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<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und Arbeitsstelle Radiometrie<br />
Annual Research Report<br />
2005<br />
<strong>Ruprecht</strong>-<strong>Karls</strong>-<strong>Universität</strong> Heidelberg<br />
und<br />
Heidelberger Akademie der Wissenschaften
Professor Dr. Karl Otto Münnich<br />
(1. 1. 1925 – 26. 10. 2003)<br />
It has been more than 25 years since the last Annual Report on the scientific work in our<br />
<strong>Institut</strong>e. We, thus, want to take this opportunity to commemorate Karl Otto Münnich,<br />
the founding father and first Director of the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (Environmental<br />
Physics), to whom we dedicate this report.<br />
Karl Otto Münnich was born and grew up in Heidelberg. He studied Physics at the<br />
University of Heidelberg and received his doctoral degree in 1957. During his PhD work<br />
he established the Radiocarbon Dating Laboratory in Heidelberg which later became<br />
part of the Heidelberger Akademie der Wissenschaften (Academy of Sciences). Karl<br />
Otto Münnich quickly realised the universal significance of the Radiocarbon method<br />
far beyond its application in archaeology. As one of the first topics, together with John<br />
C. Vogel, he pioneered the ground water dating method. Also during the 1950s and 60s<br />
Münnich became witness of the dramatic consequences of atmospheric nuclear weapon<br />
testing on radionuclide concentrations in the environment. He was among the first<br />
to utilise this “global tracer experiment” and study exchange processes between the<br />
important compartments of the climate system, therewith establishing the new research<br />
field of Environmental Physics. After a sabbatical in the US and a directorate at the<br />
Forschungszentrum Jülich, Karl Otto Münnich was appointed director of the newly<br />
founded <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (<strong>Institut</strong>e for Environmental Physics) in 1974. Here<br />
he demonstrated a unique combination of abstract thinking in terms of fundamental<br />
physics, experimental skills, and interdisciplinary insight. His excellent sense to extract<br />
the pivotal points of the often highly complex processes in nature permitted him to<br />
elaborate fundamental, but still simple solutions in a variety of fields. He was an<br />
excellent and adored teacher, colleague and friend to many of us. Karl Otto Münnich<br />
attracted a large number of students, and his work became well established world-wide<br />
with many of his alumni now teaching this discipline themselves.<br />
Today the various methods originally introduced by Karl Otto Münnich are applied to<br />
all major environmental subsystems, where physics plays the central role for process<br />
understanding. At the Heidelberg <strong>Institut</strong>e his pioneering ideas have been well implemented<br />
and are successfully pursued. The 2005 Scientific Report nicely illustrates how<br />
we endeavour to carry Karl Otto Münnich’s early visions into the future.
Contents<br />
1 Introduction/Overview of institute 9<br />
2 Atmosphere and Remote Sensing 11<br />
2.1 Tropospheric Research Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 15<br />
2.1.1 Halogen oxide and sulphur dioxide emission of volcanoes . . . . . . . . . . . . . 19<br />
2.1.2 Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal<br />
Boundary Layer by Active Longpath Differential Optical Absorption Spectroscopy<br />
(DOAS) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 20<br />
2.1.3 Improvement of the Detection Limit of Active-DOAS-Measurements by use of<br />
fibre coupled light source . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21<br />
2.1.4 New Operational Software for Automatic DOAS Measurement and Analysis . . 22<br />
2.1.5 Ground based MAX-DOAS measurements . . . . . . . . . . . . . . . . . . . . . 23<br />
2.1.6 Imaging DOAS. Imaging of two-dimensional trace gas distributions . . . . . . . 24<br />
2.1.7 Multi Axis Differential Optical Absorption Spectroscopy (MAX-DOAS) of Trace<br />
Gas and Aerosol Distributions . . . . . . . . . . . . . . . . . . . . . . . . . . . 25<br />
2.1.8 The flying laboratory: DOAS on board the CARIBIC aircraft project . . . . . 26<br />
2.1.9 Heidelberg ground-based network . . . . . . . . . . . . . . . . . . . . . . . . . . 27<br />
2.1.10 Applicability of light-emitting diodes as light sources<br />
for active DOAS measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . 28<br />
2.1.11 Active DOAS measurements of trace gases in the free troposphere . . . . . . . 29<br />
2.1.12 Long Term Observations of Urban Atmospheric Radical Chemistry<br />
(TURBAN) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30<br />
2.2 Stratospheric Ozone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 35<br />
2.2.1 Investigation of Inorganic Stratospheric Bromine . . . . . . . . . . . . . . . . . 38<br />
2.2.2 Stratospheric photochemistry of ozone, nitrogen and chlorine species . . . . . . 39<br />
2.2.3 Photolytic lifetime of stratospheric N2O5 . . . . . . . . . . . . . . . . . . . . . 40<br />
2.2.4 Spectroscopic measurements of halogen oxides in the marine boundary layer in<br />
Alcântara/Brazil . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 41<br />
2.2.5 Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil:<br />
Comparison of tropospheric air mass pollution in the dry and wet season . . . 42<br />
2.3 Radiative Transfer . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45<br />
2.3.1 Development and Application of a Versatile Balloon-Borne DOAS Instrument<br />
for Skylight Radiance and Atmospheric Trace Gas Profile Measurements . . . . 48<br />
2.3.2 Oxygen A-band measurements for solar photon path length distribution studies 49<br />
2.3.3 Absolutely calibrated solar irradiance measurements . . . . . . . . . . . . . . . 50<br />
2.3.4 Atmospheric detection of water dimers and their contribution to solar shortwave<br />
absorption . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 51<br />
2.4 DOAS Tomography Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 55<br />
2.4.1 Intercomparison of ambient in-situ Formaldehyde Measurements in urban Air . 58<br />
2.4.2 Trace gas distributions from long-path DOAS measurements . . . . . . . . . . 59<br />
2.4.3 Airborne measurements of the CH2O and NO2 distributions in the Po basin . 60<br />
2.4.4 Development of a Multibeam instrument for simultaneous measurements along<br />
multiple light paths . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 61<br />
2.4.5 An Indoor Test Campaign of the Tomography Long Path Differential Optical<br />
Absorption Spectroscopy (DOAS) Technique . . . . . . . . . . . . . . . . . . . 62<br />
2.4.6 2D and 3D tomographic LP-DOAS measurements of trace gas distributions in<br />
Heidelberg over an area of 4 ∗ 4 km 2 . . . . . . . . . . . . . . . . . . . . . . . . 63<br />
2.4.7 Two-dimensional measurement of motorway emission plumes . . . . . . . . . . 64<br />
5
6 CONTENTS<br />
2.4.8 Two dimensional concentration distributions of a NO2 Emission plume from a<br />
point source derived by Airborne DOAS Tomography . . . . . . . . . . . . . . 65<br />
2.4.9 Development of a computer tool for the inversion and optimization of airborne<br />
tomographic DOAS measurements (Tomolab2) . . . . . . . . . . . . . . . . . . 66<br />
2.5 Satellite Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69<br />
2.5.1 Quantifying NOx from lightning using satellite data . . . . . . . . . . . . . . . 72<br />
2.5.2 Evaluation of global tropospheric NO2 from SCIAMACHY . . . . . . . . . . . 73<br />
2.5.3 Development of a radiative transfer model . . . . . . . . . . . . . . . . . . . . . 74<br />
2.5.4 Retrieval of methane from SCIAMACHY onboard ENVISAT . . . . . . . . . . 75<br />
2.5.5 Retrieval of carbon monoxide from SCIAMACHY onboard ENVISAT . . . . . 76<br />
2.5.6 Retrieval of cloud parameters using SCIAMACHY and GOME data . . . . . . 77<br />
2.5.7 Satellite validation using the airborne multi axis DOAS instrument . . . . . . . 78<br />
2.5.8 Analysis of global long-term tropospheric and stratospheric BrO from GOME<br />
measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 79<br />
2.5.9 Enhanced SO2 Column Densities Observed Over South East Asian Region: Consequence<br />
of El Niño . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 80<br />
2.5.10 Retrieving vertical profiles of stratospheric trace gases from satellite observations 81<br />
2.5.11 Comparison of OClO nadir measurements from SCIAMACHY and GOME . . 82<br />
2.5.12 Identification of tropospheric emissions sources from satellite observations: Synergistic<br />
use of HCHO and NO2 trace gas measurements . . . . . . . . . . . . . 83<br />
2.5.13 Trace gas profile retrieval from SCIAMACHY limb measurements . . . . . . . 84<br />
2.5.14 Mie theory based characterization and modeling of atmospheric aerosols . . . . 85<br />
2.5.15 Satellite observations of the global water vapor distribution . . . . . . . . . . . 86<br />
