mail: [email protected]
A. Matzarakis
Meteorological Institute, Albert Ludwigs University of Freiburg,
79085 Freiburg, Germany
123
Reg Environ Change (2014) 14:1967–1981
DOI 10.1007/s10113-013-0530-7

Munich Energy-balance Model for Individuals (MEMI),
which describes the thermal conditions of the human body
in a physiological relevant way (Fanger 1972; Hoppe
1993). UTCI was developed following the concept of an
equivalent temperature and has been applied in recent
human biometeorological studies, such as daily forecasts
and extreme weather warnings, bioclimatic mapping, urban
and regional planning, environmental epidemiology, and
climate impacts research (Jendritzky et al. 2012). The
UTCI represents an equivalent temperature that equals to
the ambient air temperature resulting in the same level of 7
crucial physiological parameters, which an average person
would experience in a reference environment (Jendritzky
et al. 2002, 2008; Fiala et al. 2012).
The bioclimatic analysis in this study concerns Crete
Island, a climate-sensitive area, affected by frequent Sah-
aran dust episodes especially during spring and summer
periods, when the development of suitable synoptic mete-
orological conditions often occurs (Kaskaoutis et al. 2008).
Furthermore, the topography of the island and the conse-
quent Fohn winds develop worse bioclimatic conditions
(Nastos et al. 2011), which are exacerbated due to atmo-
spheric pollution in urban agglomerations and strongly
impact public health.
Climate change is considered to be the main driving
force and its effects are expected to be more intense in the
forthcoming years. The stake, therefore, lies in mitigating
the environmental, social, and economic impacts on the
lucrative sectors of the region and tourism, agriculture, and
services related to civil protection. An overarching priority
in future research is the adaptation to climate and envi-
ronmental changes and related issues such as sustainable
cities and coastal zones as well as resilient societies, as
identified in the 7th Framework Program. Coastal areas are
highly threatened since they are hotspots for pollution,
increased water demands, and high urbanization pressures.
Located on the land and sea boundary, they are particularly
vulnerable to climate and global changes. Thus, the
purpose of the present study is to quantify the bioclimatic
conditions on Crete Island, during the 1975–2004 period,
based on PET and UTCI human thermal indices.
Data and analysis
The climatic data used in this study concern mean daily
values of air temperature, relative humidity, cloudiness,
and wind speed, acquired from the archives of the Hellenic
National Meteorological Service (HNMS) concerning ten
meteorological stations in Crete, during the period
1975–2004. The geographic characteristics of the HNMS
stations are presented in Table 1. The stations are divided
into three groups: stations located on the northern coasts,
mountainous stations, and stations on the southern coasts of
Crete Island.
The data sets have been tested for homogeneity in pre-
vious studies (Matzarakis and Nastos 2011; Nastos et al.
2002) and were used for the calculation of PET and UTCI
in order to assess the level of the thermo-physiological
stress.
For bioclimatic purposes, the wind velocity for all the
examined stations was adjusted according to the following
formula (Kuttler 2000):
WS1:1 ¼WSh � ð1:1=hÞa a ¼ 0:12 � z0 þ 0:18
where WSh is the wind speed (m s-1) at the station’s height
(h, usually 10 m), a is an empirical exponent, depending on
the surface roughness, and z0 is the roughness length. Wind
velocity was estimated at 1.1 m, which is the center of
gravity of the human body, and builds the reference level
for human biometeorological studies. In this study, three
different values of roughness length were applied
depending on the landscape around the examined station.
Thus, z0 = 0.2 for agricultural land with many houses,
shrubs, and plants, or 8-m-tall sheltering hedgerows within
a distance of about 250 m (stations: Palaiochora and
Table 1 Characteristics of the
meteorological stations in Crete
Island
Code Station Latitude
(degrees)
Longitude
(degrees)
Altitude
(m)
Period
1 746 SOUDA 35.3 24.0 10 1975–2004
2 758 RETHYMNO 35.4 24.5 7 1975–2004
3 754 HERAKLION 35.3 25.2 39 1975–2004
4 757 SITIA 35.2 26.1 22 1975–2004
5 755 FOURNI 35.3 25.7 315 1975–2004
6 752 ANOGEIA 35.3 24.9 822 1975–2004
7 760 KASTELLI 35.2 25.3 333 1975–2004
8 751 PALAIOCHORA 35.2 23.7 4 1975–2004
9 759 TYBAKI 35.0 24.5 7 1975–2004
10 756 IERAPETRA 35.0 25.7 13 1975–2004
1968 A. Bleta et al.
123

Kastelli); z0 = 0.4 for villages, small towns, agricultural
land with many or tall sheltering hedgerows, forests, and
very rough and uneven terrain (stations: Souda, Anogeia,
Fourni, Tymbaki); z0 = 0.8 for larger cities with tall
buildings (stations: Heraklion, Ierapetra, Sitia, Rethymno).
