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<article xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:oasis="http://docs.oasis-open.org/ns/oasis-exchange/table" xml:lang="en" dtd-version="3.0"><?xmltex \bartext{Tenth International Symposium on Land Subsidence (TISOLS)}?>
  <front>
    <journal-meta><journal-id journal-id-type="publisher">PIAHS</journal-id><journal-title-group>
    <journal-title>Proceedings of the International Association of Hydrological Sciences</journal-title>
    <abbrev-journal-title abbrev-type="publisher">PIAHS</abbrev-journal-title><abbrev-journal-title abbrev-type="nlm-ta">Proc. IAHS</abbrev-journal-title>
  </journal-title-group><issn pub-type="epub">2199-899X</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/piahs-382-345-2020</article-id><title-group><article-title>Characterizing marshland compressibility <?xmltex \hack{\break}?> by an in-situ loading test: design and set-up <?xmltex \hack{\break}?> of an experiment in the Venice Lagoon</article-title><alt-title>Characterizing marshland compressibility by an in-situ loading test</alt-title>
      </title-group><?xmltex \runningtitle{Characterizing marshland compressibility by an in-situ loading test}?><?xmltex \runningauthor{P.~Teatini et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="yes" rid="aff1">
          <name><surname>Teatini</surname><given-names>Pietro</given-names></name>
          <email>pietro.teatini@unipd.it</email>
        <ext-link>https://orcid.org/0000-0001-9525-4561</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Da Lio</surname><given-names>Cristina</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Tosi</surname><given-names>Luigi</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Bergamasco</surname><given-names>Alessandro</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff2">
          <name><surname>Pasqual</surname><given-names>Stefano</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Simonini</surname><given-names>Paolo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Girardi</surname><given-names>Veronica</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Zorzan</surname><given-names>Paolo</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Zoccarato</surname><given-names>Claudia</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-3199-8681</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Ferronato</surname><given-names>Massimiliano</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff4">
          <name><surname>Roner</surname><given-names>Marcella</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Marani</surname><given-names>Marco</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff4">
          <name><surname>D'Alpaos</surname><given-names>Andrea</given-names></name>
          
        <ext-link>https://orcid.org/0000-0003-1172-8278</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Cola</surname><given-names>Simonetta</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff5">
          <name><surname>Zambon</surname><given-names>Giuseppe</given-names></name>
          
        </contrib>
        <aff id="aff1"><label>1</label><institution>Department of Civil, Environmental and Architectural Engineering,
University of Padova, Padova, 35131, Italy</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>Institute of Marine Sciences, CNR, Venice, 30122, Italy</institution>
        </aff>
        <aff id="aff3"><label>3</label><institution>Institute of Geosciences and Earth Resources, CNR, Padova, 30131,
Italy</institution>
        </aff>
        <aff id="aff4"><label>4</label><institution>Department of Geosciences, University of Padova, Padova, 30131, Italy</institution>
        </aff>
        <aff id="aff5"><label>*</label><institution>retired</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Pietro Teatini (pietro.teatini@unipd.it)</corresp></author-notes><pub-date><day>22</day><month>April</month><year>2020</year></pub-date>
      
