3.2 Status of Europe’s floodplains: remaining areas and environmental quality

please provide general comments on section 3.2 here

  • romaocar (Carlos Romao) 09 Oct 2015 16:00:01

    maybe it would be useful to have a note on the geographical scope of this section: it refers to Europe's floodplains, but the content is limited to data and analysis of 9 countries?

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When assessing the status of Europe’s floodplains it is important to look at the location and remaining areas of floodplains, but at their functionality and at the quality of the ecosystem services they provide too.

  • Francine (invited by Wouter Vanneuville) 05 Oct 2015 15:20:58

    In Europe already up to 90 % of the former riparian floodplains have been lost during the last centuries or they are functionally no longer intact (Tockner, et al., 2009, 2002). In addition, only about 10% of the original amount of European floodplain forest remains, mostly in the larger river systems of Eastern Europe.  In recognition of this they have been placed on Annexe 1 of the European Habitats Directive  where they are collectively referred to as ‘Alluvial Forests’ (Hughes et al, 2012).  The main reason for the loss of active floodplains is the continued decline in floodplain area due to flood protections to prevent land uses not or less compatible with inundations (such as agriculture, or urban expansion), or infrastructure for hydropower development or maintenance of shipping channels (see section 3.3).

    Hughes, F.M.R.  del Tanago, M. G.  and Mountford, J.O. (2012) Restoring floodplain forests in Europe. In Stanturf, J., Madsen, P. and Lamb, D. (eds.) A Goal-Oriented Approach to Landscape Restoration. Springer-Verlag, pp.393-422.

  • schotkee (Kees Schotten) 09 Oct 2015 10:12:30

    Quality of ecosystem services – sounds strange even if I understand what the authors mean here. It suggests that there is  ‘bad’ and ‘good’ quality of a service. Change may be to ‘delivery of ecosystem services’? Please also check the use of quality and quantity as on page 28 you mention the ‘quantity of the service’. So is it quantity or quality or both?

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3.2.1        Today’s floodplains in Europe

In Europe already up to 90 % of the former riparian floodplains have been lost during the last centuries or they are functionally no longer intact (Tockner, et al., 2009, 2002). The main reason for the loss of active floodplains is the continued decline in floodplain area due to flood protections to prevent land uses not or less compatible with inundations (such as agriculture, or urban expansion), or infrastructure for hydropower development or maintenance of shipping channels (see section 3.3).

For example in Germany, where a national inventory accounted 70 to 90 % of floodplain area loss along 10 000 kilometres of 79 larger rivers and streams of 8 river basins (BMU and BfN 2009; Brunotte, et al., 2009). For the larger rivers, the loss is around 90 % of the 15 000 km² there once was, and in general only 1 % to 2 % of the former morphological floodplain is currently covered with near-nature floodplain forest (Brunotte, et al., 2009). For the different river sections of the Danube River the floodplain area loss varies between 73 and 95 %, where the Danube delta only lost around 30 % (Schneider, 2010; Schneider, et al., 2009). When including the tributaries, the floodplain loss can be estimated at 80 % (see table 3.1).

  • Jean-Marie Stam (invited by Wouter Vanneuville) 12 Oct 2015 15:09:25

    This whole section describes the floodplains lost  in a process over centuries, and in some cases more than a thousand years. It would not be realistic to want to restore this and we would suggest to add a sentence to that effect; e.g.: “It would not be feasible to return to a completely natural floodplain as was the case centuries ago.”

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Table 3.1        Examples for Floodplain area loss along large rivers in Europe

River section

Morphological floodplain area (km2)

Remaining floodplain area (km2)

Loss of floodplain area (%)

Upper Danube (a,b)

1 762

95

95

Central Danube (a)

8 161

2 002

75

Lower Danube (a)

8 173

2 193

73

Danube Delta (a)

5 402

3 799

30

Tisza (HU, RO, UA) (c)

36 000

1 800

95

Upper Rhine (FR, DE) (d)

 

 

93

River Rhine (A, CH, F, DE, NL) (d)

8 000

1 200

85

River Rhine (DE) (b)

2 064

454

80

Rhine and Meuse (NL) (e)

 

 

90 – 100

Seine (f)

 

 

99

Oder (PL, DE) (g)

3 593

970

73

Oder (only DE) (b)

941

94

90

Middle Ebro River (ES) (h)

 

 

58

Sources: (a) (Schneider, et al., 2009) (b) (Brunotte, et al., 2009) (c) (Haraszthy, 2001), (d) (Schmid-Breton, 2015) (e) personal communication Tom Buijse, Deltares (NL) (*) (f) (Tockner, et al., 2009),  (g) (WWF Germany 2000) (h) (Ollero, 2010)
(*) reference to be updated

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The remaining floodplains in Europe are very often far away from being functionally intact, and are faced by a multitude of hydraulic measures or separated from the riverbed by summer levees. Despite these alterations, the fragments of remaining floodplains are important areas for nature conservation: more than 30 % of all classified riparian zones are protected under EU law (Clerici, et al., 2013), i.e. are part of the Natura2000 network.

