<?xml version="1.0" encoding="UTF-8"?>
<!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing with OASIS Tables v3.0 20080202//EN" "journalpub-oasis3.dtd">
<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-382-689-2020</article-id><title-group><article-title>Vulnerability of Venice's coastland to <?xmltex \hack{\break}?>relative sea-level rise</article-title><alt-title>Vulnerability of Venice's coastland</alt-title>
      </title-group><?xmltex \runningtitle{Vulnerability of Venice's coastland}?><?xmltex \runningauthor{L.~Tosi et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="yes" rid="aff1">
          <name><surname>Tosi</surname><given-names>Luigi</given-names></name>
          <email>luigi.tosi@igg.cnr.it</email>
        <ext-link>https://orcid.org/0000-0001-5254-4059</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="aff1">
          <name><surname>Donnici</surname><given-names>Sandra</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff3">
          <name><surname>Strozzi</surname><given-names>Tazio</given-names></name>
          
        <ext-link>https://orcid.org/0000-0002-9054-951X</ext-link></contrib>
        <contrib contrib-type="author" corresp="no" rid="aff4">
          <name><surname>Teatini</surname><given-names>Pietro</given-names></name>
          
        </contrib>
        <aff id="aff1"><label>1</label><institution>Institute of Geosciences and Earth Resources, National Research
Council, Padova, 35131, Italy</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>Institute of Marine Sciences, National Research Council, Venice,
30122, Italy</institution>
        </aff>
        <aff id="aff3"><label>3</label><institution>Gamma Remote Sensing, Gümligen, 3073, Switzerland</institution>
        </aff>
        <aff id="aff4"><label>4</label><institution>Dept. of Civil, Environmental and Architectural Engineering,
University of Padova, Padova, 35131, Italy</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Luigi Tosi (luigi.tosi@igg.cnr.it)</corresp></author-notes><pub-date><day>22</day><month>April</month><year>2020</year></pub-date>
      
      <volume>382</volume>
      <fpage>689</fpage><lpage>695</lpage>
      
      <permissions>
        <copyright-statement>Copyright: © 2020 Luigi Tosi 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/382/689/2020/piahs-382-689-2020.html">This article is available from https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020.html</self-uri><self-uri xlink:href="https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020.pdf">The full text article is available as a PDF file from https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020.pdf</self-uri>
      <abstract><title>Abstract</title>
    <p id="d1e126">Relative sea-level rise (RSLR), i.e. sea-level rise due
to climate changes combined with land subsidence, is one of the processes
that is most severely threatening the coastal systems around the world. The
Venice coastland forms the major low-lying area in Italy and encompasses a
variety of environments, such as farmlands, estuaries, deltas, lagoons and
urbanized areas. Valuable ecosystems, historical heritages and economic
activities are located in this area. Since most of the territory lies at a
ground elevation below or slightly above the mean sea-level, also a few
mm yr<inline-formula><mml:math id="M1" 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> of land subsidence can seriously impacts on the Venice coastal system.
In this study, we present an analysis of the vulnerability to RSLR
considering an uneven land subsidence distribution, with an application on
the Venice coastland. The analysis is delineated at the regional scale by an
index-based model and a proper coupling of various thematic layers, such as
high spatial resolution land subsidence data retrieved by satellite SAR
interferometry, ongoing and projected sea-level rise trends, and
morpho-physiographic setting of the coastland.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Introduction</title>
      <p id="d1e150">Sea-level rise due to climate changes (SLR) combined with land subsidence,
namely relative sea-level rise (RSLR), is one of the processes that is
threatening most severely the coastal systems around the world. Flooding,
saltwater contamination of farmlands and aquifers, coastal erosion, loss of
tidal morphologies along with severe damages to infrastructures are among
the major effects of RSLR.</p>
      <p id="d1e153">Although at different rates, the ocean levels increased over the last
decades up to a few mm yr<inline-formula><mml:math id="M2" 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 are expected to rise even more quickly by the
end of the century (e.g., IPCC, 2014). Despite this general rise, land
subsidence in many coastlands worldwide has exceeded the SLR up to a factor
of ten (Erkens et al., 2015).</p>
      <p id="d1e168">At regional scales, SLR can be considered spatially homogeneous whereas
ground dynamics is often characterized by a considerable variability. During
the last decade, the growing use of satellite SAR interferometry over large
areas reveled that land subsidence in low-lying coastlands often depicts
uneven distribution patterns, primarily controlled by shallow sediment
compaction, especially the Holocene deposits (Tosi et al., 2010; Teatini et
al., 2011; Jankowski et al., 2017), and the hydro-morphological setting.
These are key driving mechanisms in the susceptibility of the low-lying
coastal plains to RSLR</p>
      <p id="d1e171">Vulnerability analysis is a powerful method for studying the interaction of
the various environmental features that determine the exposure of coastlands
to RSLR (e.g., Gornitz, 1991). However, previous investigations neglected or
poorly considered the variability of the coastal subsidence, generally
assuming a quite homogeneous sinking trend also over large areas, or at
least with a regional pattern.</p>
      <p id="d1e175">Here we present a step forward in the analysis of the vulnerability to RSLR
of the Venice coastal system (Fig. 1), considering the actual pattern of the
coastal subsidence (e.g., Teatini et al., 2011; Strozzi et al., 2013; Tosi
et al., 2016).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F1"><?xmltex \currentcnt{1}?><label>Figure 1</label><caption><p id="d1e180">Satellite image of the Venice coastland facing the northern
Adriatic Sea, Italy. Red line: boundary of the study area in the mainland;
Blue lines: major rivers; Green polygons: lagoon boundaries. Base map
source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS,
USDA, USGS, Aerogrid, IGN, and the GIS User Community.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020-f01.png"/>

