photolysis rate coefficients calculations from broadband uv-b irradiance: model-measurement...
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Atmospheric Environment 39 (2005) 857–866
www.elsevier.com/locate/atmosenv
Photolysis rate coefficients calculations from broadband UV-Birradiance: model-measurement interaction
Gustavo G. Palancar, Rafael P. Fernandez, Beatriz M. Toselli�
Departamento de Fısico Quımica/INFIQC, Facultad de Ciencias Quımicas, Universidad Nacional de Cordoba, Ciudad Universitaria, 5000
Cordoba, Argentina
Received 15 May 2004; accepted 19 October 2004
Abstract
Broadband UV-B irradiance measurements (YES UVB-1) from a 4-year campaign in Cordoba City (311 240 S, 641 110
W, 454m a.s.l.) and the TUV 4.1 model were used to apply a new approach (exp-mod) to convert broadband irradiance
measurements at surface under clear sky conditions to actinic flux and then to J-values. The structure of the model was
used to split each measurement into its diffuse and direct component and, in turn, in wavelengths. The results for the
daily variation of JO3shows an agreement better than 5% for solar zenith angles (SZA) up to 651 and better than 10%
up to 701 compared against an 8-stream discrete ordinate method. The annual variation of JO3for clear sky days at
solar noon shows a general agreement better than 10%. The effects of the natural variation of ozone column and the
Cordoba meteorology on this agreement are analyzed. Empirical relations between experimental measurements and J-
values calculated with a 2-stream d-Eddington method are also presented.
r 2004 Elsevier Ltd. All rights reserved.
Keywords: Actinic flux; Radiative transfer calculations; Cordoba City; Broadband UV-B measurements; Diffuse ratio
1. Introduction
Photodissociation reactions are the driving force of
the atmospheric chemistry. These processes generate
highly reactive species, which are involved in many
mechanisms, and they are responsible for removing
most of the trace gases in the troposphere. As a
consequence of their importance for the chemical
behavior of the atmosphere, the rates at which
the photolysis reactions occur must be included
as input parameters in all photochemical models.
This is done by calculating the photolysis rate
e front matter r 2004 Elsevier Ltd. All rights reserve
mosenv.2004.10.033
ing author. Tel.: +54351 4334169;
4188.
ess: [email protected] (B.M. Toselli).
coefficients (J-values), also called photolysis frequen-
cies, as follows:
J ¼
ZjðlÞsðlÞF ðlÞ dl: (1)
In Eq. (1) jðlÞ is the quantum yield, sðlÞ is the
absorption cross section, and FðlÞ is the actinic
flux. As it can be seen from this equation, a J-value
is proportional to the actinic flux, which is defined
as the radiant flux density incident on a spherical
surface (e.g. Madronich, 1987; Lenoble, 1993; Rugga-
ber et al., 1993). Thus, the appropriate radiometric
quantity to calculate photolysis frequencies is the
actinic flux, and not the irradiance EðlÞ: Actinic
flux can be computed by integrating the radiance
Lðl; y;fÞ over all angles of both hemispheres of a
d.
ARTICLE IN PRESSG.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866858
sphere according to
F �
Zf
Zy
Lðy;fÞ sin y dy df; (2)
where y and f are the zenith angle and the azimuth
angle, respectively. The irradiance, on the other hand,
is the radiation received on a flat horizontal surface and
is calculated by integrating the radiance Lðl; y;fÞ overall angles of the upper hemisphere.
E �
Zf
Zy
Lðy;fÞ cos y sin y dy df: (3)
The irradiance expresses flow of energy and is the
radiometric quantity most frequently measured in the
atmosphere, e.g. with flat-plate radiometers. The factor
cos y which appears in its expression reflects the changein the projected area of the surface as the angle of
incidence is varied (Madronich, 1987). This is the
reason why irradiance is also known as cosine-weighted
irradiance.
The actinic flux can be either calculated by using a
radiative transfer model or directly measured. Actinic
flux detectors have been recently developed (Hofzuma-
haus et al., 1999; Shetter and Muller, 1999) but the
measurements are still experimentally complex and very
expensive. As a result, the current database of actinic
flux measurements is very limited. On the contrary, due
to its widespread use in chemical, biological, and
meteorological applications, a much more extensive
database of global irradiance exists (both broadband
and spectrally resolved). This kind of measurements
exists at several sites nearly all over the world and, at
present, more than a decade of data is available.
Although both radiometric quantities are closely related,
they are not equal and the usage of irradiance instead of
actinic flux to calculate J-values (e.g. O3 or NO2) leads
to errors of approximately 35% (McKenzie et al., 2002).
That is why a considerable effort has been devoted to
find a robust method to convert irradiance to actinic
flux. The theoretical formulation for this transformation
was outlined by Madronich (1987) and many researchers
have proposed empirical conversions for both broad-
band and, more recently, spectrally resolved measure-
ments (Van Weele et al., 1995; Kazadzis et al., 2000;
Webb et al., 2002; McKenzie et al., 2002).
