1. Introduction
Radiation reaching the Earth’s surface under all sky conditions is highly dependent on multiple atmospheric factors that introduce various absorption and scattering processes. Gases and aerosols are the key parameters that govern solar radiation reaching the ground under clear skies. The main absorbing gases are ozone, oxygen, water vapor, and carbon dioxide, while all other atmospheric gases scatter solar radiation at all wavelengths [
1,
2]. The presence of aerosols in the atmosphere in the liquid or solid phase also decreases the amount of solar radiation reaching the Earth’s surface [
3] through absorption and scattering processes. The loss will be approximately 25–35% for a PhotoVoltaic (PV) energy conversion system. This justifies the importance of quantifying and studying the temporal properties of aerosol effects on solar radiation, particularly in areas considered suitable for the exploitation of solar energy using PV conversion systems. More generally, aerosols play a crucial role in the radiation budget of the Earth by affecting its temperature at different time and space scales. Generally, ground-based active and passive remote sensing instruments offer reliable measurements to study aerosol properties. Their long-term, continuous observations enhance our understanding of both global and regional properties and their impact on the Earth’s climate. Among the passive methods, sun-photometers and sky-radiometers are recognized as particularly effective for aerosol measurements [
4,
5,
6]. Consequently, various global and regional observation networks, such as AERONET, have been established. For the active method, LIDAR and RADAR remote sensing instruments are widely used due to their advantages of detecting the vertical distribution of aerosols [
6,
7].
Aerosols have different shapes, size distributions, and residence times. They come from different sources such as the condensation of gases, the action of the wind on the surface of the Earth, volcanoes, fires, and human activity. Aerosol turbidity or atmospheric turbidity can define the state of the atmosphere with suspended aerosols [
8,
9]. The Aerosol Optical Depth
(AOD), the Angstrom exponent
, and the Angstrom coefficient
are the parameters usually used to characterize them. The AOD, which is wavelength-dependent, measures the extinction of sunlight due to scattering and absorption by aerosols in the atmosphere [
4], while the Angstrom coefficient
is related to their quantity [
1]. The parameter
is normally between 0.0 and 0.5 but can exceed this upper limit in the case of a highly charged atmosphere. The Angstrom turbidity equation given hereafter expresses the dependence of AOD
with the wavelength
, the number of particles (
), and their sizes (
):
where the wavelength
is in micrometers.
The Angstrom coefficient
therefore corresponds to AOD at 1
m wavelength. AOD is related to the Angstrom coefficient through Equation (
1) for other wavelengths. The Angstrom coefficient can be obtained from aerosol spectral transmissions at two wavelengths [
10] and appears to be independent of air mass [
11]. The experimental determination of
can be obtained from spectral measurements of direct solar radiation (sun-photometer) but measurements are generally not easy to implement. Several authors have proposed different parametric models to obtain
from integrated measurements of solar irradiance [
12,
13].
The Angstrom exponent
is a reliable index of the particle size distribution of aerosols, i.e., it is a good indicator of the dominant size of atmospheric particles [
14,
15]. Its values vary from 0 to 4. It takes values around 4 when the aerosol particles are very small, of the order of air molecules, while it approaches 0 for large particles. The Angstrom formula (Equation (
1)) applied to two AOD measurements allows one to obtain this indicator by
where
and
are the AOD values obtained, respectively, at the two wavelengths
and
.
Knowing the properties of aerosols through these parameters is very useful in the field of renewable energies because, depending on their nature, they affect the propagation of solar energy in the atmosphere differently. Indeed, aerosols coming from various sources have different optical and physicochemical properties, in addition to being wavelength-dependent [
16]. The classification of aerosols therefore proves to be an important step in quantifying these effects. For this reason, many studies were conducted to classify aerosols [
14,
17,
18]. The correlation between aerosol properties facilitates their characterization, although, in the majority of cases, well-mixed aerosol types are quite difficult to classify [
19]. The most common scatter plot for discriminating aerosol types is between the AOD
and Angstrom exponent
[
20]. Other techniques have also been used, such as the wavelength dependence of Single Scattering Albedo (SSA), the correlation between the fine-mode fraction and SSA [
21], and the correlation between the absorption and extinction of the Angstrom exponent [
22]. Most research studies classify aerosols in the atmosphere into four main types, namely biomass-burning aerosols, urban aerosols, maritime aerosols, and dust aerosols [
16,
21,
23,
24,
25]. The remaining cases that do not belong to the threshold proposed in the literature are characterized as mixed type (MT or undetermined aerosols). These aerosols have different physicochemical, optical, and radiative characteristics depending on their origin. Certain types of aerosols can interact with cloud droplets and, therefore, modify their micro-physical properties, influencing the radiative properties and precipitation processes. Thus, the relationship between
and
will be used in this paper to classify aerosol types for the studied site. High values of
are affected by biomass burning, dust, or urban aerosols where
values close to zero correspond to sea spray and dust, and values above 1.5 indicate the significant presence of smokes or urban aerosols [
22].
