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Erosive rainfall in the Rio do Peixe Valley: Part III--Risk of extreme events/Chuvas erosivas do Vale do Rio do Peixe: Parte III--Risco de eventos extremos.

Palavras-chave:

conservacao do solo erosao hidrica precipitacao probabilidade

Introduction

Water erosion is considered one of the main forms of environmental degradation, causing losses of arable land as well as contaminating and silting watercourses and dam reservoirs (Alves Sobrinho et al., 2011; Syvitski & Kettner, 2011; Almeida et al., 2012; Mello et al., 2015).

Among the several mathematical models that were developed to estimate soil erosion and evaluate impacts of different land uses and management practices, the Universal Soil Loss Equation (USLE) is the most prominent (Kinnell, 2010; Oliveira et al., 2011). Bertoni & Lombardi Neto (2010) state that determining erosive factors through USLE contributes to a more accurate prediction of soil losses. In addition, it serves as a guide for planning the use, and development of more appropriated conservation practices for an area.

The rainfall erosivity factor (USLE R factor) is considered very important in the estimation of soil loss (Shamshad et al., 2008). The value of R corresponds to the average of the annual erosivity EI30 index, and is evaluated by using a long pluviographic data series (Cassol et al., 2008; Silva et al., 2009). Several studies show that there is a large annual variation in rainfall erosivity (Eltz et al., 2013; Valvassori & Back, 2014; Back et al., 2016).

Knowledge of the future soil erosion processes is very important for managers and decision makers (Hazbavi & Sadeghi, 2016; Davudirad et al., 2016). Sadeghi et al. (2017) highlights that a proper forecasting of rainfall erosivity and soil erosion is difficult due to the governing uncertainties regarding rainfall storms: they can vary from day to day and be random and unpredictable. Nonetheless, such processes might be evaluated based on probabilistic approaches like frequency distribution analysis leading to an estimation of variable magnitudes with different return periods.

Although there are studies carried out evaluating the risk of erosivity (Bazzano et al., 2007; Colodro et al., 2002; Eltz et al., 2011; Santos & Montenegro, 2012), most use empirical distribution to estimate the return period, or the Gumbel distribution without assessing its adherence. Few studies investigate the risk of extreme events related to erosivity in the state of Santa Catarina. Therefore, the objective of the this study was to determine the rainfall erosivity values with different return periods for the Valley of the Rio do Peixe in Santa Catarina, Brazil.

Material and Methods

Daily pluviographic data series from the Agricultural Research and Rural Extension Service of Santa Catarina's (EPAGRI) of three meteorological stations located in the Valley of the Rio do Peixe in Santa Catarina were used. The data used were from 1984 to 2014 for the Campos Novos, and Cacador stations, and from 1986 to 2014 of the Videira station.

The pluviograms were digitized and a computer program was developed to read the digitized data in order to identify and individualize erosive rainfall and calculate the EI30 erosivity index of each erosive rainfall, as described by Valvassori & Back (2014).

The data series of maximum annual rainfall intensity in 30 min (I30), the rainfall erosivity index (EI30), and the total annual erosivity (EI30) were analysed. The parameters of the Gumbel-Chow distribution were adjusted for each data series and the probability of an event X occurring greater or equal to x is given by

[mathematical expression not reproducible] (1)

Y being the reduced variable calculated by

Y = (X-[beta])[alpha] (2)

The model parameters ([alpha] and [beta]) can be estimated as follows:

[alpha] = Sn/S (3)

P = X - (4)

[beta] = [bar.x] - Yn/[alpha] (4)

Wherein x is the mean observed values of X; S is the standard deviation of the observed values of X; and Sn is the standard deviation of the reduced variable Y, calculated for each position i of a sample of size n through Eq.5 (Kite, 1977).

Sn = [square root of [n.summation over (i=1)][([Y.sub.i] - [Y.sub.n]).sup.2]/n] (5)

Wherein Yi is the reduced variable calculated for each position i of a sample of size n through:

Yi - ln[-ln(1 - i/n+1)] (6)

Wherein Yn is the average of the Yi values.

