https://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&feed=atom&action=historyCategory:Ecosystem Services - Revision history2024-03-29T10:49:21ZRevision history for this page on the wikiMediaWiki 1.23.5https://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=30256&oldid=prevClara at 09:13, 3 January 20192019-01-03T09:13:50Z<p></p>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as [[media: <del class="diffchange diffchange-inline">Deliverable2_3</del>.pdf | REFORM deliverable D2.3]].</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as [[media: <ins class="diffchange diffchange-inline">2.3_Analytical_framework_ecosystem_services</ins>.pdf | REFORM deliverable D2.3]].</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td></tr>
</table>Clarahttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=30248&oldid=prevClara at 13:31, 18 December 20182018-12-18T13:31:46Z<p></p>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|400px|Economic value Regge case]]</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|400px|<ins class="diffchange diffchange-inline">Figure 1: </ins>Economic value Regge case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td></tr>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value Vääräjoki case]]</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|<ins class="diffchange diffchange-inline">Figure 2: </ins>Economic value Vääräjoki case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td></tr>
</table>Clarahttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=30247&oldid=prevClara at 13:29, 18 December 20182018-12-18T13:29:25Z<p></p>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 13:29, 18 December 2018</td>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>==Valuing the ecosystem services provided by European river corridors – an analytical framework==</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>==Valuing the ecosystem services provided by European river corridors – an analytical framework==</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>A methodology is provided to first assess ecosystem services in biophysical terms and then value these in economic terms. The methodological framework <del class="diffchange diffchange-inline">Is </del>geared to allow a differentiation of restored and unrestored section of the river and its floodplain in Europe. It closely follows the CICES/MEA typology of ecosystem services focusing on final services that are of direct benefit to society. Underlying, supporting services are incorporated in these final services to which they contribute, sometimes in a convolute way. The methodology is designed and <del class="diffchange diffchange-inline">is currently being </del>tested for a range of specific cases selected in REFORM, notably the Regge (NL), Skjernaa (DK), Vääräjoki  (FIN), Narev (POL), Emaa (SWED), Drae and Enns (AU) and Thoess (CH). Below <del class="diffchange diffchange-inline">at </del>two cases are briefly presented.</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>A methodology is provided to first assess ecosystem services in biophysical terms and then value these in economic terms. The methodological framework <ins class="diffchange diffchange-inline">ss </ins>geared to allow a differentiation of restored and unrestored section of the river and its floodplain in Europe. It closely follows the CICES/MEA typology of ecosystem services focusing on final services that are of direct benefit to society. Underlying, supporting services are incorporated in these final services to which they contribute, sometimes in a convolute way. The methodology is designed and <ins class="diffchange diffchange-inline">has been </ins>tested for a range of specific cases selected in REFORM, notably the Regge (NL), Skjernaa (DK), Vääräjoki  (FIN), Narev (POL), Emaa (SWED), Drae and Enns (AU) and Thoess (CH). Below two cases are briefly presented.</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as <del class="diffchange diffchange-inline">deliverable 2.3 from the </del>[<del class="diffchange diffchange-inline">http</del>:<del class="diffchange diffchange-inline">//www</del>.<del class="diffchange diffchange-inline">reformrivers.eu/valuing-ecosystem-services-provided-european-river-corridors-%E2%80%93-analytical-framework </del>REFORM <del class="diffchange diffchange-inline">website under deliverables</del>].</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as [<ins class="diffchange diffchange-inline">[media</ins>: <ins class="diffchange diffchange-inline">Deliverable2_3</ins>.<ins class="diffchange diffchange-inline">pdf | </ins>REFORM <ins class="diffchange diffchange-inline">deliverable D2.3]</ins>].</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># The CICES/MEA typology of ecosystem services</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># The CICES/MEA typology of ecosystem services</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A breakdown of the river corridor into homogeneous landscape elements, or habitat units, adhering to the European, harmonised EUNIS/CORINE habitat classification.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A breakdown of the river corridor into homogeneous landscape elements, or habitat units, adhering to the European, harmonised EUNIS/CORINE habitat classification.</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div># A list of potential services provided by each habitat type, with an indicative potential range of the service delivered in biophysical terms (e.g kg/ha<del class="diffchange diffchange-inline">/</del>yr) and an approach to quantify these locally as fluxes in these same units.</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div># A list of potential services provided by each habitat type, with an indicative potential range of the service delivered in biophysical terms (e.g kg/<ins class="diffchange diffchange-inline">(</ins>ha<ins class="diffchange diffchange-inline">.</ins>yr) and an approach to quantify these locally as fluxes in these same units.</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A toolbox of economic valuation techniques to estimate monetary values for these fluxes.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A toolbox of economic valuation techniques to estimate monetary values for these fluxes.</div></td></tr>