The aforementioned values of roughness length for a spe-
cific terrain were derived from the European Wind Atlas
(Troen and Petersen, 1989).
PET is equivalent to the air temperature at which—in a
typical indoor setting (without wind and solar radiation)—
the heat balance of the human body (work metabolic rate
80 W of light activity that should be added to the basic
metabolic rate 86.5 W, Stolwijk and Hardy 1977; heat
resistance of clothing 0.9 clo, which is the reference
clothing insulation value used for the formulation of PET)
is maintained with core and skin temperatures equal to
those of the under assessment conditions (Mayer and
Hoppe 1987; Hoppe 1999). The following assumptions are
made for indoor reference climate: Mean radiant temper-
ature equals air temperature (Tmrt = Ta). Air velocity is
set to 0.1 m/s. Water vapor pressure is set to 12 hPa
(approximately equivalent to relative humidity of 50 % at
Ta = 20.0 �C). The PET assessment scale (Table 2) is
derived by calculating Fanger’s (1972) PMV for varying
air temperatures in the reference environment using the
settings for the PET reference person (height: 1.75 m,
weight: 75 kg, age: 35 years, and sex: male; work meta-
bolic rate 80 W of light activity that should be added to the
basic metabolic rate and heat resistance of clothing 0.9
clo,) (Matzarakis et al. 1999). According to Hoppe (1999),
the assumption of constant values for clothing and activity
in the calculation of PET were made in order to define an
index independent of individual behavior.
UTCI is defined as the equivalent ambient temperature
(�C) of a reference environment providing the same
physiological response of a reference person as the actual
environment (Weihs et al. 2012). The calculation of the
physiological response to the meteorological input is based
on a multi-node model of human thermoregulation (Fiala
et al. 2001), associated with a clothing model. The UTCI
assessment scale is presented in Table 3. The assessment
scale is based on different combinations of rectal and skin
temperatures, sweat rate, shivering, etc., that might indicate
‘‘identical’’ strain causing non-unique values for single
variables like rectal or mean skin temperature in different
climatic conditions with the same value of UTCI (Błaz-
ejczyk et al. 2012). Static clothing insulation is adjusted to
the ambient temperature considering seasonal clothing
adaptation habits of Europeans, which notably affects
human perception of the outdoor climate (Havenith et al.
2012). In this point, it is worth mentioning that while in
principle the PET scale represents thermal sensations of
thermal environment experienced by specific population,
the UTCI scale represents heat/cold stress intensities
regardless the population type. The UTCI scale can be
applied to a very wide range of temperatures, from -70 to
?50 �C.
The input variables in modeling mean daily PET and
UTCI are mean daily values of air temperature, relative
humidity, wind speed, and radiant temperature. The input
variable of mean daily radiant temperature (the uniform
temperature of a surrounding surface that results in the
same radiation energy gain on a human body as the pre-
vailing radiation fluxes) is modeled based on mean daily
cloud coverage. In the study, both PET and UTCI were
calculated using ‘‘RayMan’’ model, appropriate to calcu-
late radiative heat transfer and human biometeorological
indices (Matzarakis et al. 1999, 2010). The ‘‘RayMan’’
model, developed according to Guideline 3787 of the
German Engineering Society (VDI 1998), calculates the
radiative heat transfer in both simple and complex envi-
ronments. The main feature and advantage of ‘‘RayMan’’
compared to other similar models is the calculation of
short- and long-wave radiation fluxes, the possibility to
Table 2 Physiological equivalent temperature (PET) for different
grades of thermal sensation and physiological stress on human beings
(Matzarakis et al. 1999)
PET (�C) Thermal sensation Physiological stress level
\4 Very cold Extreme cold stress
4–8 Cold Strong cold stress
8–13 Cool Moderate cold stress
13–18 Slightly cool Slight cold stress
18–23 Comfortable No thermal stress
23–29 Slightly warm Slight heat stress
29–35 Warm Moderate heat stress
35–41 Hot Strong heat stress
[41 Very hot Extreme heat stress
Table 3 UTCI Assessment Scale: UTCI categorized in terms of
thermal stress (Brode et al. 2012b)
UTCI (�C) Stress category
[ ?46 Extreme heat stress
?38 to ?46 Very strong heat stress
?32 to ?38 Strong heat stress
?26 to ?32 Moderate heat stress
?9 to ?26 No thermal stress
?9 to 0 Slight cold stress
0 to -13 Moderate cold stress
-13 to -27 Strong cold stress
-27 to -40 Very strong cold stress
\-40 Extreme cold stress
Bioclimatic conditions on Crete Island 1969
123

evaluate the thermal environment throughout the year for
both cold and hot seasons, and the use of a common unit
(�C).
