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date: 30 April 2017

Climatology of Flooding in the United States

Summary and Keywords

Flood losses in the United States have increased dramatically over the course of the past century, averaging US$7.96 billion in damages per year for the 30-year period ranging from 1985 to 2014. In terms of human fatalities, floods are the second largest weather-related hazard in the United States, causing approximately 80 deaths per year over the same period. Given the wide-reaching impacts of flooding across the United States, the evaluation of flood-generating mechanisms and of the drivers of changing flood hazard are two areas of active research.

Flood frequency analysis has traditionally been based on statistical analyses of the observed flood distributions that rarely distinguish among physical flood-generating processes. However, recent scientific advances have shown that flood frequency distributions are often characterized by “mixed populations” arising from multiple flood-generating mechanisms, which can be challenging to disentangle. Flood events can be driven by a variety of physical mechanisms, including rain and snowmelt, frontal systems, monsoons, intense tropical cyclones, and more generic cyclonic storms.

Temporal changes in the frequency and magnitude of flooding have also been the subject of a large body of work in recent decades. The science has moved from a focus on the detection of trends and shifts in flood peak distributions towards the attribution of these changes, with particular emphasis on climatic and anthropogenic factors, including urbanization and changes in agricultural practices. A better understanding of these temporal changes in flood peak distributions, as well as of the physical flood-generating mechanisms, will enable us to move forward with the estimation of future flood design values in the context of both climatic and anthropogenic change.

Keywords: flooding, United States, detection, attribution, mixed distributions, urbanization, agriculture, flood frequency, hydrology, precipitation


Flood losses have increased dramatically in the United States over the course of the past century (Downton, Miller, & Pielke, 2005; Pielke & Downton, 2000), averaging US$7.96 billion in damages per year for the 30-year period ranging from 1985 to 2014 (NOAA National Weather Service, 2016). The costliest recent floods in terms of economic damages were the Midwest floods of 1993 and 2008, followed by the 1997 floods in the Northern Plains and on the U.S. West Coast, with costs ranging from $35 to $4.5 billion, respectively (National Climate Data Center, 2016). The growth in damages arising from these major flood events can be related to climatic drivers—i.e., the increasing frequency of average and extreme precipitation events—and societal or economic drivers—i.e., the concentration of population and assets in flood-exposed areas (e.g., Pielke & Downton, 2000). As a result, major (or “billion-dollar”) floods have been increasing by about 5% per year (Smith & Katz, 2013), and projections based on the statistical relationship between socio-economic drivers and annual precipitation for 1929–1998 suggest that a mere 1% increase in annual precipitation may lead to a 6.5% increase in annual flood losses (Choi & Fisher, 2003). In terms of human fatalities, floods are the second largest weather-related hazard in the United States, with an average of 82 deaths per year between 1986 and 2015 (vs. 130 for heat and 70 for tornadoes; Office of Services, 2016). Overall, flooding has major societal and economic impacts across the United States, with the total value of properties insured through the National Flood Insurance program reaching over $1 trillion in the past decade (Kousky & Michel-Kerjan, 2015). This article examines the physical mechanisms that are driving the occurrence of these flood events in the United States; it provides a broad overview of how flood hazards have changed over the 20th and 21st centuries, and of the methods used to attribute the different drivers of flooding.

Flood Generating Mechanisms

Flood Agents and Mixed Populations

Traditionally, our understanding of flood frequency has been based on mathematical modeling of the observed historical flood records. However, these empirical analyses tend to lack a physically based understanding of the flood frequency distribution, based on the underlying flood processes. As described by Klemeš (1974, p. 2), “The empirical data representing a hydrologic event are treated as a collection of abstract numbers that could pertain to anything or to nothing at all.” Klemeš argued that a solid characterization of flood frequency could arise only from the physics of the phenomena, rather than from the mathematics (Klemeš, 1993, p. 168). The examination of flood agents, the physical mechanisms that are conducive to flooding across different areas of the United States, presents multiple benefits: from a scientific perspective, it advances our understanding of the interrelationship between hydrology, atmospheric, and climate sciences; and from an engineering perspective it is vital for improving our ability to predict floods and to plan the appropriate design structures.

The distribution of flood events at any given location in space and time often results from a combination of different types of flood-generating weather systems and storms (e.g., Berghuijs et al., 2016; Villarini, 2016). These combined distributions are known as mixed populations, and it can be challenging to determine which flood peaks result from the different processes. The official U.S. guidelines for determining flood frequency, known as Bulletin 17-B (U.S. Interagency Advisory Committee on Water Data, 1982) acknowledged this difficulty and indicated that flooding could be produced by different mechanisms across the United States, such as rain and snowmelt (e.g., Sierra Nevada), intense tropical cyclones, or more generic cyclonic storms (e.g., on the Atlantic and Gulf Coasts). Bulletin 17-B highlighted the need to identify the agents of flooding, and warned that a simplistic stratification of flood records (e.g., based on calendar periods distinguishing between spring and summer flood events) was not “hydrologically reasonable.” The authors wrote that “[i]f the flood events that are believed to comprise two or more populations cannot be identified and separated by an objective and hydrologically meaningful criterion, the record [should] be treated as coming from one population” (p. 16). Thus, while Bulletin 17-B identified the need for a better understanding of flood processes to improve flood frequency estimation, it provided limited guidance on how to achieve such an understanding; similar conclusions hold with the upcoming Bulletin 17-C.

At the continental scale, a number of studies have attempted to provide a synthesis of the variety of spatial and seasonal flood generating mechanisms across the United States. One of the most comprehensive discussions and frameworks for the interpretation of flooding in terms of mixtures of different flood generating mechanisms was developed by Hirschboeck (1987, 1988, 1991) in a series of studies investigating the physical flood-driving processes. More recently, Villarini (2016) used circular statistics to examine the seasonality of flooding at 7,506 U.S. Geological Survey (USGS) stations in terms of different major flood agents, including tropical cyclones, atmospheric rivers, snowmelt, and monsoon. Berghuijs, Woods, Hutton, and Sivapalan (2016) tackled this issue from a hydrologic perspective: at 420 catchments across the United States, they related the annual maximum peak discharge to maximum or weekly daily precipitation, maximum soil moisture dependent precipitation excess or snowmelt. Overall, the studies in this area suggest that, across large areas of the United States, different parts of the flood peak distributions are controlled by specific agents.

Rainfall- and Snowmelt-Driven Flood Events

The issue of mixed flood-generating mechanisms has been addressed through a variety of assumptions and modeling approaches since the early 1980s, with an initial focus on rainfall- and snowmelt-driven flood events. Waylen and Woo (1982) first described flooding in the Cascade Mountains in terms of snowmelt and rainfall events. The authors used antecedent precipitation to differentiate between the snowmelt and rainfall populations and fit a Gumbel distribution to the flood events associated with each flood-generating process. They found that, by compounding the two distributions at each site, they obtained a better characterization of the observed annual flood series. This approach was further formalized by Rossi, Fiorentino, and Versace (1984), who developed a statistical framework to characterize flood distributions at 39 stream gages in Italy in terms of the two-component extreme value distribution. They argued that the flexibility introduced by the mixture of two exponential distributions provided a more realistic representation of the annual maximum flood peak records; one component (the basic distribution) allowed the characterization of the more common and less severe flood events, while the other one (the outlying distribution) was geared toward the description of the more severe flood events that would be qualified as outliers using a single distribution. This framework led to an improved fit across a wide range of flood magnitudes that would not have been possible by using just one distribution. Diehl and Potter (1987) used data from 29 stream gaging stations to describe flooding in Wisconsin in terms of mixtures of two populations. They used a calendar-based approach to stratify the records into spring and summer floods occurring before and after May 20th. A similar approach was followed by Todhunter (2012), who examined the issue and implications of mixed flood distributions for the Red River of the North by describing the flood record in terms of snowmelt and rainfall peaks. Because the majority of the flood peaks were associated with snowmelt (85%) rather than rainfall (15%), the mixed distribution closely resembled that based on the whole record, with minor departures at the higher and lower tails. Jarrett and Costa (1988) also examined flood peak time series in the Colorado Front Range and stratified the records in terms of snowmelt- and rain-generated flood peaks.

Merz and Blöschl (2003) examined the idea of mixtures of different flood agents from a catchment-based, rather than an atmospheric circulation-based perspective. They considered five flood types (long-rain floods, short-rain floods, flash floods, rain-on-snow floods, and snowmelt floods), and focused on different indicators, including storm duration and rainfall depth/snowmelt, catchment state (i.e., soil moisture conditions), runoff response dynamics (e.g., fast or slow response), flood seasonality, and spatial coherence. They also acknowledge that these flood types do not likely have sharp boundaries in terms of their processes and characteristics. Shaw and Riha (2011) examined long-term (50+ years of data) records from three watersheds in the state of New York. They found that about 20% of the annual flood peak records were associated with annual maximum rainfall, about 20% with annual maximum snowmelt events, and about 60% with moderate rainfall and saturated soil conditions. The authors also investigated potential future changes in annual maximum peak discharge values by developing a compound distribution to account for the different flood generating mechanisms, and they examined flood response for changes in the contribution of each flood agent.

Frontal Systems, Monsoons and Tropical Cyclones

Rainfall-related flood events have been further examined in terms of storm types, with particular emphasis on tropical cyclones and their controls on the upper tail of the flood peak distributions. Waylen (1991) examined the role of tropical cyclones on flooding in the Santa Fe River basin in Florida over the 1928–1988 period. He found that tropical cyclone related flood magnitudes were larger than those associated with summer convective events. Webb and Betancourt (1992) focused on the Santa Cruz River in Arizona and characterized the flood frequency in terms of three different populations: floods associated with frontal systems, with monsoons, and with tropical cyclones. They showed the effects of each of these flood-generating mechanisms on flood frequency and discussed the limitations of flood frequency analyses in the context of mixtures. Murphy (2001) described flood flows in Massachusetts in terms of three agents: tropical cyclones, ice-jam release, and ordinary flooding (i.e., not caused by either of the other two agents). He found that the probability that one of the studied Massachusetts stream gauges would have an annual maximum associated with a tropical cyclone was 0.0515/year, but also that the peak flows caused by these storms were statistically different from the other annual flood peaks. Overall, he showed that the flood peaks associated with tropical cyclones and ice-jam releases would be classified as outliers if a single distribution was used. Alila and Mtiraoui (2002) stratified the annual flood series of the San Francisco River at Clifton (Arizona) into two main classes (monsoon and frontal systems), with the monsoon (frontal) systems controlling the lower (upper) tail of the distribution.

