The effects of extreme rainfall events on agricultural foothill slopes in the Wiśnicz Foothills

 

Jolanta Święchowicz

Institute of Geography and Spatial Management

7 Gronostajowa Str, 30-387 Cracow, Poland

j.swiechowicz@geo.uj.edu.pl

 

 

Abstract:

Extreme rainfall events have the potential to cause intensive transformation of slopes surfaces and significant damage to agriculture. This paper presents the geomorphic and economic effects of three extreme rainfall events which took place at the Jagiellonian University’s farmland (Wiśnicz Foothills, southern Poland) in 2002-2006, giving special attention to the influence of land-use pattern on surface and rill erosion processes. Soil erosion by extreme rainfalls means the transport of the suspended material downslope and its deposition at the foot of the slopes and in valley bottoms. The loss of soil from farmland may be reflected in the farm’s production outcome, triggering an immediate loss of crop in the short term and reduction of yields in the longer term.

Key words: extreme rainfall events; soil erosion; rill erosion; Carpathian Foothills; southern Poland

 

Introduction

Soil erosion resulting from rainfall is usually most noticeable and spectacular during extreme events like local heavy downpours. In the temperate climate zone, agricultural slopes, devoid of natural vegetation cover, react very quickly to short-duration, high-intensity rainfall events and are one of the most dynamically developing relief forms especially in uplands and foothills (Olecki 1970; Teisseyre 1992, 1994; Smolska 1996, 2006; Starkel 1997; Gil 1998; Janicki and Zgłobicki 1998; Rodzik et al. 1998; Stankoviansky 2002; Szpikowski 2002; Cerdan et al. 2006). Soil erosion rarely happens on all the slopes in a catchment simultaneously and its intensity is differentiated along the longitudinal profile of the slope (Święchowicz 2000, 2004). Soil loss from farmland causes the reduction of the thickness of soil layer leading at times to its complete removal. Erosion not only causes permanent impoverishment of soil and the reduction of crop yield, but also makes farming difficult, and sometimes it permanently damages large land areas (Clark, Havercamp, Chapman 1985; Józefaciuk, Józefaciuk 1996; Morgan 1995; Rejman and Rodzik 2006). Additionally, if the cultivated fields are adjacent to built-up areas, those areas are likely to suffer damage as well (Auzet et al. 1990; Boardman 1995; Boardman et al. 2006; Stankoviansky et al. 2006). The aim of this paper is to present geomorphic and economic effects of three extreme rainfall events in the hydrological years 2002, 2005 and 2006 on agricultural fields on the Jagiellonian University farm and to explain the role of extreme precipitation on slope transformation in the Carpathian Foothills

 

Study area and methods

The paper uses the results of research carried out in the lowest part of the Carpathian Foothills, where the Field Research Station of the Institute of Geography and Spatial Management is located. The dominant type of relief are low hills and typical cover for this part of foothills is Quaternary loess-like formation (Święchowicz 2002).

The study was carried out in 2002-2006 on the basis of mapping of selected results of extreme rainfalls, which took place on the Jagiellonian University’s estate (Fig.1).

 

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Fig. 1. Location of the study area.

 

The estate covers the area of 103 ha. The soils are weakly differentiated. The majority of them are pseudogley soils (Stagnic Luvisols) developed from lessive soil (Haplic Luvisols) (Klimek 1995). In hydrological years 2002-2006, almost 86% of the area was arable land, which was used for crops like winter wheat, winter rape and sugar-beet (Fig. 2).

 

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Fig. 2. The Jagiellonian University’s farmland in Łazy. A – land use pattern,

B – agricultural land pattern in 2002, C – agricultural land pattern in 2005,

D – agricultural land pattern in 2006.

 

The analysis of the data collected at Meteorological Station in Łazy (Fig. 1) in hydrological years 1987-2006 makes it possible to assess the role of extreme rainfalls in slope transformation.

 

Extreme precipitation events

Mean annual precipitation from 1987 to 2006 amounted to 656.9 mm. Annual precipitation totals varied from almost 800 mm (1998, 2001) to 433.4 (2003) (Fig. 3a).

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Fig. 3. The characteristics of precipitation in hydrological years 1987-2006 (Łazy Research Station). A - annual precipitation totals, B - maximum daily precipitation from 1987-2006, C - number of days with daily amount of precipitation above 20 mm, 30 mm, 40 mm, 50 mm, 60 mm, 70 mm and 80 mm in hydrological years 1987-2006.