      </fig>

      <p id="d1e189">The analysis is conducted at the regional scale by combining high spatial
resolution ground movement data obtained<?pagebreak page690?> through multi-temporal SAR
interferometry with information on the hydro-morphological setting of the
coastal system and the present and projected sea-level rise trends.</p>
</sec>
<sec id="Ch1.S2">
  <label>2</label><title>Data and Methodology</title>
      <p id="d1e200">The coastal vulnerability to RSLR was assessed by means of an index-based
model that considers the following input dataset: high spatial resolution
land subsidence; hydro-morphological setting, including the distance of
emerged land from potential pathways for inundation due to RSLR, i.e. the
coastline, watercourses, lagoons and wetlands; surface elevation of emerged
and submerged sectors; present and projected sea-level rise.</p>
<sec id="Ch1.S2.SS1">
  <label>2.1</label><title>Land subsidence dataset</title>
      <p id="d1e210">Ground movements are derived from a stack of 194 Sentinel-1 images
(<inline-formula><mml:math id="M3" display="inline"><mml:mrow><mml:mo>∼</mml:mo><mml:mn mathvariant="normal">3</mml:mn><mml:mo>×</mml:mo><mml:mn mathvariant="normal">20</mml:mn></mml:mrow></mml:math></inline-formula> m spatial resolution) acquired between
30 March 2015 and 23 February 2019 processed with the Interferometric Point Target
Analysis (IPTA) PSI chain (e.g., Wegmüller et al., 2004). Permanent GPS
stations located within the study area allowed calibration and validation of
the interferometric product. The line of sight (LOS) displacements detected
by the satellite have been assumed as to the ground vertical movements to
simplify the analysis. This assumption introduces an error in the range of
20 %–25 % for the ground movement velocities, which can be reasonably
neglected considering the intervals of the thematic layer classification
adopted for the vulnerability analysis to RSLR.</p>
</sec>
<sec id="Ch1.S2.SS2">
  <label>2.2</label><title>Hydro-morphological data</title>
      <p id="d1e235">The hydro-morphological dataset includes the ground elevation of emerged and
submerged areas and the physiographic setting of the major water bodies
considered as the main potential flooding sources.</p>
      <p id="d1e238">The ground elevations data of emerged areas refers to a 20 m pixel size
Digital Elevation Model (DEM). The DEM was obtained by Wegmüller et al. (2009)
using SAR cross-interferometry on four pairs of satellite images as part of
the ERS2-ENVISAT tandem mission in winter 2007, 2008 and 2009, i.e. the
season with the lowest presence of vegetation, and validated on the basis of
GPS surveys (Gasparetto-Stori et al., 2012).</p>
      <p id="d1e241">The bathymetric data are available from reclamation and regional authorities
and refers to the main lagoon basins.</p>
      <p id="d1e244">The potential flooding sources are the Adriatic Sea, lagoons, wetlands and
the main rivers. The boundaries and paths of the water bodies were drawn
manually using images from Google Earth.</p>
</sec>
<sec id="Ch1.S2.SS3">
  <label>2.3</label><title>Sea-level rise scenarios</title>
      <p id="d1e255">Three SLR rates were adopted, i.e. the ongoing long-time series scenario, ongoing short-time series scenario and future scenario, referring to the time intervals
1875–2018, 1992–2018 and 2018–2050, respectively. The SLR rates for the
ongoing long-time series scenario and ongoing short-time series scenario amount to 1.3 and 3.8 mm yr<inline-formula><mml:math id="M4" 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>, respectively, and  were computed from the
data recorded by the tide gauge station of Trieste (Northern Adriatic Sea).
Since this station is located in an area where land movements are known to
be negligible, the records are representative of the sea level changes.
Regarding the future scenario, this study adopts the worst-case projection of global mean
sea-level rise provided by the IPCC's Fifth Assessment Report (AR5) (IPCC,
2014). Under the Representative Concentration Pathway RCP8.5 scenario, a
sea-level rise of 0.74 m with a likely range of 0.52 to 0.98 m (Church et
al., 2013) is projected by 2100. For the future scenario, a mean rate of 5 mm yr<inline-formula><mml:math id="M5" 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> by 2050 is
consequently used.</p>
</sec>
<sec id="Ch1.S2.SS4">
  <label>2.4</label><title>Index-based model</title>
      <p id="d1e291">The vulnerability to RSLR was assessed by the following steps: (a) Set-up of
the thematic layers derived from the selected indices (i.e. land subsidence,
water distance and DEM); (b) Classification of the thematic layers; (c) Assignment of a weigh to each index; (d) Aggregation of the thematic layers
into a GIS environment; (e) Computation and classification of vulnerability
to RSLR.</p>
      <?pagebreak page691?><p id="d1e294">The thematic layers SUBS (land subsidence), DEM (integrated ground elevation and
bathymetric dataset) and WD (water distance) were set up through the
interpolation of the associated indices by the kriging technique.
Specifically, a 200 m regular grid was chosen as it is a good compromise for
mapping both high density data areas (e.g., urban areas) and sectors where
SAR reflectors are diffused (e.g., farmlands and wetlands).</p>
      <p id="d1e297">The three SLR rates were included in the SUBS layer for obtaining the RSUBS thematic
layers corresponding to the different scenarios. SUBS rates were kept the same
for the three scenarios, assuming that the groundwater regulation will
prevent future increase in induced land sinking and the secondary
consolidation rates of Holocene deposits will remain unchanged during such a
relatively short time period (e.g., Teatini et al., 2011).</p>
      <p id="d1e300">The DEM dataset consists in measurements carried out over various time spans
with a common mid-range year around 2008. Because land subsidence is
referred to the 2015–2019 period, the DEM dataset was updated by adding the
contribution due to ground displacements and SLR for the time interval
2008–2019. The land subsidence trend is assumed to remain unchanged before
2015.</p>
      <p id="d1e304">In addition, depending on the investigated scenario, the DEM layer was computed
by two different approaches. For the ongoing scenarios, DEM represents the present coastland
elevation estimated for the year 2019. For the future scenario, i.e. in 2050, the DEM is
estimated as in Eq. (1):
            <disp-formula id="Ch1.E1" content-type="numbered"><label>1</label><mml:math id="M6" display="block"><mml:mtable columnspacing="1em" class="split" rowspacing="0.2ex" displaystyle="true" columnalign="right left"><mml:mtr><mml:mtd><mml:mrow><mml:msub><mml:mtext>DEM</mml:mtext><mml:mn mathvariant="normal">2050</mml:mn></mml:msub><mml:mo>=</mml:mo></mml:mrow></mml:mtd><mml:mtd><mml:mrow><mml:mo>(</mml:mo><mml:msub><mml:mtext>DEM</mml:mtext><mml:mn mathvariant="normal">2019</mml:mn></mml:msub><mml:mo>)</mml:mo><mml:mo>+</mml:mo><mml:mo>(</mml:mo><mml:msub><mml:mtext>SUBS</mml:mtext><mml:mn mathvariant="normal">2019</mml:mn></mml:msub><mml:mo>⋅</mml:mo><mml:mi mathvariant="normal">Δ</mml:mi><mml:mi>t</mml:mi><mml:mo>)</mml:mo></mml:mrow></mml:mtd></mml:mtr><mml:mtr><mml:mtd><mml:mrow><mml:mo>-</mml:mo></mml:mrow></mml:mtd><mml:mtd><mml:mrow><mml:mo>(</mml:mo><mml:msub><mml:mtext>SLR</mml:mtext><mml:mn mathvariant="normal">2050</mml:mn></mml:msub><mml:mo>⋅</mml:mo><mml:mi mathvariant="normal">Δ</mml:mi><mml:mi>t</mml:mi><mml:mo>)</mml:mo></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
          where <inline-formula><mml:math id="M7" display="inline"><mml:mrow><mml:mi mathvariant="normal">Δ</mml:mi><mml:mi>t</mml:mi></mml:mrow></mml:math></inline-formula> is the interval period between 2019 and 2050.</p>
      <p id="d1e383">The thematic layers were classified by converting their values to an
“importance” scale using a rating from 0 to 4 (e.g., Gornitz, 1991). The
classification depends on local conditions, with high ratings corresponding
to high impact of RSLR. The upper and lower bounds of the classes for the
thematic layers were defined by adapting the limit values to the frequency
distribution of the gridded dataset. The WD index is assumed to remain
unchanged by 2050, as it is reasonable to believe that mitigation measures
(e.g. beach nourishment, embankment reinforcing) will keep the boundaries of
the water bodies roughly at present.</p>