2.5.16 Analysis of MAXDOAS observations in various observing geometries . . . . . . 87<br />
2.5.17 Comparison of Radiative Transfer Models . . . . . . . . . . . . . . . . . . . . . 88<br />
2.5.18 GOME observations of stratospheric trace gas distributions during the split<br />
vortex event in the Antarctic winter 2002 . . . . . . . . . . . . . . . . . . . . . 89<br />
2.5.19 Comparison of GOME NO2 retrievals analysed by different scientific groups . . 90<br />
2.6 MarHal - Modeling of marine and halogen chemistry . . . . . . . . . . . . . . . . . . . 95<br />
2.6.1 Modeling the possible role of iodine oxides in new particle formation . . . . . . 99<br />
2.6.2 Ozone Depletion Events in the Polar Boundary Layer in Spring: A Model Study 100<br />
2.6.3 Modeling Organic Films on Atmospheric Aerosol Particles and their Influence<br />
on Cloud Microphysics and Chemistry . . . . . . . . . . . . . . . . . . . . . . . 101<br />
2.6.4 Impact of reactive bromine chemistry in the troposphere . . . . . . . . . . . . . 102<br />
2.7 Carbon Cycle Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 105<br />
2.7.1 Global long-term observations of Radiocarbon in atmospheric CO2, revisited . 108<br />
2.7.2 Simulating Bomb Radiocarbon: Implications for the Global Carbon Cycle . . . 109<br />
2.7.3 Coupling and modernisation of the Heidelberg Greenhouse Gases and CO - GC<br />
systems for continuous measurements . . . . . . . . . . . . . . . . . . . . . . . 110<br />
2.7.4 Investigating CO2, CO and Fossil Fuel CO2 in Heidelberg . . . . . . . . . . . . 111<br />
3 Terrestrial Systems 115<br />
3.1 Soil Physics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 117<br />
3.1.1 Estimation of effective hydraulic parameters for heterogeneous porous media . 122<br />
3.1.2 X-ray attenuation techniques to study the dynamics of water in porous media . 123<br />
3.1.3 Fingered Flow Through Initially Dry Porous Hele-Shaw cell . . . . . . . . . . . 124<br />
3.1.4 Near Infrared Imaging Spectroscopy of Water States in Porous Silicate Media . 125<br />
3.1.5 Evaporation Experiment to determine Soil Hydraulic Properties . . . . . . . . 126<br />
3.1.6 Free Parameterisation of Soil Hydraulic Properties . . . . . . . . . . . . . . . . 127<br />
3.1.7 Modelling water flow and solute transport in heterogeneous soil . . . . . . . . . 128<br />
3.1.8 Unsaturated Flow in Strongly Heterogeneous Porous Media . . . . . . . . . . . 129<br />
3.1.9 Assessing temporal changes in volumetric soil water content from ground-penetrating<br />
radar profiles . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 130<br />
3.1.10 Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />
Domain Reflectometry . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 131<br />
3.1.11 Efficient reconstruction of dispersive dielectric profiles using TDR . . . . . . . 132<br />
3.1.12 3D Full-wave, electromagnetic model of ground penetrating radar systems . . . 133<br />
3.1.13 Simulation and Observation of an Evanescent Wave in Ground Penetrating<br />
Radar Applications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 134<br />
3.2 Ice and Climate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137
CONTENTS 7<br />
3.2.1 Glaciological pilot studies on a cold miniature ice cap . . . . . . . . . . . . . . 140<br />
3.2.2 Constraining the anthropogenic fraction of carbonaceous aerosol by 14 C-analysis 141<br />
3.2.3 Recent variability of the cosmogenic nuclides 10 Be and 7 Be in coastal Antarctica 142<br />
3.2.4 Climatic significance of stable water isotope records from Alpine ice cores. . . 143<br />
3.2.5 Analyses of dissolved organic carbon (DOC) at low levels in Alpine and polar<br />
glaciers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 144<br />
3.2.6 Novel tools in ice core research . . . . . . . . . . . . . . . . . . . . . . . . . . . 145<br />
4 Aquatic Systems 149<br />
4.1 Groundwater and Paleoclimate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 151<br />
4.1.1 A tracer study of paleoclimate and groundwater recharge in the North China<br />
Plain . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 154<br />
4.1.2 A multi-tracer study of groundwater in reclamation areas south-west of the Nile<br />
Delta, Egypt . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 155<br />
4.1.3 A multi tracer study to investigate the groundwater in the Odenwald region . . 156<br />
4.1.4 A new mass spectrometric system for measurement of noble gases and first<br />
applications to perform measurements of fluid inclusions in speleothems . . . . 157<br />
4.1.5 Advancing the use of noble gases as palaeoclimate indicators . . . . . . . . . . 158<br />
4.1.6 Radon as tracer for lake - groundwater interaction . . . . . . . . . . . . . . . . 159<br />
4.2 Lake Research (Limnophysics) . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 161<br />
4.2.1 Sulfurhexaflourid (SF6) as tracer for transport and mixing processes in mining<br />
lakes . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 163<br />
4.2.2 Vertical transport in stratified lakes . . . . . . . . . . . . . . . . . . . . . . . . 164<br />
4.2.3 Investigation of Water Currents in Lake Willersinnweiher using Acoustic Doppler<br />
Current Profiler . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 165<br />
5 Small-Scale Air-Sea Interaction 167<br />
5.1 Small-Scale Air-Sea Interaction . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 169<br />
5.1.1 Investigation of transport processes across the sea-surface microlayer by active<br />
thermography . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 174<br />
5.1.2 Water flow measurements in environmental and biological systems . . . . . . . 175<br />
5.1.3 Time resolved Measurements of Air Water Gas Exchange . . . . . . . . . . . . 176<br />
5.1.4 3-D flow measurements within a porous gravel layer . . . . . . . . . . . . . . . 177<br />
5.1.5 3D fluid flow measurement close to surfaces . . . . . . . . . . . . . . . . . . . . 178<br />
5.1.6 Imaging concentration profiles of water boundary layer by Double-Dye LIF . . 179<br />
5.1.7 Combined slope/height measurements of short wind waves : ISHG . . . . . . . 180<br />
5.1.8 Development of a depth resolving boundary layer visualization for gas exchange<br />
at free water surfaces . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 181<br />
6 Forschungsstelle “Radiometrie” of the Heidelberger Akademie der Wissenschaften185<br />
6.1 Radiometric Dating of Water and Sediments . . . . . . . . . . . . . . . . . . . . . . . . 187<br />
6.1.1 Reconstruction of the geomagnetic field strength over the past 300,000 years<br />
derived from 10 Be data of deep sea sediments from the North and South Atlantic<br />
Ocean . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 191<br />
6.1.2 Possible solar origin of the glacial 1,470-year climate cycle demonstrated in a<br />
coupled climate model . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 192<br />
6.1.3 Solar variability and rapid climate change on decadal to centennial scales . . . 193<br />
6.1.4 Establishment of a method for measuring 231 Pa in deep-sea sediments via ICP-MS194<br />
6.1.5 Modelling of stable isotope records of stalagmites . . . . . . . . . . . . . . . . . 195<br />
6.1.6 Reconstruction of the 10 Be-production based on deep sea sediments from the<br />
North Atlantic . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 196<br />
6.1.7 U/Th dating of deep-water corals from the North Atlantic . . . . . . . . . . . . 197<br />
6.1.8 Isochron dating of fossil reef corals and the reconstruction of past sea level<br />
fluctuations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 198<br />
6.1.9 Dating and interpretation of the carbon and oxygen isotopes of two Holocene<br />
stalagmites from the South of Chile (Patagonia) . . . . . . . . . . . . . . . . . 199<br />
6.1.10 Chronostratigraphy of the Nasca culture and palaeoclimate reconstruction of<br />
the Palpa region (Peru) by AMS- 14 C dating . . . . . . . . . . . . . . . . . . . . 200<br />
6.1.11 Nonlinear time-series analysis of nonstationary signals . . . . . . . . . . . . . . 201<br />
6.1.12 The authigenic 10 Be/ 9 Be ratio in deep sea sediments as a proxy for the Earth‘s<br />
magnetic field intensity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 202
8 CONTENTS<br />
Bibliography 207<br />
Peer Reviewed Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 209<br />
Grey Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 215<br />
PhD Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217<br />
Diploma Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 219<br />
Invited Talks . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 221
Introduction<br />
In Heidelberg, environmental physics continuously developed since the 1950s from the application of<br />
nuclear physics methods to environmental research, mainly driven by Otto Haxel. In 1975, this led to<br />
the foundation of the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> (<strong>Institut</strong>e of Environmental Physics), the first of its<br />
