| Title | Abstract | Case study(ies) |
|---|---|---|
| WETLIFE project's final report and deliverables | The WETLIFE project aimed at reversal of negative changes in Amalva and Ž’uvintas mires. Restoration of hydrological conditions necessary for regeneration of mire habitats was the main key to reaching the aim. Additionally, the project had a goal to facilitate a shift in agricultural practices on peatlands in order to improve conditions for biodiversity and reduce rate of peat mineralization with all related environmental consequences. Finally, the project expected to raise awareness about wetlands and to serve as an example of successful wetland restoration and more sustainable use that could be replicated in other parts of the country. see also project video: http://vimeo.com/41861643 |
Restoration of Amalvas and Žuvintas Wetlands, Lithuania |
| Small (natural) water retention in rural areas | Since 1960`s in Poland a phrase „small retention† has been used although it has been unknown in other countries. †œSmall retention† means various forms of human activity aiming towards limiting the fast water runoff after snow melting and heavy rains. It is believed that water that has been retained in periods of its excess can supply water courses during summer. It can also be used for agricultural purposes as it increases water availability for crops and improves biodiversity of rural areas. Many different methods of water retention have been defined. Among others, increase of potential retention of surface waters can be achieved by construction of reservoirs or damming on rivers and lakes. Ground water retention capacity can be improved by increasing recharge of aquifers and improvement of soil structure in the aeration zone. Due to the form and way of implementation of small retention measures they can be divided into technical and non-technical measures. In other words, small retention can be defined as a set of measures aiming towards reconstruction of natural retention in the catchment that has been modified or destroyed by human activity. In this paper, it has been stressed that activities and tasks undertaken in Europe in recent years under phrase †œincrease of natural retention† can be covered by the definition of small retention. | Reconstruction and modernization of existing and construction of new reservoirs and ponds in rural areas of Poland |
| Small water reservoirs †“ their function and construction | Small water reservoirs play important role in rural areas. They used to be very popular, but most of them have been devastated in the last century. It is worth to restore them and to construct new ones. Very small reservoirs (ponds) can be constructed in economical and cost efficient way by individual farmers. In regard to damming below 1.0 m and to reservoirs situated outside protected areas, the permission for construction and the environmental impact assessment is not required. However, one should always keep in mind that even the smallest construction is the work of engineering and should be performed in accordance with the current standards. The increase of available water resources and improvement of water quality demand various measures including those aimed at reducing and limiting water runoff and pollutants transport from the river basins. One of the methods to improve the structure of water balance and the amount of water in rivers is the construction of a large number of small reservoirs, wetland reconstruction etc. Such reservoirs may be divided to: recreational, floristic and faunistic conservation sites, swimming pools, water quality protection (constructed wetlands) and infiltration reservoirs. Reservoirs can have many functions of the economic and natural character. If they are designed and constructed properly they can be a valuable element of the natural landscape in rural areas. Basic data for designing of small reservoirs serving mainly recreational (decorative) purposes and those used for water treatment and ground water recharge are given in the paper. |
Reconstruction and modernization of existing and construction of new reservoirs and ponds in rural areas of Poland |
| kowalewski.htm | An increase of water retention in the programmes of small retention in the country to the year 2015 is estimated at 1141 million m3. It means annual mean increase of retention capacity by c. 60 million m3. Accomplishment of relevant actions in the years 1997†“2007 allowed collecting 57 million m3 in lakes, c. 56 million m3 in artificial reservoirs, 18.5 million m3 in fishponds, c. 10.5 million m3 with the channel retention and over 2 million m3 in other investments. It makes total increase of water retention by 142 million m3 which is 12.4% of target retention and the mean annual increment of c. 13 million m3. The paper presents volumes of retained water, sources and structure of financing, mean unit costs of retention increments and the increase of retention capacity in particular voivodships (acc. to new administration division) in the years 1998†“2007. |