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</table>Clarahttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28725&oldid=prevGertjan: /* Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). */2014-05-07T19:30:54Z<p><span dir="auto"><span class="autocomment">Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN).</span></span></p>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value <del class="diffchange diffchange-inline">Regge </del>case]]</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value <ins class="diffchange diffchange-inline">Vääräjoki </ins>case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td></tr>
</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28718&oldid=prevGertjan: /* Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). */2014-05-07T14:50:00Z<p><span dir="auto"><span class="autocomment">Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN).</span></span></p>
<table class='diff diff-contentalign-left'>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|400px|Economic value Regge case]]</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|400px|Economic value Regge case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><br /><ins class="diffchange diffchange-inline"><br /></ins></div></td></tr>
<tr><td colspan="2"> </td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div> </div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value Regge case]]</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value Regge case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td></tr>
</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28717&oldid=prevGertjan: /* Valuing the ecosystem services provided by European river corridors – an analytical framework */2014-05-07T14:49:22Z<p><span dir="auto"><span class="autocomment">Valuing the ecosystem services provided by European river corridors – an analytical framework</span></span></p>
<table class='diff diff-contentalign-left'>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 14:49, 7 May 2014</td>
</tr><tr><td colspan="2" class="diff-lineno">Line 5:</td>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as deliverable 2.3 from the [http://www.reformrivers.eu/valuing-ecosystem-services-provided-european-river-corridors-%E2%80%93-analytical-framework REFORM website under deliverables].</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The methodology can be downloaded as deliverable 2.3 from the [http://www.reformrivers.eu/valuing-ecosystem-services-provided-european-river-corridors-%E2%80%93-analytical-framework REFORM website under deliverables].</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /><br /></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del style="font-weight: bold; text-decoration: none;"></del></div></td><td colspan="2"> </td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The main components of the methodology are:</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># The CICES/MEA typology of ecosystem services</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># The CICES/MEA typology of ecosystem services</div></td></tr>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A list of potential services provided by each habitat type, with an indicative potential range of the service delivered in biophysical terms (e.g kg/ha/yr) and an approach to quantify these locally as fluxes in these same units.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A list of potential services provided by each habitat type, with an indicative potential range of the service delivered in biophysical terms (e.g kg/ha/yr) and an approach to quantify these locally as fluxes in these same units.</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A toolbox of economic valuation techniques to estimate monetary values for these fluxes.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div># A toolbox of economic valuation techniques to estimate monetary values for these fluxes.</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del class="diffchange diffchange-inline"><br /></del><br /></div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The report contains cross-links to the geomorphological river typology also carried out in WP2 of REFORM.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>The report contains cross-links to the geomorphological river typology also carried out in WP2 of REFORM.</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del class="diffchange diffchange-inline"><br /></del><br /></div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>{|</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>{|</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|-</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|-</div></td></tr>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|}</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|}</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td colspan="2"> </td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins style="font-weight: bold; text-decoration: none;"></ins></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td></tr>
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</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28716&oldid=prevGertjan at 14:47, 7 May 20142014-05-07T14:47:04Z<p></p>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 14:47, 7 May 2014</td>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>== Application of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|<del class="diffchange diffchange-inline">200px</del>|Economic value Regge case]]</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>[[Image:ES_Regge_economic_value.png|right|thumb|<ins class="diffchange diffchange-inline">400px</ins>|Economic value Regge case]]</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins class="diffchange diffchange-inline">[[Image:ES_vaarajoki_economic_value.png|right|thumb|400px|Economic value Regge case]]</ins></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del style="font-weight: bold; text-decoration: none;"></del></div></td><td colspan="2"> </td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del style="font-weight: bold; text-decoration: none;">[[Image:ES_vaarajoki_economic_value.png]]</del></div></td><td colspan="2"> </td></tr>
</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28715&oldid=prevGertjan at 14:45, 7 May 20142014-05-07T14:45:46Z<p></p>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">← Older revision</td>
<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 14:45, 7 May 2014</td>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|colspan="2"|Left:  Floodplain of the river Rhine near Wageningen (The Netherlands). Annual floodwater ensures considerable sediment and nutrient retention, offering natural fertility to the floodplain, and less nutrient enrichment downstream, which both can be important, valuable regulating ecosystem services. Right: Spring flooding in the Vääräjoki (Northern Finland).</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|colspan="2"|Left:  Floodplain of the river Rhine near Wageningen (The Netherlands). Annual floodwater ensures considerable sediment and nutrient retention, offering natural fertility to the floodplain, and less nutrient enrichment downstream, which both can be important, valuable regulating ecosystem services. Right: Spring flooding in the Vääräjoki (Northern Finland).</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|}</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>|}</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins class="diffchange diffchange-inline"><br /></ins></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>== <del class="diffchange diffchange-inline">Exploratory summary of the application </del>of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>== <ins class="diffchange diffchange-inline">Application </ins>of the method in two cases, the Regge (NL) and the Vaarajoki (FIN). ==</div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div> </div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins class="diffchange diffchange-inline"><br /></ins></div></td></tr>
<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del class="diffchange diffchange-inline">(For the underlying calculations, consult the first author</del>.<del class="diffchange diffchange-inline">)</del></div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins class="diffchange diffchange-inline">[[Image:ES_Regge_economic_value</ins>.<ins class="diffchange diffchange-inline">png|right|thumb|200px|Economic value Regge case]]</ins></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Regge case, the floodplain has been lowered , ponds have been created and the former meandering course has been re-installed over a considerable stretch, and this will be carried out along most of the length of the river. A restored section (Archemermaten, 105 ha) has been compared with a non-restored section (Dalmsholte, 50 ha), a bit further downstream. Restoration greatly increased the cultural value, mainly due to recreation (in 2012 over 11000 visitors rented kayaks, canoes and rafts) and appreciation of the enhanced scenic landscape (Fig. 1). Agricultural hay production was less in the restored section, whereas reduction of downstream flood risk was contributing substantially to an increased value of regulatory services. Also an increased aquifer infiltration of drinking water from the restored floodplain of the Regge added value.</div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div><br /></div></td></tr>
<tr><td colspan="2"> </td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins style="font-weight: bold; text-decoration: none;"></ins></div></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"></td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>In the Vääräjoki, restoration involved the return of large boulders into the streambed along 16 km of river and the application of some gravel beds. The restored reach was downstream of the non-restored reach. Here these returned boulders increased roughness of the streambed, which hampered drainage, raised the water level a bit, hence also affected upstream flooding of agricultural land during spring snow melt floods and summer floods. This reduced agricultural productivity as well as revenues a bit. The substantial willingness to pay of 29 euro per household per year for this increased esthetical aspect of the river was reduced to a minor fraction of the total value per ha because of a low population density. Total annual economic value (Fig. 2) as estimated from ecosystem services in this river is mainly due to arable crops in parts of the floodplain (15%, forest 50%), is comparatively low and restoration has slightly reduced this value.</div></td></tr>
