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@PHDTHESIS{Mennicken:53875,
author = {Mennicken, Guido},
title = {{A}nalysis of the adsorption kinetics of pyrene to soil
using laser-induced fluorescence spectroscopy ({LIF})},
volume = {4178},
issn = {0944-2952},
school = {Techn. Hochsch. Aachen},
type = {Dr. (FH)},
address = {Jülich},
publisher = {Forschungszentrum Jülich GmbH Zentralbibliothek, Verlag},
reportid = {PreJuSER-53875, Juel-4178},
series = {Berichte des Forschungszentrums Jülich},
pages = {125 p.},
year = {2005},
note = {Record converted from VDB: 12.11.2012; Aachen, Techn.
Hochsch., Diss., 2005},
abstract = {The main objective of this work was to contribute to the
development of an in-situ analytical method for polycyclic
aromatic hydrocarbons (PAH´s) in soils. Beside natural
sources like forest fires, PAH´s result from any incomplete
combustion of organic material. Man-made sources come from
heating systems, industrial power generators, diesel engines
or gaswork sites (Dabestani and Ivanov 1999). For that
reason, the US Environmental Protection Agency (EPA)
indicates 16 PAH´s as priority pollutants (see appendix 1).
The background level for PAH´s in soils of Europe and
North-America varies between 50 μg/kg and 500 μg/kg soil
(Maxin and Kögel-Knabner 1995). Because pyrene is widely
prevalent as a soil contaminant and only little information
is available about its sorption kinetics to soils (Hwang et
al. 2003), pyrene was chosen as a model compound for PAH´s
in this work. The classic way to analyse the adsorption
characteristics of compounds to soil are batch experiments.
They are easy to handle and useful for sorption equilibrium
studies. One aim of this work was to follow the adsorption
kinetics of pyrene to soil components. In this case batch
studies are not the ideal instrument. Maxin and
Kögel-Knabner (1995) reported, that the adsorption of
PAH´s to water soluble soil components is completed within
15 min and therefore it is difficult to analyse it by batch
experiments due to the time-consuming phase separation.
Additionally many authors emphasise the advantages of
procedures without a separation step for the adsorption
analysis (Belardi, Pawliszyn 1989, Ohlenbusch et al. 2000).
Aiken and Leenheer (1993) point out, that centrifugation and
filtration processes lead to a concentration of the sample
and therefore the quantity and quality of the interactions
between the components and the sample might be changed. In
this context, we intended to show the potentials and
limitations of the laser-induced fluorescence spectroscopy
(LIF) as an in-situ, real-time method for the analysis of
adsorption kinetics in soil. Until now, laser applications
in the pedosphere and in aquifer systems are scarce. Recent
investigations of petroleum products in soils have shown
that a quantitative determination of oil contaminations on
soil surfaces is possible with LIF spectroscopy (Schade and
Bublitz 1996, Löhmannsröben and Roch 1997). These
measurements were carried out on the soil surface or through
the glass wall of soil columns. In combination with
measurements in a flow-through cell at the column outlet,
the breakthrough of free pyrene can be observed (Baumann et
al. 2000).[...]},
cin = {ICG-IV},
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/53875},
}