The Mann–Kendall rank statistic method was applied
concerning the trends of the time series of annual number
of days with mean daily PET/UTCI falling in the extreme
classes of PET/UTCI (Mitchell et al. 1966).
Results and discussion
The northern, mountainous and southern meteorological
stations of HNMS were kept in different groups (Table 1).
The northern coasts of Crete are under the influence of the
northerly winds, especially during summer time and early
autumn, when the ‘‘Etesians’’ prevail. These are periodical
winds of the north section established over the Aegean Sea,
when a high-pressure center in the central and south Eur-
ope is combined with the Indian low-pressure system over
Asia Minor and the Eastern Mediterranean Sea (Metaxas
and Bartzokas 1994). A characteristic effect of the Etesians
regime is summer droughts and uniform weather conditions
in Greece (Nastos et al. 2002). This prevailing weather type
(cool and dry winds over the Aegean Sea) in summer
moderates the intensity of heat stress at the northern coasts
of Crete. The beneficial impacts of ‘‘Etesians’’ winds do
not appear at the southern coasts, due to the blocking
induced by the mountain ranges, leading to increased heat
stress within the summer period. In addition, the southern
coasts are protected against the winter northerly winds and,
thus, mild bioclimatic conditions prevail during the cold
period of the year. It is evident that the topography of the
island is responsible for extreme weather conditions. This
is the case of Heraklion city located in the basin northward
the Mount Psiloritis (2,456 m), which is perpendicular to
the southern air mass flow, causing the so-called Fohn
winds. Coming down from the lee of the mountain, these
winds are getting warm at a dry adiabatic rate and arrive at
lower elevations both warmer and drier than they were at
corresponding levels on the windward side. Descending to
the lowlands on the leeward side of the range, the air
arrives as a strong, gusty, desiccating wind. The wind often
lasts for 3 days or more, gradually weakening after the first
or second day. Sometimes, it stops very abruptly (Nastos
et al. 2011).
Figures 1, 2, and 3 depict the bioclimatic diagrams for
PET with respect to the stations under examination taking
into consideration the aforementioned division in three
groups (northern, southern, and mountainous stations). The
human thermal bioclimatic conditions are expressed in
percentages of the occurrence of PET classes (Table 2) for
each month. The respective bioclimatic diagrams for UTCI
are not shown for brevity, but are also discussed along with
PET diagrams further below.
As far as the stations on the northern coasts of the island
(Souda, Rethymno, Heraklion, and Sitia) are concerned, the
analysis of the bioclimatic diagrams showed that the thermal
comfort class (18 �C \ PET \ 23 �C) occurs throughout
the year in all stations. The frequency of the thermal comfort
class ranges from 0.3 % (August, in Souda) to 38.4 %
(October, in Heraklion). The thermal comfort class presents
frequencies from 1.3 % (August, in Tybaki) to 38.4 %
(March, in Palaiochora) throughout the year, concerning the
southern coastal cities, while this class disappears in July
and August in Palaiochora. Our findings indicate that the
thermal comfort class counts for higher frequencies for the
northern stations against the southern ones.
Taking into account the thermal index UTCI, the class
of thermal comfort (9 �C \ UTCI \ 26 �C) for northern
stations is missing in December and January in Souda,
while it reaches 90.9 % in November in Heraklion. Con-
cerning the southern stations, UTCI appears to be between
0.1 % (August, in Palaiochora) and 95.7 % (December, in
Palaiochora).
The frequency of the strong heat stress class for PET on
the northern coasts of the island does not appear in cold
months (December to February, in Souda and Rethymno;
November to March, in Sitia; December to March, in
Heraklion), while the maximum frequency (31.8 %) comes
up in August, in Rethymno. Concerning the southern
coastal cities, the strong heat stress class does not appear in
January in Tybaki, from December to January in Ierapetra,
and from December to March in Palaiochora, while the
highest frequency is 52.1 % in September, in Palaiochora.
On the other hand, the strong cold stress class is absent
from May to June and October in Sitia, and from May to
October in Souda, Rethymno, and Heraklion, regarding the
northern coastal stations. Similar patterns occur in the
southern coastal cities, where this class does not appear
from May to October at any of the stations, whereas it
reaches maximum frequency (15.3 %) in February, in
Ierapetra.
