Considering first , converting land use and terrain
information into a fractional coverage of breeding areas provided by
permanent water bodies is a significant challenge. Wave/ripples
action that can drown larvae [#!leprince:27!#] and the presence of
predators in larger bodies [#!fillinger:09!#] imply that larvae exist
only in a sub-fraction of such water bodies, in pooling that occurs on
the edges of lakes and rivers or the shallow edges of ponds. Higher
soil moisture in the vicinity of large water bodies can boost
available breeding sites by reducing infiltration loss and increasing
the lifetime of temporary puddles and ponds. Lastly, rivers and
streams can even confound classic relationships between rainfall and
vector density by actually providing more breeding sites during
drought periods when flow slows or stops altogether [#!haque:10!#].
This remains the subject of current research and the default VECTRI
model therefore sets
to zero in each grid cell, implying
that the breeding site availability is dominated by seasonal ephemeral
ponds and malaria incidence will be potentially underestimated in the
vicinity of larger semi-permanent water bodies. A user operating the
model for a local area with knowledge of permanent water bodies can
set this value appropriately in the namelist (default is 1.e-6).
From version 1.9 a optional database is provided for which
is derived from a 20m spatially resolved map of water bodies
(downloadable at
http://2016africalandcover20m.esrin.esa.int/viewer.php). As
stated above, large bodies of water are not suitable for vectors, and
instead the assumption is made that the enhancement is breeding site
availability is instead associated with pond site along lake/river
shores. Thus the CCI land cover product has been preprocessed to
count all land-water border cells at 20 meter resolution which are
then summed over a 5x5km grid to give a permanent breeding site
fraction. This fraction is usually much lower than 1%, but can
obtain values as high as 10% in swampy/marshland type environments.
Note that this derivation is static in time and does not account for
the seasonal cycle of emphemeral water bodies. It is recommended to
ensure that vector diffusion is switched on when using the spatial map
of permanent breeding sites in order to allow vectors to radiate out
from these malaria “hot-spots” zones associated with the
availability of year-round, perennial water sites. The dataset is
available in the file
“permanent_breeding_fraction_sentinal_africa.nc” in the data
directory. The user will need to project this onto the same grid as
the climate driving files and merge the information into the
datafile. The standard netcdf name for the field is “wperm”, but a
revised name can be specified in the namelist by using the field
“wperm_name”.
INCLUDE GRAPHIC OF FRACTION HERE.