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BY 4.0 license Open Access Published by De Gruyter Open Access October 26, 2019

Rainfall erosivity and extreme precipitation in the Pannonian basin

  • Tin Lukić , Aco Lukić , Biljana Basarin , Tanja Micić Ponjiger EMAIL logo , Dragana Blagojević , Minučer Mesaroš , Miško Milanović , Milivoj Gavrilov , Dragoslav Pavić , Matija Zorn , Blaž Komac , Ðurđa Miljković , Dušan Sakulski , Snežana Babić-Kekez , Cezar Morar and Sava Janićević
From the journal Open Geosciences

Abstract

In order to assess the rainfall erosivity in the Pannonian basin, several parameters which describe distribution, concentration and variability of precipitation were used, as well as 9 extreme precipitation indices. The precipitation data is obtained from the European Climate Assessment and Dataset project for the period 1961-2014, for 8 meteorological stations in northern Serbia, 5 in Hungary and 1 in eastern Croatia. The extreme values of precipitation were calculated following the indices developed by the ETCCDI. RclimDex software package was used for indices calculation. Based on statistical analysis and the calculated values, the results have been presented with Geographic Information System (GIS) to point out the most vulnerable parts of the Pannonian basin, with regard to pluvial erosion. This study presents the first result of combined rainfall erosivity and extreme precipitation indices for the investigated area. Results of PCI indicate presence of moderate precipitation concentration (mean value 11.6). Trend analysis of FI (mean value 22.7) and MFI (mean value 70.2) implies a shift from being largely in the low erosivity class, to being completely in the moderate erosivity class in the future, thus indicating an increase in rainfall erosivity for most of the investigated area (except in the northwestern parts). Furthermore, the observed precipitation extremes suggest that both the amount and the intensity of precipitation are increasing. The knowledge about the areas affected by strong soil erosion could lead to introducing effective measures in order to reduce it. Long term analysis of rainfall erosivity is a significant step concerning flood prevention, hazard mitigation, ecosystem services, land use change and agricultural production.

1 Introduction

The precipitation is seen as a variable element in time and space and it directly affects natural water cycles, but also provides information on the state of the climate [1]. During the last decades, numerous studies focused on precipitation variability all over the world. The results indicated a significant decrease in the number of rainy days and a significant increase in the precipitation intensity in many places in the world, such as China [2, 3, 4] and America [5]. There are numerous studies that investigate the trends in annual and seasonal precipitation, for larger areas [6, 7, 8], but also for the entire nations or regions [9, 10, 11, 12, 13]. Luković etal. [14] could not find the significant trends in total annual precipitation for the whole territory of Serbia during the period 1961-2009. However, they found minor tendencies toward drier conditions on a seasonal scale. The winter season, as well as spring are receiving less rain, while autumn experienced wetter conditions. For the territory of Vojvodina, Tošić et al. [15] analyzed the precipitation data for more than 90 stations during the period 1949-2006. They found that the time series of leading Principal Component of the Vojvodinian precipitation has a decreasing trend during the winter and spring seasons while the increase was detected for autumn, summer, and annual precipitation. Bartholy and Pongrácz [16] observed the decreased precipitation totals in Hungary and argued that the climate became slightly drier during 20th century. The changes in annual precipitation levels for Croatia were analyzed based on the data for 22 meteorological stations during the period 1950 to 2010. Pannonian part of eastern Croatia experienced a slight increase in precipitation while the other regions recorded stagnation of slight decrease [17]. The general decline of precipitation totals in Croatia are probably due to the spring and autumn reduction in the northern part as well as winter and spring decrease along the coast and in the mountains [18].

Extreme precipitation events, such as droughts [19] and floods [20], are seen as highly variable and could cause economic, as well as ecological damage, but in the worst cases induce increased mortality. Studies around the globe showed that during the last few decades, extreme precipitation events are becoming more frequent (e.g. [21, 22, 23, 24]). The changes in precipitation are very important due to their significance for economic agriculture, energy production and drinking water supply. Also, the changes in precipitation have a major role in natural hazards such as droughts, floods, landslides and severe soil erosion [25]. The changes in precipitation, along with their extreme values, occur over a wide range of temporal and spatial scales. Many studies conducted globally [26, 27, 28, 29]), regionally [30, 31, 32] as well as on local scales [11, 33, 34, 35, 36], have emphasized growing precipitation variability with rises in northern and central Asia, in the eastern parts of North and South America and in northern Europe [37, 38, 39, 40].Onthe other hand, some areas such as the Mediterranean display either a decrease in which is not always significant, or the absence of a linear trend (e.g. [31, 36, 41, 42, 43, 44, 45, 46]).

Magnitude and sign of the trend for extreme precipitation events are different for certain parts of Europe (e.g. [47, 48, 49, 50, 51]). In the Hungarian part of Pannonian basin during the last 20 years of the 20th century decreases were predominant in both warm and cool seasons [52]. The recent changes in Serbian climate extreme indices were evaluated by Malinović-Milićević et al. [53]. They showed that there is a pronounced increase in daily precipitation totals as well as in precipitation intensity, especially in the north and the west of Serbia. Anđelković et al. [54] calculated the critical number of meteorological stations above which an event is considered as an extreme precipitation event, or a climate extreme of national significance. The respective authors found that this number is 6.21 stations (theoretically covering more 22.17% of the total territory), meaning that if during one day more than seven stations experience event that is above normal, they could be considered as very harmful and have great consequences for the environment.

Willems [55] found the presence of increasing trends in numerous features of extreme precipitation in Central and Western Europe. Additionally, the study argued that the precipitation extremes in Europe display oscillatory pattern on multidecadal time scales and could be linked to Atlantic Multidecadal Oscillation [56].

The changes in precipitation, the presence of extreme values affect the soil erosion, and unlike some other natural factors, such as relief or soil characteristics, is not responsive to human modification. The soil erosion by water is very complex phenomenon and it is one of the major threats to soil degradation [57, 58, 59, 60]. Land loss as a result of erosion can lead to a decrease in organic matter and nutrient content, a change in soil structure, and a decrease in water capacity. Loss in productivity can be significant for the lives of people in the given area; the re-fertile layer of soil, which is the most fertile layer, is also most exposed to pluvial erosive processes [60, 61, 62]. In the work of Markantonis et al. [63], Rawat et al. [64], Berger and Rey [65], Gares et al. [66] and Mather [67] it was pointed out that soil erosion is intrinsically entangled with many other natural hazards. Respective authors such as Van Beek [68] and Bosco and Sander [69] pointed out that soil erosion is also part of a system of multiple interacting processes operating in a complex hierarchy. Therefore, mass movements play an important role within soil erosion processes due to their capacity to remove and expose large parts of slopes in a relatively short period. Pradhan et al. [70] stated that high soil erosion rates can also lead to an increase of landslide susceptibility due to the reduced capacity of soil to support a good vegetation cover. Landslides may also directly occur on gullies created by surface erosion processes [71].

Soil erosion is generally manifested through three main phases: the tearing of the surface material by the action of a certain agent, the transport of the material and its accumulation. Soil erosion by water is one of the most important causes of degradation of land and a critical environmental hazard in modern times. Soil erosion destroys land resources and increase the risk posed by the blockage of rivers as well as causes degradation of the water quality because of the pesticides, the fertilizers and the nutrients carried by the sediment [72]. Precipitation (pluvial) erosion denotes the potential ability of the atmospheric precipitate to cause soil erosion and represents the climatological component in the overall water erosion process [73].

Numerous indices of rainfall aggressivity (erosivity) have been developed in order to estimate soil erosion. Among those the most appropriate ones are those that relate soil erosion to kinetic energy of rainfall (storm erosivity), such as EI30 [74]. However, for the calculation of this index relatively continuous rainfall data series, with a time resolution of at least 15 min (pluviograph data) are needed [75, 76]. High quality datasets on such temporal and regional scale are very rare. In order to avoid this problem, other indices based on monthly data have been proposed, such as Fournier Index (FI) and its modification (Modified Fournier Index-MFI) by Arnoldus [77]. The FI and MFI have been used as the input aggressivity factor in the development of regional models [78], since they correspond very good with USLE rainfall erosivity factor (R-factor) [75, 76, 79, 80, 81].

Also, one of the most important aspects of the climate is the concentration of the rainfall amounts throughout the year. Since the precipitation during the year is highly variable, irregular and unpredictable, rainfall distribution varies from year to year. This has to be taken when one considers soil erosion, soil conservation and land evaluation [82, 83]. Precipitation Concentration Index (PCI) allows the calculation of the relative distribution of rainfall patterns, and also evaluates the seasonality of the precipitation. Generally, the MFI may be expressed as the product of Total Annual Precipitation (P) and monthly precipitation concentration (PCI) [84]. Based on this, the rainfall erosivity (MFI) is more intense where there are high values of precipitation concentration (high PCI) and Total Annual Precipitation (P).

In this paper climatological parameters from the area of northern Serbia (Vojvodina), Hungary and eastern Croatia will be processed. In order to assess the hazardous vulnerability for this part of the Pannonian basin, three parameters will be used: precipitation amount, rainfall erosivity and extreme precipitation indices.

2 Materials and methods

2.1 Study area

The Pannonian basin is located in the central part of Europe. It occupies the territory between 4350 and 4915 latitude N and 1506 and 2330 longitude E (Figure 1). The region extends over nine countries: Austria, Slovenia, Hungary, Croatia, Bosnia and Herzegovina, Serbia, Montenegro, Romania, Slovakia and Ukraine and largely overlaps with the Pannonian plain. The Great Hungarian Plain, the Danube plain, the Sava plain and the Drava plain constitute the physical characteristics of the Pannonian basin. The Alps range in the west, the Carpathians in the north and east and the Dinaric in the south bound the surroundings of this region [85].