 

There were an average of 167.1 days with precipitation in the hydrological years from 1987 to 2006. Dominant were days with very weak (0.1-1 mm) and weak (1.1-5.0 mm) precipitation and they constituted 76.5% of all the days with precipitation. Days with strong and very strong precipitation (above 20.0 mm) constituted only 3.3% of all the days with precipitation and occurred mainly in the summer half-year. Maximum daily precipitation in a year varied from 21.0 mm in 1993 to 83.4 mm in 2006 (Fig. 3b). During 20 years of observation (1987-2006) rainfalls of daily sums over 40 mm took place 17 times and happened mainly in June (9) when the majority of slopes were sufficiently covered by vegetation. The rainfalls of daily sums over 50 mm took place four times and happened only in June. The rainfalls above 60 mm took place only twice in May and in July and the rainfall of daily sum of 83. 4 mm (rain gauge) took place only once (Fig. 3c).

 

Slope transformation during the extreme rainfall events

 

Hydrological year 2002

In 2002, 14% of the agricultural land of the university’s farmland was sugar-beet, which was sown in mid-April. The plants germinate within 7-20 days after sowing, and the first leaves start to appear within 7-10 days after germination. When plants form four leaves, they are thinned. As a result, distances between the plants in a row are 20-25 cm. Consequently, the period during which the cultivated land is devoid of a protective cover of leaves is quite long.

On the 29th of May there was rainfall of the amount of 40.2 mm. The result of the rainfall was among others a system of erosion rills, which joined and became the main route for transport of water and soil material. In June there were three intensive rainfalls; of the amounts of 42.7 mm (10-11th June), 30.1 mm (24th June) and 29.2 mm (28th June). After the rainfall of 28th June, the length of the main rill was 30 m, and its maximum depth was 68 cm. On the 16th July there was another rainfall with the amount of 40.4 mm and its initial intensity within the first 15 minutes was almost 1.3 mm/min (Fig 4a,b).

 

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Fig. 4. The characteristics of precipitation in hydrological year 2002 (Łazy Research Station) and the morphological results of intensive rainfall which took place on 16 July, 2002. A – daily precipitation totals in July 2002, B – precipitation total and mean intensity on 16 July, 2002, C – rill on the sugar-beet field in the Dworski Stream catchment, D – deluvial fan in the footslope part of the sugar-beet field in the Dworski Stream catchment, E – selected cross sections of the eroded rill on the sugar-beet field.

 

 

As a result of linear slope wash, the main rill deepened to maximum 120 cm and widened in its middle and lower section (Fig. 4c, e; Święchowicz 2004). There was also removal of parts of soil material which broke off its edges and the shift of the eroded rill up the slope. The deluvial fan was built up (Fig. 4d).

Such results were seen only on land with sugar-beet crops. On the remaining slopes the erosion was insignificant. The eroded material was accumulated in the footslope deluvial plain above the edge which separated it from the valley bottom. The deep rill was an incidental example of the results of linear slope wash on the slope in the catchment. Its formation was a consequence of a rainfall of a significant amount (daily total slightly above 40 mm) which occurred in the initial stage of the plant growth and of sowing of one type of crop on a significant area of the field. Subsequent rainfalls of high amounts and intensities led to the deepening and widening of the existing form irrespective of the vegetation cover (Święchowicz 2004). The eroded rills functioned only in the vegetation season and were removed by tillage.

 

Hydrological year 2005

In 2005, the dominant crop on the Jagiellonian University’s farm was sugar-beet, which covered 22% of the arable land. On the 9th and 10th of June took place the rainfalls which had the daily amounts of 14.6 and 51.1 mm respectively (Fig. 5).

 

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Fig. 5. The characteristics of precipitation in hydrological year 2005 (Łazy Research Station). A - daily precipitation totals in June 2005, B - daily precipitation totals in July 2005, C - daily precipitation totals in August 2005, D - daily precipitation totals in September 2005.