<?xmltex \floatpos{t}?><table-wrap id="Ch1.T1"><?xmltex \currentcnt{1}?><label>Table 1</label><caption><p id="d1e389">Range of scores and weightings assigned to each classified thematic
layer.</p></caption><oasis:table frame="topbot"><oasis:tgroup cols="4">
     <oasis:colspec colnum="1" colname="col1" align="left"/>
     <oasis:colspec colnum="2" colname="col2" align="left"/>
     <oasis:colspec colnum="3" colname="col3" align="right"/>
     <oasis:colspec colnum="4" colname="col4" align="right"/>
     <oasis:thead>
       <oasis:row>
         <oasis:entry colname="col1">Thematic</oasis:entry>
         <oasis:entry colname="col2">Classified thematic</oasis:entry>
         <oasis:entry colname="col3">Score</oasis:entry>
         <oasis:entry colname="col4">Weight</oasis:entry>
       </oasis:row>
       <oasis:row rowsep="1">
         <oasis:entry colname="col1">layer</oasis:entry>
         <oasis:entry colname="col2">layer</oasis:entry>
         <oasis:entry colname="col3"/>
         <oasis:entry colname="col4"/>
       </oasis:row>
     </oasis:thead>
     <oasis:tbody>
       <oasis:row>
         <oasis:entry colname="col1">RSUBS</oasis:entry>
         <oasis:entry colname="col2">cRSUBS</oasis:entry>
         <oasis:entry colname="col3">0–4</oasis:entry>
         <oasis:entry colname="col4">0.5</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">WD</oasis:entry>
         <oasis:entry colname="col2">cWD</oasis:entry>
         <oasis:entry colname="col3">0–4</oasis:entry>
         <oasis:entry colname="col4">0.25</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">DEM</oasis:entry>
         <oasis:entry colname="col2">cDEM</oasis:entry>
         <oasis:entry colname="col3">0–4</oasis:entry>
         <oasis:entry colname="col4">0.25</oasis:entry>
       </oasis:row>
     </oasis:tbody>
   </oasis:tgroup></oasis:table></table-wrap>

