factors affecting solar ultraviolet irradiance measured since 1990 at thessaloniki, greece
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This article was downloaded by: [University of Illinois Chicago]On: 21 November 2014, At: 22:29Publisher: Taylor & FrancisInforma Ltd Registered in England and Wales Registered Number: 1072954 Registeredoffice: Mortimer House, 37-41 Mortimer Street, London W1T 3JH, UK
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Factors affecting solar ultravioletirradiance measured since 1990 atThessaloniki, GreeceC. Meleti a , A. F. Bais a , S. Kazadzis b , N. Kouremeti a , K.Garane a & C. Zerefos c da Laboratory of Atmospheric Physics, Aristotle University ofThessaloniki , Thessaloniki, Greeceb Finnish Meteorological Institute, Climate Change Unit , Helsinki,Finlandc Biomedical Research Foundation, Academy of Athens , Athens,Greeced Laboratory of Climatology and Atmospheric Environment,National and Kapodistrian University of Athens , Athens, GreecePublished online: 29 Jul 2009.
To cite this article: C. Meleti , A. F. Bais , S. Kazadzis , N. Kouremeti , K. Garane & C. Zerefos(2009) Factors affecting solar ultraviolet irradiance measured since 1990 at Thessaloniki, Greece,International Journal of Remote Sensing, 30:15-16, 4167-4179, DOI: 10.1080/01431160902822864
To link to this article: http://dx.doi.org/10.1080/01431160902822864
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Factors affecting solar ultraviolet irradiance measuredsince 1990 at Thessaloniki, Greece
C. MELETI*†, A. F. BAIS†, S. KAZADZIS‡, N. KOUREMETI†, K. GARANE†
and C. ZEREFOS§¶
†Laboratory of Atmospheric Physics, Aristotle University of Thessaloniki,
Thessaloniki, Greece
‡Finnish Meteorological Institute, Climate Change Unit, Helsinki, Finland
§Biomedical Research Foundation, Academy of Athens, Athens, Greece
¶Laboratory of Climatology and Atmospheric Environment,
National and Kapodistrian University of Athens, Athens, Greece
Factors affecting the solar spectral ultraviolet (UV) irradiance at Thessaloniki,
Greece were investigated using measurements with single- and double-
monochromator Brewer spectroradiometer, which started operating respectively
in 1989 and 1993 and continue up to the present. The two data records were quality
controlled, homogenized and finally merged into one dataset, which was used in
the analysis. Subsets of these data corresponding to different solar zenith angles
(SZAs) and to cloud-free skies were used to quantify the long-term changes in
surface UV irradiance at different wavelengths, and the importance of the factors
responsible for these changes is discussed. It is shown that the calculated UV
changes vary with SZA due to the different atmospheric path of the photons and
the dependence of the diffuse to direct irradiance ratio on the SZA. The effect of
total ozone and aerosols on UV irradiance is examined and the corresponding
radiation amplification factors (RAFs) at the various wavelengths are calculated.
The observed changes in UV irradiance due to ozone are smaller than those
expected for the changes in total ozone, suggesting that the influence of the
ozone is masked by other factors. An important finding of this study is that the
improvement in air quality at Thessaloniki, during the period under examination,
is the main reason for the observed increase in solar UV irradiance.