An alternative method to obtain direct measurements
of the J-values is the use of the called J-radiometers or
chemical actinometers (Junkermann et al., 1989; Shetter
et al., 1992; Kraus and Hofzumahaus, 1998; Muller et
al., 1995). In this case each studied molecule requires
selective equipment and, consequently, only a reduced
set of reactions can be studied. Thus, the use of actinic
flux data has a big advantage over a J-radiometer: if the
corresponding cross sections and quantum yields data
are known, the photolysis frequency for any molecule
can be calculated by using Eq. (1). This fact means that
there is a potential to increase our knowledge about the
past photolysis frequencies at surface by using the world
wide historical data set of irradiance.
In this paper we present the results of applying an
approach for converting a set of experimental broad-
band irradiance data to J-values by using the structure
of a radiative transfer model. To show this approach we
will use the ozone (O3) and the formaldehyde (HCHO)
photolysis frequencies at the surface level although
many different reactions have been also tested (e.g. NO2,
NO3, HNO4, etc.). The converted J-values will be
compared against the results of a model which uses an
8-stream discrete ordinate radiative transfer method,
which will be used as a reference all through this work.
However, considering that the 2-stream methods and the
broadband irradiance measurements are the most widely
used tools throughout the world, an empirical relation-
ship between them will be also shown. The analysis will
be focused, on one hand, on the results of the daily
variation of the J-values and, on the other hand, on
their annual variation at midday, both of them at
surface.
The main advantage of this method is that the effect
of the variation of the ozone column along the day can
be included in the J-values calculations. To include the
effects of clouds or the variation of the aerosol loading
some other assumptions, concerning to the diffuse ratio,
should be formulated. In the future, these J-values
calculated at surface from irradiance measurements will
be used as input parameters of an atmospheric model to
assess the air quality and the tropospheric O3 formation
in Cordoba City.
2. Instrumentation and data gathering
The instruments used in this work were manufactured
by Yankee Environmental Systems, Inc. (YES). The
YES UVB-1 pyranometer measures broadband global
UV-B irradiance (280–315 nm) while the YES TSP-700
pyranometer measures broadband global total irradi-
ance (300–3000 nm). Due to the fact that the total
irradiance is quite sensitive to the cloud presence these
data have been used to assure the cloudless condition on
each day. Both instruments were mounted on a wide-
open area in the university campus in Cordoba City,
Argentina (311 240 S, 641 110 W, 454m a.s.l.). Basically,
the site can be described as an open semi-urban place
with some buildings, scattered trees and with different
kind of surfaces such as bare soil and grass. There are no
snow precipitations at any season in Cordoba City. A
more complete description of the characteristic and the
meteorology of the measurement site can be found in
Olcese and Toselli (1998) and Palancar and Toselli
(2002). The global UV-B and total observations were
recorded systematically as 5-min average values from
ARTICLE IN PRESSG.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866 859
March 1999 until September of the same year and
as half-a-minute average values from October 1999
onward.
3. Radiative transfer model
In the present work all the calculations have been
carried out by using the Tropospheric Ultraviolet and
Visible radiation model (TUV) version 4.1a (Madronich,
1993) developed at the National Center for Atmospheric
Research (NCAR, United States). A sensitivity analysis
was carried out on this model in order to establish the
appropriate setup and the best values for the most
important parameters for the calculations at surface in
Cordoba City (Palancar, 2003). According to this
analysis the surface albedo was assumed to be lamber-
tian, wavelength-independent, and with a constant value
of 0.05 throughout the year; the extraterrestrial irra-
diance values were taken from Van Hoosier et al. (1987)
and Neckel and Labs (1984); the wavelength grid ranged
from 280 to 735 nm with 1 nm intervals between 280 and
420 nm and with 5 nm intervals from 420 to 735 nm. A 2-
stream method (d-Eddington approximation) and an 8-
stream discrete ordinate method were used for the
calculations, both with no aerosols and cloudless sky
conditions. In all the calculations the scattering was
computed with a pseudo-spherical correction (Dahlback
and Stamnes, 1991). Although many studies using up to
32 streams have been done, it has been shown that the
differences with the irradiance calculated with 8 streams
are meaningless while the CPU time can increase by a
factor up to 4. Thus, the 8-stream method was used as a
reference against both the experimental measurements
and the 2-stream calculations. The d-Eddington approx-
imation was selected among nine 2-stream approxima-
tions (Toon et al., 1989) due to the good agreement
between its results and the results of the more
sophisticated methods using 8, 16, and 32 streams.
Due to the low levels of tropospheric UV-B-absorbing
pollutants like O3, SO2, and NO2 in Cordoba City
(Olcese and Toselli, 2002), they have not been con-
sidered in the calculations. Total ozone column values
were obtained daily by the Total Ozone Mapping
Spectrometer (TOMS) instrument onboard Earth Probe
spacecraft and were provided by the Ozone Processing
Team of the Goddard Space Flight Center of the
National Aeronautic and Space Administration (NASA,
United States).
