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  <front>
    <journal-meta><journal-id journal-id-type="publisher">HESS</journal-id><journal-title-group>
    <journal-title>Hydrology and Earth System Sciences</journal-title>
    <abbrev-journal-title abbrev-type="publisher">HESS</abbrev-journal-title><abbrev-journal-title abbrev-type="nlm-ta">Hydrol. Earth Syst. Sci.</abbrev-journal-title>
  </journal-title-group><issn pub-type="epub">1607-7938</issn><publisher>
    <publisher-name>Copernicus Publications</publisher-name>
    <publisher-loc>Göttingen, Germany</publisher-loc>
  </publisher></journal-meta>
    <article-meta>
      <article-id pub-id-type="doi">10.5194/hess-25-3071-2021</article-id><title-group><article-title>River runoff in Switzerland in a changing climate – <?xmltex \hack{\break}?> runoff regime changes and their time of emergence</article-title><alt-title>River runoff in Switzerland in a changing climate</alt-title>
      </title-group><?xmltex \runningtitle{River runoff in Switzerland in a changing climate}?><?xmltex \runningauthor{R.~Muelchi et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="yes" rid="aff1">
          <name><surname>Muelchi</surname><given-names>Regula</given-names></name>
          <email>regula.muelchi@giub.unibe.ch</email>
        <ext-link>https://orcid.org/0000-0002-7291-9775</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff3">
          <name><surname>Rössler</surname><given-names>Ole</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Schwanbeck</surname><given-names>Jan</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Weingartner</surname><given-names>Rolf</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Martius</surname><given-names>Olivia</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-8645-4702</ext-link></contrib>
        <aff id="aff1"><label>1</label><institution>Institute of Geography and Oeschger Centre for Climate Change Research, University of Bern, Bern, Switzerland</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>Mobiliar Lab for Natural Risks, University of Bern, Bern, Switzerland</institution>
        </aff>
        <aff id="aff3"><label>a</label><institution>now at: German Federal Institute of Hydrology (BfG), Koblenz, Germany</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Regula Muelchi (regula.muelchi@giub.unibe.ch)</corresp></author-notes><pub-date><day>8</day><month>June</month><year>2021</year></pub-date>
      
      <volume>25</volume>
      <issue>6</issue>
      <fpage>3071</fpage><lpage>3086</lpage>
      <history>
        <date date-type="received"><day>7</day><month>October</month><year>2020</year></date>
           <date date-type="rev-request"><day>19</day><month>October</month><year>2020</year></date>
           <date date-type="rev-recd"><day>6</day><month>May</month><year>2021</year></date>
           <date date-type="accepted"><day>7</day><month>May</month><year>2021</year></date>
      </history>
      <permissions>
        <copyright-statement>Copyright: © 2021 Regula Muelchi et al.</copyright-statement>
        <copyright-year>2021</copyright-year>
      <license license-type="open-access"><license-p>This work is licensed under the Creative Commons Attribution 4.0 International License. To view a copy of this licence, visit <ext-link ext-link-type="uri" xlink:href="https://creativecommons.org/licenses/by/4.0/">https://creativecommons.org/licenses/by/4.0/</ext-link></license-p></license></permissions><self-uri xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021.html">This article is available from https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021.html</self-uri><self-uri xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021.pdf">The full text article is available as a PDF file from https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021.pdf</self-uri>
      <abstract><title>Abstract</title>
    <p id="d1e133">Assessments of climate change impacts on runoff regimes are essential to climate change adaptation and mitigation planning. Changing runoff regimes and thus changing seasonal patterns of water availability strongly influence various economic sectors such as agriculture, energy production, and fishery and also affect river ecology. In this study, we use new transient hydrological scenarios driven by the most up-to-date local climate projections for Switzerland, the Swiss Climate Change Scenarios. These provide detailed information on changes in runoff regimes and their time of emergence for 93 rivers in Switzerland under three Representative Concentration Pathways (RCPs): RCP2.6, RCP4.5, and RCP8.5. These transient
scenarios also allow changes to be framed as a function of global mean
temperature.</p>
    <p id="d1e136">The new projections for seasonal runoff changes largely confirm the sign of
changes in runoff from previous hydrological scenarios with increasing winter runoff and decreasing summer and autumn runoff. Spring runoff is
projected to increase in high-elevation catchments and to decrease in
lower-lying catchments. Despite the increases in winter and some increases
in spring, the annual mean runoff is projected to decrease in most catchments. Compared to lower-lying catchments, runoff changes in high-elevation catchments (above 1500 m a.s.l.) are larger in winter,
spring, and summer due to the large influence of reduced snow accumulation
and earlier snowmelt and glacier melt. The changes in runoff and the
agreement between climate models on the sign of change both increase with
increasing global mean temperatures and higher-emission scenarios. This
amplification highlights the importance of climate change mitigation.</p>
    <?xmltex \hack{\newpage}?>
    <p id="d1e141">The time of emergence is the time when the climate signal emerges
significantly from natural variability. Under RCP8.5, times of emergence
were found early, before the period 2036–2065, in winter and summer for
catchments with mean altitudes above 1500 m a.s.l. Significant changes in
catchments below 1500 m a.s.l. emerge later in the century. Not all
catchments show significant changes in the distribution of seasonal means; thus, no time of emergence could be determined in these catchments.
Furthermore, the significant changes of seasonal mean runoff are not
persistent over time in some catchments due to nonlinear changes in runoff.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Introduction</title>
      <p id="d1e153">Anthropogenic climate change is certain to affect regional and local
hydrology (IPCC, 2013, 2014a, b). Major research efforts have enabled more precise and more reliable projections of regional and local temperature and precipitation changes (CH2018, 2018). The new Swiss Climate Change Scenarios (CH2018) are the result of a large modeling effort to downscale regional climate projections for Switzerland to local scales (CH2018, 2018). Warming in Switzerland is projected to be higher than the global mean warming. Without major mitigation efforts, mean temperatures are projected to increase by up to 6.8 <inline-formula><mml:math id="M1" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C by end of the 21st century in Switzerland (CH2018, 2018). This large increase in temperatures is accompanied by changes in many other hydrologically relevant variables such as precipitation amounts, precipitation type, and glacier volumes. The projected combination of increasing temperatures, changing precipitation<?pagebreak page3072?> patterns, retreating glaciers, and changes in snowpack will have a potentially strong impact on runoff regimes. Runoff regimes reflect the integral response in time and space of the hydrological conditions within a catchment and hence its water supply. Understanding and assessing changes in runoff regimes are crucial for many economic sectors, such as agriculture, fishery, hydropower generation, and tourism, and for the ecology within and around the rivers. Assessments of climate change impacts on river runoff are therefore particularly important for decision makers in adaptation planning and can also provide a basis for mitigation policies.</p>
      <p id="d1e165">Several studies on the impacts of climate change on hydrology in Switzerland
have been conducted in recent years. These have focused on changes in runoff
regimes (Horton et al., 2006; Köplin et al., 2012, 2014; Addor et al., 2014; Milano et al., 2015), on changes in low flows (Jenicek al., 2018; Brunner et al., 2019a, b), on changes in high flows (Keller et al., 2018; Brunner et al., 2019a), and on the effects of retreating glaciers for rivers (Huss et al., 2008, 2014; Farinotti et al., 2012; Finger et al., 2012; Fatichi et al., 2015; Etter et al., 2017). Studies on climate change impacts on various aspects of the hydrology in the Alpine area have also been carried out in Austria (e.g., Weber et al., 2010; Blöschl et al., 2011; Prasch et al., 2011; Tecklenburg et al., 2012; Goler et al., 2016; Wijngaard et al., 2016; Hanzer et al., 2018), in Italy (e.g., Groppelli et al., 2011), in Germany (e.g., Hattermann et al., 2015; Nilson et al., 2014), and in France (e.g., Ruiz-Villanueva et al., 2015; Vidal et al., 2016). Most of these studies are case studies or focus on specific aspects of hydrology.</p>
      <p id="d1e168">Previous studies have focused on changes in runoff regimes and included many catchments with diverse properties in Switzerland (Horton et al., 2006; Koeplin et al., 2012; Köplin et al., 2014; Addor et al., 2014). Köplin et al. (2012) found a shift in seasonality with increasing winter runoff, decreasing summer runoff, unchanging annual mean runoff for lower-lying catchments, and increasing annual mean runoff for high-Alpine catchments. However, these studies are based either on older climate model generations or on climate simulations downscaled with a delta change approach. The delta change method is based on climate simulations downscaled for 30-year periods both in the reference period and in future periods and does not provide continuous transient simulations for the whole 21st century. Therefore, this approach does not simulate daily to interannual variability (Bosshard et al., 2011). More sophisticated downscaling approaches have been developed, such as quantile mapping (Teutschbein and Seibert, 2012; Gudmundsson et al., 2012). They correct not only for the mean bias but also for the full distribution; they are applicable to long-term climate simulations and allow transient scenarios to be established. Using quantile mapping as a downscaling approach can intensify and increase the number of projected extremes (Rössler et al., 2019). Therefore, the present study uses the Hydro-CH2018-Runoff ensemble (dataset: Muelchi et al., 2020, 2021) run with the most up-to-date local climate change scenarios for Switzerland (CH2018). These scenarios used the quantile mapping approach to downscale the coarse climate model output. The Hydro-CH2018-Runoff ensemble includes transient daily simulations from 1981 to 2099 for 93 catchments in Switzerland and three Representative Concentration Pathways (RCPs): RCP2.6, RCP4.5, and RCP8.5. The new ensemble enables detailed quantification of changes in runoff regimes. In this study, we investigate changes in runoff regimes under a range of RCP scenarios. These 119-year continuous daily runoff simulations enable the estimation of the time of emergence (Giorgi and Bi, 2009; Leng et al., 2016) of those changes. The time of emergence is the time when the climate signal emerges significantly from natural variability. It is of particular importance to the question of how much time is left for adaptation planning. In this study, we analyze not only the time of emergence but also the evolution of time of emergence over time. Moreover, the ensemble allows for the quantification of changes at different global warming levels; these warming levels are particularly relevant for policymakers (e.g., James et al., 2017). The framing of the results as a function of global mean temperature change rather than time enables a direct link to the Paris Agreement target and indicates the changes to be expected in a
<inline-formula><mml:math id="M2" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M3" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C world and the consequences of missing this target. In this
study, we assess changes for global warming levels of <inline-formula><mml:math id="M4" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M5" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M6" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M7" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p>
</sec>
<sec id="Ch1.S2">
  <label>2</label><title>Data</title>
      <p id="d1e238">For this study, we use the Hydro-CH2018-Runoff ensemble of daily discharge
simulations for 93 medium-sized (catchment size between 14–1700 km<inline-formula><mml:math id="M8" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula>)
catchments in Switzerland (Fig. 1; Muelchi et al., 2020, 2021). The Precipitation-Runoff-Evapotranspiration HRU-related Model (PREVAH) hydrological modeling system (Viviroli et al., 2009) was used for simulating the hydrological response to the climate change scenarios. PREVAH is a semidistributed model based on hydrological response units and includes submodules to account for important hydrological processes related to snow,
glacier, and soil moisture dynamics and evapotranspiration. PREVAH was
calibrated and validated for each catchment (for more details, see Muelchi
et al., 2021). The calibrated parameters were kept constant for the simulation of runoff under climate change, and land use was held unchanged
for nonglaciated catchments. The minor impact of land use changes on changes
in the runoff regime for Switzerland was assessed by Köplin et al. (2014). For glaciated catchments, glacier extents were updated every 5 years according to the glacier projections by Zekollari et al. (2019), which are based on the same climatic dataset. The land use of areas from which glaciers disappear was replaced by rock for areas above 3000 m a.s.l. and by bare soil for areas below 3000 m a.s.l.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F1" specific-use="star"><?xmltex \currentcnt{1}?><?xmltex \def\figurename{Figure}?><label>Figure 1</label><caption><p id="d1e252">Overview of the study region and the location of the gauging stations in Switzerland. Shading indicates the mean elevation of the respective catchment. Red contours indicate the six example catchments:
Rosegbach–Pontresina (1), Kander–Hondrich (2), Plessur–Chur (3),
Emme–Emmenmatt (4), Venoge–Ecublens (5), and Verzasca–Lavertezzo (6).</p></caption>
        <?xmltex \igopts{width=398.338583pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f01.png"/>