kind in Germany, in the Fakultät <strong>für</strong> Physik und Astronomie with Karl-Otto Münnich as its founding<br />
director.<br />
From the start, the IUP focused on the underlying physics of a wide spectrum of environmental processes<br />
and less on specific applications in atmospheric sciences, soil sciences, hydrology, or oceanography.<br />
This turned out to be a major strength and it continues to distinguish the IUP from other large<br />
environmental research institutes. With this focus, the IUP attains great flexibility in its methods<br />
and is able to provide an environment where classical divisions between systems and disciplines can<br />
be overcome. For instance, we investigate boundary layers between compartments which determine<br />
the soil-atmosphere and ocean-atmosphere interactions. This direction of research is also adopted<br />
by large international programs, like the International Geosphere Biosphere Project (IGBP), which<br />
in recent times focus increasingly on investigation of interaction between compartments of the Earth<br />
system. With its firm rooting in physics, the IUP sees itself in an excellent position to recognize and<br />
investigate system properties of our environment and the interplay of its subsystems (atmosphere,<br />
cryosphere, soil, groundwater, oceans,. . . ).<br />
The IUP is a strongly experiment-oriented institution. Our current major fields of research are:<br />
• physical foundations of climate research (budgets of greenhouse gases, oxidation capacity of the<br />
atmosphere, radiation in the atmosphere),<br />
• consequences of global change on central cycles in the earth system (water, carbon), and<br />
• reconstruction of paleoclimate from a variety of environmental archives.<br />
Our spectrum of methods still contains those developed from nuclear physics inheritance, specifically<br />
the analysis of 14 C and various stable isotopes including noble gases. In addition, we employ an<br />
array of new techniques like spectroscopy (of the atmosphere) and imaging spectroscopy, remote<br />
sensing from ground-, air-, and space-borne platforms, time series analysis, as well as experiment- and<br />
process-oriented modeling and simulation.<br />
This report gives a snapshot of the research performed at the IUP by diploma students, doctoral<br />
students, and senior scientist. It is intended as a comprehensive but concise overview for the members<br />
of the institute as well as for the scientific community.<br />
9
Atmosphere and Remote Sensing<br />
2.1 Tropospheric Research Group . . . . . . . . . . . . . . . . . . . . . . . . . 15<br />
2.2 Stratospheric Ozone . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 35<br />
2.3 Radiative Transfer . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 45<br />
2.4 DOAS Tomography Group . . . . . . . . . . . . . . . . . . . . . . . . . . . 55<br />
2.5 Satellite Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69<br />
2.6 MarHal - Modeling of marine and halogen chemistry . . . . . . . . . . . 95<br />
2.7 Carbon Cycle Group . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 105<br />
11
Overview<br />
Summary<br />
Atmospheric research at the IUP concentrates on the processes governing the oxidation capacity<br />
of the atmosphere, its physical and chemical properties and its role in the global climate system.<br />
Central topics are release processes and the influence of reactive halogen species as well as other free<br />
radical cycles in the stratosphere and troposphere, fundamental research related to scattering and<br />
absorption of short-wave radiation transport in the atmosphere, and on the abundance and role of<br />
trace and greenhouse gases in atmospheric chemistry and in the climate system. Tools of our research<br />
are observing systems on global, continental and regional scales relying on sophisticated ground and<br />
aircraft-based in-situ and sampling techniques as well as air-borne and space-borne remote sensing.<br />
Observations are integrated in modeling studies of marine and stratospheric photochemistry with a<br />
particular focus put on the chemistry of halogens, atmospheric radiation transport, and on global,<br />
regional and trajectory models of source and sink processes of greenhouse gases.<br />
Central topics include:<br />
• Atmospheric composition and links to human health<br />
• Radiation transfer processes and links to climate<br />
• Tropospheric halogen species and their role in the oxidation capacity of the atmosphere<br />
• Stratospheric ozone as influenced by halogen and nitrogen species<br />
• Sources and sink processes as well as isotopic abundances of greenhouse gases<br />
• Global observing systems<br />
For a detailed description of the different topics see individual group reports.<br />
Atmospheric composition and links to human health<br />
Studies of radical processes in tropospheric chemistry were performed, free radicals determine the<br />
oxidation capacity of the troposphere, i.e. the capacity of the atmosphere to clean itself from natural<br />
and anthropogenic pollutants. Scientific objectives include studies of the processes governing the<br />
oxidation capacity of the troposphere. In particular the release and activation processes of reactive<br />
halogen species in the troposphere. Studies in this year centered on the following questions:<br />
• The abundance of reactive halogen species (BrO, IO, I2) in the marine boundary layer in coastal<br />
regions.<br />
• The abundance of reactive halogen species (BrO, IO) and related compounds over the open<br />
ocean.<br />
• The abundance of reactive halogen species, in particular BrO, and related species like NO2, NO3<br />
and CH2O in the free troposphere<br />
• The rate of volcanic emissions of reactive halogen species, e.g. BrO, ClO, OClO.<br />
• Chemical evolution of reactive halogen species in volcanic plumes, in particular what are the<br />
processes after O2 and O3 mixes into the originally reducing plume.<br />
For a detailed description of the different topics see individual group reports.<br />
Future Work<br />
Future work will encompass<br />
1. Establishment of a large network of ground based remote sensing instruments to quantify volcanic<br />
emissions, which will provide the first comprehensive study of volcanic sulfur and halogen<br />
emissions (EU-project NOVAC).<br />
2. Study of the marine halogen chemistry with particular emphasis on iodine-particle formation<br />
(EU-project MAP), nonlinear chemistry, and emission ”hot spots”.<br />
13
14 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
3. Spectroscopic studies of atmospheric particles will be performed within a large long-term intercomparison<br />
exercise (EU-project ICARTT).<br />
4. Study of the inter-annual variation of the solar radiation field including 2-D imaging spectroscopy<br />
of the radiative properties of the atmosphere with a particular focus on the radiative properties<br />
during the life cycle of individual clouds (DFG Forschergruppe ’life cycles of clouds’)<br />
5. Using novel ballon-based instrumentation (Mini-DOAS), the time-dependence of ozone destroying<br />
radicals (BrO, and OClO) and inferred reactive chlorine will be investigated from which<br />
conclusions on the most important loss reactions for stratospheric ozone in polar winter can be<br />
drawn.<br />
6. Investigation of the transport and photochemical processes at the major entrance of tropospheric<br />
air into the stratosphere, i.e. the tropical upper troposphere layer/lowermost stratosphere<br />
(TTL/LMS) Conclusions will be drawn on the ozone depletion potential of major manmade<br />
and naturally emitted ozone destroying chemicals passing the TTL/LMS (EU-project<br />
SCOUT-O3).<br />
7. Study of the European carbon balance and in particular the fossil fuel CO2 contribution (EUproject<br />
CarboEurope-IP)<br />
8. Within the carbon system, investigation of independent constraints on global carbon exchange<br />
as derived from long-term high precision 14 CO2 observations in combination with model studies<br />
(DFG project, Atmospheric 14 C).<br />
9. Investigation of the continental European hydrogen budget (in particular the anthropogenic<br />
source and the soil sink) using continuous and aircraft observations over Europe and Siberia<br />
(EUROHYDROS and TCOS II, submitted EU proposals)<br />
Instrument development will be continued, a particular topic being preparation for the new German<br />
research aircraft HALO. In this context we are developing novel instruments based on imaging and<br />
near-IR spectroscopy.<br />
Literature<br />
A total of 16 peer reviewed manuscripts where accepted by or appeared in scientific journals. Members<br />
of the institute were invited to give 19 presentations on topics related to atmospheric research at<br />
scientific conferences<br />
Diploma and Doctoral Theses<br />
A total of 4 Diploma theses and 2 Doctoral theses on topics related to atmospheric research were<br />
completed in the reporting period.