In this way, the extreme variable with return period T ([X.sub.T]) can be estimated by the equation:

[X.sub.T] = [beta] + [Y.sub.T]/[alpha] (7)

The reduced variable of Gumbel distribution is calculated by:

[Y.sub.T] = -ln [-ln(1 - 1/T)] (8)

The data series' adherence to the adjusted distribution was tested by the Kolmogorov-Smirnov test at a significance level of 5%. The null hypothesis tested is the observed data following the theoretical distribution. The statistic test is given by the largest absolute difference between the values of F (x), that is:

[D.sub.max] = |F(x) empirical - F(x) theoretical (9)

Each value of X is compared to the critical values ([D.sub.crit]) for a given significance level ([alpha]) and sample size (n) (Steel & Torrie, 1981). If the calculated [D.sub.max] is greater than [D.sub.crit], the null hypothesis must be rejected.

Results and Discussion

Table 1 shows the descriptive statistics of the data series of annual maximum rainfall intensity in 30 min (I30), and kinetic energy of rainfall (EI30). It also shows the parameters of the Gumbel-Chow distributions adjusted with the results of the adhesion test, shown in Figure 1.

A higher I30 for the extremes and mean values, and a higher standard deviation were found in Campos Novos. Contrastingly, the lowest values were recorded in Cacador. This is partly due to data record failures, which resulted in the exclusion of values, presenting the annual maximum data series with 22 values.

The results of I30 are consistent with a study on heavy rains conducted by Back (2013), who analysed data from thirteen rain gauge stations in Santa Catarina and described the mean intensity in 30 min ranging from 33.4 to 64.4 mm with a coefficient of variation ranging from 17.3 to 39.3%. In Campos Novos (Figure 1A) and Videira (Figure 1C), the [D.sub.max] value was around 0.06; therefore, the difference in probabilities between the data series observed and estimated are less than 6%. In Cacador, that maximum difference is 11.86% (Figure 1E); however, the [D.sub.max] were lower than the critical value [D.sub.crit], indicating that adjusted distribution can be used to estimate the extreme values of I30 in all data series.

In the data series of annual maximum EI30, greater dispersion was observed with a coefficient of variation between 47 and 50%. The highest [D.sub.max] (0.1423 was recorded for Campos Novos. However, this was still lower than the critical value. Larger differences occur in the lower segment of the probability curve (Figure 1B), which shows the lowest values. The higher segment, or interest range, represents the highest return period values where there was better adherence. For Videira (Figure 1D) and Cacador (Figure 1F), good adherence is observed in all probability bands.

Eltz et al. (1992), who analysed data from Santa Maria (RS) and tested different distributions of probability, concluded that the Gumbel distribution was the only one to present satisfactory erosivity data. Table 2 shows the statistics of the annual rainfall erosivity and the adjusted Gumbel-Chow distribution parameters. The mean value is considered the rainfall erosivity factor (R factor) to be employed in the Universal Soil Loss Equation (Kinnel, 2010).

The mean EI30 in Campos Novos is 7405.1 MJ mm [ha.sup.-1] [h.sup.-1] [year.sup.-1]. However, it ranged from 4292.5 to 11711.6 MJ mm [ha.sup.-1] [h.sup.-1] [year.sup.-1]. The lowest EI30 in Videira and Cacador, were 2881.9 and 2484.1 MJ mm [ha.sup.-1] [h.sup.-1] [year.sup.-1], respectively. Even though the lowest extreme value was observed in Cacador, it showed the highest dispersion, with a coefficient of variation of 36.8%. Almeida et al. (2012), who analyzed data from four municipalities in the state of Mato Grosso, found a coefficient of variation for the annual EI30 ranging from 14.1 to 25.2%. Santos & Montenegro (2012) found a coefficient of variation of 50% in the data of annual erosion of the central rural area of Pernambuco State.

All data series showed slightly positive asymmetry ranging from 0.22 to 0.33. The Gumbel-Chow distribution was adequate for the three stations, as can be seen in Figure 2.