 

The result of the rainfall was the deep rill, which became the main route for transport of water and soil material. The deep rill formed only on one location on the field with sugar-beet crop, namely along a cart road going downslope. After the rainfalls which took place in June the maximum depth of eroded rill was 95.5 cm. The rill was active during the subsequent heavier rainfalls and was deepened during the rainfalls in July, August and September (Fig. 5). As a result of linear slope wash the rill deepened to maximum 200 cm and widened in its upper and middle section. There was also removal of parts of soil material which broke off its edges and the shift of the rill up the slope. The deluvial fan was to built up. Such a deep eroded rill was the only example of his type observed on the university’s arable land since 1987 (Fig. 6).

 

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Fig. 6. The geomorphic results of intensive rainfall which took place in 2005.

 

Hydrological year 2006

The transformation on the slopes took place on 17th June 2006 during rainfall of the amount of 83.4 mm, which lasted only 85 minutes and its maximum intensity was slightly above 3.8 mm.min-1 (Fig. 7).

 

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Fig. 7. The characteristics of precipitation in hydrological year 2006 (Łazy Research Station).A - daily precipitation totals in June 2006, B - daily totals precipitation in July 2006.

 

The rainfall caused intensive surface flow on the field with sugar-beet, which covered 12% of the crops in 2006. On one plot on the area of about 0.5 ha, all the plant seedlings were washed away together with the eroded soil. On the remaining fields with sugar-beets, the crops were silted up and consequently the yields were reduced. The results of the extreme rainfall were most visible on the grape-vine field. The vineyard was started in spring 2005 on the area of 0.3 ha. In spring (May) 2006 grape-vines were planted on additional 0.7 ha. Thus in June, when the rainfall took place, 0.7 ha of the vineyard was devoid of vegetation cover. Between the rows of grape-vine (which were 2.5 m apart) an intensive surface flow took place in several sections. Along the rows of grape-vine there formed rills which were most often several to over ten cm deep (Phot. 1). The eroded material was accumulated in the footslope deluvial plain above the edge which separated it from the valley bottom (Phot. 2). On the land with cereals there was intensive surface flow. However there wasn't intensive slope wash because of the dense vegetation cover.

 

Economic results of the extreme rainfall in 2006

Extreme rainfalls not only cause a change in the relief and profile of slopes, leading to the build-up of footslope deluvial plains but also cause financial losses and economic damage. The immediate result of thunderstorm rainfalls and heavy downpours may be damage to the natural land forms and to farm buildings or infrastructure faclities. The extreme rainfall event with 83.4 mm within 85 minutes and maximum intensity of 3.8 mm.min-1, which took place in June 2006 caused a lot of damage on the Jagiellonian University’s farm. The total damage was estimated to almost 38.5 thousand zloty. As a result of rainfalls, intensive erosion took place on fields where sugar-beet was sown. Although the sugar-beet crop of that year covered only 12% of the farm’s arable land, there was considerable damage. On slopes on the area of about 0.5 ha, the sugar-beet plants were totally washed off the field together with the soil (a), and on the footslope area the soil was accumulated, which brought about the silt-up of crops (b). On the remaining fields where sugar-beet was sown in the sections of accumulation of the soil eroded from slopes the crops were also silted up. The immediate result of the silt-up was that the growth of plants was stopped for 2-3 weeks. This and the drought in July were responsible for the fact that the sugar-beet crop yield in 2006 was 45% lower than in previous years, the damage being estimated to 30 thousand zloty. Such considerable damage was caused not only by the intensive rainfall but also the conditions of plants’ growth. The late and cold spring delayed the sowing. The plants which are usually sown in mid-April, in 2006 were sown at the beginning of May. This means that when the extreme rainfall took place, the plants were too small to manage the results of the rainfall. Intensive slope wash destroyed the herbicide protection and caused the spread of weeds, which in turn lowered the crop yield.

The insignificant damage was caused to fields with winter wheat which in 2006 was the dominant crop and covered almost 49% of the arable land. Considerable silt-up of crops took place only on fields with spring wheat, and consequently the crop yield was lowered from 5.5 t.ha-1 in 2004 to only 2.0 t.ha-1 in 2006. However, due to the small area of that crop (2%), the damage to the cereals were only a small portion in the total damage the farm suffered in 2006 as a result of one extreme rainfall. Despite high intensity of the rainfall and the accumulation of the washed-off soil in the footslope area covered by the vineyard, there was no damage to the grape-vine plants (Phot. 1 and 2).

 

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Water flowed freely between the rows forming in several sections erosion rills several to more than ten cm deep. 