2.1. TROPOSPHERIC RESEARCH GROUP 15<br />
2.1 Tropospheric Research Group<br />
Group members<br />
Prof Dr. U. Platt, Chief of Staff<br />
Dipl. Phys. N. Bobrowski, PhD Student<br />
Dipl. Phys. B. Dix, PhD Student<br />
M. Gillmann, Staff<br />
MSc. O. Ibrahim, PhD Student<br />
Dipl. Phys. C. Kern, PhD Student<br />
I. Louban, Diploma Student<br />
Dipl. Phys. A. Merten, PhD Student<br />
Dr. C. Peters, Post Doc<br />
K. Seitz, Diploma Student<br />
Dipl Phys. R. Sinreich, PhD Student<br />
T. Stein, Diploma Student<br />
Dr. S. Trick, Staff<br />
Dr. J. Zingler, Post Doc<br />
Abstract<br />
Tropospheric research in the IUP concentrates on the processes governing the oxidation capacity of the<br />
atmosphere. Of particular interest are release processes of reactive halogen species from a multitude of<br />
sources (marine biology, sea spray, volcanoes, etc.) into the troposphere. Consequences for the state<br />
of the troposphere are studied together with the other atmospheric subgroups and within national<br />
and international collaborations.<br />
Scientific Objectives<br />
include studies of the processes governing the oxidation capacity of the troposphere. In particular the<br />
release and activation processes of reactive halogen species in the troposphere. the questions studied<br />
in this year centered on the following questions:<br />
• The abundance of reactive halogen species (BrO, IO, I2) in the marine boundary layer in coastal<br />
regions.<br />
• The abundance of reactive halogen species (BrO, IO) and related compounds over the open<br />
ocean.<br />
• The abundance of reactive halogen species, in particular BrO, and related species like NO2, NO3<br />
and CH2O in the free troposphere.<br />
• The rate of volcanic emissions of reactive halogen species, e.g. BrO, ClO, OClO.<br />
• Chemical evolution of reactive halogen species in volcanic plumes, in particular what are the<br />
processes after O2 and O3 mixes into the originally reducing plume.<br />
Overarching topic<br />
Studies of radical processes in tropospheric chemistry, the oxidation capacity of the troposphere, i.e.<br />
the camacity of the atmosphere to clean itself from natural and anthropogenic pollutants.<br />
Background<br />
Free radicals play a pivotal role in atmospheric chemistry. Despite their exceedingly small concentration<br />
(mixing ratios around 10-12), these species are the driving force for most chemical processes<br />
in the atmosphere. While the role of hydrogen radicals (OH, HO2) is relatively well studied and<br />
largely understood, other free radicals like halogen atoms or halogen oxides (e.g. IO, BrO, ClO) have<br />
been neglected until recently. In particular, at the levels suggested by the available measurements<br />
tropospheric halogen species can have profound effects on many aspects of tropospheric chemistry,<br />
these include: (1) Reactive halogen species, and in particular reactive bromine and iodine can readily<br />
destroy tropospheric ozone, which can have a multitude of consequences, both chemical and climatic<br />
(e.g. [Roscoe et al. , 2001], [Platt & Hönninger, 2003]). Catalytic ozone destruction essentially occurs<br />
by two distinct reaction cycles. Either (I) involving self reaction of halogen oxide radicals with other<br />
halogen oxide radicals (XO+XO or XO+YO) or (II) reaction of halogen oxides with hydrogen radicals
16 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
XO+HO2): leading to the net result:<br />
O3 + O3 → 3O2<br />
Cycle (I) has been identified as the prime cause for polar boundary layer ozone destruction [Barrie<br />
& Platt, 1997]. Since the rate of ozone destruction is usually proportional to the square of the halogen<br />
oxide concentration, cycle (I) ineffective at low XO levels usually found in mid-latitude coastal<br />
areas. At low RHS levels, however O3 destruction takes place by reaction cycle II, here the rate of<br />
O3 destruction is linearly dependent on the XO concentration. (2) An important side effect of cycle<br />
(II) the conversion of HO2 to OH and thus a reduction of the HO2/OH ratio, in particular at low<br />
NOX levels. At a given photochemical situation (O3, H2O levels, insolation) the presence of BrO or<br />
IO will therefore increase the OH concentration. It is interesting to note that both effects have been<br />
observed in the upper troposphere (e.g. [Wennberg et al. , 1998]). (3) The reaction of XO with NO,<br />
leads to conversion of NO to NO2 and thus to an increase of the Leighton ratio (L=[NO2]/[NO]). An<br />
increase in L is thus usually regarded as an indicator for photochemical ozone production (due to the<br />
presence of RO2 (R = organic radical)) in the troposphere. However, as already noted by [Platt &<br />
Janssen, 1996] an increase in L due to halogen oxides will not lead to O3 production. (4) A more<br />
subtle consequence of reactive halogen species for the ozone levels in the free troposphere is due to<br />
the combination of the above effects (2) and (3) as pointed out by [Stutz et al. , 1999]: Photochemical<br />
ozone production in the troposphere is limited by the reaction<br />
(2.1)<br />
NO + HO2 → NO2 + OH (2.2)<br />
However, the presence of reactive bromine will reduce the concentrations of both educts of the above<br />
reaction and thus reduce the NOX - catalysed ozone production. (5) Heterogeneous reactions of<br />
bromine species (i.e. HOBr) with (sea salt) chloride can lead to the release of Cl-atoms. This process<br />
constitutes a Br catalysed chlorine activation. Since Cl-atoms are highly reactive, this process directly<br />
enhances the oxidation capacity of the troposphere, see e.g. [Platt et al. , 2004]. (6) Gas-phase iodine<br />
species (like IO, OIO or HOI) may facilitate transport of I from the coast to inland areas and thus<br />
contribute to our iodine supply [Cauer, 2004], [Cox et al. , 1999]. (7) Deposition of mercury was found<br />
to be enhanced by the presence of reactive bromine species in particular in polar regions (e.g. [Barrie<br />
& Platt, 1997]), this process appears to be linked to the oxidation of Hg0 to Hg(II), likely by reaction<br />
with BrO [Lindberg et al. , 2002]. (8) The reaction of BrO with dimethyl sulfide (DMS) might be<br />
important in the unpolluted remote marine boundary layer where the only other sink for DMS is<br />
the reaction with OH radicals (e.g. [von Glasow et al. , 2004], [von Glasow & Crutzen, 2004]). (9)<br />
Iodine species have been shown to be involved in particle formation in the marine BL ([Leck & Bigg,<br />
1999], [Hoffmann et al. , 2001], [O’Dowd et al. , 2002], [Burkholder et al. , 2004]). (10) Evidence is<br />
accumulating (see e.g. [Platt & Hönninger, 2003]) that there is a wide-spread ”background” level of<br />
BrO radicals in the free troposphere, due to the processes described under (1)-(5) and (8) above there<br />
might be an important effect of reactive halogens on the global tropospheric chemistry as summarised<br />
by [von Glasow et al. , 2004].<br />
Main methods<br />
include the experimental determination of the halogen oxide distribution and the distribution of related<br />
species in several compartments of the troposphere: 1) The marine boundary layer in coastal regions<br />
(French Brittany). 2) The open ocean. 3) The free troposphere 4) Volcanic emissions (contents of<br />