1. Introduction
The decrease in stratospheric ozone and the character of its expected recovery havebeen the subject of intense research. A worldwide decline in the total ozone column
over the past few decades has been ascertained using ground-based measurements,
as well as satellite observations (e.g. WMO 2003). With the implementation of the
Montreal Protocol, the production of ozone-depleting substances has been reduced
by 95%, resulting in decreasing rates of the concentrations of these chemicals in the
atmosphere. Recently reported evidence for the first stage of ozone recovery (i.e. a
slowdown in the ozone depletion rate) in the upper stratosphere at 35–45 km
(WMO 2007) has confirmed the positive effect of the Montreal Protocol and itsamendments. The direct consequence of the stratospheric ozone recovery is a
decrease in the ultraviolet (UV) irradiance at the Earth’s surface. A number of
*Corresponding author. Email: [email protected]
International Journal of Remote SensingISSN 0143-1161 print/ISSN 1366-5901 online # 2009 Taylor & Francis
http://www.tandf.co.uk/journalsDOI: 10.1080/01431160902822864
International Journal of Remote Sensing
Vol. 30, Nos. 15–16, August 2009, 4167–4179
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models predict the rates and the timing of the return to pre-1980 ozone and UV
values, but not very accurately because of the complexity of the atmosphere’s
system and the interactions between ozone variability and climate change
(Kondratyev and Varotsos 1995, Andrady et al. 2009). Long-term changes in UV
radiance may provide evidence for the success of the implementation of theMontreal Protocol.
As stratospheric ozone is the major atmospheric absorber of solar UV radiation,
the observed changes in ozone are expected to lead to inverted changes in UV levels
at the ground level with relevant impacts on humans and the biosphere
(e.g. Kondratyev and Varotsos 1996, NRPB 2002). However, local changes in
meteorological conditions and atmospheric composition may mask the expected
effect of the ozone recovery on the UV radiation received at the Earth’s surface.
Apart from the total ozone column, clouds, aerosols, ground albedo and altitudealso influence the ground-level UV radiation. Long-term ozone measurements exist
and can be used for partly explaining UV variability in the past using alternative
methodologies (e.g. Efstathiou et al. 1998, Lindfors et al. 2007, Feister et al. 2008).
Attempts to attribute the observed long-term changes in surface solar UV irradiance
to different factors have been reported (e.g. Krzyscin and Puchalski 1998,
Chubarova and Nezval 2000, Kylling et al. 2000, Fioletov et al. 2001, Arola et al.
2003, den Outer et al. 2005, 2006).
The short temporal record and the sparse spatial coverage of UV radiationmonitoring sites continue to cause difficulties in determining UV trends or in
establishing a global UV climate using UV radiation measurements alone. Due to
the complexity of the problem, it is important to develop and validate methods for
investigating the relationships between the measurements of ground-level UV radia-
tion and those of ozone, clouds, aerosols and ground albedo. The effect of ozone is
quantified through the concept of the radiation amplification factor (RAF)
(Madronich 1992) or by comparison of the changes in irradiance at two distinct
wavelengths, one with strong and one with negligible ozone absorption. However,the effects from changes in surface albedo, aerosols or clouds are more difficult to
distinguish and quantify. Aerosols affect surface UV radiation directly, through
scattering and absorption (e.g. Coakley et al. 1983, Charlson et al. 1992), semi-
directly, by changing atmospheric thermodynamics and cloud formation
(e.g. Ackerman et al. 2000, Koren et al. 2004), and also indirectly, by changing the
cloud microphysics (e.g. Twomey 1977, Rosenfeld and Lensky 1998). Krzyscin and
Puchalski (1998) showed that, in highly polluted areas, absorption of solar UV
radiation by urban anthropogenic aerosols may mask the surface UV irradianceincrease associated with low total ozone episodes. Other studies have shown that a
decline in aerosol concentration of up to 60% has led to a statistically significant
increase in solar irradiance under cloud-free skies since the 1980s (Ruckstuhl et al.
2008, Philipona et al. 2009).
As long-term measurements of UV levels are able to confirm the continuing
success of the Montreal Protocol (Andrady et al. 2009), in this work we attempt to
separate and explain the effect of ozone and aerosols. To eliminate the effect of
clouds, we used irradiance measurements in the period 1991–2006 performed undercloud-free conditions at Thessaloniki, Greece. The time series presented are of the
longest duration worldwide and the high quality of the measurements has been
confirmed by various intercomparison campaigns (Bais et al. 2001, Grobner et al.
2005, Garane et al. 2006).