Figure 1 Meteorological stations in the Pannonian basin used in this study.
Figure 1

Meteorological stations in the Pannonian basin used in this study.

The Pannonian basin represents an area of high diversity of the physical, biophysical and socio-economic conditions. During the past few decades, an increase in number of hydrometeorological extreme events, such as heat waves, droughts and extreme precipitation, have been observed and had powerful effect on various regions in the Pannonian basin [60, 62, 86, 87, 88, 89, 90, 91, 92, 93, 94, 95]. Results of the climate change models suggest great impacts on multiple sectors and the ecosystem in the Pannonian basin implying that this part of Europe will be among the hotspot regions with the highest number of severely affected sectors in Europe [95, 96, 97].

Since, the Pannonian basin is located in the midlatitudes of the Northern Hemisphere, the lowest temperatures occur in January and the highest in July and August, the rainfall season ranges from mid-April to September, and the cloud cover is highest from November to January [85, 98, 99, 100]. When observing the trends of 10 different meteorological variables Spinioni et al. [99] found that temperature was increasing in every season, particularly during the last three decades. This finding was in the good agreement with the trends occurring in Europe. Wind speed was found to decrease in every season throughout the year, while cloud cover and relative humidity decreased in spring, summer, and winter, and increased in autumn. On the other hand relative sunshine duration had trends in the opposite way. For the precipitation and surface air pressure no significant trends were found, even though they increased slightly on an annual basis [99].

2.2 Data and methods

For the purpose of this analysis the daily data on precipitation from the database of the European Climate Assessment and Dataset (ECA&D) for the period 1961-2014 was used. The daily data was then aggregated on monthly and yearly basis. The data were obtained for the calculation of individual indices: PCI, FI, MFI and the extreme rainfall indices.

The list of the meteorological stations used in this study is given in Table 1. For the analysis and calculation of the indices the blended ECA data sets were used. The daily ECA datawere tested and homogenized by Wijngaard et al. [101]. Only validated participant data indicated by 0 in the column labeled Q (RR) given in each data file in the blended datasets were used.

Table 1

Meteorological stations analyzed in this study.

No.Station nameCountryLatitudeLongitudeAltitude (m)
1.SomborSerbia4546’12”1909’00”87
2.PalićSerbia4606’00”1946’12”102
3.Rimski ŠančeviSerbia4519’48”1951’00”86
4.KikindaSerbia4551’00”2028’12”81
5.ZrenjaninSerbia4522’00”2025’00”80
6.Banatski KarlovacSerbia4503’00”2102’12”100
7.VršacSerbia4509’00”2119’12”83
8.Sremska MitrovicaSerbia4501’00”1933’00”82
9.PécsHungary4600’21”1813’58”203
10.SzegedHungary4615’22”2005’25”82
11.DebrecenHungary4729’25”2136’39”108
12.BudapestHungary4730’40”1901’14”153
13.SzombathelyHungary4711’54”1638’52”201
14.OsijekCroatia4532’00”1838’00”88

PCI [102] was used in order to assess regional rainfall erosivity. PCI was proposed as an indicator of rainfall concentration and rainfall erosivity [83]. This index was calculated on an annual basis according to Eq. (1):

(1)PCIannual=i=112pi2i=112pi2×100

where the mean monthly amounts of precipitation are marked with pi. In order to further examine the impact of erosion and determine the regional distribution of precipitation during the year, PCI is calculated at seasonal level for climatological winter (December – January – February), spring (March – April – May), summer (June – July – August) and autumn (September – October – November) according to Eq. (2):

(2)PCIseasonal=i=13pi2i=13pi2×25

It was also calculated for wet (from April to September) and dry (from October to March) periods following the Eq. (3) [103]:

(3)PCIsupraseasonal=i=16pi2i=16pi2×50

According to the presented equations, the lowest theoretical value on the annual, seasonal and supra-seasonal scale of PCI is 8.3, indicating the perfect uniformity in precipitation distribution (i.e., that same amount of precipitation occurs in each month). Also, on all scales, a PCI value of 16.7 will indicate that the total precipitation was concentrated in half of the period and a PCI value of 25 will indicate that the total precipitation occurred in one third of the period (i.e. total annual precipitation occurred in 4 months; total supra-seasonal precipitation occurred in 2 months and total seasonal precipitation occurred in 1 month). According to this classification, Oliver [102] suggested that PCI values of less than 10 represent a uniform precipitation distribution (i.e. low precipitation concentration); values from 11 to 15 denote a moderate precipitation concentration; values from 16 to 20 denote irregular distribution and values above 20 represent a strong irregularity (i.e. high precipitation concentration) of precipitation distribution (Table 2) [103, 104, 105].

Table 2

PCI value classes based on [102, 103].

Spatial distributionPCI values
Uniform distribution≤ 10
Moderate distribution>10 ≤ 15
Irregular distribution>15 ≤ 20
Strongly irregular distribution>20

FI and MFI are perceived as useful in studies that are focused on assessment of rainfall aggressiveness and are subjected to the correlation to other climatic variables that are contributing factors in the triggering/ or reactivation of erosion phenomena (e.g. [58, 103, 105, 106]). FI is calculated as follows:

(4)FI=p2maxP

where pmax is the maximum precipitation amount of the wettest month of the year and P is the mean annual rainfall amount.

This index has some disadvantages as an indicator of soil erosion within the USLE model, as low values of monthly rainfall amounts can have substantial erosive power, an increase in total rainfall amount should result in an increase of erosivity. It is also illogic that if the maximum monthly rainfall pmax remains the same while the mean annual rainfall increases the FI decreases. For these reasons, Arnoldus [77] modified FI into MFI, taking into account the atmospheric precipitation of all months during the year. The relationship between these two indices is described in numerous studies and is often used to achieve more complete display of the evolution of precipitation erosion in a given area (e.g. [60, 80, 107, 108, 109]). MFI is presented as a product of squared monthly precipitation ammount (p) and total annual rainfall (P) [84] and can be calculated according to Eq. (5):

(5)MFI=i=112p2P

The erosive classes of the two indices (FI, MFI) are presented in Table 3.

Table 3

Erosive classes of FI and MFI indices based on [102, 110, 111]

Erosive classFIErosive classMFI
Very low0 – 20Very low0 - 60
Low20 – 40Low60 - 90
Moderate40 – 60Moderate90 - 120
Severe60 – 80High120 - 160
Very severe80 – 100Very high> 160
Extremely> 100
severe

The extreme values of precipitation were calculated following the indices developed by the Expert Team on Climate Change Detection and Indices (ETCCDI) (http://cccma.seos.uvic.ca/ETCCDI) (Table 4). The RclimDex software package was used for this occasion. Nine precipitation indices were used for further analysis, and they are presented in Table 4.

Table 4

Definitions of 9 precipitation indices used in this study.

Index IDIndicator nameDefinitionUnitsIndex IDIndicator nameDefinitionUnits
RX1dayMax 1-day precipitation amountMonthly maximum 1-day precipitationmmCWDConsecutive wet daysMaximum number of consecutive daysdays
Rx5dayMax 5-day precipitation amountMonthly maximum consecutive 5-day precipitationmmR95pVery wet dayswith RR>=1 mm Annual total PRCP when RR>95th percentiledays
SDIISimple daily intensity indexAnnual total precipitation divided by the number of wet days (defined as PRCP>=1.0 mm) in the yearmm/ dayR99pExtremely wet daysAnnual total PRCP when RR>99th percentilemm
R10mmNumber of heavy precipitation daysAnnual count of days when PRCP>=10 mmdaysPRCPTOTAnnual total wet-day precipitationAnnual total PRCP in wet days (RR>=1 mm)mm
CDDConsecutive dry daysMaximum number of consecutive days with RR<1 mmdays

For the spatial presentation of selected hazard indices in this paper, the Geographic Information Systems (GIS), ArcMap 10.6 software was applied. The most suitable interpolation method for the precipitation data visualization was the Ordinary Cokriging (COK) [112], which was employed through the ArcMap (extension Geostatistical Analyst).

The obtained time series of precipitation and pluvial indices were tested for trends using the nonparametric Mann-Kendall test (MK). According to Gilbert [113] the MK test relates the relative magnitudes of data rather than the data values themselves. In the MK test two hypotheses are examined: the null hypothesis (H0) that states there is no trend in the time series and the alternative hypothesis (Ha) which states there is a significant trend in the series, for a certain significance level. Statistical significance (as seen as the probability p) takes values between 0 and 100 in percentage. In fact, p is used to test the level of confidence in H0. If the computed p value is lower than the chosen significance level, α (e.g. α = 1%, α = 5%, α = 10%), the H0 should be rejected, and Ha should be accepted. On the other hand, if computed p value is greater than the significance level α, the H0 cannot be rejected [113]. In order to prevent the effects of the serial correlation in time series, the Yue-Pilon method was used [114]. For this purpose, R package ZYP (http://www.r-project.org) was utilized.

3 Results and discussion

One of the main triggering factors of erosion in the Pannonian basin is precipitation amount (e.g. [115]). In order to gain more complete insight into erosivity in this part of Europe the trends in annual amount of precipitation are discussed.

The Table 5 shows the calculated trends in annual precipitation amounts at the investigated stations. It could be seen that the larger parts of the area display an increase in total annual rainfall with the exception of three stations, Debrecen, Budapest and Szombathely, where the decrease was observed. Only Budapest meteorological station exhibits a statistically significant declining trend at the given confidence level (p<0.05).

Table 5

Trends in annual precipitation amount at the investigated stations.