<tr><td colspan="2"> </td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins style="font-weight: bold; text-decoration: none;"></ins></div></td></tr>
<tr><td colspan="2"> </td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div><ins style="font-weight: bold; text-decoration: none;">[[Image:ES_vaarajoki_economic_value.png]]</ins></div></td></tr>
</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28714&oldid=prevGertjan: /* Valuing the ecosystem services provided by European river corridors – an analytical framework */2014-05-07T14:31:59Z<p><span dir="auto"><span class="autocomment">Valuing the ecosystem services provided by European river corridors – an analytical framework</span></span></p>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 14:31, 7 May 2014</td>
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<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>| [[Image:ES_floodplain_wageningen.png|<del class="diffchange diffchange-inline">100px|frame|Wageningen</del>]]|| [[Image:ES_springflood_Vaarajoki.png|<del class="diffchange diffchange-inline">100px|frame|Vaarajoki</del>]]</div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>|[[Image:ES_floodplain_wageningen.png|<ins class="diffchange diffchange-inline">300px</ins>]]|| [[Image:ES_springflood_Vaarajoki.png|<ins class="diffchange diffchange-inline">300px</ins>]]</div></td></tr>
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<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div>|<del class="diffchange diffchange-inline">Caption</del></div></td><td class='diff-marker'>+</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #a3d3ff; vertical-align: top; white-space: pre-wrap;"><div>|<ins class="diffchange diffchange-inline">colspan="2"|Left:  Floodplain of the river Rhine near Wageningen (The Netherlands). Annual floodwater ensures considerable sediment and nutrient retention, offering natural fertility to the floodplain, and less nutrient enrichment downstream, which both can be important, valuable regulating ecosystem services. Right: Spring flooding in the Vääräjoki (Northern Finland).</ins></div></td></tr>
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</table>Gertjanhttps://wiki.reformrivers.eu/index.php?title=Category:Ecosystem_Services&diff=28713&oldid=prevGertjan at 14:29, 7 May 20142014-05-07T14:29:00Z<p></p>
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<td colspan='2' style="background-color: white; color:black; text-align: center;">← Older revision</td>
<td colspan='2' style="background-color: white; color:black; text-align: center;">Revision as of 14:29, 7 May 2014</td>
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<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>==Valuing the ecosystem services provided by European river corridors – an analytical framework==</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>==Valuing the ecosystem services provided by European river corridors – an analytical framework==</div></td></tr>
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<tr><td class='diff-marker'>−</td><td style="color:black; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #ffe49c; vertical-align: top; white-space: pre-wrap;"><div><del style="font-weight: bold; text-decoration: none;"></del></div></td><td colspan="2"> </td></tr>
<tr><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>A methodology is provided to first assess ecosystem services in biophysical terms and then value these in economic terms. The methodological framework Is geared to allow a differentiation of restored and unrestored section of the river and its floodplain in Europe. It closely follows the CICES/MEA typology of ecosystem services focusing on final services that are of direct benefit to society. Underlying, supporting services are incorporated in these final services to which they contribute, sometimes in a convolute way. The methodology is designed and is currently being tested for a range of specific cases selected in REFORM, notably the Regge (NL), Skjernaa (DK), Vääräjoki  (FIN), Narev (POL), Emaa (SWED), Drae and Enns (AU) and Thoess (CH). Below at two cases are briefly presented.</div></td><td class='diff-marker'> </td><td style="background-color: #f9f9f9; color: #333333; font-size: 88%; border-style: solid; border-width: 1px 1px 1px 4px; border-radius: 0.33em; border-color: #e6e6e6; vertical-align: top; white-space: pre-wrap;"><div>A methodology is provided to first assess ecosystem services in biophysical terms and then value these in economic terms. The methodological framework Is geared to allow a differentiation of restored and unrestored section of the river and its floodplain in Europe. It closely follows the CICES/MEA typology of ecosystem services focusing on final services that are of direct benefit to society. Underlying, supporting services are incorporated in these final services to which they contribute, sometimes in a convolute way. The methodology is designed and is currently being tested for a range of specific cases selected in REFORM, notably the Regge (NL), Skjernaa (DK), Vääräjoki  (FIN), Narev (POL), Emaa (SWED), Drae and Enns (AU) and Thoess (CH). Below at two cases are briefly presented.</div></td></tr>
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</table>Gertjan