      <volume>382</volume>
      <fpage>345</fpage><lpage>351</lpage>
      
      <permissions>
        <copyright-statement>Copyright: © 2020 Pietro Teatini et al.</copyright-statement>
        <copyright-year>2020</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://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020.html">This article is available from https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020.html</self-uri><self-uri xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020.pdf">The full text article is available as a PDF file from https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020.pdf</self-uri>
      <abstract><title>Abstract</title>
    <p id="d1e227">The fate of coastal marshlands in the near future will strongly depend on their capability to maintain their elevation above a rising mean sea level. Together with the deposition of inorganic sediments during high tides, organic soil production by halophytic vegetation, and organic matter decomposition, land subsidence due to natural soil compression is a major factor controlling the actual elevation of salt-marsh platforms. Due to their high porosity and compressibility, the marsh sedimentary body undergoes large compression because of the load of overlying more recent deposits. The characterization of the geotechnical properties of these deposits is therefore of paramount importance to quantify consolidation versus accretion and relative sea level rise. However, undisturbed sampling of this loose material is extremely challenging and lab tests on in-situ collected samples are not properly representative of in-situ conditions due to the scale effects in highly heterogeneous silty soils such as those of the Venice lagoon. To overcome this limitation, an in-situ loading test was carried out in the Lazzaretto Nuovo salt-marsh in the Venice Lagoon, Italy. The load is obtained by a number of plastic tanks that are filled with seawater, reaching a cumulative load of 40 kN applied on a <inline-formula><mml:math id="M1" display="inline"><mml:mrow><mml:mn mathvariant="normal">2.5</mml:mn><mml:mo>×</mml:mo><mml:mn mathvariant="normal">1.8</mml:mn></mml:mrow></mml:math></inline-formula> m<inline-formula><mml:math id="M2" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> surface. Specific instrumentations were deployed before positioning the tanks to measure soil vertical displacement at various depths below the load (0, 10, and 50 cm) and distances (0, 40, and 80 cm) from the load centre. Moreover, six pressure transducers were used to record overpressure dissipation over time. The collected datasets will be interpreted through a 3-D flow-deformation model that, once calibrated, provides reliable estimates of the compressibility values for each monitored depth interval.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Introduction</title>
      <p id="d1e260">Characterizing the hydrogeological and geomechanical properties of recent
deposits, i.e. the top soils of prograding Holocene deltas, estuaries, and
lagoon landforms, is very challenging and, simultaneously, of paramount
importance. The difficulties mainly arise from the high porosity and
compressibility of these loose sediments (e.g., Brain et al., 2015) together
with heterogeneous nature of many sedimentary deposits such as those
investigated in this study (Cola and Simonini, 2002), that hamper the
possibility of collecting undisturbed samples for laboratory testing. The
significance of the physical characterization of these shallow soils is at
least twofold. From a geological perspective, sediments in coastal
transitional environments are considered (paleo-)sea level proxies and
provide precise and near-continuous reconstructions of relative sea level
over the last millennia (Brain et al., 2017). However, deriving the past sea
level evolution<?pagebreak page346?> from a marsh stratigraphy is challenging. Because of the
large porosity typical of newly formed landforms, shallow deposits experience a significant compaction (Allen, 1999; Cahoon et al., 2002; Jankowski et al., 2017; Zoccarato et al., 2018), with the ongoing consolidation over a certain depth range depending on the load of the overlying more recent deposits (Brain et al., 2015). If auto-compaction is improperly accounted for or neglected, inaccurate reconstructions of sea level rise, land subsidence, and sedimentation rates are obtained (Morton et al., 2000; Serandrei-Barbero et al., 2006).</p>
      <p id="d1e263">A second key aspect is related to the resilience of transitional coastal
ecosystems. In fact, the fate of these landforms in the next decades will be
strictly connected to their capability to keep their height with respect to
a rising mean sea level. The loss of relative elevation because of land
subsidence, erosion, decrease of sedimentation, and/or sea level rise can cause the loss of large portions of these environments or the shift of
lagoon tidal marshes to a less environmentally valuable state, e.g. tidal
flats. This is ongoing, for example, in the Mississippi delta, Louisiana
(Törnqvist et al., 2008), and in the Venice Lagoon, Italy (Marani et al., 2010), respectively. Auto-compaction of Holocene deposits occurs on the top of regional land subsidence due to tectonics, consolidation of deep formations, glacial and sediment isostatic adjustment, and fluid withdrawal
from the subsurface (Da Lio et al., 2018). Depending on the hydro-geomechanical properties of the recent deposits, auto-compaction can
significantly enhance the regional land subsidence (Zoccarato and Teatini,
2017), with a nonlinear feedback between sedimentation, compaction, and
accretion. This is generally neglected in morphological models developed to
investigate the possible evolution of transitional environments in relation
to the expected climate change or sedimentation scenarios (Lesser et al.,
2004; D'Alpaos and Marani, 2016).</p>
      <p id="d1e266">Until now, the properties of these soils have been estimated through empirical relationships and lab tests. Brain et al. (2015) and van Asselen
et al. (2011) linked void ratio at 1 kPa (<inline-formula><mml:math id="M3" display="inline"><mml:mrow><mml:msub><mml:mi>e</mml:mi><mml:mn mathvariant="normal">0</mml:mn></mml:msub></mml:mrow></mml:math></inline-formula>), the compression (<inline-formula><mml:math id="M4" display="inline"><mml:mrow><mml:msub><mml:mi>C</mml:mi><mml:mi mathvariant="normal">c</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>), and re-compression (<inline-formula><mml:math id="M5" display="inline"><mml:mrow><mml:msub><mml:mi>C</mml:mi><mml:mi mathvariant="normal">r</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>) indices to the percentage of organic matter quantified through the loss on ignition (LOI). Cola et al. (2008) and Brain et al. (2017) collected samples at various depths in the upper 1 to 2 m soil range from the San Felice marsh, Venice Lagoon, and the East River Marsh in Connecticut, respectively, and estimated the main geomechanical parameters (<inline-formula><mml:math id="M6" display="inline"><mml:mrow><mml:msub><mml:mi>C</mml:mi><mml:mi mathvariant="normal">c</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M7" display="inline"><mml:mrow><mml:msub><mml:mi>C</mml:mi><mml:mi mathvariant="normal">r</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>, the yield stress <inline-formula><mml:math id="M8" display="inline"><mml:mrow><mml:msubsup><mml:mi mathvariant="italic">σ</mml:mi><mml:mi>v</mml:mi><mml:mo>′</mml:mo></mml:msubsup></mml:mrow></mml:math></inline-formula> and the Young modulus <inline-formula><mml:math id="M9" display="inline"><mml:mi>E</mml:mi></mml:math></inline-formula>) from one-dimensional compression tests at a stress level corresponding to the site overburden stress.</p>
      <p id="d1e345">However, the representativeness of these data is questionable because sampling these loose soils in undisturbed conditions in highly challenging.
To avoid problematic generalizations or challenges related to soil sampling
and lab testing at very small stresses, an original in-situ loading test has
been planned and carried out in July 2019 on a tidal marsh of the Venice Lagoon, Italy.</p>
      <p id="d1e349">This contribution mainly reports on the design of the loading experiment and
its implementation with the aim that this approach may be implemented somewhere else. The collected records are finally illustrated.</p>
</sec>
<sec id="Ch1.S2">
  <label>2</label><title>The study area</title>
      <p id="d1e360">The study area is a lagoon sector located about 5 km NW of the Venice historical center and close to the Lido inlet, known as Lazzaretto Nuovo
(Fig. 1). Specifically, the loading experiment was conducted in a portion
of the saltmarsh bounded by lagoon channels and crossed by a branching network of tidal creeks, which allow the water exchange with the mudflats
and ponds, thus enhancing the sediment transport and deposition above the
marsh platform (Amos et al., 2010).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F1"><?xmltex \currentcnt{1}?><label>Figure 1</label><caption><p id="d1e365">Location of the Lazzaretto Nuovo salt-marsh and the site where the
loading test has been carried out.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f01.png"/>

      </fig>

      <p id="d1e374">Nowadays, the amount of sediments entering the lagoon from the rivers is
negligible. Thus, the main sources of sediments is erosion at the marsh fronts and on the lagoon bottom by waves, tides and other hydrodynamic processes, and sediment input through the lagoon inlets (Marani et al., 2011).</p>
      <p id="d1e378">The elevation of the Lazzaretto Nuovo marsh, which is a natural marsh with
the margins partially reinforced by stone-filled rolls to reduce erosion,
ranges from 0.3 to 0.5 m a.s.l. (above sea level) on the strip banks of the channels and creeks. Depending on the surface elevation, different halophytic species of vegetation colonized the saltmarsh (Da Lio et al., 2013). The vegetation plays an important role in the sedimentation process since it favors the trapping of the suspended sediment transported on the top of the marshes during high tide events and contributes to organic soil production. This allows the saltmarshes to counteract relative<?pagebreak page347?> sea-level rise, i.e. land
subsidence combined with sea level rise due to climate changes (Rizzetto and
Tosi, 2011).</p>
      <p id="d1e381">An image of the surface movements of Lazzaretto Nuovo marsh is shown in Fig. 2. The measurements were obtained by Persistent Scattered Interferometry (PSI) on a stack of 143 TerraSAR-X stripmap images acquired
between 2008 and 2013 with a regular 11 d revisiting time. Positive velocities were interpreted as accretion rates (Da Lio et al., 2018).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F2"><?xmltex \currentcnt{2}?><label>Figure 2</label><caption><p id="d1e386">Lazzaretto Nuovo salt-marsh: average land displacement between 2008 and 2013 measured by PSI. Positive values mean uplift, negative values land subsidence. The red box shows the location of the loading experiment (modified after Da Lio et al., 2018).</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f02.png"/>

