<?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" article-type="research-article">
  <front>
    <journal-meta><journal-id journal-id-type="publisher">NHESS</journal-id><journal-title-group>
    <journal-title>Natural Hazards and Earth System Sciences</journal-title>
    <abbrev-journal-title abbrev-type="publisher">NHESS</abbrev-journal-title><abbrev-journal-title abbrev-type="nlm-ta">Nat. Hazards Earth Syst. Sci.</abbrev-journal-title>
  </journal-title-group><issn pub-type="epub">1684-9981</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/nhess-23-317-2023</article-id><title-group><article-title>Quantifying unequal urban resilience to rainfall across<?xmltex \hack{\break}?> China from
location-aware big data</article-title><alt-title>Rainfall across China from location-aware big data</alt-title>
      </title-group><?xmltex \runningtitle{Rainfall across China from location-aware big data}?><?xmltex \runningauthor{J. Qian et al.}?>
      <contrib-group>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Qian</surname><given-names>Jiale</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="yes" rid="aff1 aff2">
          <name><surname>Du</surname><given-names>Yunyan</given-names></name>
          <email>duyy@lreis.ac.cn</email>
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Yi</surname><given-names>Jiawei</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1">
          <name><surname>Liang</surname><given-names>Fuyuan</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Wang</surname><given-names>Nan</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Ma</surname><given-names>Ting</given-names></name>
          
        </contrib>
        <contrib contrib-type="author" corresp="no" rid="aff1 aff2">
          <name><surname>Pei</surname><given-names>Tao</given-names></name>
          
        </contrib>
        <aff id="aff1"><label>1</label><institution>State Key Laboratory of Resources and Environmental Information
System, Institute of Geographic Sciences and<?xmltex \hack{\break}?> Natural Resources Research,
Chinese Academy of Sciences, Beijing 100101, China</institution>
        </aff>
        <aff id="aff2"><label>2</label><institution>College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China</institution>
        </aff>
      </contrib-group>
      <author-notes><corresp id="corr1">Yunyan Du (duyy@lreis.ac.cn)</corresp></author-notes><pub-date><day>26</day><month>January</month><year>2023</year></pub-date>
      
      <volume>23</volume>
      <issue>1</issue>
      <fpage>317</fpage><lpage>328</lpage>
      <history>
        <date date-type="received"><day>9</day><month>June</month><year>2022</year></date>
           <date date-type="rev-request"><day>4</day><month>July</month><year>2022</year></date>
           <date date-type="rev-recd"><day>12</day><month>December</month><year>2022</year></date>
           <date date-type="accepted"><day>8</day><month>January</month><year>2023</year></date>
      </history>
      <permissions>
        <copyright-statement>Copyright: © 2023 Jiale Qian et al.</copyright-statement>
        <copyright-year>2023</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://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023.html">This article is available from https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023.html</self-uri><self-uri xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023.pdf">The full text article is available as a PDF file from https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023.pdf</self-uri>
      <abstract><title>Abstract</title>

      <p id="d1e146">Disaster-relevant authorities could make uninformed decisions due to the lack of a clear picture of urban
resilience to adverse natural events. Previous studies have seldom examined the
near-real-time human dynamics, which are critical to disaster emergency
response and mitigation, in response to the development and evolution of
mild and frequent rainfall events. In this study, we used the aggregated
Tencent location request (TLR) data to examine the variations in collective
human activities in response to rainfall in 346 cities in China. Then two
resilience metrics, rainfall threshold and response sensitivity, were
introduced to report a comprehensive study of the urban resilience to
rainfall across mainland China. Our results show that, on average, a
1 mm increase in rainfall intensity is associated with a 0.49 % increase
in human activity anomalies. In the cities of northwestern and
southeastern China, human activity anomalies are affected more by rainfall
intensity and rainfall duration, respectively. Our results highlight the
unequal urban resilience to rainfall across China, showing current heavy-rain-warning standards underestimate the impacts of heavy rains on residents in the northwestern arid region and the central underdeveloped areas
and overestimate impacts on residents in the southeastern coastal
area. An overhaul of current heavy-rain-alert standards is therefore needed
to better serve the residents in our study area.</p>
  </abstract>
    </article-meta>
  </front>
<body>
      

<sec id="Ch1.S1" sec-type="intro">
  <label>1</label><title>Introduction</title>
      <p id="d1e158">Heavy rains with intense precipitation have become more frequent in the
context of global climate
changes (Myhre et
al., 2019; Ogie et al., 2018) and pose significant threats to urban
residents, mainly due to uncoordinated watershed management and
undersized
infrastructures (Chan
et al., 2018; Dewan, 2015; Nahiduzzaman et al., 2015; Song et al., 2019).
China is frequently affected by urban flooding, particularly in summer when
the Asian monsoon brings heavy rains to inland China. It is estimated that
55.15 million people were affected by floods in China in 2017 alone and the
direct economic loss was approximately CNY 214 billion, which
significantly exceeds the impacts of the 2017 typhoon disasters (5.879 million people,
CNY 34.62 billion). In addition to threatening human daily activities and
cities' normal
operation (Aerts
et al., 2014; Grinberger and Felsenstein, 2016; Kasmalkar et al., 2020;
Owrangi et al., 2014), the ever-increasing rainstorms endlessly challenge
cities' flood resistance capacity and relevant authorities' real-time
decisions in response to such adverse events. Urban decision-makers have
learned that city management and planning would significantly benefit from a
better understanding of urban
resilience (O'Sullivan
et al., 2012; Bertilsson et al., 2019; de Bruijn, 2004).</p>
      <p id="d1e161">Urban resilience refers to the ability of an urban system to prepare for,
respond to, and recover from adverse
events (Ambelu
et al., 2017; Hong et al., 2021; Liao, 2012; Meerow et al., 2016).
Biologists, psychologists, engineers, and geographers have all made their
own contributions to urban resilience
studies (Adger
et al., 2005; Brusberg and Shively, 2015; Olsson et al., 2015; Ouyang et
al., 2012; Poulin and Kane, 2021; Shiferaw et al., 2014). Over the past 20 years, geographers have heavily relied on satellite imagery to assess
disaster-related resilience as satellites have been providing
ever-increasing information about the Earth at a relatively low
cost (Mpandeli
et al., 2019; Stefan et al., 2016; Tellman et al., 2021). For example,
satellite-based emergency mapping systems have been developed to monitor the
inundation and recovery processes of the 2005 Switzerland
flood (Buehler et al., 2006); assess the
damage, restoration, and reconstruction induced by the 2010 Haiti
earthquake (Honey et al., 2010); and evaluate the changes
in power supply before and after Hurricane Maria in
2017 (Román et al., 2019). Emergency
rescuers can use high-resolution images to closely monitor ongoing natural
disasters and coordinate disaster relief. However, it is almost impossible
to extract near-real-time human dynamics over the evolution of a disaster
from satellite images, and such information is very important in disaster
mitigation and reduction (Liu et al.,
2015; Ghaffarian et al., 2018).</p>
      <p id="d1e164">Location-aware big data, such as smartphone call records, signalling
data, and social media posts, have been widely used to infer real-time human
activities (Yi
et al., 2019; Wang et al., 2020, 2019; Yue et al., 2017), estimate
disaster-induced losses (Kryvasheyeu et al., 2016;
Liu et al., 2019b), monitor resettlement and
restoration (Martín
et al., 2020a, b; Wang and Taylor, 2018; Yabe et al., 2020), and study
disaster-related
resilience (Hong
et al., 2021; Huang and Ling, 2018; Kasmalkar et al., 2020; Zou et al.,
2018). Urban residents adjust their activities when their living
environments are socially and physically impacted by an adverse event, and
such adjustment can be inferred from location-aware big data (Qian et al., 2021b). In other
words, the changes in human activities extracted from location-aware big
data could be used to study the resilience capacity of an urban system in
response to an adverse event. For example, Hong et al. (2021) quantified changes in mobility behaviour before,
during, and after the Hurricane Harvey using smartphone geolocation data,
and they analysed the spatial variable of community resilience capacity, which was
defined as the function of the magnitude of impact and time to recovery.</p>
      <p id="d1e167">Human activities may also change in response to mild yet frequent adverse
natural events, such as urban rainstorms. Unlike in the case of hurricanes, dwellers are
usually not mobilized by relevant authorities to prepare for and resettle
after such events. Instead, nearly 90 % of flood-related tweets in a city
are released during heavy rains (Wang et al., 2020).
Consequently, human activities mainly show how an urban system responds to
but not how it prepares for and recovers from such adverse natural events (Qian et al., 2022; Zhang et al.,
2022). As a result, urban resilience to mild and frequent adverse events
refers to the ability of an urban system to respond to adverse events.
Furthermore, urban resilience could significantly differ from that of
destructive disasters and may show significant spatiotemporal variations due
to the areal difference in local natural settings, socioeconomic status, and
infrastructure
completeness (Adger
et al., 2005; Guan and Chen, 2014; Östh et al., 2015; Zou et al., 2019,
2018). Study of such regional inequality is therefore of great value to
disaster relief and mitigation.</p>
      <p id="d1e171">However, previous resilience metrics, which have mainly focused on unique disaster
events, were not suitable for making assessments at a large scale. Two resilience
metrics were introduced into this study from other fields. Sensitivity
is a widely used tool for understanding resilience in different regions in
many other weather events, such as heat waves and air pollution (Hong et al., 2021; Wang et al.,
2021). For example, Zheng et al. (2019) defined the links
between a city-level happiness index calculated from social media data
and a daily local air quality metric as the perception sensitivity and
explored its spatial variation. However, response sensitivity has not yet been studied for rainstorm events through analysing the relation between a
city-scale human activity response metric and a rainstorm event index. Another
index, the rainfall threshold, is commonly used to study rainfall events that
have resulted in landslides (Marra
et al., 2016; Naidu et al., 2018). In this study, the rainfall threshold, which
is defined as the minimum rainfall index that corresponds to a significant
urban human activity response anomaly, is introduced into the study of
urban resilience. These two metrics can effectively depict urban resilience at
different levels of focus.</p>
      <p id="d1e174">In this study, we propose a method for measuring and evaluating how urban
systems respond to heavy rains as reflected in location-aware big data. We
extracted human activities from the Tencent location request (TLR) data in
346 cities across mainland China from May to August 2017 and used two
indicators – rainfall threshold and response sensitivity – to quantify the
urban resilience across our study area. We found significant regional
inequality of urban resilience in mainland China, and the inequality could be
explained by variations in the regional natural, socioeconomic, and
infrastructure variables. The findings from this study provide a new
perspective and method to quantify urban resilience to frequent yet not
so destructive adverse events across a large geographic scale. Practically,
our findings suggest an urgent need to revise current unified rainstorm
warning standards to better serve residents.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F1"><?xmltex \currentcnt{1}?><?xmltex \def\figurename{Figure}?><label>Figure 1</label><caption><p id="d1e179">A flow chart showing the data analysis process in this study. S-H-ESD denotes seasonal hybrid extreme Studentized deviate.</p></caption>
        <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f01.png"/>

      </fig>

</sec>
<sec id="Ch1.S2">
  <label>2</label><title>Data and methods</title>
<sec id="Ch1.S2.SS1">
  <label>2.1</label><title>Data</title>
      <p id="d1e203">We collected Tencent location request (TLR) data from 1 May to
31 August 2017 from Tencent's big data portal. Tencent, with over
700 million users, is the largest social media platform in China. A Tencent
user may check in the platform for a variety of purposes such as
location-based searching, navigation, or location sharing. The
dataset we downloaded has an hourly temporal resolution and a 1 km <inline-formula><mml:math id="M1" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 1 km
spatial resolution. The data have been proven as a reliable proxy for
collective human activities in many studies from multiple dimensions of time
and space (Liu et
al., 2019b; Qian et al., 2021a; Ma, 2018).</p>
      <p id="d1e213">We used the Integrated
Multi-satellitE Retrievals for GPM (IMERG; GPM denotes Global Precipitation Measurement v6) 30 min precipitation
dataset (Levizzani et al., 2020, p.1). This
dataset has a spatial resolution of 0.1<inline-formula><mml:math id="M2" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula> <inline-formula><mml:math id="M3" display="inline"><mml:mo>×</mml:mo></mml:math></inline-formula> 0.1<inline-formula><mml:math id="M4" display="inline"><mml:msup><mml:mi/><mml:mo>∘</mml:mo></mml:msup></mml:math></inline-formula>
and has been evaluated and widely used in related
studies (Yi et al., 2019; Liu et al.,
2019a). We used this dataset to extract the characteristics of rainfall
events of interest.</p>
      <p id="d1e241">We collected six natural, socioeconomic, or infrastructure indicators to
help explain the variations in urban resilience, including the annual
precipitation in China calculated by aggregating GPM data in 2017,
population density, gross domestic product, green coverage rate, drainage
network density, and per capita area of paved roads.</p>
</sec>
<sec id="Ch1.S2.SS2">
  <label>2.2</label><title>Methods</title>
      <p id="d1e252">Figure 1 shows the data process and analysis flow chart of this study. We
first proposed a multilevel human activity anomaly detection (MHAAD)
methodological framework to detect and characterize the TLR anomalies in
response to rainfall events. The framework has two major parts. In the first
part, we identified the grids with a stable TLR number and then the
anomalies from the time series TLR data of each grid. We then used the two-sided
Welch's <inline-formula><mml:math id="M5" display="inline"><mml:mi>t</mml:mi></mml:math></inline-formula> test and probability density function (PDF) method to detect
whether human activity anomalies are triggered by a rainfall event or not.
Rainfall indices were extracted for the grids with a stable TLR number and
selected by their importance as shown in the random forest model. We then
explored the multilevel relationship between rainfall characteristics and
human activity anomalies. We proposed two indicators – rainfall threshold and
response sensitivity – to describe urban resilience. Lastly, we assessed the
association between urban resilience and natural, socioeconomic,
and infrastructure explanatory variables.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F2"><?xmltex \currentcnt{2}?><?xmltex \def\figurename{Figure}?><label>Figure 2</label><caption><p id="d1e264">The schematic diagram <bold>(a)</bold> and contingency table <bold>(b)</bold> of the
binary classifier for Beijing.</p></caption>
          <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f02.png"/>