      <p id="d1e485">Finally, the Index of Coastal Vulnerability (CVI) to RSLR was computed with a
weighted linear regression for both the ongoing and future scenarios as in Eq. (2):
            <disp-formula id="Ch1.E2" content-type="numbered"><label>2</label><mml:math id="M8" display="block"><mml:mtable rowspacing="0.2ex" class="split" columnspacing="1em" displaystyle="true" columnalign="right left"><mml:mtr><mml:mtd><mml:mrow><mml:msub><mml:mtext>CVI</mml:mtext><mml:mi>i</mml:mi></mml:msub><mml:mo>=</mml:mo></mml:mrow></mml:mtd><mml:mtd><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>RSUBS</mml:mtext></mml:msub><mml:mo>⋅</mml:mo><mml:msub><mml:mtext>cRSUBS</mml:mtext><mml:mi>i</mml:mi></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mi>w</mml:mi><mml:mtext>WD</mml:mtext></mml:msub><mml:mo>⋅</mml:mo><mml:msub><mml:mtext>cWD</mml:mtext><mml:mi>i</mml:mi></mml:msub></mml:mrow></mml:mtd></mml:mtr><mml:mtr><mml:mtd><mml:mrow><mml:mo>+</mml:mo></mml:mrow></mml:mtd><mml:mtd><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>DEM</mml:mtext></mml:msub><mml:mo>⋅</mml:mo><mml:msub><mml:mtext>cDEM</mml:mtext><mml:mi>i</mml:mi></mml:msub></mml:mrow></mml:mtd></mml:mtr></mml:mtable></mml:math></disp-formula>
          where cRSUBS, cWD, cDEM are the rating for each cell <inline-formula><mml:math id="M9" display="inline"><mml:mi>i</mml:mi></mml:math></inline-formula> of the classified thematic layers and
<inline-formula><mml:math id="M10" display="inline"><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>SUBS</mml:mtext></mml:msub><mml:mo>,</mml:mo><mml:msub><mml:mi>w</mml:mi><mml:mtext>WD</mml:mtext></mml:msub></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M11" display="inline"><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>DEM</mml:mtext></mml:msub></mml:mrow></mml:math></inline-formula> are the assigned subjective weights as shown in
Table 1. Note that the weight of RSUBS (<inline-formula><mml:math id="M12" display="inline"><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>RSUBS</mml:mtext></mml:msub><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula>is double those associated to
<inline-formula><mml:math id="M13" display="inline"><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>W</mml:mtext></mml:msub></mml:mrow></mml:math></inline-formula> and <inline-formula><mml:math id="M14" display="inline"><mml:mrow><mml:msub><mml:mi>w</mml:mi><mml:mtext>DEM</mml:mtext></mml:msub></mml:mrow></mml:math></inline-formula>, as high subsidence rates and projected SLR trends are
the major driving forces affecting delta vulnerability.</p>
      <p id="d1e623">Lastly, the CVI values obtained from Eq. (2) were reclassified into five
classes (from negligible to extreme) by the Jenks optimization method
(Jenks, 1967), which reduces variance within classes and maximizes variance
between them.</p>
</sec>
</sec>
<sec id="Ch1.S3">
  <label>3</label><title>Results</title>
      <p id="d1e635">The set-up of the SUBS, RSUBS, DEM and WD thematic layers was the first step of the data
analysis. The maps developed on the 200 m regular grid are shown in Fig. 2.</p>
      <p id="d1e638">The SUBS thematic layer clearly depicts the variability of the ground displacements
although the SAR data are interpolated on the 200 m grid. In general, this
pattern is primarily controlled by compaction of the Holocene deposits,
which thickness increases from less than 1 m in the mainland to more than 20 m in the northern and southern coastal sectors (Tosi et al., 2010). The
presence of buried geomorphological features, such as sandy paleo-channel
and littoral ridge systems contributes in increasing the local variabilities
patterns. To the author knowledge, induced land subsidence due to
groundwater exploitation is limited to local sectors in the northern area.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F2"><?xmltex \currentcnt{2}?><label>Figure 2</label><caption><p id="d1e643">Thematic layers: <bold>(a)</bold> SUBS, <bold>(b)</bold> RSUBS – ongoing long-time series scenario, <bold>(c)</bold> RSUBS – ongoing short-time series scenario, <bold>(d)</bold> RSUBS – future scenario, <bold>(e)</bold> DEM, <bold>(f)</bold> DEM – future scenario, <bold>(g)</bold> WD.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020-f02.png"/>

      </fig>

      <p id="d1e675">The thematic layer has been classified based on the statistical distribution
of the RSUBS, WD, and DEM values (Table 2).</p>

<?xmltex \floatpos{t}?><table-wrap id="Ch1.T2"><?xmltex \currentcnt{2}?><label>Table 2</label><caption><p id="d1e681">Thematic layer classification: upper and lower bounds of the
classes and related scores.</p></caption><oasis:table frame="topbot"><?xmltex \begin{scaleboxenv}{.97}[.97]?><oasis:tgroup cols="5">
     <oasis:colspec colnum="1" colname="col1" align="left"/>
     <oasis:colspec colnum="2" colname="col2" align="right"/>
     <oasis:colspec colnum="3" colname="col3" align="right"/>
     <oasis:colspec colnum="4" colname="col4" align="right"/>
     <oasis:colspec colnum="5" colname="col5" align="right"/>
     <oasis:thead>
       <oasis:row>
         <oasis:entry colname="col1">RSUBS</oasis:entry>
         <oasis:entry colname="col2">WD</oasis:entry>
         <oasis:entry colname="col3">DEMma</oasis:entry>
         <oasis:entry colname="col4">DEMla</oasis:entry>
         <oasis:entry colname="col5">Score</oasis:entry>
       </oasis:row>
       <oasis:row rowsep="1">
         <oasis:entry colname="col1">(mm yr<inline-formula><mml:math id="M15" 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>)</oasis:entry>
         <oasis:entry colname="col2">(m)</oasis:entry>
         <oasis:entry colname="col3">(m a.m.s.l.)</oasis:entry>
         <oasis:entry colname="col4">(m a.m.s.l.)</oasis:entry>
         <oasis:entry colname="col5"/>
       </oasis:row>
     </oasis:thead>
     <oasis:tbody>
       <oasis:row>
         <oasis:entry colname="col1"><inline-formula><mml:math id="M16" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col2"><inline-formula><mml:math id="M17" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mn mathvariant="normal">4000</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col3"><inline-formula><mml:math id="M18" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mn mathvariant="normal">4</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col4"><inline-formula><mml:math id="M19" display="inline"><mml:mrow><mml:mo>&lt;</mml:mo><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col5">0</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1"><inline-formula><mml:math id="M20" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M21" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col2">2000–4000</oasis:entry>
         <oasis:entry colname="col3">2–4</oasis:entry>
         <oasis:entry colname="col4"><inline-formula><mml:math id="M22" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M23" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">2</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col5">1</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1"><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">3</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col2">1000–2000</oasis:entry>
         <oasis:entry colname="col3">1–2</oasis:entry>
         <oasis:entry colname="col4"><inline-formula><mml:math id="M26" 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="M27" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col5">2</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1"><inline-formula><mml:math id="M28" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">3</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M29" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">7</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col2">500–1000</oasis:entry>
         <oasis:entry colname="col3">0–1</oasis:entry>
         <oasis:entry colname="col4"><inline-formula><mml:math id="M30" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula> to <inline-formula><mml:math id="M31" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.5</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col5">3</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1"><inline-formula><mml:math id="M32" display="inline"><mml:mrow><mml:mo>&lt;</mml:mo><mml:mo>-</mml:mo><mml:mn mathvariant="normal">7</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col2"><inline-formula><mml:math id="M33" display="inline"><mml:mrow><mml:mo>&lt;</mml:mo><mml:mn mathvariant="normal">500</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col3"><inline-formula><mml:math id="M34" display="inline"><mml:mrow><mml:mo>&lt;</mml:mo><mml:mn mathvariant="normal">0</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col4"><inline-formula><mml:math id="M35" display="inline"><mml:mrow><mml:mo>&gt;</mml:mo><mml:mo>-</mml:mo><mml:mn mathvariant="normal">0.5</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
         <oasis:entry colname="col5">4</oasis:entry>
       </oasis:row>
     </oasis:tbody>
   </oasis:tgroup><?xmltex \end{scaleboxenv}?></oasis:table></table-wrap>

      <p id="d1e1023">The values 0 and 4 mean a low and a high contribution to vulnerability,
respectively. Considering the peculiarity of the Venice area, whose
territory lies at an elevation below or slightly above the mean sea-level,
also a few mm yr<inline-formula><mml:math id="M36" display="inline"><mml:msup><mml:mi/><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1<?pagebreak page692?></mml:mn></mml:mrow></mml:msup></mml:math></inline-formula> of relative sea-level rise seriously damage the coastal
system. Therefore, the class with null value has been limited to RSLR less
than 1 mm yr<inline-formula><mml:math id="M37" 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>. In addition, since RSLR differently affects the ecosystem of
transitional environments, the DEM thematic layer has been classified
separately for the mainland (littoral strips included) and lagoon areas
(islands included), hereinafter referred as DEMma and DEMla, respectively.
Specifically, in the lagoon areas, RSLR threats the morphologies with a
surface elevation within the tidal range (e.g., salt marshes) and above sea
level (e.g. islands and historical centers) more than the lagoon bottom
deeper than <inline-formula><mml:math id="M38" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:math></inline-formula> m a.m.s.l. (e.g., channels). Conversely, in the mainland,
the most threaten sectors are those with the lowest elevation with respect
to the sea level.</p>
      <p id="d1e1060">The adopted classification is the same for the three scenarios, since the
threat-classes are preserved even if subsidence and SLR change.</p>
      <p id="d1e1063">The classified thematic layers, with scores from 0 to 4 (from low to high
contribution to vulnerability), are shown in Fig. 3. The colour-coding
highlights the rating in accordance with the classification shown in Table 2.</p>
      <p id="d1e1067">The Index of Coastal Vulnerability (CVI) to RSLR was computed with a weighted
linear regression for both the ongoing and future scenarios (see Eq. 2) and the values reclassified
into five classes, i.e. negligible, marginal, moderate, critical, and
extreme.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3"><?xmltex \currentcnt{3}?><label>Figure 3</label><caption><p id="d1e1072">Classified thematic layers influencing vulnerability to RSLR:
cRSUBS for the ongoing long-time series scenario <bold>(a)</bold>, ongoing short-time series scenario <bold>(b)</bold>, future scenario <bold>(c)</bold>; cWD <bold>(d)</bold>; cDEM computed for both the ongoing long-time series and short-time series <bold>(e)</bold>, and for the
future scenario <bold>(f)</bold>.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020-f03.png"/>

      </fig>

      <p id="d1e1100">The maps showing the vulnerability to RSLR of the Venice coastland for the
ongoing long-time series scenario, ongoing short-time series scenario and future scenario in 2050 are presented in Fig. 4.</p>
</sec>
<?pagebreak page693?><sec id="Ch1.S4">
  <label>4</label><title>Discussion</title>
      <p id="d1e1111">The use of high spatial resolution land subsidence maps obtained by
Satellite SAR interferometry makes it possible to take a step forward in the
analysis of the vulnerability to RSLR with respect to previous works that
generally considered land subsidence quite homogeneous or with a region
trend.</p>
      <p id="d1e1114">The vulnerability analysis of Venice's coastland to RSLR presented here uses
thematic layers at 200 m spatial resolution (Figs. 2 and 3).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4"><?xmltex \currentcnt{4}?><label>Figure 4</label><caption><p id="d1e1119">Vulnerability to RSLR of the Venice coastal area: <bold>(a)</bold> ongoing long-time series scenario; <bold>(b)</bold> ongoing short-time series scenario; <bold>(c)</bold> future scenario in 2050. Base map source: Esri, DigitalGlobe, GeoEye, Earthstar
Geographics, CNES/Airbus DS, USDA, USGS, Aerogrid, IGN, and the GIS User
Community.</p></caption>
        <?xmltex \igopts{width=199.169291pt}?><graphic xlink:href="https://piahs.copernicus.org/articles/382/689/2020/piahs-382-689-2020-f04.png"/>

      </fig>

      <p id="d1e1138">Regarding the outcome of the vulnerability analysis (Fig. 4), the
percentages of the Venice coastland in each class of the CVI under the ongoing long-time series,
ongoing short-time series and future scenarios are summarized in Table 3.</p>

<?xmltex \floatpos{t}?><table-wrap id="Ch1.T3"><?xmltex \currentcnt{3}?><label>Table 3</label><caption><p id="d1e1144">Percentages of the Po delta area in each class of the <italic>CVI</italic> under the
three scenarios.</p></caption><oasis:table frame="topbot"><oasis:tgroup cols="4">
     <oasis:colspec colnum="1" colname="col1" align="left"/>
     <oasis:colspec colnum="2" colname="col2" align="right"/>
     <oasis:colspec colnum="3" colname="col3" align="right"/>
     <oasis:colspec colnum="4" colname="col4" align="right"/>
     <oasis:thead>
       <oasis:row>
         <oasis:entry colname="col1"/>
         <oasis:entry rowsep="1" namest="col2" nameend="col4" align="center">Scenario </oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">Vulnerability</oasis:entry>
         <oasis:entry colname="col2">Ongoing  long-</oasis:entry>
         <oasis:entry colname="col3">Ongoing  short-</oasis:entry>
         <oasis:entry colname="col4">Future</oasis:entry>
       </oasis:row>
       <oasis:row rowsep="1">
         <oasis:entry colname="col1">classes</oasis:entry>
         <oasis:entry colname="col2">time series</oasis:entry>
         <oasis:entry colname="col3">time series</oasis:entry>
         <oasis:entry colname="col4"/>
       </oasis:row>
     </oasis:thead>
     <oasis:tbody>
       <oasis:row>
         <oasis:entry colname="col1">Negligible</oasis:entry>
         <oasis:entry colname="col2">13.5</oasis:entry>
         <oasis:entry colname="col3">0.0</oasis:entry>
         <oasis:entry colname="col4">0.0</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">Marginal</oasis:entry>
         <oasis:entry colname="col2">30.5</oasis:entry>
         <oasis:entry colname="col3">16.0</oasis:entry>
         <oasis:entry colname="col4">15.0</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">Moderate</oasis:entry>
         <oasis:entry colname="col2">23.5</oasis:entry>
         <oasis:entry colname="col3">27.0</oasis:entry>
         <oasis:entry colname="col4">24.5</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">Critical</oasis:entry>
         <oasis:entry colname="col2">22.0</oasis:entry>
         <oasis:entry colname="col3">33.5</oasis:entry>
         <oasis:entry colname="col4">28.5</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">Extreme</oasis:entry>
         <oasis:entry colname="col2">10.5</oasis:entry>
         <oasis:entry colname="col3">23.5</oasis:entry>
         <oasis:entry colname="col4">32.0</oasis:entry>
       </oasis:row>
     </oasis:tbody>
   </oasis:tgroup></oasis:table></table-wrap>

      <p id="d1e1282">Under the ongoing long-time series scenario, the areas with negligible vulnerability to RSL cover
only 13.5 %. Areas with marginal, moderate and critical vulnerability are
more extended, amounting to 30.5 %, 23.5 % and 22 %, respectively. About
10 % of the coastland is in an extreme vulnerability condition. Using the
ongoing short-time series and future scenarios the areas with negligible class vanish and 27 %, 33 %, 23.5 % are the
percentages of areas with moderate, critical and extreme vulnerability,
respectively.</p>
      <p id="d1e1285">By 2050, under the future scenario, 60 % of the coastland will be in a critical and
extreme vulnerability condition.</p>
      <p id="d1e1288">At the coastland scale, the high variability of vulnerability to RSLR
reflects the variability of land subsidence, which superposes that due to
the hydro-morphology setting.</p>
      <p id="d1e1292">Land subsidence plays a key role resulting in the variability of the
vulnerability to RSLR. Land subsidence rates vary from less than 1 to about
5 mm yr<inline-formula><mml:math id="M39" 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>, with local peaks reaching 10 mm yr<inline-formula><mml:math id="M40" 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>. Thus also under future scenario in some
sectors of the Venice coastland land subsidence and sea-level rise of the
Adriatic Sea contribute equally by 2050.</p>
      <p id="d1e1319">It is important to highlight that the specific indices used here do not
exhaustively cover all of the various factors influencing the Venice
coastland in view of the expected RSLR and various assumptions based on the
scientific knowledge of the study area have been made to simplify the
analysis. Assumptions, along with classification and weighting criteria
inevitably lead to some degree of subjective judgments. The choice of the
SLR scenarios to be used in the analysis is a critical issue. Regarding the
present state, notice<?pagebreak page694?> that the yearly average value of sea level changes is
quite variable and is characterized by pseudo-cyclicity and oscillations
(e.g., Carbognin et al., 2010). Time series shorter than 50–60 years often
yield fuzzy and contradictory predictions. The 1.3 mm yr<inline-formula><mml:math id="M41" 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> average SLR over
the 1875–2018 time interval, i.e. the ongoing long-time series scenario, is certainly significant and robust
for the Adriatic Sea. However, the 3.8 mm yr<inline-formula><mml:math id="M42" 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> resulting from the 1992–2018
period, i.e. the ongoing short-time series scenario, shows a fairly uniform trend that could be more
representative for the present state. Regarding the future scenario, the uncertainty
characterizes the quantification of both the expected SLR and land
subsidence evolution. To this end, the expected scenario here considered is
limited to 2050, being an evolution model of land subsidence unavailable for
the study area and the large difference of the SLR projections by 2100. In
any case, it is possible to assume that land subsidence will continue in
accordance with the present trend because the groundwater regulation adopted
in Venice and the long-term secondary consolidation of the Holocene deposits
will remain almost unchanged over a relatively short period. Regarding the
global sea-level rise by 2050, a rate of 5 mm yr<inline-formula><mml:math id="M43" 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> computed from the IPCC
projections is adopted (IPCC, 2014).</p>
      <p id="d1e1358">In relation to the shoreline erosion and the sinking of the embankments, it
was assumed that over the next 30 years, beaches nourishment and land
reclamation will be able to keep pace with the RSLR.</p>
</sec>
<sec id="Ch1.S5" sec-type="conclusions">
  <label>5</label><title>Conclusions</title>
      <p id="d1e1370">The vulnerability to RSLR exhibits substantial variability among individual
areas reflecting the heterogeneity of land subsidence and the
hydro-morphology setting. The key results of this study are the following:</p>
      <p id="d1e1373">Land subsidence rates vary from less than 1 to more than 5 mm yr<inline-formula><mml:math id="M44" 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>. Thus, it
means that also under future scenario land subsidence in some sectors of the Venice
coastland contributes equally with the sea-level rise of the Adriatic Sea in
the vulnerability analysis.</p>
      <p id="d1e1388">Under the ongoing long-time series scenario, 30.5 %, 23.5 % and 22 % of the coastland area is classified with
marginal, moderate and critical vulnerability, respectively.</p>
      <p id="d1e1391">Under the future scenario, i.e. by 2050, the areas with critical and extreme vulnerability
are expected to cover 60 % of the Venice coastland.</p>
      <p id="d1e1395">Although this study represents a step forward in the assessment of the
vulnerability to RSLR of the Venice coastland, the authors are aware that
further studies will have to face the uncertainties not addressed in this
analysis.</p>
</sec>

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

      <p id="d1e1402">The majority of the data presented here
are from an ongoing and yet incomplete project. The datasets generated
during the current study are available from the corresponding author on
reasonable request. Data courtesy: (1) Sentinel-1 data from ESA and EU Copernicus Programme are free available through Copernicus Open Access Hub (https://scihub.copernicus.eu); (2) Bathymetric data are from Consorzio di Bonifica Delta del Po and Venice Water Authority.</p>
  </notes><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e1408">LT and CDL conceived the idea, designed the study concept and developed the analysis; TS processed SAR data; LT, CDL, PT wrote the manuscript with support by TS and SD.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e1414">The authors declare that they have no conflict of interest.</p>
  </notes><notes notes-type="sistatement"><title>Special issue statement</title>

      <p id="d1e1420">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="d1e1426">This work has been developed in the framework 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. This article is also a contribution to the International
Geoscience Programme Project 663 “Impact, Mechanism, Monitoring of Land
Subsidence in Coastal Cities”.</p></ack><ref-list>
    <title>References</title>

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    <!--<article-title-html>Vulnerability of Venice's coastland to relative sea-level rise</article-title-html>
<abstract-html><p>Relative sea-level rise (RSLR), i.e. sea-level rise due
to climate changes combined with land subsidence, is one of the processes
that is most severely threatening the coastal systems around the world. The
Venice coastland forms the major low-lying area in Italy and encompasses a
variety of environments, such as farmlands, estuaries, deltas, lagoons and
urbanized areas. Valuable ecosystems, historical heritages and economic
activities are located in this area. Since most of the territory lies at a
ground elevation below or slightly above the mean sea-level, also a few
mm&thinsp;yr<sup>−1</sup> of land subsidence can seriously impacts on the Venice coastal system.
In this study, we present an analysis of the vulnerability to RSLR
considering an uneven land subsidence distribution, with an application on
the Venice coastland. The analysis is delineated at the regional scale by an
index-based model and a proper coupling of various thematic layers, such as
high spatial resolution land subsidence data retrieved by satellite SAR
interferometry, ongoing and projected sea-level rise trends, and
morpho-physiographic setting of the coastland.</p></abstract-html>
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Wegmuller, U.: Dem of the Veneto plain by ERS2-ENVISAT cross interferometry,
edited by: Scappini, S. and Zapparoli, S., 7th EUREGEO, European Congress on Regional
Geoscientific Cartography and Information Systems, Centro Stampa Regione
Emilia-Romagna Publ, Vol. I, 345–350, 2012.

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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>
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Jenks, G. F.: The data model concept in statistical mapping, International
Yearbook of Cartography, 7, 186–190, 1967.
</mixed-citation></ref-html>
<ref-html id="bib1.bib9"><label>9</label><mixed-citation>
Strozzi, T., Teatini, P., Tosi, L., Wegmüller, U., and Werner, C.: Land
subsidence of natural transitional environments by satellite radar
interferometry on artificial reflectors, J. Geophys. Res.-Earth, 118,
1177–1191, <a href="https://doi.org/10.1002/jgrf.20082" target="_blank">https://doi.org/10.1002/jgrf.20082</a>, 2013.

</mixed-citation></ref-html>
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Teatini, P., Tosi, L., and Strozzi, T.: Quantitative evidence that compaction
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Italy, J. Geophys. Res., 116, B08407, <a href="https://doi.org/10.1029/2010JB008122" target="_blank">https://doi.org/10.1029/2010JB008122</a>, 2011.
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Tosi, L., Teatini, P., Strozzi, T., Carbognin, L., Brancolini, G., and
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over the last two decades, Rend. Fis. Acc. Lincei, 21, 115–129, <a href="https://doi.org/10.1007/s12210-010-0084-2" target="_blank">https://doi.org/10.1007/s12210-010-0084-2</a>, 2010.
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Tosi, L., Da Lio, C., Strozzi, T., and Teatini, P.: Combining L- and X-band
SAR interferometry to assess ground displacements in heterogeneous coastal
environments: the Po River Delta and Venice Lagoon, Italy, Remote Sens., 8,
308, <a href="https://doi.org/10.3390/rs8040308" target="_blank">https://doi.org/10.3390/rs8040308</a>, 2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib13"><label>13</label><mixed-citation>
Wegmüller, U., Werner, C., Strozzi, T., and Wiesmann, A.: Multitemporal
interferometric point target analysis,  Ser. Remote Sens., 3, 136–144, 2004.
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Wegmüller, U., Santoro, M., Werner, C., Strozzi, T., Wiesmann, A., and
Lengert, W.: DEM generation using ERS-ENVISAT interferometry, J. Appl.
Geophys., 69, 51–58, <a href="https://doi.org/10.1016/j.jappgeo.2009.04.002" target="_blank">https://doi.org/10.1016/j.jappgeo.2009.04.002</a>, 2009.
</mixed-citation></ref-html>--></article>