The strong heat stress for UTCI index on the north
coasts of the Crete Island does not appear from September
to May in Souda, from November to April in Heraklion and
Rethymno, and from November to March in Sitia, reaching
its maximum frequency (55.8 %) in August, in Rethymno.
Regarding the southern coastal stations, this class does not
come up from December to April in Palaiochora, from
November to April in Tybaki, and from November to
March in Ierapetra, while the maximum frequency
(79.0 %) appears in August in Palaiochora. The strong cold
stress class is really scarce for northern stations. More
specifically, this class does not occur at all in Souda and
1970 A. Bleta et al.
123

Fig. 1 Frequencies of various
classes of PET index for
northern coastal areas of Crete
Island (period 1975–2004)
Bioclimatic conditions on Crete Island 1971
123

does not appear from April to December in Heraklion, from
March to September and November in Rethymno, and from
March to November and January in Sitia. The maximum
frequency is 0.6 % in February, in Heraklion. For the
southern coastal stations, the strong cold stress does not
exist throughout the year for Palaiochora and Tybaki,
neither does it appear from April to November in Ierapetra.
However, it reaches the maximum frequency 0.83 % in
February, in Ierapetra.
The extreme heat class for PET at the northern stations
is absent from November to March in Souda, Rethymno,
and Sitia, and from November to April in Heraklion, pre-
senting the maximum frequency (13.7 %) in July in Ret-
hymno. Similar temporal patterns appear at the southern
stations; there is no extreme heat stress from November to
April in Palaiochora, from November to February in Ty-
baki, and from November to March in Ierapetra. The
maximum frequency (36.5 %) occurs in July in
Fig. 2 Frequencies of various
classes of PET index for
southern coastal areas of Crete
Island (period 1975–2004)
1972 A. Bleta et al.
123

Palaiochora. Taking into account the frequencies of the
extreme cold class for northern stations, the highest fre-
quency (4.9 %) appears in February in Souda, while this
class does not exist from April to October in Souda, from
April to November in Heraklion, from April to September
and November in Rethymno, and in April, May, July,
September, and October in Sitia. Regarding the southern
stations, the class of extreme cold stress does not appear
from March to November in Palaiochora, from April to
November in Tybaki, and from April to June, and August
to October in Ierapetra, presenting the maximum frequency
(4.2 %) in February, in Ierapetra.
The very strong heat class for UTCI at the northern
stations ranges from 0.2 % (August, in Sitia) to 4.3 %
(July, in Rethymno) against 0.1 % (November in Palai-
ochora and September in Ierapetra) to 14.9 % (July, in
Palaiochora). The very strong cold class is not apparent at
the northern and southern stations throughout the year. The
Fig. 3 Frequencies of various
classes of PET index for
mountain areas of Crete Island
(period 1975–2004)
Bioclimatic conditions on Crete Island 1973
123

1974 A. Bleta et al.
123

extreme heat class for UTCI index (UTCI [ 46 �C) does
not exist at the northern stations, with the exception of
Sitia, where the class slightly appears from June to August
presenting the highest frequency (0.5 %) in July. Besides,
this class is absent at the southern stations with the
exception of Palaiochora, where it presents a value of
0.4 % in July. The extreme cold class of the assessment
scale (UTCI \ -40 �C) does not appear at any of the
northern and southern stations.
Regarding the mountain stations, the main characteristic
is that the extreme cold stress class for PET appears within
7 months (October to April) in Anogeia and Kastelli, and
6 months (November to April) in Fourni, ranging from
0.1 % (April, in Fourni and October in Kastelli) to 18.8 %
(January, in Fourni). The strong cold stress is apparent
within 8 months (October to May) in Kastelli and Anogeia,
and 7 months (October to April) in Fourni, ranging from
0.1 % (October, in Kastelli) to 27.4 % (January, in Kas-
telli). On the other hand, the class of extreme heat stress
has been decreased to 5–6 months (May to September in
Fourni and Anogeia; April to September in Kastelli),
ranging from 0.1 % (September, in Anogeia and May in
Fourni) to 6.9 % (July, in Anogeia). The strong heat stress
is estimated to appear from March to November (in Kas-
telli and Anogeia) and from April to October in Fourni,
having frequencies from 0.1 % (March, in Anogeia) to
37.5 % (July, in Anogeia). Finally, the thermal comfort
conditions range from 0.3 % (January, in Fourni) to 38.9 %
(May, in Kastelli).
