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OPTAIN : Csorsza and Felső-Válicka [Hungary]

Last update
2025
Summary
The Csorsza case study is located in Veszprém County, Hungary. The size of the study site is 21.3 km2, where 29% of the total catchment area is forest, 29% orchards and vineyards, 17% shrubs, 13% is arable land, 6% is grassland, and 5% is urban.

Some selected analysis are performed at the Felső-Válicka catchment, too. The Felső-Válicka study site is located in Zala County, flows in south-north direction into the River Zala. The size of the catchment is 131 km2. 27% of the total catchment area is forest, 35% is cropland, 11% is grassland, 3% is wetland and 11% is urban.

Both study sites are located in the catchment of Lake Balaton, therefore state of the environment and nature in these small catchments influences the touristic and economic potential of the Balaton region. Their water and nutrient management affects water quantity and quality of the lake. Extreme weather events will increase the environmental and social conflicts in the region.

Main challenges identified in both sites are decreasing soil erosion and nutrient load, preventing flash floods, and implementing integrated water resources conservation.

OPTAIN project aims to identify effective combination of the NSWRMs and optimize their allocation, in order to improve water and nutrient retention in the soil and the catchments. Emphasis will be put on suitable options to foster the resilience of agricultural production to climate change.
Position
Latitude
46.90908
Longitude
17.67489
Biogeographical Region
Pannonian
Project
OPTAIN
National Id
HU_07
Implementation Status
Modeled

NUTS Code
HU23 - Dél-Dunántúl
Involved Partners
Authority type Authority name Role Comments

Water quality

Site Information Summary

Felső-Válicka: The case study belongs to the catchment of Lake Balaton. Its climate is  moderately cool and moderately humid. During the study period, the average annual temperature was 11 °C, and the average annual precipitation was 720 mm. The catchment is an erosional hilly area with an average elevation of 186 m, and its highest point reaches 328 m. The study area consists of 30% forest, 24% arable land, 6% other agricultural areas, 15% semi-natural shrub and grass vegetation, 6% meadow, 4% wetland, and 12% urban areas. 

Csorza: The case study belongs to the catchment of Lake Balaton. Its climate is  moderately warm and moderately humid. For the study period, the average annual temperature is 15.5 °C, and the average annual precipitation around 600 mm. Elevation ranges from 113 m to 385 m. Its dominant soil types are Cambisols, Calcisols, and Regosols. The study area consists of 29 % forest, 13 % arable land, 29 % orchard and vineyard, 17 % shrub,  6 % grassland and 5 % urban areas. 

Scale of the project

Project scale
Micro
Project scale specification
Micro-scale: catchment of Felső-Válicka Stream, which is the subcatchment of River Zala.
Micro-scale: soil profile-based modeling of different land use types (forest, vineyards) of the catchment of Csorsza Stream, which belong to the catchment of Lake Balaton.
Lifespan
analysed period: 2010-2020

Size of the project

Project area
Felső-Válicka: size of the modelled catchment is 124 km2. Csorsza: size of the modelled catchment is 21 km2.
Design land use change
 

Total cost
The total estimated cost is approximately 3,000 €/ha
Financing authorities
Authority name Type of funding Financing share Comments

Community involvment
No
Design consultation activity
Activity stage Name Key issues Comments
Policy target
Target purpose
Erosion Control
Improved Biodiversity
Increase Water Storage
Policy area
Policy area type Policy area focus Name Comments
Part of wider plan
0
Wider plan type
Wider plan type Wider plan focus Name Comments
Requirement directive
Requirement directive Specification
Policy and general governance summary

Hungary's Common Agricultural Policy (CAP) Strategic Plan for 2023-2027 emphasizes sustainable water management through various water retention measures aimed at enhancing environmental sustainability and climate resilience. Key initiatives include financial support for non-productive water protection investments and implementation of NSWRMs. For the 2025–2029 period, the payment system supports soil-improving managements on arable land.

Monitoring system

Presence of formal monitoring system
Hydrometeorological monitoring of the Felső-Válicka Stream is performed by the West-Transdanubian Water Directorate. Hydrometeorological monitoring of the Csorsza Stream is performed by the ATK.
Monitoring and Maintenance Summary

The maintenance cost for forested riparian buffers is 335 €/ha, while shrub-grass riparian buffers cost 248 €/ha and grassed riparian buffers 196 €/ha. Forested erosion control strips also require 335 €/ha for maintenance, with shrub-grass erosion control strips at 248 €/ha and grassed erosion control strips at 196 €/ha. No-till with cover crops leads to a maintenance cost reduction of 55 €/ha, thanks to fewer field operations, less machinery use, and lower fuel and labor costs. The practice of no-till with cover crops results in a reduction in maintenance costs of 2 Euro/ha compared to conventional tillage, due to lower fuel consumption. Finally, the conversion of arable land to grassland has the highest maintenance cost, amounting to 787 €/ha.

Success factor(s)
Success factor type Success factor role Comments Order
Barrier
Barrier type Barrier role Comments Order
Driver
Driver type Driver role Comments Order
Lessons learned Summary

No-till with cover crops management is projected to be the most efficient in reducing sediment loss and increasing soil moisture – its efficiency is related to the area covered as well, which was 100% of the cropland in our study.
Conversion to grassland uses more water, but it is expected to significantly decrease sediment loss and it is effective in ecosystem restoration, improved soil health, or flood mitigation.
Riparian buffers are projected to be effective in improving water quality, but have low influence on water retention. Erosion control strips are expected to reduce sediment loss. These linear landscape elements cover small areas, however, they are converted into non-productive land.

In Csorza we investigated drought tolerant plants and reduced tillage as NSWRM management methods. Among them we found that the drought tolerant plants had the lowest amount of water stored, next to the reduced tillage, and the highest was observed for the baseline, with no NSWRM implemented based on the profile scale simulations.