This paper has two main parts. The first concerns the estimation of aerosol parameters (, , and ) from measurements of direct solar radiation recorded during the period 2005–2014 at Tamanrasset, in the south of Algeria, and different empirical clear-sky models of direct solar radiation. Eleven empirical models based on the parameters of interest were chosen and tested to select the best one(s) relative to the measurements. The results obtained were then compared to AERONET (AErosol RObotic NETwork) data to select the model best suited to the Tamanrasset site. The second part of the article discusses and presents the method to improve the results, mainly the poor estimate of obtained from the model fitting. An innovative method based on a Recurrent Neural Network (RNN) was therefore developed to improve its estimation thanks to AERONET measurements. This method will be presented, as well as the results obtained, which now make it possible to classify the aerosols present in the atmosphere of Tamanrasset.
5. Conclusions
This article dealt with the estimation of aerosol parameters (Angstrom coefficient , Angstrom exponent , and Aerosol Optical Depth AOD ) in cloudless conditions using clear-sky models and ground measurements of direct solar radiation. The radiometric measurements used were those collected in Tamanrasset, in southern Algeria, during the period from 2005 to 2014. AERONET measurements carried out on the same site were used for comparison and validation purposes. The Tamanrasset radiometric measurements were first processed by considering eleven clear-sky models to estimate the aerosol parameters on which they depend, mainly and . A least-squares fitting method was used to find the best-suited model to approximate the solar radiation measurements. The best estimate of the two parameters and was then used to calculate the spectral and Broadband Aerosol Optical Depth using the Angstrom relationship.
The study first focused on the estimation of the Angstrom coefficient
considering the 11 models and the direct solar radiation measurements. The best estimation of this parameter was obtained with the REST2 or CPCR2 models with, respectively, 0.04 and 0.03 for RMSE and 0.91 and 0.95 for the correlation factor R. Moreover, the monthly variation of
plotted throughout the year showed a maximum value in June, which is consistent with AERONET data and the result found in a previous study on turbidity in Tamanrasset covering the same period [
9].
The second step of this work then continued with the estimation of the Angstrom exponent . The results were not conclusive with the method of fitting the model to the data when the comparison was made with the AERONET data, even in the case of using the best models that provided the best estimate for . There was just a weak correlation with the AERONET measurements, which did not exceed 0.38 at best. A complement to the fitting method was, therefore, necessary. This led us to employ and exploit an unsupervised predicted algorithm, namely the Recurrent Neural Network (RNN). The model predicted with RNN used the Angstrom coefficient as input and the Angstrom exponent as output. The results obtained revealed that the predicted Angstrom exponent was more conclusive with a correlation R of 0.69 with AERONET data.
The spectral AOD was then calculated using the Angstrom relation and the values estimated with the CPCR2 model and the RNN complement. The Angstrom parameters used showed good consistency of the estimated spectral AOD with AERONET measurements taken at different wavelengths. The closest coherence was obtained at the wavelength 0.870 µm, at which low statistical errors (RMSE = 0.05, MAPE = 0.36, and MBE = 0.02) were observed with a strong correlation (R = 0.95). The radiometric observations were performed over a wide spectral range, so the integration of the spectral AOD data was calculated to estimate the Broadband Aerosol Optical Depth, the BAOD. A strong correlation between data obtained from CPCR2-RNN models and AERONET measurements was also found (), confirming the reliability of these models for estimating aerosols’ optical properties. However, we found, as for the spectral AOD, that BAODs obtained from the radiometric measurements were very close to the AODs measured with AERONET at 0.870 µm, with the same very strong correlation (R = 0.95).
Finally, a classification of aerosol types was carried out from the estimated parameters ( and ) and those measured by the AERONET photometer. We observed in Tamanrasset the presence of maritime, dust, and mixed aerosols, both with radiometric data or AERONET. We found that mixed aerosols are present during all seasons, but with a slightly lower occurrence in the winter (DJF), when maritime aerosols are predominant but decrease with the other seasons to reach a minimum in the summer (JJA). Dust aerosols begin their appearance in February to be mainly present in the spring (MAM) and summer (JJA), then disappear in September.