Paolo Billi

Prof. Paolo Billi

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Research Focus & Metrics

Academic Career Length

13Years (2014-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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24 March 2015
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Massimiliano FazziniMassimiliano Fazzini
Massimiliano Fazzini
CBCarlo Bisci
Carlo Bisci
PBPaolo Billi
Paolo Billi

14 December 2014 in Natural Hazards
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PBPaolo Billi
Paolo Billi
YAYonas Tadesse Alemu
Yonas Tadesse Alemu
RCRossano Ciampalini
Rossano Ciampalini

23 October 2020 in Water
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Velibor SpalevicVelibor Spalevic
Velibor Spalevic
GBGoran Barovic
Goran Barovic
DVDuško Vujačić
Duško Vujačić
MCMilic Curovic
Milic Curovic
MBMorteza Behzadfar
Morteza Behzadfar
PBPaolo Billi
Paolo Billi
Land use change in all river basins leads to changes in hydrologic response, soil erosion, and sediment dynamics characteristics. Those changes are often viewed as the main cause of accelerated erosion rates. We studied the impact of land use changes on soil erosion processes in one of the watersheds in Montenegro: the Miocki Potok, using this watershed as a pilot river basin for this area. We simulated responses of soil erosion processes by using a process-oriented soil erosion Intensity of Erosion and Outflow (IntErO) model, with different settings of land use for the years 1970, 1980, 1990, 2000, 2010, and 2020. The model provides fast, effective, and affordable insight into the effects of land use change on soil erosion processes. Testing of the applied procedures was important for the further establishment of watershed management methodologies at the national level, for the other 300 river basins of Montenegro. For the current state of land use, calculated peak discharge for the Miocki Potok was 364 m3 s−1 (2020)–372 m3 s−1 (1970) for the incidence of 100 years, and there is a possibility for large flood waves to appear in the studied basin. Real soil losses, Gyear, were calculated at 13680 m3 year−1 (2020) and specific 333 m3 km−2 year−1 (2020). A Z coefficient value of 0.439 (2020) indicated that the river basin belongs to destruction category III. The strength of the erosion process was medium, and according to the erosion type, it was mixed erosion. According to our analysis, the land use changes in the last 50 years influenced a decrease in the soil erosion intensity for 14% in the Miocki Potok River Basin. Further studies should be focused on the detailed analysis of the land use changes trends with the other river basins at the national level, closely following responses of soil erosion to the changed land use structure, and effects of plant-and-soil interaction on soil erosion and sediment dynamics.

24 March 2015
Verified
Book Chapter
Closed access
PDF file
PBPaolo Billi
Paolo Billi

1 August 2017 in Global and Planetary Change
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Journal Article
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PBPaolo Billi
Paolo Billi
Massimiliano FazziniMassimiliano Fazzini
Massimiliano Fazzini

23 March 2021 in Water
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MMMaziar Mohammadi
Maziar Mohammadi
Abdulvahed Khaledi DarvishanAbdulvahed Khaledi Darvishan
Abdulvahed Khaledi Darvishan
Velibor SpalevicVelibor Spalevic
Velibor Spalevic
BDBranislav Dudic
Branislav Dudic
PBPaolo Billi
Paolo Billi
Land use change is known as one of the main influencing factors on soil erosion and sediment production processes. The objective of the article is to study on how land use change impacts on soil erosion by using Intensity of Erosion and Outflow (IntErO) as a process-oriented soil erosion model. The study has been conducted under land use changes within the period of 1991–2014 in the Talar watershed located in northern Iran. The GIS environment was used to prepare the required maps including Digital Elevation Model (DEM), geology, land use, soil, and drainage network. The climatology data including average annual precipitation and air temperature as well as the volume of torrential rain were extracted from the data of meteorological stations located inside and around the study watershed. The results indicates that, within the period of 1991–2014, the forest area decreased by 12,478.04 ha (6%), while the other land uses including rainfed agriculture, rangeland, irrigated agriculture, and residential area increased by 7248.25, 4481.05, 476.00, and 273.95 ha, respectively. The estimated outflow with 100 year return interval was 432.14 m3 s−1 in 1991, which increased to 446.91 m3 s−1 in 2014. It can be concluded that the probability of larger and/or more frequent floods waves in the Talar River is expected to increase. In addition, the amount of production of erosion material (gross erosion) in the watershed increased from 1,918,186 to 2,183,558 m3 yr−1, and the real soil losses per year (sediment yield) of the watershed increased from 440,482.4 to 501,421.3 m3 yr−1. The results clearly emphasized how the lack of appropriate land management and planning leads to increase the maximum flow discharge and sediment yield of the watershed.