At the European scale no floodplain inventory or systematic assessment on floodplain status has so far been made. Floodplain loss and assessment of its quality is not registered or reported in a consistent way in the EU. With new spatial data reported under the European Floods Directive (EU 2007), combined with Corine Land Cover (CLC) data as well as information reported under the Habitats Directive (EU 1992), potentially new overviews will be possible but still these will have limitations (see subsection 3.2.2)

Where the German floodplain inventory (see Box 3.1) contains information of remaining and former floodplains of larger rivers, the Austrian (Lazowski, et al., 2014) and the Swiss (Hausammann, et al., 2005) inventories focus on the remaining high value areas. The latter contains a multitude of spatial, hydromorphologic, habitat and management information, including threats and pressures on the selected floodplain areas.

  • romaocar (Carlos Romao) 09 Oct 2015 15:48:38

    '30 % of all classified riparian zones' classified where, by what? Not clear what this 30 % correspond to...

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Box 3.1           German floodplain inventory and assessment

A first nationwide consistent and updatable inventory of the loss and quality status of German floodplains provides an efficient overview of the position, dimension and status of floodplains at larger rivers in Germany (Brunotte, et al., 2009). The survey of the floodplain areas was conducted for sections of the rivers with a catchment area of at least 1 000 km² and tidal waters were not included. The geomorphologic floodplain, consisting of the remaining active and former floodplains, which is defined in this case as the area which could be inundated, if there were no man-made dikes was assessed. For each 1-km section of the rivers, separately for the left and the right side, the active and former floodplain areas were mapped and land use cover in seven classes, nature conservation value, and protection status were documented

Based on a standardized approach (Koenzen, 2005) to define reference conditions for riverine landscapes (their potential natural status), the status of all mapped floodplains was assessed. Main input data for this assesment comprises the main factors of habitat quality for all species, including the geomorphologic and hydrologic habitat conditions, and land use.

As for the Water Framework Directive (EU 2000) the floodplain assessment methodology refers to a reference status (which is close to being unaffected by human intervention) and the results are  presented in five classes giving the degree of modification compared to the potentially natural status (table 3.2).

Floodplains of larger rivers in the past covered about 15 000 km², which corresponds to 4.4% of the German territory. Two-thirds of the morphological floodplain was lost by embanking. At large parts of rivers like Rhine, Elbe, Danube and Oder only 10-20 % of the former floodplains can still be inundated nowadays. More than one-third of the remaining active floodplains are intensively used as arable land use (28 %) or urban (6 %) areas and less than 10 % of the active floodplains fully provide their ecological functions. The remaining near-natural hardwood forests of floodplains cover only about 1 % of the active floodplain area. Compared to the potential natural status, less than 1% of the assessed active floodplain sections are classified as “nearly natural” (see figure 3.1), while 54 % of the floodplain sections are assessed as “severely modified” or “totally modified”. On the one hand, this situation resulted from the intense agricultural use on fertile soils of floodplains and on the other hand from the former importance of rivers as waterways for transport and trade as well as the arising urbanisation.

As expected, the classes severely modified and totally modified are more abundant (79 %) in the former floodplains compared to active floodplains (54%). However, there is a small percentage (4 %) of “slightly modified” former floodplain sections, which apparently still maintained a “floodplain- like” environment without being inundated for a longer period. Hence, these areas should be targeted for a potential restoration (activation) of former floodplains.