4168 C. Meleti et al.
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2. Data and Methodology
The UV monitoring station of Thessaloniki has one of the longest records of spectral
UV irradiance measurements, conducted by single- and double-monochromator
Brewer spectroradiometers operating on a regular basis at the Laboratory of
Atmospheric Physics, University of Thessaloniki, Greece. For the single monochro-
mator the data record spans 1989–2006 while for the double monochromator the data
are from 1993 to 2006. In this study we are concerned with spectral measurements of
solar UV irradiance on a horizontal surface that have been derived by combiningspectral measurements from both spectroradiometers. The instruments are positioned
on the roof of the Physics Department building (latitude 40.634�N, longitude 22.956� E,
altitude 60 m asl), which is located in the centre of the city of Thessaloniki. The horizon
of their input optics is free to the south and west. Buildings and local obstructions block
the east side up to an angle of 10� and the north side up to an angle of 30�. These
obstacles reduce the diffuse irradiance by up to 2% for both instruments. More details
on the instrument characteristics, the calibration history and the quality control of the
measurements can be found in Garane et al. (2006).The total ozone record spans from 1982 to the present and is derived from the single
monochromator using direct spectral irradiance measurements at five wavelengths in
the UV-B region, nominally at 306.3, 310.0, 313.5, 316.8 and 320.1 nm (Kerr et al.
1981). From these direct irradiance data the aerosol optical depth (AOD) is derived at
all six wavelengths and has been available since 1984. The retrieval of the AOD,
especially at the shorter UV-B wavelengths, is difficult and is associated with sub-
stantial uncertainties (Marenco et al. 1997), requiring accurate and precise calibration
and quality control procedures. The extraterrestrial flux at the six wavelengths hasbeen determined by applying the Langley extrapolation method. The days used for
the Langley method are dispersed throughout the whole period of measurements, and
the extraterrestrial fluxes for each day were determined by linear interpolation. Then
the AOD is calculated as the residual optical depth after subtracting from the total
atmospheric optical depth the optical depths due to molecular scattering and due to
absorption by O3 and SO2. Details on the methodology can be found in Meleti and
Cappellani (2000), Cheymol and De Backer (2003) and Grobner and Meleti (2004).
For the selection of the cloud-free days we used the methodology described inVasaras et al. (2001), which is based on the variability of shortwave solar irradiance
measurements (300–3000 nm) from a collocated pyranometer. In case of missing
measurements, the cloud cover at Thessaloniki International Airport ‘Macedonia’
as reported by the Hellenic National Meteorological Service was used instead.
Interpretation of the measurements was assisted by radiative transfer calculations,
performed with the libRadtran (Library for Radiative transfer) code developed by
Mayer and Kylling (2005). The spectral irradiance in the wavelength range 300–400
nm was calculated for total ozone ranging between 240 and 500 m-atm-cm and forSZAs ranging between 20� and 70�. In these calculations a constant AOD of 0.45 at
350 nm was used, representative of the mean annual value at Thessaloniki.
3. Results
3.1 UV Irradiance and Total Ozone
Spectral UV irradiance measurements at Thessaloniki started in September 1989 with
the single-monochromator Brewer spectroradiometer. During the first year of
Remote sensing and the Montreal Protocol 4169
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operation data were acquired only near local noon. Measurements at SZAs of 50� and
63� were added to the monitoring schedule in October 1990. Since August 1992
spectral irradiance has also been monitored at 5� of SZA intervals from sunrise to
sunset. The same measurement protocol is followed by the double-monochromator
Brewer spectroradiometer, which started operating in May 1993.Although both instruments were calibrated with the use of the same calibration unit
and standard lamps of spectral irradiance, their spectral irradiance measurements
differ because of the different instrumental characteristics. To homogenize the time
series of UV irradiance, the almost coincident measurements of the two instruments
under clear skies were compared. The relationships derived for the various SZAs were
applied and the corresponding datasets were merged into one dataset.