More recent work has investigated the spatial variability of the influence of tropical cyclones on flood peaks across the United States. Villarini and Smith (2010) showed that flood drivers in the eastern United States present a strong spatial variability: snowmelt and extra-tropical cyclones tend to be responsible for much of the flooding in the northeastern and southeastern United States, while tropical cyclones contribute to a large fraction of annual maximum flood peaks in Florida (~40%) and the U.S. Eastern Seaboard, ranging from South Carolina to New Jersey. These insights were further developed in Smith, Villarini, and Baeck (2011), who provided a detailed characterization of the spatial structure and temporal evolution of rainfall and flooding associated with tropical and extra-tropical cyclones. The relationship between tropical cyclones and flooding in Texas was examined by Villarini and Smith (2013), who showed that tropical cyclones were responsible for up to 18% of the annual maximum flood peak records, especially along the Gulf of Mexico, even though their control on the upper tail of the flood peak distribution was smaller than in the eastern United States (see Villarini, Goska, Smith, and Vecchi (2014) for an extensive discussion on flooding from tropical cyclones).

Statistical Modeling of Mixed Populations

From a statistical perspective, different approaches have been proposed and developed to model these mixed distributions. Alila and Mtiraoui (2002) described three different approaches to account for heterogeneity in flood frequency depending on the assumptions that one is willing to make in terms of occurrence of different flood events, and whether the data are stratified a priori based on the flood generating mechanisms (see also discussion in Singh, Wang, and Zhang (2005).

The first approach builds on the additive rule of probability and assumes that the flood populations are independent of one another, so any given annual maximum peak discharge must be associated with a single flood generating mechanism (e.g., the annual maximum is assumed to be caused either by a tropical or monsoonal storm, but not by both) (e.g., Jarrett & Costa, 1988; Webb & Betancourt, 1992). Each subset is then fit separately and combined using the additive rule of probability. The disadvantage of this approach is that the records must be subset, so larger sampling uncertainties occur in the estimated parameters of the fitted distributions, and long-term historical datasets are required to classify the different flood events.

The second approach does not require sub-setting the annual maximum time series into two or more populations, but assumes that two flood peaks occur sequentially during the year. One example of this would be snowmelt flood peaks occurring in the spring, followed by rainfall flood peaks in the winter (e.g., Diehl & Potter, 1987; Waylen & Woo, 1982). In such a case, the spring flood events are assumed to be homogenous, and are fit with a given distribution. The same is done for the winter events. Using the multiplicative rule of probability, the two distributions are then combined. The advantage of this approach is that the sample size used for the fitting is not reduced, since one event per year is associated with each of the identified flood generating mechanisms. The downside, however, is that it does not allow for different types of storms to occur in the same season, which may not be a realistic assumption (as discussed above, this approach is not recommended by Bulletin 17-B).

Finally, the third approach does not necessitate any a priori stratification of flood peaks, but requires selecting the number of mixtures for the distributions, estimating the parameters for each distribution and choosing the mixing parameter(s) to weight the mixed distribution (e.g., Alila & Mtiraoui, 2002; Grego & Yates, 2010; Rossi et al., 1984). Following this line of research, recent studies have provided insights on the use of finite mixture models, including improved estimation of the parameters and the associated standard errors (e.g., Grego & Yates, 2010; Grego, Yates, & Mai, 2015). The strength of this approach is that the flood peaks do not need to be stratified in terms of flood generating mechanisms. However, this is also the weakness of the approach, because it favors a purely statistical perspective over the physical interpretation of the flood peak records and, therefore, is vulnerable to the abovementioned criticisms by Klemeš (1974).

Substantial progress has been made in recent years in incorporating a physical understanding of flood-generating mechanisms in flood frequency analysis. However, more effort is required to tackle this problem successfully, as it is not an easy task to accomplish and is fraught with complications. To move forward successfully, hydrologists must engage with climate and atmospheric scientists to understand the physical processes leading to different kinds of events. At the same time, hydrologists would also benefit from a closer relationship with applied statisticians to formalize the statistical modeling. Overcoming these obstacles would advance the science of flooding and allow for a better and more accurate estimation of design discharge values, which are so critical in in a number of engineering applications.

Temporal Changes in Flood Peaks (Annual Maxima and Peaks Over Threshold)

Historically, the occurrence of major floods in different parts of the globe has been viewed through the lens of stationarity, using probability distributions that are invariant to translations in time (e.g., Brillinger, 2001), and that have no abrupt and gradual changes or periodicities (e.g., Salas, 1993). This assumption of stationarity has served as the foundation for engineering structures and flood design. However, in the early 21st century, it has become widely accepted that, as a result of human activities and their influence on the climate system, increasing temperatures and the associated moisture-holding capacity of the atmosphere have altered the frequency with which extreme precipitation events occur (e.g., Karl, Melillo, & Peterson, 2009, Trenberth, 2011). Increases in the frequency and magnitude of heavy and extreme precipitation events are now well documented across the United States, and it is expected that flooding may intensify as a result (Georgakakos et al., 2014). In fact, changes in peak flow distributions are so common that the concept of stationarity in flood risk and water management was declared “dead” (Milly et al., 2008). These changes are particularly problematic for planning, management, and forecasting of major floods. While many water managers still operate under the assumption of stationarity, it is increasingly recognized that flood planning and “design floods” (and more generally any climatic extremes, as discussed in Cheng et al., 2014) should be revised in the context of nonstationarity, to incorporate the notion that future floods may be magnified in comparison with historical estimates (e.g., Vogel, Yaindl, & Walter, 2011).

Two indicators are typically used to assess whether floods are changing over time: changes in the magnitude (are floods getting bigger or smaller?) and in the frequency (are they occurring more or less often than before?) of flood events. Within these two categories, changes may be gradual (occurring in the form of trends), or abrupt (referred to as shifts, or step changes) (e.g., Rougé, Ge, & Cai, 2013). Step changes are often the result of anthropogenic influences on water networks, such as impoundment or water abstraction. Trends, however, are of a progressive, incremental nature, often resulting from changes in climate or land use. These changes in the magnitude or frequency of flooding may arise from a combination of causes, including atmospheric changes (e.g., precipitation type, timing, phase, volume, and temperature), land use and land cover (e.g., agriculture, urbanization), and anthropogenic water management (including dams, diversions, and abstraction).

Detection of Changes in Flood Magnitude

Trends in Flood Magnitude

To assess changes in the magnitude of flooding, the annual maximum series (AMS) is typically employed because it is a simple indicator that only requires extracting the largest daily flood in every year (referred to as the 100th percentile, Q100, or Qmax). Traditionally, the non-parametric Mann-Kendall test (Kendall, 1975; Mann, 1945) is used to detect monotonic changes in the average magnitude of the annual maximum series (i.e., progressive increases or decreases over time). The null hypothesis of the Mann-Kendall test can thus be described as the probability that [Yj > Yi] is equal to 0.5, where time Tj > Ti, as long as there is no serial correlation in the values of Y (Helsel & Hirsch, 1992). Because the Mann-Kendall test is non-parametric, it allows the investigator to make minimal assumptions about the distribution of the peak flow data (which are typically skewed) and the type of changes over time (it tests for monotonic patterns, which would include, for instance, linear, exponential, logarithmic changes). The Spearman test is also used, though less frequently. In comparison with the Mann-Kendall test, it is nonparametric and works with the ranks of the data sample. The Spearman’s estimator is the same as the Pearson’s correlation coefficient computed on the ranks and has a similar power to the Mann-Kendall test for detecting trends in the time series (Yue, Pilon, & Cavadias, 2002).

Numerous studies have been conducted since the end of the 20th century to detect trends in the magnitude of flood flows across the United States. While strong regional patterns of increasing versus decreasing flows have been found, generally speaking, the trends in the highest flows (Q100) often tend to be non-statistically significant (e.g., Lins & Slack, 1999) or less significant than other streamflow percentiles (McCabe & Wolock, 2002), and generally display far less spatial coherence (Lins & Slack, 1999). The difficulty in detecting significant trends in flow maxima arises from their strong inter-annual variability, which requires much stronger trends (or longer time series) in comparison with lower discharge quantiles before the trends can become statistically significant (Wilby, 2006). Therefore, comparing trends detected in short annual maximum time series with those found in longer records may result in notable discrepancies.

Regionally, increases in flood flows have been more marked in the Midwest than across the rest of the United States. Studies using discharge records from hundreds of stream gauges have found strong increases in flood flows in the region (Kundzewicz, Graczyk, Maurer, Pińskwar, Svensson, & Szwed, 2005; Villarini, Smith, Baeck, & Krajewski, 2011) occurring mostly as a result of change points, rather than trends (Villarini et al., 2011). In the Upper Mississippi, changes in agricultural land use over the last two centuries, alongside an earlier timing of snowmelt runoff, appear to have been a major contributor to the increases in flood magnitudes, particularly in the second half of the 20th century (Knox, 2001). The observed increases in the magnitude of large floods spread from the Midwest right across the northeastern United States (Hirsch & Ryberg, 2012), with upward trends in flood magnitude across New England (Collins, 2009). Many of the changes detected in the eastern United States (Villarini & Smith, 2010), and in the Delaware basin (Smith, Baeck, Villarini, & Krajewski, 2010) are associated with abrupt changes in the peak flow distributions, often linked to regulation. Across the rest of the eastern United States, increases in high flows have been relatively common (Groisman, Knight, & Karl, 2001): upward trends in peak discharges have been detected in New England (Armstrong et al., 2012) and in annual flood trend magnitudes across the eastern United States, and Atlantic coast (Collins et al., 2014). In the mid-Atlantic region, long discharge time series also showed upward trends in annual flood magnitude, with step changes occurring around 1970 (Armstrong, 2013); while in Maine, annual peak flows have increased notably during the past 50 to100-year period (Hodgkins, 2010).

Streamflow changes in the western United States paint a different picture. In regions of the north-western and western-central United States, where streamflow is snowmelt-dominated (see e.g., Barnett, Adam, & Lettenmaier, 2005), precipitation is generally stored in the form of high-altitude snowpacks that melt in the warm season. Increases in mean temperature occurring since the late 1940s have progressively reduced these snowpacks and altered snowmelt patterns (Dettinger & Cayan, 1995): the upward shift in spring and early summer temperatures that occurred in the mid-1980s has produced an earlier timing of snowmelt runoff (McCabe & Clark, 2005). Concomitantly, the earlier timing of peak streamflows in the winter/spring and autumn has resulted in a retreat in the streamflow centre of volume date (Hodgkins, Dudley, & Huntington, 2003), so higher flood peaks are produced from runoff in the early spring months (Knowles & Cayan, 2002).While the center-of-volume date, or hydrograph centroid, is widely used to interpret the effects of warming temperature on hydrographs (see Groisman et al., 2001, for an illustration), it is not considered a robust indicator, because flow contributions other than snowmelt influence the indicator and can produce false center-of-volume values (Whitfield, 2013). In California, streamflow responses are dependent on catchment elevation and the seasonality of the climate forcing, so they have been most accentuated in middle “moderate” latitudes (Dettinger & Cayan, 1995). More generally however, the western United States has witnessed widespread decreases in flood flow magnitudes across the Rocky Mountains and the arid Southwest (Hirsch & Ryberg, 2012).