The extreme cold stress class for UTCI does not appear
at any of the mountain stations, while the class of the very
strong cold stress comes up only in January (0.1 %) in
Fourni. The strong cold stress is estimated to appear within
2 months (January to February in Kastelli and Anogeia)
and 4 months (December to March in Fourni), ranging
from 0.1 % (February, in Anogeia) to 1.9 % (February, in
Fourni). On the other hand, the extreme heat stress class is
missing throughout the year with an exception in July
(0.1 %) in Fourni, against very strong heat stress, which
appears within 4 months (June to September in Kastelli
and May to August in Anogeia) and 2 months (July and
August in Fourni), ranging from 0.1 % (May, in Anogeia)
to 2.5 % (July, in Fourni). The strong heat stress is esti-
mated to be within 7 months (April to October, in Fourni
and Anogeia) and 5 months (May to September in Kas-
telli), taking frequencies from 0.1 % (April in Anogeia) to
41.7 % (July in Anogeia). Finally, the thermal comfort
class ranges from 0.3 % (August, in Anogeia) to 93.2 %
(November, in Anogeia). It is worth noting that the small
frequencies of extreme classes of UTCI can be explained
by the nature of this index as its values and scale represent
a very wide range of air temperatures. The climate of Crete
does not present extremely low or high temperatures,
which accounts for the absence of extreme UTCI classes.
The findings extracted by the analysis of bioclimatic
diagrams using ground-based observations are in good
agreement with the results presented by Matzarakis and
Nastos (2011), who used climate data from the 10-min
climatology (New et al. 1999, 2000) in order to create a
PET map of high spatial resolution (1 km 9 1 km) for
Crete Island, within the period 1961–1990.
The intra-annual variations of the daily composite
(averages) of mean daily PET, as well as the highest and
lowest mean daily PETs for each Julian day through the
period 1975–2004 for the examined stations in Crete are
depicted in Fig. 4 (right graphs). Looking at the extreme
values of the mean daily PET, the highest mean daily PET
at the northern coastal stations ranges between 14.1 �C
(February 20, in Heraklion) and 55.8 �C (July 27, in Sou-
da), against 17.1 �C (January 16, in Ierapetra) and 56.8 �C
(July 20, in Tybaki), for the southern coastal stations. The
estimated highest mean daily PET remains above 41.0 �C
(extreme heat stress) for a long period in southern stations
compared to northern ones. As mentioned above, this is
very likely due to the blocking of the northerly cold winds
by the mountain ranges along the island. Taking into
account the lowest mean daily PET, it appears within
-6.1 �C (December 10, in Sitia) and 28.7 �C (August 9, in
Souda) concerning the northern stations, against -3.0 �C
(February 9, in Ierapetra) to 33.0 �C (August 14, in Pal-
aiochora), for the southern stations. Regarding the moun-
tain stations, the highest mean daily PET varies between
13.0 �C (January 20, in Fourni) and 52.0 �C (July 10, in
Kastelli), while the lowest mean daily PET presents values
within the range -10.0 �C (February 18, in Anogeia) and
29.0 �C (July 19 in Anogeia).
The intra-annual variations of the daily composite
(averages) of mean daily UTCI, as well as the highest and
lowest mean daily UTCIs for each Julian day through the
period 1975–2004 for the examined stations of HNMS in
Crete are depicted in Fig. 5 (right graphs). The highest
mean daily UTCI at the northern coastal stations ranges
between 18.0 �C (January 12, in Herkalion) and 42.0 �C
(July 27, in Souda). At the southern coastal stations, the
highest mean daily UTCI lies between 21.0 �C (January
10, in Ierapetra) and 47.0 �C (July 7, in Palaiochora). On
the other hand, the lowest mean daily UTCI for northern
coastal stations varies from -21.0 �C (February 18, in
Heraklion) to 29.4 �C (August 9, in Souda), against
-23.0 �C (February 9, in Ierapetra) and 32.3 �C (August
Fig. 4 Time series of annual number of days within extreme classes
of mean daily PET, along with linear trends, (left graphs) and intra-
annual variation of the daily composite (averages) of mean daily
PET, as the highest and lowest mean daily PETs for each Julian day
through the period 1975–2004 for the examined stations of HNMS in
Crete (right graphs)
b
Bioclimatic conditions on Crete Island 1975
123

1976 A. Bleta et al.
123

14, in Palaiochora), with respect to the southern coastal
stations. Finally, the highest mean daily UTCI for the
mountain station ranges between 16.7 �C (January 20, in
Fourni) and 49.2 �C (July 5, in Fourni), while the lowest
mean daily UTCI presents values within the range
-30.0 �C (January 7, in Fourni) and 29.3 �C (August 10, in
Anogeia).
An analysis of the trends of the time series of annual
number of days with mean daily PET within classes of
strong heat stress, extreme heat stress, strong cold stress,
and extreme cold stress is presented, during the period
1975–2004 (Fig. 4, left graphs). We only focus and com-
ment on statistically significant trends of p \ 0.05
(Table 4). Regarding the northern coastal cities, only in the
case of Sitia, the days with strong cold stress show an
increasing trend (0.460 days/year), while days with
extreme and strong heat stress have a decreasing trend.
Concerning the mountainous stations, Fourni station indi-
cates an increasing trend in extreme heat stress, against
Kastelli, where an increasing trend in extreme cold stress
occurs. On the southern coasts, Tybaki presents an
increasing trend of extreme cold stress and decreasing
trends of strong/extreme heat stress during the study per-
iod. Furthermore, an increasing trend of strong heat stress
appears in Ierapetra.
Additionally, the trends of the time series of annual
number of days with mean daily UTCI within extreme
classes during the period 1975–2004 are depicted in Fig. 5
(left graphs). It is worth mentioning that the time series of
very strong/strong cold stress and very strong heat stress is
missing for the majority of the examined stations with the
exceptions of Palaiochora and Tybaki (southern coastal
stations) presenting increasing and decreasing trends of
strong heat stress, respectively (Table 5). The dominant
class is that of strong heat stress indicating significantly
increasing trends in Souda and Ierapetra, and decreasing
trends in Sitia and Tybaki. This is in agreement with the
trends appearing in the time series of PET strong heat stress.
Further, a comparison between the examined thermal
indices, UTCI, and PET is made. High correlations were
found for these two thermal indices (Table 6), namely the
R-squared varies from 89.7 % in Fourni to 96.4 % in
Anogeia, with slopes from 0.715 in Palaiochora to 0.954 in
Ierapetra. This is in agreement with the findings of Błaz-
ejczyk et al. (2012), who concluded that the values for
indices deriving from human heat balance models, i.e.,
PET, PT (perceived temperature), and SET* (standard
effective temperature), were most similar to those of UTCI,
because these indices indicate equivalent temperature.
In our case, the lowest mean daily PET values range
from ?0.2 �C (at Palaiochora) to -10.1 �C (at Anogeia),
against the lowest mean daily UTCI values ranging from
-7.6 �C (at Palaiochora) to -30.0 �C (at Fourni). The
scattering pattern of UTCI versus PET increases with
decreasing UTCI, and this can be explained due to the PET
fixed clothing insulation under cold conditions against the
wind-dependent clothing insulation of UTCI. As Blaz-
ejczyk et al. (2012) commented UTCI is very sensitive to
changes in air temperature, solar radiation, humidity, and
especially wind speed, whereas PET is more closely related
to air temperature.
Thorsson et al. (2007) showed good agreement of PET
with the perception of interviewees by comparing the
results of structured interviews and of PET evaluation in an
Fig. 5 Time series of annual number of days within extreme classes
of mean daily UTCI, along with linear trends, (left graphs) and intra-
annual variation of the daily composite (averages) of mean daily
UTCI, as well as the highest and lowest mean daily UTCIs for each
Julian day through the period 1975–2004 for the examined stations of
HNMS in Crete (right graphs)
Table 4 Trends of the time series of the annual number of days with mean daily PET within specific classes, representing the extreme/strong
cold and heat stress
Station PET \ 4 �C 4 �C \ PET \ 8 �C 35 �C \ PET \ 41 �C PET [ 41 �C
b ± SE b ± SE b ± SE b ± SE
SOUDA n.s. n.s. n.s. n.s.
RETHYMNO n.s. n.s. n.s. n.s.
HERAKLION n.s. n.s. n.s. n.s.
SITIA n.s. 0.460 ± 0.155* -0.634 ± 0.138* -0.328 ± 0.090*
FOURNI n.s. n.s. n.s. 0.144 ± 0.062*
ANOGEIA n.s. n.s. n.s. n.s.
KASTELLI 0.371 ± 0.145* n.s. n.s. n.s.
PALAIOCHORA n.s. n.s. n.s. n.s.
TYBAKI 0.110 ± 0.044* n.s. -1.001 ± 0.273* -1.352 ± 0.325*
IERAPETRA n.s. n.s. 0.950 ± 0.172* n.s.
* Statistically significant values at p \ 0.05, while n.s. for not significant relationships
b
Bioclimatic conditions on Crete Island 1977
123

urban park and a square in Matsudo, a satellite city near
Tokyo, Japan. Besides, PET has been used in urban built-
up area with complex shading patterns and generated
accurate predictions of thermal environments (Thorsson
et al. 2007; Gulyas et al. 2006). Svensson et al. (2003)
presented the PET distribution map of Goteborg using the
geographic information system. Gulyas et al. (2006) eval-
uated thermal comfort in Szeged, Hungary. Bouyer et al.
(2007) evaluated the thermal comfort in two stadia (Stade
de France, Paris, and the Ataturk Olympic stadium, Istan-
bul), using wind tunnel experiments and PET. They con-
cluded that PET maps should not be regarded as
‘‘absolute’’ results, and detailed analysis of the main heat
transfers, due to wind and radiative contributions, is nec-
essary. A high (or even unacceptable) level of wind
velocity combined with a high amount of solar loads leads
to PET values that could have been obtained with mild
conditions.
Further to the above discussion, we must acknowledge a
constraint related to the PET assessment scale. We used the
PET scale for Western/Middle European countries taking
into consideration that Crete Island has a temperate cli-
mate, not significantly different from the climate of Wes-
tern/Middle European countries. Thus, the use of the PET
assessment scale for Western/Middle European countries is
almost acceptable. A recent study by Cohen et al. (2012)
confirms our assumption, revealing that the acceptable
comfort range of PET for the Mediterranean climate of Tel
Aviv is 19–26 �C, against 18–23 �C for the acceptable
comfort range of PET for Western/Middle European
countries. Besides, the assessment scale is frequently used
in international literature (Matzarakis et al. 1999) to esti-
mate bioclimatic conditions in different places, such as
Istanbul and Paris (Bouyer et al. 2007), Goteborg (Svens-
son et al. 2003), Szeged (Gulyas et al. 2006), Matsudo (a
satellite city near Tokyo), Japan (Thorsson et al. 2007),
Far-Eastern Federal District of the Russian Federation
(temperate monsoon climate zone, which is characterized
by an extreme continental regime of annual temperatures)
(Grigorieva and Matzarakis 2011). Another important issue
of using this assessment scale concerns international tour-
ists, who visit the Island of Crete, meaning that the thermal
comfort of international tourists coming from areas of high
latitude (or moderate climate zones) differentiates from
that of local tourists on Crete Island. International tourists
want to know the bioclimatic conditions of a region
according to their thermal sensation and not to the
respective one of the local people. This conclusion is in
agreement with Lin (2009), who compared a modified PET
scale for Taiwan with the PET scale for Western/Middle
European countries. He concluded that compared to the
thermal acceptable range on Western/middle European
scale (18–23 �C PET), the thermal acceptable range in
Table 5 Trends of the time series of the annual number of days with mean daily UTCI within specific classes, representing the very strong/
strong cold and heat stress
Station -40 �C \ UTCI \ -27 �C -27 �C \ UTCI \ -13 �C 32 �C \ UTCI \ 38 �C 38 �C \ UTCI \ 46�CC
b ± SE b ± SE b ± SE b ± SE
SOUDA – – 0.820 ± 0.388* –
RETHYMNO – – n.s. –
HERAKLION – – n.s. –
SITIA – – –0.963 ± 0.208* –
FOURNI – – n.s. –
ANOGEIA – – n.s. –
KASTELLI – – n.s. –
PALAIOCHORA – – n.s. 0.377 ± 0.145*
TYBAKI – – -1.080 ± 0.321* -0.174 ± 0.754*
IERAPETRA – – 1.010 ± 0.195* –
* Statistically significant values at p \ 0.05, while n.s. for not significant relationships
Table 6 Statistical characteristics of the relationship between Uni-
versal Thermal Climate Index (UTCI) and physiological equivalent
temperature (PET), for the examined sites in Crete Island, during the
period 1975–2004
Stations Slope R-squared (%)
SOUDA 0.813 94.2
RETHYMNO 0.894 91.4
HERAKLION 0.940 91.5
SITIA 0.901 91.7
FOURNI 0.922 89.7
ANOGEIA 0.728 96.4
KASTELLI 0.887 92.8
PALAIOCHORA 0.715 95.2
TYBAKI 0.829 92.6
IERAPETRA 0.954 90.3
1978 A. Bleta et al.
123

Taiwan, which has a hot and humid climate, is much higher
(21.3–28.5 �C PET), confirming the different thermal
requirements of people living in different regions.
Concerning UTCI, one limitation might be the applica-
tion in studies concerning health risk assessment under
extreme conditions (in extreme hot or extreme cold envi-
ronments), where a one-scale deviation might already lead
to a critical decision argument (Weihs et al. 2012). UTCI
has been applied in order to differentiate cities in terms of
thermal stress. Idzikowska (2010) examining the biocli-
matic conditions on the basis of the UTCI in four cities
such as Rome, Budapest, Paris, and Warsaw showed that
‘‘no thermal stress’’ occurs throughout the year in all four
cities. Extreme values of heat appeared in Rome and
Budapest, while cold stress was observed in Warsaw, Paris,
and Budapest. Furthermore, the application of UTCI in
bioclimatic research was performed in Warsaw by Lindner
(2011) and in Czech Republic by Novak (2011). Bakowska
(2010) performed bioclimatic analysis concerning the daily
course of UTCI in Koszalin, Warsaw, and Wroclaw for
different air masses such as arctic, polar maritime, polar
continental, and tropical. The results showed that advec-
tions of polar continental air masses in winter caused most
severe bioclimatic conditions in Poland, while these masses
were responsible for strong heat stress in summer. Kunert
(2010), simulating UTCI in the landscape of the Warsaw
Lowland in different weather conditions, found that relief
features have the greatest influence on the modification of
thermal conditions. Differences of UTCI between the
warmest and the coldest areas, in similar weather condi-
tions, rise above 30 �C. Besides, the impacts of bioclimatic
conditions with respect to UTCI in organic-cause mortality
in Athens and Bangladesh have been analyzed by Nastos
and Matzarakis (2012) and Burkart and Endlicher (2010),
respectively. Besides, UTCI can serve as a suitable plan-
ning tool for urban thermal comfort in subtropical regions
(Brode et al. 2012a, b).
Conclusions
The assessment of the bioclimatic conditions on Crete
Island was carried out based on the analysis of the human
thermal indices PET and UTCI. PET is a universal index
and is irrespective of clothing and metabolic activity, while
UTCI is very sensitive to changes in air temperature, solar
radiation, humidity, and especially wind speed. Besides,
the accuracy of PET and UTCI calculations depends on the
accuracy and the uncertainties of the used meteorological
parameters.
The estimated UTCI thermal comfort class presents
higher frequencies and duration throughout the year
compared to the respective PET class, for all the examined
stations; especially, during the cold months, this UTCI
class dominates and in many cases exceeds 90 % against
PET thermal comfort class, reaching approximately 38 %.
Another finding is that the UTCI values of extreme/very
strong/strong cold stress and very strong heat stress are
missing for the majority of the examined stations with the
exceptions of Palaiochora and Tybaki (southern coastal
stations) showing increasing and decreasing trends of
strong heat stress, respectively. Taking into consideration
the scatter plots of UTCI versus PET, we found that scat-
tering increases with decreasing UTCI, and this can be
explained due to the PET fixed clothing insulation under
cold conditions against the wind-dependent clothing insu-
lation of UTCI.
The analysis showed that during the summer period, the
intensity of heat stress decreases in urban areas on the
northern coasts of Crete, due to the cooling impacts of
‘‘Etesians’’ winds, which do not appear on the southern
coasts. The ‘‘Etesians’’ winds are blocked by the mountain
ranges along the island and thus the southern coastal
regions experience longer periods with estimated PET
extreme/strong heat stress. Nevertheless, the blow of
southern winds (associated with Saharan dust episodes in
spring/summer time) exacerbates the bioclimatic condi-
tions at northern coastal urban areas (such as Heraklion),
because of the development of the hot and dry Fohn winds
coming from the lees of the mountain ranges. On the other
hand, the bioclimatic conditions over the mountainous
regions indicate that the estimated PET extreme heat stress
class shows low frequencies from June to August against
moderate frequencies of extreme cold stress appearing
from October to April.
In the region of Crete Island, the time series of the
annual number of days with mean daily extreme values of
PET/UTCI do not present clear either increasing or
decreasing trends during the 30-year period 1975–2004. It
is worthy to remark that the examined human thermal
indices are based on the energy balance of the human body
and not on individual climatic parameters. Thus, the
observed global warming, mainly referring to air temper-
ature trends, has had no important impacts on human
physiology in the region of Crete Island until now. This is
very likely due to some kind of compensation among the
climatic parameters included in PET/UTCI modeling, such
as air temperature, relative humidity, wind speed, and
cloudiness, and to the synergistic effects of all these
parameters on thermal perception.
Acknowledgments This research is supported by HERAKLEITOS
project, which is co-funded by EU and National Resources. The
authors would like to acknowledge the Hellenic National Meteoro-
logical Service for providing the long meteorological time series.
Bioclimatic conditions on Crete Island 1979
123

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