No.StationCountryTrendp-value
1.name SomborSerbia(mm/y) 0.750.5
2.PalićSerbia1.380.35
3.RimskiSerbia1.870.16
Šančevi
4.KikindaSerbia0.570.62
5.ZrenjaninSerbia0.90.82
6.BanatskiSerbia0.660.8
Karlovac
7.VršacSerbia0.580.18
8.SremskaSerbia0.410.9
Mitrovica
9.PécsHungary1.1590.6
10.SzegedHungary0.980.5
11.DebrecenHungary−0.0650.6
12.BudapestHungary−2.0560.03
13.SzombathelyHungary−0.50.74
14.OsijekCroatia0.6370.77

Figure 2a shows the spatial distribution pattern of the precipitation values for the investigated period. In the Pannonian basin the rainy season lasts from May to July and there are more rainfall over the mountains (up to 1,650 mm in the Ukrainian Carpathians and in the Tatra Mountains) than in the plain terrain. According to Spinioni et al. [99] the lowest annual precipitation totals are observed for eastern Hungary (550 mm), the lowest summer totals in Northern Serbia (80 mm),while the lowest winter totals in northern Romania (70 mm). Statistically significant trends in Pannonian basin for precipitation totals during the period 1961 – 2010 were not found, but the small increase was detected during the last few decades compared to the 1980’s, which was characterized as the driest decade [99]. Further-more, regional intensity and frequency of extreme precipitation in the Pannonian basin has increased between 1976 and 2001,while the total precipitation has decreased in the region. Bartholy and Pongrácz [52] emphasized that the increase of extreme rainfall events, coupled with a lower frequency, lead to constant precipitation totals during the investigated period.

Figure 2 Spatial patterns of pluvial parameters used in this study for the observed period.
Figure 2

Spatial patterns of pluvial parameters used in this study for the observed period.

For the future, the results of the climate models indicate that drier summers are very likely to occur, mainly in the southern parts of the Pannonian basin [116]. More frequent and more intense extreme precipitation events are projected for winter and autumn seasons, especially in the northern regions. Spatial distribution of precipitation is not going to change significantly in the future, but the annual distribution of precipitation will most likely be restructured [100].

3.1 Precipitation Concentration Index (PCI)

The results of PCI tendencies for all meteorological stations are shown in Figure 4, while the spatial distribution pattern of the index values can be seen on Figure 2b. In northern Serbia PCI values belong to the group of moderate precipitation distribution (values from 11 to 15). The highest index values were obtained for Banatski Karlovac (18.22 units) in 2014,when the highest rainfall amount was recorded in this area (976.98 mm). The north of the Vojvodina province shows more uniform distribution. At the investigated stations the presence of a statistically significant trend in the variability of PCI was not observed. Only Sombor, Zrenjanin and Vršac meteorological stations display a declining trend in PCI values, while other record a slight increase, but the trends were not statistically significant at given significance levels.

Figure 4 Tendencies of the pluvial erosion parameters and indices for the observed period in the investigated area.
Figure 4

Tendencies of the pluvial erosion parameters and indices for the observed period in the investigated area.

PCI during the half-year periods (wet and dry) indicate that values for the wet part of the year (from April to September) correspond to moderate precipitation distribution (Figure 4). Highest values are recorded for certain years, so the level of PCI of 43.88 units was recorded for the Kikinda station in 2014, which indicates a high precipitation concentration. For the station Rimski Šančevi irregular precipitation concentration (16.01) was observed in 2003, but also in 1992. Irregular distribution of precipitation (16.39) was recorded at Palić at the same year. The meteorological station Zrenjanin records the largest number of unusually high values of PCI: 16.56 (1961), 19.08 (1972) and 17.65 (1992) indicating irregular precipitation concentration without the presence of statistical significance. The values for the dry semi-annual period (from October to March) belong to the group of uniform precipitation distribution, with increasing trend in 75% of the observed stations. The statistically significant increasing trend at the confidence level of 90% and higher was observed for Banatski Karlovac, Kikinda, Rimski Šančevi and Vršac stations (Figure 4).

The seasonal values of PCI for the Vojvodina area show generally uniform values. The winter season exhibits higher values than other seasons for all analyzed stations during the investigated period. Statistically significant increasing trend was not detected. The spring season (March-May) exhibits values that range from 3.4 for Sremska Mitrovica station to 3.55 for Palić station. Trend analysis indicates that the stations have an increasing trend, but statistically significant trends were not found (Figure 3).

Figure 3 Seasonal PCI trends for the observed period in the investigated area.
Figure 3

Seasonal PCI trends for the observed period in the investigated area.

The PCI values during the summer season (June-August) are ranging from 3.3 for the Vršac station to 3.6 for Palić station. Based on the trend analysis it can be noted that all stations show an increase in PCI values. Only Vršac station recorded a statistically significant increasing trend (p<0.1) for summer season (Figure 3).

During the autumn season (September-November) the values range from 3.5 for Sombor station to 3.8 for Zrenjanin station. All the observed stations show decreasing trend, but only Kikinda has a statistical significance at 90% confidence interval (Figure 3).

Since all the observed seasonal PCI values weight below 10, it can be pointed out that there is a uniform precipitation distribution within the investigated area. The winter season indicates much higher PCI values than the other seasons, but variation within the seasons is low.

PCI for the stations in Hungary ranges from 11 to 15, similarly to Vojvodina region (northern Serbia). According to the index classification this area can be seen as having a moderate precipitation concentration. The highest index value was recorded at Debrecen station in 2011 (19.19), indicating the irregular concentration precipitation. Generally, meteorological stations in Hungary do not show the presence of a statistically significant trend, although the trend has a positive tendency that indicates an increase in the index value at annual level.

This suggests that in the future, moderate precipitation concentration could shift into the second class: an irregular precipitation concentration in this part of the Pannonian basin.

PCI during the half-year periods (wet and dry) indicate that values for the wet part of the year (from April to September) correspond to moderate precipitation distribution (Figure 4). The highest value for the entire investigated period was detected at Debrecen station (18.8) in 1974, which indicates an irregular precipitation concentration. For the Budapest station irregular precipitation concentration (16.9) was observed in 1965. Irregular distribution of precipitation (18.7) was recorded at Szeged and Szombathely (17.8) respectively. Statistically significant increasing or decreasing trends were not recorded for the stations in Hungary (Figure 4).

The values for the dry semi-annual period (from October to March) belong to the group of moderate precipitation distribution, with increasing trend in 60% of the observed stations. The statistically significant increasing trend at the confidence level of 99% was observed for Budapest meteorological station (Figure 4).

Seasonal variations of PCI for Hungary have similar tendency as the ones in northern Serbia, but with pronounced presence of statistically significant trends. For the winter season the increasing trend is present at all investigated stations but Budapest, Debrecen and Szombathely have statistically significant trend (Figure 3). Similar situation is observed for spring season with the same tendencies for the observed stations (Figure 3). Summer season is also characterized by an increase of PCI values, but here only station Pécs and Szeged display statistically positive trend at 90% significance level. Due to the decline in precipitation during autumn, declining trends were detected at all investigated stations, but without statistical significance (Figure 3).

The Pannonian part of eastern Croatia also does not show the presence of a statistically significant trend and lies within the moderate precipitation concentrations recorded for the Osijek station (values from 11 to 15). The highest recorded value in Osijek is 16.08 for 1972 and falls within the irregular precipitation concentration class (Figure 4).

PCI during the wet half-year period indicate that values for this part of the year (from April to September) correspond to moderate precipitation distribution (Figure 4). The highest value at Osijek station was detected in 1992 and it was 16.6, which belongs to irregular precipitation concentration. The presence of statistically significant declining trend was not detected. The values for the dry semi-annual period (from October to March) belong to the group of moderate precipitation distribution, with increasing trend for Osijek station. The statistically significant increasing trend was not observed (Figure 4).

Seasonal variations of PCI at Osijek correspond to the situation observed for Vojvodina region with increasing tendencies for winter and summer and declining values for spring and autumn (Figure 3).

The PCI index was used to assess the changes in precipitation concentrations in different parts of the world. Spatial and temporal variations of this parameter were investigated in China [117, 118, 119, 120, 121, 122, 123], Italy [124, 125], Portugal [126], Spain [127, 128], Iran [129] and Turkey [130]. The opposite relationship between seasonal PCI and annual precipitation was found for Spain [103]. The respective authors showed that the PCI is superior for quantifying the heterogeneity of the monthly and daily precipitation in Spain. The similar pattern is observed for the Pannonian region. PCI distribution is not uniform over the whole territory, the seasonality is more pronounced especially during winter season.

When exploring the correlation between the precipitation and the North Atlantic Oscillation index (NAO) in Vojvodina, Tošić et al. [15] found that it is negative and significant. This implies that the positive phase of the NAO results in decreased intraseasonal fluctuations and deficient precipitation over Vojvodina. The significant correlation (at the 1% level of significance) is observed between the East Atlantic/ West Russian index (EA/WR) and precipitation totals for winter and autumn precipitation.

Tošić [131] investigated spatial and temporal variability of winter and summer precipitation over Serbia and Montenegro. Respective author pointed out that the large-scale atmospheric circulation could be responsible for the winter and summer precipitation variability. The time series associated with the first precipitation pattern (PC1) emphasized a decreasing trend in winter precipitation (that was also reported for southern Europe by other researchers). Strong correlation between the winter PC1 and the NAO index indicated that the NAO could be responsible for the winter precipitation variability over the investigated area. The second winter and summer EOF patterns displayed an opposite sign of climate variability between areas with Mediterranean and continental climates, highlighting the influence of orography and the Adriatic Sea on the precipitation regime. Also, all of the performed analyses were coherent in demonstrating that winter precipitation in Vojvodina region is influenced by the NAO. An intensification of the positive phase of the NAO could be one of the causes of the observed decrease in winter precipitation in northern Serbia [15]. The differences in magnitude and sign of the trends detected in this study and the previously published studies could be due to the different time spans of the precipitation series as well as used methods.