      </fig>

      <p id="d1e395">In the upper 1 m, the saltmarsh deposit consists of silty clay and silt
alternated with thin peaty layers, and abundant recent plant remains and
root traces at the top. A picture of sediment cores and the grain size
distribution of the silt in the 20–30 cm depth interval are shown in Fig. 3. Silt is the prevailing lithology of the salt-mashes located in the
northern lagoon basin close to the actual littoral strips (Tonni et al., 2006; Biscontin et al., 2007; Cola et al., 2008). Mudflat deposits are composed mainly of clayey silt whereas channel units are medium to fine sand
layers, often with shell fragments, interbedded by silt laminations. At the
Lazzaretto marsh, the total thickness of the soft Holocene sediments amounts
to 6 to 7 m.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3"><?xmltex \currentcnt{3}?><label>Figure 3</label><caption><p id="d1e400"><bold>(a)</bold> Grain size distribution of a sample collected in the
Lazzaretto Nuovo marsh at about 20 cm depth. <bold>(b)</bold> Picture of a 50 cm deep core drilled to establish one of the piezometers. The main lithological units are highlighted.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f03.png"/>

      </fig>

</sec>
<sec id="Ch1.S3">
  <label>3</label><title>Set-up of the loading experiment</title>
      <p id="d1e422">An in-situ loading experiment was carried out in July 2019 on the Lazzaretto
Nuovo marsh to reliably characterize the hydro-geomechanical response of the
shallow marsh deposits at low vertical effective stress levels when subjected to small vertical stress increments.</p>
      <p id="d1e425">The execution of such a test has been very challenging from several points
of view. The marsh is difficult to reach, the material transportation is not
easy, the setting up of the specific instrumentation required to track the
evolution of the hydro-geomechanical parameters is not straightforward without disturbing the marsh soil, thus affecting the potential test results. In addition, the mash is flooded twice a day during high tides. Safety conditions for the researchers remaining on the marsh for a few consecutive days must also be guaranteed.</p>
      <p id="d1e428">The load was represented by eight polyethylene tanks that, once put in the
appropriate location, were filled with seawater. The tank dimensions are
<inline-formula><mml:math id="M10" display="inline"><mml:mrow><mml:mn mathvariant="normal">78</mml:mn><mml:mo>×</mml:mo><mml:mn mathvariant="normal">69</mml:mn><mml:mo>×</mml:mo><mml:mn mathvariant="normal">104</mml:mn></mml:mrow></mml:math></inline-formula> cm<inline-formula><mml:math id="M11" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">3</mml:mn></mml:msup></mml:math></inline-formula>, can contain 500 L, and their empty weigh is approximately 0.1 kN each.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4" specific-use="star"><?xmltex \currentcnt{4}?><label>Figure 4</label><caption><p id="d1e459"><bold>(a)</bold> Picture of the loading and monitoring equipment and <bold>(b)</bold> the experimental equipment in high-tide conditions with the marsh flooded by approximately 0.2 m sea water.</p></caption>
        <?xmltex \igopts{width=341.433071pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f04.jpg"/>

      </fig>

      <?xmltex \floatpos{t}?><fig id="Ch1.F5" specific-use="star"><?xmltex \currentcnt{5}?><label>Figure 5</label><caption><p id="d1e475"><bold>(a)</bold> Displacement transducers (C0: central position at the land surface; C10: central position at 10 cm depth; M10: median position at 10 cm depth; E10: external position at 10 cm depth; C50: central position at 50 cm depth). <bold>(b)</bold> Displacements recorded during phase 2 unloading and phase 3 loading cycles; negative values mean uplift, positive subsidence.</p></caption>
        <?xmltex \igopts{width=398.338583pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f05.jpg"/>

      </fig>

      <p id="d1e489">The tanks were arranged in two rows, each constituted by four tanks (Fig. 4a). This configuration allowed to transfer a sufficiently high load on a sufficiently large area, thus the assumption of vertical one-dimensional
deformation is acceptable at least below the central portion of the system. A reinforced geotextile and four wooden pallets were put between the marsh surface and the tanks to guarantee a more uniform load distribution on the
marsh platform and eliminate (or at least reduce) buoyancy forces on the
tanks in high tide conditions (Fig. 4b). The tanks were separated by a 10 cm gap to allow for a correct working of the monitoring instrumentations. Consequently, the whole loading area is <inline-formula><mml:math id="M12" display="inline"><mml:mrow><mml:mn mathvariant="normal">2.5</mml:mn><mml:mo>×</mml:mo><mml:mn mathvariant="normal">1.8</mml:mn></mml:mrow></mml:math></inline-formula> m<inline-formula><mml:math id="M13" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula>. The tanks were properly interconnected trough plastic tubes<?pagebreak page348?> to guarantee the same water levels during filling, which guarantees a uniformly distributed load.</p>
      <p id="d1e513">We measured vertical displacements and groundwater pressure at various depths and locations below the load. A number of five dial indicators (Borletti SC50, 0.01 mm accuracy) were installed to measure the movements of
the marsh surface, at 10 and 50 cm depth in the load center, just outside the load, and at an intermediate position (Fig. 5a). Each transducer is attached at one end to a H-shaped steel structure anchored on two piles set
into the ground to a 6 m depth where an over-consolidated layer is located.
The other end is fixed to the prescribed soil depth through an ad hoc aluminum anchor designed while taking into account the following two main
constraints: (i) minimize the soil disturbance during the insertion at the
reference depth; (ii) guarantee the anchor solidity with the soil at the depth of interest although the loose nature of the shallow deposits forming the tidal marsh. The anchor is constituted by a 5 cm radius helicoidal disk with a 0.5 cm diameter, 50 cm long wire in the center and is inserted into the soil by rotation only.</p>
      <p id="d1e516">Before positioning the tanks, six water pressure loggers (ONSET Hobo U20-001-04-Ti, resolution 0.014 kPa, accuracy <inline-formula><mml:math id="M14" display="inline"><mml:mrow><mml:mo>±</mml:mo><mml:mn mathvariant="normal">0.3</mml:mn></mml:mrow></mml:math></inline-formula> % FS, 0.43 kPa maximum error) were put into Casagrande filter units and established at depths ranging from 20 to 100 cm below the marsh surface. Similar to the displacement transducers, the pressure measurements were carried out directly below the load center, at the edge of the tanks and in intermediate positions (Fig. 6).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F6"><?xmltex \currentcnt{6}?><label>Figure 6</label><caption><p id="d1e532">Sketch of the loading with dimensions and location of the monitoring instruments.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f06.png"/>