4. Theoretical considerations
In this section will be described the formal process to
convert the broadband irradiance measurements at
surface into J-values, the necessary interaction between
the experimental measurements and the model, and the
different assumptions involved in this process.
In general, to convert the irradiance into actinic flux
the measured broadband global irradiance must be split,
in first place, into its direct and diffuse components.
Then, the contribution of each wavelength to both the
direct and diffuse components must be assigned
separately. Finally, the ‘‘spectrally resolved’’ direct and
diffuse irradiances can be converted into the correspond-
ing actinic flux quantity and in J-values.
If the direct part of the solar radiation is considered as
a collimated beam, essentially parallel, and originated
from a very small solid angle, the radiance ðLðl; y;fÞÞ inEqs. (2) and (3) may be taken as constant. Under these
conditions, the integrals in those equations can be
evaluated and the direct part of the actinic flux ðFdirÞ can
be obtained by dividing the direct part of the irradiance
ðEdirÞ by the cosine of the SZA (Madronich, 1987).
Due to the fact that the angular distribution of the
diffuse radiation is not known, no simple assumptions
can be made to relate the diffuse parts of the irradiance
ðEdif Þ and the actinic flux ðFdif Þ: As a consequence, the
relation between the two radiometric quantities is
usually established through the ‘‘diffuse ratio’’ rd (or
through the ‘‘diffusivity factor’’ ¼ 1/rd) defined as
rd ¼Edif
Fdif: (4)
The diffuse ratio depends on the wavelength, the SZA,
and other atmospheric parameters such as clouds and
aerosols. This factor has already been evaluated and
approximated under a range of conditions (Madronich,
1987; Ruggaber et al., 1993; Van Weele et al., 1995;
Hofzumahaus et al., 1999; McKenzie et al., 2002).
According to these studies, for isotropically scattered
radiation rd takes a value of 0.5 while for collimated
light incident from a SZA of 01 rd is equal to 1.
In this way, the total actinic flux at each wavelength
can be derived from the irradiance by using
F tot ¼Edir
cos yþ
Edif
rd: (5)
It should be pointed out that in the diffuse part of the
actinic flux the contribution of the reflection due to the
surface albedo (Fm) is usually included, although, from
the experimental point of view, in most cases this
component is not considered due to the low surface
albedo in the UV-B range.
Once the actinic flux at each wavelength is obtained,
the photolysis frequencies can be calculated by resolving
the integral in Eq. (1). Although this approximation is
widely used in many models, it should be taken into
account that in some specific conditions rd can take
values larger or smaller than 0.5, as for example at larger
SZA and longer wavelengths (horizon brightening),
leading to errors of considerable magnitude in the
ARTICLE IN PRESS
08:00 10:00 12:00 14:00 16:00 18:000.0
0.5
1.0
1.5
2.0
2.5
11/11/99
309 DU
Irra
dia
nce
(W
m-2
)
Local hour
Experimental Exp-mod Modeled
Fig. 1. Daily courses of the UV-B irradiance on 11th
November 1999. Direct measurements, model calculations
and calculations using direct measurements.
G.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866860
photolysis frequencies calculations. The accurate meth-
ods, like the n-stream discrete ordinate methods, avoid
these errors by computing the actinic flux directly. That
is the reason why all the calculations carried out through
formula (5) will be evaluated by comparing them against
an 8-stream method.
4.1. Methodology: model-measurement interaction
The TUV model in the 2-stream version calculates the
actinic flux, and then the J-values, from the previously
calculated irradiance values. These irradiance values are
calculated by using an unique value of ozone column
(the daily value provided by TOMS) for the whole day.
Thus, replacing the calculated irradiance values for the
experimental ones, the J-values calculations will show
the real variation of the ozone column along the day.
As it has been mentioned in the previous section, to
include the irradiance measurements in the model not
only the knowledge of the direct and the diffuse
fractions but also the irradiance values spectrally
resolved are required. Due to the lack of simultaneous
global and diffuse measurements, in order to distribute
the experimental irradiance in its direct and diffuse
components we used the distribution given by the TUV
model running an 8-stream discrete ordinate method.
This procedure is based on the excellent agreement
between the experimental and the modeled irradiance
values. It consists in calculating the broadband global,
direct, and diffuse irradiances with an 8-stream method
and, from these values, calculate the percentages of
diffuse and direct irradiances at each solar zenith angle.
Then, the corresponding broadband experimental irra-
diance values are divided into its direct and diffuse
components according to these percentages. A similar
process is carried out to assign the contribution of each
wavelength to the direct and the diffuse components of
the experimental values. Thus, the experimental irra-
diance values ‘‘spectrally resolved’’ are used as input in
the TUV model replacing the calculated ones. The
actinic flux at each wavelength is subsequently calcu-
lated from the spectral irradiance values using Eq. (5)
and the following equations:
F tot ¼ Fdir þ Fdif þ F"; (6)
F tot ¼ Fdir þ Fdif þ Fdir2A cos yþ FdifA; (7)
F tot ¼Edir
cos yð1þ 2A cos yÞ þ
Edif
rdð1þ AÞ; (8)
where A represents the surface albedo and the last two
terms in Eq. (7) represent the contributions of the
downward direct and diffuse radiation to the upward
diffuse radiation (Madronich, 1987). After carrying out
the actinic flux calculations the program follows the
usual steps (in the 2-stream version) to calculate the J-
values. From now on, the J-values obtained in this way
will be named as ‘‘exp-mod’’.