        </fig>

<sec id="Ch1.S2.SS2.SSS1">
  <label>2.2.1</label><title>TLR anomaly detection</title>
      <p id="d1e286">We first identified all grids with a stable TLR number (hereafter
referred to as stable grids unless stated otherwise) using the method Qian
et al. (2021b) proposed. Based on the empirical cumulative distribution function (CDF)  of parameters <inline-formula><mml:math id="M6" display="inline"><mml:mi>P</mml:mi></mml:math></inline-formula> and <inline-formula><mml:math id="M7" display="inline"><mml:mi>M</mml:mi></mml:math></inline-formula>, we can get all of the stable grids which are the regions with stable human activity and rhythm in an urban area. In total,
832 630 out of the 9 600 903 grids across our study area are identified as
stable grids. The numbers of smartphone users and TLRs vary significantly by
grid. We therefore normalized the TLRs using the median interquartile
normalization method (Geller et al., 2003) to make
the TLRs in the stable grids comparable. We then employed the seasonal hybrid
extreme Studentized deviate (S-H-ESD) method (Vallis et al.,
2014) to detect anomalies from the gridded TLR time series. The S-H-ESD
method can be denoted by the following additive model:
              <disp-formula id="Ch1.E1" content-type="numbered"><label>1</label><mml:math id="M8" display="block"><mml:mrow><mml:msub><mml:mi>T</mml:mi><mml:mi mathvariant="normal">s</mml:mi></mml:msub><mml:mo>=</mml:mo><mml:msub><mml:mi>T</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mi>S</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub><mml:mo>+</mml:mo><mml:msub><mml:mi>R</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub><mml:mo>,</mml:mo></mml:mrow></mml:math></disp-formula>
            where <inline-formula><mml:math id="M9" display="inline"><mml:mrow><mml:msub><mml:mi>T</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>, <inline-formula><mml:math id="M10" display="inline"><mml:mrow><mml:msub><mml:mi>S</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula>, and <inline-formula><mml:math id="M11" display="inline"><mml:mrow><mml:msub><mml:mi>R</mml:mi><mml:mi mathvariant="normal">C</mml:mi></mml:msub></mml:mrow></mml:math></inline-formula> represent the trend, seasonality, and residual
components, respectively.</p>
      <p id="d1e371">The S-H-ESD method has two major steps. First, the piecewise median method
is used to fit and remove the long-term trend. Then the seasonal-trend
decomposition using locally weighted regression (LOESS) method is employed to remove
seasonality (Cleveland et al., 1990). We then used the
generalized extreme Studentized deviate (G-ESD)
statistic (Rosner, 1975) to identify significant
anomalies in the residuals. In this study, we used a piecewise combination
of the biweekly medians to model the underlying trend, which shows little
change in the TLR time series. The significance level <inline-formula><mml:math id="M12" display="inline"><mml:mi>a</mml:mi></mml:math></inline-formula> is set to 0.05,
and the number of anomalies is set to no more than 25 % of the total
observations.</p>
      <p id="d1e381">We then extracted the total numbers of the grids with positive anomalies (PTLR) and
negative anomalies (NTLR) by city, respectively, and then examined the
variations in the PTLR and NTLR time series over the periods with rains and
without rains to identify whether a rainfall event triggers collective human
activity anomalies. The two-sided Welch's <inline-formula><mml:math id="M13" display="inline"><mml:mi>t</mml:mi></mml:math></inline-formula> test was used for the
significance test. Human activity anomalies usually happen shortly before or
after the peak rainfall intensity and last as a spell instead of the entire
rainfall event. We therefore employed a moving-time-window method to find
the period with the largest accumulative rainfall and used the period to
detect the statistical significance of the change in relation to the
PTLR/NTLR time series in a raining and non-raining period. In this study, we
used a 6 h moving window, which is half of the average duration of all
rainfall events of interest in this study (see Fig. S3 in the Supplement).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F3"><?xmltex \currentcnt{3}?><?xmltex \def\figurename{Figure}?><label>Figure 3</label><caption><p id="d1e394"><bold>(a)</bold> The schematic definitions of the human activity anomaly
associated with a specific rainfall event used in this study, where the <inline-formula><mml:math id="M14" display="inline"><mml:mi>x</mml:mi></mml:math></inline-formula> axis presents the “month–day hour”. <bold>(b)</bold> The
relative proportions and numbers of the rainfall events with various cPTLR
and cNTLR values (see the main text for definitions of cPTLR and cNTLR). <bold>(c)</bold> The probability density distribution curves of the
events with significantly increased cPTLR/cNTLR. <bold>(d)</bold> Box plots by peak
rainfall intensity groups per 0.5 mm. Trend lines are shown for the ordinary least squares (OLS)
regression (dashed black), 0.25 quantile (purple), median (red), and 0.75 quantile (blue)
range. The numbers in Fig. 3d show the numbers of rainfall events with
specific peak intensity as shown along the <inline-formula><mml:math id="M15" display="inline"><mml:mi>x</mml:mi></mml:math></inline-formula> axis.</p></caption>
            <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f03.png"/>

          </fig>

</sec>
<sec id="Ch1.S2.SS2.SSS2">
  <label>2.2.2</label><title>Feature selection of rainfall indices</title>
      <p id="d1e437">The GPM data were first resampled to the same spatiotemporal resolutions as
those of the TLR data using the nearest-neighbour interpolation method. We then
extracted the rainfall intensity for each city per hour, i.e. the average
hourly GPM precipitation within the stable grids of the city.</p>
      <p id="d1e440">In this study, a rainfall event is defined as a precipitation process that
lasts for at least 3 h and with no rains preceding for at least 1 h. The number of rainfall events in each city is normally distributed. We
selected the 346 cities with at least 40 (the top 5 % quantile) rainfall
events for this study (Figs. S1 and S2).</p>
      <p id="d1e443">Every rainfall event is described with three rainfall indices (the 1 h
peak intensity, 6 h peak intensity, and cumulative rainfall) and two
temporal indices (the duration and peak hour) (Table S1). From
these indices, we used a random forest model (RF) to calculate the
importance score (mean decrease accuracy) for each indicator. The importance
score shows the global importance over all the out-of-bag cross-validated
predictions. The random forest model is robust and less susceptible to
multicollinearity as it averages all predictions for a given feature
variable and is more efficient in terms of feature selection than
multi-linear regression (Strobl et al., 2007; Pal,
2005). We then identified the most important indicator that triggers human
activity anomalies (Liaw and Wiener, 2001).</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F4"><?xmltex \currentcnt{4}?><?xmltex \def\figurename{Figure}?><label>Figure 4</label><caption><p id="d1e449"><bold>(a)</bold> The importance of the five rainfall indicators obtained
by the random forest model. The peak hour is the most important covariate
that triggers human activity anomalies and has the highest decrease accuracy
value of 114.5. <bold>(b)</bold> The peak hour thresholds identified from the differences
in the peak hour PDF values between the rainfall events with and without
significant collective human activity anomalies. When the peak hours are
between 08:59 and 18:50 UTC<inline-formula><mml:math id="M16" display="inline"><mml:mo>+</mml:mo></mml:math></inline-formula>8, the PDF values of the events with human
activity anomalies are higher than those without. In other words, daytime
rains are more likely to trigger human activity anomalies. There are 11 491
daytime rains (i.e. from 08:59 to 18:50 UTC<inline-formula><mml:math id="M17" display="inline"><mml:mo>+</mml:mo></mml:math></inline-formula>8) out of the total 20 860
rainfall events (ratio: 55.11 %).</p></caption>
            <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f04.png"/>

          </fig>

      <?xmltex \floatpos{t}?><fig id="Ch1.F5" specific-use="star"><?xmltex \currentcnt{5}?><?xmltex \def\figurename{Figure}?><label>Figure 5</label><caption><p id="d1e479">Spatial distribution of the rainfall threshold that triggers
human activity anomalies for rainfall events lasting 3 <bold>(a)</bold>, 6 <bold>(b)</bold>, and
12 h <bold>(c)</bold> and slope <bold>(d)</bold> of the decision boundary. The
isohyets show the 2017 annual rainfall.</p></caption>
            <?xmltex \igopts{width=412.564961pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f05.png"/>

          </fig>

</sec>
<sec id="Ch1.S2.SS2.SSS3">
  <label>2.2.3</label><title>Quantifying the rainfall threshold and response sensitivity</title>
      <p id="d1e508">In this study, we used two indices, rainfall threshold and response
sensitivity, to quantitatively characterize urban resilience. The rainfall
threshold is the peak intensity of the rainfall event which triggers
collective human activity anomalies. We first used a linear binary
classifier to examine the paired values of the peak intensity and duration
to determine whether a rainfall event brings more or less rain than the
threshold to trigger collective human activity anomalies (Fig. 2a). The
Fisher discriminant analysis method was then applied to identify the
discriminant function to minimize the classification
errors (Mika et al., 1999). The rainfall
thresholds associated with different rainfall durations are directly
extracted from Fig. 2a.</p>
      <p id="d1e511">Three quantitative indices, the probability of detection (POD), false alarm
rate (FAR), and critical success index (CSI), are used to evaluate the performance
of the threshold identification method based on the contingency table (Fig. 2b):

                  <disp-formula specific-use="gather" content-type="numbered"><mml:math id="M18" display="block"><mml:mtable displaystyle="true"><mml:mlabeledtr id="Ch1.E2"><mml:mtd><mml:mtext>2</mml:mtext></mml:mtd><mml:mtd><mml:mrow><mml:mstyle class="stylechange" displaystyle="true"/><mml:mi mathvariant="normal">POD</mml:mi><mml:mo>=</mml:mo><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mi>H</mml:mi><mml:mrow><mml:mi>H</mml:mi><mml:mo>+</mml:mo><mml:mi>M</mml:mi></mml:mrow></mml:mfrac></mml:mstyle><mml:mo>,</mml:mo></mml:mrow></mml:mtd></mml:mlabeledtr><mml:mlabeledtr id="Ch1.E3"><mml:mtd><mml:mtext>3</mml:mtext></mml:mtd><mml:mtd><mml:mrow><mml:mstyle displaystyle="true" class="stylechange"/><mml:mi mathvariant="normal">FAR</mml:mi><mml:mo>=</mml:mo><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mi mathvariant="normal">FA</mml:mi><mml:mrow><mml:mi>H</mml:mi><mml:mo>+</mml:mo><mml:mi mathvariant="normal">FA</mml:mi></mml:mrow></mml:mfrac></mml:mstyle><mml:mo>,</mml:mo></mml:mrow></mml:mtd></mml:mlabeledtr><mml:mlabeledtr id="Ch1.E4"><mml:mtd><mml:mtext>4</mml:mtext></mml:mtd><mml:mtd><mml:mrow><mml:mstyle class="stylechange" displaystyle="true"/><mml:mi mathvariant="normal">CSI</mml:mi><mml:mo>=</mml:mo><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mi>H</mml:mi><mml:mrow><mml:mi>H</mml:mi><mml:mo>+</mml:mo><mml:mi>M</mml:mi><mml:mo>+</mml:mo><mml:mi mathvariant="normal">FA</mml:mi></mml:mrow></mml:mfrac></mml:mstyle><mml:mo>=</mml:mo><mml:mstyle displaystyle="true"><mml:mfrac style="display"><mml:mn mathvariant="normal">1</mml:mn><mml:mrow><mml:msup><mml:mi mathvariant="normal">POD</mml:mi><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup><mml:mo>+</mml:mo><mml:msup><mml:mfenced close=")" open="("><mml:mrow><mml:mn mathvariant="normal">1</mml:mn><mml:mo>-</mml:mo><mml:mi mathvariant="normal">FAR</mml:mi></mml:mrow></mml:mfenced><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:msup><mml:mo>-</mml:mo><mml:mn mathvariant="normal">1</mml:mn></mml:mrow></mml:mfrac></mml:mstyle><mml:mo>,</mml:mo></mml:mrow></mml:mtd></mml:mlabeledtr></mml:mtable></mml:math></disp-formula>

              where <inline-formula><mml:math id="M19" display="inline"><mml:mi>H</mml:mi></mml:math></inline-formula>, FA, and <inline-formula><mml:math id="M20" display="inline"><mml:mi>M</mml:mi></mml:math></inline-formula> represent the percent of hits, false alarms, and misses,
respectively. All three indices range from 0 to 1. A value of 1 for the POD
and FAR indicates a perfect hit and a 100 % false-positive rate. A higher
CSI is associated with a higher POD and a lower FAR value.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F6" specific-use="star"><?xmltex \currentcnt{6}?><?xmltex \def\figurename{Figure}?><label>Figure 6</label><caption><p id="d1e647">Spatial distribution of the response sensitivity <bold>(a)</bold> and
adjusted <inline-formula><mml:math id="M21" display="inline"><mml:mrow><mml:msup><mml:mi>R</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:mrow></mml:math></inline-formula> <bold>(b)</bold> in multiple linear regression. The
isohyets show the 2017 annual rainfall.</p></caption>
            <?xmltex \igopts{width=412.564961pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f06.png"/>