reactive halogen species, e.g. BrO, ClO, OClO in volcanic plumes) The measurements are made by<br />
Differential Optical Absorption Spectroscopy (DOAS), which allows the detection of many atmospheric<br />
trace gases at a sensitivity in the ppt - range (i.e. at mixing ratios down to 10-12ppt). For studies<br />
in the different compartments a series of variants of the technique were applied: 1) Studies in the<br />
marine boundary layer were performed by active DOAS (i.e. using artificial light sources), which<br />
allows also nighttime studies, as well as by passive ”Multi-Axis” DOAS (MAX-DOAS). 2) Shipborne<br />
measurements in the open ocean relied on MAX-DOAS observations requiring relatively little<br />
logistic prerequisites and allowed unattended operation. 3) Aircraft-based measurements in the free<br />
troposphere are also based on passive MAX-DOAS observations, while ground based observations<br />
(at the Zugspitze) employ active DOAS measurements. 4) Observation at volcanoes were made by<br />
passive MAX-DOAS and by the novel Imaging-DOAS technique recently developed in our group. In<br />
addition to the field campaigns a number of projects is aimed at technological improvements of the<br />
DOAS technology. Activities included studies on the reduction of the optical noise [Platt, 1994] by the<br />
use of optical fibers and mode mixers to connect light source and transmitting telescope, the use of
2.1. TROPOSPHERIC RESEARCH GROUP 17<br />
Light Emitting Diodes as DOAS light sources, and development of novel techniques for the inversion<br />
of MAX-DOAS measurements to derive the aerosol optical density as well as the vertical distribution<br />
of trace gases in the lower atmosphere.<br />
Main activities<br />
A large number of field campaigns were conducted:<br />
• Expeditions to the volcanoes Etna (Italy) and ... to study emission of halogen oxide radicals<br />
and SO2.<br />
• Studies of nitrate radicals and related species at the Schneeferner Haus (Zugspitze, Germany)<br />
• Ship expedition (on RV Polarstern) during ... to study the NO2, O3, and BrO from 52 o S to<br />
72 o N.<br />
• Studies of the oxidation capacity of the lower atmosphere in New England (USA ) within the<br />
framework of the ICARTT project.<br />
• Participation in the CARIBIC - Project.<br />
• Also world wide long-term measurements of halogen oxides and related species were performed<br />
by the ”Heidelberg Ground-Based Network”.<br />
Funding<br />
DORSIVA (EU)<br />
IALSI (EU)<br />
AFO-2000: ReHaTrop (BMBF)<br />
CARIBIC<br />
Two Ph.D. students are funded through the International Max-Planck Research School in ”Experimental<br />
Atmospheric Chemistry”<br />
Cooperation within the institute and with groups outside of the institute<br />
Obviously there is close cooperation within the atmospheric groups.<br />
National and international cooperation exists with the following groups:<br />
Chalmers University, Gothenburg, Sweden (Galle)<br />
Volcanic observatory Etna, Italy<br />
Max-Planck Institue for Chemistry, Mainz<br />
University of Mainz (Heumann)<br />
University of Bayreuth<br />
<strong>Institut</strong>e for Physical Chemistry, University of Wuppertal (Barnes)<br />
Alfred Wegener <strong>Institut</strong>e for Polar Research, Bremerhafen<br />
NOAA, Boulder<br />
University of Cambridge (Oppenheimer)<br />
Future Work<br />
will encompass the establishment of a large network of volcanic stations to provide the first comprehensive<br />
and quantitative study of volcanic sulfur and halogen emissions (EU-project NOVAC). Also<br />
marine halogen chemistry will be studied, particular emphasis will be of iodine-particle formation (EUproject<br />
MAP), nonlinear chemistry, and emission ”hot spots”. Spectroscopic studies of atmospheric<br />
particles will be performed within a large long-term intercomparison exercise (EU-projcet ICARTT).<br />
Instrument development will be continued, a particular topic being preparation for the new German<br />
research aircraft HALO.<br />
Peer Reviewed Publications<br />
1. Sinreich et al. [2005]<br />
2. von Friedeburg et al. [2005]<br />
3. Pundt et al. [2005]
18 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
4. Zingler & Platt [2005]<br />
5. Volkamer et al. [2005]<br />
6. Bobrowski et al. [2005]<br />
7. Tas et al. [2005]<br />
8. Wenig et al. [2005]<br />
9. Hak et al. [2005]<br />
10. Peters et al. [2005]<br />
11. Kern et al. [2005]<br />
12. Lee et al. [2005]<br />
13. Wagner et al. [2004]<br />
14. Platt et al. [2004]<br />
15. von Glasow et al. [2004]<br />
Other Publications<br />
1. Platt et al. [2005]<br />
2. Volkamer et al. [2004]<br />
Diploma Theses<br />
1. Kern [2004]<br />
2. Louban [2005]<br />
3. Seitz [2005]<br />
PhD Theses<br />
1. Bobrowski [2005]<br />
2. Peters [2005]
2.1. TROPOSPHERIC RESEARCH GROUP 19<br />
2.1.1 Halogen oxide and sulphur dioxide emission of volcanoes<br />
Participating scientist Nicole Bobrowski<br />
Abstract A novel instrument, the ’Mini-MAX-DOAS’ was applied to study reactive halogen and<br />
sulphur emissions of several volcanoes. The study was focussed on the determination of SO2 and BrO<br />
concentrations, but also ClO and OClO could be detected for the first time in a volcanic plume. The<br />
chemistry of volcanic plumes can give insights into volcanic processes, which could help to improve the<br />
forecast of volcanic eruptions and is also of atmospheric relevance as the volcanic source of aerosols<br />
and trace gases can have significant climatic impact.<br />
Figure 2.1: The BrO/SO2 ratios for the different distances from the summit (left panel). Sketch of<br />
processes in a volcanic plume: after emission the plume mixes with ambient air, thus ozone becomes<br />
available and radical chemistry starts (right panel).<br />
Background The chemistry of volcanic plumes<br />
can give insights into volcanic processes, which<br />
could help improving the forecast of volcanic eruptions<br />
and is also of atmospheric relevance as the<br />
volcanic source of aerosols and trace gases can<br />
have a significant climatic impact. Although both<br />
are very important aspects until now the chemical<br />
processes are hardly understood and unfortunately<br />
still rarely studied.<br />
Funding IMPRS Fellowship and DORSIVA<br />
(Development of Optical Remote Sensing for Volcanic<br />
Applications- EU-project)<br />
Methods and results Spectroscopic measurements<br />
were carried out with the new Mini-MAX-<br />
DOAS instrument combined with a Pocket PC.<br />
The main results obtained in this work are: BrO<br />
is formed downwind, although it is not yet clear<br />
by what chemical processes. Nevertheless a suggested<br />
chemistry is given in Figure 1, right panel.<br />
Experimental studies at two volcanic sites, Mt.<br />
Etna and Mt. Villarica, were carried out and<br />
showed similar results. At Mt. Etna, measurements<br />
took place from the summit up to a distance<br />
of 19 km in downwind direction (see Figure 2.1,<br />
left panel). ClO and OClO were detected for the<br />
first time as further active halogen compounds in<br />
volcanic plumes. ClO was already detected next<br />
to the source (in contrast to BrO), and shows no<br />
significant increase in the ClO/SO2 ratio in the<br />
aging plume. The ClO/SO2 ratio even seems to<br />
decrease by measuring further downwind.<br />
The BrO/SO2 variations were studied during and<br />