      </fig>

      <?pagebreak page3073?><p id="d1e261"><?xmltex \hack{\newpage}?>The meteorological input used for the simulations comes from the latest Swiss
Climate Change Scenarios CH2018 (CH2018, 2018). The CH2018 scenarios used
EURO-CORDEX simulations (Jacob et al., 2014; Kotlarski et al., 2014) and
applied statistical downscaling (quantile mapping; Teutschbein and Seibert,
2012; Gudmundsson et al., 2012) on chains of global circulation models and
regional climate models (GCM–RCM chains). The results consist of gridded
high-resolution (<inline-formula><mml:math id="M9" display="inline"><mml:mrow><mml:mn mathvariant="normal">2</mml:mn><mml:mrow class="unit"><mml:mspace linebreak="nobreak" width="0.125em"/><mml:mi mathvariant="normal">km</mml:mi></mml:mrow><mml:mo>×</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> km) daily temperature and precipitation data for Switzerland for the period 1981–2099. This dataset was then used to drive the hydrological model, resulting in the Hydro-CH2018-Runoff ensemble, which comprises daily runoff time series for 1981–2099 for each of the GCM–RCM chains. The Hydro-CH2018-Runoff ensemble contains simulations for three RCPs: 8 simulations under RCP2.6, 16 simulations under RCP4.5, and 20 simulations under RCP8.5. The GCM–RCM chains and their underlying emission scenarios used for this study are listed in Table 1. The Hydro-CH2018-Runoff ensemble comprises transient long-term daily runoff projections for Switzerland for the period 1981–2099. These transient simulations incorporate the daily to interannual climate variability. Changes in runoff constrained by the different warming levels were analyzed using the global mean temperatures of the driving GCMs (CMIP5; Taylor et al., 2012).</p>

<?xmltex \floatpos{t}?><table-wrap id="Ch1.T1" specific-use="star"><?xmltex \currentcnt{1}?><label>Table 1</label><caption><p id="d1e285">List of GCM–RCM chains used, their initial resolution, and the RCP
available.</p></caption><oasis:table frame="topbot"><?xmltex \begin{scaleboxenv}{.97}[.97]?><oasis:tgroup cols="10">
     <oasis:colspec colnum="1" colname="col1" align="left"/>
     <oasis:colspec colnum="2" colname="col2" align="left"/>
     <oasis:colspec colnum="3" colname="col3" align="center"/>
     <oasis:colspec colnum="4" colname="col4" align="center"/>
     <oasis:colspec colnum="5" colname="col5" align="left"/>
     <oasis:colspec colnum="6" colname="col6" align="center"/>
     <oasis:colspec colnum="7" colname="col7" align="center"/>
     <oasis:colspec colnum="8" colname="col8" align="left"/>
     <oasis:colspec colnum="9" colname="col9" align="center"/>
     <oasis:colspec colnum="10" colname="col10" align="center"/>
     <oasis:thead>
       <oasis:row>

         <oasis:entry colname="col1">GCM</oasis:entry>

         <oasis:entry colname="col2">RCM</oasis:entry>

         <oasis:entry rowsep="1" namest="col3" nameend="col4">RCP8.5 </oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry rowsep="1" namest="col6" nameend="col7">RCP4.5 </oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry rowsep="1" namest="col9" nameend="col10">RCP2.6 </oasis:entry>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col1"/>

         <oasis:entry colname="col2"/>

         <oasis:entry colname="col3">EUR-11</oasis:entry>

         <oasis:entry colname="col4">EUR-44</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">EUR-11</oasis:entry>

         <oasis:entry colname="col7">EUR-44</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9">EUR-11</oasis:entry>

         <oasis:entry colname="col10">EUR-44</oasis:entry>

       </oasis:row>
     </oasis:thead>
     <oasis:tbody>
       <oasis:row>

         <oasis:entry rowsep="1" colname="col1" morerows="4">ICHEC-EC-EARTH</oasis:entry>

         <oasis:entry colname="col2">KNMI-RACMO22E</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col2">DMI-HIRMAM5</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

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         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col2">CLMcom-CCLM4-8-17</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

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         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row rowsep="1">

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         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9">X</oasis:entry>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry rowsep="1" colname="col1" morerows="3">MOHC-HadGEM2-ES</oasis:entry>

         <oasis:entry colname="col2">CLMcom-CCLM4-8-17</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col2">CLMcom-CCLM5-0-6</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col2">KNMI-RACMO22E</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

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         <oasis:entry colname="col10">X</oasis:entry>

       </oasis:row>
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         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10">X</oasis:entry>

       </oasis:row>
       <oasis:row>

         <oasis:entry rowsep="1" colname="col1" morerows="3">MPI-M-MPI-ESM-LR</oasis:entry>

         <oasis:entry colname="col2">CLMcom-CCLM4-8-17</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
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         <oasis:entry colname="col2">CLMcom-CCLM5-0-6</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10">X</oasis:entry>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col2">MPI-CSC-REMO2009-2</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9">X</oasis:entry>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row>