Similary, the studies (e.g. [132]) showed that decreased precipitation totals in Hungary could be linked to the intensification of the NAO and the northeastward shift of the mean positions of the main pressure centers over the Atlantic. Similar results were obtained for Pannonian part of Croatia indicating that NAO in general, have a strong influence on winter precipitation in this region, with negative NAO phases corresponding to periods of high precipitation [133].

3.2 Fournier (F) and Modified Fournier Index (MFI)

Figure 2c shows the spatial distribution pattern of the FI values for the investigated period in the Pannonian basin. Based on the detailed results of the FI, it can be noticed that the area of northern Serbia generally belongs to the erosive class of low values (20-40). The weather station Vršac (102.88) and its surroundings recorded the highest value for 2014 (indicating the presence of extremely high erosivity), while the station Palić recorded the lowest value on the territory of Vojvodina during 1983 (8.60 – very low erosivity). Only Banatski Karlovac station (63.50 in 1999 and 62.78 in 2014) and Vršac (63.24 in 1987) recorded amoderate high erosion class for the mentioned years. The trend values for 5 out of 8 stations indicate a slight rise in the index value on an annual basis, while the presence of a negative trend was observed for the stations Sombor, Vršac and Zrenjanin. The stations Banatski Karlovac, Palić, Zrenjanin, Sombor and Vršac do not show the presence of a statistically significant trend of variability of FI, while the stations Kikinda, Sremska Mitrovica and Rimski Šančevi show statistical significance at the confidence levels of 95%and 90%. The examined area of Hungary also belongs to the erosive class of low values (20-40). The Szeged’s meteorological station (63.19 in 1992) shows the highest value, while the station Pécs (6.93) has the lowest value recorded for 1983. Rising trend is noticed for all stations except Budapest meteorological station where a negative trend is observed but without statistical significance. The Osijek weather station in Croatia also belongs to the same erosive class with the highest index value of 81.79 in 1972, while the lowest was recorded in 1971 (10.75). The station generally has a positive trend but without statistical significance (Figure 4). The investigated trends generally point to a progressive increase in the values of the erosion index at the annual level, which in the future can lead to the transition to higher erosive classes and increase the sensitivity in the Pannonian basin. These results are generally accompanied by observations that Lukić et al. [60, 62] pointed out in their selected case studies and meteorological stations in the north and south of Vojvodina.

The results of MFI correspond to the results of the FI, and according to this index, the investigated area belongs to the erosive class of low values (Figure 2d). The weather station Vršac (149.16 in 2014) and its surroundings show the highest index value, while the Rimski Šančevi record the lowest value for 2000 (86.93). However, as this index is a modification of FI, it is more sensitive to the average monthly PCI values, and the results are significantly more reliable and indicate a higher diversity of erosive classes during the examined period. The results of the MK trend test indicate that the statistically significant possitive trend is observed only for the Rimski Šančevi station (an increase of 0.3 units per year). On the annual basis the MFI values are increasing at all stations in Vojvodina (Figure 4).

For the investigated stations in Hungary it was noted that the maximum value occurs in the area of Debrecen (126.22 in 1970), and the minimum is recorded at Szeged station (34.51) during 1971. The declining trend (−0.183) at the level of significance of 0.03 (p<0.05), was detected at Budapest station. The decreasing trend was also observed at Szombathely station (−0.024) but without the presence of statistical significance. Osijek station records the highest value of 142.26 (1972) and the lowest of 35.81 (2000). The MFI values are decreasing, but the trend test showed no statistical significance (Figure 4). As with FI, the investigated MFI trends generally indicate a progressive increase in the values at the annual level (except for the northwestern parts of the Pannonian basin), which in the future could lead to a transition to higher erosion classes and an increase in hazardous sensitivity in the investigated area.

Mezo˝si and Bata [115] found a significant correlation between the Rainfall erosivity factor (R) and the MFI by using the precipitation data of the past nearly 30 years for Hungary. They managed to compute a 50-80% increase in rainfall intensity for this century, by using calculated trends and the data provided by the model results. Good correlation between rainfall intensity (R) and the calculated MFI values for Hungary indicated that the increase in R also corresponds with the increase in MFI values. On the other hand, the estimated increase in intensity significantly lags behind the maximum values of certain regions in Italy, Croatia, or Slovenia (as well as western Scotland and southern Spain) [134]. The extent of soil erosion was calculated using the climate data provided by the models. The results predict greater R values and greater erosivity values on multy-decadal scales even though summer precipitation is decreasing. Apart from the R, the extent of soil erosion is also regulated by terrain, soil, and land cover related data [115].

Panagos et al. [134] observed similar condition for the Pannonian zone. Results of this study are in good accordance with the results of respective authors.

3.3 Extreme Precipitation Indices

The spatial distribution of the extreme precipitation indices (Figure 5) is analyzed on annual basis for the study period (1961-2014). The results of MK test indicate that values of RXIday index are increasing at all investigated stations except for Debrecen and Szombathely. The statistically significant trend was observed at only four stations in Vojvodina region (Figure 5). Monthly maximum consecutive 5-day precipitation index tends to decrease in some areas in the east, south and west of Hungary. Similarly the statistical significance of the rising trend was observed for only four stations in Vojvodina. Daily precipitation intensity index (SDII) for the investigated part of Pannonian basin is increasing except for Szombathely and Budapest stations. Statistical significant increase was observed in the southern part of the area (Vojvodina and south of Hungary) (Figure 5).

Figure 5 Tendencies for the extreme precipitation indices for the observed period in the investigated area.
Figure 5

Tendencies for the extreme precipitation indices for the observed period in the investigated area.

The number of heavy precipitation days (R10mm) is increasing, with varying degree of statistical significance at only three stations in Vojvodina (Banatski Karlovac, Kikinda and Palić) (Figure 5). The number of consecutive dry days (CDD) is declining in the southern part of the investigated area with only one station recording statistical significance (Rimski Šančevi in northern Serbia). The number of consecutive wet days (CWD) is declining in Hungary, and in Osijek this value is rising. The only station with the significant positive trend is Pécs.

Annual total precipitation when it exceeds 95th percentile (R95p) is increasing in the investigated area, with the exception of Budapest meteorological station (Figure 5). The increasing trend is significant at different confidence intervals (Figure 5). There are few stations that have negative trends such as Szombathely and Debrecen.

For R95p and R99p positive station trend for Europe dominates the period between 1946 and 1999 [47]. The mentioned authors also found that positive trend is mostly correlated with stations where the annual amount of precipitation increases. On the other hand, a negative trend does occur mostly at stations in areas with decreased precipitation. Similarly, for the Carpathian basin Bartholy and Pongrácz [52] found that the regional intensity and frequency of extreme precipitation has increased during the period between 1976 and 2001, while the total precipitation has decreased in the region.

Also, several IPCC emission scenarios have been compared and GCM outputs have been used to calculate precipitation extremes in Carpathian basin. The results suggested that climate of this region may become drier in summer and wetter in winter [16, 99, 100]. During the twentieth century, on the wettest day across Serbia the average annual precipitation increased by nearly 9%. Statistically insignificant increasing trends were found on each of the ten wettest days across Serbia. At the end of the 20th century in Serbia heavy precipitation indices also increased.

Similar results were obtained by Malinović-Milićević et al. [135]. Amount and intensity of precipitation in Serbia had statistically significant increase but only during autumn and were most pronounced in the northern (Vojvodina) and western parts of the country. Generally, no significant decrease in the maximum number of consecutive dry days or increase in the wet days (except in autumn) was found. The authors showed that that “dry” regimes dominate over “wet”, with increasing trend of “warm” regimes and decreasing trend of “cold” regimes. The correlation between the examined extreme indices and the large-scale circulation patterns showed that EA and NAO had significant influence on duration of winter warm periods, while their influence on duration of cold periods cannot be confirmed with certainty.

4 Conclusion

The potential of rain to generate soil erosion is known as rainfall erosivity, and its estimation is of great importance for the understanding of climatic vulnerability of a given region. Also, the occurrence of extreme events such as very heavy precipitation episodes, have a great impact on society due to the greater climate variability effects.

Observation of rainfall erosivity in the Pannonian basinwas carried out on the basis of the analysis of rainfall aggressiveness trends, extreme precipitation indices, and their spatial variability for the period 1961-2014. This study presents the first results of combined rainfall erosivity and extreme precipitation indices for the investigated area. Furthermore, the analysis, applied to the present climate conditions, reveal necessary information which can be used by decision makers on various levels, for the development of prevention activities and for the promotion of mitigation measures at all levels: local, national and regional.

Trends in annual precipitation amounts indicate that the larger parts of the investigated area display an increase in total annual rainfall with the exception of Debrecen, Budapest and Szombathely, where the decrease was observed.

In northern Serbia PCI values belong to the group of moderate precipitation distribution, and the presence of a statistically significant trend in the variability of PCI was not observed. For the stations in Hungary, PCI suggests that this area can be seen as having a moderate precipitation concentration. Meteorological stations in Hungary do not show the presence of a statistically significant trend, although the trend has a positive tendency that indicates an increase in the index value at annual level. The Pannonian part of eastern Croatia also does not show the presence of a statistically significant trend and lies within the moderate precipitation concentrations class.

The seasonal values of PCI for the Vojvodina area (northern Serbia) generally show uniform values, where the winter season exhibits higher values than other seasons for all investigated stations during the investigated period. Statistically significant increasing trend was not detected. PCI on seasonal scale for Hungary have similar tendency as the ones in northern Serbia, but with pronounced presence of statistically significant trends. On the other hand, seasonal variations of PCI for Pannonian part of Croatia correspond to the situation observed for Vojvodina region with increasing tendencies for winter and summer seasons and declining values for spring and autumn seasons, but without statistical significance.