5. Results and discussion
The key factor to convert irradiance data to actinic
flux is the diffuse ratio. Ruggaber et al. (1993) have
evaluated the diffuse ratio at different wavelengths and
under different conditions. They have shown that for a
Rayleigh atmosphere with a defined ozone column, a
surface albedo of 0.05, at 300 nm, an altitude of 1 km,
and SZA up to 601 the diffuse ratio takes values very
close to 0.5 while at longer wavelength (700 nm), larger
SZA (751), and higher altitudes (10 km) it can take
values lower than 0.3. This change in the rd value is due
to the fact that not only the isotropy conditions (visible
light is less isotropic than the UV-B) but also the diffuse
fraction change considerably under these conditions.
Besides, Mckenzie et al. (2002) suggest that the errors in
the J-values calculated from irradiance data are
associated with departures from the isotropy of the
skylight (e.g. caused by clouds or aerosols) rather than
in calculating the diffuse fraction. In this work a
constant value of 0.5 was used for rd while, in order to
minimize the departures from the isotropy, the day
selected to show the daily variation of the J-values was a
cloudless day after a rain.
5.1. Daily variation
To verify the validity of the approach described in
Section 4 the output of the modified model and the
original broadband global measurements were plotted
along with the global irradiance calculated by using an
8-stream method. The results are shown in Fig. 1 where
it can be seen that the measurements and the output of
the modified model for 11th November 1999 present a
ARTICLE IN PRESS
08:00 10:00 12:00 14:00 16:00 18:000
1x10-5
2x10-5
3x10-5
4x10-5
0
1x10-5
2x10-5
3x10-5
4x10-5
J O3 (
s-1)
Local hour
Exp-mod Modeled
J HC
HO
(s-1
)
Exp-Mod Modeled
(a)
(b)
Fig. 2. Daily courses of the J-values for formaldehyde (a) and
ozone (b) photolysis calculated from experimental measure-
ments (exp-mod) and by using an 8-stream model.
G.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866 861
very good agreement. The differences between measure-
ments and a 2-stream d-Eddington method have been
analyzed for 29 clear sky days along 4 years in Palancar
and Toselli (2004a) where it was found a model-
measurement agreement better than 75% for SZA less
than 701.
In order to evaluate the conversion of the daily
variation of broadband irradiance to J-values many
reactions were analyzed. These reactions are listed in
Table 1. In order to show the results, reactions 2 and 8
were chosen. These reactions were selected due to their
well-known importance for the tropospheric chemistry
in the UV-B range. Fig. 2 shows the daily variation of
JHCHO (a) and JO3(b) calculated from the experimental
irradiance data. The J-values calculated with an 8-
stream discrete ordinate method is also shown in each
figure. Fig. 3 shows the differences between JO3
calculations. Here it can be seen that the agreement is
better than 5% for SZA up to 651 and better than 10%
up to 701. Beyond the 701 the differences show a steep
increase (in negative values) to reach 50% for a SZA of
801. However, these last differences are not critical
because they arise as a consequence of the low J-values
at sunrise and sunset and due to the well-known
problems for models and UV-B monitoring sensors at
these large SZA. Another important factor which can
also contribute to the differences at large SZA is the
departure from the isotropy. The differences for all the
other studied reactions are less than 20% at all SZA.
In Fig. 3 two important features should be remarked.
First, the spikes observed between 151 and 201 and also
at nearly 301 and 451 are consequences of the
instabilities shown in Fig. 2b. These numerical instabil-
ities, not present in the typical 2-stream calculations,
have appeared in the JO3exp-mod values. They are of
unknown origin but they were generated in the
calculation of the J-values because they were observed
neither in the irradiance (see Fig. 1) nor in the exp-mod
actinic flux values (not shown). The 8-stream results also
exhibit some numerical instabilities. This kind of
Table 1
Photolysis reactions of tropospheric relevance analyzed in this study
No. J Reaction
1 JO3O3+hn-O(3P)+O2
2 JO3O3+hn-O(1D)+O2
3 JNO2NO2+hn-NO+O(3P)
4 JNO3NO3+hn-NO2+O(3P)
5 JHONO HONO+hn-NO+OH
6 JHNO3HNO3+hn-NO2+OH
7 JHO2NO2HO2NO2+hn-NO2+HO2
8 JCH2O HCHO+hn-H+CHO
9 JCH2O HCHO+hn-H2+CO
10 JCH3OOH CH3OOH+hn-CH3O+OH
instabilities was previously observed in the TUV model
even by using 16 and 32 streams (Palancar, 2003) and
they usually affect only one wavelength. The irradiance
at this wavelength take a value either very high or very
low affecting the whole integral. Since these instabilities
are of random nature, only sporadic, and easily detected
(cf. Figs. 1 and 2b) they affect neither the analysis nor
the results of the present work. The second feature is
related to the observed changes in the J-values along the
day as a consequence of the natural changes in the
properties of the atmosphere. The daily variation of
many factors, which define the atmospheric conditions
(aerosol loading, contaminant levels, ozone column
content, etc.), is different for each day and it depends
Range (nm) Zone
315olo1200 Troposp., Stratosp.