         <oasis:entry rowsep="1" colname="col1" morerows="1">MIROC-MIROC5</oasis:entry>

         <oasis:entry colname="col2">CLMcom-CCLM5-0-6</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10">X</oasis:entry>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col1">CCCma-CanESM2</oasis:entry>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col1">CSIRO-QCCCE-CSIRO-Mk3-6-0</oasis:entry>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col1">IPSL-IPSL-CM5A-MR</oasis:entry>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3">X</oasis:entry>

         <oasis:entry colname="col4"/>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6">X</oasis:entry>

         <oasis:entry colname="col7"/>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
       <oasis:row rowsep="1">

         <oasis:entry colname="col1">NCC-NorESM1-M</oasis:entry>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10">X</oasis:entry>

       </oasis:row>
       <oasis:row>

         <oasis:entry colname="col1">NOAA-GFDL-GFDL-ESM2M</oasis:entry>

         <oasis:entry colname="col2">SMHI-RCA4</oasis:entry>

         <oasis:entry colname="col3"/>

         <oasis:entry colname="col4">X</oasis:entry>

         <oasis:entry colname="col5"/>

         <oasis:entry colname="col6"/>

         <oasis:entry colname="col7">X</oasis:entry>

         <oasis:entry colname="col8"/>

         <oasis:entry colname="col9"/>

         <oasis:entry colname="col10"/>

       </oasis:row>
     </oasis:tbody>
   </oasis:tgroup><?xmltex \end{scaleboxenv}?></oasis:table></table-wrap>

</sec>
<sec id="Ch1.S3">
  <label>3</label><title>Methods</title>
<sec id="Ch1.S3.SS1">
  <label>3.1</label><title>Study area</title>
      <p id="d1e923">The study area consists of 93 catchments distributed over Switzerland (Fig. 1) and covering a wide range of catchment characteristics with an average catchment size of 314 km<inline-formula><mml:math id="M10" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> (from 14 to 1700 km<inline-formula><mml:math id="M11" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula>) and a
mean altitude of 1344 m a.s.l. (range in mean altitude: 476–2700 m a.s.l.). Of the 93 catchments, 22 are glaciated with a modeled degree of glaciation varying between 1 % and 29 % (Fig. S1 in the Supplement). The present runoff regimes range from glacier-fed catchments in high-Alpine areas, mainly snow-driven catchments (mean altitude above 1550 m a.s.l.) in the Alps and pre-Alps, to rain-fed catchments predominant in the Swiss Plateau and at lower elevations in the southern part of Switzerland. Six catchments (highlighted in Fig. 1) are used as example catchments representing typical runoff regimes: Rosegbach, highly glaciated (29 %); Kander, slightly glaciated (5 %); Plessur, high-Alpine snow influenced; Emme, pre-Alpine rain and snow influenced; Venoge, lowland rain dominated; and Verzasca, southern Alpine rain and snow dominated. An overview of the catchment characteristics (Table S1 in the Supplement), the degree of glaciation (Fig. S1), and the fraction of precipitation falling as snow (Fig. S2) can be found in the Supplement.</p>
</sec>
<sec id="Ch1.S3.SS2">
  <label>3.2</label><title>Determining changes in seasonal and annual mean runoff</title>
      <p id="d1e952">The simulations were analyzed using annual and seasonal changes of runoff under the three RCPs. The seasons were defined as winter (December–February), spring (March–May), summer (June–August), and
autumn (September–November). All changes were specified for 30-year periods to remove interannual variability. The reference period covers the years 1981–2010 and was compared with the far future period 2070–2099. The median among all simulations within an RCP pathway was considered the best estimate. To obtain an indication of the robustness of the estimation, the changes were highlighted when at least 90 % of the simulations showed the same direction of change, whether<?pagebreak page3074?> positive or negative. This criterion corresponds to “very likely” in the terminology of the Intergovernmental Panel on Climate Change (IPCC) that the runoff changes are either positive or negative (Mastrandrea et al., 2010). The changes in seasonal and annual runoff were also analyzed as a function of the mean elevation of the catchments to show the elevation dependence of runoff responses. Other elevation-related characteristics of a catchment might have been used. However, a study by Köplin et al. (2012) showed that catchment responses to climate change in Switzerland can be directly linked to mean altitude.</p>
      <p id="d1e955">For the analysis of changes in the runoff regime, monthly means for 30-year
periods were calculated with the median representing the best estimate and with the uncertainty band showing the full range among all models within an RCP.
To simplify the interpretation of the results, this article focuses only on
changes up to the period 2070–2099 under RCP8.5 and RCP2.6. These two emission scenarios provide the broadest range of changes available from the
full Hydro-CH2018-Runoff ensemble. Results for the near-future period of 2045–2074 and for RCP4.5 can be found in the Supplement.</p>
</sec>
<sec id="Ch1.S3.SS3">
  <label>3.3</label><title>Determination of the time of emergence of seasonal and annual runoff changes</title>
      <p id="d1e966">The time of emergence (Giorgi and Bi, 2009; Leng et al., 2016) indicates the
time when significant changes in the distribution of seasonal and annual
means emerge from natural variability. The Kolmogorov–Smirnov test was used
to test whether two 30-year samples of seasonal or annual means are drawn
from the same distribution. This test was conducted on the distributions of
moving 30-year windows and the distribution of the reference period. The
Kolmogorov–Smirnov test procedure was also used in previous studies (e.g.,
for precipitation Mahlstein et al., 2011; Gaetani et al., 2020), but other
definitions of time of emergence also exist. Although Mahlstein et al. (2011) did not find significant differences from other definitions, Gaetani et al. (2020) found that the Kolmogorov–Smirnov testing procedure results in a more robust and earlier time of emergence. The testing was performed for each simulation under RCP8.5 and each catchment separately. Constraining the analysis to the RCP8.5 ensemble was motivated by the sufficiently large
number of simulations, 20, within the ensemble. The time of emergence was
then defined by following the procedure used in Mahlstein et al. (2011) and refers to the last year of the 30-year moving window in which the Kolmogorov–Smirnov test was rejected for the first time at 95 %<?pagebreak page3075?> significance. We then considered the significance of changes in the seasonal
and annual mean when at least 66 % of the models detect a significant change in the same 30-year window. Sixty-six percent corresponds to the
threshold referred to as “likely” in the IPCC terminology (Mastrandrea et
al., 2010). Because changes in runoff may not be linear over time, the time
of emergence may not be stable after the first detection. Even though changes in seasonal and annual runoff are tested as significant in one period, they may not be significant in all subsequent periods (e.g., due to nonlinear effects in snowmelt or glacier melt contributions). Therefore, we also analyzed the temporal evolution of rejections of the null hypothesis for the Kolmogorov–Smirnov test (<inline-formula><mml:math id="M12" display="inline"><mml:mi>p</mml:mi></mml:math></inline-formula> values smaller than 0.05).</p>
</sec>
<sec id="Ch1.S3.SS4">
  <label>3.4</label><title>Stratification of seasonal and annual runoff changes by increases in global mean temperature</title>
      <p id="d1e984">For the analysis of runoff changes as a function of global mean temperature
change, temperature targets were defined at <inline-formula><mml:math id="M13" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M14" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M15" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M16" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C with respect to the preindustrial state. Because the temperature targets are defined with respect to the preindustrial state, the warming observed between the preindustrial state (1864–1900) and the reference period (1981–2010) was subtracted from the temperature targets. The observed warming is estimated to be 0.6 <inline-formula><mml:math id="M17" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C; thus, the remaining global warming for the 1.5, 2, and 3 <inline-formula><mml:math id="M18" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C temperature targets is 0.9, 1.4, and 2.4 <inline-formula><mml:math id="M19" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, respectively (Morice et al., 2012;
for technical details, see CH2018, 2018). For each of the driving GCMs used in
the Hydro-CH2018-Runoff ensemble for RCP8.5, we computed differences in moving 30-year averages of global mean temperatures compared to the reference period. The 30-year windows when global mean temperature change exceeds <inline-formula><mml:math id="M20" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.9</mml:mn></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M21" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.4</mml:mn></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M22" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2.4</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M23" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C were selected for each GCM. Subsequently, the seasonal and annual changes in runoff were extracted for each of the time periods and the driving GCM in the GCM–RCM combination. Again, catchments with robust signs were highlighted if at least 90 % of simulations agreed on the direction of change.</p>
</sec>
</sec>
<sec id="Ch1.S4">
  <label>4</label><title>Results</title>
<sec id="Ch1.S4.SS1">
  <label>4.1</label><title>Changes in seasonal and annual mean runoff for Switzerland</title>
      <p id="d1e1109">Changes in the multimodel median of seasonal and annual mean runoff by end
of the century (2070–2099) are shown in Fig. 2 for RCP8.5 and in Fig. 3 for
RCP2.6 (see Fig. S3 for RCP4.5 and Figs. S4–S6 for the period 2045–2074).
Highlighted catchments show changes where at least 90 % of the models agree on the sign of change.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F2" specific-use="star"><?xmltex \currentcnt{2}?><?xmltex \def\figurename{Figure}?><label>Figure 2</label><caption><p id="d1e1114">Multimodel median of seasonal and annual mean changes of runoff
under RCP8.5 by 2070–2099 for winter <bold>(a)</bold>, spring <bold>(b)</bold>, summer <bold>(c)</bold>, autumn <bold>(d)</bold>, and annual means <bold>(e)</bold>. Black circles indicate catchments whose direction of change agrees across at least 90 % of the models.</p></caption>
          <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f02.png"/>