The area of northern Serbia, Hungary and eastern Croatia generally belongs to the erosive class of low values (20-40). The investigated trends generally point to a progressive increase in the values of the erosion index at the annual level, which in the future can lead to the transition to higher erosive classes and increase the sensitivity to pluvial erosion in the Pannonian basin. The results of MFI correspond to the results of the FI, and according to this index, the investigated area belongs to the erosive class of low values. The observed MFI trends generally follows the FI indicating a progressive increase in the values at the annual level (except for the northwestern parts of the Pannonian basin), which in the future could lead to a transition to higher erosion classes and an increase in hazardous sensitivity in the Pannonian basin.

The precipitation extremes suggest that both the amount and the intensity of precipitation are increasing and varying in some areas of the Pannonian basin, which is in a good agreement with the studies conducted for Serbia, Hungary and Croatia, as well as the ones done for the European continent.

The results of this study can contribute to the erosivity studies since the focus is given to the dynamics of the main climatological agent of erosion – precipitation. Hence, utilization of the more complex and sensitive indices such as EI30 along with physically based models for estimating soil erosion rates (e.g. USLE, RUSLE, RUSLE2), can provide a more suitable approach for detailed rainfall erosivity estimation in some future studies when it comes to filling the gap on the rainfall erosivity map of Europe provided by Panagos et al. [134]. Since erosion is highly dependent on topography and land use, the next stage of the investigation of these parameters should be oriented towards incorporation into the GIS environment in order to determine erosion potential and its spatial causality.

Acknowledgement

This research was supported by Projects 176020 and 43002 of the Serbian Ministry of Education, Science and Technological Development and by Project 114-451-2080/2017 of the Provincial Secretariat for Science and Technological Development, Vojvodina Province. Part of the research was supported by the HUSRB/1602/11/0057 – WATER@RISK – Improvement of drought and excess water monitoring for supporting water management and mitigation of risks related to extreme weather conditions. We confirm that all the authors made an equal contribution to the study’s development. Authors are grateful to the anonymous reviewer’s whose comments and suggestions greatly improved the manuscript.

References

[1] IPCC. Climate Change 2007. The Scientific Basis. Cambridge, University Press, New York, 1-976Search in Google Scholar

[2] Ren G.Y., Wu H., Chen Z.H., Spatial patterns of change trend in rainfall of China. Q. J. Appl. Meteorol., 2000, 11(3), 322-330Search in Google Scholar

[3] Gong D.Y., Ho C.H., The Siberian High and climate change over middle to high latitude Asia. Theor. Appl. Climatol., 2002, 72(1-2), 1-910.1007/s007040200008Search in Google Scholar

[4] Zhai P.M., Zhang X.B., Wang H., Pan X.H., Trends in total precipitation and frequency of daily precipitation extremes over China. J. Clim., 2005, 18, 1096-110810.1175/JCLI-3318.1Search in Google Scholar

[5] Karl T.R., Knight R.W., Easterling D.R., Quayle R.G., Indices of climate change for the United States. Bull. Amer. Meteor. Soc., 1996, 77, 279-29210.1175/1520-0477(1996)077<0279:IOCCFT>2.0.CO;2Search in Google Scholar

[6] Kutiel H., Maheras P., Guika S., Circulation indices over the Mediterranean and Europe and their relationship with rainfall conditions across the Mediterranean. Theor. Appl. Climatol., 1996, 54, 125-13810.1007/BF00865155Search in Google Scholar

[7] Piervitali E., Colacino M., Conte M., Rainfall over the central-western Mediterranean basin in the period 1951 – 1995, Part I: Precipitation trends, Nuovo Cimento, 1998, C21, 331-344Search in Google Scholar

[8] Xoplaki E., Luterbacher J., González-Rouco J.F., Mediterranean summer temperature and winter precipitation, large-scale dynamics, trends. Il Nuovo Cimento, 2006, 29, 45-54Search in Google Scholar

[9] Amanatidis G.T., Paliatsos A.G., Reparis C.C., Bartzis J.G., Decreasing precipitation trend in the Marathon Area, Greece. Int. J. Climatol., 1993, 13, 191-20110.1002/joc.3370130205Search in Google Scholar

[10] Esteban-Parra M., Rodrigo F.S., Castro-Díez Y., Spatial and temporal patterns of precipitation in Spain for the period 1880-1992. Int. J. Climatol., 1998, 18(14), 1557-157410.1002/(SICI)1097-0088(19981130)18:14<1557::AID-JOC328>3.0.CO;2-JSearch in Google Scholar

[11] De Luis M., Raventos J., Gonzalez-Hidalgo J.C., Sanchez J.R., Cortina J., Spatial analysis of rainfall trends in the region of Valencia (East Spain). Int. J. Climatol., 2000, 20, 1451-146910.1002/1097-0088(200010)20:12<1451::AID-JOC547>3.0.CO;2-0Search in Google Scholar

[12] Feidas H., Noulopoulou Ch., Makrogiannis T., Bora-Senta E., Trend analysis of precipitation time series in Greece and their relationship with circulation using surface and satellite data: 1955–2001. Theor. Appl. Climatol., 2007, 87(1), 155-17710.1007/s00704-006-0200-5Search in Google Scholar

[13] Del Rio S., Herrero L., Frale R., Penas A., Spatial distribution of recent rainfall trends in Spain (1961-2006). Int. J. Climatol., 2011, 31(5), 656-66710.1002/joc.2111Search in Google Scholar

[14] Luković J., Bajat B., Blagojević D., Kilibarda M., Spatial pattern of recent rainfall trends in Serbia (1961-2009). Reg. Environ. Change., 2014, 14(5), 1789-179910.1007/s10113-013-0459-xSearch in Google Scholar

[15] Tošić I., Hrnjak I., Gavrilov M.B., Unkašević M., Marković S.B., Lukić T., Annual and seasonal variability of precipitation in Vojvodina, Serbia. Theor. Appl. Climatol., 2014, 117, 331-34110.1007/s00704-013-1007-9Search in Google Scholar

[16] Bartholy J., Pongrácz R., Analysis of precipitation conditions for the Carpathian Basin based on extreme indices in the 20th century and climate simulations for 2050 and 2100. Phys. Chem. Earth., 2010, Parts A/B/C, 35(1-2), 43-5110.1016/j.pce.2010.03.011Search in Google Scholar

[17] Filipčić A., Orešić D., Maradin M., Changes in precipitation levels in Croatia from the mid 20th century to the present, Geoadria, 2013,18(1), 29-3910.15291/geoadria.145Search in Google Scholar

[18] Gajić-Čapka M., Cindrić K., Secular trends in indices of precipitation extremes in Croatia, 1901-2008, Geofizika, 2011, 28(2), 293-312Search in Google Scholar

[19] Zhang L., Su F., Yang D., Hao Z., Tong K., Discharge regime and simulation for the upstream of major rivers over Tibetan Plateau. J. Geophys. Res. Atmos., 2013, 118, 8500-851810.1002/jgrd.50665Search in Google Scholar

[20] Parajka J., Kohnova S., Balint G., Barbuc M., Borga M, Claps P. et al., Seasonal characteristics of flood regimes across the Alpine–Carpathian range. J. Hydrol., 2010, 394(1-2), 78-8910.1016/j.jhydrol.2010.05.015Search in Google Scholar PubMed PubMed Central

[21] Beniston M., Stephenson D.B., Extreme climatic events and their evolution under changing climatic conditions. Glob. Planet. Change, 2004, 44, 1-910.1016/j.gloplacha.2004.06.001Search in Google Scholar

[22] Kunkel K.E., Easterling D.R., Redmond K., Hubbard K., Temporal variations of extreme precipitation events in the United States: 1895-2000. Geophys. Res. Lett., 2003, 30(17), 1900, doi:10.1029/2003GL01805210.1029/2003GL018052Search in Google Scholar

[23] Peterson T.C., Taylor M.A., Demeritte R., Duncombe D.L., Burton S., Thompson F. et al., Recent changes in climate extremes in the Caribbean region. J. Geophys. Res., 2002, 107, (D21), 4601, doi:10.1029/2002JD00225110.1029/2002JD002251Search in Google Scholar

[24] Zhang X., Aguilar E., Sensoy S., Melkonyan H., Taguyeva U., Nader A. et al., Trends in Middle East climate extreme indices from 1950 to 2003. J. Geophys. Res., 2005, 110, D22104, doi:10.1029/2005JD00618110.1029/2005JD006181Search in Google Scholar

[25] Ferrari E., Caloiero T., Coscarelli R., Influence of the North Atlantic Oscillation on winter rainfall in Calabria (southern Italy). Theor. Appl. Climatol., 2013, 114, 479-49410.1007/s00704-013-0856-6Search in Google Scholar

[26] Bradley R.S., Diaz H.F., Eischeid J.K., Jones P.D., Kelly P.M., Good-ess C.M., Precipitation fluctuation over Northern Hemisphere land areas since mid-19th century. Science, 1987, 237, 171-17510.1126/science.237.4811.171Search in Google Scholar

[27] Diaz H.F., Bradley R.S., Eischeid J.K., Precipitation fluctuation over global land areas since the late 1800s. J. Geophys. Res., 1989, 94, 1195-121010.1029/JD094iD01p01195Search in Google Scholar

[28] Hulme M., Osborn T.J., Precipitation sensitivity to global warming: Comparison of observations with HadCM2 simulations. Geo-phys. Res. Lett., 1998, 25(17), 3379-338210.1029/98GL02562Search in Google Scholar