In Campos Novos, the maximum rainfall intensity in 30 min (Table 3) varied from 57.0 mm [h.sup.-1] for the return period of 2 years to 122.7 mm [h.sup.-1] for the return period of 100 years. The estimated value with a return period of 2 years corresponds to the value close to the average because, according to the Gumbel distribution, the average return period is 2.33 years. I30 are important to estimate the surface runoff and design the surface drainage structures such as terraces, canals, and culverts.

Eltz et al. (1992) state that the estimates of rainfall intensity with different return periods are important to design urban and agricultural engineering projects, such as the mechanics of drainage channels, terracing systems, and the spacing between terraces. They also affirm that overestimated structures can provide good security; however, they are expensive, and efficient sizing lowers costs and considers the risks. In addition, the value of I30 is used in hydrological models such as SWAT (Soil and Water Assessment Tool) (Brighenti, 2015).

The magnitude of annual maximum rainfall erosivity represents 15 to 20% of annual erosion rainfall for the return periods greater than 2 years. The effects of extreme rainfall on annual erosivity was highlighted by Edwards & Owens (1991) with data from 28 years of observation and more than 4,000 rainfall events, in which only five major rainfall events--with a return period of over 100 years--accounted for 66% of the occurred soil losses. In addition, Eltz et al. (2011) observed in the Encruzilhada do Sul (RS) municipality data that a single extreme rainfall event represented 74% of the erosivity that occurred in one year. The aforementioned observations reinforce the hypothesis that extreme events are the ones that generally cause major erosion problems.

Cassol et al. (2008) highlighted some limitations of the USLE, such as its inability to predict short-term soil losses, because of the use of average annual rainfall erosivity, which presents considerable variability, as the R factor. Oliveira et al. (2012) recommended the inclusion of rainfall return periods in future soil erosion studies. According to Ferro et al. (1991), places with the same mean annual R factor may actually have different R factor values for storms in different return periods that should be considered in applying managerial strategies. Sadeghi et al. (2017) comments that return period analysis was adopted as a tool to help engineers and hydrologists to deal with this uncertainty.

It is important for managers and planners to make rational decisions for soil erosion control and management based on acceptable information and event analysis. In addition, the R factor estimation for a given return period is necessary for holistic planning and proper management of watershed resources.

Conclusions

1. The Gumbel-Chow distribution was adequate to estimate the maximum intensity of a 30 min rainfall, the maximum annual erosivity, and the rainfall erosivity index.

2. The mean annual erosivity based on the pluviographic records of Campos Novos, Videira, and Cacador is 7405.1, 6940.8 and 5955.9 MJ mm [ha.sup.-1] [h.sup.-1] [year.sup.-1], respectively.

3. The R factor use as the annual mean erosivity corresponds to the return period of 2.25 years.

4. The data series of the annual maximum individual rainfall erosivity coefficients vary from 47 to 50%.

5. Maximum annual erosive rainfall with a return period of more than 2 years corresponds to 15 to 20% of the estimated annual erosivity with the same return period.

Acknowledgments

The authors thank the National Council of Scientific and Technological Development (CNPq) for the financial support of this research.

Literature Cited

Almeida, C. O. S.; Amorim, R. S. S.; Eltz, F. L. F.; Couto, E. G.; Jordani, S. A. Erosividade da chuva em municipios do Mato Grosso: Distribuicao sazonal e correlacoes com dados pluviometricos. Revista Brasileira de Engenharia Agricola e Ambiental, v.16, p.142-152, 2012. https://doi.org/10.1590/S1415-43662012000200003

Alves Sobrinho, T.; Pertussatti, C. A.; Rebucci, L. C. S.; Oliveira, P. T. S. de; Estimativa da erosividade local das chuvas, utilizando redes neurais artificiais. Revista Ambiente & Agua, v.6, p.246-254, 2011. https://doi.org/10.4136/ambi-agua.197

Back, A. J. Chuvas intensas e chuva para dimensionamento de estruturas de drenagem para o Estado de Santa Catarina. Florianopolis: EPAGRI, 2013. 193p.