lo315 Troposp., Stratosp.
lo420 Troposp., Stratosp.
lo580 Troposp., Stratosp.
300olo400 Troposphere
180olo330 Troposp., Stratosp.
190olo325 Troposp., Stratosp.
260olo360 Troposp., Stratosp.
260olo360 Troposp., Stratosp.
lo360 Troposphere
ARTICLE IN PRESSG.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866862
on the characteristics of each site. Hence, models do not
include the daily variation of the atmospheric properties,
and the calculations are only related to the SZA, that is
to say, at equal SZA, equal J-value, irradiance, or
actinic flux. This leads to the characteristic symmetry
(respect to the solar noon) between morning and
afternoon. Fig. 3 shows that, even though the sky was
cloudless throughout the day, the atmospheric condi-
tions have changed from the morning to the afternoon.
By using this method the changes along the day in the
properties of the atmosphere can be observed and
analyzed. In fact, for the particular conditions presented
in the analyzed day, the exp-mod JO3-values show
differences up to 7% for the same SZA (701) in the
morning and in the afternoon. These differences reach
10% for SZA up to 801.
The JHCHO calculations show a variation similar to
the JO3calculations. The agreement is better than 3% at
SZA less than 701 and better than 15% for SZA up to
10 20 30 40 50 60 70 80
-50
-40
-30
-20
-10
0
10
20
30
J O3
dif
fere
nce
s (
%)
Solar zenith angle (°)
Fig. 3. Percentage differences between 8-stream and exp-mod
calculations for ozone photolysis. The spikes are due to the
model instabilities. The differences between the morning and
the afternoon reveal the changing atmospheric conditions along
the day.
Table 2
Percentage differences between 8-stream and exp-mod calculations at
No. Reaction SZA
141 201
1 O3+hn-O(3P)+O2 3.1 3.1
2 O3+hn-O(1D)+O2 2.6 4.9
3 NO2+hn-NO+O(3P) 3.9 4.1
4 NO3+hn-NO2+O(3P) 4.1 4.3
5 HONO+hn-NO+OH 3.5 3.7
6 HNO3+hn-NO2+OH 2.3 1.6
7 HO2NO2+hn-NO2+HO2 2.1 1.5
8 HCHO+hn-H+CHO 0.0 0.0
9 HCHO+hn-H2+CO 1.5 1.6
10 CH3OOH+hn-CH3O+OH 2.1 2.0
801. As in the JO3case the best agreement is reached at
midday. Correspondingly, after 651 the calculations
using 2 streams (exp-mod) increasingly overestimate
those ones which use 8 streams. The differences between
morning and afternoon for the exp-mod JHCHO-values
are not as pronounced as in the JO3results. In this case
the maximum deviation is smaller than 4%.
Table 2 shows the variations of the differences
between the 8-stream and the exp-mod calculations as
a function of the SZA (during the morning) for all the
studied reactions. The minimum SZA (141) corresponds
to the solar noon. In this table two different trends can
be observed. In reactions 1, 3, 4, and 5 the exp-mod
calculations undervalue the 8-stream results at all SZA.
On the other hand, reactions 2, and from 6 to 10, show a
behavior in which for SZA greater than 65–701 the 2-
stream calculations overestimate the 8-stream ones.
With only one exception (reaction 2), all the exp-mod
results at solar noon undervalue the 8-stream ones.