        </fig>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3" specific-use="star"><?xmltex \currentcnt{3}?><?xmltex \def\figurename{Figure}?><label>Figure 3</label><caption><p id="d1e1140">Equivalent to Fig. 2 but with projections for RCP2.6.</p></caption>
          <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f03.png"/>

        </fig>

<?xmltex \hack{\newpage}?>
<sec id="Ch1.S4.SS1.SSS1">
  <label>4.1.1</label><title>Changes in winter runoff for Switzerland</title>
      <p id="d1e1159">In winter, all catchments show positive mean runoff changes under RCP8.5 by
the end of the century (Fig. 2a) compared to the reference period. The mean
runoff changes range from <inline-formula><mml:math id="M24" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M25" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">221</mml:mn></mml:mrow></mml:math></inline-formula> % with larger changes in
higher-elevation catchments. The mean change among all catchments is
<inline-formula><mml:math id="M26" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">48</mml:mn></mml:mrow></mml:math></inline-formula> %. In all, 84 out of 93 catchments show good agreement (<inline-formula><mml:math id="M27" display="inline"><mml:mrow><mml:mi mathvariant="italic">&gt;=</mml:mi><mml:mn mathvariant="normal">90</mml:mn></mml:mrow></mml:math></inline-formula> %) on the sign of change. Under RCP2.6, 87 out of 93 catchments show positive changes, with mean runoff changes across all catchments of <inline-formula><mml:math id="M28" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">13</mml:mn></mml:mrow></mml:math></inline-formula> % (Fig. 3a). However, only 41 catchments show robust model agreement on the sign of change. The range among the catchments is between <inline-formula><mml:math id="M29" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> % and
<inline-formula><mml:math id="M30" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">58</mml:mn></mml:mrow></mml:math></inline-formula> %, again with stronger changes in the mountainous areas.</p>
</sec>
<sec id="Ch1.S4.SS1.SSS2">
  <label>4.1.2</label><title>Changes in spring runoff for Switzerland</title>
      <p id="d1e1241">In spring, both positive and negative changes are found in mean runoff (Figs. 2b and 3b). The mean change across all catchments is <inline-formula><mml:math id="M31" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">9</mml:mn></mml:mrow></mml:math></inline-formula> % under
RCP8.5 (Fig. 2b). Although most of the lower catchments show a decrease in
runoff (up to <inline-formula><mml:math id="M32" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">21</mml:mn></mml:mrow></mml:math></inline-formula> %), the higher-elevation catchments exhibit an increase
(up to <inline-formula><mml:math id="M33" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">166</mml:mn></mml:mrow></mml:math></inline-formula> %) under RCP8.5. The strong increase in spring runoff is
mainly found in the highest-elevation catchments (Fig. 2b), where snowmelt
is increased due to higher temperatures that shift the snowmelt season from
early summer to spring. However, only 34 out of 93 catchments exhibit robust
changes across the climate models. Compared to the high-emission scenario,
the changes in the low-emission scenario (RCP2.6) tend to be more moderate
(Fig. 3b). Under RCP2.6, the changes range from <inline-formula><mml:math id="M34" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">15</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M35" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">70</mml:mn></mml:mrow></mml:math></inline-formula> % with a
slightly positive mean (<inline-formula><mml:math id="M36" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> %) across all catchments. Fifty-eight catchments show
robust changes in spring mean runoff under RCP2.6. Some catchments show
negative changes under RCP2.6 but positive changes under RCP8.5. This transition from negative to positive changes is also found in RCP4.5 (Fig. S3).</p>
</sec>
<sec id="Ch1.S4.SS1.SSS3">
  <label>4.1.3</label><title>Changes in summer runoff for Switzerland</title>
      <p id="d1e1313">In summer and under RCP8.5, all catchments show a decrease in mean runoff,
ranging from <inline-formula><mml:math id="M37" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">16</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M38" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">59</mml:mn></mml:mrow></mml:math></inline-formula> % with mean change of <inline-formula><mml:math id="M39" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">35</mml:mn></mml:mrow></mml:math></inline-formula> % across all
catchments (Fig. 2c). Again, more pronounced negative changes are found in
higher-elevation catchments, where summer runoff is projected to decrease by
up to half of the runoff of the reference period. All catchments except one
agree on the sign of change among the climate models. Under RCP2.6, the signs and magnitude of the changes are less clear (Fig. 3c). The average change across all catchments is negative (<inline-formula><mml:math id="M40" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">6</mml:mn></mml:mrow></mml:math></inline-formula>%), but mean runoff change ranges from <inline-formula><mml:math id="M41" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">26</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M42" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> %. Just 9 catchments show positive but non-robust mean runoff changes in summer, whereas 34 catchments yield robust negative signs.</p><?xmltex \hack{\newpage}?>
</sec>
<?pagebreak page3076?><sec id="Ch1.S4.SS1.SSS4">
  <label>4.1.4</label><title>Changes in autumn runoff for Switzerland</title>
      <p id="d1e1386">In autumn, all catchments but one show decreasing runoff under RCP8.5 (Fig. 2d). Changes range from <inline-formula><mml:math id="M43" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">36</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M44" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> % with an average change of
<inline-formula><mml:math id="M45" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">19</mml:mn></mml:mrow></mml:math></inline-formula> % across all catchments. More than 50 % of the catchments reveal
robust changes. In contrast to the changes in summer, the autumn runoff
tends to decrease more strongly in the lower-lying catchments than in the
higher-elevation catchments. Under RCP2.6, the changes are much smaller than
under RCP8.5, with an average change of <inline-formula><mml:math id="M46" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">5</mml:mn></mml:mrow></mml:math></inline-formula> % (ranging from <inline-formula><mml:math id="M47" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">20</mml:mn></mml:mrow></mml:math></inline-formula> % to
<inline-formula><mml:math id="M48" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:math></inline-formula> %; Fig. 3d). The changes are also less robust, with only 17 catchments showing good agreement on the sign of change.</p>
</sec>
<sec id="Ch1.S4.SS1.SSS5">
  <label>4.1.5</label><title>Changes in annual runoff for Switzerland</title>
      <p id="d1e1458">Despite the increases in winter and partial increases in spring, the annual
runoff is projected to decrease by 8 % (range: <inline-formula><mml:math id="M49" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">23</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M50" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> %) under
RCP8.5 (Fig. 2e) and by 2 % (range: <inline-formula><mml:math id="M51" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">13</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M52" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">11</mml:mn></mml:mrow></mml:math></inline-formula> %) under RCP2.6
(Fig. 3e) on average. Whereas 82 out of 93 catchments show negative changes
under RCP8.5, only 65 catchments exhibit negative changes under RCP2.6. However, the robustness of the sign of change in the annual mean runoff is
weaker than that of the seasonal mean changes.</p>
</sec>
<sec id="Ch1.S4.SS1.SSS6">
  <label>4.1.6</label><title>Elevation dependence of mean seasonal and annual changes in runoff</title>
      <?pagebreak page3077?><p id="d1e1509">Considering the results above, changes in seasonal and annual mean runoff
are heavily dependent on the mean elevation of the catchment. This dependence is highlighted in Fig. 4, where changes in runoff are plotted against mean altitude of the catchments. The higher-elevation catchments generally show larger changes in winter, spring, and summer than the lower-elevation catchments. For autumn and annual runoff, no distinct pattern can be seen. Under RCP8.5 and for catchments with mean altitude below 1500 m a.s.l., the average change is <inline-formula><mml:math id="M53" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">27</mml:mn></mml:mrow></mml:math></inline-formula> % in winter, <inline-formula><mml:math id="M54" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">5</mml:mn></mml:mrow></mml:math></inline-formula> % in spring, <inline-formula><mml:math id="M55" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">31</mml:mn></mml:mrow></mml:math></inline-formula> % in summer, <inline-formula><mml:math id="M56" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">21</mml:mn></mml:mrow></mml:math></inline-formula> % in autumn, and <inline-formula><mml:math id="M57" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">8</mml:mn></mml:mrow></mml:math></inline-formula> % in the annual mean (Fig. 4a). For
catchments with mean elevation above 1500 m a.s.l., runoff changes on average by <inline-formula><mml:math id="M58" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">77</mml:mn></mml:mrow></mml:math></inline-formula> % in winter, by <inline-formula><mml:math id="M59" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">28</mml:mn></mml:mrow></mml:math></inline-formula> % in spring, by <inline-formula><mml:math id="M60" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">41</mml:mn></mml:mrow></mml:math></inline-formula> % in summer, by <inline-formula><mml:math id="M61" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">15</mml:mn></mml:mrow></mml:math></inline-formula> % in autumn, and by <inline-formula><mml:math id="M62" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">9</mml:mn></mml:mrow></mml:math></inline-formula> % in the annual mean. However, the changes in the higher-elevation catchments are less pronounced under RCP2.6, with an average change in catchments below 1500 m a.s.l. of <inline-formula><mml:math id="M63" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">5</mml:mn></mml:mrow></mml:math></inline-formula> % in winter, <inline-formula><mml:math id="M64" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">6</mml:mn></mml:mrow></mml:math></inline-formula> % in spring, <inline-formula><mml:math id="M65" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> % in summer, <inline-formula><mml:math id="M66" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">6</mml:mn></mml:mrow></mml:math></inline-formula> % in autumn, and <inline-formula><mml:math id="M67" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> % in
annual mean runoff (Fig. 4b). In higher-elevation catchments (<inline-formula><mml:math id="M68" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mn mathvariant="normal">1500</mml:mn></mml:mrow></mml:math></inline-formula> m a.s.l.), the mean changes under RCP2.6 amount to <inline-formula><mml:math id="M69" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">24</mml:mn></mml:mrow></mml:math></inline-formula> % in winter, <inline-formula><mml:math id="M70" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">16</mml:mn></mml:mrow></mml:math></inline-formula> % in spring, <inline-formula><mml:math id="M71" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">9</mml:mn></mml:mrow></mml:math></inline-formula> % in summer, <inline-formula><mml:math id="M72" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> % in autumn, and <inline-formula><mml:math id="M73" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.6</mml:mn></mml:mrow></mml:math></inline-formula> % across the year.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4" specific-use="star"><?xmltex \currentcnt{4}?><?xmltex \def\figurename{Figure}?><label>Figure 4</label><caption><p id="d1e1727">Elevation dependence of the multimodel median (dots) of seasonal and annual mean changes of runoff by 2070–2099 under RCP8.5 <bold>(a)</bold> and RCP2.6 <bold>(b)</bold>. Colors indicate the mean elevation of the 93 catchments.</p></caption>
            <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f04.png"/>