      </fig>

      <p id="d1e541">The displacements of the reference H-shaped steel structure and the four external corners of wooden pallets were checked during the whole test by
means of very-high precision spirit levelling. A reference benchmark was
established 50 m far from the load using a steel pole inserted into the soil
at about 6 m depth. The tide was also measured in the<?pagebreak page349?> channel in front of the experimental apparatus. Also the tidal gauge equipment was connected to
the same 6 m deep reference pole.</p>
      <p id="d1e544">The movement of the material and researchers during the 4 d experiment period was also very challenging. This required the use of three boats. A
large one was used to transport the bulky equipment, provide the power supply, and hosted the people at night and during a couple of severe
thunderstorms that affected the northern Venice Lagoon on 8 and 9 July. A smaller one was used to as a “link” between the large boat, which cannot
dock to the marsh margin for safety reason, and the marsh. The third one was
devoted to the movements of the researchers that alternating remained on the
marsh to collect the measurements and checked the ongoing experiment.</p>
      <p id="d1e547">A set of wood boards was also placed on the marsh surface and used to reduce
the loading disturbance induced by the people walking on the marsh during the apparatus establishment and the experimentation.</p>
</sec>
<sec id="Ch1.S4">
  <label>4</label><title>The loading experiment and preliminary results</title>
      <p id="d1e558">The experiment was carried out from 8 to 11 July 2019, and consisted of various phases to characterize the geomechanical properties in virgin loading, unloading, and secondary compression conditions. The phases can be
summarized as follows (Fig. 7):
<list list-type="order"><list-item>
      <p id="d1e563">a load of <inline-formula><mml:math id="M15" display="inline"><mml:mrow><mml:mo>∼</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula> kPa (the bottom tanks were filled to the middle) was applied in half an hour, maintained over 3 h, and then quickly
removed;
<?xmltex \hack{\newpage}?></p></list-item><list-item>
      <p id="d1e578">a load of <inline-formula><mml:math id="M16" display="inline"><mml:mrow><mml:mo>∼</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula> kPa (the four bottom tanks were completely filled) was applied in half an hour, maintained over 20 h, and then quickly removed;</p></list-item><list-item>
      <p id="d1e592">a load of <inline-formula><mml:math id="M17" display="inline"><mml:mrow><mml:mo>∼</mml:mo><mml:mn mathvariant="normal">8</mml:mn></mml:mrow></mml:math></inline-formula> kPa (all the eight tanks were completely filled) was applied in 1 h, maintained over almost 24 h, removed in 1 h, and the monitoring prolonged over the next 3 h.</p></list-item></list>
The load path is schematically depicted with the dashed orange colored line in Fig. 7. Notice that phase 2 was repeated due to a severe thunderstorm with hail that partially destroyed the equipment. Consequently, we were able to monitor the system evolution only during the phase 2 repetition.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F7"><?xmltex \currentcnt{7}?><label>Figure 7</label><caption><p id="d1e608">Time behavior of the applied load, tide level and pressure at
piezometer 25A, which is 20 cm deep and at a distance of 15 cm from the load center (Fig. 6). The records cover the whole period of the loading test,
i.e. from 8 July at 12:00 LT to 11 July at 14:00 LT.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/345/2020/piahs-382-345-2020-f07.png"/>

      </fig>

      <p id="d1e617">A few preliminary results of the test are provided in Figs. 5b and 7. Figure 5b shows the displacements recorded by the various transducers over
phase 2 unloading and phase 3 loading. As expected, the marsh body swelled
when the load was removed and then compressed again when the eight tanks were filled. Generally, but not strictly, the shallower the reference depth and the closer the location to the center of the load, the larger is the recorded displacement.</p>
      <p id="d1e621">Figure 7 compares the pressure recorded over the whole experiment by a 20 cm
deep pressure transducer with the tidal fluctuation of the lagoon level and
the load applied on the marsh surface. The groundwater pressure is significantly affected by the tide, but the effect exerted by the load
application and removal is also clearly recorded.</p>
</sec>
<sec id="Ch1.S5" sec-type="conclusions">
  <label>5</label><title>Conclusion</title>
      <p id="d1e633">An in-situ loading test has been carried out in July 2019 on the Lazzaretto
Nuovo tidal marsh, a few km north-east of Venice. The test was carried out by means of original equipment specifically designed to meet the challenges of working in a tidal transitional environment. The test was composed of<?pagebreak page350?> three loading and unloading cycles, with a maximum pressure exerted on the marsh surface that amounted to <inline-formula><mml:math id="M18" display="inline"><mml:mrow><mml:mo>∼</mml:mo><mml:mn mathvariant="normal">8</mml:mn></mml:mrow></mml:math></inline-formula> kPa over a 4.5 m<inline-formula><mml:math id="M19" display="inline"><mml:msup><mml:mi/><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:math></inline-formula> area. A number of sensors recorded the vertical displacement of the marsh deposits and the groundwater pressure below the load at three depths and three distances from the central axis of the load. Due to the peculiarity of the environment and the softness of the marsh shallow deposits, the set-up and management of the experiment required a large effort.</p>
      <p id="d1e655">Despite the adverse meteorological conditions that destroyed part of the
instrumentation, the collected dataset seems valuable. Because of the complex geometry and the variability of the external conditions, namely a tidal fluctuation in the order of 1 m, the measurement interpretation is not
straightforward. This will be carried out by means of a three-dimensional
visco-elasto-plastic poromechanical model that, once properly calibrated, will allow characterizing the hydrological and geomechanical properties of
the tidal marsh deposits. These properties will be finally used in long-term
biomorpho-geomechanical simulations of tidal marsh evolution.</p>
</sec>

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

      <p id="d1e662">Since the project is still ongoing, data are not available to the public. Data can be required to the funding agency. Data will become freely accessible at the end of the VENEZIA 2021 Research Programme expected in December 2021.</p>
  </notes><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e668">PT, LT, AB, PS, VG, PZ, CZ, MF and MM designed the experiment. PT, CD, LT, AB, SP, VG, PZ, CZ, MR, MM, AD and GZ carried out the experiment. PS, VG, PZ and SC carried out the lab testing. PT, CD, LT, AB, PS and VG wrote the paper.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e674">The authors declare that they have no conflict of interest.</p>
  </notes><notes notes-type="sistatement"><title>Special issue statement</title>

      <p id="d1e680">This article is part of the special issue “TISOLS: the Tenth International Symposium On Land Subsidence – living with subsidence”. It is a result of the Tenth International Symposium on Land Subsidence, Delft, the Netherlands, 17–21 May 2021.</p>
  </notes><ack><title>Acknowledgements</title><p id="d1e686">This article is an outcome of the VENEZIA-2021 Research Programme, Topic 3.1, funded by the “Provveditorato Interregionale Opere Pubbliche per il Veneto, Trentino Alto Adige e Friuli Venezia Giulia” through the “Concessionario Consorzio Venezia Nuova” and coordinated by CORILA, Venice. The authors gratefully acknowledge the great assistance in the field provided by the crew of the research boat Litus (CNR-ISMAR) Daniele Penzo, Mauro Penzo, and Gianni Zennaro.</p></ack><notes notes-type="financialsupport"><title>Financial support</title>

      <p id="d1e691">This research has been supported by the Provveditorato Interregionale Opere Pubbliche per il Veneto, Trentino Alto Adige e Friuli Venezia Giulia (grant no. VENEZIA-2021 Research Programme, Topic 3.1).</p>
  </notes><ref-list>
    <title>References</title>

      <ref id="bib1.bib1"><label>1</label><?label 1?><mixed-citation>Allen, J. R. L.: Geological impact on coastal wetland landscapes: some general effects of sediment auto-compaction in the Holocene of northwest Europe, Holocene, 9, 1–12, <ext-link xlink:href="https://doi.org/10.1191/095968399674929672" ext-link-type="DOI">10.1191/095968399674929672</ext-link>, 1999.</mixed-citation></ref>
      <ref id="bib1.bib2"><label>2</label><?label 1?><mixed-citation>Amos, C. L., Umgiesser, G., Tosi, L., and Townend, I. H.: The coastal
morphodynamics of Venice lagoon, Italy: An introduction, Cont. Shelf Res., 30, 837–846, <ext-link xlink:href="https://doi.org/10.1016/j.csr.2010.01.014" ext-link-type="DOI">10.1016/j.csr.2010.01.014</ext-link>, 2010.</mixed-citation></ref>
      <ref id="bib1.bib3"><label>3</label><?label 1?><mixed-citation>
Biscontin, G., Cola, S., Pestana, J. M., and Simonini, P.: Unified compression model for Venice lagoon natural silts, J. Geotech. Geoenviron. Eng., 133, 932–942, 2007.</mixed-citation></ref>
      <ref id="bib1.bib4"><label>4</label><?label 1?><mixed-citation>Brain, M. J., Kemp, A. C., Horton, B. P., Culver, S. J., Parnell, A. C., and
Cahill, N.: Quantifying the contribution of sediment compaction to late Holocene salt-marsh sea-level reconstruction, North-Carolina, USA,
Quaternary Res., 83, 1151, <ext-link xlink:href="https://doi.org/10.1016/j.yqres.2014.08.003" ext-link-type="DOI">10.1016/j.yqres.2014.08.003</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib5"><label>5</label><?label 1?><mixed-citation>Brain, M. J., Kemp, A. C., Hawkes, A. D., Engelhart, S. E., Vane, C. H., Cahill, N., Hill, T. D., Donnelly, J. P., and Horton, B. P.: Exploring
mechanisms of compaction in salt-marsh sediments using Common Era relative
sea-level reconstructions, Quaternary Sci. Rev., 167, 96–111,
<ext-link xlink:href="https://doi.org/10.1016/j.sedgeo.2010.10.005" ext-link-type="DOI">10.1016/j.sedgeo.2010.10.005</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib6"><label>6</label><?label 1?><mixed-citation>Cahoon, D. R., Lynch, J. C., Hensel, P., Boumans, R., Perez, B. C., Segura, B., and Day Jr., J. W.: High-precision measurements of wetland sediment elevation: 1. Recent improvements to the sedimentation-erosion table, J. Sediment Res., 72, 730–733, <ext-link xlink:href="https://doi.org/10.1306/020702720730" ext-link-type="DOI">10.1306/020702720730</ext-link>, 2002.</mixed-citation></ref>
      <ref id="bib1.bib7"><label>7</label><?label 1?><mixed-citation>
Cola, S. and Simonini, P.: Mechanical behavior of silty soils of the Venice
lagoon as a function of their grading characteristics, Can. Geotech. J., 39, 879–893, 2002.</mixed-citation></ref>
      <ref id="bib1.bib8"><label>8</label><?label 1?><mixed-citation>Cola, S., Sanavia, L., Simonini, P., and Schrefler, B. A.: Coupled thermohydromechanical analysis of Venice lagoon salt marshes, Water Resour. Res., 44, W00C05, <ext-link xlink:href="https://doi.org/10.1029/2007WR006570" ext-link-type="DOI">10.1029/2007WR006570</ext-link>, 2008.</mixed-citation></ref>
      <ref id="bib1.bib9"><label>9</label><?label 1?><mixed-citation>Da Lio, C., D'Alpaos, A., and Marani, M.: The secret gardener: vegetation and the emergence of biogeomorphic patterns in tidal environments, Philos. T. Roy. Soc. A, 371, 20120367, <ext-link xlink:href="https://doi.org/10.1098/rsta.2012.0367" ext-link-type="DOI">10.1098/rsta.2012.0367</ext-link>, 2013.</mixed-citation></ref>
      <ref id="bib1.bib10"><label>10</label><?label 1?><mixed-citation>Da Lio, C., Teatini, P., Strozzi, T., and Tosi, L.: Understanding land subsidence in salt marshes of the Venice Lagoon from SAR Interferometry and
ground-based investigations, Remote Sens. Environ., 205, 56–70,
<ext-link xlink:href="https://doi.org/10.1016/j.rse.2017.11.016" ext-link-type="DOI">10.1016/j.rse.2017.11.016</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib11"><label>11</label><?label 1?><mixed-citation>D'Alpaos, A. and Marani, M.: Reading the signatures of biologic-geomorphic
feedbacks in salt-marsh landscapes, Adv. Water Resour., 93, 265–275, <ext-link xlink:href="https://doi.org/10.1016/j.advwatres.2015.09.004" ext-link-type="DOI">10.1016/j.advwatres.2015.09.004</ext-link>, 2016.</mixed-citation></ref>
      <ref id="bib1.bib12"><label>12</label><?label 1?><mixed-citation>Jankowski, K. L., Törnqvist, T. E., and Fernandes, A. M.: Vulnerability of Louisiana's coastal wetlands to present-day rates of relative sea-level
rise, Nat. Commun., 8, 14792, <ext-link xlink:href="https://doi.org/10.1038/ncomms14792" ext-link-type="DOI">10.1038/ncomms14792</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib13"><label>13</label><?label 1?><mixed-citation>Lesser, G. R., Roelvink, J. A., van Kester, J. A. T. M., and Stelling, G. S.: Development and validation of a three-dimensional morphological model, Coast. Eng., 51, 883–915, <ext-link xlink:href="https://doi.org/10.1016/j.coastaleng.2004.07.014" ext-link-type="DOI">10.1016/j.coastaleng.2004.07.014</ext-link>, 2004.</mixed-citation></ref>
      <ref id="bib1.bib14"><label>14</label><?label 1?><mixed-citation>Marani, M., D'Alpaos, A., Lanzoni, S., Carniello, L., and Rinaldo, A.: The
importance of being coupled: Stable states and catastrophic shifts in tidal
bio-morphodynamics, J. Geophys. Res., 115, F04004, <ext-link xlink:href="https://doi.org/10.1029/2009JF001600" ext-link-type="DOI">10.1029/2009JF001600</ext-link>, 2010.</mixed-citation></ref>
      <ref id="bib1.bib15"><label>15</label><?label 1?><mixed-citation>Marani, M., D'Alpaos, A., Lanzoni, S., and Santalucia, M.: Understanding and
predicting wave erosion of marsh edge, Geophys. Res. Lett., 38, L21401,
<ext-link xlink:href="https://doi.org/10.1029/2011GL048995" ext-link-type="DOI">10.1029/2011GL048995</ext-link>, 2011.</mixed-citation></ref>
      <ref id="bib1.bib16"><label>16</label><?label 1?><mixed-citation>Morton, R. A., Ward, G. H., and White, W. A.: Rates of sediment supply and
sea-level rise in a large coastal lagoon, Mar. Geol., 167, 261–284,
<ext-link xlink:href="https://doi.org/10.1016/S0025-3227(00)00030-X" ext-link-type="DOI">10.1016/S0025-3227(00)00030-X</ext-link>, 2000.</mixed-citation></ref>
      <ref id="bib1.bib17"><label>17</label><?label 1?><mixed-citation>Rizzetto, F. and Tosi, L.: Aptitude of modern salt marshes to counteract
relative sea-level rise, Venice Lagoon (Italy), Geology, 39, 755–758,
<ext-link xlink:href="https://doi.org/10.1130/G31736.1" ext-link-type="DOI">10.1130/G31736.1</ext-link>, 2011.</mixed-citation></ref>
      <ref id="bib1.bib18"><label>18</label><?label 1?><mixed-citation>Serandrei-Barbero, R., Albani, A., Donnici, S., and Rizzetto, F.: Past and
recent sedimentation rates in the Lagoon of Venice (Northern Italy), Estuar.
Coast. Shelf Sci., 69, 255–269, <ext-link xlink:href="https://doi.org/10.1016/j.ecss.2006.04.018" ext-link-type="DOI">10.1016/j.ecss.2006.04.018</ext-link>, 2006.
</mixed-citation></ref><?xmltex \hack{\newpage}?>
      <ref id="bib1.bib19"><label>19</label><?label 1?><mixed-citation>
Tonni, L., Cola, S., and Pastor, M.: A generalized plasticity approach for
describing the behaviour of silty soils forming the Venetian lagoon basin, in: Proc. of the 6th Eur. Conf. on Numerical Methods in Geotechnical
Engineering, 6–8 September 2006, Graz, Austria, 93–99, 2006.</mixed-citation></ref>
      <ref id="bib1.bib20"><label>20</label><?label 1?><mixed-citation>Törnqvist, T. E., Wallace, D. J., Storms, J. E. A., Wallinga, J., Dam, R. L., Blaauw, M., Derksen, M. S., Klerks, C. J. W., Meijneken, C., A., and Snijders, E. M. A.: Mississippi Delta subsidence primarily caused by compaction of Holocene strata, Nat. Geosci., 1, 173–176, <ext-link xlink:href="https://doi.org/10.1038/ngeo129" ext-link-type="DOI">10.1038/ngeo129</ext-link>, 2008.</mixed-citation></ref>
      <ref id="bib1.bib21"><label>21</label><?label 1?><mixed-citation>van Asselen, S., Karssenberg, D., and Stouthamer, E.: Contribution of peat
compaction to relative sea-level rise within Holocene deltas, Geophys. Res.
Lett., 38, L24401, <ext-link xlink:href="https://doi.org/10.1029/2011GL049835" ext-link-type="DOI">10.1029/2011GL049835</ext-link>, 2011.</mixed-citation></ref>
      <ref id="bib1.bib22"><label>22</label><?label 1?><mixed-citation>Zoccarato, C. and Teatini, P.: Numerical simulations of Holocene salt-marsh
dynamics under the hypothesis of large soil deformations, Adv. Water Resour.,
110, 107–119, <ext-link xlink:href="https://doi.org/10.1016/j.advwatres" ext-link-type="DOI">10.1016/j.advwatres</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib23"><label>23</label><?label 1?><mixed-citation>Zoccarato, C., Minderhoud, P. S. J., and Teatini, P.: The role of sedimentation and natural compaction in a prograding delta: Insights from the mega Mekong delta, Vietnam, Scient. Rep., 8, 11437, <ext-link xlink:href="https://doi.org/10.1038/s41598-018-29734-7" ext-link-type="DOI">10.1038/s41598-018-29734-7</ext-link>, 2018.</mixed-citation></ref>

  </ref-list></back>
    <!--<article-title-html>Characterizing marshland compressibility  by an in-situ loading test: design and set-up  of an experiment in the Venice Lagoon</article-title-html>
<abstract-html><p>The fate of coastal marshlands in the near future will strongly depend on their capability to maintain their elevation above a rising mean sea level. Together with the deposition of inorganic sediments during high tides, organic soil production by halophytic vegetation, and organic matter decomposition, land subsidence due to natural soil compression is a major factor controlling the actual elevation of salt-marsh platforms. Due to their high porosity and compressibility, the marsh sedimentary body undergoes large compression because of the load of overlying more recent deposits. The characterization of the geotechnical properties of these deposits is therefore of paramount importance to quantify consolidation versus accretion and relative sea level rise. However, undisturbed sampling of this loose material is extremely challenging and lab tests on in-situ collected samples are not properly representative of in-situ conditions due to the scale effects in highly heterogeneous silty soils such as those of the Venice lagoon. To overcome this limitation, an in-situ loading test was carried out in the Lazzaretto Nuovo salt-marsh in the Venice Lagoon, Italy. The load is obtained by a number of plastic tanks that are filled with seawater, reaching a cumulative load of 40&thinsp;kN applied on a 2.5×1.8&thinsp;m<sup>2</sup> surface. Specific instrumentations were deployed before positioning the tanks to measure soil vertical displacement at various depths below the load (0, 10, and 50&thinsp;cm) and distances (0, 40, and 80&thinsp;cm) from the load centre. Moreover, six pressure transducers were used to record overpressure dissipation over time. The collected datasets will be interpreted through a 3-D flow-deformation model that, once calibrated, provides reliable estimates of the compressibility values for each monitored depth interval.</p></abstract-html>
<ref-html id="bib1.bib1"><label>1</label><mixed-citation>
Allen, J. R. L.: Geological impact on coastal wetland landscapes: some general effects of sediment auto-compaction in the Holocene of northwest Europe, Holocene, 9, 1–12, <a href="https://doi.org/10.1191/095968399674929672" target="_blank">https://doi.org/10.1191/095968399674929672</a>, 1999.
</mixed-citation></ref-html>
<ref-html id="bib1.bib2"><label>2</label><mixed-citation>
Amos, C. L., Umgiesser, G., Tosi, L., and Townend, I. H.: The coastal
morphodynamics of Venice lagoon, Italy: An introduction, Cont. Shelf Res., 30, 837–846, <a href="https://doi.org/10.1016/j.csr.2010.01.014" target="_blank">https://doi.org/10.1016/j.csr.2010.01.014</a>, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib3"><label>3</label><mixed-citation>
Biscontin, G., Cola, S., Pestana, J. M., and Simonini, P.: Unified compression model for Venice lagoon natural silts, J. Geotech. Geoenviron. Eng., 133, 932–942, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib4"><label>4</label><mixed-citation>
Brain, M. J., Kemp, A. C., Horton, B. P., Culver, S. J., Parnell, A. C., and
Cahill, N.: Quantifying the contribution of sediment compaction to late Holocene salt-marsh sea-level reconstruction, North-Carolina, USA,
Quaternary Res., 83, 1151, <a href="https://doi.org/10.1016/j.yqres.2014.08.003" target="_blank">https://doi.org/10.1016/j.yqres.2014.08.003</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib5"><label>5</label><mixed-citation>
Brain, M. J., Kemp, A. C., Hawkes, A. D., Engelhart, S. E., Vane, C. H., Cahill, N., Hill, T. D., Donnelly, J. P., and Horton, B. P.: Exploring
mechanisms of compaction in salt-marsh sediments using Common Era relative
sea-level reconstructions, Quaternary Sci. Rev., 167, 96–111,
<a href="https://doi.org/10.1016/j.sedgeo.2010.10.005" target="_blank">https://doi.org/10.1016/j.sedgeo.2010.10.005</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib6"><label>6</label><mixed-citation>
Cahoon, D. R., Lynch, J. C., Hensel, P., Boumans, R., Perez, B. C., Segura, B., and Day Jr., J. W.: High-precision measurements of wetland sediment elevation: 1. Recent improvements to the sedimentation-erosion table, J. Sediment Res., 72, 730–733, <a href="https://doi.org/10.1306/020702720730" target="_blank">https://doi.org/10.1306/020702720730</a>, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib7"><label>7</label><mixed-citation>
Cola, S. and Simonini, P.: Mechanical behavior of silty soils of the Venice
lagoon as a function of their grading characteristics, Can. Geotech. J., 39, 879–893, 2002.
</mixed-citation></ref-html>
<ref-html id="bib1.bib8"><label>8</label><mixed-citation>
Cola, S., Sanavia, L., Simonini, P., and Schrefler, B. A.: Coupled thermohydromechanical analysis of Venice lagoon salt marshes, Water Resour. Res., 44, W00C05, <a href="https://doi.org/10.1029/2007WR006570" target="_blank">https://doi.org/10.1029/2007WR006570</a>, 2008.
</mixed-citation></ref-html>
<ref-html id="bib1.bib9"><label>9</label><mixed-citation>
Da Lio, C., D'Alpaos, A., and Marani, M.: The secret gardener: vegetation and the emergence of biogeomorphic patterns in tidal environments, Philos. T. Roy. Soc. A, 371, 20120367, <a href="https://doi.org/10.1098/rsta.2012.0367" target="_blank">https://doi.org/10.1098/rsta.2012.0367</a>, 2013.
</mixed-citation></ref-html>
<ref-html id="bib1.bib10"><label>10</label><mixed-citation>
Da Lio, C., Teatini, P., Strozzi, T., and Tosi, L.: Understanding land subsidence in salt marshes of the Venice Lagoon from SAR Interferometry and
ground-based investigations, Remote Sens. Environ., 205, 56–70,
<a href="https://doi.org/10.1016/j.rse.2017.11.016" target="_blank">https://doi.org/10.1016/j.rse.2017.11.016</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib11"><label>11</label><mixed-citation>
D'Alpaos, A. and Marani, M.: Reading the signatures of biologic-geomorphic
feedbacks in salt-marsh landscapes, Adv. Water Resour., 93, 265–275, <a href="https://doi.org/10.1016/j.advwatres.2015.09.004" target="_blank">https://doi.org/10.1016/j.advwatres.2015.09.004</a>, 2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib12"><label>12</label><mixed-citation>
Jankowski, K. L., Törnqvist, T. E., and Fernandes, A. M.: Vulnerability of Louisiana's coastal wetlands to present-day rates of relative sea-level
rise, Nat. Commun., 8, 14792, <a href="https://doi.org/10.1038/ncomms14792" target="_blank">https://doi.org/10.1038/ncomms14792</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib13"><label>13</label><mixed-citation>
Lesser, G. R., Roelvink, J. A., van Kester, J. A. T. M., and Stelling, G. S.: Development and validation of a three-dimensional morphological model, Coast. Eng., 51, 883–915, <a href="https://doi.org/10.1016/j.coastaleng.2004.07.014" target="_blank">https://doi.org/10.1016/j.coastaleng.2004.07.014</a>, 2004.
</mixed-citation></ref-html>
<ref-html id="bib1.bib14"><label>14</label><mixed-citation>
Marani, M., D'Alpaos, A., Lanzoni, S., Carniello, L., and Rinaldo, A.: The
importance of being coupled: Stable states and catastrophic shifts in tidal
bio-morphodynamics, J. Geophys. Res., 115, F04004, <a href="https://doi.org/10.1029/2009JF001600" target="_blank">https://doi.org/10.1029/2009JF001600</a>, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib15"><label>15</label><mixed-citation>
Marani, M., D'Alpaos, A., Lanzoni, S., and Santalucia, M.: Understanding and
predicting wave erosion of marsh edge, Geophys. Res. Lett., 38, L21401,
<a href="https://doi.org/10.1029/2011GL048995" target="_blank">https://doi.org/10.1029/2011GL048995</a>, 2011.
</mixed-citation></ref-html>
<ref-html id="bib1.bib16"><label>16</label><mixed-citation>
Morton, R. A., Ward, G. H., and White, W. A.: Rates of sediment supply and
sea-level rise in a large coastal lagoon, Mar. Geol., 167, 261–284,
<a href="https://doi.org/10.1016/S0025-3227(00)00030-X" target="_blank">https://doi.org/10.1016/S0025-3227(00)00030-X</a>, 2000.
</mixed-citation></ref-html>
<ref-html id="bib1.bib17"><label>17</label><mixed-citation>
Rizzetto, F. and Tosi, L.: Aptitude of modern salt marshes to counteract
relative sea-level rise, Venice Lagoon (Italy), Geology, 39, 755–758,
<a href="https://doi.org/10.1130/G31736.1" target="_blank">https://doi.org/10.1130/G31736.1</a>, 2011.
</mixed-citation></ref-html>
<ref-html id="bib1.bib18"><label>18</label><mixed-citation>
Serandrei-Barbero, R., Albani, A., Donnici, S., and Rizzetto, F.: Past and
recent sedimentation rates in the Lagoon of Venice (Northern Italy), Estuar.
Coast. Shelf Sci., 69, 255–269, <a href="https://doi.org/10.1016/j.ecss.2006.04.018" target="_blank">https://doi.org/10.1016/j.ecss.2006.04.018</a>, 2006.