after the Mt. Etna eruption 2004. They were<br />
compared with filter pack measurements and SO2<br />
flux variations. This measurements show differences<br />
of the feeding systems of Mt. Etna (North<br />
East Crater and Voragine). The North East<br />
Crater showed larger BrO/SO2 ratios than Voragine.<br />
Outlook/Future work The Mini-MAX-<br />
DOAS system will be set-up at many volcanic<br />
sites in the frame of a new started EU-project -<br />
NOVAC. The extension of the data set will open<br />
the possibility of a better estimation of the volcanic<br />
reactive bromine source and also allows the<br />
investigation of changes in the BrO/SO2 ratio<br />
with volcanic activity.<br />
Main publications [Bobrowski, 2005],<br />
[Bobrowski & Filsinger, 2005],<br />
[Bobrowski et al. , 2005]
20 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.2 Studies of Reactive Halogen Species (RHS) in the Marine and mid-<br />
Latitudinal Boundary Layer by Active Longpath Differential Optical<br />
Absorption Spectroscopy (DOAS)<br />
Participating scientist Christina Peters<br />
Abstract Appearance and distribution of a variety of reactive halogen species like BrO, IO, OIO<br />
and I2 in coastal areas was investigated within the framework of this PhD thesis.<br />
Figure 2.2: I2 time series recorded during the Mace Head campaign in 1998. The dotted line indicates<br />
the mean detection limit of 20 ppt. The shaded areas indicate I2 clearly identified above the detection<br />
limit (with respect to the individual error<br />
Background The importance of reactive halogen<br />
species (RHS) in the troposphere is on the one<br />
hand due to their strong effect on tropospheric<br />
ozone levels, which was discovered during ozone<br />
depletion events in the polar boundary layer during<br />
polar sunrise. On the other hand recent field<br />
and laboratory studies are indicating a great relevance<br />
of reactive iodine in new particle formation<br />
processes. Since particles in the marine atmosphere<br />
affect the microphysical properties of<br />
clouds, they have a potential impact on climate.<br />
Funding PhD Thesis in the framework of the<br />
AFO2000 program, funded by the BMBF.<br />
Methods and results Within the framework<br />
of this thesis three field campaigns using active<br />
longpath DOAS technique for studies of the<br />
reactive halogen species BrO, IO, OIO and I2<br />
were conducted in different mid-latitudinal regions.<br />
Ground based measurements in the lower<br />
Arctic at the Hudson Bay yielded high levels<br />
of the BrO radical up to 35 ppt in the boundary<br />
layer, coinciding with nearly complete surface<br />
near ozone depletion. Two field campaigns investigated<br />
the appearance of RHS in the coastal<br />
environments of the German North Sea and the<br />
French Atlantic Coast, IO was the only halogen<br />
oxide found in both locations with concentrations<br />
reaching 7.7±0.5 ppt. BrO in the marine boundary<br />
layer was estimated to remain below 1.5 ppt,<br />
neither OIO nor I2 could be unequivocally identified<br />
in the spectra. Within a re-analysis of spectra<br />
taken during an earlier campaign in 1998 in Mace<br />
Head, Ireland up to 61±12 ppt I2 were detected at<br />
night during extraordinary low water levels. Most<br />
likely the I2 was emitted by laminaria algae inhabiting<br />
parts of the lower intertidal zone.<br />
Outlook/Future work Further studies will be<br />
performed within the EU project ”Marine Aerosol<br />
Production” (MAP).<br />
Main publications [Peters et al. , 2005],<br />
[Peters, 2005]
2.1. TROPOSPHERIC RESEARCH GROUP 21<br />
2.1.3 Improvement of the Detection Limit of Active-DOAS-Measurements<br />
by use of fibre coupled light source<br />
Participating scientist André Merten<br />
Abstract Xenon-high-pressure lamps are commonly used in DOAS measurements. Unfortunately<br />
these lamps show strong spectral variability, which determines the minimum detectable optical density.<br />
A combination of a technical solution and a mathematical treatment to reduce the residual structures<br />
and therefore the detection limit was developed.<br />
Figure 2.3: Fibre light source prevents residual structures caused by a Xenon lamp.<br />
Background In active DOAS meausurements<br />
the minimum detectable optical density and thus<br />
the detection limit for trace gases are primarily<br />
determined by the spectral stability of the Xenonlight<br />
source. This is particularly important in<br />
spectral ranges where Xe-lines exist. Due to the<br />
large temperature gradient (several 1000 K/mm)<br />
and turbulent flow inside the arc these spectral<br />
structures strongly vary with time and across the<br />
arc of the Xe–high pressure lamp. When using<br />
a ’shortcut optics’, to remove this Xe-lines by<br />
a lamp reference, it is not guaranteed that the<br />
same area of the arc is imaged as is used in the<br />
measurement, causing strong residual structures<br />
which can be misinterpreted as optical densities.<br />
Imaging the lamp in a fibre and ’mode-mixing’ the<br />
light improves the situation, since all light leaving<br />
the fibre has the same spectral composition.<br />
Funding IALSI<br />
Methods and results After preliminary tests,<br />
a fibre coupled Xe-lamp was installed at the White<br />
cell (multireflection cell) at the EUPHORE smog<br />
chamberb (CEAM Valencia / Spain). Tests before<br />
and after the installation of this arrangement<br />
show a clear reduction of the residual structures<br />
and of the error in the concentration of detected<br />
trace gases. For a long path telescope it<br />
is even more complicated to run a short cut system<br />
that images the lamp arc in the same way<br />
as in the measurement mode, if the lamp is im-<br />
aged directly into the telescope. The Xenon-lamp<br />
was replaced by a Xenon-fibre light source, which<br />
was mounted at the optical axis of the telescope,<br />
instead of a Newton-like telescope set-up, which<br />
makes the complicate alignment of the telescope<br />
easier. Figure 2.3 shows the results of a DOAS<br />
evaluation of NO2 and H2O from the old (left)<br />
and the new (right) set-up. In the left graph<br />
strong residual structures dominate the fit-result.<br />
In the right graphs (new set-up with fibre source),<br />
only very small residual structures are visible and<br />
the detection of weak water absorption is possible.<br />
Due to the easier alignment, effectively no<br />
loss of light occurred. Xenon lamps show also a<br />
spectral drift with time. If it is not possible to<br />
take lamp spectra at short time periods, residual<br />
structures arise. Fortunately the spectrum of<br />
the lamp does not change randomly, which can be<br />
determined by correlation analysis of lamp spectra.<br />
A linear model can describe the variation of<br />
the lamp spectrum. This was combined with the<br />
DOAS-analysis. A change in the lamp spectrum is<br />
now treated like an absorber and can removed by<br />
the fitting procedure. The necessary mathematical<br />
functions were integrated in a new evaluation<br />
software, developed to perform an efficient DOAS<br />
analysis.<br />
Outlook/Future work Using fibre optics offers<br />
the possibility to work with other light sources<br />
such as LED and to design a new type of long path<br />
telescopes.