Step Changes in Flood Magnitude

In addition to progressive changes in the annual maxima that can be detected through trend analysis, abrupt changes or shifts, also referred to as step changes, can be detected through change point analysis. Statistical methods for distinguishing between the two are still an active area of research in hydrology (e.g., Rougé et al., 2013). Step changes or shifts occur when streamflow maxima increase suddenly, rather than as a progressive trend. The vast majority of the available statistical tests seek for changes in the mean and/or variance (e.g., Villarini, Serinaldi, Smith, & Krajewski, 2009). Complicating factors can obscure the detection of step changes, including the presence of multiple shifts in the data, the lack of a priori knowledge as to their location and magnitude, and the effect of skew within the hydrological maxima time series.

Various statistical techniques exist to detect change points in the mean of hydrologic maxima. Using 50 U.S. Geological Survey stations with at least 100 year-long records and documented changes in discharge occurring from regulation or diversion, Villarini et al. (2009) found that the Pettitt test best detected the step changes when compared with other change point tests. The Pettitt test (Pettitt, 1979) is a non-parametric test that is used for detecting changes in the mean of a distribution; it is based on the Mann-Whitney rank-based statistic and determines whether two samples come from the same population. When used for observing shifts in extremes, the sensitivity of the Pettitt test increases with the magnitude of the shift, record length, centrality of location of the shift within the time series, and low variability in the data (Mallakpour & Villarini, 2016a). Villarini et al. (2009) showed that significant change points could be detected in almost half of the studied long-term discharge records across the conterminous United States. In contrast, a slightly simpler approach for step-change detection is to seek for a statistical difference in the data between two fairly long (e.g., multi-decadal) time periods. McCabe and Wolock (2002) used standardized departures of the maximum daily streamflow (i.e., subtracting the long-term mean from the flow values and dividing by the standard deviation) at 400 sites, and found differences between two time periods (1941–1970 and 1971–1999) using the Student’s t-test. Few significant step changes were found for the maximum daily flow, in comparison with mean and low flows, as above in the case of trend analysis. Collins (2009) used time series of average standardized departures to detect step changes and found abrupt shifts in New England flood peaks around 1970, coincidental with a shift to a positive phase in the North Atlantic Oscillation.

In addition to detecting changes in the mean of annual maximum time series, the flood literature is beginning to consider changes in variance. Generally, extreme events tend to be more sensitive to shifts in hydro-climatic variance than to shifts in the mean (e.g., Katz & Brown, 1992). The Lombard test (Lombard, 1987), like the Pettitt test, is non-parametric and rank-based, and is used to test for changes in the mean, but also allows consideration of changes in variance. Such changes might occur as a result of both climatic and anthropogenic influences (dams, reservoirs, changes in water management), and can obscure changes in the mean (Kundzewicz & Robson, 2004). The performance of the Lombard test increases with the magnitude and significance of the changes in variance, the sample size, and the centrality of location of the change point within the time series, and is reduced with the presence of changes in the mean (Nayak & Villarini, 2016).

Detection of Changes in Flood Frequency

While most studies have focused on the detection of gradual and abrupt changes in the magnitude of flood events, comparatively little has been done on changes in flood frequency across the United States. Frequency-based methods enable the detection of changes in how often events of a given magnitude occur. They do not provide the same information as trends in flood magnitude, and they may not necessarily exhibit the same sign (floods may be getting larger, but occurring less frequently (e.g., Petrow & Merz, 2009; Svensson, Kundzewicz, Maurer, 2005) or significance levels (Mallakpour & Villarini, 2015).

Two types of data are typically used for quantifying changes in the frequency of flood events: the annual maximum series (AMS) and the partial duration series (PDS) (Langbein, 1949). The AMS approach considers only the maximum flow in each year, so it can be used to see how frequently floods of a given size occurred over a set historical record. However, one inherent difficulty with the AMS is that, by considering only the maximum flow in each year, the resulting records are poorly adapted for semi-arid or arid regions where floods may occur at a sub-annual frequency (e.g., only every 5 to10 years or more). The PDS approach, in comparison, records all flows above a set discharge threshold (q0), which can be either a given flow magnitude or a flow of a given exceedance probability (e.g., the flow that is exceeded twice, or four times per year on average). For this reason it is commonly referred to as the peaks-over-threshold (POT) method (e.g., Leadbetter, 1991; Smith, 1984), as it consists in using only a fraction of the time series—the largest flood events.

Different approaches are used to select the appropriate q0 threshold. The first consists in selecting a fixed value of q0 and counting the frequency of floods exceeding that chosen value. By choosing the lowest annual flood, for instance, at least one flood in each year can be included (Langbein, 1949). If a high threshold is selected, then the years with no true flood will be counted as zeroes, and thus can be included using strictly positive trend detection methods, such as Poisson regression, to obtain a precise estimation of changes in the frequency of flooding. A second approach consists in setting q0 at the threshold that is exceeded on average n times per year (e.g., two events per year, Mallakpour & Villarini, 2015). This latter approach allows the user to scale POT to enable a comparison between rivers of different size. Thus, the q0 and β‎ parameters (i.e., the threshold value and the slope coefficient to quantified changes over time) are estimated from a fixed sample size at every site. Overall, the choice of the most appropriate threshold remains relatively arbitrary, as long as it is high enough to justify the model assumptions and low enough to capture sufficient observations (Dupuis, 1998).

Peak-over-threshold methods have gained in popularity in recent years, as they enable the investigator to determine whether the rate of occurrence parameter is a linear function of time, and whether non-stationarity can be detected within the non-normally distributed time series. The principal advantage of the POT approach is that it considers a greater number of events than the AMS approach, and theoretically provides a more representative characterization of changes in the frequency of flows. It also allows the user to select different thresholds, thus controlling the number of floods that are included in the analysis (Lang, Ouarda, & Bobée, 1999). However, the flood data (daily or instantaneous) that are listed are not necessarily independent, as in the AMS approach. A frequency distribution is fit to the time series of floods exceeding q0, and typically, the partial duration series is formulated using the Poisson distribution (Kirby, 1969; Smith & Karr, 1986). Generally, recurrence intervals in the POT series tend to be smaller than those computed using the annual flood series (Langbein, 1949) and the values have smaller sampling variance (Cunnane, 1973).

In contrast with analyses of trends in flood magnitude, relatively little has been done on changes in flood frequency across the United States. The frequency of bankfull flows in river channels was first quantified using the annual peak flow time series (Dury, 1961; Leopold, Wolman, & Miller, 1964); in more recent years, geomorphic studies have measured the effects of channel management (e.g., Booth, 1991), catchment development, and urbanization (Booth & Jackson, 1997) on changing flood frequencies across the United States (Slater, Singer, & Kirchner, 2015). Studies specifically focused on detecting hydrologic trends in flood frequency across the United States are all relatively recent. Collins (2009) documented increases in the recurrence of set flood magnitudes at seven gauges in New England before and after 1970. The POT approach has been adopted even more recently. Armstrong et al. (2012) found widespread upward trends in the frequency of peaks above flood thresholds at 23 climate-sensitive New England stream gauges using the Mann-Kendall test. Mallakpour and Villarini (2015) found widespread increases in frequency and magnitude, which were much more significant in terms of frequency than in terms of flood peak magnitude, across the Midwest. Slater et al. (2015) measured POT trends in the number of days where streamflow exceeded the average “channel capacity” at flood stage (i.e., hydrologic trends), and compared them with trends in flood hazard arising from changes in the capacity of river channels (i.e., geomorphic effects on flood hazard).

One difficulty with the POT method lies in selecting the threshold in an objective manner, given that large and small basins have different peak arrival times, with much flashier flows and steeper scaled peak discharges for the same return period in small versus large basins (Blöschl & Sivapalan, 1995). In other terms, because flood peaks tend to last longer above flood levels in large versus small catchments, an increase in flood frequency of n days per year may be proportionally more important in small channels. Thus, to meet the independence condition of separate peak events, it has been suggested that flood events should be separated by a given number of days, adjusted by catchment size, for example, 5+ the natural logarithm of the basin area in square miles (e.g., Lang et al., 1999). Hence, to observe trends in the frequency of flood events above the National Weather Service’s flood categories, Slater and Villarini (2017) use an approach that detects trends in the frequency of independent events based on catchment size. They quantified changes in the number of annual days in which stage exceeded the four flood categories (action, minor, moderate and major), and found increases in flood risk in the Midwest and northeastern United States and decreases in the southern half of the country, which were partly explained by changes in long-term antecedent basin wetness.

Figure 1 shows a comparison of trend analyses that were performed to detect changes in the frequency, magnitude, and duration of flood events over the 1965–2015 period at 3,830 sites across the continental United States, Alaska, Hawaii, and Puerto Rico.

Climatology of Flooding in the United StatesClick to view larger

Figure 1. Trends in flooding across the United States (water years 1965–2015). Flood trends are expressed in terms of the number of flood events (N EVENTS), flood magnitude (AMAX), and number of flood days (N DAYS), from the top to the bottom row, respectively. Increasing trends are indicated in red, decreasing trends in blue, with the significant trends (at the 5% level) represented as solid colors, and the non-significant trends as transparent colors. The left-hand column shows all gauging stations, and the right-hand column is a subset of climate-sensitive sites, selected using the GAGES-II reference classification (Falcone, Carlisle, Wolock, & Meador, 2010). The tables in the bottom of each panel indicate the number of sites with significant and non-significant trends, separated by their sign: increases (+) and decreases (–).

Large areas of the eastern United States, the Great Lakes region, and the Midwest show increasing trends in the magnitude and frequency of flood events, while the southeastern and western United States are mostly characterized by decreasing trends. The distinct regional pattern of increasing versus decreasing trends in flood magnitude (AMAX) is even more prominent when one focuses on the duration (NDAYS) of the flood events. The number of statistically significant trends is similar for flood magnitude and frequency across all sites (Figure 1, left column), however in climate-sensitive catchments, statistically significant trends are detected far more often in the frequency than in the magnitude of flood events (Figure 1, right column; 16% of the time for NEVENTS versus 6% of the time for AMAX), in line with most of the conclusions and findings in the literature.

Attribution of Changes in Flood Hazard

Following the extensive number of studies that have been published on the detection of flood trends across the United States, many research groups have now moved on to attempting to understand the causes of these changes, through attribution science. The idea behind attribution studies is to formally detect the drivers that are responsible for temporal changes in the magnitude and frequency of flood flows, whether they are gradual or abrupt (trends or step-changes). Attribution studies typically associate flood patterns with changes in land cover/land use, water management of river basins, and anthropogenically driven climate change. They separate the relative influence or magnitude of each driver by decomposing the flood series behavior in time. Merz, Vorogushyn, Uhlemann, Delgado, and Hundecha (2012) propose a distinction between “soft” and “hard” attribution studies. In the first case, the flood trends are attributed to certain drivers, but only in a speculative fashion, through hypotheses and referrals to previous studies. “Hard” attribution, on the other hand, would include the following three ingredients, namely (a) evidence of consistency, showing that the detected change is consistent with the assumed driver of change; (b) evidence of inconsistency, showing that the change is inconsistent with changes due to alternative possible drivers; and (c) a provision of confidence level associated with the attribution statement. At the time of writing (2012), the authors considered that no studies yet satisfied those three criteria because the published literature focussed only on consistency, generally through simple qualitative reasoning and without attempting to quantify the relationship between cause and effect. However, the wide range of approaches that have been used in attribution studies in the past few decades can also be laid out on a spectrum ranging from soft to hard, or from the least to the most quantitative.