Source: (BMU et al., 2009), see http://www.geodienste.bfn.de/flussauen online

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Table 3.2        The five classes of floodplain status with a condensed specification

Class

Specification

1

nearly
natural

  • Floodplains not or to a very small degree disconnected from floods by river regulation and/or flood protection measures
  • Rivers only slightly regulated, with high flooding possibility
  • Mainly no or very low intensity land use, mostly forest, wetlands, and rarely grassland

2

slightly
modified

  • Floodplains to a small degree disconnected from floods by river development and/or flood protection measures
  • Rivers variably regulated, but usually with high flooding possibility
  • Mainly low intensity land use, mostly forest, wetlands and grassland

3

moderately modified

  • Floodplains partly disconnected from floods by river development and/or flood protection measures
  • Rivers generally regulated, but usually with flooding possibility
  • Variable intensity of land use

4

severely modified

  • Floodplains widely disconnected from floods by river development and/or flood protection measures
  • Rivers generally regulated, partly dammed
  • High intensity land use, mainly intensive agriculture and urban areas

5

totally
modified

  • Floodplains completely disconnected from floods by river development and/or flood protection measures
  • Rivers generally regulated heavily, frequently dammed
  • High intensity land use, mostly with high percentage of urban areas

Source: (Brunotte, et al., 2009)

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Figure 3.1: Comparison of the distribution of the floodplain status classes

Note: for all assessed sections of active floodplains (left) with former floodplain areas (right)

  • romaocar (Carlos Romao) 09 Oct 2015 15:51:33

    it should be clear that this refers to the German inventory

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3.2.2        Distribution of floodplain areas

To get an overview where active floodplains still occur, reported flood hazard and risk maps (FHRMs) (EU 2007, Art. 6)are used as proxies. The medium probability flood hazard maps, all with a likely return period of 100 years ([1]), for nine countries (see table 3.3) overall covers around 5% of the total area of these countries, with significant differences from country to country. Under 2% of the country territory for the Czech Republic, Austria and Slovenia up to over 10% for Romania, Italy and Hungary is mapped as being part of the medium probability flooded area. In Germany, more than 6 % is mapped as belonging to the flooded area of this scenario. This is slightly more than the national floodplain inventory but incudes more rivers. It should be noted that important floodplain areas along the Danube were not included in the FHRMs and that it was not always possible to clearly distinguish between river floodplains and coastal flood-prone areas.



[1] To be understood as an annual probability of occurrence of 1%

  • Clemens Neuhold (invited by Wouter Vanneuville) 13 Oct 2015 07:53:40

    From the Austrian point of view this table is misleading for 2 reasons (and therefore also the following assessments / tables made based on Table 3.3):

    1) FHRM areas for Austria represent < 3 % of the total river length in Austria (2.700 km out of 100.000 km)

    2) APSFR and, therefore, FHRM are focused on areas which are settled, retention areas are up- or downstream of these areas (in AT there are approx. 110 MIO m³ of artificial retention areas/basins, besides numerous natural inundation areas).

    Therefore, this table is not representative for AT to evaluate the distribution of floodplain areas .

    The footnote (a) "Danube floodplain is missing" is not correct, as there are also APSFRs along the Danube and, therefore, implicitly included in to the FHRM areas.

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Table 3.3        Medium scenario flood hazard maps for selected countries as a proxy for floodplain occurrence

country

FHRM Area [km2]

Flood hazard Area [%]

AT (a)

903

1.08

CZ

200

0.25

DE (b)

20 189

5.64

HR

3 929

6.94

HU

14 510

15.60

IT

36 540

12.15

PL (a) (b)

12 390

3.97

RO

25 424

10.67

SI (c)

352

1.74

(a) Danube floodplain is missing
(b)
Some flood hazard areas especially closely to the coastline close to the North Sea (DE) or Baltic Sea (DE, PL) are clearly prone to sea flooding
(c) Data obtained from national portal

Source: reporting obligation of flood hazard and risk maps for the Floods Directive (EU 2007), http://rod.eionet.europa.eu/obligations/602

  • vannewou (Wouter Vanneuville) 11 Sep 2015 11:57:16

    Unfortunately something went wrong with the table 3.3.

    The new values are:

    country

    FHRM Area Medium [km2]

    Flood hazard Area [%]

    comments

    AT

    903

    1.08

    no changes

    CZ

    1 671

    2.12

    topological errors resolved

    DE

    12 778

    3.57

    topological errors resolved, excluding low probability maps

    HR

    3 929

    6.94

    no changes

    HU

    6 218

    6.68

    excluding low probability maps

    IT

    28 121

    9.35

    excluding low probability maps

    PL

    11 974

    3.84

    minor changes

    RO

    14 362

    6,02

    excluding low probability maps

    SI

    352

    1,74

    no changes

  • romaocar (Carlos Romao) 09 Oct 2015 15:53:50

    the title of the table is somehow confusing since it refers to maps... or make the acronym in the table more explicit...