[29] New M., Todd M., Hulme M., Jones P., Precipitation measurements and trends in the twentieth century. Int. J. Climatol., 21, 1899-192210.1002/joc.680Search in Google Scholar

[30] Lawrimore J.H., Halpert M.S., Bell G.D., Menne M.J., Lyon B., Schnell R.C. et al., Climate Assessment for 2000. Bull. Amer. Meteor. Soc., 2001, 82(6), 1304-130410.1175/1520-0477(2001)082<1304:CAF>2.3.CO;2Search in Google Scholar

[31] Klein Tank A.M.G., Wijngaard J.B., Können G.P., Bohm R., Demaree G., Gocheva A. et al., Daily dataset of 20th-century surface air temperature and precipitation series for the European climate assessment. Int. J. Climatol., 2002, 22, 1441-145310.1002/joc.773Search in Google Scholar

[32] Ciofl F., Lall U., Rus E., Krishnamurthy B.C.K., Space-time structure of extreme precipitation in Europe over the last century. Int. J. Climatol., 2015, 35, 1749-176010.1002/joc.4116Search in Google Scholar

[33] Brunetti M., Maugeri M., Nanni T., Auer I., Böhm R., Schöner W., Precipitation variability and changes in the greater Alpine region over the 1800–2003 period. J. Geophys. Res., Atmospheres, 2006, 111 (D11107), doi:10.1029/2005JD00667410.1029/2005JD006674Search in Google Scholar

[34] Brunetti M., Maugeri M., Monti F., Nanni T., Temperature and precipitation variability in Italy in the last two centuries from homogenised instrumental time series. Int. J. Climatol., 2006, 26, 345-38110.1002/joc.1251Search in Google Scholar

[35] Norrant C., Douguédroit A., Monthly and daily precipitation trends in the Mediterranean (1950-2000). Theor. Appl. Climatol., 2006, 83(1-4), 88-10610.1007/s00704-005-0163-ySearch in Google Scholar

[36] Gonzalez-Hidalgo J.C., Brunetti M., de Luis M., A new tool for monthly precipitation analysis in Spain: MOPREDAS database (monthly precipitation trends December 1945-November 2005). Int. J. Climatol., 2011, 31, 715-73110.1002/joc.2115Search in Google Scholar

[37] Sharma K.P., Moore III B., Vorosmarty C.J., Anthropogenic, Climatic and Hydrologic Trends in the Koshi Basin, Himalaya. Clim. Change, 2000, 47(1-2), 141-16510.1023/A:1005696808953Search in Google Scholar

[38] Hamilton J.P., Whitelaw G.S., Fenech A., Mean annual temperature and total annual precipitation trends at Canadian biosphere reserves. Environ. Monit. Assess., 2001, 67, 239-27510.1023/A:1006490707949Search in Google Scholar

[39] Lucero O.A., Rozas D., Characteristics of aggregation of daily rainfall in a middle-latitudes region during a climate variability in annual rainfall amount. Atmos. Res., 2002, 61, 35-4810.1016/S0169-8095(01)00101-6Search in Google Scholar

[40] Boyles R.P., Raman S., Analysis of climate trends in North Carolina (1949-1998). Environ. Int., 2003, 29, 263-27510.1016/S0160-4120(02)00185-XSearch in Google Scholar

[41] De Luis M., Gonzalez-Hidalgo J.C., Raventos J., Cortina J., Sanchez J.R., Estudio espacial y temporal de las tendencias de la lluvia en la comunidad valenciana (1961-1990). Cuadernos de Investigacion Geografica, 1998, 24, 7-24 (in Spanish with English summary)10.18172/cig.1023Search in Google Scholar

[42] Lana X., Burgueño A., Some statistical characteristics of monthly and annual pluviometric irregularity for the Spanish Mediterranean coast. Theor. Appl. Climatol., 2000, 65, 79-9710.1007/s007040050006Search in Google Scholar

[43] Douguédroit A, Norrant C., Annual and seasonal century-scale trends of the precipitation in the Mediterranean area during the twentieth century, In: Bölle H-J (Ed.), Mediterranean climate, Variability and trends. Springer, 2003, 159-16310.1007/978-3-642-55657-9_9Search in Google Scholar

[44] Norrant C., Douguédroit A., Trécentes des précipitations et des pressions de surface dans le Bassin méditerranéen. Ann. Géo., 2003, 631, 298-305 (in French)10.3406/geo.2003.917Search in Google Scholar

[45] Xoplaki E., González-Rouco J.F., Luterbacher J., Wanner H., Wet season Mediterranean precipitation variability: Influence of large-scale dynamics and trends. Clim. Dyn., 2004, 23(1), 63-7810.1007/s00382-004-0422-0Search in Google Scholar

[46] Brunetti M., Buffoni L., Maugeri M., Nanni T., Precipitation intensity trends in Northern Italy. Int. J. Climatol., 2000, 20, 1017-103110.1002/1097-0088(200007)20:9<1017::AID-JOC515>3.0.CO;2-SSearch in Google Scholar

[47] Klein Tank A.M.G., Können G.P., Trends in Indices of Daily Temperature and Precipitation Extremes in Europe, 1946–99. J. Climate., 2003, 16, 3665-368010.1175/1520-0442(2003)016<3665:TIIODT>2.0.CO;2Search in Google Scholar

[48] Moberg A, Jones P.D. Trends in indices for extremes in daily temperature and precipitation in central and western Europe, 1901-99. Int. J. Climatol., 2005, 25, 1149-117110.1002/joc.1163Search in Google Scholar

[49] Zolina O., Simmer C., Kapala A., Gulev S., On the robustness of the estimates of centennial-scale variability in heavy precipitation from station data over Europe. Geophys. Res. Lett., 2005, 32: L14707, doi:10.1029/2005GL02323110.1029/2005GL023231Search in Google Scholar

[50] Moberg A., Jones P.D., Lister D., Walther A., Brunet M., Jacobeit J. et al. Indices for daily temperature and precipitation extremes in Europe analyzed for the period 1901-2000. J. Geophys. Res., 2006, 111, D22106. doi:10.1029/2006JD00710310.1029/2006JD007103Search in Google Scholar

[51] Burt T.P., Horton B.P., Inter-decadal variability in daily rainfall at Durham (UK) since the 1850s. Int. J. Climatol., 2007, 27, 945-95610.1002/joc.1443Search in Google Scholar

[52] Bartholy J., Pongrácz R., Regional analysis of extreme temperature and precipitation indices for the Carpathian Basin from 1946 to 2001. Glob. Planet. Change, 2007, 57, 83-9510.1016/j.gloplacha.2006.11.002Search in Google Scholar

[53] Malinovic-Milicevic S., Radovanovic M.M., Stanojevic G., Milovanovic B. Recent changes in Serbian climate extreme indices from 1961 to 2010. Theor. Appl. Climatol., 2016, 124, 1089–1098.10.1007/s00704-015-1491-1Search in Google Scholar

[54] Anđelković G., Jovanović S., Manojlović S., Samardžić I., Živković Lj., Šabić D. et al. Extreme Precipitation Events in Serbia: Defining the Threshold Criteria for Emergency Preparedness. Atmosphere, 2018, 9, 188, doi:10.3390/atmos905018810.3390/atmos9050188Search in Google Scholar

[55] Willems P., Multidecadal oscillatory behaviour of rainfall extremes in Europe. Clim. Change, 2013, 120, 931-94410.1007/s10584-013-0837-xSearch in Google Scholar

[56] Łupikasza B.E., Seasonal patterns and consistency of extreme precipitation trends in Europe, December 1950 to February 2008. Clim. Res., 2017, 72, 217-23710.3354/cr01467Search in Google Scholar

[57] Vallejo V.R., Diaz-Fierros F. De la Rosa D. Impactos sobre los recursos edaficos. In: Moreno J.M (Ed.), Evaluacion Preliminar General de Los Impactos en Espanapor Efecto del Cambio Climatico, Ministerio de Medio Ambiente, Madrid, 2005, 355-398Search in Google Scholar

[58] De Luis M., Gonzales-Hidalgo J.C., Longares L.A., Is rainfall erosivity increasing in Mediterranean Iberian Peninsula. Land Degrad. Dev., 2010, 21, 139-14410.1002/ldr.918Search in Google Scholar

[59] Blinkov I., The Balkans: The most erosive part of Europe? Glasnik Šumarskog fakulteta, 2015, 111, 9-2010.2298/GSF1511009BSearch in Google Scholar

[60] Lukić T., Leščešen I., Sakulski D., Basarin B., Jordaan A., Rainfall erosivity as an indicator of sliding occurrence along the southern slopes of the Bačka loess plateau: a case study of the Kula settlement, Vojvodina (North Serbia). Carpath. J. Earth Env., 2016, 11(2), 303-318Search in Google Scholar

[61] Bjelajac D, Lukić T, Micić T, Miljković Ð, Sakulski D. Rainfall erosivity as an indicator of potential threat to erosion vulnerability in protected areas of Vojvodina (North Serbia). In: Vasiljević Ð. (Ed.), Conference Proceedings: Monitoring and management of visitors in recreational and protected areas, Novi Sad, 2016, 478–480Search in Google Scholar

[62] Lukić T., Bjelajac D., Fitzsimmons K.E., Marković S.B., Basarin B., Mlađan D. et al., Factors triggering landslide occurrence on the Zemun loess plateau, Belgrade area, Serbia. Environ. Earth Sci., 2018, 77, 519, doi:10.1007/s12665-018-7712-z10.1007/s12665-018-7712-zSearch in Google Scholar