Attribution of Flooding to Climate

The attribution of trends in flood magnitude and frequency to changes in the climate system is possibly the largest area of flood attribution studies. Four main approaches can be distinguished to assess whether climate changes are expressed in flood flows and will be elaborated: (a) simple spatial (visual) correlation and inference, (b) the use of minimally impacted or climate-sensitive gauges, (c) approaches that explicitly measure the relationship between flooding and climate variables, and (d) hydrologic modeling.

The simplest approach is that of spatial correlation between trends in precipitation and flooding on a purely visual level. Analyses of precipitation patterns across the conterminous United States have indicated that, during the 20th century, precipitation increased by approximately 10% (Karl & Knight, 1998) due to the heightened frequency of rainfall days and of heavy or extreme precipitation events (e.g., Field et al., 2012). Extreme precipitation events grew by +3% per decade for 1931–1996, particularly over the region ranging from the central Great Plains to the southern Great Lakes (Kunkel, Andsager, & Easterling, 1999), while the top 1% of precipitation events increased by almost 20% (Gutowski et al., 2008). These increases become greater towards the end of the century (Pryor, Howe, & Kunkel, 2009), and the amounts of rain falling as precipitation have been significantly above average since 1991 (Walsh et al., 2014). Regionally, the third National Climate Assessment indicates that heavy precipitation—measured as the 99th percentile of daily precipitation events—has increased more than would be expected from natural variations across the Northeast, Midwest, Puerto Rico, Southeast, Great Plains, and Alaska, but not in the Southwest, Hawaii or the Northwest (Walsh et al., 2014). The strongest increases (more than 30% above average) are detected in the Northeast, Midwest, and upper Great Plains (Walsh et al., 2014), and the increases in the number of days with heavy precipitation (defined as the heaviest 1% of events, or using an extreme precipitation index) have been strongest over the Northeast and Midwest (Karl et al., 2009; Kunkel et al., 2013). These spatial trends have been correlated visually with trends in flooding: Mallakpour and Villarini (2015) showed a strong visual correlation between the direction of trends in heavy rainfall and in flood magnitude and frequency over the central United States between 1962 and 2011. Slater et al. (2015) also pointed to the spatial correlation between detected trends in flood frequency and other studies that assessed changes in climate characteristics over the conterminous United States, such as the extreme precipitation index (Janssen, Wuebbles, & Kunkel, 2014).

A second approach tries to detect the hydro-climatic signal in flood flows by using only streamflow records obtained from climate sensitive stations. A number of stream gauge networks were set up in the second half of the 20th century with the purpose of enabling such attribution studies. The idea was to select sites with records that were sufficiently long to capture climatic variations (e.g., more than 50 years), and minimally affected, that is, unimpaired by the various anthropogenic influences to river systems (e.g., regulation, abstraction, or flow augmentation). The first such network to be set up was the USGS Hydrologic Benchmark Network, or HBN (Leopold, 1962), which aimed to provide long-term time series of flow and water chemistry in stations least affected by human activities. Now only a few dozen of the initial stations remain (Murdoch, McHale, Mast, & Clow, 2005). Several decades later, in 1992, the USGS Hydro-Climatic Data Network (HCDN) was established, with 1,659 stations selected based on low basin development, lack of regulations and/or diversions, and record length (Slack & Landwehr, 1992), and slightly less rigid selection criteria in data-sparse regions (Whitfield & Burn, 2012). Many studies have used these minimally impacted stream gauge networks to document climatically driven trends in flood flows. The HCDN has been by far the most widely used network (e.g., Douglas, Vogel, & Kroll, 2000; Lins & Slack, 1999, 2005; McCabe & Clark, 2005; McCabe & Wolock, 2002). Lins and Slack (2005), for instance, used 435 HCDN stations to investigate changes in the timing of annual flows. They found no systematic change across the conterminous United States and concluded that the increases in low to moderate flows were not accompanied by an increase in flooding.

Because the original HCDN flow records ended in 1988, many studies have sought to update and verify the original HCDN stream gauge selection. Collins (2009) selected 28 HCDN gauges not influenced by regulation (by reviewing peak flow qualification codes and water-data reports) with continuous data spanning 1951–2006; Armstrong et al. (2012) focused on 23 of the same gauges; and Collins et al. (2014) used ten of the gauges over New England. Armstrong (2013) also reviewed HCDN stations for inclusion in their study, and retained only the records lacking regulation/diversion, with over 60 years of record reaching beyond 2009, and no less than 5% of missing data. Hodgkins, Dudley, and Huntington (2003) used HCDN stations in New England with flows free of anthropogenic influences and at least 50 continuous years of record up to water year 2000. Many of these HCDN stations have now been discontinued and, due to the lack of updates, the network was progressively abandoned.

In 2010, the Geospatial Attributes of Gages for Evaluating Streamflow (GAGES) network was established (Falcone, Carlisle, Wolock, & Meador, 2010). Of the 9,324 stations in the network, 2,061 were identified as being located in “reference” catchments, those least affected by anthropogenic influences. Reference sites were identified based on three criteria: (a) the hydrologic disturbance within the watershed had to be less than in 75% of all watersheds within the ecoregion (resulting from reservoirs, withdrawal, road density, and other factors); (b) lack of regulation; and (c) verification of satellite imagery for the presence of human activities. As a subset of the reference stations, the GAGES-II project also included an updated HCDN network, composed of 743 stations, distributed relatively homogeneously across the United States, 203 of which have at least 60 years of data (Lins, 2012). Surprisingly, the GAGES-II classification of reference sites and the HCDN-2009 update are not very well known and have not yet been widely used for attributing climate drivers in flood studies. Slater et al. (2013) used GAGES-II reference sites to assess the relationship between trends in high flows (Q90) and bed elevation, and found that short-term variability in flood flows altered riverbed level, capturing shifts in climate, and altering the frequency of overbank flows. Slater and Villarini (2017) used predictors from GAGES-II (including the reference classification) to assess controls on the relationship between trends in precipitation and flood frequency.

In addition to the GAGES-II set of reference stream gauges, the “Sentinel Watersheds” program was established by the USGS National Streamflow Information Program (NSIP) as a set of catchments that are minimally affected by human activities and used for trend studies aiming to assess the effects of changes in climate, land use, and management on water resources (National Research Council, 2004). The Sentinel Watersheds program is a network of 874 sites, including both HCDN stations and HBN stations, which are relatively free from anthropogenic influence (i.e., have no large reservoir upstream) and where 80% of the catchment area is within one single eco-hydrologic unit. See Whitfield and Burn (2012) for a comprehensive description of global reference hydrologic networks for trend analyses. Last, the international Model Parameter Estimation Project (MOPEX; Duan et al., 2006) was initiated in 1996 at the global scale to facilitate parameter estimation for hydrologic modeling and to bring together international hydrologists and land surface modelers. A large number of hydrologic records within MOPEX are from the United States (Schaake, Cong, & Duan, 2006) and provide hydrometeorological data (precipitation, temperature, and streamflow), a dominant soil type, and a dominant vegetation type.

Because the existing minimally impaired gauge datasets were of variable quality and/or not inclusive of all USGS gauging stations, a number of studies developed their own reference classifications. Dettinger and Cayan (1995) selected five river basins in California where flow is “wild or nearly unimpaired,” with little development or land use change. Slater et al. (2015) classified 401 USGS stream gauges based on their level of anthropogenic flow modification (least, intermediate, and most modified), by assessing the mean daily flow time series, USGS annual water data reports, maps and Google Earth aerial images, to determine if geomorphic effects on flood frequency varied according to the level of human interference in flow records. Hirsch and Ryberg (2012) selected 200 USGS stream gauges in the conterminous United States, with at least 85 years’ length through water year 2008, in basins with little or no reservoir storage or urban development (<150 persons/km2 in 2000). Using these gauges, they analyzed relationships between long-term flood records and global mean carbon dioxide concentration across four large regions of the conterminous United States and found no evidence of a significant relationship after correcting for the effects of spatial and serial correlation. Groisman et al. (2001) used a network of collocated rain and streamflow gauges with more than 60 years of synchronous daily observations, and computed the number of days above the monthly 90th and 99th percentiles for 1961–1990. To reduce the variance in flow data, eliminate noise, and facilitate the detection of climate-induced changes in flood frequency, they pooled these data and computed standardized regionally averaged trends for comparison with changes in the frequency of heavy precipitation. They found that in the western states, trends in heavy precipitation did not translate into flood records, suggesting that the decrease in snow cover extent is complicating the relationship between heavy precipitation and streamflow. In the eastern United States, on the contrary, where snowmelt has been a small fractional contribution to heavy runoff, the data revealed a significant relationship between the frequency of heavy precipitation and high streamflow, both annually and during months of maximum discharge.

A third approach, which goes further than spatial correlation and the use of climate-sensitive gauges, aims to quantify the association between the time series of one variable (e.g., flood frequency) and the climate variable (e.g., annual rainfall). Relatively few studies have used this approach to detect changes in flooding. Slater and Villarini (2017) observed time series of flood peaks and basin-averaged rainfall extremes, tailored over the same time periods, and quantified the association between the two.

Last, approaches that are based on hydrologic modeling typically attempt to reproduce the flow distribution over time, so if a divergence is found between the observed and modeled distributions, then the difference can be isolated and attributed to external (e.g., climate-driven) forcing rather than to natural internal variability (Harrigan, Murphy, Hall, Wilby, & Sweeney, 2014). Hamlet and Lettenmaier (2007) forced the Variable Infiltration Capacity (VIC) hydrologic model with observed temperature data. They found that, as a result of increasing temperatures and reduced spring snowpack, the flood risk had reduced in snowmelt-dominated basins and increased in the warm coastal basins of Washington, Oregon, and California. Other studies are mostly at the basin-scale. Davis Todd, Goss, Tripathy, and Harbor (2007) used the VIC model with long-term records of flow, precipitation, and land-use in a rapidly urbanizing basin in Indiana. By holding the climatology constant and modeling the land-cover changes, they showed that the increases in flows that occurred between 1940 and 2005 were not climate-driven, and that over two-thirds of peak flow events were not directly caused by the peak daily precipitation events. Similar hydrological attribution/modeling approaches can also be used to project the influence of specific drivers on flood flows in the future. Praskievicz and Chang (2011) simulated the impacts of climate change versus urban development in Oregon. They forced two catchment-scale models with statistically downscaled data from seven GCMs with two scenarios of possible land use, and found that high flows were likely to increase by 69 to 80% for the high climate change scenario. Similarly, Jung and Chang (2011) used the Precipitation Runoff Modeling System to simulate future changes in the Willamette basin in Oregon under eight GCM scenarios and found projected increasing trends in the top 5% of streamflows associated with winter flooding.