Reconstruction and modernization of existing and construction of new reservoirs and ponds in rural areas of Poland |
| The regulation of stream water quality and flow by a forested wetland, Kylmäojankorpi, Vantaa. | The Kylmäojankorpi case study represents a research work which aimed to assess whether and how existing forested wetland improves and regulates stream water quality and flow. | Kylmäojankorpi forested wetland, Vantaa, Finland |
| The Tolka catchment - fulfilling multiple roles: local government perspectives | Presentation on Tolka Valley Park, showing ecological measures and effects | River Tolka constructed wetland and enhancements, Ireland |
| Tolka Valley Greenway opening speech by Lord Mayor | Speech thanking participants and giving site overview | River Tolka constructed wetland and enhancements, Ireland |
| Performance Assessment of an Integrated Constructed Wetland-Pond System in Dublin, Ireland |
Chemical results from integrated wetlands, installtion of barley straw. | River Tolka constructed wetland and enhancements, Ireland |
| The Tolka catchment - fulfilling multiple roles: local government perspectives | Presentation of the Tolka catchment and its assets | River Tolka constructed wetland and enhancements, Ireland |
| Biodiversity Survey of the Integrated Constructed Wetland at Tolka Valley Park, Finglas, Co. Dublin | Ecological survey | River Tolka constructed wetland and enhancements, Ireland |
| Impact Assessment Of Urbanisation On Hydrology For The River Tolka In Dublin, Ireland: A Case Study Of Remote Sensing Supported Hydrological Modelling |
Discussion of a hydrological model studying the connections between surface water and land use in the Tolka catchment. | River Tolka constructed wetland and enhancements, Ireland |
| Modelprojekt Holter-Hammrich | As a secondary result of structures and buildings of flood water protection, NWRMs aiming at nature conservation can be implemented in the Holter-Hammrich Area. | Holter-Hammrich Area - Flood Protection and Nature Conservation, Germany |
| Project RMP5455: Slowing the Flow at Pickering, Final Report to Defra, Forest Research | The Project 'Slowing the Flow at Pickering' implements multiple natural flood risk measures including low level bunds, large woody debris dams, planting riparian and floodplain woodland, planting farm woodland, blocking moorland drains and establishing no-burn buffer zones, blocking forest drains and implementing farm-scale measures. The aim of the project is to show how land management measures can help to reduce flood risk from a river in the town and is implemented in close cooperation with local stakeholders. The project involved both the Pickering Beck and adjacent River Seven catchments, the description of measures described below relate to the former. | Slowing the Flow at Pickering, UK |
| WFD Surface Water Objectives 2012 | Spreadsheet containing the classification status and environmental objectives for surface water bodies across all River Basin Districts in England and Wales. | Slowing the Flow at Pickering, UK |
| National River Flow Archive | Data and catchment characteristics for Pickering Beck gauging station 27056 - Pickering Beck at Ings Bridge | Slowing the Flow at Pickering, UK |
| Potential Use of Runoff Attenuation Features in small Rural Catchments for Flood Mitigation | Development of a number of small scale, low cost soft engineered flood reduction schemes, designed to store/attenuate rapid runoff in small rural catchments. Design and implimentation of a network of 35 NWRM measures in a Northumberland catchment. To aid understanding of how features impact on downstream flood hazard. | Rural runoff attenuation in the Belford catchment, UK |
| A framework for managing runoff and pollution in the rural landscape using a Catchment Systems Engineering approach | Here a framework for applying a CSE approach to the catchment is shownin a step by step guide to implementing mitigation measures in the Belford Burn catchment. The framework is based around engagement with catchment stakeholders. | Rural runoff attenuation in the Belford catchment, UK |
| Belford catchment proactive flood soutions: storing and attenuating runoff on farms | This paper represents the hydrological charateristics of the catchment, the design of pilot ponds and initial results | Rural runoff attenuation in the Belford catchment, UK |
| Runoff management: Mitigation measures for disconnecting flow pathways in the Belford Burn catchmen to reduce flood Risk | This paper provides information on the NWRM features applied in the site | Rural runoff attenuation in the Belford catchment, UK |