[63] Markantonis V., Meyer V., Schwarze R. Valuating the intangible effects of natural hazards – review and analysis of the costing methods, Nat. Hazards Earth Syst. Sci., 2012, 12, 1633-164010.5194/nhess-12-1633-2012Search in Google Scholar

[64] Rawat P. K., Tiwari P.C., Pant C.C., Sharama A.K., Pant P.D., Modelling of stream run-off and sediment output for erosion hazard assessment in Lesser Himalaya: need for sustainable land use plan using remote sensing and GIS: a case study, Nat. Hazards, 2011, 59, 1277-129710.1007/s11069-011-9833-5Search in Google Scholar

[65] Berger F., Rey F., Mountain protection forests against natural hazards and risks: new French developments by integrating forests in risk zoning, Nat. Hazards, 2004, 33, 395-40410.1023/B:NHAZ.0000048468.67886.e5Search in Google Scholar

[66] Gares P.A., Sherman D.J., Nordstrom K.F., Geomorphology and natural hazards, Geomorphology, 1994, 10, 1-1810.1016/B978-0-444-82012-9.50005-0Search in Google Scholar

[67] Mather A.S., The changing perception of soil erosion in New Zealand, The Geogr. J., 1982, 148, 207-21810.2307/633772Search in Google Scholar

[68] Van Beek R., Assessment of the influence of changes in climate and land use on landslide activity in a Mediterranean environment. PhD thesis, Faculty of Geosciences, Utrecht University, Netherlands, 2002 (in English)Search in Google Scholar

[69] Bosco C., Sander G., Estimating the effects of water-induced shallow landslides on soil erosion, IEEE Earthzine 7(2), 2014, 1-1410.1101/011965Search in Google Scholar

[70] Pradhan B., Chaudhari A., Adinarayana J., Buchroithner M.F., Soil erosion assessment and its correlation with landslide events using remote sensing data and GIS: a case study at Penang Island, Malaysia, Environ. Monit. Assess., 2012, 184, 715-72710.1007/s10661-011-1996-8Search in Google Scholar

[71] Bosco C., de Rigo D., Dewitte O., Poesen J., Panagos P., Modelling soil erosion at European scale: towards harmonization and reproducibility. Nat. Hazards Earth Sys. Sci., 2015, 15, 225-24510.5194/nhess-15-225-2015Search in Google Scholar

[72] Li X., Ye X., Variability of Rainfall Erosivity and Erosivity Density in the Ganjiang River Catchment, China: Characteristics and Influences of Climate Change. Atmosphere, 2018, 9(2), 48, doi:10.3390/atmos902004810.3390/atmos9020048Search in Google Scholar

[73] Silva A.M., Rainfall erosivity map for Brazil. Catena, 2004, 57, 251-25910.1016/j.catena.2003.11.006Search in Google Scholar

[74] Wischmeier W.H., A Rainfall Erosion Index for a Universal Soil-Loss Equation. Soil Sci. Soc. Am. J., 1959, 23, 246-24910.2136/sssaj1959.03615995002300030027xSearch in Google Scholar

[75] Angulo-Martińez M., Begueriá S., Estimating rainfall erosivity from daily precipitation records: A comparison among methods using data from the Ebro Basin (NE Spain). J. Hydrol., 2009, 379(1), 111-12110.1016/j.jhydrol.2009.09.051Search in Google Scholar

[76] De Santos Loureiro N., De Azevedo Coutinho M., A new procedure to estimate the RUSLE EI30 index, based on monthly rainfall data and applied to the Algarve region, Portugal. J. Hydrol., 2001, 250(1-4), 12-1810.1016/S0022-1694(01)00387-0Search in Google Scholar

[77] Arnoldus H.M.J., An approximation of the rainfall factor in the Universal Soil Loss Equation. In: De Boodt M., Gabriels D. (Ed.), Assessment of Erosion, John Wiley and Sons, New York, 1980, 127-132Search in Google Scholar

[78] Gregori E., Costanza M., Zorn G., Assessment and classification of climatic aggressiveness with regard to slope instability phenomena connected to hydrological and morphological processes. J. Hydrol., 2006, 329, 489-49910.1016/j.jhydrol.2006.03.001Search in Google Scholar

[79] Renard K.G., Freimund J.R., Using Monthly Precipitation Data to Estimate the R-Factor in the Revised USLE. J. Hydrol., 1994, 157, 287-30610.1016/0022-1694(94)90110-4Search in Google Scholar

[80] Gabriels D., Rain erosivity in Europe. In: Rubio J.L., Morgan R.P.C., Asins S., Andreu V. (Ed.), Man and Soil in the Third Millenium, Geoforma Ediciones, Logroño, 2002, 99-108Search in Google Scholar

[81] Diodato N., Bellocchi G., Estimating monthly (R) USLE climate input in a Mediterranean region using limited data. J. Hydrol., 2007, 345, 224-23610.1016/j.jhydrol.2007.08.008Search in Google Scholar

[82] Sanguësa C., Pizarro R., Ibañez A., Pino J., Rivera D., Garćıa-Chevesich P. et al., Spatial and Temporal Analysis of Rainfall Concentration Using the Gini Index and PCI. Water, 2018, 10(2), 112, doi:10.3390/w1002011210.3390/w10020112Search in Google Scholar

[83] Michiels P., Gabriels D.,Hartmann R., Using the seasonal and temporal precipitation concentration index for characterizing monthly rainfall distribution in Spain. Catena, 1992, 19, 43-5810.1016/0341-8162(92)90016-5Search in Google Scholar

[84] Apaydin H., Erpul G., Bayramin I., Gabriels D., Evaluation of indices for characterizing the distribution and concentration of precipitation: A case for the region of Southeastern Anatolia Project, Turkey. J. Hydrol., 2006, 328: 726-73210.1016/j.jhydrol.2006.01.019Search in Google Scholar

[85] European Environment Agency, 2007Search in Google Scholar

[86] Van den Hurk B., Siegmund P., Klein Tank A., Attema J., Bakker A., Beersma, J., et al. KNMI14: climate change scenarios for the 21st century. De Bilt, The Netherlands, Technical report WR 2014-01, Royal Netherlands Meteorological Institute, 2015Search in Google Scholar

[87] Marx A., Bastrup-Birk A., Louwagie G., Wugt-Larsen F., Biala K., Fussel H.M., et al., Terrestrial ecosystems, soil and forests. In: Füssel M.H., Jol A., Marx A., Hildén M (Ed.), Climate Change, Impacts and Vulnerability in Europe 2016 - An indicator-based report. European Environment Agency, Luxembourg, 2017, 153-182Search in Google Scholar

[88] Croitoru A.E., Piticar A., Ciupertea F.A., Rosca C.F., Changes in heat wave indices in Romania over the period 1961-2015. Glob. Planet. Change, 2016, 146, 109-12110.1016/j.gloplacha.2016.08.016Search in Google Scholar

[89] Stadtherr L., Coumou D., Petoukhov V., Petri S. Rahmstorf S., Record Balkan floods of 2014 linked to planetary wave resonance. Sci. Adv., 2016, 2(4), p. e1501428, doi: 10.1126/sciadv.150142810.1126/sciadv.1501428Search in Google Scholar PubMed PubMed Central

[90] Spinoni J., Naumann G., Vogt J.V., Barbosa P., The biggest drought events in Europe from 1950 to 2012. J. Hydrol. Reg. Stud., 2015, 3, 509-52410.1016/j.ejrh.2015.01.001Search in Google Scholar

[91] Vučetić V., Feist O., Heat stress and agriculture in Croatia: past, present and future. In: Jug D, Güttler I. (Ed.), GEWEX workshop on the climate system of the Pannonian Basin, Osijek, Croatia, 2015, 1-1Search in Google Scholar

[92] Lukić T., Gavrilov M.B.,Marković S.B., Komac B., Zorn M., Mlađan D., et al., Classification of natural disasters between the legislation and application: experience of the Republic of Serbia. Acta Geogr. Slov., 2013, 53(1), 149-16410.3986/AGS53301Search in Google Scholar

[93] Basarin B., Lukić T., Pavić D., Wilby R.L., Trends and multi-annual variability of water temperatures in the river Danube, Serbia. Hydrol. Process., 2016, 30, 3315-332910.1002/hyp.10863Search in Google Scholar

[94] Basarin B., Lukić T., Mesaroš M., Pavić D., Ðorđević J., Matzarakis A., Spatial and temporal analysis of extreme bioclimate conditions in Vojvodina, Northern Serbia. Int. J. Climatol., 2018, 38, 142-15710.1002/joc.5166Search in Google Scholar

[95] Lung T., Hilden M., Multi-sectoral vulnerability and risks: Socioeconomic scenarios for Europe. In: Füssel M.H., Jol A., Marx A., Hildén M (Ed.), Climate Change, Impacts and Vulnerability in Europe 2016 - An indicator-based report. European Environment Agency, Luxembourg, 2017, 268-272Search in Google Scholar

[96] Milanović M., Micić T., Lukić T., Nenadović S.S., Basarin B., Filipović D.J., et al., Application of Landsat-derived NDVI in monitoring and assessment of vegetation cover changes in Central Serbia. Carpath. J. Earth Env., 2019, 14(1), 119-12910.26471/cjees/2019/014/064Search in Google Scholar

[97] UNEP, 2007. Carpathians Environment Outlook. GenevaSearch in Google Scholar

[98] Spinoni J., Vogt J., Barbosa P., European degree-day climatologies and trends for the period 1951–2011. Int. J. Climatol., 2014, 35, 25-3610.1002/joc.3959Search in Google Scholar

[99] Spinoni J., Szalai S., Szentimrey T., Lakatos M., Bihari Z., Nagy A., et al. Climate of the Carpathian Region in the period 1961–2010: climatologies and trends of 10 variables. Int. J. Climatol., 2015, 35, 1322-134110.1002/joc.4059Search in Google Scholar