While it is clear that precipitation plays a major role in flood events, it not yet well understood whether flooding and climate modes can be related over longer timescales. Climate modes are patterns or indices that recur spatially, often in an oscillatory manner (e.g., Wang & Schimel, 2003) over interannual and interdecadal time scales, and influence the atmospheric drivers of regional precipitation. By establishing a relationship between precipitation and these modes, it becomes possible to connect climate and flooding. This is a topic that has not been dealt with extensively, but one that could have large benefits for flood predictions by leveraging the memory of the climate system. Hamlet and Lettenmaier (2007) showed, for instance, that flood risks vary with the Pacific Decadal Oscillation (PDO) and the interannual El Nino-Southern Oscillation (ENSO). They found that the largest changes in flood patterns occurred when PDO/ENSO were in phase, especially in the southwestern United States. In the mid-Atlantic region and New England, Armstrong (2013) found that increases in flood magnitude and frequency were related to the winter North Atlantic Oscillation phase. Collins et al. (2014), however, found little evidence of a relationship between flood-producing synoptic storms and the North Atlantic Oscillation (NAO)/ENSO over the eastern United States. Mallakpour and Villarini (2016b) conducted a broad investigation of the relationship between long-term trends in POT at 774 stream gauges and five climate indices affecting both the Atlantic and Pacific oceans, including the PDO, the NAO, the Southern Oscillation Index (SOI), the Atlantic Multidecadal Oscillation (AMO), and the Pacific-North American pattern (PNA). They showed that the variability in the frequency of POT was driven by variability in the climate system, and in particular by the PNA.

Attribution of Flooding to Dams And Engineering Structures

Dams and impoundment structures have had notable effects on the distribution of flood flows across the continental United States. The widespread construction of dams throughout the 20th century has had substantial influence on the spatial and temporal distribution of peak flows across the United States. Dams alter the natural flow regime by reducing the magnitude and frequency of high flows for the purpose of flood control, electric power generation, irrigation, local water use, recreational activities, and navigation (Poff, Allan, Bain, & Karr, 1997). By the late 1980s, almost one million kilometers of rivers in the United States were already controlled by dams (Echeverria, Barrow, & Roos-Collins, 1989), and by the end of the 20th century, 75,000 dams were in place and capable of storing almost the equivalent of one year’s runoff (Graf, 1999). The largest of these dams have been shown to reduce the annual peak discharges by two-thirds and sometimes by up to 90% (Graf, 2006). At gauges on the Great Miami River, Hiwassee River, Red River at Fargo, and the Columbia River, for example, significant change points in the peak flow time series were detected as a result of regulation and diversions, in 1922 on the Great Miami River, 1942 on the Hiwassee River and Red River at Fargo, and 1938 on the Columbia River (Villarini et al., 2009).

The effects of dams on flood flows can also be indirect, due to the narrowing and simplification of river channels below the dam (Graf, 2006, Van Steeter & Pitlick, 1998). By reducing the capacity of river channels to contain flood flows, these geomorphic effects can heighten the frequency and inundation extent (Slater, 2016; Slater et al., 2015). Such changes can occur over tens of kilometers beneath the dam (Gregory & Park, 1974). High-flow that is released immediately below dams is termed hungry (Kondolf, 1997), because it is sediment-starved: flows with reduced sediment concentration have excess energy and transport capacity, so they erode the riverbed and banks until the riverbed material coarsens and a new equilibrium is reached, where the channel can no longer incise (Williams & Wolman, 1984). The eroded sediment is deposited further downstream, resulting in channel aggradation lower in the basin (Schmidt & Wilcock, 2008) and heightened flood flows (Stover & Montgomery, 2001). As a result, dams create a redistribution of flood hazard at basin scales, as river channel capacity of stream channels is increased immediately below the dams (reducing flood frequency) and decreased lower in the basins (increasing flood frequency) (Slater et al., 2015). Flood attribution studies have focused on two other areas specifically: the effects of urbanization and agriculture on flood flows.

Attribution of Flooding to Urbanization

In the United States, more than 80% of the population now lives in urban areas (US Census Bureau, 2010). Urbanization was considered by Leopold (1968) as the single most forceful land-use change affecting runoff, through its effects on the percentage of impervious area, and it is now the second leading cause of stream impairment (Paul & Meyer, 2001). Increases in imperviousness arise from the construction of buildings, roads, and paved areas, so rainwater infiltration is reduced, runoff increased, and stormwater flows rapidly off the land, accelerating the rate of transmission of water to the streams. As a result, peak flows arising during storm events are altered: the lag time, or time interval between the center of the mass of the storm and that of the hydrograph, is decreased by the construction of artificial paths (e.g., streets, roofs, storm sewers), so floods are larger in magnitude and peak more rapidly (Leopold, 1968). Additionally, the average flood duration is decreased, and larger floods recur more frequently (see Jacobson, 2011; Paul & Meyer, 2001, for a review). One exception to these effects occurs in urban areas with in-channel or detention storage, where flood peaks may actually be reduced in comparison with rural catchments (Sauer, Thomas, Stricker, & Wilson, 1983).

Existing attribution research regarding the effects of urbanization on flooding is based largely on case studies and paired catchment approaches. Graf (1977) considered the progressive suburbanization in a catchment in Iowa City and found that it reduced the hydrograph lag time, while heightening the kurtosis (i.e., peakedness) of flood events. Smith et al. (2002) observed an urbanizing catchment in the Charlotte metropolitan area of North Carolina, and found faster flood peak response in the urbanized section of the basin. White and Greer (2006) showed that increases in urban land from 9% to 37%, from 1966 to 2000, in Los Peñasquitos Creek, Southern California, heightened flood magnitudes substantially, despite a doubling of the area of riparian vegetation.

The paired catchment approach is considered one of the most robust methods for understanding the effects of land-use changes on streamflow (Salavati, Oudin, Furusho-Percot, & Ribstein, 2016). Paired catchment studies function best in small catchments (e.g., <1km2), where the precipitation, soil/geology, topography, and other physical parameters can be controlled for, to ascertain similar conditions between the treatment and the control catchment. McCormick, Eshleman, Griffith, and Townsend (2009), for example, use a paired catchment approach in Maryland to detect trends in normalized annual maximum flows under coal mining versus un-mined conditions, and they showed that peak runoff was higher and the centroid lag time shorter in the coal-mined basin in comparison with the un-mined basin. Other hydrologic modeling approaches, like those described at the end of the section “Attribution of Flooding to Climate”), are also being used increasingly to detect the effects of land-use changes on flood flows.

Attribution of Flooding to Agriculture and Other Land-Use Changes

The field of attribution of changes in flooding to agriculture is also still an active area of research. As with the previous fields of attribution, it is possible to distinguish between soft and hard approaches ranging from case studies and paired catchment approaches to physically and statistically based modeling.

Case studies are generally based on time series of flood patterns and agricultural land use at the catchment-scale, which allow inferences to be drawn on the causes of change. Potter (1991) observes decreases in flood peaks and winter/spring flood volumes in a watershed in southwestern Wisconsin. The lack of any relationship between the hydrological and climatological variables, alongside the increase in row crops (which would normally heighten flood peaks) leads the author to speculate that the decreases must result from soil conservation practices such as strip cropping, contour ploughing, crop rotations, and forest management. These types of inference-based approaches have been largely abandoned in favor of paired catchment approaches. Paired catchment approaches are also commonly used in hydrological studies to detect any effects arising from changes in agricultural practices and/or forestry, such as thinning, clear-cutting, or removal of riparian vegetation. Kramer, Burkart, Meek, Jaquis, and James (1999), for example, observed four small watersheds of 30–60 hectares in southwest Iowa that were cultivated in corn, with different forms of tillage and conservation practices. The authors showed that the implementation of conservation tillage practices between the 1970s and 1990s reduced storm-driven runoff.

Modeling studies are also considered as a robust attribution approach for quantifying the effects of agriculture on flood distributions and can be subdivided into two groups: physical and statistical modeling. Physically based modeling allows the investigators to modulate the influence of different driving variables and measure the outcomes. Schilling, Jha, Zhang, Gassman, and Wolter (2008) investigate the impacts of land use and land cover change on the water balance of an Iowan watershed using the soil and water assessment (SWAT) model. They show that increased corn production in place of grasslands (perennial cover) produces an increase in surface runoff due to the decreased soil infiltration. Seibert and McDonnell (2010) use change-detection methods based on the HBV model (Bergström, 1992) in a headwater catchment in Oregon. By simulating daily discharge with precipitation and temperature inputs, they were able to determine that peak flows increased in response to forest clear-cutting.

Statistically based modeling approaches are becoming increasingly popular in flood attribution. Zhang and Schilling (2006) use simple statistical trend analysis to infer the effect of agricultural practices (namely the conversion of perennial vegetation to seasonal row crops, especially soybeans) on streamflow. They separate long-term daily flow time series in the Mississippi River Basin into storm flow (surface runoff) and base flow (groundwater discharge). The authors find that the overall trend towards increasing streamflow is caused by the component, and not the stormwater, suggesting that changes in soybean cover have not altered peak flows. New statistical approaches are now emerging to model the relationship between changing flood flows, precipitation, and agriculture. Villarini and Strong (2014) modeled discharge as a function of observed annual precipitation and total harvested corn and soybean acreage using a gamma distribution. The goodness-of-fit of these models was such that the variations in discharge could be attributed to the corresponding changes in precipitation and agricultural intensity. Villarini, Scoccimarro, White, Arnold, Schilling, and Ghosh (2015) developed a modeling framework to evaluate the relative influence of precipitation and land use/land cover on discharge in an agricultural watershed. They showed that the projected increases in high flows could be offset by reducing the fraction of the catchment that was cultivated (and converting it to perennial vegetation such as switchgrass). Slater, Villarini, Bradley, and Vecchi (unpublished manuscript a) used a similar approach to Villarini and Strong (2014) to develop dynamic seasonal flow forecasts using the most recently available precipitation forecasts from the North American multi-model ensemble (NMME) (Kirtman et al., 2014). Statistically, the approach allows disentanglement of the different drivers of changing flood magnitudes.

These different flood-attribution methods can be compared and contrasted. Bowling, Storck, and Lettenmaier (2000) observed changes in flood magnitude across 23 catchments in western Washington in response to changes in logging practices over a period of 70 years. They found increasing peak flows in the hydrological model, but not in the paired catchment analysis, suggesting that the model was better able to filter out the natural variability and detect the signal in the data than the paired catchment approach. More recently, Salavati et al. (2016) considered the strengths and weaknesses of both methods (paired catchment and modeling) in 43 U.S. river basins to detect the influence of urbanization on high and low flows. They found good agreement between the two approaches, although, surprisingly, they noted that the impacts of urbanization on the flow distributions was hard to generalize.

Changes in the magnitude and frequency of flood flows can thus be attributed to fluctuations in climate, water management, urbanization, agriculture, and other types of land-cover using a variety of approaches that range from soft to hard. Future research in this area will undoubtedly seek to develop the most statistically robust techniques for disentangling the different drivers of changing flood hazards and, ultimately, to achieve the different “ingredients” of the attribution process, as described by Merz et al. (2012).