Back, A. J.; Alberton, J. V.; Poleto, C. Avaliacao da erosividade das chuvas de Chapeco, Santa Catarina. In: Simposio sobre Sistemas Sustentaveis, 3, 2016, Porto Alegre. Anais ... Porto Alegre: ABRH, 2016. p.1-6.

Bazzano, M. G. P.; Eltz, F. L. F.; Cassol, E. A. Erosividade, coeficiente de chuva, padroes e periodo de retorno das chuvas de Quarai, RS. Revista Brasileira de Ciencia do Solo, v.31, p.1205-1217, 2007. https://doi.org/10.1590/S0100-06832007000500036

Bertoni, J.; Lombardi Neto, F. Conservacao do solo. Sao Paulo: icone, 2010. 355p.

Brighenti, T. M. Modelagem hidrologica e avaliacao de diferentes metodos de calibracao para o modelo SWAT. Florianopolis: UFSC, 2015. 116p. Dissertacao Mestrado

Cassol, E. A.; Eltz, F. L. F.; Martins, D.; Lemos, A. M. de; Lima, V. D. de; Bueno, A. C. Erosividade, padroes hidrologicos, periodo de retorno e probabilidade de ocorrencia das chuvas em Sao Borja, RS. Revista Brasileira de Ciencia do Solo, v.32, p.1239-1251, 2008. https://doi.org/10.1590/S0100-06832008000300032

Colodro, G.; Carvalho, M. P.; Roque, C. G.; Prado, R. M. Erosividade da chuva: Distribuicao e correlacao com a precipitacao pluviometrica de Teodoro Sampaio (SP). Revista Brasileira de Ciencia do Solo, v.26, p.809-818, 2002. https://doi.org/10.1590/ S0100-06832002000300027

Davudirad, A. A.; Sadeghi, S. H.; Sadoddin, A. The impact of development plans on hydrological changes in the Shazand Watershed, Iran. Land Degradation & Development, v.27, p.1236-1244, 2016. https://doi.org/10.1002/ldr.2523

Edwards, W. M.; Owens, L. B. Large storm effects on the total soil erosion. Journal of Soil and Water Conservation, v.46, p.75-78, 1991.

Eltz, F. L. F.; Cassol, E. A.; Pascotini, P. B. Potencial erosivo e caracteristicas da chuva de Encruzilhada do Sul, RS. Revista Brasileira de Engenharia Agricola e Ambiental, v.15, p.331-337, 2011. https://doi.org/10.1590/S1415-43662011000400001

Eltz, F. L. F.; Cassol, E. A.; Pascotini, P. B.; Amorim, R. S. S. Potencial erosivo e caracteristicas das chuvas de Sao Gabriel, RS, de 1963 a 1993. Revista Brasileira de Engenharia Agricola e Ambiental, v.17, p.647-654, 2013. https://doi.org/10.1590/S141543662013000600011

Eltz, F. L. F.; Reichert, J. M.; Cassol, E. A. Periodo de retorno de chuvas em Santa Maria, RS. Revista Brasileira de Ciencia do Solo, v.16, p.265-269, 1992.

Ferro, V.; Giordano, G.; Iovino, M. Isoerosivity and erosion risk map for Sicily. Hydrological Sciences Journal, v.36, p.549-564, 1991. https://doi.org/10.1080/02626669109492543

Hazbavi, Z.; Sadeghi S. H. R. Potential effects of vinasse as a soil amendment to control runoff and soil loss. Soil, v.2, p.71-78, 2016. https://doi.org/10.5194/soil-2-71-2016

Kinnell, P. I. A. Event soil loss, runoff and the universal soil loss equation family of models: A review. Journal of Hydrology, v.385, p.384-397, 2010. https://doi.org/10.1016/j.jhydrol.2010.01.024

Kite, G. W. Frequency and risk analyses in hydrology. Fort Collins: Water Resources Publications, 1977. 224p.

