Environmental Engineering Reference
In-Depth Information
Table 1.2
Summary of drivers of change in fluvial flooding systems (adapted from Hall et al. 2003b)
SPR
classi cation
Driver set
Drivers
Explanation
Catchment
runoff
Precipitation
Source
Quantity, spatial distribution of rainfall and intensity. Rain/snow
proportion
Urbanization
Pathway
Changes in land surface (e.g. construction of impermeable surfaces and
stormwater drainage systems)
Rural land management
Pathway
In
uences the function of surface and subsurface runoff. Changes include
the proportion of conservation/recreation areas and wetlands
Fluvial
processes
River morphology and
sediment supply
Pathway
Changes in river morphology that in uence ood storage and ood
conveyance
River vegetation and
conveyance
Pathway
Changes in river vegetation extent and type, e.g. in response to climate
change or due to changed maintenance or regulatory contraints
Societal
changes
Public behaviour
Pathway
Behaviour of oodplain occupants before, during and after oods can
signi cantly modify the severity of oods
Social vulnerability
Receptor
Changes in social vulnerability to ooding, e.g. due to changes in health
and tness, equity and systems of social provision
Economic
changes
Buildings and contents
Receptor
Changes in the cost of ood damage to domestic, commercial and other
buldings and their contents (e.g. due to increasing vulnerability of
domestic and commerical goods or increasing domestic wealth)
Urban vulnerability
Receptor
Changes in the number and distribution of domestic, commerical and
other buildings in oodplains
Infrastructure
Receptor
Systems of communication (physical and telecommunication), energy
distribution, etc.
Changes in the extent to which society is dependent on these systems
Agriculture
Receptor
Changes in the intensity and seasonality of agriculture, including removal
of agricultural land from production and hence changes in
vulnerability to
ood damage
relative importance of different drivers of change
for flood managers in the future.
The implications of change within flooding
systems are profound. Milly et al. (2008) observe
that water management decisions - their discus-
sion was of water management in general rather
than flood risk management in particular - can no
longer proceed under the assumption that 'the idea
that natural systems fluctuatewithin an unchang-
ing envelope of variability'. The stationarity-based
assumptions that have underpinned engineering
design and, in our case, flood riskmanagement are
therefore no longer valid. Consequently there is a
need for adaptive policies that can deliver effective
riskmanagement without relying upon untenable
assumptions of an unchanging environment.
This implies a need for better models to repre-
sent these changing conditions and better obser-
vations with which to parameterize models. A
recent study for the UK Environment Agency
(Wheater et al. 2007) indicated that, to address
these processes of long-term change, a new holis-
tic modelling framework is needed, to encompass
the following:
. quantitative scenario modelling of the drivers
and pressures that impact upon flood risk, includ-
ing global climate and socioeconomic change;
. whole catchment and shoreline modelling of
flood and erosion risks under uncertain future
climatic and socioeconomic conditions, andunder
a wide range of policy and human response
options;
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