Moving Forward

Much effort has been dedicated to the quantification of changes in flood events across the United States and to the examination of their possible causal mechanisms. The increasing availability of hydro-climatologic data across the globe, including satellite-based estimates of precipitation (Quintero et al., 2016), land surface temperature (Parinussa, Lakshmi, Johnson, & Sharma, 2016), river discharge (Gleason & Smith, 2014), and basin-scale water storage (Reager, Thomas, and Famiglietti, 2014), is leading to continual improvements in flood hazard estimates and projections (García-Pintado et al., 2015). Moving forward, it is becoming increasingly critical to shift the paradigm of flood analysis from the sole detection of changes in flood frequency to the attribution and projection of those changes. This paradigm shift has major implications from both a scientific and a practical perspective. From a scientific standpoint, the attribution of changes in flood peak records will lead to an improved understanding of the physical processes that are responsible for the inter-annual variability in these records, thus advancing the hydrologic sciences. From an engineering perspective, the sole detection of changes is no longer a viable option, as past flood records are no longer representative of the future (e.g., Milly et al., 2008), and the extrapolation of trend lines into the future is technically hazardous, as it is not known when or where the next step changes may occur. However, if we can understand what factors are responsible for the observed changes, and can project them using global climate model predictions and projections, then we will be better positioned to provide estimates of future flood design.


Alila, Y., & Mtiraoui, A. (2002). Implications of heterogeneous flood-frequency distributions on traditional stream-discharge prediction techniques. Hydrological Processes, 16, 1065–1084.Find this resource:

Armstrong, W. H. (2013). Hydroclimatic flood trends in the northeastern United States and linkages with large-scale atmospheric circulation patterns. Hydrological Sciences, 59(9), 1636–1655.Find this resource:

Armstrong, W. H., Collins, M. J., & Snyder, N. P. (2012). Increased frequency of low-magnitude floods in New England. Journal of the American Water Resources Association, 48(2), 306–520.Find this resource:

Barnett, T. P., Adam, J. C., & Lettenmaier, D. P. (2005). Potential impacts of a warming climate on water availability in snow-dominated regions. Nature, 438(7066), 303–309.Find this resource:

Berghuijs, W. R., Woods, R. A., Hutton, C. J., & Sivapalan, M. (2016). Dominant flood generating mechanisms across the United States. Geophysical Research Letters, 43(9), 4382–4390.Find this resource:

Bergström, S. (1992). The HBV model: Its structure and applications (Report No. 4). Swedish Meteorological and Hydrological Institute.

Blöschl, G., & Sivapalan, M. (1995). Scale issues in hydrological modeling: A review. Hydrological Processes, 9(3–4), 251–290.Find this resource:

Booth, D. B. (1991). Urbanization and the natural drainage system: Impacts, solutions, and prognoses. The Northwest Environmental Journal, 7, 93–118.Find this resource:

Booth, D. B., & Jackson, C. R. (1997). Urbanization of aquatic systems: Degradation thresholds, stormwater detection, and the limits of mitigation. Journal of the American Water Resources Association, 33(5), 1077–1090.Find this resource:

Bowling, L. C., Storck, P., & Lettenmaier, D. P. (2000). Hydrologic effects of logging in western Washington, United States. Water Resources Research, 36(11), 3223–3240.Find this resource:

Brillinger, D. R. (2001). Time series: Data analysis and theory. Classics in Applied Mathematics Book 36, Philadelphia: SIAM.Find this resource:

Cheng, L., AghaKouchak, A., Gilleland, E., & Katz, R. W. (2014). Non-stationary extreme value analysis in a changing climate. Climatic Change, 127(2), 353–369.Find this resource:

Choi, O., & Fisher, A. (2003). The impacts of socioeconomic development and climate change on severe weather catastrophe losses: Mid-Atlantic Region (MAR) and the US. Climatic Change, 58(1), 149–170.Find this resource:

Collins, M. J. (2009). Evidence for changing flood risk in New England since the late 20th century. Journal of the American Water Resources Association, 45(2), 279–290.Find this resource:

Collins, M. J., Kirk, J. P., Pettit, J., DeGaetano, A. T., McCown, M. S., Peterson, T. C., et al. (2014). Annual floods in New England (USA) and Atlantic Canada: Synoptic climatology and generating mechanisms. Physical Geography, 35(3), 195–219.Find this resource:

Cunnane, C. (1973). A particular comparison of annual maxima and partial duration series methods of flood frequency prediction. Journal of Hydrology, 18, 257–271.Find this resource:

Davis Todd, C. E., Goss, A. M., Tripathy, D., & Harbor, J. M. (2007). The effects of landscape transformation in a changing climate on local water resources. Physical Geography, 28(November), 21–36.Find this resource:

Dettinger, M. D., & Cayan, D. R. (1995). Large-scale atmospheric forcing of recent trends toward early snowmelt runoff in California. Journal of Climate, 8(3), 606–623.Find this resource:

Diehl, T., & Potter, K.W. (1987). Mixed flood distribution in Wisconsin. In V. P. Singh (Ed.), Hydrologic frequency modeling (pp. 213–226). Dordrecht, Netherlands: Kluwer Academic.Find this resource:

Douglas, E. M., Vogel, R. M., & Kroll, C. N. (2000). Trends in floods and low flows in the United States: Impact of spatial correlation. Journal of Hydrology, 240(1), 90–105.Find this resource:

Downton, M. W., Miller, J. Z. B., & Pielke, R. A. (2005). Reanalysis of US National Weather Service flood loss database. Natural Hazards Review, 6, 13–22.Find this resource:

Duan, Q., Schaake, J., Andreassian, V., Franks, S., Goteti, G., Gupta, H. V., et al. (2006). Model Parameter Estimation Experiment (MOPEX): An overview of science strategy and major results from the second and third workshops. Journal of Hydrology, 320(1–2), 3–17.Find this resource:

Dupuis, D. J. (1998). Exceedances over high thresholds: A guide to threshold selection. Extremes, 1(3), 251–261.Find this resource:

Dury, G. H. (1961). Bankfull discharge: An example of its statistical relationships. International Association of Scientific Hydrology. Bulletin, 6(3), 48–55.Find this resource:

Echeverria, J. D., Barrow, P., Roos-Collins, R. (1989). Rivers at risk: The concerned citizen’s guide to hydropower. Washington, DC: Island Press.Find this resource:

Falcone, J. A., Carlisle, D. M., Wolock, D. M., & Meador, M. R. (2010). GAGES: A stream gage database for evaluating natural and altered flow conditions in the conterminous United States. Ecology, 91(2), 621–621.Find this resource:

Field, C. B., Barros, V., Stocker, T. F., Dahe, Q., Dokken, D. J., Ebi, K. L., et al. (Eds.). (2012). Managing the risks of extreme events and disasters to advance climate change adaptation: Special report of the Intergovernmental Panel on Climate Change. Cambridge, U.K.: Cambridge University Press.Find this resource:

García-Pintado, J., Mason, D. C., Dance, S. L., Cloke, H. L., Neal, J. C., Freer, J., et al. (2015). Satellite-supported flood forecasting in river networks: A real case study. Journal of Hydrology, 523, 706–724.Find this resource:

Georgakakos, A., Fleming, P., Dettinger, M., Peters-Lidard, C., Richmond, T.C., Reckhow, K., et al. (2014). Water resources. In J. M. Melillo, T. C. Richmond, & G. W. Yohe (Eds.), Climate change impacts in the United States: The Third National Climate Assessment (pp. 69–112). U.S. Global Change Research Program. Washington, DC: U.S. Government Printing Office.Find this resource:

Gleason, C. J., & Smith, L. C. (2014). Toward global mapping of river discharge using satellite images and at-many-stations hydraulic geometry. Proceedings of the National Academy of Sciences, USA, 111(13), 4788–4791.Find this resource:

Graf, W. L. (1977). Network characteristics in suburbanizing streams. Water Resources Research, 13(2), 459–463.Find this resource:

Graf, W. L. (1999). Dam nation: A geographic census of American dams and their large-scale hydrologic impacts. Water Resources Research, 35(4), 1305.Find this resource:

Graf, W. L. (2006). Downstream hydrologic and geomorphic effects of large dams on American rivers. Geomorphology, 79, 336–360.Find this resource:

Grego, J. M., & Yates, P. A. (2010). Point and standard error estimation for quantiles of mixed flood distributions, Journal of Hydrology, 391, 289–301.Find this resource:

Grego, J. M., Yates, P. A., & Mai, K. (2015). Standard error estimation for mixed flood distributions with historic maxima. Environmetrics, 26, 229–242.Find this resource:

Gregory, K. J., & Park, C. (1974). Adjustment of river channel capacity downstream from a reservoir. Water Resources Research, 10(4), 870–873.Find this resource:

Groisman, P. Y., Knight, R. W., & Karl. T. R. (2001). Heavy precipitation and high streamflow in the contiguous United States: Trends in the twentieth century. Bulletin of the American Meteorological Society 82(2), 219–246.Find this resource:

Gutowski, W. J., Hegerl, G. C., Holland, G. J., Knutson, T. R., Mearns, L. O., Stouffer, R. J., et al. (2008). Causes of observed changes in extremes and projections of future changes. In T. R. Karl, G. A. Meehl, C. D. Miller, S. J. Hassol, A. M. Waple, & W. L. Murray (Eds.), Weather and climate extremes in a changing climate: Regions of focus: North America, Hawaii, Caribbean, and U. S. Pacific Islands (pp. 81–116). Synthesis and Assessment Product 3.3. Washington, DC: U.S. Climate Change Science Program.Find this resource:

Hamlet, A. F., & Lettenmaier, D. P. (2007). Effects of 20th century warming and climate variability on flood risk in the western U.S. Water Resources Research, 43(6).Find this resource:

Harrigan, S., Murphy, C., Hall, J., Wilby, R. L., & Sweeney, J. (2014). Attribution of detected changes in streamflow using multiple working hypotheses. Hydrology and Earth System Sciences, 18(5), 1935–1952.Find this resource:

Helsel, D. R., & Hirsch, R. M. (1992). Statistical methods in water resources. In Techniques of Water Resources Investigations of the United States Geological Survey: Book 4: Hydrologic analysis and interpretation. Washington, DC: U.S. Dept. of the Interior, Geological Survey.Find this resource:

Hirschboeck, K. K. (1987). Hydroclimatically defined mixed distributions in partial duration flood series. In V. P. Singh (Ed.), Hydrologic Frequency Modelling (pp. 199–212). Dorrdrecht, Netherlands: D. Reidel.Find this resource:

Hirschboeck, K. K. (1988). Flood hydroclimatology. In V. R. Baker, R. C. Kockel, & P. C. Patton (Eds.), Flood Geomorphology (pp. 27–49). New York: John Wiley.Find this resource:

Hirschboeck, K. K. (1991). Climate and floods. Water Supply Paper No. 2375. In R. W. Paulson (Ed.), National Water Summary 1988–1989: Hydrologic Events and Floods and Droughts (pp. 67–88). Washington, DC: U.S. Government Printing Office.Find this resource:

Hirsch, R. M., & Ryberg, K. R. (2012). Has the magnitude of floods across the USA changed with global CO 2 levels? Hydrological Sciences Journal, 57(1), 1–9.Find this resource:

Hodgkins, G. A. (2010). Historical changes in annual peak flows in Maine and implications for flood-frequency analyses. Scientific Investigations Report 2010–5094. Reston, VA: U.S. Geological Survey.Find this resource:

Hodgkins, G. A., Dudley, R., & Huntington, T. (2003). Changes in the timing of high river flows in New England over the 20th Century. Journal of Hydrology, 278(1–4), 244–252.Find this resource:

Jacobson, C. R. (2011). Identification and quantification of the hydrological impacts of imperviousness in urban catchments: A review. Journal of Environmental Management, 92(6), 1438–1448.Find this resource:

Janssen, E., Wuebbles, D., & Kunkel, K. E. (2014). Observational and model based trends and projections of extreme precipitation over the contiguous United States. Earth’s Future, 2(2), 99–113.Find this resource:

Jarrett, R. D., & Costa, J. E. (1988). Evaluation of the flood hydrology in the Colorado Front Range using precipitation, streamflow, and paleoflood data for the Big Thompson River basin. U.S. Geological Survey Water-Resources Investigations Report 87–4117. Reston, VA: U.S. Geological Survey.Find this resource:

Jung, I. W., & Chang, H. (2011). Assessment of future runoff trends under multiple climate change scenarios in the Willamette River Basin, Oregon, USA. Hydrological Processes, 25(2), 258–277.Find this resource:

Karl, T. R., & Knight, R. W. (1998). Secular trends of precipitation amount, frequency, and intensity in the United States. Bulletin of the American Meteorological Society, 79(2), 231–241.Find this resource:

Karl, T. R., Melillo, J. M., & Peterson, T. C. (eds.) (2009). Global Climate Change Impacts in the United States. Cambridge University Press.Find this resource:

Katz, R. W., & Brown, B. G. (1992). Extreme events in a changing climate: Variability is more important than averages. Climatic Change, 21(3), 289–302.Find this resource:

Kendall, M. G. (1975). Rank correlation methods. London: Griffin.Find this resource:

Kondolf, G. M. (1997). Hungry water: Effects of dams and gravel mining on river channels. Environmental Management, 21(4), 533–551.Find this resource:

Kousky, C., & Michel-Kerjan, E. (2015). Examining flood insurance claims in the United States: Six key findings. Journal of Risk and Insurance.Find this resource:

Kirby, W. (1969). On the random occurrence of major floods. Water Resources Research, 5(4), 778–784.Find this resource:

Kirtman, B. P., Min, D., Infanti, J. M., Kinter, J. L., Paolino, D. a., Zhang, Q., et al. (2014). The North American multimodel ensemble: Phase-1 seasonal-to-interannual prediction: Phase-2 toward developing intraseasonal prediction. Bulletin of the American Meteorological Society, 95(April), 585–601.Find this resource:

Klemeš, V. (1974). Some problems in pure and applied stochastic hydrology. Proceedings of the Symposium on Statistical Hydrology Miscellaneous Publication, No. 1275 (pp. 2–15). Washington, DC: U.S. Department of Agriculture.Find this resource:

Klemeš, V. (1993). Probability of extreme hydrometeorological events; A different approach. In Z. W. Kundzewicz Extreme hydrological events: Precipitation, floods and droughts (pp. 167–176). Publication No. 213. Oxfordshire: IAHS.Find this resource:

Knowles, N., & Cayan, D. R. (2002). Potential effects of global warming on the Sacramento/San Joaquin watershed and the San Francisco estuary. Geophysical Research Letters, 29(18), 1891, 1810.Find this resource:

Knox, J. C. (2001). Agricultural influence on landscape sensitivity in the Upper Mississippi River Valley. Catena, 42(2–4), 193–224.Find this resource:

Kramer, L. A., Burkart, M. R., Meek, D. W., Jaquis, R. J., & James D. E. (1999). Field-scale watershed evaluations in deep-loess soils: II. Hydrologic responses to different agricultural land management systems, Journal of Soil Water Conservation, 54, 705–710.Find this resource:

Kundzewicz, Z. W., Graczyk, D., Maurer, T., Pińskwar, I., Svensson, C., & Szwed, M. (2005). Trend detection in river flow series: Annual maximum flow. Hydrological Sciences Journal, 50(5).Find this resource:

Kundzewicz, Z. W., Robson, A. J. (2004). Change detection in hydrological records: A review of the methodology/Revue méthodologique de la détection de changements dans les chroniques hydrologiques. Hydrological Sciences Journal, 49(1), 7–19.Find this resource:

Kunkel, K. E., Andsager, K., & Easterling D. R. (1999). Long-term trends in extreme precipitation events over the conterminous United States and Canada. Journal of Climate, 12(8), 2515–2527.Find this resource:

Kunkel, K. E., Karl, T. R., Brooks, H., Kossin, J., Lawrimore, J. H., Arndt, D., et al. (2013). Monitoring and understanding trends in extreme storms: State of knowledge. Bulletin of the American Meteorological Society, 94(4), 499–514.Find this resource:

Lang, M., Ouarda, T. M. B. J., & Bobée, B. (1999). Towards operational guidelines for over- threshold modeling. Journal of Hydrology, 225, 103–117.Find this resource:

Langbein, W. B. (1949). Annual floods and the partial-duration flood series. American Geophysical Union Transactions, 30(6), 879–881.Find this resource:

Leadbetter, M. R. (1991). On a basis for “Peaks over Threshold” modeling. Statistics and Probability Letters, 12(4), 357–362.Find this resource:

Leopold, L. (1968). Hydrology for urban land planning: A guidebook on the hydrologic effects of urban land use. United States Geological Survey Circular 554.

Leopold, L. B. (1962). A national network of hydrologic bench marks. United States Geological Survey Circular 460-B.

Leopold, L. B., Wolman, M. G., & Miller, J. (1964). Fluvial processes in geomorphology. San Francisco: W. H. Freeman.Find this resource:

Lins, H. F. (2012). USGS Hydro-Climatic Data Network 2009 (HCDN-2009). US Geological Survey Fact Sheet 3047.

Lins, H. F., & Slack, J. R. (1999). Streamflow trends in the United States. Geophysical Research Letters, 26(2), 227–230.Find this resource:

Lins, H.F., & Slack, J.R. (2005). Seasonal and regional characteristics of U.S. streamflow trends in the United States from 1940 to 1999. Physical Geography, 26(6), 489–501.Find this resource:

Lombard, F. (1987). Rank test for changepoint problems. Biometrika, 74(3), 615–624.Find this resource:

Mallakpour, I., & Villarini, G. (2016a). A simulation study to examine the sensitivity of the Pettitt test to detect abrupt changes in mean. Hydrological Sciences Journal, 61(2), 245–254.Find this resource:

Mallakpour, I., & Villarini, G. (2015). The changing nature of flooding across the central United States. Nature Climate Change, 5(3), 250–254.Find this resource:

Mallakpour, I., & Villarini, G. (2016b). Investigating the relationship between the frequency of flooding over the central United States and large-scale climate. Advances in Water Resources, 92, 159–171.Find this resource:

Mann, H. B. (1945). Nonparametric tests against trend. Econometrica, 13, 245–259.Find this resource:

McCabe, G. J., Clark, M P. (2005). Trends and variability in snowmelt runoff in the western United States. Journal of Hydrometeorology, 6, 476–482.Find this resource:

McCabe, G. J. & Wolock, D. M. (2002). A step increase in streamflow in the conterminous United States. Geophysical Research Letters, 29(24), 38-1–38-4.Find this resource:

McCormick, B. C., Eshleman, K. N., Griffith, J. L., & Townsend, P. A. (2009). Detection of flooding responses at the river basin scale enhanced by land use change. Water Resources Research, 45(8), 1–15.Find this resource:

Merz, B., Vorogushyn, S., Uhlemann, S., Delgado, J., & Hundecha, Y. (2012). HESS opinions “more efforts and scientific rigour are needed to attribute trends in flood time series.” Hydrology and Earth System Sciences, 16(5), 1379–1387.Find this resource:

Merz, R., & Blöschl, G. (2003). A process typology of regional floods, Water Resour. Res., 39(12), 1340.Find this resource:

Milly, P. C. D, Betancourt, J., Falkenmark, M., Hirsch, R. M., Kundzewicz, Z. W., Lettenmaier, D. P., et al. (2008). Stationarity is dead: Whither water management? Science, 319(5863), 573–574.Find this resource:

Murphy, P. J. (2001). Evaluation of mixed-population flood-frequency analysis. Journal of Hydrologic Engineering, 6(1), 62–70.Find this resource:

Murdoch, P. S., McHale, M. R., Mast, M. A., & Clow, D.W. (2005). The U.S. Geological Survey Hydrologic Benchmark Network. U.S. Geological Survey Fact Sheet 2005–3135.

National Climate Data Center (NCDC). (2016). Billion-dollar weather and climate disasters.

National Research Council. (2004). Assessing the National Streamflow Information Program. Washington, DC: National Academies Press.Find this resource:

NOAA National Weather Service (2016). Hydrologic Information Center: Flood Loss Data.

Nayak, M. A., & Villarini, G. (2016). Evaluation of the capability of the Lombard test in detecting abrupt changes in variance. Journal of Hydrology, 534, 451–465.Find this resource:

Office of Services (2016). U.S. Natural Hazard Statistics, compiled by the Office of Climate, Water, and Weather Services, NOAA. See the 76-year list of severe weather fatalities.