          </fig>

      <p id="d1e674">The second index, the response sensitivity, is defined as the rate of
abnormal change in collective human activities triggered by a rainfall
event. We first selected the rainfall events with precipitation above the
threshold and that trigger human activity anomalies, i.e. those represented
with red crosses and above the decision boundary in Fig. 2a. Then we
defined two indicators, cPTLR and cNTLR, to describe the rate of abnormal change
in collective human activities (Fig. S4). The cPTLR and cNTLR were
calculated as the difference between the mean of the two time series, i.e.
the PTLR and NTLR in the 6 h raining time window and non-raining time window.
A multiple linear regression model was then constructed between the cPTLR
and the rainfall intensity/duration for each city. In the end, we calculated
the marginal city-specific partial derivatives of cPTLR with respect to the
peak intensity and the duration. The response sensitivity
index is calculated as the average of the regression coefficients of the
peak intensity and the duration. The adjusted <inline-formula><mml:math id="M22" display="inline"><mml:mrow><mml:msup><mml:mi>R</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:mrow></mml:math></inline-formula> was also calculated to
assess the model accuracy.</p>
      <p id="d1e688">Finally, we separately classified the rainfall threshold and response
sensitivity indices of the 346 cities into three classes using the Jenks
natural breaks classification method, which clusters data into different
groups by seeking minimum variance within a class and maximum variance
between classes (McDougall and Temple-Watts,
2012). In this study, we used the 6 h rainfall threshold index in line
with the time window in Fig. S4. In total, there are nine
different combinations between the threshold and response sensitivity
indices.</p>
</sec>
<sec id="Ch1.S2.SS2.SSS4">
  <label>2.2.4</label><title>Quantifying the relationships between resilience and urban
characteristics</title>
      <p id="d1e699">We then examined the relationships between the two urban resilience indices
and the annual rainfall, population density, gross domestic product, green
coverage rate, drainage network density, and per capita area of paved roads.
The Kendall, Pearson, and Spearman correlation coefficients and multi-linear
regression were used to measure the correlation between rainfall threshold,
response sensitivity, and city characteristics at the city level.</p>
</sec>
</sec>
</sec>
<sec id="Ch1.S3">
  <label>3</label><title>Results</title>
<sec id="Ch1.S3.SS1">
  <label>3.1</label><title>Collective human activities in response to rainfall events</title>
      <p id="d1e719">The gridded TLR numbers could increase (positive anomaly) or decrease (negative
anomaly) in response to rains (Fig. S5). Counting the overall
TLR changes by city would not show how rains impact collective human
activities (Yi et al., 2019). In this study, instead, we calculated
the changes in the total numbers of the grids showing positive (cPTLR) and
negative anomalies (cNTLR) by city during a raining period in relation to
those over the non-raining period (Fig. 3a) to illustrate how
collective human activities change in response to rains.</p>
      <p id="d1e722">The city-level collective human activities jump to an excited state (Fig. 3b) with a significantly increased number of grids exhibiting positive
anomalies in response to 55.11 % of the daytime rains (Fig. 4), whereas
nighttime rains show no significant impact on  collective human
activities. About 93.2 % (i.e. 10 710) of the rainfall events in this
study are associated with a greater change in the number of grids with
positive anomalies than that of the grids with negative anomalies (i.e.
<inline-formula><mml:math id="M23" display="inline"><mml:mrow><mml:mo>|</mml:mo><mml:mi mathvariant="normal">cPTLR</mml:mi><mml:mo>|</mml:mo><mml:mo>&gt;</mml:mo><mml:mo>|</mml:mo><mml:mi mathvariant="normal">cNTLR</mml:mi><mml:mo>|</mml:mo></mml:mrow></mml:math></inline-formula>). Around
59.7 % of the 10 710 (i.e. 6394) rains show an increased number of
grids with positive anomalies by city. Furthermore, 35.3 % of the 6394
(i.e. 2257) rainfall events associated with excited-state human activities
show a significantly increased number of grids with positive anomalies,
which we believed could be attributed to heavy rains. We noticed that a
small number (103, 13.19 % <inline-formula><mml:math id="M24" display="inline"><mml:mrow><mml:mo>|</mml:mo><mml:mi mathvariant="normal">cPTLR</mml:mi><mml:mo>|</mml:mo><mml:mo>≤</mml:mo><mml:mo>|</mml:mo><mml:mi mathvariant="normal">cNTLR</mml:mi><mml:mo>|</mml:mo></mml:mrow></mml:math></inline-formula>) of heavy rains brought by typhoons trigger city-level
collective human activities to be in a dispirited state, with a significantly
increased number of grids exhibiting NTLR (Fig. 3c) as compared to the
non-typhoon rains. Accordingly, we excluded all typhoon-related rainfall
events from this study.</p>
      <p id="d1e765">The higher rainfall intensity could trigger more excited-state collective
human activities (Fig. 3d). The 1 h peak intensity values of the rainfall
events associated with excited-state human activities are positively
correlated with the corresponding cPTLR values (fitting slope <inline-formula><mml:math id="M25" display="inline"><mml:mo>=</mml:mo></mml:math></inline-formula> 0.49 %,
<inline-formula><mml:math id="M26" display="inline"><mml:mi>p</mml:mi></mml:math></inline-formula> value <inline-formula><mml:math id="M27" display="inline"><mml:mo>&lt;</mml:mo></mml:math></inline-formula> 0.001). However, the cPTLR slope against rainfall is
affected by the divergence of the peak intensity anomaly. Quantile
regression results show that the cPTLR slope coefficient estimates gradually
increase from 0.17 % for the lower 25 % quantile to 0.84 % for the
higher 75 % quantile (<inline-formula><mml:math id="M28" display="inline"><mml:mi>p</mml:mi></mml:math></inline-formula> value <inline-formula><mml:math id="M29" display="inline"><mml:mo>&lt;</mml:mo></mml:math></inline-formula> 0.01). In other words, the cPTLR
growth rate generally increases from the lower-anomaly to the
sensitive-anomaly rainfall events with respect to the increasing magnitude
of the rainfall peak intensity.</p>
</sec>
<sec id="Ch1.S3.SS2">
  <label>3.2</label><title>Regional inequality of urban resilience</title>
      <p id="d1e811">We derived two indicators – rainfall threshold and response sensitivity –
from the perspective of the public's social response to rains to evaluate
urban resilience. The threshold is defined as the intensity of an event that
triggers a city to reach an undesirable state (Liao, 2012). In
this study, we defined the threshold of a rainfall event with a specific
duration as the minimum rainfall intensity that corresponds to significant
urban TLR anomalies. As shown in Fig. 4a, the peak rain intensity and rain
duration are the second and third most important characteristics, respectively, that trigger
human activity anomalies. We extracted the rainfall thresholds
for each city using binary classification models (Fig. S6), and
the results show that the rainfall thresholds drop with increased rainfall
duration across all 346 cities in China (Fig. 5a–c). The 3, 6, and
12 h rainfall thresholds all show significant spatial autocorrelation and
a pattern of gradual decrease from the southeastern coast to the northwestern
inland. However, with increased rainfall durations, the average rainfall
thresholds of all 346 cities decrease from 4.24 to 2.75, whereas their
standard deviations decrease from 3.55 to 2.45. Such results indicate the
public's response to the short rainfall events varies greatly in different
cities and tends to be more consistent with increased rainfall durations.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F7"><?xmltex \currentcnt{7}?><?xmltex \def\figurename{Figure}?><label>Figure 7</label><caption><p id="d1e816">Spatial distribution of urban resilience. The basemap colours
indicate the 2017 annual rainfall.</p></caption>
          <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f07.png"/>

        </fig>

      <p id="d1e825">The impacts of the peak rain intensity and duration on human activity vary
across our study area as shown by the slopes of the decision boundary of
different cities (Fig. 5d). In arid and semi-arid northwestern China,
the slope is close to zero, showing the public response is mainly affected
by peak intensity. Residents in northwestern China may adjust their
activities in response to the rain peak intensity as rains in this area
seldom last long. By contrast, the slope is high for the southeastern
region, indicating the public's response is more affected by rainfall
duration. The wet southeastern China usually receives frequent and heavy
rains and residents have already adapted to it. Consequently, residents in
this area may change their activities in response to rainfall duration more
than to the peak intensity.</p>
      <p id="d1e829">Results of the binary classification are solid as shown by the anomaly
detection POD, FAR, and CSI values for different rainfall durations based on
rainfall thresholds (Fig. S7). More specifically, the POD
values for different rainfall durations in the 346 cities range from 0.71 to
1.00, the FAR values from 0 to 0.46, and the CSI values from 0.48 to 1.</p>

      <?xmltex \floatpos{t}?><fig id="Ch1.F8"><?xmltex \currentcnt{8}?><?xmltex \def\figurename{Figure}?><label>Figure 8</label><caption><p id="d1e834">Regression coefficients between the six explanatory variables
and the 6 h rainfall threshold <bold>(a)</bold> and response sensitivity <bold>(b)</bold>. The
horizontal lines mean the 95 % confidence interval.</p></caption>
          <?xmltex \igopts{width=236.157874pt}?><graphic xlink:href="https://nhess.copernicus.org/articles/23/317/2023/nhess-23-317-2023-f08.png"/>

        </fig>

      <p id="d1e849">The other urban resilience indicator, the response sensitivity, is defined
as the rate of the collective human activity anomalies triggered by a
rainfall event and was extracted from multiple regression analysis. The
response sensitivity is low on the southeastern coast and high in the northwestern
inland, showing a trend opposite to that of the rainfall threshold (Fig. 6a). The higher response sensitivity in the northwest suggests that the
residents in this area tend to change their activities more significantly in
response to rains. By contrast, activities of the residents in the southeast
are not significantly impacted by rains. Such findings are consistent with
those derived from the rain threshold indicator. The accuracy of the
regression model (the adjusted <inline-formula><mml:math id="M30" display="inline"><mml:mrow><mml:msup><mml:mi>R</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup><mml:mo>)</mml:mo></mml:mrow></mml:math></inline-formula> also shows a similar trend to that
of the response sensitivity (Fig. 6b), which indicates that the response mode
of collective human activities to rainfall in the southeastern coastal area is
more complex.</p>

<?xmltex \floatpos{t}?><table-wrap id="Ch1.T1" specific-use="star"><?xmltex \currentcnt{1}?><label>Table 1</label><caption><p id="d1e868">Urban resilience indices from this study for different city
groups and the difference from the current yellow Chinese heavy-rain-alert
standard. Note that the different types of urban resilience are defined in Fig. 7.</p></caption><oasis:table frame="topbot"><oasis:tgroup cols="6">
     <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:colspec colnum="6" colname="col6" align="right"/>
     <oasis:thead>
       <oasis:row>
         <oasis:entry colname="col1"/>
         <oasis:entry colname="col2">Threshold</oasis:entry>
         <oasis:entry colname="col3">Response</oasis:entry>
         <oasis:entry colname="col4">Alarm</oasis:entry>
         <oasis:entry colname="col5">Yellow</oasis:entry>
         <oasis:entry colname="col6">Difference from</oasis:entry>
       </oasis:row>
       <oasis:row rowsep="1">
         <oasis:entry colname="col1">Type</oasis:entry>
         <oasis:entry colname="col2">(mm)</oasis:entry>
         <oasis:entry colname="col3">sensitivity</oasis:entry>
         <oasis:entry colname="col4">standard (mm)</oasis:entry>
         <oasis:entry colname="col5">warning (mm)</oasis:entry>
         <oasis:entry colname="col6">yellow warning</oasis:entry>
       </oasis:row>
     </oasis:thead>
     <oasis:tbody>
       <oasis:row>
         <oasis:entry colname="col1">LH</oasis:entry>
         <oasis:entry colname="col2">1.8</oasis:entry>
         <oasis:entry colname="col3">0.71</oasis:entry>
         <oasis:entry colname="col4">10.8</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M31" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">39.2</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">LM</oasis:entry>
         <oasis:entry colname="col2">2.08</oasis:entry>
         <oasis:entry colname="col3">0.51</oasis:entry>
         <oasis:entry colname="col4">12.46</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M32" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">37.54</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">LL</oasis:entry>
         <oasis:entry colname="col2">2.23</oasis:entry>
         <oasis:entry colname="col3">0.39</oasis:entry>
         <oasis:entry colname="col4">13.35</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M33" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">36.65</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">MH</oasis:entry>
         <oasis:entry colname="col2">3.61</oasis:entry>
         <oasis:entry colname="col3">0.63</oasis:entry>
         <oasis:entry colname="col4">21.68</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M34" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">28.32</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">ML</oasis:entry>
         <oasis:entry colname="col2">4.99</oasis:entry>
         <oasis:entry colname="col3">0.41</oasis:entry>
         <oasis:entry colname="col4">29.94</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M35" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">20.06</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">MM</oasis:entry>
         <oasis:entry colname="col2">5.03</oasis:entry>
         <oasis:entry colname="col3">0.49</oasis:entry>
         <oasis:entry colname="col4">30.19</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6"><inline-formula><mml:math id="M36" display="inline"><mml:mrow><mml:mo>-</mml:mo><mml:mn mathvariant="normal">19.81</mml:mn></mml:mrow></mml:math></inline-formula></oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">HL</oasis:entry>
         <oasis:entry colname="col2">17.5</oasis:entry>
         <oasis:entry colname="col3">0.42</oasis:entry>
         <oasis:entry colname="col4">104.97</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6">54.97</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">HM</oasis:entry>
         <oasis:entry colname="col2">18.94</oasis:entry>
         <oasis:entry colname="col3">0.48</oasis:entry>
         <oasis:entry colname="col4">113.64</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6">63.64</oasis:entry>
       </oasis:row>
       <oasis:row>
         <oasis:entry colname="col1">HH</oasis:entry>
         <oasis:entry colname="col2">22.34</oasis:entry>
         <oasis:entry colname="col3">0.64</oasis:entry>
         <oasis:entry colname="col4">134.05</oasis:entry>
         <oasis:entry colname="col5">50</oasis:entry>
         <oasis:entry colname="col6">84.05</oasis:entry>
       </oasis:row>
     </oasis:tbody>
   </oasis:tgroup></oasis:table></table-wrap>