          </fig>

</sec>
</sec>
<sec id="Ch1.S4.SS2">
  <label>4.2</label><title>Changes in the runoff regime of six representative catchments</title>
      <p id="d1e1751">Changes in runoff regime for six example catchments representing typical
runoff regime types in Switzerland are depicted in Fig. 5. These are the
catchments highlighted in Fig. 1: Rosegbach–Pontresina, Kander–Hondrich,
Plessur–Chur, Emme–Emmenmatt, Venoge–Ecublens, and Verzasca–Lavertezzo.
The runoff regimes with absolute monthly mean runoff presented in this
chapter help to interpret the relative changes of seasonal and annual runoff
means discussed in Sect. 4.1. Figures with Pardé coefficients and
runoff regimes for each RCP separately can be found in the Supplement (Figs. S7–S11).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F5" specific-use="star"><?xmltex \currentcnt{5}?><?xmltex \def\figurename{Figure}?><label>Figure 5</label><caption><p id="d1e1756">Runoff regimes for the six representative catchments: Rosegbach <bold>(a)</bold>, Kander <bold>(b)</bold>, Plessur <bold>(c)</bold>, Emme <bold>(d)</bold>, Venoge <bold>(e)</bold>, and Verzasca <bold>(f)</bold>. Thick lines represent the multimodel median for the reference period (grey), for 2070–2099 under RCP2.6 (turquoise), and for 2070–2099 under RCP8.5 (orange). Shading shows the full model range for each RCP.</p></caption>
          <?xmltex \igopts{width=398.338583pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f05.png"/>

        </fig>

<sec id="Ch1.S4.SS2.SSS1">
  <label>4.2.1</label><title>Highly glaciated catchment: Rosegbach–Pontresina</title>
      <p id="d1e1791">The glaciated catchment, Rosegbach–Pontresina, exhibits a pronounced
decrease in July, August, and September (<inline-formula><mml:math id="M74" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3.1</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M75" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">6.7</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M76" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) and a small increase in winter runoff (<inline-formula><mml:math id="M77" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.5</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M78" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M79" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) under RCP8.5 (Fig. 5a). Monthly mean runoff does not change significantly in October. The typical glacier runoff regime with low flows in winter and peak flows in summer in the reference period changes to a nival regime with a peak runoff shifted from July or August to June under RCP8.5 (Fig. 5a). Although there are large relative (<inline-formula><mml:math id="M80" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">200</mml:mn></mml:mrow></mml:math></inline-formula> %) increases in the winter months, the contribution of winter runoff to the total runoff remains small. The mean runoff between June and September drops dramatically due to the absence of snowmelt and glacier melt contributions. However, runoff in late spring and summer remains the major contributor to the annual volume. Under RCP2.6,<?pagebreak page3078?> the changes for winter, spring, and autumn runoff are small (<inline-formula><mml:math id="M81" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.1</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M82" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.7</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M83" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>). For July, August, and September, the runoff decreases significantly (<inline-formula><mml:math id="M84" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.7</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M85" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3.5</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M86" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>), and the summer peak shifts from July or August to June or July. The change in summer runoff under RCP2.6 is approximately halved compared to the changes under RCP8.5.</p>
</sec>
<sec id="Ch1.S4.SS2.SSS2">
  <label>4.2.2</label><title>Slightly glaciated catchment: Kander–Hondrich</title>
      <p id="d1e1943">A similar behavior with a shift of the peak in the runoff regime from summer
to late spring or early summer is also found for the runoff regime in the
slightly glaciated catchment, Kander–Hondrich, under RCP8.5 (Fig. 5b). The
regime is characterized by a peak in early summer runoff in the reference
period. Under RCP8.5, the summer and<?pagebreak page3079?> early autumn runoff (July–September) decreases significantly (<inline-formula><mml:math id="M87" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.8</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M88" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3.2</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M89" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>), whereas winter
runoff increases (<inline-formula><mml:math id="M90" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.8</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M91" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.3</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M92" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>). This leads to a flattening of the runoff regime curve, resulting in similar contributions of winter and
summer runoff to the annual volume. Under RCP2.6, there is also a decrease
in July, August, and September (<inline-formula><mml:math id="M93" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.7</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M94" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.1</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M95" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) but less pronounced than the decrease under RCP8.5.</p>
</sec>
<sec id="Ch1.S4.SS2.SSS3">
  <label>4.2.3</label><title>Nival catchment: Plessur–Chur</title>
      <p id="d1e2051">The nival regime of the river Plessur–Chur shows a shift in peak flow from
June to May under both emission scenarios (Fig. 5c). Due to the increase in winter months (<inline-formula><mml:math id="M96" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.4</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M97" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.9</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M98" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) and decrease in summer runoff
(<inline-formula><mml:math id="M99" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.9</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M100" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">2.1</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M101" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>), the regime curve flattens under RCP8.5. The results also show increasing winter runoff and decreasing summer runoff under RCP2.6 but far less pronounced than under RCP8.5.</p>
</sec>
<sec id="Ch1.S4.SS2.SSS4">
  <label>4.2.4</label><title>Nival-to-pluvial catchment: Emme–Emmenmatt</title>
      <p id="d1e2127">In the reference period, the runoff regime in the nival-to-pluvial catchment, Emme–Emmenmatt, shows a peak in spring and early summer due to snowmelt and stable mean runoff from August to February (Fig. 5d). By end of the century under RCP8.5, the peak runoff in spring almost disappears. The runoff decreases strongly in the summer months (<inline-formula><mml:math id="M102" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.7</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M103" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.3</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M104" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) and less in the autumn months (<inline-formula><mml:math id="M105" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.1</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M106" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.2</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M107" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>).</p>
</sec>
<sec id="Ch1.S4.SS2.SSS5">
  <label>4.2.5</label><title>Pluvial catchment: Venoge–Ecublens</title>
      <p id="d1e2203">The shape of the runoff regime curve for the pluvial river Venoge–Ecublens remains the same for the reference period and the two emission scenarios with higher runoff in winter and lower runoff in summer (Fig. 5e). Although the regime changes only marginally under RCP2.6, the amplitudes under RCP8.5 become more distinct, with higher winter runoff (<inline-formula><mml:math id="M108" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.3</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M109" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.9</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M110" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) and lower summer runoff (<inline-formula><mml:math id="M111" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.2</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M112" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.3</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M113" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) than in the reference period. However, in comparison to other catchments, this change is smaller.</p>
</sec>
<sec id="Ch1.S4.SS2.SSS6">
  <label>4.2.6</label><title>Southern Alpine catchment: Verzasca–Lavertezzo</title>
      <p id="d1e2279">The southern Alpine catchment, Verzasca–Lavertezzo, shows a two-peaked runoff regime, with a first runoff peak in late spring and a second runoff
peak in autumn in the reference period (Fig. 5f). This pattern is still
present at the end of the century under both scenarios. However, the amplitudes of the peaks are less pronounced under RCP8.5 because of increasing winter runoff and decreasing spring (<inline-formula><mml:math id="M114" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.2</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M115" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.9</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M116" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) and summer (<inline-formula><mml:math id="M117" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.4</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M118" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1.7</mml:mn></mml:mrow></mml:math></inline-formula> mm d<inline-formula><mml:math id="M119" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup></mml:math></inline-formula>) runoff.</p>
      <p id="d1e2347">Summarizing the differences under RCP8.5 and RCP2.6 shows that the sign of
change under RCP2.6 is equal to the sign under RCP8.5 in almost all months and catchments. Comparisons with RCP4.5 (see Fig. S5) show that the magnitude of changes increases with the strength of the emission scenario and the distance in time. Also, the model agreement on the direction of change among the climate models is weaker under the low-emission scenario, RCP2.6, than under RCP8.5.</p>
</sec>
</sec>
<sec id="Ch1.S4.SS3">
  <label>4.3</label><title>Time of emergence of changes in the seasonal and annual means</title>
      <p id="d1e2359">The time of emergence, when at least 66 % of the models under RCP8.5 agree
on significant changes in the distribution of seasonal and annual means, is
depicted in Fig. 6. In winter, 45 out of 93 catchments show a time of emergence in the 21st century (Fig. 6a). An elevation dependence can be
identified: times of emergence are earlier in higher-elevation catchments and
later in lower-lying catchments. The high-Alpine catchments show particularly early times of emergence, with the end of the period 2017–2046 the earliest. The mean elevation of catchments with times of emergence earlier than 2065 is higher than 1500 m a.s.l., with one exception. Among the 48 catchments that do not show a time of emergence, 46 catchments have mean elevations lower than 1200 m a.s.l.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F6" specific-use="star"><?xmltex \currentcnt{6}?><?xmltex \def\figurename{Figure}?><label>Figure 6</label><caption><p id="d1e2364">Time of emergence for winter <bold>(a)</bold>, spring <bold>(b)</bold>, summer <bold>(c)</bold>, autumn <bold>(d)</bold>, and year <bold>(e)</bold> when at least 66 % of the models agree on significant changes in the distribution of seasonal and annual means.</p></caption>
          <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f06.png"/>