Parinussa, R. M., Lakshmi, V., Johnson, F. M., & Sharma, A. (2016). A new framework for monitoring flood inundation using readily available satellite data, Geophysical Research Letters, 43(6), 2599–2605.Find this resource:

Paul, M. J., & Meyer, J. L. (2001). Streams in the urban landscape. Annual Review of Ecology and Systematics, 32, 333–365.Find this resource:

Pettitt, A. N. (1979). A non-parametric approach to the change-point problem. Applied Statistics, 28(2), 126–135.Find this resource:

Petrow, T., & Merz, B. (2009). Trends in flood magnitude, frequency, and seasonality in Germany in the period 1951–2002. Journal of Hydrology, 371(1–4), 129–141.Find this resource:

Pielke, R. A. Jr., & Downton, M. W. (2000) Precipitation and damaging floods: Trends in the United States, 1932–97. Journal of Climate, 13(20), 3625–3637.Find this resource:

Poff, N., Allan, J., Bain, M., & Karr, J. (1997). The natural flow regime. BioScience, 47(11), 769–784.Find this resource:

Potter, K. W. (1991). Hydrological impacts of changing land management practices in a moderate-sized agricultural catchment. Water Resources Research, 27(5), 845–855.Find this resource:

Praskievicz, S., & Chang, H. (2011). Impacts of climate change and urban development on water resources in the Tualatin River Basin, Oregon. Annals of the Association of American Geographers, 101(2), 249–271.Find this resource:

Pryor, S. C., Howe, J. A., & Kunkel, K. E. (2009). How spatially coherent and statistically robust are temporal changes in extreme precipitation in the contiguous USA? International Journal of Climatology, 29(1), 31–45.Find this resource:

Quintero, F., Krajewski, W. F., Mantilla, R., Small, S., & Seo, B.-C. (2016). A spatial–dynamical framework for evaluation of satellite rainfall products for flood prediction, Journal of Hydrometeorology, 17(8), 2137–2154.Find this resource:

Reager, J. T., Thomas, B. F., & Famiglietti, J. S. (2014). River basin flood potential inferred using GRACE gravity observations at several months lead time, National Geoscience, 7(8), 588–592.Find this resource:

Rossi, F., Fiorentino, M., & Versace, P. (1984). Two-component extreme value distribution for flood frequency analysis. Water Resources Research, 20, 847–856.Find this resource:

Rougé, C., Ge, Y., & Cai, X. (2013). Detecting gradual and abrupt changes in hydrological records. Advances in Water Resources, 53, 33–44.Find this resource:

Salas, J. D. (1993). Analysis and modeling of hydrologic time series. In D. R. Maidment (Ed.), Handbook of Hydrology (pp. 1–72). New York: McGraw-Hill.Find this resource:

Salavati, B., Oudin, L., Furusho-Percot, C., & Ribstein, P. (2016). Modelling approaches to detect land-use changes: Urbanization analyzed on a set of 43 US catchments. Journal of Hydrology, 538, 138–151.Find this resource:

Sauer, V. B., Thomas, W. O., Stricker, V. A., & Wilson, K. V. (1983). Flood characteristics of urban watersheds in the United States. U.S. Geol. Water Supply Paper, 2207. Alexandria, VA: U.S. Government Printing Office.Find this resource:

Schaake, J., Cong, S., & Duan, Q. (2006). The US MOPEX data set. IAHS publication no. 307.

Schilling, K. E., Jha, M. K., Zhang, Y.-K., Gassman, P. W., & Wolter C. F. (2008). Impact of land use and land cover change on the water balance of a large agricultural watershed: Historical effects and future directions. Water Resources Research, 44(7).Find this resource:

Schmidt, J. C., & Wilcock, P. R. (2008). Metrics for assessing the downstream effects of dams. Water Resources Research, 44(4).Find this resource:

Seibert, J., & McDonnell, J. J. (2010). Land-cover impacts on streamflow: A change-detection modelling approach that incorporates parameter uncertainty. Hydrological Sciences Journal, 55(3), 316–332.Find this resource:

Shaw, S. B., & Riha, S. J. (2011). Assessing possible changes in flood frequency due to climate change in mid-sized watersheds in New York State, USA. Hydrological Processes, 25(16), 2542–2550.Find this resource:

Singh, V. P., Wang, S. X., & Zhang, L. (2005). Frequency analysis of nonidentically distributed hydrologic flood data, Journal of Hydrology, 307, 175–195.Find this resource:

Slack, J. R., & Landwehr J. M. (1992). Hydro-climatic data network: A U.S. Geological Survey streamflow data set for the United States for the study of climate variations, 1974–1988. U.S. Geological Survey Report No. 92–129.Find this resource:

Slater, L. J. (2016). To what extent have changes in channel capacity contributed to flood hazard trends in England and Wales? Earth Surface Processes and Landforms, 41(8), 1115–1128.Find this resource:

Slater, L. J., & Singer, M. B. (2013). Imprint of climate and climate change in alluvial riverbeds: Continental United States, 1950–2011. Geology, 41(5), 595–598.Find this resource:

Slater, L. J., Singer, M. B., & Kirchner, J. W. (2015). Hydrologic versus geomorphic drivers of trends in flood hazard. Geophysical Research Letters, 42(2), 370–376.Find this resource:

Slater, L.J., and Villarini, G. (2017). Recent trends in US flood risk. Geophysical Research Letters.Find this resource:

Smith, A. B., & Katz, R. W. (2013). US billion-dollar weather and climate disasters: Data sources, trends, accuracy and biases. Natural Hazards, 67(2), 387–410.Find this resource:

Smith, J. A., & Karr, A. F. (1986). Flood frequency analysis using the Cox Regression Model. Water Resources Research, 22(6), 890–896.Find this resource:

Smith, J. A., Baeck, M. L., Morrison, J. E., Sturdevant-Rees, P., Turner-Gillespie, D. F., & Bates, P. D. (2002). The regional hydrology of extreme floods in an urbanizing drainage basin. Journal of Hydrometeorology, 3(3), 267–282.Find this resource:

Smith, J. A., Baeck, M. L., Villarini, G., & Krajewski, W. F. (2010). The hydrology and hydrometeorology of flooding in the Delaware River Basin. Journal of Hydrometeorology, 11(4), 841–859.Find this resource:

Smith, J. A., Villarini, G., & Baeck M. L. (2011). Mixture distributions and the climatology of extreme rainfall and flooding in the Eastern US. Journal of Hydrometeorology, 12(2), 294–309.Find this resource:

Smith, R. L. (1984). Threshold methods for sample extremes. In J. T. de Oliveira (Ed.), Statistical extremes and applications (pp. 621–638). Dordrecht, Netherlands: Springer.Find this resource:

Stover, S., & Montgomery, D. R. (2001). Channel change and flooding, Skokomish River, Washington. Journal of Hydrology, 243(3–4), 272–286.Find this resource:

Svensson, C., Kundzewicz, Z. W., Maurer, T. (2005). Trend detection in river flow series: 2. Flood and low-flow index series. Hydrological Sciences Journal, 50(5), 811–824.Find this resource:

Todhunter, P. E. (2012). Uncertainty of the assumptions required for estimating the regulatory flood: Red River of the North. Journal of Hydrologic Engineering, 17(9), 1011–1020.Find this resource:

Trenberth, K. (2011). Changes in precipitation with climate change. Climate Research, 47(1), 123–138.Find this resource:

U.S. Census Bureau. (2010).

U.S. Interagency Advisory Committee on Water Data. (1982). Guidelines for determining flood flow frequency. Bulletin 17-B of the Hydrology Subcommittee. Reston, VA: U.S. Geological Survey, Office of Water Data Coordination.Find this resource:

Van Steeter, M. M., & Pitlick, J. (1998). Geomorphology and endangered fish habitats of the upper Colorado River: 1. Historic changes in streamflow, sediment load, and channel morphology. Water Resources Research, 34(2), 287–302.Find this resource:

Villarini, G. (2016). On the seasonality of flooding across the continental United States, Advances in Water Resources, 87, 80–91.Find this resource:

Villarini, G., Goska, R., Smith, J. A., & Vecchi, G. A. (2014). North Atlantic tropical cyclones and U.S. flooding, Bulletin of the American Meteorological Society, 95(9), 1381–1388.Find this resource:

Villarini, G., Scoccimarro, E., White, K. D., Arnold, J. R., Schilling, K. E., & Ghosh, J. (2015). Projected changes in discharge in an agricultural watershed in Iowa. Journal of the American Water Resources Association, 51(5), 1361–1371.Find this resource:

Villarini, G., Serinaldi, F., Smith, J. A., & Krajewski, W. F. (2009). On the stationarity of annual flood peaks in the continental United States during the 20th century. Water Resources Research, 45(8), 1–17.Find this resource:

Villarini, G., & Smith, J. A. (2010). Flood peak distributions for the eastern United States. Water Resources Research, 46(6), 1–17.Find this resource:

Villarini, G., & Smith, J. A. (2013). Flooding in Texas: Examination of temporal changes and impacts of tropical cyclones. Journal of the American Water Resources Association, 49(4), 825–837.Find this resource:

Villarini, G., Smith, J. A., Baeck, M. L., & Krajewski, W. F. (2011). Examining flood frequency distributions in the Midwest U.S. Journal of the American Water Resources Association, 47(3), 447–463.Find this resource:

Villarini, G., & Strong, A. (2014). Roles of climate and agricultural practices in discharge changes in an agricultural watershed in Iowa. Agriculture, Ecosystems, & Environment, 188, 204–211.Find this resource:

Vogel, R. M., Yaindl, C., & Walter, M. (2011). Nonstationarity: Flood magnification and recurrence reduction factors in the United States. Journal of the American Water Resources Association, 47(3), 464–474.Find this resource:

Walsh, J., Wuebbles, D., Hayhoe, K., Kossin, J., Kunkel, K., Stephens, G., et al. (2014). Our changing climate. In J. M. Melillo, T. C. Richmond, & G. W. Yohe (Eds.), Climate change impacts in the United States: The Third National Climate Assessment. U.S. Global Change Research Program (pp. 19–67).Find this resource:

Wang, G., & Schimel, D. (2003). Climate change, climate modes, and climate impacts. Annual Review of Environment and Resources, 28(1), 1–28.Find this resource:

Waylen, P. (1991). Modeling the effects of tropical cyclones on flooding in the Santa Fe River basin, Florida. GeoJournal, 23, 361–373.Find this resource:

Waylen, P., & Woo, M. (1982). Prediction of annual floods generated by mixed processes. Water Resources Research, 18(4), 1283–1286.Find this resource:

Webb, R. H., & Betancourt, J. L. (1992). Climatic variability and flood frequency of the Santa Cruz River, Pima County, Arizona. U.S. Geological Survey Water Supply Paper No. 2379.

White, M. D., & Greer, K. A. (2006). The effects of watershed urbanization on the stream hydrology and riparian vegetation of Los Peñasquitos Creek, California. Landscape and Urban Planning, 74(2), 125–138.Find this resource:

Whitfield, P. H. (2013). Is “Centre of Volume” a robust indicator of changes in snowmelt timing? Hydrological Processes, 27(18), 2691–2698.Find this resource:

Whitfield, P., & Burn, D. (2012). Reference hydrologic networks I. The status and potential future directions of national reference hydrologic networks for detecting trends. Hydrological Sciences Journal, 57(8).Find this resource:

Wilby R. L. 2006. When and where might climate change be detectable in UK river flows? Geophysical Research Letters, 33(19).Find this resource:

Williams, G. P., & Wolman, M. G. (1984). Downstream effects of dams on alluvial rivers. In Geological Survey Professional Paper 1286 (pp. 1–83). Washington, DC: U. S. Government Printing Office.Find this resource:

Yue, S., Pilon, P., & Cavadias, G. (2002). Power of the Mann-Kendall and Spearman’s rho tests for detecting monotonic trends in hydrological series. Journal of Hydrology, 259, 254–271.Find this resource:

Zhang, Y. K., & Schilling, K. E. (2006). Increasing streamflow and baseflow in Mississippi River since the 1940s: Effect of land use change. Journal of Hydrology, 324, 412–422.Find this resource: