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@PHDTHESIS{Weihermller:46201,
author = {Weihermüller, Lutz},
title = {{C}omparison of different soil water extraction systems for
the prognoses of solute transport at the field scale using
numerical simulations, field and lysimeter experiments},
volume = {55},
school = {Universität Bonn},
type = {Dr. (Univ.)},
address = {Jülich},
publisher = {Forschungszentrum Jülich GmbH Zentralbibliothek, Verlag},
reportid = {PreJuSER-46201},
isbn = {3-89336-402-1},
series = {Schriften des Forschungszentrums Jülich. Reihe Umwelt /
Environment},
pages = {XXII, 145 S.},
year = {2005},
note = {Record converted from VDB: 12.11.2012; Universität Bonn,
Diss., 2005},
abstract = {Sampling of water and solutes in soils is of major
importance to understand water movement and solute transport
in soils and to validate mathematical models. Porous cups
are widely used to extract soil water for monitoring solute
transport. However, it is not yet clear how the suction cup
influences the matrix potential in the surrounding soil and
which part of the soil is sampled. This research was
designed to numerically evaluate the activity domain, the
extraction domain and sampling area of a suction cup under
constant infiltration. A finite element model (HYDRUS-2D)
was used to simulate the effect of various applied suctions
at two infiltration rates on the water status in three soils
(clay loam, sandy clay and sandy soil). Particle tracking
was used to track the streamlines which define the sampling
area and extraction domain of the suction cup. In general,
the activity domain, the extraction domain and sampling area
of the suction cup depend primarily on the soil hydraulic
parameters and the upper boundary, and secondarily on the
applied suction. The results showed that the activity
domain, the extraction domain and the sampling area are
largest for highest ambient hydraulic conductivities. The
activity domain and the sampling area also decrease with
increasing infiltration rates. Further, the extraction
domain of the suction cup depends strongly on the duration
of water extraction. Soil heterogeneity seems to play a
minor role with respect to the activity domain and sampling
area of the cup, but a major role in the amount of extracted
water and solute breakthrough. In a second step, a lysimeter
and field experiment equipped with porous ceramic plates,
tensiometers, TDR-probes and suction cups was conducted over
a 427 day period to evaluate differences in soil water
sampling and solute transport for a conservative tracer and
the test compounds Methabenzthiazuron (MBT) and Ethidimuron
(ETD). In general, the two lysimeters at the lysimeter
station at the $\textit{Forschungszentrum Jülich}$ showed
comparable leaching behaviour over time, reflected by the
tensiometer, TDR and drainage measurements. In comparison to
the lysimeters the sampling pits at the test site
Merzenhausen indicate lower water contents and amounts of
extracted water over the whole sampling period. These
differences can be traced back to variability in the
climatic data (e.g. precipitation and evaporation) caused by
microclimatic distinctions at the two locations. The results
of the field and lysimeter experiments show that no complete
tracer breakthrough could be determined at a depth of 120 cm
for the sampling pits and the lysimeters as a consequence of
the short sampling time and the dry summer in 2003. As a
result of retardation the breakthrough of the test
substances MBT and ETD is not complete even for the samplers
at 40 cm depth. Therefore, bromide breakthrough at 120 cm
depth and MBT/ETD breakthrough for 40 and 120 cm depth were
just described in qualitative terms. The variability in
bromide tracer breakthrough at 40 cm depth for the different
samplers at the two locations is reflected in the
variability of the mean pore water velocity, $\nu$, and
dispersivity, $\lambda$. On the other hand, no transport
parameters could be determined for the pesticide
breakthrough at all locations. In general, larger ETD
recoveries were measured compared to the MBT for all
samplers, whereby high peak concentrations in the samplers
can be traced back to single events. The differences in the
amount of extracted water, bromide masses, and as a result
variability in transport [...]},
cin = {ICG-IV},
ddc = {333.7},
cid = {I:(DE-Juel1)VDB50},
pnm = {Chemie und Dynamik der Geo-Biosphäre},
pid = {G:(DE-Juel1)FUEK257},
typ = {PUB:(DE-HGF)11 / PUB:(DE-HGF)3},
url = {https://juser.fz-juelich.de/record/46201},
}