        </fig>

      <p id="d1e2388">In summer, 73 catchments exhibit a time of emergence and again generally an
earlier time of emergence for higher-elevation catchments (Fig. 6c). Catchments showing a time of emergence earlier than 2065 are all located in
mountainous areas with mean elevations higher than 1500 m a.s.l., again with one exception. The earliest time of emergence in summer is found for the
year 2043 (period 2014–2043). Catchments without time of emergence show a
mean elevation lower than 1000 m a.s.l., with one exception.</p>
      <p id="d1e2392">In spring, only 20 catchments exhibit a time of emergence (Fig. 6b). Again,
significant changes in the distribution are mainly found in the higher
Alpine catchments (above 1500 m a.s.l.). Only 14 catchments out of 93 exhibit a time of emergence in autumn (Fig. 6d). In contrast to the other
seasons, there is no clear elevation pattern distinguishable in autumn.</p>
      <p id="d1e2395">In all seasons, some of the catchments do not show a time of emergence, meaning that there is no statistically significant change in the distribution of the seasonal means. Clear patterns of significant changes in the distribution of seasonal means are mainly found in winter and summer.</p>
      <p id="d1e2398">For the annual means, 11 catchments reveal a time of emergence in the
21st century (Fig. 6e). Time of emergence in the annual mean is not
restricted to high-Alpine catchments, but only two catchments below 1500 m a.s.l. show significant changes, which are after 2095.</p>
      <p id="d1e2401">Due to the definition of time of emergence as the last year of a moving window in which the Kolmogorov–Smirnov test is rejected for the first time,
time of emergence is not necessarily given for all periods after the first
detection. Figure 7<?pagebreak page3080?> shows the temporal evolution of the time of emergence for
the seasons under RCP8.5. Most of the catchments show persistent significant
changes after the first detection of a time of emergence. However, few catchments do not reveal persistent significant changes after the first
detection due to nonlinear changes in the runoff response to climate change. The problem of nonconstant rejections affects 17 catchments in winter, 3 catchments in spring, 25 catchments in summer, and 6 catchments in autumn. Most of these catchments show a persistent time of emergence for the rest of the century a few years after the first detection.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F7"><?xmltex \currentcnt{7}?><?xmltex \def\figurename{Figure}?><label>Figure 7</label><caption><p id="d1e2406">Temporal evolution of time of emergence for the seasons. Periods where the <inline-formula><mml:math id="M120" display="inline"><mml:mi>p</mml:mi></mml:math></inline-formula> value of the Kolmogorov–Smirnov test is lower than 0.05 are
highlighted. Only catchments with at least one detection of time of emergence in one of the seasons are shown. Catchments are ordered by decreasing mean elevation of catchment.</p></caption>
          <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f07.png"/>

        </fig>

      <p id="d1e2423">'</p>
</sec>
<sec id="Ch1.S4.SS4">
  <label>4.4</label><title>Changes in seasonal means with increasing global mean temperatures</title>
      <p id="d1e2434">Changes in the multimodel median of seasonal and annual mean runoff for
different levels of global warming are shown in Fig. 8 for warming targets <inline-formula><mml:math id="M121" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M122" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M123" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M124" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. Generally, the patterns of change with levels of global warming are similar to the patterns for the two emission scenarios. Both the range of change between the catchments and the climate model agreement increase with higher global warming levels.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F8" specific-use="star"><?xmltex \currentcnt{8}?><?xmltex \def\figurename{Figure}?><label>Figure 8</label><caption><p id="d1e2478">Multimodel median of seasonal and annual mean changes of runoff due to <inline-formula><mml:math id="M125" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M126" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C <bold>(a, d, g, j, m)</bold>, <inline-formula><mml:math id="M127" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M128" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C <bold>(b, e, h, k, n)</bold>, and <inline-formula><mml:math id="M129" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula><inline-formula><mml:math id="M130" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> C global warming for winter <bold>(a–c)</bold>, spring <bold>(d–f)</bold>, summer <bold>(g–i)</bold>, autumn <bold>(j–l)</bold>, and year <bold>(m–o)</bold>. Black circles indicate catchments whose direction of change agrees across at least 90 % of the models.</p></caption>
          <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://hess.copernicus.org/articles/25/3071/2021/hess-25-3071-2021-f08.png"/>