</mixed-citation></ref-html>
<ref-html id="bib1.bib19"><label>19</label><mixed-citation>
Tonni, L., Cola, S., and Pastor, M.: A generalized plasticity approach for
describing the behaviour of silty soils forming the Venetian lagoon basin, in: Proc. of the 6th Eur. Conf. on Numerical Methods in Geotechnical
Engineering, 6–8 September 2006, Graz, Austria, 93–99, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib20"><label>20</label><mixed-citation>
Törnqvist, T. E., Wallace, D. J., Storms, J. E. A., Wallinga, J., Dam, R. L., Blaauw, M., Derksen, M. S., Klerks, C. J. W., Meijneken, C., A., and Snijders, E. M. A.: Mississippi Delta subsidence primarily caused by compaction of Holocene strata, Nat. Geosci., 1, 173–176, <a href="https://doi.org/10.1038/ngeo129" target="_blank">https://doi.org/10.1038/ngeo129</a>, 2008.
</mixed-citation></ref-html>
<ref-html id="bib1.bib21"><label>21</label><mixed-citation>
van Asselen, S., Karssenberg, D., and Stouthamer, E.: Contribution of peat
compaction to relative sea-level rise within Holocene deltas, Geophys. Res.
Lett., 38, L24401, <a href="https://doi.org/10.1029/2011GL049835" target="_blank">https://doi.org/10.1029/2011GL049835</a>, 2011.
</mixed-citation></ref-html>
<ref-html id="bib1.bib22"><label>22</label><mixed-citation>
Zoccarato, C. and Teatini, P.: Numerical simulations of Holocene salt-marsh
dynamics under the hypothesis of large soil deformations, Adv. Water Resour.,
110, 107–119, <a href="https://doi.org/10.1016/j.advwatres" target="_blank">https://doi.org/10.1016/j.advwatres</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib23"><label>23</label><mixed-citation>
Zoccarato, C., Minderhoud, P. S. J., and Teatini, P.: The role of sedimentation and natural compaction in a prograding delta: Insights from the mega Mekong delta, Vietnam, Scient. Rep., 8, 11437, <a href="https://doi.org/10.1038/s41598-018-29734-7" target="_blank">https://doi.org/10.1038/s41598-018-29734-7</a>, 2018.
</mixed-citation></ref-html>--></article>