Mello, C. R. de; Viola, M. R.; Owens, P. R.; Mello, J. M. de; Beskow, S. Interpolation methods for improving the RUSLE R-factor mapping in Brazil. Journal of Soil and Water Conservation, v.70, p.182-197, 2015. https://doi.org/10.2489/jswc.70.3.182

Oliveira, P. T. S. de; Alves Sobrinho, T.; Rodrigues, D. B. B.; Panachuki, E. Erosion risk mapping applied to environmental zoning. Water Resources Management, v.25, p.1021-1036, 2011. https://doi. org/10.1007/s11269-010-9739-0

Oliveira, P. T. S. de; Rodrigues, D. B. B.; Alves Sobrinho, T.; Carvalho, D. F.; Panachuki, E. P. Spatial variability of the rainfall erosive potential in the state of Mato Grosso do Sul, Brazil. Engenharia Agricola, v.32, p.69-79, 2012. https://doi.org/10.1590/S010069162012000100008

Sadeghi, S. H.; Zabihi, M.; Vafakhah, M.; Hazbavi, Z. Spatiotemporal mapping of rainfall erosivity index for different return periods in Iran. Natural Hazards, v.87, p.35-56, 2017. https://doi. org/10.1007/s11069-017-2752-3

Santos, T. E. M. dos; Montenegro, A. A. de A. Erosividade e padroes hidrologicos de precipitacao no agreste central pernambucano. Revista Brasileira de Engenharia Agricola e Ambiental, v.16, p.871880, 2012. https://doi.org/10.1590/S1415-43662012000800009

Steel, R. G. D.; Torrie, J. H. P. Principles and procedures of statistics: A biometrical approach. New York: McGraw Hill, 1981. 633p.

Shamshad, A.; Azhari, M. N.; Isa, M. H.; Hussin, W. M. A. W.; Parida, B. P. Development of an appropriate procedure for estimation of RUSLE EI30 index and preparation of erosivity maps for Pulau Penang in Peninsular Malaysia. Catena, v.72, p.423-432, 2008. https://doi.org/10.1016/jxatena.2007.08.002

Silva, R. B. da; Iori, P.; Silva, F. A. de M. Proposicao e validacoes de equacoes para estimativa da erosividade de dois municipios do estado de Sao Paulo. Irriga, v. 14, p.533-547, 2009.

Syvitski, J. P. M.; Kettner, A. Sediment flux and the Anthropocene. Philosophical Transactions of the Royal Society, v.369, p.957-975, 2011. https://doi.org/10.1098/rsta.2010.0329

Valvassori, M. L; Back, A. J. Avaliacao do potencial erosivo das chuvas em Urussanga, SC, no periodo de 1980 a 2012. Revista Brasileira de Ciencia do Solo, v.38, p.1011-1019, 2014. https:// doi.org/10.1590/S0100-06832014000300033

DOI: http://dx.doi.org/10.1590/1807-1929/agriambi.v22n1p63-68

Alvaro J. Back (1), Augusto C. Pola (1), Nilzo I. Ladwig (2) & Hugo Schwalm (2)

(1) Empresa de Pesquisa Agropecuaria e Extensao Rural de Santa Catarina/Estacao Experimental de Urussanga. Urussanga, SC. E-mail: ajb@epagri.sc.gov.br (Corresponding author); pola@epagri.sc.gov.br

(2) Universidade do Extremo Sul Catarinense/Programa de Pos Graduacao em Ciencias Ambientais. Criciuma, SC. E-mail: ladwig@unesc.net; hsc@unesc.net

Ref. 175508--Received 7 Feb, 2017 * Accedpted 28 Aug, 2017 * Published 16 Nov, 2017

Caption: Figure 1. Adherence of the data series of annual maximum of I30 of Campos Novos (A), Videira (C), and Cacador (E), and EI30 erosivity index of Campos Novos (B), Videira (D), and Cacador (F) (Blue diamonds--empirical distribution; Red line--Gumbel distribution)

Caption: Figure 2. Adherence of the data series of EI30 of Campos Novos (A), Videira (B), and Cacador (C) to the Gumbel-Chow distribution (Blue diamonds--empirical distribution; Red line--Gumbel distribution)
Table 1. Statistics of the data series of annual maximum
I30 and EI30, parameters of the Gumbel-Chow distribution
and the adhesion test