        </fig>

      <p id="d1e2566">In winter, the mean runoff change across all catchments is <inline-formula><mml:math id="M131" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">17</mml:mn></mml:mrow></mml:math></inline-formula> % for a
global warming of <inline-formula><mml:math id="M132" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M133" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, <inline-formula><mml:math id="M134" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">23</mml:mn></mml:mrow></mml:math></inline-formula> % for <inline-formula><mml:math id="M135" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M136" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and
<inline-formula><mml:math id="M137" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">35</mml:mn></mml:mrow></mml:math></inline-formula> % for <inline-formula><mml:math id="M138" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M139" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (Fig. 8a–c). Stronger global warming increases not only the mean but also the range of change across the catchments. At <inline-formula><mml:math id="M140" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M141" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global warming, the range across all catchments is between <inline-formula><mml:math id="M142" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula> % and <inline-formula><mml:math id="M143" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">53</mml:mn></mml:mrow></mml:math></inline-formula> %, but at <inline-formula><mml:math id="M144" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M145" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global
warming, the range is <inline-formula><mml:math id="M146" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">5</mml:mn></mml:mrow></mml:math></inline-formula> % to <inline-formula><mml:math id="M147" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">127</mml:mn></mml:mrow></mml:math></inline-formula> %. Whereas two catchments show
slightly negative changes at <inline-formula><mml:math id="M148" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M149" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C warming, all catchments show positive changes for higher warming levels. Moreover, the agreement across the climate models per catchment increases with increasing warming.</p>
      <p id="d1e2757">The mean change in spring runoff among all catchments is <inline-formula><mml:math id="M150" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> % for
<inline-formula><mml:math id="M151" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">1.5</mml:mn></mml:mrow></mml:math></inline-formula> <inline-formula><mml:math id="M152" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global warming, <inline-formula><mml:math id="M153" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">6</mml:mn></mml:mrow></mml:math></inline-formula> % for 2 <inline-formula><mml:math id="M154" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and <inline-formula><mml:math id="M155" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">10</mml:mn></mml:mrow></mml:math></inline-formula> % for 3 <inline-formula><mml:math id="M156" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C (Fig. 8d–f). The changes in spring vary with elevation (see results in Sect. 4.1), with positive changes mainly for the higher-elevation catchments and negative changes for lower-lying catchments. Even though the average across all catchments changes little between warming levels, the range of change across the catchments and the<?pagebreak page3081?> model agreement
per catchment increase with higher warming levels; thus, the regional
elevation-dependent patterns become more pronounced.</p>
      <p id="d1e2828">In summer, the average among all catchments is <inline-formula><mml:math id="M157" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">7</mml:mn></mml:mrow></mml:math></inline-formula> % for 1.5 <inline-formula><mml:math id="M158" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
global warming, <inline-formula><mml:math id="M159" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">13</mml:mn></mml:mrow></mml:math></inline-formula> % for 2 <inline-formula><mml:math id="M160" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and <inline-formula><mml:math id="M161" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">23</mml:mn></mml:mrow></mml:math></inline-formula> % for 3 <inline-formula><mml:math id="M162" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C
(Fig. 8g–j). Again, the ranges across catchments and the model agreement
increase with higher warming levels. Compared to summer, the decrease in autumn runoff is smaller, with an average across all catchments of <inline-formula><mml:math id="M163" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">9</mml:mn></mml:mrow></mml:math></inline-formula> %
for 1.5 <inline-formula><mml:math id="M164" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global warming, <inline-formula><mml:math id="M165" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">7</mml:mn></mml:mrow></mml:math></inline-formula> % for 2 <inline-formula><mml:math id="M166" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and <inline-formula><mml:math id="M167" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">13</mml:mn></mml:mrow></mml:math></inline-formula> %
for 3 <inline-formula><mml:math id="M168" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. Most catchments, 89 out of 93, show a negative multimodel median for both 1.5 and 3 <inline-formula><mml:math id="M169" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C warming levels. Although only three catchments show a model agreement of more than 90 % for 1.5 <inline-formula><mml:math id="M170" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global warming, 43 catchments show robust model agreement on the direction of change for 3 <inline-formula><mml:math id="M171" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C global warming.</p>
      <p id="d1e2974"><?xmltex \hack{\newpage}?>For annual mean runoff, the mean among all catchments is <inline-formula><mml:math id="M172" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">0.2</mml:mn></mml:mrow></mml:math></inline-formula> % for
1.5 <inline-formula><mml:math id="M173" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, <inline-formula><mml:math id="M174" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.9</mml:mn></mml:mrow></mml:math></inline-formula> % for 2 <inline-formula><mml:math id="M175" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, and <inline-formula><mml:math id="M176" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3.7</mml:mn></mml:mrow></mml:math></inline-formula> % for 3 <inline-formula><mml:math id="M177" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C. Despite the slightly positive sign for 1.5 <inline-formula><mml:math id="M178" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C warming, 53 catchments out of 93 show negative changes. This number increases to 66 catchments for 2 <inline-formula><mml:math id="M179" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C and to 77 catchments for 3 <inline-formula><mml:math id="M180" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.
Moreover, model agreement increases from 3 catchments with robust model
agreement for 1.5 <inline-formula><mml:math id="M181" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C to 17 catchments for 3 <inline-formula><mml:math id="M182" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C.</p>
</sec>
</sec>
<sec id="Ch1.S5">
  <label>5</label><title>Discussion</title>
      <p id="d1e3091">Winter runoff is projected to increase in Switzerland due to enhanced winter
precipitation and increasing temperatures with climate change (CH2018, 2018). The higher temperatures result in more liquid precipitation and less solid precipitation in winter. This leads to less snow accumulation and thus to more direct runoff in winter. The relative changes in winter mean runoff in glaciated catchments are very high but still negligible as a contribution to the annual runoff volume. In nival and pluvial catchments, the contribution of winter runoff to the annual volume increases.</p>
      <p id="d1e3094">In spring, runoff in glaciated and nival catchments is projected to increase
due to increased snowmelt, particularly in early spring. The combination of
reduced snow accumulation in winter and earlier snowmelt shifts the peak in
runoff regime to a month earlier. Lower-lying catchments show decreasing runoff in spring due to reduced snow accumulation in winter, which reduces the snow available for snowmelt.</p>
      <p id="d1e3097">The summer runoff in Switzerland generally decreases with climate change. The processes governing this decrease differ with location and elevation of the catchments. In lower-lying catchments, reduced summer precipitation and enhanced evapotranspiration result in decreasing runoff in Switzerland. In
high-Alpine regions, where summer snowmelt and glacier melt dominate the runoff generation in the reference period, reduced snowpack and glacier
retreat amplify the decrease in summer runoff. The large model spread in
glaciated catchments in summer stems from the sensitivity of the runoff response to the glaciation of the catchment. In catchments where not all
climate projections result in a complete disappearance of glaciers, the model spread increases, so future glacier retreat is a major source of uncertainty.</p>
      <p id="d1e3100">Autumn runoff is also projected to decrease due to increased evapotranspiration and slightly reduced precipitation in most catchments
(CH2018, 2018). In a few of the eastern catchments, autumn precipitation
slightly increases, but the effect of enhanced evapotranspiration and the
reduced contribution from glacier melt and snowmelt are more dominant; autumn runoff also decreases in those catchments. Again, this decrease is amplified in catchments where glacier melt is important in early autumn under current climate conditions. However, the decrease in autumn runoff is most noticeable in early autumn, whereas in late autumn, at the end of October<?pagebreak page3082?> and November, the changes are less significant and can even change direction to positive values. This pattern is mainly found in very high Alpine catchments, where late autumn precipitation can fall more often as rain instead of snow and thus cannot be stored as snowpack. For the annual mean, a decrease in runoff was found in most catchments but with less robust signs among the climate models. This leads to the conclusion that, on the annual average, less water will be available in Swiss rivers. The shift in seasonality and thus a shift in the seasonal availability of water will impact many economic sectors. For example, increasing winter runoff may be beneficial for energy production, but decreasing summer runoff may lead to limitations in irrigation, particularly in lower-lying catchments where agricultural irrigation plays a crucial role.</p>
      <p id="d1e3104">In most catchments and seasons, the sign of change is the same for the high-emission scenario, RCP8.5, and the low-emission scenario, RCP2.6.
Changes in seasonality or in the runoff regime are amplified by higher
emissions and thus by increasing global mean temperatures. This amplification due to increased emissions and with intensified global warming shows the large benefits of mitigation. By mitigating climate<?pagebreak page3083?> change and following the RCP2.6 pathway, the magnitude of change can be reduced or even avoided, depending on the season and the runoff regime. However, some of the seasonal changes can no longer be avoided by mitigation actions, particularly in high-Alpine catchments with glacier influence. Responsible planners and policymakers need to adapt to this shift in the seasonal availability of water in our rivers.</p>
      <p id="d1e3107">Previous studies on climate change impacts on the runoff regime in
Switzerland (e.g., Köplin et al., 2012, 2014; Horton et al., 2006) were
driven by other emission scenarios, other and fewer climate model chains,
different methods of postprocessing the climate model output, and/or different hydrological models and calibration. Despite these differences, the sign of change in those studies agrees in most seasons with the signs in this study. A pronounced dependence of runoff changes on elevation was also found by Köplin et al. (2012), with lower-lying catchments being less affected by climate change. The largest difference concerns the annual mean runoff. Köplin et al. (2012) found an increase (up to <inline-formula><mml:math id="M183" display="inline"><mml:mrow><mml:mo>+</mml:mo><mml:mn mathvariant="normal">50</mml:mn></mml:mrow></mml:math></inline-formula> %) in annual runoff for high-elevation catchments and no change for lower-lying catchments in the annual volume. In contrast, our study projects a decrease in the annual mean runoff not only for high-elevation catchments but also for most of the lower-lying catchments. However, not all catchments show a robust decrease among the climate model chains. This difference between our results and previous studies may arise from the use of the most recent generation of Swiss Climate Change Scenarios (CH2018), which project slightly different precipitation changes with less summer drying and wetter winters (CH2018, 2018) than the previous generation of scenarios, CH2011, which was used by Köplin et al. (2012). The different handling of glacier melt processes and the new projections of glacier extents (Zekollari et al., 2019) may also result in slightly different projections in glaciated catchments. The Hydro-CH2018-Runoff ensemble uses transient glacier projections that are updated every 5 years in the hydrological model. Köplin et al. (2012) used static glacier projections for 30 years. The largest uncertainties in glaciated catchments were also found by Addor et al. (2014) due to the different handling of glacier extents and resulting glacier melt. Furthermore, the difference in the input data (transient projections versus delta change projections with same baseline time series for the reference period) may add to the different signs.</p>
      <p id="d1e3120">Even though not all catchments show a time of emergence in the 21st century, significant changes in the distribution of seasonal means emerge particularly early in high-elevation catchments. This is due to the importance of snowmelt and glacier melt for Alpine runoff regimes. With climate change, the influence of snowmelt and glacier melt decreases due to higher temperatures and subsequent glacier retreat. Lower-lying catchments generally show a later time of emergence. This may arise from the large interannual variability in pluvial catchments in the reference period and in future periods. Köplin et al. (2014) also assessed a time of emergence for Swiss catchments but only based on significant changes for two scenario periods and 10 climate models. Since their climate models were postprocessed with a delta change approach, only the natural variability of the reference period is reflected in their simulations. Despite these differences in methodology and data, they also found earlier time of emergence in winter and summer for high-elevation catchments. Although the definition of time of emergence applied here is commonly used in other climate change studies (e.g., Mahlstein et al., 2011), this definition also has disadvantages. For example, if the rejection of the null hypothesis is unstable in its temporal evolution, the time of emergence may be determined too early. This has been shown for some of the catchments in the present study. However, in most catchments a persistent detection of time of emergence (<inline-formula><mml:math id="M184" display="inline"><mml:mi>p</mml:mi></mml:math></inline-formula> value <inline-formula><mml:math id="M185" display="inline"><mml:mo>&lt;</mml:mo></mml:math></inline-formula> 0.05) in the distribution of the seasonal means was found shortly after the first detection of a time of emergence.</p>
      <p id="d1e3137">The findings of this study concern runoff regime changes for Switzerland. The pronounced changes in high-elevation catchments highlight the important
influence of temperature changes on snowmelt- and glacier-melt-driven catchments; thus, they also indicate that similar runoff responses may be found in other snow- and glacier-dominated regions. The results for lower-lying catchments, which are mainly driven by evapotranspiration and precipitation changes, may not be directly transferable to other regions. The runoff response in such catchments depends on local precipitation patterns and their changes under climate change.</p>
      <p id="d1e3140">Various sources of uncertainty affect our results. A detailed discussion of
the uncertainties for the simulations is provided in Muelchi et al. (2021).
Uncertainties arise from all the steps in the modeling chain: the scenarios
of greenhouse gas concentrations, the climate models and their boundary and
initial conditions, the postprocessing method (Gutiérrez et al., 2019), the hydrological model (Addor et al., 2014) and its calibration, and the underlying glacier projections; all these need to be considered in adaptation planning (e.g., Wilby and Dessai, 2010). Working with three emission scenarios and an ensemble of climate models partly addresses some of the uncertainty issues. Muelchi (2021) compared the results for three catchments to simulations from three different versions of hydrological models, and the key findings are robust among the models and the catchments.</p>
</sec>
<sec id="Ch1.S6" sec-type="conclusions">
  <label>6</label><title>Conclusions</title>
      <p id="d1e3151">Changes in runoff regimes and their time of emergence were assessed with the
new hydrological scenarios for 93 catchments in Switzerland. This study is
based on the most recent generation of climate change scenarios, postprocessed with quantile mapping. Compared to previous studies on runoff
regime changes, the results show similar signs of change for most seasons.
The largest differences were found for the high-elevation catchments, which
is likely due to the transient characteristic of the simulations and the
implementation<?pagebreak page3084?> of transient glacier projections driven by the same climate
model chains.</p>
      <p id="d1e3154">In general, winter runoff is projected to increase and summer runoff to decrease in Switzerland. The sign of change is robust across catchments, but
the magnitude of change is more pronounced for high-elevation catchments.
Particularly in summer, when snowmelt and glacier melt play an important role in
runoff generation, glaciated catchments will face a strong decrease in runoff due to the retreating glaciers. In rainfall-dominated catchments, the changes are also often robust but at a lower magnitude. Whereas the higher-elevation catchments show increasing spring runoff due to earlier snowmelt, the pluvial catchments in the lowlands will face decreasing spring runoff. A decrease in runoff is also found for autumn and annual mean runoff in most catchments. These seasonal patterns amplify with global warming and with higher-emission scenarios. Furthermore, the model agreement among the climate models increases with the strength of the emission scenario and the distance in time. A time of emergence of seasonal mean runoff was mainly found in summer and winter and for only a few catchments in spring and autumn. Early times of emergence, before 2060 in winter and before 2065 in summer, were found for catchments above 1500 m a.s.l. Significant changes in catchments below 1500 m a.s.l. emerge later in the century. However, not all catchments show a time of emergence in all seasons.</p>
      <p id="d1e3157">The amplification of changes by enhanced global warming highlights the importance of climate change mitigation. By mitigating climate change and following the RCP2.6 pathway to keep global warming below 2 <inline-formula><mml:math id="M186" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>C, the magnitude of change can be reduced substantially. The large decrease in summer runoff in glaciated catchments can be strongly dampened but not avoided entirely, because glacier retreat is projected even for the low-emission scenario. The present study can help to support adaptation planning in various sectors by presenting detailed information on changes in mean runoff.</p>
</sec>

      
      </body>
    <back><notes notes-type="dataavailability"><title>Data availability</title>

      <p id="d1e3173">The data used in this study are available under
<ext-link xlink:href="https://doi.org/10.5281/zenodo.3937485" ext-link-type="DOI">10.5281/zenodo.3937485</ext-link> (Muelchi et al., 2020).</p>
  </notes><app-group>
        <supplementary-material position="anchor"><p id="d1e3179">The supplement related to this article is available online at: <inline-supplementary-material xlink:href="https://doi.org/10.5194/hess-25-3071-2021-supplement" xlink:title="pdf">https://doi.org/10.5194/hess-25-3071-2021-supplement</inline-supplementary-material>.</p></supplementary-material>
        </app-group><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e3188">RM performed the analysis of the results and drafted the article. JS, OR, RW, and OM helped with interpreting the results. All authors reviewed the resulting data and assisted with paper writing.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e3194">The authors declare that they have no conflict of interest.</p>
  </notes><ack><title>Acknowledgements</title><p id="d1e3200">The authors would like to thank Harry Zekollari for processing and providing the glacier projections used in this study. We thank MeteoSwiss and FOEN for
providing the data necessary for this study.</p></ack><notes notes-type="financialsupport"><title>Financial support</title>

      <p id="d1e3205">This research has been supported by the Bundesamt für Umwelt.</p>
  </notes><notes notes-type="reviewstatement"><title>Review statement</title>

      <p id="d1e3211">This paper was edited by Ryan Teuling and reviewed by two anonymous referees.</p>
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    <!--<article-title-html>River runoff in Switzerland in a changing climate –  runoff regime changes and their time of emergence</article-title-html>
<abstract-html><p>Assessments of climate change impacts on runoff regimes are essential to climate change adaptation and mitigation planning. Changing runoff regimes and thus changing seasonal patterns of water availability strongly influence various economic sectors such as agriculture, energy production, and fishery and also affect river ecology. In this study, we use new transient hydrological scenarios driven by the most up-to-date local climate projections for Switzerland, the Swiss Climate Change Scenarios. These provide detailed information on changes in runoff regimes and their time of emergence for 93 rivers in Switzerland under three Representative Concentration Pathways (RCPs): RCP2.6, RCP4.5, and RCP8.5. These transient
scenarios also allow changes to be framed as a function of global mean
temperature.</p><p>The new projections for seasonal runoff changes largely confirm the sign of
changes in runoff from previous hydrological scenarios with increasing winter runoff and decreasing summer and autumn runoff. Spring runoff is
projected to increase in high-elevation catchments and to decrease in
lower-lying catchments. Despite the increases in winter and some increases
in spring, the annual mean runoff is projected to decrease in most catchments. Compared to lower-lying catchments, runoff changes in high-elevation catchments (above 1500&thinsp;m&thinsp;a.s.l.) are larger in winter,
spring, and summer due to the large influence of reduced snow accumulation
and earlier snowmelt and glacier melt. The changes in runoff and the
agreement between climate models on the sign of change both increase with
increasing global mean temperatures and higher-emission scenarios. This
amplification highlights the importance of climate change mitigation.</p><p>The time of emergence is the time when the climate signal emerges
significantly from natural variability. Under RCP8.5, times of emergence
were found early, before the period 2036–2065, in winter and summer for
catchments with mean altitudes above 1500&thinsp;m&thinsp;a.s.l. Significant changes in
catchments below 1500&thinsp;m&thinsp;a.s.l. emerge later in the century. Not all
catchments show significant changes in the distribution of seasonal means; thus, no time of emergence could be determined in these catchments.
Furthermore, the significant changes of seasonal mean runoff are not
persistent over time in some catchments due to nonlinear changes in runoff.</p></abstract-html>
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