All the hyetographs have been adapted to have the designed duration (5 h).

The economical, agricultural and societary transformations that over the last decades occurred in the Veneto floodplain have also brought changes in the way water is organized throughout the landscape. Water flow infrastructures have been progressively rearranged: some of them persisted, some were adapted, others were removed. In addition to having direct effects on the landscape arrangement in general, these changes also strongly affected the overall state of health of the drainage system itself. The magnitude of the changes learn more of the last fifty years is evident from the comparison of the patterns of the drainage systems of 1954, 1981 and 2006 (Fig. 9). At the beginning of the 1950s, the area was served by a network having a total length of about 72.7 km. This network decreased to 47.1 km in 1981, and 30.1 km in 2006. The average network drainage Hydroxychloroquine purchase density was about 30.7 km/km2 in 1954, 18.9 km/km2 in 1981 and 10.8 km/km2 in 2006. Considering the years 1954 and 1981, the main drainage structures remained fairly consistent, however the networks and field patches are relatively different. The ditches and channels between each field patch strongly shaped

the whole network system, and changes in the plot sizes determined the major changes in the network system. Other countries in Europe faced similar changes

during the BCKDHA years, with consequence on the flooding risk. For the UK agricultural landscape, for example, O’Connell et al. (2007) and Wheater and Evans, 2009 described how in the 1950s the British landscape was characterized by small fields with dense hedgerows and natural meandering rivers, but the subsequent drive for increased productivity in farming brought about major changes including the loss of ditches due to the increasing in field size. A similar condition can be found in Germany, where ditches built during the last 50 years have been progressively abandoned and eliminated because not always considered economical from an agricultural point of view (Krause et al., 2007). Moving from 1981 to 2006, we slowly assist to a more widespread urban development along the major roadways, with an increment of the urban areas. As a consequence, a bigger part of the ditches is modified into culverts, and others are dismissed in favor of urban areas, or because no longer needed. The network storage capacity is shown in Fig. 10. In 1954 the whole area had an average storage capacity of about 47.40 m3/ha, reaching a maximum value of about 130 m3/ha.