Statistics                Campos Novos   Videira   Cacador

                          Maximum annual I30 (mm [h.sup.-1])

Highest value (mm)            92.2        90.2      77.2
Lowest value (mm)             36.0        33.0      22.4
Mean (mm)                     59.6        56.5      42.7
Standard deviation (mm)       17.1        14.9      11.5
CV (%)                        28.7        26.4      26.9
Asymmetry                     0.43        0.55      1.33
Number of data                 27          26        22
Parameter [alpha]            0.0644      0.0734    0.0938
Parameter [beta]              51.3        49.3      37.0
[D.max]                      0.0600      0.0580    0.1186
[D.sub.crit]                 0.254        0.259     0.281

                                   Maximum annual EI30
                             (MJ mm [ha,sup.-1] [h.sup.-1])

Highest value (mm)           2520.1      1837.8    1725.7
Lowest value (mm)            509.4        290.0     253.5
Mean (mm)                    998.0        948.1     837.9
Standard deviation (mm)      498.4        452.5     407.0
CV (%)                        49.9        47.7      48.6
Asymmetry                     1.47        0.53      0.88
Number of data                 27          26        22
Parameter [alpha]            0.0022      0.0024    0.0026
Parameter [beta]             756.5        728.0     636.1
[D.max]                      0.1423      0.0731    0.0944

Table 2. Statistics of the data series of total annual EI30,
Gumbel-Chow distribution parameters, and the adherence
test

Statistics                Total annual EI30 (MJ mm [ha.sup.-1]
                              [h.sup.-1] [year.sup.-1])

                          Campos Novos   Videira   Cacador

Highest value (mm)          11711.6      11826.4   10219.0
Lowest value (mm)            4292.5      2881.9    2484.1
Mean (mm)                    7405.1      6940.8    5955.9
Standard deviation (mm)      2126.6      1725.5    2194.6
CV (%)                        28.7        24.9      36.8
Asymmetry                     0.22        0.33      0.33
Number of data                 30          29        27
Parameter [alpha]           0.000518     0.000638  0.000501
Parameter [beta]             6374.8      6104.9    4892.6
[D.sub.max]                  0.0900      0.1079    0.0718
[D.sub.crit]                 0.242        0.246     0.254

Table 3. Estimated values of the maximum rain intensity in 30 min
(I30), EI30 rainfall, and annual erosivity value for the Campos
Novos, Videira, and Cacador stations

Return period               I30 (mm [h./sup.-1])
(years)
                Campos Novos   Videira   Cacador

2                   57.0        54.3      40.9
5                   74.6        69.6      52.7
10                  86.2        79.8      60.6
20                  97.4        89.6      68.1
25                 100.9        92.7      70.4
50                 111.8        102.2     77.8
100                122.7        111.7     85.0

Return period   EI30 (MJ mm [ha.sup.-1] [h.sup.-1])
(years)
                Campos Novos   Videira   Cacador

2                  922.5        879.6     776.2
5                  1435.8      1345.6    1195.4
10                 1775.6      1654.1    1472.9
20                 2101.6      1950.0    1739.1
25                 2205.0      2043.9    1823.6
50                 2523.5      2333.1    2083.7
100                2839.7      2620.2    2341.9

Return period   EI30 (MJ mm [ha.sup.-1] [h.asup.-1] [ano.sup.-1])
(years)
                Campos Novos   Videira   Cacador

2                  7083.1      6679.5    5623.5
5                  9273.2      8456.6    7883.6
10                10723.3      9633.2    9380.0
20                12114.3      10761.8   10815.4
25                12555.5      11119.8   11270.8
50                13914.7      12222.6   12673.4
100               15263.9      13317.3   14065.7
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Author:Back, Alvaro J.; Pola, Augusto C.; Ladwig, Nilzo I.; Schwalm, Hugo
Publication:Revista Brasileira de Engenharia Agricola e Ambiental
Date:Jan 1, 2018
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