[100] Kiss A., Pongrácz R., Bartholy J.Multi-model analysis of regional dry and wet conditions for the Carpathian Region. Int. J. Climatol. 2017, 37, 4543-456010.1002/joc.5104Search in Google Scholar

[101] Wijngaard J.B., Klein Tank, A.M.G., Können G.P., Homogeneity of 20th century European daily temperature and precipitation series. Int. J. Climatol., 2003, 23, 679-69210.1002/joc.906Search in Google Scholar

[102] Oliver J.E., Monthly precipitation distribution: A comparative index. Prof. Geogr., 1980, 32, 300-30910.1111/j.0033-0124.1980.00300.xSearch in Google Scholar

[103] De Luis M., Gonzales-Hidalgo J.C., Bruneti M., Longares L.A., Precipitation concentration changes in Spain 1946-2005. Nat. Hazard Earth Sys., 2011, 11, 1259-126510.5194/nhess-11-1259-2011Search in Google Scholar

[104] Lobo Lujan D., Gabriels D., Assessing the rain erosivity and rain distribution in different agro-climatological zones in Venezuela. Sociedade & Natureza, 2005, 1(1), 16-29Search in Google Scholar

[105] Mello C.R., Viola M.R., Beskow S., Norton L.D., Multivariate models for annual rainfall erosivity in Brazil. Geoderma, 2013, 202-203, 88-10210.1016/j.geoderma.2013.03.009Search in Google Scholar

[106] Khorsandi N., Mohdian H.M., Pazira E., Nikkami D., Comparison of Rainfall Erosivity Indices in Runoff-Sediment Plots in Northern Iran. World Appl. Sci. J., 2010, 10(8), 975-979Search in Google Scholar

[107] Renard K.G., Freimund J.R., Using monthly precipitation data to estimate the R-factor in the revised USLE. J. Hydrol., 1994, 157(1-4), 287-30610.1016/0022-1694(94)90110-4Search in Google Scholar

[108] Loureiro N.D., Coutinho M.D., A new procedure to estimate the RUSLE EI30 index, based on monthly rainfall data and applied to the Algarve region, Portugal. J. Hydrol., 2001, 250, 12-1810.1016/S0022-1694(01)00387-0Search in Google Scholar

[109] Diodato N., Bellocchi G., Estimating monthly (R) USLE climate input in a Mediterranean region using limited data. J. Hydrol., 2007, 345(3-4), 224-23610.1016/j.jhydrol.2007.08.008Search in Google Scholar

[110] Sfîru R., Cârdei P., Herea V., Ertekin C., Calculation of rainfall erosion intensity (rainfall erosivity) in Valea Călugărească wine growing area. INMATEH - Agricultural Engineering, 2011, 34(2), 23-28Search in Google Scholar

[111] Costea M. Using the Fournier Indexes in estimating Rainfall Erosivity. Case Study - The Secaşul Mare Basin. Aerul şi Apa: Componente ale Mediului, 2012, 313-320Search in Google Scholar

[112] Pellicone G., Caloiero T., Modica G., Guagliardi I., Application of several spatial interpolation techniques to monthly rainfall data in the Calabria region (southern Italy). Int. J. Climatol., 2018, 38, 3651-366610.1002/joc.5525Search in Google Scholar

[113] Gilbert R. O., Statistical methods for environmental pollution monitoring. Van Nostrand Reinhold, New York, 1987Search in Google Scholar

[114] Yue S., Pilon P., Phinney B., Cavadias G., The influence of autocorrelation on the ability to detect trend in hydrological series. Hydrol. Process., 2002, 16(9), 1807-182910.1002/hyp.1095Search in Google Scholar

[115] Mezo˝si G., Bata T., Estimation of the changes in the rainfall erosivity in Hungary. J. Environ. Geogr., 2016, 9(3-4), 43-4810.1515/jengeo-2016-0011Search in Google Scholar

[116] Krüzselyi I., Bartholy J., Horányi A., Pieczka I., Pongárcz R., Szabó P. et al. The future climate characteristics of the Carpathian Basin based on a regional climate model mini-ensemble. Adv. Sci. Res., 2011, 6, 69-7310.5194/asr-6-69-2011Search in Google Scholar

[117] Li X.M., Jiang F.Q., Li L.H., Wang G.G., Spatial and temporal variability of precipitation concentration index, concentration degree and concentration period in Xinjiang, China. Int. J. Climatol., 2011, 31, 1679-169310.1002/joc.2181Search in Google Scholar

[118] Shi P., Qiao X.Y., Chen X., Zhou M., Qu S.M., Ma X.X. et al., Spatial distribution and temporal trends in daily and monthly precipitation concentration indices in the upper reaches of the Huai River, China. Stoch. Env. Res. Risk Assess., 2014, 28, 201-21210.1007/s00477-013-0740-zSearch in Google Scholar

[119] Zhang Q., Xu C.Y.,Marco G., Chen Y.P., Liu C.L., Changing properties of precipitation concentration in the Pearl River basin, China. Stoch. Env. Res. Risk Assess., 2009, 23, 377-38510.1007/s00477-008-0225-7Search in Google Scholar

[120] Huang J., Sun S.L., Zhang J.C., Detection of trends in precipitation during 1960-2008 in Jiangxi Province, Southeast China. Theor. Appl. Climatol., 2013, 114, 237-25110.1007/s00704-013-0831-2Search in Google Scholar

[121] Wang W.G., Xing W.Q., Yang T., Shao Q.X., Peng S.Z., Yu Z.B. et al., Characterizing the changing behaviors of precipitation concentration in the Yangtze River Basin, China. Hydrol. Process., 2013, 27, 3375-339310.1002/hyp.9430Search in Google Scholar

[122] Huang Y., Wang H., Xiao W., Chen L., Yan D., Zhou Y. et al., Spatial and Temporal Variability in the Precipitation Concentration in the Upper Reaches of the Hongshui River Basin, Southwestern China. Adv. Meteorol., 2018, Article ID 4329757, 1-19, doi:10.1155/2018/432975710.1155/2018/4329757Search in Google Scholar

[123] He X., Chaney N.W., Schleiss M., Shefleld J., Spatial downscaling of precipitation using adaptable random forests, Water Resour. Res., 2016, 52, 8217-823710.1002/2016WR019034Search in Google Scholar

[124] Coscarelli R., Caloiero T., Analysis of daily and monthly rainfall concentration in Southern Italy (Calabria region). J. Hydrol., 2012, 416-417, 145-15610.1016/j.jhydrol.2011.11.047Search in Google Scholar

[125] Longobardi P., Montenegro A., Beltrami H., Eby M., Deforestation Induced Climate Change: Effects of Spatial Scale. PLoS One, 2016, 11(4), e0153357, doi:10.1371/journal.pone.015335710.1371/journal.pone.0153357Search in Google Scholar

[126] Martins D.S., Raziei T., Paulo A.A., Pereira L.S., Spatial and temporal variability of precipitation and drought in Portugal. Nat. Hazards Earth Syst. Sci., 2012, 12, 1493-150110.5194/nhess-12-1493-2012Search in Google Scholar

[127] Michiels P., Gabriels D., Hartmann R., Using the seasonal and temporal Precipitation concentration index for characterizing the monthly rainfall distribution in Spain. Catena, 1992, 19(1), 43-5810.1016/0341-8162(92)90016-5Search in Google Scholar

[128] Martin-Vide J., Spatial Distribution of a Daily Precipitation Concentration Index in Peninsular Spain. Int. J. Climatol., 2004, 24, 959-97110.1002/joc.1030Search in Google Scholar

[129] Alijani B., O’Brien J., Yarnal B., Spatial analysis of precipitation intensity and concentration in Iran. Theor. Appl. Climatol., 2008, 94(1), 107-12410.1007/s00704-007-0344-ySearch in Google Scholar

[130] Yeşilırmak E., Atatanır L., Spatiotemporal variability of precipitation concentration in western Turkey. Nat. Hazards, 2016, 81(1), 687-70410.1007/s11069-015-2102-2Search in Google Scholar

[131] Tošić I., Spatial and temporal variability of winter and summer precipitation over Serbia and Montenegro. Theor. Appl. Climatol., 2004, 77, 47-5610.1007/s00704-003-0022-7Search in Google Scholar

[132] Domonkos P., Kysely J., Piotrowicz K., Petrovic P., Likso, T., Variability of extreme temperature events in south – Central Europe during the 20th century and its relationship with large-scale circulation. Int. J. Climatol., 2003, 23, 987-101010.1002/joc.929Search in Google Scholar

[133] Bice D., Montanari A., Vucˇetić V., Vucˇetić M., The influence of regional and global climatic oscillations on Croatian climate. Int. J. Climatol., 2012, 32(10), 1537-155710.1002/joc.2372Search in Google Scholar

[134] Panagos P., Ballabio C., Borrelli P., Meusburger K., Klik A., Rousseva S. et al, Rainfall erosivity in Europe. Sci. Total Environ., 2015, 511, 801-81410.1016/j.scitotenv.2015.01.008Search in Google Scholar PubMed

[135] Malinović-Milićević S., Mihailović D.T., Radovanović M.M., Drešković N., Extreme Precipitation Indices in Vojvodina Region (Serbia). J. Geogr. Inst. Jovan Cvijić SASA, 2018, 68(1), 1-1510.2298/IJGI1801001MSearch in Google Scholar

Received: 2019-02-19
Accepted: 2019-08-27
Published Online: 2019-10-26

© 2019 T. Lukić et al., published by De Gruyter

This work is licensed under the Creative Commons Attribution 4.0 Public License.

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