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The nine countries (see table 3.3) with spatial information on flooded areas available, consist of 4029 subcatchments (catchments with fourth Straler order CCM2/WS04 (JRC 2008)) with an average area of 383 km². Higher floodplain coverage (see Map 3.1) is significant for subcatchment for the Italian rivers Reno, Arno, Po, the Croatian parts of Sava and Drava rivers, the Tisza river in Hungary, the Elbe river in northern Germany and the Danube river in the eastern Romania.

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Map 3.1          Floodplain distribution

Note: Percentage of flood hazard area (medium probability) per subcatchment used as a proxy for floodplain coverage

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Land uses in floodplains

An intersection of the medium scenario flood hazard maps with the land uses types is shown in Figure 3.2. The 15 land use types are aggregated from the Corine Land Cover types on level 2 and3 (EC and EEA 1995), providing most detail on forest, semi-natural areas and wetland and being more aggregated for artificial surfaces ([2]). More than 40% of the floodplains are used for arable farming, being almost exclusively (over 99 %) non-irrigated. With 57 % (or 16 000 km2) the highest absolute coverage of arable land in floodplains of the nine selected countries can be found in Italy. The vast majority of these areas are located in northern Italy within the Po and Reno catchments (Map 3.1).

[2] Corine Land Cover 2006 seamless vector data, see http://www.eea.europa.eu/data-and-maps/data/clc-2006-vector-data-version-3 online

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Figure 3.2       Share of land use types in floodplains

Note: for nine countries: AT, CZ, DE, HR, HU, IT, PL RO and SI, see Table 3.3 with flooded areas under the medium scenario in the FHRMs as a proxy for floodplains.

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Pastures are covering almost 13.5 % of total floodplain area for all nine countries together. In Poland, pastures cover around one third of floodplains, making it the most present land use category in the floodplains for this country and with pastures equally distributed over Oder and Vistula catchments.

Forests cover around 9 %, where Croatia has the highest floodplain coverage with forests (nearly 30 %). Italy and Hungary only reach around 4 % of forest and all other countries in this exercise are close to the average of 10 % forest coverage.

Inland wetlands in floodplains reach in total about 4 % of the floodplain area, where Romania (with around 15%) reaches the highest cover for this land use category. Artificial areas, being mostly urban areas, cover around 6% of the assessed floodplains 6 % with large differences in between countries: from 25% in Austria and 14% in the Czech Republic to roughly 4% in Hungary and only 2% in Croatia.

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Box 3.2 River Mur recognised for effective river basin management

The River Mur flows from Austria, Slovenia, Hungary and Croatia before reaching the River Drava, a tributary of the Danube. The organisation managing the Mur Basin was awarded the second European River Prize during the 6th European River restoration conference (ERRC) in October 2014 (EEA 2014f).

Systematic river regulation since the late 19th Century has separated the river loops, branches and floodplain forests, which are important for the health of natural systems. Modifications including hydropower stations (in the upper part) and embankments have also degraded habitats. Nonetheless the Upper Mur is considered an ecologically valuable rivers in Europe, not least because it is the natural breeding site of the Danube salmon. It also has the second largest alluvial forest in Austria, one of Europe´s most species-rich habitats. The River Mur corridor in Slovenia is up to 1 km wide, and has a high variety of typical plant and animal communities ranging from pioneer to mature stages, including Pannonian–Dinaric and Pontic–Caspian elements, with large floodplain forests and side arm systems (Globevnik, and Mikoš, 2009).

Due to its high biotic diversity, a large part of the Mur corridor in Slovenia has been designated as a Natura 2000 site. The Natura-protected habitats are alluvial forests and hydrophilous tall herb fringe communities of floodplains. Nevertheless, ecological conditions for flood forest tree species in floodplains are deteriorating due to water shortage in oxbows, side arm channels and soils. The mouth of  the River Mur is one of the last remaining preserved system lowland rivers in Europe. Here both rivers, Drava and Mura are unregulated and continually create new habitats and restore existing which maintains high biological diversity.

River management on the Mur has largely focused on restoring old structures and recovering natural river habitats by reconnecting them with the dynamic river-system. Besides environmental benefits, these measures have other advantages including better passive flood protection and new natural recreation areas for the residents. Looking ahead, a section of the river will be designated where hydropower plants will be prohibited. Such measures show that management of the Mur is a good example of policy integration and stakeholder dialogue, two elements that are vitally important in successful river basin management.

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