| Runoff Attenuation Features - A guide for all those working in catchment Management | This is a guide to runoff attenuation features (technical issues, environmental considerations etc) based on the work carried out as part of the Belford Catchment Solutions Project. | Rural runoff attenuation in the Belford catchment, UK |
| Pilootprojecten Stroomgebied Voer | This presentation gives a short graphical overview of two executed NWRM's on the Horstergrub river less than one on the Belgian side of the border, one on the Dutch side of the border. The NWRM on the Belgian side of the border is the discussed NWRM. | Horstergrub sediment management, Belgium |
| Minimum Tillage Field Trials in Lower Austria | Project on several testing sides: application of directseeding, mulchseeding and conventional tillage. | No Tillage Field Trials in lower Austria |
| conserving soil treatment systems- trials in Lower Austria | Summary of several field trials in Lower Austria Comparison of conventional tillage, mulchseeding and no tillage regarding Mykotoxins, yield,erosion etc. |
No Tillage Field Trials in lower Austria |
| Telephone -Interview with PhD Josef Rosner | Telephone interview given by PhD Josef Rosner on Monday 28/04/2014 | No Tillage Field Trials in lower Austria |
| Economic aspects of mulch and direct seeding- reduction of soil treatment, which changes in the operational result have to be expected? | comparison of different soil treating systems (conventional tillage, mulchseeding and direct seeding). By reducing tillage savings are possible. This is shown for different crops. | No Tillage Field Trials in lower Austria |
| Soil management effects on runoff, erosion and soil properties in an olive grove of Southern Spain. | Rainfall, runoff and soil loss from 6 m × 12 m plots were recorded during 7 years (2000†“2006) in an experiment in which three different soil management systems were compared in a young olive grove installed on a heavy clay soil, near Cordoba, Southern Spain. No-tillage (NT) system, kept weed-free with herbicides, cover crop (CC) of barley, and conventional tillage (CT). | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Hydrological and erosive response of a small catchment under olivecultivation in a vertic soil during a five-year period: Implications forsustainability | Monitoring results during five hydrological years representative of the typical climate conditions in the region, in a commercial olive farm on a vertic soil with a soil management basedon limited tillage and growing of natural weed vegetation along the traffic lanes. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Application of the water erosion prediction project (WEPP) in olive orchards on Vertic soil with different management conditions | The WEPP model was evaluated using monthly runoff and erosion data collected from an experiment in an olive orchard on a Vertic soil during four hydrological years, comparing three different soil management systems: no tillage with bare soil (NT), conventional tillage (CT), and cover crop (CC). These three systems differed greatly in average annual runoff and soil losses. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Curve number values for olive orchards under different soil management | A physically based runoff model for olive orchards at a hillslope scale was used to generate rainfall†“runoff relationships for different scenarios of soil type (four), tree size (two), tree spacing (two), antecedent soil moisture (three), and soil management (11) for a 140-m-long and 5% steep hillslope. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| The influence of cover crops and tillage on water and sediment yield, and on nutrient, and organic matter losses in an olive orchard on a sandy loam soil | Rainfall, runoff, sediments, nutrient and organic carbon losses from 8 × 60 m plots were measured during four hydrological years (2002†“2007) in a field trial, in which two different soil management systems were used to confirm this hypothesis: a cover crop (CC), and conventional tillage (CT) near Seville, southern Spain. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Francia Martínez, J. R., Durán Zuazo, V. H., & Martínez Raya, A. (2006). Environmental impact from mountainous olive orchards under different soil-management systems (SE Spain). | Soil erosion, runoff and nutrient-loss patterns over a two-year period (1999-2000) were monitored in erosion plots on a mountainside with olive (Olea europaea cv. Picual) trees under three different types of soil management: (1) non-tillage with barley (Hordeum vulgare) strips of 4 m width (BS); (2) conventional tillage (CT); (3) non-tillage without plant strips (NT). The erosion plots, located in Lanjaron (Alpujarras) on the southern flank of the Sierra Nevada Mountains in south-eastern Spain, had 30% slope | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| The role of ancillary benefits on the value of agricultural soils carbon sequestration programmes: Evidence from a latent class approach to Andalusian olive groves. | The research assesses society's willingness to pay using a discrete choice analysis for a soil management programme in Andalusian olive groves identifying different groups based on preference heterogeneity. The results show that soil carbon sequestration in olive groves provides net social value and can be a cheap and cost-effective way of combating climate change. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Evaluating the demand for carbon sequestration in olive grove soils as a strategy toward mitigating climate change | Estimation of the economic value of carbon sequestration in olive grove soils derived from the implementation of different agricultural management systems. Carbon sequestration is considered jointly with other environmental co-benefits, such as enhanced erosion prevention and increased biodiversity. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Medidas beneficiosas para las aves ligadas a medios agrícola - Sugerencias para su diseño y aplicación en NATURA 2000, en el marco de la programación de desarrollo rural 2007-2013 | Para avanzar en la línea marcada por las directrices europeas de desarrollo rural respecto a la conservación de la biodiversidad, lo más idóneo hubiera sido establecer desde la base, en el Plan Estratégico nacional, los sistemas prioritarios para la conservación ligados a medios agrícolas en España, orientando la elaboración de los programas regionales de desarrollo rural, y garantizando así la preservación de estos agrosistemas en el conjunto del territorio. En opinión de SEO/BirdLife, en lo que se refiere a biodiversidad de la avifauna, estos sistemas prioritarios serían las zonas pseudoesteparias de agricultura de secano, los pastizales, las dehesas y los arrozales costeros. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| EU policies for olive farming. Unsustainable on all counts | Olive farming could be a model for sustainable land-use in the Mediterranean region, producing highly-valued foodstuffs and environmental benefits, while helping to maintain populations in marginal areas. | Cover Crops and No-Tillage in an Olive Grove (Andalusia, Spain) |
| Analysis of inadequate water quality of the Vonarje reservoir / Sutla Lake and the possibility of restoration and utilisation. | The model for the Sutla (Sotla) river and the Sutlansko Lake reservoir applies a life-cycle concept with the the DPSIR framework approach. | The Vonarje flood storage reservoir in Croatia |
| Komplex vízvisszatartási akcioprogram a NagyszéksosTo vízrendszerében | Enhancement of water supply of a former lake/wetland area to preserve ecologic circumstances. Redirection of surplus drainage water to the area and the creation of a sepatate wetland site to give extra cleaning to water received from the treated municipal wastewater treatement plan | Water supply and rehabilitation in Nagyszeksos-to Southern Hungary |
| A MÓRAHALMI NAGYSZÉKSÓS-TÓ VíZKÉMIAI VIZSGíLATAINAK ELEMZÉSE | Overview of the water quality monitoring results of the lake (HURO/0901/207/2.2.2 project) | Water supply and rehabilitation in Nagyszeksos-to Southern Hungary |
| A bivaly-rehabilitácios területek elemzése a Nagyszéksos-To és a Tanaszi-semlyék eltérÅ‘ biotopjain | Analysis of buffalo driven landscape rehabilitation projects | Water supply and rehabilitation in Nagyszeksos-to Southern Hungary |
| "After us, the desert and the deluge" | In a short period of 18 months the villages and towns involved in the Programme carried out about 80 thausand different water retention elments in degraded landscape. | Landscape revitalisation program in Slovakia |
| An integrated approach towards assessing the feasibility of domestic rainwater harvesting in Malta | This paper explores the potential of small scale domestic rainwater harvesting on the island of Malta by taking an integrated look at the physical, social, and economic environments. It explores the extent to which domestic rainwater harvesting has been forgotten despite the fact of it being embedded within Malta†™s history for centuries. The study closely examines the cost-effectiveness of this technology both at a local and national scale and teases out the hurdles that have brought about its rejection by means of residential and water professional interviews. | Domestic rainwater harvesting in Malta |