22 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.4 New Operational Software for Automatic DOAS Measurement and<br />
Analysis<br />
Participating scientist André Merten<br />
Abstract The opportunity offered by the DOAS method to do an automatic measurement and<br />
analysis of atmospheric trace gases has not been used because of the leak of adequate software. The<br />
requirements of modern measurement software were studied and a new, easier to handle DOASsoftware<br />
was developed, which can be used to monitor trace gases.<br />
Figure 2.4: Screen shots of the program ’LabDOAS Measurement’.<br />
Background The DOAS method is only practicable<br />
by use of computers. Therefore, the software<br />
is of great importance for the quality of measurement<br />
and data evaluation – especially for a fully<br />
automatic measurement and analysis mode e.g.<br />
for monitoring air quality. The DOAS method<br />
should be an analytical tool in atmospheric science,<br />
and instead the major content of the work.<br />
To meet this requirements, a new software tool<br />
was designed.<br />
Funding IALSI<br />
Methods and results The requirements for a<br />
modern DOAS software were determined:<br />
• Reliable communication with instrument<br />
controllers<br />
• Complete control by graphical user interface<br />
(GUI)<br />
• Status of the devices and the measurement<br />
is reported by graphs<br />
• Recording of all important information together<br />
with the spectra (digital log-book)<br />
• Parallel execution of measurement and data<br />
analysis<br />
• Automatic documentation of measurement<br />
and analysis (as text and graphics)<br />
According to these requirements a software package<br />
consisting of three programs based on Lab-<br />
VIEW was developed: The program ’LabDOAS<br />
MEASUREMENT’ controls an active DOAS device.<br />
It can run in an automatic measurement<br />
and evaluation mode, completely controlled by<br />
GUI and remote acces. Status of measurement<br />
and analysis are exported automatically as graphics.<br />
The easy handling supports the operator especially<br />
in case of adjusting the DOAS device.<br />
’LabDOAS ANALYSIS’ is designed for more intensive<br />
data evaluation. A single spectrum as<br />
well a whole time series of spectra can be analysed<br />
with mathematical functions like digital filters<br />
and Fourier transformation, including methods<br />
to analyse residual structures of lamp spectra<br />
like correlation analysis. ’LabDOAS CALIBRA-<br />
TION’ offers automatic wavelength calibration of<br />
the spectrograph with spectra of atomic emmissions.<br />
It contains a comprehensive database of<br />
atomic spectral lines. This calibration is used to<br />
prepare the reference cross sections for the DOAS<br />
evaluation.<br />
Outlook/Future work This software package<br />
was tested successfully at a long path telescope<br />
and has shown its advantages also in the examination<br />
of lamp noise and exploration of absorption<br />
cross sections. Additional functions such as<br />
automatic adjusting and evaluation of stray light<br />
spectra are in preparation.
2.1. TROPOSPHERIC RESEARCH GROUP 23<br />
2.1.5 Ground based MAX-DOAS measurements<br />
Participating scientists Ossama Ibrahim, Thomas Wagner, Ulrich Platt<br />
Abstract The Multi-axis DOAS technique uses scattered sunlight to obtain information about the<br />
trace gases in the atmosphere by pointing a telescope to different elevation angles and thus receiving<br />
light from different directions. Using Multi-axis DOAS instrument on a stable or movable ground<br />
based platform can also be used to validate DOAS measurements done by satellite instruments.<br />
Figure 2.5: Latitudinal distribution of Stratospheric NO2 VCDs in comparison with SCIAMACHY<br />
results as an example of satellite data validation using ground based MAX-DOAS. The morning<br />
measurements were taken between 5-7 AM O’clock morning and the afternoon ones are between 5-7<br />
PM O’clock afternoon and SCIAMACHY data were collected at 10 AM local equator time.<br />
Background The measurement of trace gases<br />
(identification and quantification) is important for<br />
the investigation of the chemical and physical processes<br />
in the atmosphere. The development of the<br />
Multi Axis DOAS was an important milestone on<br />
the way of DOAS technique evolution. The ability<br />
to direct telescopes to different elevation angles<br />
(multi-axis) allows to emphasize absorption<br />
paths from lowermost atmospheric layers onto the<br />
stratosphere. Measurements from the ground can<br />
provide information on the vertical profile of the<br />
absorbing trace gases under investigation.<br />
Funding IMPRS fellowship<br />
Methods and results Measurements using<br />
Multi-axis DOAS (Differential Optical Absorption<br />
Spectroscopy) on board of a ship platform<br />
(Polarstern research vessel of Alfred-Wegner <strong>Institut</strong>e<br />
<strong>für</strong> Polar- und Meeresforschung) were carried<br />
out successfully in a latitudinal range between<br />
52 ◦ N and 72 ◦ S every year in the last four years<br />
and gave the possibility to measure several trace<br />
gases like NO2, O3 and BrO in the stratosphere<br />
and/or in the marine boundary layer (MBL). The<br />
measurements showed elevated tropospheric NO2<br />
values in the English channel area and the existence<br />
of the tropospheric BrO in the MBL westerly<br />
from Africa in the latitudinal range between<br />
10 ◦ N and 30 ◦ N, which cannot be seen by satellite<br />
instruments because of their higher detection<br />
limit in mid-latitudes. Also a latitudinal cross sectional<br />
distribution of the stratospheric NO2, O3<br />
and BrO were compared to those obtained from<br />
satellite measurements from GOME and SCIA-<br />
MACHY (see figure 2.5). Ground based measurements<br />
from a stable platform in Cabauw in Holland<br />
were performed to retrieve information about<br />
the tropospheric values of trace gases like NO2<br />
and compare them to those obtained from satellite<br />
OMI. Arranging the viewing geometry using<br />
three different telescopes in three viewing planes<br />
can provide some data on the variation of the NO2<br />
concentrations within an OMI pixel. For information<br />
about the satellites see satellite group report.<br />
Outlook/Future work More investigation of<br />
trace gas concentrations in the troposphere and<br />
stratosphere using ground based measurements<br />
from different platforms comparing with results<br />
from satellite measurements for validation of especially<br />
the newer generations SCIAMACHY and<br />
OMI is going to be performed in the near future.<br />
The Multi-axis DOAS will be used on a moving<br />
platform (car) in urban areas to make estimation<br />
of the in and out flux of trace gases from cities besides<br />
measurements for single plumes from powerplants<br />
or industrial activities. This is a promising<br />
application which has already started.
24 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.6 Imaging DOAS. Imaging of two-dimensional trace gas distributions<br />
Participating scientists Ilia Louban, Nicole Bobrowski<br />
Abstract The two-dimensional trace gas distributions in volcanic plumes was quantitatively determinated.<br />
The measurements at Mt. Etna volcano (spring 2005) and on the island Vulcano (autumn<br />
2004) were carried out with an instrument, based on the principle of Differential Optical Absorption<br />
Spectroscopy combined with an imaging spectrograph (I-DOAS).<br />
Figure 2.6: Two dimensional distribution of sulphur dioxide (SO2) in volcanic plume of Mt. Etna,<br />
measured on May 9. 2005 at 13:30 local time. The image represents a scanned solid angle of (v×h)<br />
13.1 ◦ × 36.4 ◦ of a emission source 10 km away. The Values are slant column densities.<br />
Background Spatial resolved data of trace gas<br />
distributions have a wide spectrum of applications.<br />
In many cases it is essential to be able to<br />
determinate the location of the sources and the<br />
strength of their emissions. Also the dynamical<br />
development and behavior of trace gas concentrations<br />
(trace gas clouds) are very interesting and<br />
important for environmental sciences. The advantage<br />
of the DOAS technique to measure several<br />
trace gases simultaneously can be used to investigate<br />
the chemical balances and processes within<br />
the emissions and high spatial resolution of the<br />
instrument allows to estimate those fluxes.<br />
Funding The developments and investigations<br />
took place within the Project for Development of<br />
Optical Remote Sensing for Volcanic Applications<br />
(DORSIVA), supported by the European Union.<br />
Methods and results Imaging of an object<br />
means to produce a two-dimensional dataset of<br />
spatial information, i.e. each picture element<br />
(pixel) of an image is assigned to a defined solid<br />
angle of the space. In case of imaging spectroscopy<br />
third dimension of data accrued, the spectral information<br />
of each pixel. An imaging spectrograph<br />