As clouds are a major factor in modifying the irradiance at the surface, the present
study focused on cloud-free measurements to investigate separately the effect of ozoneand aerosol. We analysed the time series of the spectral UV irradiance at selected
wavelengths and for SZAs ranging from 20� to 70� with a step of 5�, and at 63�
(minimum SZA during the whole year). Most of the data subsets cover a period of 16
years, from 1990 to 2006. As an example, figure 1 shows the irradiance at 305 nm
(strong absorption by ozone) and 324 nm (weak absorption by ozone) at SZA = 63�.The statistics of the monthly mean irradiance at these wavelengths and of the corre-
sponding total ozone are given in table 1 for different SZAs.
The estimated long-term variability of the irradiance at selected wavelengths and ofthe total ozone as a function of SZA is shown in figure 2. Evidently, the higher the
wavelength, the larger the observed increase in irradiance. The different time periods
and seasons corresponding to the different SZAs result in different estimates of the
long-term changes, which are positive in all but one case. This is in contradiction to
the changes expected by the long-term variability of total ozone, and hence it must be
1.0
3.0
5.0
Sol
ar ir
radi
ance
(m
w m
–2 n
m–1
)
280
320
360
400
1991 1993 1995 1997 1999 2001 2003 2005 2007Year
50
100
150
305 nm
280
320
360
400
Total ozone (m
-atm-cm
)
324 nm
(a)
(b)
Irradiance
Total ozone+ 9.2%/dec
+ 5.0%/dec
+ 1.1%/dec
+ 1.1%/dec
Figure 1. Monthly mean spectral UV irradiance at (a) 305 nm and (b) 324 nm measured atThessaloniki at solar zenith angle (SZA) 63� (solid line-circles) and the corresponding monthlymean total ozone column (broken line-diamonds). The straight lines represent linear regres-sions on the data.
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Ta
ble
1.
Mo
nth
lym
ean
sa
nd
lon
g-t
erm
cha
ng
esw
ith
the
corr
esp
on
din
gsi
gn
ific
an
cele
vel
for
the
tim
ese
ries
of
tota
lo
zon
ev
alu
esa
nd
the
spec
tra
lir
rad
ian
ces
at
30
5a
nd
32
4n
ma
td
iffe
ren
tso
lar
zen
ith
an
gle
s(S
ZA
s)fo
rT
hes
salo
nik
ia
nd
for
the
per
iod
19
90
–2
00
6.
To
tal
ozo
ne
Irra
dia
nce
at
30
5n
mIr
rad
ian
cea
t3
24
nm
SZ
A(�
)P
erio
dM
ean
(DU
)C
ha
ng
e(%
/dec
ad
e)S
ign
ific
an
cele
vel
Mea
n(D
U)
Ch
an
ge
(%/d
eca
de)
Sig
nif
ica
nce
lev
elM
ean
(DU
)C
ha
ng
e(%
/dec
ad
e)S
ign
ific
an
cele
vel
20
Ma
y–
July
33
2.1
0.2
0.0
54
.94
.59
8.0
40
7.4
4.7
99
.92
5M
ay
–A
ug
ust
33
2.5
1.0
60
.04
8.1
2.2
80
.03
80
.53
.79
9.9
30
Ap
ril–
Au
gu
st3
33
.61
.08
0.0
41
.02
.99
8.0
35
4.6
4.1
99
.93
5A
pri
l–S
epte
mb
er3
28
.51
.89
9.0
34
.91
.36
0.0
32
4.5
4.2
99
.94
0M
arc
h–
Sep
tem
ber
33
1.0
2.5
99
.52
7.3
0.3
99
.52
90
.44
.99
9.9
45
Ma
rch
–O
cto
ber
32
5.4
2.1
99
.52
1.0
2.1
80
.02
53
.05
.99
9.9
50
Feb
rua
ry–
Oct
ob
er3
29
.30
.55
0.0
14
.44
.59
8.0
21
4.9
6.5
99
.95
5F
ebru
ary
–O
cto
ber
32
4.5
3.5
99
.99
.62
.06
0.0
17
6.5
8.2
99
.96
0Ja
nu
ary
–N
ov
emb
er3
26
.02
.99
9.9
5.5
–0
.96
0.0
14
0.6
6.5
99
.96
3Ja
nu
ary
–D
ecem
ber
32
2.4
1.1
90
.03
.85
.09
9.0
11
9.7
9.2
99
.97
0Ja
nu
ary
–D
ecem
ber
32
0.6
3.2
99
.91
.20
.97
0.0
75
.77
.69
9.9
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attributed to other factors affecting UV radiation. It should be mentioned here that
the significance of the changes in irradiance at 310, 315 and 320 nm lies between the
significance of 305 and 324 nm, and increases with wavelength.
Figure 2 suggests that the changes in irradiance at the UV-A wavelengths increase
with SZA. At these wavelengths the ozone absorption is weak, and because the
different SZAs correspond to different seasons (the smallest SZA corresponds onlyto the summer months), this behaviour is probably related to seasonality in the long-
term changes of the aerosol loading over the area and its characteristics.
Using the available datasets of irradiances, the RAF due to total ozone was
calculated. The corresponding theoretical RAF was derived from the libRadtran
model using a constant AOD of 0.4 at 350 nm. The resulted RAFs at selected
wavelengths as a function of SZA are shown in figure 3. Comparison of the two
RAFs reveals that the theoretical one is always higher, leading to the conclusion that
the effect of ozone on irradiance is masked by other factors. The RAF calculated fromthe observations at 320 and 324 nm is negative, suggesting that at these wavelengths,
where ozone absorption is very weak, the aerosols dominate the cloud-free UV
variability.
3.2 UV Irradiance and Aerosols
The ratio of the monthly climatological mean irradiance at 305 nm to that at 324 nm is
affected mainly by the seasonal change in total ozone. This relationship was repre-
sented by an exponential regression separately for SZAs 63� and 70�. It was found that
the ratio exhibits a seasonal dependence, with the highest values appearing from
November to February and the lowest from April to August, indicating the involve-
ment of seasonally dependent factors that affect the UV irradiance more at shorter
20 30 40 50 60 70Solar zenith angle (°)
–4.0
0.0
4.0
8.0
12.0
UV
irra
dian
ce c
hang
e (%
/dec
ade)
0.0
1.0
2.0
3.0
4.0
Ozone change (%
/decade)
Wavelength
305 nm
310 nm
315 nm
320 nm
324 nm
Ozone
Figure 2. Long-term changes (% per decade) for total zone and clear-sky spectral UVirradiance at various wavelengths as a function of solar zenith angle (SZA).
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wavelengths. Such behaviour may be attributed to the aerosol loading, and to confirm
this, the AOD at 320 nm was compared with the irradiance reduced to constant totalozone. The ozone effect was removed from the UV irradiance using the model-derived
RAF. Thus, all measurements were normalized to the irradiance corresponding to the
mean total ozone of the time series (322 DU). The derived irradiance at 305 and 324
nm at an SZA of 63� and the corresponding AOD time series are shown in figure 4.
The seasonal amplitude of the irradiance at 305 and 324 nm has decreased by 60% and
25%, respectively. Both time series show a positive long-term change of about 9% per
decade, while the AOD at 320 nm decreases by about 7% per decade. The negative
AOD changes are probably linked to a series of measures that had been taken duringthe 1990s concerning many aspects of the city’s activities (Petrakakis et al. 2005), such
as the use of low-sulfur crude oil in the industry, improvement in fuel quality, and
renewal of the vehicle fleet.
The same analysis was applied to all subsets of the data, and in all cases the spectral
irradiance increases throughout the examined period, while the AOD decreases. The
estimated changes are shown in figure 5. In general, the increase is more evident at
larger SZAs because of the longer optical path traversed by the radiation in the
atmosphere. The AOD changes range from -12% up to –4% per decade. The differ-ences in the estimated changes can be attributed to the different periods in the year
corresponding to the different SZAs and the different optical characteristics of the
aerosols during these periods.
The effect of the aerosols was also estimated by linearly relating the departures of the
irradiance from the long-term mean to those for the AOD. The slope of the derived
relationships is the RAF due to aerosols for the specific wavelengths and SZAs, and is
shown in figure 6 together with the mean AOD at 320 nm at each SZA. The calculated
20 30 40 50 60 70
0.0
1.0
2.0
3.0
4.0
5.0
RA
F o
zone
320
324
328
332
336
340
Total ozone (m
-atm-cm
)
305 nm
310 nm
315 nm
320 nm
324 nm
Modelled calculated
Total ozone
Solar zenith angle (°)
Figure 3. Ozone RAF calculated from the measurements at various wavelengths as a functionof solar zenith angle (SZA) (lines with symbols) and the corresponding model-derived RAF(lines). The line with crosses corresponds to the mean total ozone column for each SZA.
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RAF is higher at the shorter wavelengths and exhibits the smallest values at 324 nm. In
general, the RAF has a tendency to increase with increasing SZA, and then at SZA 70�
decreases abruptly. Minor peaks of different amplitude are shown between 50� and 63�.All these variations in the RAF result from the different time periods covered by each
20 30 40 50 60 70Solar zenith angle (°)
0.0
4.0
8.0
12.0
16.0
UV
irra
dian
ce c
hang
e (%
/dec
ade)
–16.0
–12.0
–8.0
–4.0
0.0
AO
D change (%
/decade)
Wavelength
305 nm
310 nm
315 nm
320 nm
324 nm
AOD at 320 nm
Figure 5. Long-term changes (% per decade) for AOD and clear-sky spectral UV irradiance atvarious wavelengths reduced to constant total ozone as a function of solar zenith angle (SZA).
1991100
120
140
160
2.5
3.0
3.5
4.0
(a)
(b)
4.5
305 nm+ 9.1%/dec
+ 8.7%/dec
– 7.2%/dec
– 7.2%/dec324 nm
1993
Sol
ar ir
radi
ance
(m
W m
–2 n
m–1
)
1995 1997 1999Year
2001
IrradianceAOD
AO
D at 320
nm
2003 2005 2007
1.00
0.75
0.50
0.25
0.00
0.75
0.50
0.25
0.00
Figure 4. Monthly mean spectral UV irradiance at (a) 305 nm and (b) 324 nm measured atThessaloniki at solar zenith angle (SZA) 63� and reduced to constant total ozone of 322 DU(solid line-circles) and the corresponding monthly mean AOD at 320 nm (broken line-diamonds). The straight lines represent linear regressions on the data.
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subset of data, which are characterized by differences in the AOD (see figure 6) and also
in its optical properties.
Based on the AOD RAF, it was calculated that the observed changes in the aerosols
result in an enhancement of irradiance of about 0.5–2.0% per decade. As the long-
term changes in UV irradiance estimated from the observations are much higher, part
of this increasing trend could be attributed to the improvement in air quality in the
centre of Thessaloniki (Petrakakis et al. 2005), which resulted in a reduction in the
concentration of UV-absorbing air pollutants.
4. Summary and Conclusions
The substances depleting the ozone layer are decreasing because of the implementa-
tion of the Montreal Protocol. Models have been developed to predict the timing of
the recovery, but their accuracy is still questionable, especially for the calculation of
the time of the full recovery. Long-term changes in ozone and the UV can be used to
provide evidence of the success of the Montreal Protocol. Studies have shown that the
UV levels at the ground are dependent not only on the ozone variability but also on
other factors such clouds, aerosols, ground albedo and altitude. Simulations of theUV levels on a global scale are based on ozone recovery scenarios, having as sole input
the predicted (negative) columnar ozone future trends. The tendency for reduced
anthropogenic aerosols in the atmosphere observed in the USA and in Europe during
the past decade would have a large effect on the uncertainty budget of any of the
above simulations. To judge the results of the implementation of the Montreal
Protocol and to improve the model estimations, the effect of other factors affecting
UV irradiance should be determined.
20 30 40 50 60 70Solar zenith angle (°)
0.05
0.10
0.15
0.20
0.25
RA
F A
OD
0.50
0.55
0.60
0.65
AO
D at 320 nm
305 nm
310 nm
315 nm
320 nm
324 nm
AOD at 320 nm
Figure 6. AOD RAF calculated from the measurements at various wavelengths as a functionof solar zenith angle (SZA) (lines with symbols). The line with crosses corresponds to the meanAOD for each SZA.
Remote sensing and the Montreal Protocol 4175
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In this work an attempt to establish the effect of the aerosol loading on UV
irradiance is presented. Spectral UV irradiances at specific wavelengths and SZAs
were analysed and the influence of ozone and aerosols studied for all cases.
Summarizing the results of the analysis, the following conclusions can be drawn.
Spectral UV irradiance, total ozone and AOD data measured at Thessaloniki,Greece since the beginning of the 1990s are used for investigating their long- and
short-term variability. Positive, statistically significant changes in UV irradiance
reaching 5% per decade for 305 nm and 9.2% per decade for 324 nm were calculated
from the analysis of the data in the period 1990–2006.
The total ozone column measured during this 16-year period shows a slight increase
of 1.1% per decade. However, the irradiance at all UV-B wavelengths shows a positive
change with the exception of 300 nm, where the changes are negative because of the
positive ozone change. The observed wavelength-dependent positive changes suggestthe influence of other factors, mainly changes in aerosol amount and characteristics.
This is further supported by the difference found between the calculated and model-
derived ozone RAF.
The RAF due to aerosols (AOD) calculated for various SZAs and wavelengths
shows an increasing tendency with SZA. This is because the AOD changes mostly
affect the direct component of solar irradiance, whose contribution to the global
irradiance decreases with increasing SZA.
The UV irradiance reduced to constant total ozone was compared with AOD datato quantify the influence of aerosols. The AOD over Thessaloniki exhibits a decreas-
ing tendency during the past 16 years. The calculated long-term changes in irradiance
increase with wavelength and SZA. These findings are in agreement with similar
studies (Petrakakis et al. 2005, Kazadzis et al. 2007) carried out in a similar, or slightly
larger (Papadimas et al. 2008), area. AOD changes can partly explain the observed
increases in UV irradiance over the area and the remaining part is probably linked to
changes in the aerosol absorption efficiency, as well as to a decrease in air pollutants.
Global changes in aerosol concentrations may indeed have implications for studiesdealing with ozone recovery due to the Montreal Protocol amendments and the
foreseen changes of UV radiation reaching the Earth’s surface. Maintaining existing
observational capabilities and enhancing the integration of information using long-
term measurements of both UV irradiance and AOD is crucial in separating the
effects due to changes in air quality from those due to changes in ozone-depleting
substances. Under clear skies the most important factor affecting UV radiation is
stratospheric ozone, followed by aerosols, so future levels of surface UV radiation will
depend on the evolution of both these factors, which influence the propagation ofsolar UV radiation in the atmosphere.
Acknowledgements
This work was conducted in the framework of the EC Integrated Project SCOUT-O3
(contract 505390-GOCE-CT-2004). S. Kazadzis acknowledges the Marie Curie Intra-European fellowship VAP-OMI, AOR A/119693 PIEF-GA-2008-219908 and the
Research Committee of the Aristotle University of Thessaloniki for the 2008 excel-
lence award.
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