5.2. Annual variation
As it can be seen from Fig. 3 and Table 2 the best
agreement between both methods is reached at solar
noon. Thus, in order to analyze the annual variation of
the J-values we plotted the results for the 4 years of
irradiance measurements at the SZA corresponding to
this time. Fig. 4 shows the annual and the interannual
variation of the J-values for reaction 2 calculated for 277
cloudless days by using the exp-mod method and the 8-
stream method. The J-values for the exp-mod method
range from 1.08� 105 s1 to 5.16� 105 s1 while for
the 8-stream calculations the results show a minimum of
1.01� 105 s1 and a maximum of 5.35� 105 s1. The
maximums are located between December and January
while the minimums are between June and July,
according to the seasonal variations of irradiance in
Cordoba City. As it was shown in Palancar and Toselli
surface for the photolysis reactions listed in Table 1
301 401 501 601 701 801
3.5 4.1 4.5 4.9 5.2 5.6
4.0 2.2 1.3 2.0 6.7 30.8
4.6 5.3 5.8 6.4 6.4 5.8
4.6 5.0 5.4 5.9 6.3 6.9
4.2 4.8 5.3 5.7 5.4 3.9
3.2 7.3 6.7 5.9 0.0 10.6
3.0 6.7 6.1 5.3 0.8 12.3
0.0 0.1 0.1 0.1 0.0 0.1
2.0 2.8 2.9 2.9 1.2 3.2
2.9 4.5 4.4 4.0 1.6 3.3
ARTICLE IN PRESS
10/15/1998 7/15/1999 4/15/2000 1/15/2001 10/15/2001 7/15/2002
0
2x10-5
4x10-5
6x10-5
J O3
O
(1D
) (s-1
)
Day
Exp-modModeled
↑
Fig. 4. Annual and interannual variation of the ozone photolysis at solar noon in Cordoba City. Exp-mod and 8-stream calculations
for cloudless days.
10/15/1998 7/15/1999 4/15/2000 1/15/2001 10/15/2001 7/15/2002
-40
-30
-20
-10
0
10
20
30
40
Dif
fere
nce
(%
)
Date
Fig. 5. Percentage differences between 8-stream and exp-mod calculations of J-values for ozone photolysis at solar noon in Cordoba
City. Only data for cloudless days were included (see Fig. 4).
G.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866 863
(2004b), the maximums do not agree with the summer
solstice but they are shifted toward January due to the
effect of the natural variation of ozone column. Fig. 5
shows the differences between both methods. In this
figure the full horizontal lines show the 720% limits
while the dotted lines show the 710% difference. For
nearly 84% of the days the agreement was better than
10%, in accordance with the results shown in Section 5.1
for 11th November 1999 (see Fig. 3). The rest of the
measurements shows an agreement up to 720% with a
few exceptions exceeding this value. However, note that
these differences of 720% take place periodically. The
+20% differences are originated in aerosol-loaded days,
due to the fact that the 8-stream calculations have been
done under cloudless and no-aerosol conditions. These
periodic increments in the aerosol loading occur in late
winter and spring, between August and November, due
to the particular meteorology of Cordoba City. The
ARTICLE IN PRESS
0.0 0.5 1.0 1.5 2.0 2.50
1x10-5
2x10-5
3x10-5
4x10-5
5x10-5
1x10-5
2x10-5
2x10-5
3x10-5
3x10-5
y= 1.90 x10-5 X - 1.4 x10-6
r2= 0.9661N= 277
J O
3 (s
-1)
UV-B irradiance (Wm-2)
y= -2.0 x10-6 X2 + 1.57 x10-5 X + 9.3 x10-6
r2= 0.9709N= 277
J H
CH
O (
s-1)
(a)
(b)
Fig. 6. Empirical relationship between calculated J-values for
formaldehyde (a) and ozone (b) photolysis, in units of s1, and
experimental UV-B irradiance measurements, in units of
Wm2.
Table 3
Fit parameters for the relationships between experimental UV-
B irradiance and J-values, in units of s1, calculated by using a
2-stream model. X represents the irradiance value in units of
Wm2
Jðs1Þ ¼ aX 2 þ bX þ c
a b c
JO3!Oð1DÞ 0 1.9� 105 1.4� 106
JO3!Oð3PÞ 8.6� 106 7.3� 105 3.1� 104
JNO2!Oð3PÞ 3.8� 104 2.6� 103 4.9� 103
JCH2O!H 1.8� 106 1.5� 105 9.7� 106
JCH2O!H22.6� 106 1.9� 105 2.0� 105
G.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866864
determining factors for this behavior are the strength of
the winds and the lack of rain (Palancar and Toselli
(2004b) and references therein). Aerosols not only
decrease the total radiation reaching the surface but
also they are one of the most important factors affecting
rd (Cotte et al., 1997). Thus, aerosols contribute to the
departures from the assumed isotropy condition causing
these higher errors. Besides, the 20% differences imply
that the experimental measurements overestimate the
model calculations. These differences are related to the
fact that TOMS can provide only one datum per day.
Thus, while the measurements reflex the real variation of
the ozone column along the day, the calculations have to
be done assuming a constant ozone column content. In
Palancar and Toselli (2004a) it has been shown that
although this assumption does not represent the reality,
in most cases (97%) this approximation leads to good
results because in Cordoba City the delta ozone between
two consecutive days is usually small (10% respect to an
average of 11 years). However, differences as large as 80
Dobson Units (DU) have also been registered between
consecutive days. A statistical analysis of the last 11
years of the ozone column content over Cordoba City
(1991–2002) showed that these large variations occur
systematically during the winter time. As these varia-
tions only affect the exp-mod results they lead to the
observed differences in the J-values determinations.
Due to the fact that the aerosols in Cordoba present
absorbing properties the 20% differences can only be
produced by ozone variations while the +20% can be
originated by either aerosols or ozone variations. Also in
this case the usage of the experimental values allows to
see the actual atmospheric conditions, which can be very
different from those assumed in model calculations.
5.3. Empirical relationships
The first attempts to relate irradiance with photolysis
frequencies have been done through empirical relation-
ships between broadband measurements at surface and
calculations carried out with 2-stream methods. Due to
the fact that these relations are highly dependent on the
particular meteorological conditions predominant in the
site where the measurements were taken their use to
compare with measurements in different places is very
limited. Nevertheless, they can be useful as a first step to
characterize the J variations at a specific site. To show
these relations we have used only clear sky days
(N ¼ 277) of a period of 4 years of measurements
(1999–2002) and a 2-stream method (d-Eddington).Within the reactions analyzed two different behaviors
have been observed: linear or quadratic relationships. In
order to show some examples reactions 1, 2, 3, 8, and 9
were selected. Fig. 6 shows the relationship found
between the broadband irradiance measurements
(Wm2) at solar noon and the calculated JHCHO (a)
and JO3(b) values (s1). From this figure it can also be
seen the minimum and the maximum values for the UV-
B irradiance along the year. Table 3 summarizes the fit
parameters only for the selected reactions. As it was
expected, for reaction 2 a linear relation was found. For
reactions 1, 3, 8, and 9 a quadratic relation was found.
These differences are related with the wavelength range
involving both the cross section and the quantum yield
of each molecule.
6. Summary and concluding remarks
Broadband UV-B irradiance measurements (YES
UVB-1) from a 4-year campaign in Cordoba City and
ARTICLE IN PRESSG.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866 865
the TUV model were used to apply a new approach
(exp-mod) to convert broadband irradiance measure-
ments at surface to actinic flux and J-values. In this
approach each broadband measurement was split in its
diffuse and direct components and, in turn, in wave-
lengths, based on the percentages given by an 8-stream
method. These data were used as input parameters of the
model to calculate the J-values. Clear sky days and a
constant rd value of 0.5 were used. The main advantages
of this procedure reside in that the J-values can be
calculated from the most common type of measurements
and that it allows to consider the random variations of
the atmospheric conditions along the day. It was shown
that these variations can lead to differences of up to
10% in the J-values for the same SZA (morning-
afternoon). According to the results showed in Section
5.1 for JHCHO and JO3the usage of this method to
calculate the daily variation of J-values leads to a good
agreement with more sophisticated methods (8-stream
discrete ordinate). The results for JO3show an agree-
ment better than 5% for SZA up to 651 and better than
10% for SZA up to 701 although for SZA larger than
701 the differences reached 50%. Therefore, this method
could be included in global atmospheric models to
calculate J-values with an acceptable accuracy and
without consuming as much CPU time as an 8-stream
method. Besides, this work showed that the widely
spread (geographically and temporal) database of
irradiance measurements could be used to extend the
database of either actinic flux or J-values measurements.
Although the method showed a good agreement against
more accurate calculations it should be also validated
against actual actinic flux or photolysis frequencies
determinations, which will be done in future works.
The annual variation of JO3was also analyzed. The J-
values for the exp-mod method ranged from 1.08� 105
to 5.16� 105 s1 while for the 8-stream calculations the
results showed a minimum of 1.01� 105 s1 and a
maximum of 5.35� 105 s1. The agreement for 277
days along the campaign was better than 10%. Some
deviations up to 20% were found although they were
originated by the natural variation of the ozone column
and by the meteorology of Cordoba City (aerosol
loading). Two kinds of empirical relations between the
irradiance measurements and the J-values calculated by
using a 2-stream d-Eddington method were found: linealand quadratic.
Acknowledgements
The authors would like to thank Fundacion An-
torchas, TWAS, CONICET, SeCyT (UNC), and the
Agencia Nacional de Promocion Cientıfica y Tecnolo-
gica (prestamo BID 1201/OC-AR No. PICT 06-06358)
for partial support of this work. G.G. Palancar thanks
CONICET for a post doctoral fellowship. R.P. Fernan-
dez thanks Agencia Cordoba Ciencia and CONICET
for a graduate fellowship. We are very thankful to Dr.
Sasha Madronich for his valuable help with TUV
model.
References
Cotte, H., Devaux, C., Carlier, P., 1997. Transformation of
irradiance measurements into spectral actinic flux for
photolysis rates determination. Journal of Atmospheric
Chemistry 26, 1–28.
Dahlback, A., Stamnes, K., 1991. A new spherical model for
computing the radiation field available for photolysis and
heating at twilight. Planetary and Space Science 39 (5),
671–683.
Hofzumahaus, A., Kraus, A., Muller, M., 1999. Solar actinic
flux radiometry: a new technique to measure photolysis
frequencies in the atmosphere. Applied Optics 38 (21),
4443–4460.
Junkermann, W., Platt, U., Volz, T.A., 1989. A photoelectric
detector for the measurement of photolysis frequencies of
ozone and other atmospheric molecules. Journal of Atmo-
spheric Chemistry 8, 203–227.
Kazadzis, S., Bais, A.F., Balis, D., Zerefos, C.S., Blumthaler,
M., 2000. Retrieval of downwelling UV actinic flux spectra
from spectral measurements of global and direct solar UV
irradiance. Journal of Geophysical Research 105 (D4),
4857–4864.
Kraus, A., Hofzumahaus, A., 1998. Field measurements of
atmospheric photolysis frequencies for O3, NO2, HCHO,
CH3CHO, H2O2, and HONO by UV spectroradiometry.
Journal of Atmospheric Chemistry 31 (1), 161–180.
Lenoble, J., 1993. Atmospheric Radiative Transfer. Deepack
Publishing, Hampton-Virginia.
Madronich, S., 1987. Photodissociation in the atmosphere 1.
Actinic flux and the effects of ground reflections and clouds.
Journal of Geophysical Research 92 (D8), 9740–9752.
Madronich, S., 1993. UV radiation in the natural and perturbed
atmosphere. In: Tevini, M. (Ed.), UV-B Radiation and
Ozone Depletion. Effects on Humans, Animals, Plants,
Microorganisms, and Materials. Lewis Publisher, Boca
Raton, pp. 17–69.
McKenzie, R., Johnston, P., Hofzumahaus, A., Kraus, A.,
Madronich, S., Cantrell, C., Calvert, J., Shetter, R., 2002.
Relationship between photolysis frequencies derived from
spectroscopic measurements of actinic fluxes and irradiances
during the IPMMI campaign. Journal of Geophysical
Research 107, D5 10.1029/2001JD000601, ACH 1.
Muller, M.A., Kraus, A., Hofzumahaus, A., 1995. O3 - O(1D)
photolysis frequencies determined from spectroradiometric
measurements of solar actinic UV-radiation: comparison
with chemical actinometer measurements. Geophysical
Research Letters 22, 679–682.
Neckel, H., Labs, D., 1984. The solar radiation between 3300
and 12500 A. Solar Physics 90, 205–258.
Olcese, L.E., Toselli, B.M., 1998. Unexpected high levels of
ozone measured in Cordoba, Argentina. Journal of Atmo-
spheric Chemistry 31, 269–279.
ARTICLE IN PRESSG.G. Palancar et al. / Atmospheric Environment 39 (2005) 857–866866
Olcese, L.E., Toselli, B.M., 2002. Some aspects of air pollution
in Cordoba, Argentina. Atmospheric Environment 36,
299–306.
Palancar, G.G., 2003. Estudio de procesos cineticos y radiativos
de interes atmosferico. Ph.D. Thesis, Universidad Nacional
de Cordoba, Argentina.
Palancar, G.G., Toselli, B.M., 2002. Erythemal ultraviolet
irradiance in Cordoba, Argentina. Atmospheric Environ-
ment 36, 287–292.
Palancar, G.G., Toselli, B.M., 2004a. Effects of meteorology on
the annual and interannual cycle of UV-B and total
radiation in Cordoba City, Argentina. Atmospheric Envir-
onment 38, 1073–1082.
Palancar, G.G., Toselli, B.M., 2004b. Effects of meteo-
rology and tropospheric aerosols on UV-B radia-
tion: a four year study. Atmospheric Environment 38,
2749–2757.
Ruggaber, A., Forkel, R., Dlugi, R., 1993. Spectral actinic flux
and its ratio to spectral irradiance by radiation transfer
calculations. Journal of Geophysical Research 98 (D1),
1151–1162.
Shetter, R.E., Muller, M., 1999. Photolysis frequency measure-
ments using actinic flux spectroradiometry during the PEM-
Tropics Mission: instrument description and some results.
Journal of Geophysical Research 104, 5647–5662.
Shetter, R.E., McDaniel, A.H., Cantrell, C.A., Madronich, S.,
Calvert, J.G., 1992. Actinometer and Eppley radiometer
measurements of the NO2 photolysis rate coefficient during
MLOPEX. Journal of Geophysical Research 97,
10,349–10,360.
Toon, O.B., McKay, C.P., Ackerman, T.P., Santhanan, K.,
1989. Rapid calculation of radiative heating rates and
photodissociation rates in inhomogeneous multiple scatter-
ing atmospheres. Journal of Geophysical Research 94
(D13), 16,287–16,301.
Van Hoosier, M.E., Bartoe, J.D., Brueckner, G.E., Printz,
D.K., 1987. Solar Irradiance measurements 120–400nm
from Space Lab-2. IUGG Assembly, Vancouver.
Van Weele, M., Villa-Guerau De Arellano, J., Kuik, F., 1995.
Combined measurements of UV-A actinic flux, UV-A
irradiance and global radiation in relation to photodissocia-
tion rates. Tellus 47 (Ser. B), 353–364.
Webb, A.R., Kift, R., Thiel, S., Blumthaler, M., 2002. An
empirical method for the conversion of spectral UV
irradiance measurements to actinic flux data. Atmospheric
Environment 36, 4397–4404.