      <p id="d1e1185">The associations between the two urban resilience indices also exhibit a
significant pattern across our study area (Fig. 7). Cities located in the
area with over 1600 mm annual precipitation are mainly categorized into type
HL (threshold <inline-formula><mml:math id="M37" display="inline"><mml:mo>&gt;</mml:mo></mml:math></inline-formula> 10.29 mm and response sensitivity <inline-formula><mml:math id="M38" display="inline"><mml:mo>&lt;</mml:mo></mml:math></inline-formula> 0.003) and are surrounded by the ML and HM city types. The cities located in
the areas with less than 400 mm annual precipitation are mainly classified
into LH, MH, and LL types, indicating the annual precipitation has a
significant impact on human activities in different cities.</p>
      <p id="d1e1203">The LH type cities have a low rainfall threshold (<inline-formula><mml:math id="M39" display="inline"><mml:mo lspace="0mm">&lt;</mml:mo></mml:math></inline-formula> 3.25 mm) and high
response sensitivity (<inline-formula><mml:math id="M40" display="inline"><mml:mo lspace="0mm">&gt;</mml:mo></mml:math></inline-formula> 0.025). These cities are mainly found in
the northwestern fragile region (mainly including the Yili prefecture in
Xinjiang) and the central underdeveloped China (including Shaanxi,
Shanxi, and Hebei provinces). Such cities may have underdeveloped
infrastructure, and weaker rains could trigger human activity anomalies.</p><?xmltex \hack{\newpage}?>
</sec>
<sec id="Ch1.S3.SS3">
  <label>3.3</label><title>Associations between the urban resilience with the urban indicators</title>
      <p id="d1e1229">Results of multiple regression analysis show that variations in urban
resilience by city could be explained by the variations in a variety of
natural, socioeconomic, and urban infrastructure indicators. Figure 8a shows
the relationship between rainfall thresholds and explanatory indicators.
The 3, 6, and 12 h rainfall thresholds all show similar
correlations with the indictors (Tables S2, S3, S4), and we only
show the correlations between the 6 h  rainfall and the indicators in this
section.</p>
      <p id="d1e1232">All six explanatory variables are significantly correlated with the rainfall
threshold (<inline-formula><mml:math id="M41" display="inline"><mml:mrow><mml:mi>p</mml:mi><mml:mo>&lt;</mml:mo><mml:mn mathvariant="normal">0.05</mml:mn></mml:mrow></mml:math></inline-formula>). About 42 % of the variations in the rainfall
threshold could be explained by the variations in the explanatory variables
as shown by the <inline-formula><mml:math id="M42" display="inline"><mml:mrow><mml:msup><mml:mi>R</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:mrow></mml:math></inline-formula> (Table 3). Among all explanatory
variables, the annual rainfall has the highest coefficient value of 0.43,
indicating the variations in the threshold are most affected by the annual
rainfall. In other words, residents living in regions with different annual
precipitation amounts are more likely to accordingly adjust their daily
activities once the rainfall is over a specific threshold.</p>
      <p id="d1e1258">Other explanatory variables are also positively correlated with the
threshold variable, as shown by the positive regression coefficients ranging
from 0.21 to 0.10, except the per capita area of paved road, which is
negatively correlated with the threshold. In fact, the per capita area of
paved roads is the only indicator showing a negative correlation. Increased
per capita area of paved road weakens rainwater infiltration capacity and
increases surface runoff, which is more likely to cause traffic congestion
and trigger human activity anomalies even when the rainfall amount is below a
lower threshold.</p>
      <p id="d1e1261">Multi-regression analysis shows that the response sensitivity is negatively
correlated with all explanatory variables, except for the per capita area of
paved roads, which shows a positive regression coefficient (Fig. 8b). All
correlations are statistically significant (<inline-formula><mml:math id="M43" display="inline"><mml:mrow><mml:mi>p</mml:mi><mml:mo>&lt;</mml:mo><mml:mn mathvariant="normal">0.05</mml:mn></mml:mrow></mml:math></inline-formula>) (Table S5). About 31 % of the variations in the response sensitivity could
be explained by the variations in the explanatory variables as shown by an
<inline-formula><mml:math id="M44" display="inline"><mml:mrow><mml:msup><mml:mi>R</mml:mi><mml:mn mathvariant="normal">2</mml:mn></mml:msup></mml:mrow></mml:math></inline-formula> value of 0.31.</p>
</sec>
</sec>
<sec id="Ch1.S4" sec-type="conclusions">
  <label>4</label><title>Conclusions and discussions</title>
      <p id="d1e1296">Residents in different cities may adjust and change their activities in
different ways in response to rainfall. Such activity changes and
adjustment, also known as urban resilience, could be characterized and
studied from location-aware big data. In this study, we used Tencent
aggregated location request data to examine the changes in collective human
activities in major cities in China in response to rainfall over summer 2017. Our results show that the rainfall time, peak intensity, and duration
are the three most important indicators that determine whether a rain event would
trigger human activity anomalies or not. We also proposed two indices, the
rainfall threshold and response sensitivity, to describe urban
resilience; they show significant spatial variations across our study area.
Furthermore, the unequal urban resilience could be explained by a series of
explanatory variables.</p>
      <p id="d1e1299">We believe this paper provides a new perspective for studying urban
resilience and that the results bridge the knowledge gap between heavy
rains, collective human activities, and urban resilience. Such knowledge is
of great significance to urban planning, traffic management, and emergency
response.</p>
      <p id="d1e1302">We also believe this study has three other contributions regarding urban
resilience research. First, this study expanded the research framework of
urban resilience in response to high-frequency yet mild adverse events, and
such a framework could be used to study the variations in urban resilience
across a large area. Previous studies have mainly focused on urban resilience to
a specific adverse event such as a typhoon or a hurricane. For example, Zou
et al. (2018) used a normalized ratio index to
assess the regional variations in urban resilience to Hurricane Sandy. In
this study, we examined urban resilience to rains over a relatively long
period and across a large area. Such a study can better show how residents
in different regions change their activities in different ways in response
to rains with different durations, peak intensities, and accumulative rainfall levels.</p>
      <p id="d1e1305">Secondly, our research analysed the impacts of different features of the
rainfall events on human activities. Previous studies have often simply
characterized a disaster using its threat levels. For example, Zou et
al. (2018) used the average hurricane track
kernel density and its wind speed to define the threat levels. In this
study, instead, we extracted five major elements of a rainfall event and
employed the random forest model to study the impacts of different elements
on collective human activities.</p>
      <p id="d1e1309">Thirdly, we used the rainfall threshold to quantify urban resilience, and the
threshold is valuable for authorities to revise heavy-rain alerts.
Conventionally, heavy-rain alerts are usually based on rainfall intensity
and precipitation only and seldom consider the areal difference in
infrastructures. According to current Chinese standards, Chinese authorities issue a blue, yellow, and orange alert when precipitation is or will
be over 50 mm in 12, 6, and 3 h and the rain might not
stop (Mendiondo, 2005). A red alert is issued when
precipitation is or will be over 100 mm in 3 h and the rain might not
stop. Results from this study show that it is not appropriate to apply such
a unified alert standard to different groups of cities across China. In the less
resilient, fragile areas (Fig. 7), for instance, a rainfall event with
3.25 mm of precipitation per hour (i.e. 19.5 mm in 6 h) already triggers
significant human activity anomalies. As a result, the national heavy-rain-alert standard significantly underestimates the impacts of rainfall on the
residents in northwestern and central China.</p>
      <p id="d1e1312">Table 1 shows the precipitation thresholds of different city groups that
trigger human activity anomalies and the 6 h accumulative precipitation
based on which a heavy-rain warning should be issued. For example, for the
LH cities, a rainfall intensity of 1.8 mm and 6 h accumulative
precipitation of 10.8 mm should trigger a yellow heavy-rain warning. Such a value of
the 6 h accumulative precipitation is much lower than the current yellow Chinese
heavy-rain-warning standard (50 mm in 6 h). By contrast, for the
HH cities, the rainfall threshold and 6 h accumulative precipitation that
trigger human activity anomalies are 22.34 and 134.05 mm, respectively.
The accumulative precipitation is much higher than the yellow heavy-rain-warning standard. In other words, it is amateurish to issue a heavy-rain
warning when the 6 h accumulative precipitation is 50 mm for the HH
cities. Results from this study therefore are of great value for the
authorities who revise heavy-rain alerts across China to help local
residents be better prepared for such adverse events.</p>
      <p id="d1e1315">The study could be expanded. Rather than representing all the residents of a city,
the Tencent location request dataset is generated by over 1 billion
monthly active users. The Tencent dataset's aggregate geotagged human
activities may underestimate the effects of rainstorms on infrequent users,
particularly the elderly and children. To address this limitation and
further investigate human responses to various weather events, our future
studies will aim to integrate multisource geospatial datasets. Furthermore,
identifying disaster types such as rainstorm, waterlogging, and flood from
social media data and then analysing the regional response variation in
large-scale human activity in different disasters can improve deep
understanding of urban resilience.</p>
</sec>

      
      </body>
    <back><notes notes-type="codeavailability"><title>Code availability</title>

      <p id="d1e1323">All codes can be provided by the corresponding authors upon request.</p>
  </notes><notes notes-type="dataavailability"><title>Data availability</title>

      <p id="d1e1329">The information can be made available upon request to the corresponding author.</p>
  </notes><app-group>
        <supplementary-material position="anchor"><p id="d1e1332">The supplement related to this article is available online at: <inline-supplementary-material xlink:href="https://doi.org/10.5194/nhess-23-317-2023-supplement" xlink:title="pdf">https://doi.org/10.5194/nhess-23-317-2023-supplement</inline-supplementary-material>.</p></supplementary-material>
        </app-group><notes notes-type="authorcontribution"><title>Author contributions</title>

      <p id="d1e1341">JQ, YD, JY, and FL conceived and designed the study and methods;
JQ, JY, YD, NW, TM, and TP analysed the data; JQ, FL, YD,
and JY wrote the paper, and all co-authors contributed to the
interpretation of the results and to the text. All authors read the
manuscript and approved its submission.</p>
  </notes><notes notes-type="competinginterests"><title>Competing interests</title>

      <p id="d1e1347">The contact author has declared that none of the authors has any competing interests.</p>
  </notes><notes notes-type="disclaimer"><title>Disclaimer</title>

      <p id="d1e1353">Publisher’s note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.</p>
  </notes><notes notes-type="financialsupport"><title>Financial support</title>

      <p id="d1e1359">This research was jointly supported by the Strategic Priority Research
Program of the Chinese Academy of Sciences (grant no. XDA19040501), the
National Key Research and Development Program of China (grant no.
2017YFC1503003), and the National Science Foundation of China (grant nos. 42176205 and
41901395).</p>
  </notes><notes notes-type="reviewstatement"><title>Review statement</title>

      <p id="d1e1365">This paper was edited by Paola Reichenbach and reviewed by three anonymous referees.</p>
  </notes><ref-list>
    <title>References</title>

      <ref id="bib1.bib1"><label>1</label><?label 1?><mixed-citation>Adger, W. N., Hughes, T. P., Folke, C., Carpenter, S. R., and Rockström,
J.: Social-Ecological Resilience to Coastal Disasters, Science, 309,
1036–1039, <ext-link xlink:href="https://doi.org/10.1126/science.1112122" ext-link-type="DOI">10.1126/science.1112122</ext-link>, 2005.</mixed-citation></ref>
      <ref id="bib1.bib2"><label>2</label><?label 1?><mixed-citation>Aerts, J. C. J. H., Botzen, W. J. W., Emanuel, K., Lin, N., de Moel, H., and
Michel-Kerjan, E. O.: Evaluating Flood Resilience Strategies for Coastal
Megacities, Science, 344, 473–475, <ext-link xlink:href="https://doi.org/10.1126/science.1248222" ext-link-type="DOI">10.1126/science.1248222</ext-link>,
2014.</mixed-citation></ref>
      <ref id="bib1.bib3"><label>3</label><?label 1?><mixed-citation>Ambelu, A., Birhanu, Z., Tesfaye, A., Berhanu, N., Muhumuza, C., Kassahun,
W., Daba, T., and Woldemichael, K.: Intervention pathways towards improving
the resilience of pastoralists: A study from Borana communities, southern
Ethiopia, Weather Clim. Extrem., 17, 7–16,
<ext-link xlink:href="https://doi.org/10.1016/j.wace.2017.06.001" ext-link-type="DOI">10.1016/j.wace.2017.06.001</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib4"><label>4</label><?label 1?><mixed-citation>Bertilsson, L., Wiklund, K., de Moura Tebaldi, I., Rezende, O. M.,
Veról, A. P., and Miguez, M. G.: Urban flood resilience – A
multi-criteria index to integrate flood resilience into urban planning,
J. Hydrol., 573, 970–982,
<ext-link xlink:href="https://doi.org/10.1016/j.jhydrol.2018.06.052" ext-link-type="DOI">10.1016/j.jhydrol.2018.06.052</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib5"><label>5</label><?label 1?><mixed-citation>Brusberg, M. D. and Shively, R.: Building drought resilience in agriculture:
Partnerships and public outreach, Weather Clim. Extrem., 10, 40–49,
<ext-link xlink:href="https://doi.org/10.1016/j.wace.2015.10.003" ext-link-type="DOI">10.1016/j.wace.2015.10.003</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib6"><label>6</label><?label 1?><mixed-citation>Buehler, Y. A., Kellenberger, T. W., Small, D., and Itten, K. I.: Rapid
mapping with remote sensing data during flooding 2005 in Switzerland by
object-based methods: a case study, in: Geo-Environment and Landscape
Evolution II: Monitoring, Simulation, Management and Remediation,
GEO-ENVIRONMENT 2006, Rhodes, Greece, 391–400,
<ext-link xlink:href="https://doi.org/10.2495/GEO060391" ext-link-type="DOI">10.2495/GEO060391</ext-link>, 2006.</mixed-citation></ref>
      <ref id="bib1.bib7"><label>7</label><?label 1?><mixed-citation>Chan, F. K. S., Griffiths, J. A., Higgitt, D., Xu, S., Zhu, F., Tang, Y.-T.,
Xu, Y., and Thorne, C. R.: “Sponge City” in China – A breakthrough of
planning and flood risk management in the urban context, Land Use Pol.,
76, 772–778, <ext-link xlink:href="https://doi.org/10.1016/j.landusepol.2018.03.005" ext-link-type="DOI">10.1016/j.landusepol.2018.03.005</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib8"><label>8</label><?label 1?><mixed-citation>
Cleveland, R., Cleveland, W., McRae, J. E., and Terpenning, I. J.: STL: A
seasonal-trend decomposition procedure based on loess (with discussion),
undefined, J. Off. Stat., 1990, 6, 3–73, 1990.</mixed-citation></ref>
      <ref id="bib1.bib9"><label>9</label><?label 1?><mixed-citation>de Bruijn, K. M.: Resilience and flood risk management, Water Pol., 6,
53–66, <ext-link xlink:href="https://doi.org/10.2166/wp.2004.0004" ext-link-type="DOI">10.2166/wp.2004.0004</ext-link>, 2004.</mixed-citation></ref>
      <ref id="bib1.bib10"><label>10</label><?label 1?><mixed-citation>Dewan, T. H.: Societal impacts and vulnerability to floods in Bangladesh and
Nepal, Weather  Clim. Extrem., 7, 36–42,
<ext-link xlink:href="https://doi.org/10.1016/j.wace.2014.11.001" ext-link-type="DOI">10.1016/j.wace.2014.11.001</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib11"><label>11</label><?label 1?><mixed-citation>Geller, S. C., Gregg, J. P., Hagerman, P., and Rocke, D. M.: Transformation
and normalization of oligonucleotide microarray data, Bioinformatics, 19,
1817–1823, <ext-link xlink:href="https://doi.org/10.1093/bioinformatics/btg245" ext-link-type="DOI">10.1093/bioinformatics/btg245</ext-link>, 2003.</mixed-citation></ref>
      <ref id="bib1.bib12"><label>12</label><?label 1?><mixed-citation>Ghaffarian, S., Kerle, N., and Filatova, T.: Remote Sensing-Based Proxies
for Urban Disaster Risk Management and Resilience: A Review, Remote Sens.,
10, 1760, <ext-link xlink:href="https://doi.org/10.3390/rs10111760" ext-link-type="DOI">10.3390/rs10111760</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib13"><label>13</label><?label 1?><mixed-citation>Grinberger, A. Y. and Felsenstein, D.: Dynamic agent based simulation of
welfare effects of urban disasters, Computers, Environ. Urban
Syst., 59, 129–141, <ext-link xlink:href="https://doi.org/10.1016/j.compenvurbsys.2016.06.005" ext-link-type="DOI">10.1016/j.compenvurbsys.2016.06.005</ext-link>,
2016.</mixed-citation></ref>
      <ref id="bib1.bib14"><label>14</label><?label 1?><mixed-citation>Guan, X. and Chen, C.: Using social media data to understand and assess
disasters, Nat. Hazards, 74, 837–850,
<ext-link xlink:href="https://doi.org/10.1007/s11069-014-1217-1" ext-link-type="DOI">10.1007/s11069-014-1217-1</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib15"><label>15</label><?label 1?><mixed-citation>
Honey, M., Brink, S., Chang, S., Davidson, R., Amyx, P., Pyatt, S., Mills,
R., Eguchi, R., Bevington, J., Panjwani, D., Hill, A., and Adams, B.:
Uncovering Community Disruption Using Remote Sensing: An Assessment of Early
Recovery in Post-earthquake Haiti, Disaster Research Center, Miscellaneous Report #69; University of Delaware, Disaster Research Center: Newark, DE, USA, 2010.</mixed-citation></ref>
      <ref id="bib1.bib16"><label>16</label><?label 1?><mixed-citation>Hong, B., Bonczak, B. J., Gupta, A., and Kontokosta, C. E.: Measuring
inequality in community resilience to natural disasters using large-scale
mobility data, Nat. Commun., 12, 1870,
<ext-link xlink:href="https://doi.org/10.1038/s41467-021-22160-w" ext-link-type="DOI">10.1038/s41467-021-22160-w</ext-link>, 2021.</mixed-citation></ref>
      <ref id="bib1.bib17"><label>17</label><?label 1?><mixed-citation>Huang, W. and Ling, M.: System resilience assessment method of urban
lifeline system for GIS, Computers, Environ. Urban Syst., 71,
67–80, <ext-link xlink:href="https://doi.org/10.1016/j.compenvurbsys.2018.04.003" ext-link-type="DOI">10.1016/j.compenvurbsys.2018.04.003</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib18"><label>18</label><?label 1?><mixed-citation>Kasmalkar, I. G., Serafin, K. A., Miao, Y., Bick, I. A., Ortolano, L.,
Ouyang, D., and Suckale, J.: When floods hit the road: Resilience to
flood-related traffic disruption in the San Francisco Bay Area and beyond,
Sci. Adv., 6, eaba2423, <ext-link xlink:href="https://doi.org/10.1126/sciadv.aba2423" ext-link-type="DOI">10.1126/sciadv.aba2423</ext-link>, 2020.</mixed-citation></ref>
      <ref id="bib1.bib19"><label>19</label><?label 1?><mixed-citation>Kryvasheyeu, Y., Chen, H., Obradovich, N., Moro, E., and Hentenryck, P. V.:
Rapid assessment of disaster damage using social media activity, Sci.
Adv., 2, e1500779, <ext-link xlink:href="https://doi.org/10.1126/sciadv.1500779" ext-link-type="DOI">10.1126/sciadv.1500779</ext-link>,
2016.</mixed-citation></ref>
      <ref id="bib1.bib20"><label>20</label><?label 1?><mixed-citation>
Levizzani, V., Kidd, C., Kirschbaum, D. B., Kummerow, C. D., Nakamura, K.,
and Turk, F. J.: Satellite Precipitation Measurement, Springer Nature, 500 pp., Springer Nature: Dordrecht, The Netherlands, 2020.</mixed-citation></ref>
      <ref id="bib1.bib21"><label>21</label><?label 1?><mixed-citation>Liao, K.-H.: A Theory on Urban Resilience to Floods–A Basis for Alternative
Planning Practices, E&amp;S, 17, art48,
<ext-link xlink:href="https://doi.org/10.5751/ES-05231-170448" ext-link-type="DOI">10.5751/ES-05231-170448</ext-link>, 2012.</mixed-citation></ref>
      <ref id="bib1.bib22"><label>22</label><?label 1?><mixed-citation>Liaw, A. and Wiener, M.: Classification and Regression by RandomForest,
Forest, 23, <ext-link xlink:href="https://doi.org/10.1021/ci034160g" ext-link-type="DOI">10.1021/ci034160g</ext-link>, 2001.</mixed-citation></ref>
      <ref id="bib1.bib23"><label>23</label><?label 1?><mixed-citation>
Liu, Y., Liu, X., Gao, S., Gong, L., Kang, C., Zhi, Y., Chi, G., and Shi,
L.: Social Sensing: A New Approach to Understanding Our Socioeconomic
Environments, Ann. Assoc. Am. Geogr., 105,
512–530, 2015.</mixed-citation></ref>
      <ref id="bib1.bib24"><label>24</label><?label 1?><mixed-citation>Liu, Z., Du, Y., Yi, J., Liang, F., Ma, T., and Pei, T.: Quantitative
Association between Nighttime Lights and Geo-Tagged Human Activity Dynamics
during Typhoon Mangkhut, Remote Sens., 11, 2091,
<ext-link xlink:href="https://doi.org/10.3390/rs11182091" ext-link-type="DOI">10.3390/rs11182091</ext-link>, 2019a.</mixed-citation></ref>
      <ref id="bib1.bib25"><label>25</label><?label 1?><mixed-citation>Liu, Z., Du, Y., Yi, J., Liang, F., and Pei, T.: Quantitative estimates of
collective geo-tagged human activities in response to typhoon Hato using
location-aware big data, Int. J. Dig. Earth, 1–21,
<ext-link xlink:href="https://doi.org/10.1080/17538947.2019.1645894" ext-link-type="DOI">10.1080/17538947.2019.1645894</ext-link>, 2019b.</mixed-citation></ref>
      <ref id="bib1.bib26"><label>26</label><?label 1?><mixed-citation>Ma, T.: Multi-Level Relationships between Satellite-Derived Nighttime
Lighting Signals and Social Media–Derived Human Population Dynamics, Remote
Sens., 10, 1128, <ext-link xlink:href="https://doi.org/10.3390/rs10071128" ext-link-type="DOI">10.3390/rs10071128</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib27"><label>27</label><?label 1?><mixed-citation>Marra, F., Nikolopoulos, E. I., Creutin, J. D., and Borga, M.: Space–time
organization of debris flows-triggering rainfall and its effect on the
identification of the rainfall threshold relationship, J. Hydrol.,
541, 246–255, <ext-link xlink:href="https://doi.org/10.1016/j.jhydrol.2015.10.010" ext-link-type="DOI">10.1016/j.jhydrol.2015.10.010</ext-link>, 2016.</mixed-citation></ref>
      <ref id="bib1.bib28"><label>28</label><?label 1?><mixed-citation>Martín, Y., Cutter, S. L., and Li, Z.: Bridging Twitter and Survey Data
for Evacuation Assessment of Hurricane Matthew and Hurricane Irma, Nat.
Hazards Rev., 21, 04020003,
<ext-link xlink:href="https://doi.org/10.1061/(ASCE)NH.1527-6996.0000354" ext-link-type="DOI">10.1061/(ASCE)NH.1527-6996.0000354</ext-link>, 2020a.</mixed-citation></ref>
      <ref id="bib1.bib29"><label>29</label><?label 1?><mixed-citation>Martín, Y., Cutter, S. L., Li, Z., Emrich, C. T., and Mitchell, J. T.:
Using geotagged tweets to track population movements to and from Puerto Rico
after Hurricane Maria, Popul. Environ., 42, 4–27,
<ext-link xlink:href="https://doi.org/10.1007/s11111-020-00338-6" ext-link-type="DOI">10.1007/s11111-020-00338-6</ext-link>, 2020b.</mixed-citation></ref>
      <ref id="bib1.bib30"><label>30</label><?label 1?><mixed-citation>McDougall, K. and Temple-Watts, P.: THE USE OF LIDAR AND VOLUNTEERED
GEOGRAPHIC INFORMATION TO MAP FLOOD EXTENTS AND INUNDATION, ISPRS Ann.
Photogramm. Remote Sens. Spatial Inf. Sci., I–4, 251–256,
<ext-link xlink:href="https://doi.org/10.5194/isprsannals-I-4-251-2012" ext-link-type="DOI">10.5194/isprsannals-I-4-251-2012</ext-link>, 2012.</mixed-citation></ref>
      <ref id="bib1.bib31"><label>31</label><?label 1?><mixed-citation>Meerow, S., Newell, J. P., and Stults, M.: Defining urban resilience: A
review, Landsc. Urban Plan., 147, 38–49,
<ext-link xlink:href="https://doi.org/10.1016/j.landurbplan.2015.11.011" ext-link-type="DOI">10.1016/j.landurbplan.2015.11.011</ext-link>, 2016.</mixed-citation></ref>
      <ref id="bib1.bib32"><label>32</label><?label 1?><mixed-citation>
Mendiondo, E. M.: FLOOD RISK MANAGEMENT OF URBAN WATERS IN HUMID TROPICS:
EARLY WARNING, PROTECTION AND REHABILITATION, 14, in: Proceedings of the Workshop on Integrated Urban Water Managmt in Humid Tropics, Foz de Iguaçu, Brazil, 2–3 April 2005, 2–3 pp., 2005.</mixed-citation></ref>
      <ref id="bib1.bib33"><label>33</label><?label 1?><mixed-citation>Mika, S., Ratsch, G., Weston, J., Scholkopf, B., and Mullers, K. R.: Fisher
discriminant analysis with kernels, in: Neural Networks for Signal
Processing IX: Proceedings of the 1999 IEEE Signal Processing Society
Workshop (Cat. No.98TH8468),  41–48, <ext-link xlink:href="https://doi.org/10.1109/NNSP.1999.788121" ext-link-type="DOI">10.1109/NNSP.1999.788121</ext-link>, 1999.</mixed-citation></ref>
      <ref id="bib1.bib34"><label>34</label><?label 1?><mixed-citation>Mpandeli, S., Nhamo, L., Moeletsi, M., Masupha, T., Magidi, J., Tshikolomo,
K., Liphadzi, S., Naidoo, D., and Mabhaudhi, T.: Assessing climate change
and adaptive capacity at local scale using observed and remotely sensed
data, Weather  Clim. Extrem., 26, 100240,
<ext-link xlink:href="https://doi.org/10.1016/j.wace.2019.100240" ext-link-type="DOI">10.1016/j.wace.2019.100240</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib35"><label>35</label><?label 1?><mixed-citation>Myhre, G., Alterskjær, K., Stjern, C. W., Hodnebrog, Ø., Marelle, L.,
Samset, B. H., Sillmann, J., Schaller, N., Fischer, E., Schulz, M., and
Stohl, A.: Frequency of extreme precipitation increases extensively with
event rareness under global warming, Sci. Rep., 9, 16063,
<ext-link xlink:href="https://doi.org/10.1038/s41598-019-52277-4" ext-link-type="DOI">10.1038/s41598-019-52277-4</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib36"><label>36</label><?label 1?><mixed-citation>Nahiduzzaman, K. M., Aldosary, A. S., and Rahman, M. T.: Flood induced
vulnerability in strategic plan making process of Riyadh city, Hab.
Int., 49, 375–385,
<ext-link xlink:href="https://doi.org/10.1016/j.habitatint.2015.05.034" ext-link-type="DOI">10.1016/j.habitatint.2015.05.034</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib37"><label>37</label><?label 1?><mixed-citation>Naidu, S., Sajinkumar, K. S., Oommen, T., Anuja, V. J., Samuel, R. A., and
Muraleedharan, C.: Early warning system for shallow landslides using
rainfall threshold and slope stability analysis, Geosci. Front., 9,
1871–1882, <ext-link xlink:href="https://doi.org/10.1016/j.gsf.2017.10.008" ext-link-type="DOI">10.1016/j.gsf.2017.10.008</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib38"><label>38</label><?label 1?><mixed-citation>Ogie, R. I., Holderness, T., Dunn, S., and Turpin, E.: Assessing the
vulnerability of hydrological infrastructure to flood damage in coastal
cities of developing nations, Comput., Environ. Urban Syst., 68,
97–109, <ext-link xlink:href="https://doi.org/10.1016/j.compenvurbsys.2017.11.004" ext-link-type="DOI">10.1016/j.compenvurbsys.2017.11.004</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib39"><label>39</label><?label 1?><mixed-citation>Olsson, L., Jerneck, A., Thoren, H., Persson, J., and O'Byrne, D.: Why
resilience is unappealing to social science: Theoretical and empirical
investigations of the scientific use of resilience, Sci. Adv., 1,
e1400217, <ext-link xlink:href="https://doi.org/10.1126/sciadv.1400217" ext-link-type="DOI">10.1126/sciadv.1400217</ext-link>, 2015.</mixed-citation></ref>
      <ref id="bib1.bib40"><label>40</label><?label 1?><mixed-citation>Östh, J., Reggiani, A., and Galiazzo, G.: Spatial economic resilience
and accessibility: A joint perspective, Computers, Environ. Urban
Syst., 49, 148–159, <ext-link xlink:href="https://doi.org/10.1016/j.compenvurbsys.2014.07.007" ext-link-type="DOI">10.1016/j.compenvurbsys.2014.07.007</ext-link>,
2015.</mixed-citation></ref>
      <ref id="bib1.bib41"><label>41</label><?label 1?><mixed-citation>O'Sullivan, J. J., Bradford, R. A., Bonaiuto, M., De Dominicis, S., Rotko, P., Aaltonen, J., Waylen, K., and Langan, S. J.: Enhancing flood resilience through improved risk communications, Nat. Hazards Earth Syst. Sci., 12, 2271–2282, <ext-link xlink:href="https://doi.org/10.5194/nhess-12-2271-2012" ext-link-type="DOI">10.5194/nhess-12-2271-2012</ext-link>, 2012.</mixed-citation></ref>
      <ref id="bib1.bib42"><label>42</label><?label 1?><mixed-citation>Ouyang, M., Dueñas-Osorio, L., and Min, X.: A three-stage resilience
analysis framework for urban infrastructure systems, Struct. Safe.,
36–37, 23–31, <ext-link xlink:href="https://doi.org/10.1016/j.strusafe.2011.12.004" ext-link-type="DOI">10.1016/j.strusafe.2011.12.004</ext-link>, 2012.</mixed-citation></ref>
      <ref id="bib1.bib43"><label>43</label><?label 1?><mixed-citation>Owrangi, A. M., Lannigan, R., and Simonovic, S. P.: Interaction between
land-use change, flooding and human health in Metro Vancouver, Canada, Nat.
Hazards, 72, 1219–1230, <ext-link xlink:href="https://doi.org/10.1007/s11069-014-1064-0" ext-link-type="DOI">10.1007/s11069-014-1064-0</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib44"><label>44</label><?label 1?><mixed-citation>Pal, M.: Random forest classifier for remote sensing classification,
Int. J. Remote Sens., 26, 217–222,
<ext-link xlink:href="https://doi.org/10.1080/01431160412331269698" ext-link-type="DOI">10.1080/01431160412331269698</ext-link>, 2005.</mixed-citation></ref>
      <ref id="bib1.bib45"><label>45</label><?label 1?><mixed-citation>Poulin, C. and Kane, M. B.: Infrastructure resilience curves: Performance
measures and summary metrics, Reliab. Eng. Syst. Safet.,
216, 107926, <ext-link xlink:href="https://doi.org/10.1016/j.ress.2021.107926" ext-link-type="DOI">10.1016/j.ress.2021.107926</ext-link>, 2021.</mixed-citation></ref>
      <ref id="bib1.bib46"><label>46</label><?label 1?><mixed-citation>Qian, J., Liu, Z., Du, Y., Wang, N., Yi, J., Sun, Y., Ma, T., Pei, T., and
Zhou, C.: Multi-level Inter-regional Migrant Population Estimation Using
Multi-source Spatiotemporal Big Data: A Case Study of Migrants in Hubei
Province During the Outbreak of COVID-19 in Wuhan, in: Mapping COVID-19 in
Space and Time: Understanding the Spatial and Temporal Dynamics of a Global
Pandemic, edited by: Shaw, S.-L. and Sui, D., Springer International
Publishing, Cham, 169–188,
<ext-link xlink:href="https://doi.org/10.1007/978-3-030-72808-3_9" ext-link-type="DOI">10.1007/978-3-030-72808-3_9</ext-link>, 2021a.</mixed-citation></ref>
      <ref id="bib1.bib47"><label>47</label><?label 1?><mixed-citation>Qian, J., Liu, Z., Du, Y., Liang, F., Yi, J., Ma, T., and Pei, T.: Quantify
city-level dynamic functions across China using social media and POIs data,
Comput. Environ. Urban Syst., 85, 101552,
<ext-link xlink:href="https://doi.org/10.1016/j.compenvurbsys.2020.101552" ext-link-type="DOI">10.1016/j.compenvurbsys.2020.101552</ext-link>, 2021b.</mixed-citation></ref>
      <ref id="bib1.bib48"><label>48</label><?label 1?><mixed-citation>Qian, J., Du, Y., Yi, J., Liang, F., Huang, S., Wang, X., Wang, N., Tu, W.,
Pei, T., and Ma, T.: Regional geographical and climatic environments affect
urban rainstorm perception sensitivity across China, Sustain. Cities
Soc., 87, 104213, <ext-link xlink:href="https://doi.org/10.1016/j.scs.2022.104213" ext-link-type="DOI">10.1016/j.scs.2022.104213</ext-link>, 2022.</mixed-citation></ref>
      <ref id="bib1.bib49"><label>49</label><?label 1?><mixed-citation>Román, M., Stokes, E., Shrestha, R., Wang, Z., Schultz, L., Carlo, E.,
Sun, Q., Bell, J., Molthan, A., Kalb, V., ji, C., Seto, K., Mcclain, S., and
Enenkel, M.: Satellite-based assessment of electricity restoration efforts
in Puerto Rico after Hurricane Maria, PLOS ONE, 14, e0218883,
<ext-link xlink:href="https://doi.org/10.1371/journal.pone.0218883" ext-link-type="DOI">10.1371/journal.pone.0218883</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib50"><label>50</label><?label 1?><mixed-citation>Rosner, B.: On the Detection of Many Outliers, null, Technometrics, 17, 221–227,
<ext-link xlink:href="https://doi.org/10.2307/1268354" ext-link-type="DOI">10.2307/1268354</ext-link>, 1975.</mixed-citation></ref>
      <ref id="bib1.bib51"><label>51</label><?label 1?><mixed-citation>Shiferaw, B., Tesfaye, K., Kassie, M., Abate, T., Prasanna, B. M., and
Menkir, A.: Managing vulnerability to drought and enhancing livelihood
resilience in sub-Saharan Africa: Technological, institutional and policy
options, Weather Clim. Extrem., 3, 67–79,
<ext-link xlink:href="https://doi.org/10.1016/j.wace.2014.04.004" ext-link-type="DOI">10.1016/j.wace.2014.04.004</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib52"><label>52</label><?label 1?><mixed-citation>Song, J., Chang, Z., Li, W., Feng, Z., Wu, J., Cao, Q., and Liu, J.:
Resilience-vulnerability balance to urban flooding: A case study in a
densely populated coastal city in China, Cities, 95, 102381,
<ext-link xlink:href="https://doi.org/10.1016/j.cities.2019.06.012" ext-link-type="DOI">10.1016/j.cities.2019.06.012</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib53"><label>53</label><?label 1?><mixed-citation>
Stefan, V., Fabio, G.-T., Josh, L., Jan, K., and Brenda, J.: Global Trends
in Satellite-based Emergency Mapping, Science, 353, 247–252, 2016.</mixed-citation></ref>
      <ref id="bib1.bib54"><label>54</label><?label 1?><mixed-citation>Strobl, C., Boulesteix, A.-L., Zeileis, A., and Hothorn, T.: Bias in random
forest variable importance measures: Illustrations, sources and a solution,
BMC Bioinfo., 8, 25, <ext-link xlink:href="https://doi.org/10.1186/1471-2105-8-25" ext-link-type="DOI">10.1186/1471-2105-8-25</ext-link>, 2007.</mixed-citation></ref>
      <ref id="bib1.bib55"><label>55</label><?label 1?><mixed-citation>Tellman, B., Sullivan, J. A., Kuhn, C., Kettner, A. J., Doyle, C. S.,
Brakenridge, G. R., Erickson, T. A., and Slayback, D. A.: Satellite imaging
reveals increased proportion of population exposed to floods, Nature, 596,
80–86, <ext-link xlink:href="https://doi.org/10.1038/s41586-021-03695-w" ext-link-type="DOI">10.1038/s41586-021-03695-w</ext-link>, 2021.</mixed-citation></ref>
      <ref id="bib1.bib56"><label>56</label><?label 1?><mixed-citation>Vallis, O., Hochenbaum, J., and Kejariwal, A.: A Novel Technique for
Long-Term Anomaly Detection in the Cloud, 6th {
USENIX} Workshop on Hot Topics in Cloud Computing (HotCloud
14), 15 pp., <ext-link xlink:href="https://doi.org/10.5555/2696535.2696550" ext-link-type="DOI">10.5555/2696535.2696550</ext-link>, 2014.</mixed-citation></ref>
      <ref id="bib1.bib57"><label>57</label><?label 1?><mixed-citation>Wang, B., Loo, B. P. Y., Zhen, F., and Xi, G.: Urban resilience from the
lens of social media data: Responses to urban flooding in Nanjing, China,
Cities, 106, 102884, <ext-link xlink:href="https://doi.org/10.1016/j.cities.2020.102884" ext-link-type="DOI">10.1016/j.cities.2020.102884</ext-link>, 2020.</mixed-citation></ref>
      <ref id="bib1.bib58"><label>58</label><?label 1?><mixed-citation>Wang, J., Meng, B., Pei, T., Du, Y., Zhang, J., Chen, S., Tian, B., and Zhi,
G.: Mapping the exposure and sensitivity to heat wave events in China's
megacities, Sci. Total Environ., 755, 142734,
<ext-link xlink:href="https://doi.org/10.1016/j.scitotenv.2020.142734" ext-link-type="DOI">10.1016/j.scitotenv.2020.142734</ext-link>, 2021.</mixed-citation></ref>
      <ref id="bib1.bib59"><label>59</label><?label 1?><mixed-citation>Wang, N., Du, Y., Liang, F., Yi, J., and Wang, H.: Spatiotemporal Changes of
Urban Rainstorm-Related Micro-Blogging Activities in Response to Rainstorms:
A Case Study in Beijing, China, Appl. Sci., 9, 4629,
<ext-link xlink:href="https://doi.org/10.3390/app9214629" ext-link-type="DOI">10.3390/app9214629</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib60"><label>60</label><?label 1?><mixed-citation>Wang, Y. and Taylor, J. E.: Coupling sentiment and human mobility in natural
disasters: a Twitter-based study of the 2014 South Napa Earthquake, Nat.
Hazards, 92, 907–925, <ext-link xlink:href="https://doi.org/10.1007/s11069-018-3231-1" ext-link-type="DOI">10.1007/s11069-018-3231-1</ext-link>, 2018.</mixed-citation></ref>
      <ref id="bib1.bib61"><label>61</label><?label 1?><mixed-citation>Yabe, T., Tsubouchi, K., Fujiwara, N., Sekimoto, Y., and Ukkusuri, S. V.:
Understanding post-disaster population recovery patterns, J.
Roy. Soc. Inter., 17, 20190532,
<ext-link xlink:href="https://doi.org/10.1098/rsif.2019.0532" ext-link-type="DOI">10.1098/rsif.2019.0532</ext-link>, 2020.</mixed-citation></ref>
      <ref id="bib1.bib62"><label>62</label><?label 1?><mixed-citation>Yi, J., Du, Y., Liang, F., Pei, T., Ma, T., and Zhou, C.: Anomalies of dwellers' collective geotagged behaviors in response to rainstorms: a case study of eight cities in China using smartphone location data, Nat. Hazards Earth Syst. Sci., 19, 2169–2182, <ext-link xlink:href="https://doi.org/10.5194/nhess-19-2169-2019" ext-link-type="DOI">10.5194/nhess-19-2169-2019</ext-link>, 2019.
</mixed-citation></ref><?xmltex \hack{\newpage}?>
      <ref id="bib1.bib63"><label>63</label><?label 1?><mixed-citation>Yue, Y., Zhuang, Y., Yeh, A. G. O., Xie, J.-Y., Ma, C.-L., and Li, Q.-Q.:
Measurements of POI-based mixed use and their relationships with
neighbourhood vibrancy, Int. J. Geogr. Info.
Sci., 31, 658–675, <ext-link xlink:href="https://doi.org/10.1080/13658816.2016.1220561" ext-link-type="DOI">10.1080/13658816.2016.1220561</ext-link>, 2017.</mixed-citation></ref>
      <ref id="bib1.bib64"><label>64</label><?label 1?><mixed-citation>Zhang, R., Chen, Y., Zhang, X., Ma, Q., and Ren, L.: Mapping homogeneous
regions for flash floods using machine learning: A case study in Jiangxi
province, China, Int. J. Appl. Earth Observ.
Geoinfo., 108, 102717, <ext-link xlink:href="https://doi.org/10.1016/j.jag.2022.102717" ext-link-type="DOI">10.1016/j.jag.2022.102717</ext-link>,
2022.</mixed-citation></ref>
      <ref id="bib1.bib65"><label>65</label><?label 1?><mixed-citation>Zheng, S., Wang, J., Sun, C., Zhang, X., and Kahn, M. E.: Air pollution
lowers Chinese urbanites' expressed happiness on social media, Na. Human
Behav., 3, 237–243, <ext-link xlink:href="https://doi.org/10.1038/s41562-018-0521-2" ext-link-type="DOI">10.1038/s41562-018-0521-2</ext-link>, 2019.</mixed-citation></ref>
      <ref id="bib1.bib66"><label>66</label><?label 1?><mixed-citation>Zou, L., Lam, N., Cai, H., and Qiang, Y.: Mining Twitter Data for Improved
Understanding of Disaster Resilience, Ann. Assoc. Am.
Geogr., 108, 1422–1441, <ext-link xlink:href="https://doi.org/10.1080/24694452.2017.1421897" ext-link-type="DOI">10.1080/24694452.2017.1421897</ext-link>,
2018.</mixed-citation></ref>
      <ref id="bib1.bib67"><label>67</label><?label 1?><mixed-citation>Zou, L., Lam, N. S. N., Shams, S., Cai, H., Meyer, M. A., Yang, S., Lee, K.,
Park, S.-J., and Reams, M. A.: Social and geographical disparities in
Twitter use during Hurricane Harvey, Int. J. Dig. Earth,
12, 1300–1318, <ext-link xlink:href="https://doi.org/10.1080/17538947.2018.1545878" ext-link-type="DOI">10.1080/17538947.2018.1545878</ext-link>, 2019.</mixed-citation></ref>

  </ref-list></back>
    <!--<article-title-html>Quantifying unequal urban resilience to rainfall across China from location-aware big data</article-title-html>
<abstract-html/>
<ref-html id="bib1.bib1"><label>1</label><mixed-citation>
Adger, W. N., Hughes, T. P., Folke, C., Carpenter, S. R., and Rockström,
J.: Social-Ecological Resilience to Coastal Disasters, Science, 309,
1036–1039, <a href="https://doi.org/10.1126/science.1112122" target="_blank">https://doi.org/10.1126/science.1112122</a>, 2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib2"><label>2</label><mixed-citation>
Aerts, J. C. J. H., Botzen, W. J. W., Emanuel, K., Lin, N., de Moel, H., and
Michel-Kerjan, E. O.: Evaluating Flood Resilience Strategies for Coastal
Megacities, Science, 344, 473–475, <a href="https://doi.org/10.1126/science.1248222" target="_blank">https://doi.org/10.1126/science.1248222</a>,
2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib3"><label>3</label><mixed-citation>
Ambelu, A., Birhanu, Z., Tesfaye, A., Berhanu, N., Muhumuza, C., Kassahun,
W., Daba, T., and Woldemichael, K.: Intervention pathways towards improving
the resilience of pastoralists: A study from Borana communities, southern
Ethiopia, Weather Clim. Extrem., 17, 7–16,
<a href="https://doi.org/10.1016/j.wace.2017.06.001" target="_blank">https://doi.org/10.1016/j.wace.2017.06.001</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib4"><label>4</label><mixed-citation>
Bertilsson, L., Wiklund, K., de Moura Tebaldi, I., Rezende, O. M.,
Veról, A. P., and Miguez, M. G.: Urban flood resilience – A
multi-criteria index to integrate flood resilience into urban planning,
J. Hydrol., 573, 970–982,
<a href="https://doi.org/10.1016/j.jhydrol.2018.06.052" target="_blank">https://doi.org/10.1016/j.jhydrol.2018.06.052</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib5"><label>5</label><mixed-citation>
Brusberg, M. D. and Shively, R.: Building drought resilience in agriculture:
Partnerships and public outreach, Weather Clim. Extrem., 10, 40–49,
<a href="https://doi.org/10.1016/j.wace.2015.10.003" target="_blank">https://doi.org/10.1016/j.wace.2015.10.003</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib6"><label>6</label><mixed-citation>
Buehler, Y. A., Kellenberger, T. W., Small, D., and Itten, K. I.: Rapid
mapping with remote sensing data during flooding 2005 in Switzerland by
object-based methods: a case study, in: Geo-Environment and Landscape
Evolution II: Monitoring, Simulation, Management and Remediation,
GEO-ENVIRONMENT 2006, Rhodes, Greece, 391–400,
<a href="https://doi.org/10.2495/GEO060391" target="_blank">https://doi.org/10.2495/GEO060391</a>, 2006.
</mixed-citation></ref-html>
<ref-html id="bib1.bib7"><label>7</label><mixed-citation>
Chan, F. K. S., Griffiths, J. A., Higgitt, D., Xu, S., Zhu, F., Tang, Y.-T.,
Xu, Y., and Thorne, C. R.: “Sponge City” in China – A breakthrough of
planning and flood risk management in the urban context, Land Use Pol.,
76, 772–778, <a href="https://doi.org/10.1016/j.landusepol.2018.03.005" target="_blank">https://doi.org/10.1016/j.landusepol.2018.03.005</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib8"><label>8</label><mixed-citation>
Cleveland, R., Cleveland, W., McRae, J. E., and Terpenning, I. J.: STL: A
seasonal-trend decomposition procedure based on loess (with discussion),
undefined, J. Off. Stat., 1990, 6, 3–73, 1990.
</mixed-citation></ref-html>
<ref-html id="bib1.bib9"><label>9</label><mixed-citation>
de Bruijn, K. M.: Resilience and flood risk management, Water Pol., 6,
53–66, <a href="https://doi.org/10.2166/wp.2004.0004" target="_blank">https://doi.org/10.2166/wp.2004.0004</a>, 2004.
</mixed-citation></ref-html>
<ref-html id="bib1.bib10"><label>10</label><mixed-citation>
Dewan, T. H.: Societal impacts and vulnerability to floods in Bangladesh and
Nepal, Weather  Clim. Extrem., 7, 36–42,
<a href="https://doi.org/10.1016/j.wace.2014.11.001" target="_blank">https://doi.org/10.1016/j.wace.2014.11.001</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib11"><label>11</label><mixed-citation>
Geller, S. C., Gregg, J. P., Hagerman, P., and Rocke, D. M.: Transformation
and normalization of oligonucleotide microarray data, Bioinformatics, 19,
1817–1823, <a href="https://doi.org/10.1093/bioinformatics/btg245" target="_blank">https://doi.org/10.1093/bioinformatics/btg245</a>, 2003.
</mixed-citation></ref-html>
<ref-html id="bib1.bib12"><label>12</label><mixed-citation>
Ghaffarian, S., Kerle, N., and Filatova, T.: Remote Sensing-Based Proxies
for Urban Disaster Risk Management and Resilience: A Review, Remote Sens.,
10, 1760, <a href="https://doi.org/10.3390/rs10111760" target="_blank">https://doi.org/10.3390/rs10111760</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib13"><label>13</label><mixed-citation>
Grinberger, A. Y. and Felsenstein, D.: Dynamic agent based simulation of
welfare effects of urban disasters, Computers, Environ. Urban
Syst., 59, 129–141, <a href="https://doi.org/10.1016/j.compenvurbsys.2016.06.005" target="_blank">https://doi.org/10.1016/j.compenvurbsys.2016.06.005</a>,
2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib14"><label>14</label><mixed-citation>
Guan, X. and Chen, C.: Using social media data to understand and assess
disasters, Nat. Hazards, 74, 837–850,
<a href="https://doi.org/10.1007/s11069-014-1217-1" target="_blank">https://doi.org/10.1007/s11069-014-1217-1</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib15"><label>15</label><mixed-citation>
Honey, M., Brink, S., Chang, S., Davidson, R., Amyx, P., Pyatt, S., Mills,
R., Eguchi, R., Bevington, J., Panjwani, D., Hill, A., and Adams, B.:
Uncovering Community Disruption Using Remote Sensing: An Assessment of Early
Recovery in Post-earthquake Haiti, Disaster Research Center, Miscellaneous Report #69; University of Delaware, Disaster Research Center: Newark, DE, USA, 2010.
</mixed-citation></ref-html>
<ref-html id="bib1.bib16"><label>16</label><mixed-citation>
Hong, B., Bonczak, B. J., Gupta, A., and Kontokosta, C. E.: Measuring
inequality in community resilience to natural disasters using large-scale
mobility data, Nat. Commun., 12, 1870,
<a href="https://doi.org/10.1038/s41467-021-22160-w" target="_blank">https://doi.org/10.1038/s41467-021-22160-w</a>, 2021.
</mixed-citation></ref-html>
<ref-html id="bib1.bib17"><label>17</label><mixed-citation>
Huang, W. and Ling, M.: System resilience assessment method of urban
lifeline system for GIS, Computers, Environ. Urban Syst., 71,
67–80, <a href="https://doi.org/10.1016/j.compenvurbsys.2018.04.003" target="_blank">https://doi.org/10.1016/j.compenvurbsys.2018.04.003</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib18"><label>18</label><mixed-citation>
Kasmalkar, I. G., Serafin, K. A., Miao, Y., Bick, I. A., Ortolano, L.,
Ouyang, D., and Suckale, J.: When floods hit the road: Resilience to
flood-related traffic disruption in the San Francisco Bay Area and beyond,
Sci. Adv., 6, eaba2423, <a href="https://doi.org/10.1126/sciadv.aba2423" target="_blank">https://doi.org/10.1126/sciadv.aba2423</a>, 2020.
</mixed-citation></ref-html>
<ref-html id="bib1.bib19"><label>19</label><mixed-citation>
Kryvasheyeu, Y., Chen, H., Obradovich, N., Moro, E., and Hentenryck, P. V.:
Rapid assessment of disaster damage using social media activity, Sci.
Adv., 2, e1500779, <a href="https://doi.org/10.1126/sciadv.1500779" target="_blank">https://doi.org/10.1126/sciadv.1500779</a>,
2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib20"><label>20</label><mixed-citation>
Levizzani, V., Kidd, C., Kirschbaum, D. B., Kummerow, C. D., Nakamura, K.,
and Turk, F. J.: Satellite Precipitation Measurement, Springer Nature, 500 pp., Springer Nature: Dordrecht, The Netherlands, 2020.
</mixed-citation></ref-html>
<ref-html id="bib1.bib21"><label>21</label><mixed-citation>
Liao, K.-H.: A Theory on Urban Resilience to Floods–A Basis for Alternative
Planning Practices, E&amp;S, 17, art48,
<a href="https://doi.org/10.5751/ES-05231-170448" target="_blank">https://doi.org/10.5751/ES-05231-170448</a>, 2012.
</mixed-citation></ref-html>
<ref-html id="bib1.bib22"><label>22</label><mixed-citation>
Liaw, A. and Wiener, M.: Classification and Regression by RandomForest,
Forest, 23, <a href="https://doi.org/10.1021/ci034160g" target="_blank">https://doi.org/10.1021/ci034160g</a>, 2001.
</mixed-citation></ref-html>
<ref-html id="bib1.bib23"><label>23</label><mixed-citation>
Liu, Y., Liu, X., Gao, S., Gong, L., Kang, C., Zhi, Y., Chi, G., and Shi,
L.: Social Sensing: A New Approach to Understanding Our Socioeconomic
Environments, Ann. Assoc. Am. Geogr., 105,
512–530, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib24"><label>24</label><mixed-citation>
Liu, Z., Du, Y., Yi, J., Liang, F., Ma, T., and Pei, T.: Quantitative
Association between Nighttime Lights and Geo-Tagged Human Activity Dynamics
during Typhoon Mangkhut, Remote Sens., 11, 2091,
<a href="https://doi.org/10.3390/rs11182091" target="_blank">https://doi.org/10.3390/rs11182091</a>, 2019a.
</mixed-citation></ref-html>
<ref-html id="bib1.bib25"><label>25</label><mixed-citation>
Liu, Z., Du, Y., Yi, J., Liang, F., and Pei, T.: Quantitative estimates of
collective geo-tagged human activities in response to typhoon Hato using
location-aware big data, Int. J. Dig. Earth, 1–21,
<a href="https://doi.org/10.1080/17538947.2019.1645894" target="_blank">https://doi.org/10.1080/17538947.2019.1645894</a>, 2019b.
</mixed-citation></ref-html>
<ref-html id="bib1.bib26"><label>26</label><mixed-citation>
Ma, T.: Multi-Level Relationships between Satellite-Derived Nighttime
Lighting Signals and Social Media–Derived Human Population Dynamics, Remote
Sens., 10, 1128, <a href="https://doi.org/10.3390/rs10071128" target="_blank">https://doi.org/10.3390/rs10071128</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib27"><label>27</label><mixed-citation>
Marra, F., Nikolopoulos, E. I., Creutin, J. D., and Borga, M.: Space–time
organization of debris flows-triggering rainfall and its effect on the
identification of the rainfall threshold relationship, J. Hydrol.,
541, 246–255, <a href="https://doi.org/10.1016/j.jhydrol.2015.10.010" target="_blank">https://doi.org/10.1016/j.jhydrol.2015.10.010</a>, 2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib28"><label>28</label><mixed-citation>
Martín, Y., Cutter, S. L., and Li, Z.: Bridging Twitter and Survey Data
for Evacuation Assessment of Hurricane Matthew and Hurricane Irma, Nat.
Hazards Rev., 21, 04020003,
<a href="https://doi.org/10.1061/(ASCE)NH.1527-6996.0000354" target="_blank">https://doi.org/10.1061/(ASCE)NH.1527-6996.0000354</a>, 2020a.
</mixed-citation></ref-html>
<ref-html id="bib1.bib29"><label>29</label><mixed-citation>
Martín, Y., Cutter, S. L., Li, Z., Emrich, C. T., and Mitchell, J. T.:
Using geotagged tweets to track population movements to and from Puerto Rico
after Hurricane Maria, Popul. Environ., 42, 4–27,
<a href="https://doi.org/10.1007/s11111-020-00338-6" target="_blank">https://doi.org/10.1007/s11111-020-00338-6</a>, 2020b.
</mixed-citation></ref-html>
<ref-html id="bib1.bib30"><label>30</label><mixed-citation>
McDougall, K. and Temple-Watts, P.: THE USE OF LIDAR AND VOLUNTEERED
GEOGRAPHIC INFORMATION TO MAP FLOOD EXTENTS AND INUNDATION, ISPRS Ann.
Photogramm. Remote Sens. Spatial Inf. Sci., I–4, 251–256,
<a href="https://doi.org/10.5194/isprsannals-I-4-251-2012" target="_blank">https://doi.org/10.5194/isprsannals-I-4-251-2012</a>, 2012.
</mixed-citation></ref-html>
<ref-html id="bib1.bib31"><label>31</label><mixed-citation>
Meerow, S., Newell, J. P., and Stults, M.: Defining urban resilience: A
review, Landsc. Urban Plan., 147, 38–49,
<a href="https://doi.org/10.1016/j.landurbplan.2015.11.011" target="_blank">https://doi.org/10.1016/j.landurbplan.2015.11.011</a>, 2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib32"><label>32</label><mixed-citation>
Mendiondo, E. M.: FLOOD RISK MANAGEMENT OF URBAN WATERS IN HUMID TROPICS:
EARLY WARNING, PROTECTION AND REHABILITATION, 14, in: Proceedings of the Workshop on Integrated Urban Water Managmt in Humid Tropics, Foz de Iguaçu, Brazil, 2–3 April 2005, 2–3 pp., 2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib33"><label>33</label><mixed-citation>
Mika, S., Ratsch, G., Weston, J., Scholkopf, B., and Mullers, K. R.: Fisher
discriminant analysis with kernels, in: Neural Networks for Signal
Processing IX: Proceedings of the 1999 IEEE Signal Processing Society
Workshop (Cat. No.98TH8468),  41–48, <a href="https://doi.org/10.1109/NNSP.1999.788121" target="_blank">https://doi.org/10.1109/NNSP.1999.788121</a>, 1999.
</mixed-citation></ref-html>
<ref-html id="bib1.bib34"><label>34</label><mixed-citation>
Mpandeli, S., Nhamo, L., Moeletsi, M., Masupha, T., Magidi, J., Tshikolomo,
K., Liphadzi, S., Naidoo, D., and Mabhaudhi, T.: Assessing climate change
and adaptive capacity at local scale using observed and remotely sensed
data, Weather  Clim. Extrem., 26, 100240,
<a href="https://doi.org/10.1016/j.wace.2019.100240" target="_blank">https://doi.org/10.1016/j.wace.2019.100240</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib35"><label>35</label><mixed-citation>
Myhre, G., Alterskjær, K., Stjern, C. W., Hodnebrog, Ø., Marelle, L.,
Samset, B. H., Sillmann, J., Schaller, N., Fischer, E., Schulz, M., and
Stohl, A.: Frequency of extreme precipitation increases extensively with
event rareness under global warming, Sci. Rep., 9, 16063,
<a href="https://doi.org/10.1038/s41598-019-52277-4" target="_blank">https://doi.org/10.1038/s41598-019-52277-4</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib36"><label>36</label><mixed-citation>
Nahiduzzaman, K. M., Aldosary, A. S., and Rahman, M. T.: Flood induced
vulnerability in strategic plan making process of Riyadh city, Hab.
Int., 49, 375–385,
<a href="https://doi.org/10.1016/j.habitatint.2015.05.034" target="_blank">https://doi.org/10.1016/j.habitatint.2015.05.034</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib37"><label>37</label><mixed-citation>
Naidu, S., Sajinkumar, K. S., Oommen, T., Anuja, V. J., Samuel, R. A., and
Muraleedharan, C.: Early warning system for shallow landslides using
rainfall threshold and slope stability analysis, Geosci. Front., 9,
1871–1882, <a href="https://doi.org/10.1016/j.gsf.2017.10.008" target="_blank">https://doi.org/10.1016/j.gsf.2017.10.008</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib38"><label>38</label><mixed-citation>
Ogie, R. I., Holderness, T., Dunn, S., and Turpin, E.: Assessing the
vulnerability of hydrological infrastructure to flood damage in coastal
cities of developing nations, Comput., Environ. Urban Syst., 68,
97–109, <a href="https://doi.org/10.1016/j.compenvurbsys.2017.11.004" target="_blank">https://doi.org/10.1016/j.compenvurbsys.2017.11.004</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib39"><label>39</label><mixed-citation>
Olsson, L., Jerneck, A., Thoren, H., Persson, J., and O'Byrne, D.: Why
resilience is unappealing to social science: Theoretical and empirical
investigations of the scientific use of resilience, Sci. Adv., 1,
e1400217, <a href="https://doi.org/10.1126/sciadv.1400217" target="_blank">https://doi.org/10.1126/sciadv.1400217</a>, 2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib40"><label>40</label><mixed-citation>
Östh, J., Reggiani, A., and Galiazzo, G.: Spatial economic resilience
and accessibility: A joint perspective, Computers, Environ. Urban
Syst., 49, 148–159, <a href="https://doi.org/10.1016/j.compenvurbsys.2014.07.007" target="_blank">https://doi.org/10.1016/j.compenvurbsys.2014.07.007</a>,
2015.
</mixed-citation></ref-html>
<ref-html id="bib1.bib41"><label>41</label><mixed-citation>
O'Sullivan, J. J., Bradford, R. A., Bonaiuto, M., De Dominicis, S., Rotko, P., Aaltonen, J., Waylen, K., and Langan, S. J.: Enhancing flood resilience through improved risk communications, Nat. Hazards Earth Syst. Sci., 12, 2271–2282, <a href="https://doi.org/10.5194/nhess-12-2271-2012" target="_blank">https://doi.org/10.5194/nhess-12-2271-2012</a>, 2012.
</mixed-citation></ref-html>
<ref-html id="bib1.bib42"><label>42</label><mixed-citation>
Ouyang, M., Dueñas-Osorio, L., and Min, X.: A three-stage resilience
analysis framework for urban infrastructure systems, Struct. Safe.,
36–37, 23–31, <a href="https://doi.org/10.1016/j.strusafe.2011.12.004" target="_blank">https://doi.org/10.1016/j.strusafe.2011.12.004</a>, 2012.
</mixed-citation></ref-html>
<ref-html id="bib1.bib43"><label>43</label><mixed-citation>
Owrangi, A. M., Lannigan, R., and Simonovic, S. P.: Interaction between
land-use change, flooding and human health in Metro Vancouver, Canada, Nat.
Hazards, 72, 1219–1230, <a href="https://doi.org/10.1007/s11069-014-1064-0" target="_blank">https://doi.org/10.1007/s11069-014-1064-0</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib44"><label>44</label><mixed-citation>
Pal, M.: Random forest classifier for remote sensing classification,
Int. J. Remote Sens., 26, 217–222,
<a href="https://doi.org/10.1080/01431160412331269698" target="_blank">https://doi.org/10.1080/01431160412331269698</a>, 2005.
</mixed-citation></ref-html>
<ref-html id="bib1.bib45"><label>45</label><mixed-citation>
Poulin, C. and Kane, M. B.: Infrastructure resilience curves: Performance
measures and summary metrics, Reliab. Eng. Syst. Safet.,
216, 107926, <a href="https://doi.org/10.1016/j.ress.2021.107926" target="_blank">https://doi.org/10.1016/j.ress.2021.107926</a>, 2021.
</mixed-citation></ref-html>
<ref-html id="bib1.bib46"><label>46</label><mixed-citation>
Qian, J., Liu, Z., Du, Y., Wang, N., Yi, J., Sun, Y., Ma, T., Pei, T., and
Zhou, C.: Multi-level Inter-regional Migrant Population Estimation Using
Multi-source Spatiotemporal Big Data: A Case Study of Migrants in Hubei
Province During the Outbreak of COVID-19 in Wuhan, in: Mapping COVID-19 in
Space and Time: Understanding the Spatial and Temporal Dynamics of a Global
Pandemic, edited by: Shaw, S.-L. and Sui, D., Springer International
Publishing, Cham, 169–188,
<a href="https://doi.org/10.1007/978-3-030-72808-3_9" target="_blank">https://doi.org/10.1007/978-3-030-72808-3_9</a>, 2021a.
</mixed-citation></ref-html>
<ref-html id="bib1.bib47"><label>47</label><mixed-citation>
Qian, J., Liu, Z., Du, Y., Liang, F., Yi, J., Ma, T., and Pei, T.: Quantify
city-level dynamic functions across China using social media and POIs data,
Comput. Environ. Urban Syst., 85, 101552,
<a href="https://doi.org/10.1016/j.compenvurbsys.2020.101552" target="_blank">https://doi.org/10.1016/j.compenvurbsys.2020.101552</a>, 2021b.
</mixed-citation></ref-html>
<ref-html id="bib1.bib48"><label>48</label><mixed-citation>
Qian, J., Du, Y., Yi, J., Liang, F., Huang, S., Wang, X., Wang, N., Tu, W.,
Pei, T., and Ma, T.: Regional geographical and climatic environments affect
urban rainstorm perception sensitivity across China, Sustain. Cities
Soc., 87, 104213, <a href="https://doi.org/10.1016/j.scs.2022.104213" target="_blank">https://doi.org/10.1016/j.scs.2022.104213</a>, 2022.
</mixed-citation></ref-html>
<ref-html id="bib1.bib49"><label>49</label><mixed-citation>
Román, M., Stokes, E., Shrestha, R., Wang, Z., Schultz, L., Carlo, E.,
Sun, Q., Bell, J., Molthan, A., Kalb, V., ji, C., Seto, K., Mcclain, S., and
Enenkel, M.: Satellite-based assessment of electricity restoration efforts
in Puerto Rico after Hurricane Maria, PLOS ONE, 14, e0218883,
<a href="https://doi.org/10.1371/journal.pone.0218883" target="_blank">https://doi.org/10.1371/journal.pone.0218883</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib50"><label>50</label><mixed-citation>
Rosner, B.: On the Detection of Many Outliers, null, Technometrics, 17, 221–227,
<a href="https://doi.org/10.2307/1268354" target="_blank">https://doi.org/10.2307/1268354</a>, 1975.
</mixed-citation></ref-html>
<ref-html id="bib1.bib51"><label>51</label><mixed-citation>
Shiferaw, B., Tesfaye, K., Kassie, M., Abate, T., Prasanna, B. M., and
Menkir, A.: Managing vulnerability to drought and enhancing livelihood
resilience in sub-Saharan Africa: Technological, institutional and policy
options, Weather Clim. Extrem., 3, 67–79,
<a href="https://doi.org/10.1016/j.wace.2014.04.004" target="_blank">https://doi.org/10.1016/j.wace.2014.04.004</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib52"><label>52</label><mixed-citation>
Song, J., Chang, Z., Li, W., Feng, Z., Wu, J., Cao, Q., and Liu, J.:
Resilience-vulnerability balance to urban flooding: A case study in a
densely populated coastal city in China, Cities, 95, 102381,
<a href="https://doi.org/10.1016/j.cities.2019.06.012" target="_blank">https://doi.org/10.1016/j.cities.2019.06.012</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib53"><label>53</label><mixed-citation>
Stefan, V., Fabio, G.-T., Josh, L., Jan, K., and Brenda, J.: Global Trends
in Satellite-based Emergency Mapping, Science, 353, 247–252, 2016.
</mixed-citation></ref-html>
<ref-html id="bib1.bib54"><label>54</label><mixed-citation>
Strobl, C., Boulesteix, A.-L., Zeileis, A., and Hothorn, T.: Bias in random
forest variable importance measures: Illustrations, sources and a solution,
BMC Bioinfo., 8, 25, <a href="https://doi.org/10.1186/1471-2105-8-25" target="_blank">https://doi.org/10.1186/1471-2105-8-25</a>, 2007.
</mixed-citation></ref-html>
<ref-html id="bib1.bib55"><label>55</label><mixed-citation>
Tellman, B., Sullivan, J. A., Kuhn, C., Kettner, A. J., Doyle, C. S.,
Brakenridge, G. R., Erickson, T. A., and Slayback, D. A.: Satellite imaging
reveals increased proportion of population exposed to floods, Nature, 596,
80–86, <a href="https://doi.org/10.1038/s41586-021-03695-w" target="_blank">https://doi.org/10.1038/s41586-021-03695-w</a>, 2021.
</mixed-citation></ref-html>
<ref-html id="bib1.bib56"><label>56</label><mixed-citation>
Vallis, O., Hochenbaum, J., and Kejariwal, A.: A Novel Technique for
Long-Term Anomaly Detection in the Cloud, 6th {
USENIX} Workshop on Hot Topics in Cloud Computing (HotCloud
14), 15 pp., <a href="https://doi.org/10.5555/2696535.2696550" target="_blank">https://doi.org/10.5555/2696535.2696550</a>, 2014.
</mixed-citation></ref-html>
<ref-html id="bib1.bib57"><label>57</label><mixed-citation>
Wang, B., Loo, B. P. Y., Zhen, F., and Xi, G.: Urban resilience from the
lens of social media data: Responses to urban flooding in Nanjing, China,
Cities, 106, 102884, <a href="https://doi.org/10.1016/j.cities.2020.102884" target="_blank">https://doi.org/10.1016/j.cities.2020.102884</a>, 2020.
</mixed-citation></ref-html>
<ref-html id="bib1.bib58"><label>58</label><mixed-citation>
Wang, J., Meng, B., Pei, T., Du, Y., Zhang, J., Chen, S., Tian, B., and Zhi,
G.: Mapping the exposure and sensitivity to heat wave events in China's
megacities, Sci. Total Environ., 755, 142734,
<a href="https://doi.org/10.1016/j.scitotenv.2020.142734" target="_blank">https://doi.org/10.1016/j.scitotenv.2020.142734</a>, 2021.
</mixed-citation></ref-html>
<ref-html id="bib1.bib59"><label>59</label><mixed-citation>
Wang, N., Du, Y., Liang, F., Yi, J., and Wang, H.: Spatiotemporal Changes of
Urban Rainstorm-Related Micro-Blogging Activities in Response to Rainstorms:
A Case Study in Beijing, China, Appl. Sci., 9, 4629,
<a href="https://doi.org/10.3390/app9214629" target="_blank">https://doi.org/10.3390/app9214629</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib60"><label>60</label><mixed-citation>
Wang, Y. and Taylor, J. E.: Coupling sentiment and human mobility in natural
disasters: a Twitter-based study of the 2014 South Napa Earthquake, Nat.
Hazards, 92, 907–925, <a href="https://doi.org/10.1007/s11069-018-3231-1" target="_blank">https://doi.org/10.1007/s11069-018-3231-1</a>, 2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib61"><label>61</label><mixed-citation>
Yabe, T., Tsubouchi, K., Fujiwara, N., Sekimoto, Y., and Ukkusuri, S. V.:
Understanding post-disaster population recovery patterns, J.
Roy. Soc. Inter., 17, 20190532,
<a href="https://doi.org/10.1098/rsif.2019.0532" target="_blank">https://doi.org/10.1098/rsif.2019.0532</a>, 2020.
</mixed-citation></ref-html>
<ref-html id="bib1.bib62"><label>62</label><mixed-citation>
Yi, J., Du, Y., Liang, F., Pei, T., Ma, T., and Zhou, C.: Anomalies of dwellers' collective geotagged behaviors in response to rainstorms: a case study of eight cities in China using smartphone location data, Nat. Hazards Earth Syst. Sci., 19, 2169–2182, <a href="https://doi.org/10.5194/nhess-19-2169-2019" target="_blank">https://doi.org/10.5194/nhess-19-2169-2019</a>, 2019.

</mixed-citation></ref-html>
<ref-html id="bib1.bib63"><label>63</label><mixed-citation>
Yue, Y., Zhuang, Y., Yeh, A. G. O., Xie, J.-Y., Ma, C.-L., and Li, Q.-Q.:
Measurements of POI-based mixed use and their relationships with
neighbourhood vibrancy, Int. J. Geogr. Info.
Sci., 31, 658–675, <a href="https://doi.org/10.1080/13658816.2016.1220561" target="_blank">https://doi.org/10.1080/13658816.2016.1220561</a>, 2017.
</mixed-citation></ref-html>
<ref-html id="bib1.bib64"><label>64</label><mixed-citation>
Zhang, R., Chen, Y., Zhang, X., Ma, Q., and Ren, L.: Mapping homogeneous
regions for flash floods using machine learning: A case study in Jiangxi
province, China, Int. J. Appl. Earth Observ.
Geoinfo., 108, 102717, <a href="https://doi.org/10.1016/j.jag.2022.102717" target="_blank">https://doi.org/10.1016/j.jag.2022.102717</a>,
2022.
</mixed-citation></ref-html>
<ref-html id="bib1.bib65"><label>65</label><mixed-citation>
Zheng, S., Wang, J., Sun, C., Zhang, X., and Kahn, M. E.: Air pollution
lowers Chinese urbanites' expressed happiness on social media, Na. Human
Behav., 3, 237–243, <a href="https://doi.org/10.1038/s41562-018-0521-2" target="_blank">https://doi.org/10.1038/s41562-018-0521-2</a>, 2019.
</mixed-citation></ref-html>
<ref-html id="bib1.bib66"><label>66</label><mixed-citation>
Zou, L., Lam, N., Cai, H., and Qiang, Y.: Mining Twitter Data for Improved
Understanding of Disaster Resilience, Ann. Assoc. Am.
Geogr., 108, 1422–1441, <a href="https://doi.org/10.1080/24694452.2017.1421897" target="_blank">https://doi.org/10.1080/24694452.2017.1421897</a>,
2018.
</mixed-citation></ref-html>
<ref-html id="bib1.bib67"><label>67</label><mixed-citation>
Zou, L., Lam, N. S. N., Shams, S., Cai, H., Meyer, M. A., Yang, S., Lee, K.,
Park, S.-J., and Reams, M. A.: Social and geographical disparities in
Twitter use during Hurricane Harvey, Int. J. Dig. Earth,
12, 1300–1318, <a href="https://doi.org/10.1080/17538947.2018.1545878" target="_blank">https://doi.org/10.1080/17538947.2018.1545878</a>, 2019.
</mixed-citation></ref-html>--></article>