| Non Conventional Water Resources Programme in Malta (Alter Aqua) | The Maltese Islands have limited freshwater resources and depend heavily on desalination. Therefore there is an evident need to mobilise non conventional Water Resources (NCWR) in order to secure water availability and facilitate sustainable development. | Domestic rainwater harvesting in Malta |
| REVITALIZATION OF THE CLIMATE IN DRIED - OUT COMMUNITIES IN SLOVAKIA VIA HYDRO - CLIMATE RECOVERY | Recovery of the climate and landscape via integrated rainwater retention in the damaged parts of the country utilizing water retention measures (small dams, retention ponds, rainwater gardens, re-cultivated logging roads) | Recovery of dried out communities in Slovakia |
| Case study:The Holbina-Dunavat Restoration Project | Holbina-Dunavat area (S=5630 ha) has been studied from 1994 in order to establish a strategy for ecological restoration by a reintegration of the fish farm basins with the surrounding wetlands by opening the ring dikes around the basins. The positive effects are both ecological (wetland restoration, natural habitat and breeding area for fish and aquatic birds) and socio-economical (development of traditional activities, fishing, livestock and reed harvesting, creation of recreational areas for ecotourism) for the local people. | Holbina-Dunavat Restoration Project, Romania |
| The evolution process in Holbina-Dunavat area during restoration works | Mainly during the last decades of the 20th century, the Danube Delta has suffered from human interventions that led to dramatic changes in some areas. These interventions consisted in the dyking of large areas for the purpose of agricultural use, intensive fish-farming and forestry, which resulted in dramatic alterations or disturbances of the water balance. This again had effects on the alteration of natural processes, the ecological balance as well as the characteristic functions of wetlands and led to a deterioration or worse, the loss of area-specific habitats. When the transformation measures were stopped in early 1990, the dyked area covered 97.408 ha (22 %) of the total 482.592 ha. | Holbina-Dunavat Restoration Project, Romania |
| Reviving Water Wells and Ponds in Cross-Border Area | The project envisages the restoration and arrangement of 32 water wells and ponds as monuments of cultural heritage | Restoration of water wells in the Miren-Kostanjevica Municipality, Slovenia |
| Case study: Ecoremediation System (ERM) for treatment of polluted tributary of Glinscica, Slovenia | The innovative ecoremediation (ERM) system for treatment of the polluted tributary of GlinšÄica was therefore installed in 2006, the ERM system consists of the sedimentation pond for the deposition of coarse particles and reduction of current flow velocity, a vegetated ditch filled with different mixtures of sand, planted with common reed (Phragmites australis) for the aerobic) “ anaerobic treatment and a meandered revitalized stream bed of the tributary for the additional treatment. | Pollution Treatment on the Glinščica, Slovenia |
| Run-off treatment of highly fluctuating waters with subsurface vegetated drainage ditch and river bed with meanders | Current research suggests using vegetated drainage ditch as an additional practice in the mitigation of surface water pollution. The paper discusses the prototype of vegetated drainage system Glinscica (VDSG) composed of a vege-tated drainage ditch (VDD) and a new river bed with me-anders (RBM) | Pollution Treatment on the Glinščica, Slovenia |
| Vegetated ditches for treatment of surface water with highly fluctuating water regime | Vegetated drainage ditches (VDD) as a type of constructed wetland primarily serve to remove and store excess water associated with irrigation and storm events. Current research suggests using a VDD as an additional practice in the mitigation of surface water pollution. The VDD for water treatment of the Glinscica River was constructed in 2006. The efficiency of the system was evaluated in 2008 and 2009 regarding the reduction of SS, COD, BOD5, NH4-N, NO3-N, NO2-N, TN, ON and TP. The microbiological association developed in the VDD was analyzed with a focus on the identification and quantification of the narG gene as a denitrification indicator. This paper discusses the efficiency of pollution removal and the distribution of the narG gene within the VDD. The results showed that the highly fluctuating water regime was the main reason for the even distribution and abundance of the narG gene throughout the system, regardless of oxygen saturation or the nutrient status of the wastewater. With the exception of SS, pollutant concentrations met the permitted outflow levels. | Pollution Treatment on the Glinščica, Slovenia |
| NEW: final reports for Slowing the Flow at Pickering project | This webpage links to the phase 1 and phase 2 reports of the project. | Slowing the Flow at Pickering, UK |