The remaining financial losses resulted from the damage to technical structures or facilities. The pond’s dikes (c and d) and the fence (e) were destroyed and flood waters covered the area of 1ha (f), which later had to be drained (Fig. 1).

The role of extreme precipitation on slope transformation in the Carpathian Foothills

 

Short torrential rains play a decisive role in relief transformation in the Carpathian Foothills because during such events substantial amount of soil is transported. Not all relief forms are equally transformed. Top hill areas are least affected, the slopes and valley bottoms – much more. The results obtained confirm regularities occurring in other areas that severe erosion is more intensive when large areas of land are cultivated for one type of crop like sugar beet, rape or corn (Teisseyre 1992, 1994; Rodzik et al. 1998). The examples of erosion as presented in this article happened on one of only a few big farms which use large-scale intensive agriculture in the Wiśnicz Foothills. During the study area, the majority of the farm were arable fields (86%) used for sugar-beet, rape or corn crops. It was the sugar-beet field that underwent the most intensive slope transformation which resulted in the formation of rills and gullies, and the accumulation of deluvia in the footslope areas. New erosive forms were not permanent as they were removed by tillage after the sugar-beet harvest. However, soil eroded from the field was permanently accumulated in the form of deluvial fans at the foot of the slope or in the valley bottom.

When the slopes are separated from valley bottoms with a distinct edge, the eroded material is accumulated in form of deluvial fans above the edge.  It causes a buildup and widening of footslope parts. A clear morphological contrast between the slopes and the bottom of the valley is thus created. When the slopes gently transform into valley bottoms without a distinct edge and the land is ploughed up and down slope, the deposition of the material at the foot or in the valley bottom causes lengthening of the concave sections of the slope and as a result morphological contrasts between the slopes and the valley bottom become blurred (Święchowicz 2002, 2006).

It is worth emphasising that in the Carpathian Foothills dominant are small farms which cover the area of 3 ha on average and are divided into several plots. The adjacent plots are differently used. Foothill areas, due to short and gentle slopes and low infiltration of soil cover, have a longitudinal pattern of plots without stable transverse boundary strips. A stable pattern of small plots separated by boundary strips limits the effectiveness of erosion (Święchowicz 2002). On the other hand, as research carried out in Slovakia shows, getting rid of a traditional pattern of fields as well as boundary strips and escarpments and the introduction of large-scale intensive agriculture accelerates soil erosion (Stankoviansky 2002, Stankovianski et al. 2006).

 

Conclusions

Soil erosion may be a slow process which takes place seldom and continues relatively unnoticed. Only sporadic short-duration and high intensity rainfall events may trigger severe soil erosion causing serious loss of topsoil. The process leads to significant changes of the forms already present on the slope and to the formation of rills and gullies, and the material transported down the slope is accumulated at the bottom on the foodslope plains or in the valley bottom in the form of deluvial fans. Deposition of the material at the bottom of the slope and in the valley bottom leads to the elevation and extension of the valley bottom and at the same time it hinders transport of the solid material from the slope to the channel. Slope-channel coupling and sediment supply is only local and episodic. 

However, erosion forms which formed as a result of soil erosion on the slopes were not permanent. They occurred only in the vegetation season and were removed by tillage. Soil erosion rarely happens on all the fields simultaneously and its intensity is differentiated along the longitudinal profile of the slope. In the transformation of slopes a greater role is played by land use, the area of crops and how big the crops are during the rainfall rather than by the parameters of rainfall. Rainfall of the same parameters (amount, intensity and duration) causes different results depending on land use. Soil resistance to erosion depends on the type of crops and spatial crop structure.

The loss of soil from farmland may be reflected in immediate loss of crop and reduction of yields in the longer term. However the immediate losses or damage do not always have to be the result of extreme rainfall only. Sometimes a greater influence on the size of damage in agriculture may have type of crops and weather conditions (temperatures and rain) just before the occurrence of intensive rainfalls or immediately afterwards.

 

Acknowledgements

Thanks are due to Alicja Waligóra-Zblewska for preparing the English translation of the paper and Adam Kiszka the head of Jagiellonian University’s farmstead in Łazy for the information on land use patterns, rainfall damage data and helpful comments. This paper is partially supported by the Polish State Committee for Scientific Research Grants (grant no. PBZ KBN 086/P04/2003 and grant no. KBN PB P04E 050 93).

 

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