allows simultaneous imaging and dispersion of the<br />
light, therefore a two dimensional detector, like<br />
CCD detector is needed.<br />
The instrument optics focus the light from a<br />
defined solid angle (here a column) of space on<br />
the vertical entrance slit of the spectrograph. The<br />
grating inside the spectrograph images spatial and<br />
spectral resolved light on the CCD matrix assigning<br />
the vertical dimension of the detector to the<br />
spatial information and horizontal dimension of<br />
the detector to the spectral information. After the<br />
readout of the CCD, the data of one space column<br />
(”column-shot”) is acquired. Using the horizontal<br />
scanning system a viewing angle up to 70 ◦ can<br />
be scanned. The number of horizontally resolved<br />
pixels is given by the number of acquired ”columnshots”.<br />
The width of those depends on displacement<br />
of the scanning mirror between the ”columnshots”.<br />
The number of vertically resolved pixels<br />
is limited by the number of detector-pixel rows of<br />
the CCD matrix and can be scaled down by averaging<br />
over several detector-pixels rows. After the<br />
acquisition spectral information of each pixel has<br />
to be evaluated with the DOAS method and the<br />
colour coded slant column densities (SCD) can be<br />
assembled into an image (Fig. 2.6).<br />
During the campaigns at Mt. Etna and on<br />
the island Vulcano two-dimensional distributions<br />
of sulphur dioxide (SO2) were measured and the<br />
SO2 flux of several fumaroles were estimated.<br />
Also highly resolved SO2 time series to study the<br />
plume dynamics were performed. Additionally,<br />
two dimensional distributions of bromine monoxide<br />
(BrO) were successfully retrieved. SCD up<br />
to 2.8 · 10 14 Molecules/cm 2 were detected in the<br />
plume of Mt. Etna volcano. By two-dimensional<br />
distributions of SO2 and BrO, depression of the<br />
[SO2]/[BrO] ratio from the center to the age of<br />
the plume was identified. This allows conclusions<br />
about possible ozone involved oxidation processes<br />
of BrO production.<br />
Main publication [Louban, 2005]
2.1. TROPOSPHERIC RESEARCH GROUP 25<br />
2.1.7 Multi Axis Differential Optical Absorption Spectroscopy (MAX-DOAS)<br />
of Trace Gas and Aerosol Distributions<br />
Participating scientist Roman Sinreich<br />
Abstract The combination of MAX-DOAS measurements, i.e. DOAS measurements at different<br />
elevation angles from the ground, and radiative transfer modelling is a suitable method to derive<br />
distributions of trace gases and aerosols.<br />
Figure 2.7: Comparison of MAX-DOAS and in-situ measurements of HCHO in Pinnacle State Park<br />
(USA) at August 3, 2004.<br />
Background For three decades DOAS has been<br />
applied and can be used to measure trace gases<br />
like e.g. NO2, SO2 or HCHO by means of sunlight<br />
[Platt, 1994]. Sunlight passing through the atmosphere<br />
is scattered and absorbed by gas molecules<br />
in the air whereby the absorption occurs at wavelengths<br />
which are characteristic for each trace gas.<br />
The resulting sunlight spectrum contains an absorption<br />
pattern which is suitable to detect and<br />
quantify the according trace gases.<br />
In this study, ground-based DOAS measurements<br />
were performed and their spectra analysed.<br />
One focus was to derive trace gas and aerosol<br />
distributions, by using the measured results and<br />
modelled data.<br />
Methods and results The retrieval of trace<br />
gases by means of DOAS yield Slant Column Densities<br />
(SCDs) which depend upon the concentration<br />
of the according trace gas and the light path.<br />
Since scattered sunlight is measured, the light<br />
path is not readily defined and has to be calculated<br />
by atmospheric radiation transport models.<br />
Furthermore, different elevation angles from the<br />
ground have to be performed in order to get information<br />
on the vertical profile. This method<br />
is called Multi-Axis-DOAS (MAX-DOAS) and allows<br />
to derive gas and aerosol distributions near<br />
the surface.<br />
Aerosol properties can be gained indirectly by<br />
measurements of gas species whose 3-dimensional<br />
distribution is already known and relatively constant.<br />
E.g. O4, whose concentration is proportional<br />
to the square concentration of O2, provides<br />
these qualities. So variations in measured<br />
SCDs are dominated by the aerosol distribution,<br />
which causes different light paths in the atmosphere<br />
[Wagner et al. , 2004].<br />
In summer 2004, a MAX-DOAS network measurement<br />
of 7 sites was performed in New England<br />
(USA) in the framework of ICARTT (International<br />
Consortium for Atmospheric Research on<br />
Transport and Transformation). Thereby, SCDs<br />
of NO2, HCHO, O4 and SO2 could be retrieved<br />
and are in agreement in the main lines with in-situ<br />
measurements at these sites (e.g. see figure 2.7).<br />
Furthermore, an ozone depletion event could be<br />
observed and Glyoxal (C2H2O2) which is a good<br />
tracer for Volatile Organic Compounds could be<br />
detected for the first time by a straylight DOAS<br />
device. Radiative transfer calculations allowed an<br />
estimation of the mixing ratio of about 100 ppt<br />
for Glyoxal at a specific day.<br />
Outlook/Future work Continuation of comparisons<br />
with in-situ measurements, improvement<br />
of the technique of deriving the gas and aerosol<br />
distributions and a MAX-DOAS measurement<br />
campaign in March 2006 in Mexico City.<br />
Main publication [Sinreich et al. , 2005]
26 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.8 The flying laboratory: DOAS on board the CARIBIC aircraft project<br />
Participating scientists Barbara Dix, Udo Frieß, Thomas Wagner, Ulrich Platt<br />
Abstract CARIBIC is an innovative scientific project to study atmospheric processes on board a<br />
passenger aircraft during long-distance flights. Besides in-situ measurements of various atmospheric<br />
compounds, it also features a Multi-Axis DOAS instrument to detect specific trace gases.<br />
Figure 2.8: The inlet system. Three small black holes in the upper half indicate the position of the<br />
DOAS telescope entrance holes.<br />
Background Halogen compounds and nitrogen<br />
oxides have a significant impact on the global<br />
ozone budget, e.g. reactive bromine and chlorine<br />
compounds cause stratospheric ozone depletion.<br />
Since anthropogenic sources of bromine<br />
compounds are increasing, bromine compounds<br />
are expected to have a growing impact on the<br />
chemical balance of the lower stratosphere in the<br />
future. Halogen species also play an important<br />
role in the troposphere. A possible background<br />
of reactive bromine compounds in the free troposphere<br />
could influence the ozone budget as well<br />
and thus global climate.<br />
Within the frame of CARIBIC (Civil Aircraft<br />
for the Regular Investigation of the atmosphere<br />
Based on an Instrument Container), a new DOAS<br />
(Differential Optical Absorption Spectroscopy) instrument<br />
was built. Besides BrO, it is also able to<br />
detect HCHO, OClO, O3, NO2, water vapor and<br />
O4.<br />
Methods and results The new DOAS instrument<br />
is the only remote sensing instrument within<br />
the CARIBIC project, which comprises 21 instruments<br />
of 11 European institutions in an cargo container,<br />
that has been successfully put into operation<br />
on a new long-range Airbus (A340-600) of<br />
Deutsche Lufthansa in December 2004. Since May<br />
2005 regular flights with fully automated measurements<br />
are performed once a month. A miniaturized<br />
telescope system, which was especially designed<br />
to fit into the inlet system (see Figure<br />
2.8), collects uv-visible scattered sun light from<br />
three different viewing directions (nadir, 10 degrees<br />
above and below the horizon). With this<br />
Multi-Axis technique the separation of boundary<br />
layer, free tropospheric and stratospheric columns<br />
is possible. Trace gases are then detected in<br />
recorded spectra by means of their individual absorption<br />
structures<br />
First results show that the new instrument<br />
performs well. Stratospheric columns of BrO,<br />
NO2 and O3 could be detected as well as tropospheric<br />
water vapor in the tropics. Enhanced levels<br />
of tropospheric NO2 and HCHO during landing<br />
and take-off in big cities such as Buenos Aires,<br />
Guanghzou (China) or Manila were seen due to<br />
anthropogenic pollution. Slant columns of the<br />
oxygen dimer O4 could be derived, which yield<br />
information on the radiative transport. So far no<br />
indications of enhanced BrO levels in the free troposphere<br />
could be found, yielding perhaps to an<br />
evenly distributed BrO background, but these results<br />
are not yet of statistical significance and future<br />
flights have to be awaited.<br />
Outlook/Future work The future work will<br />
consist of exploring the full scientific potential of<br />
this unique DOAS data set, being the first DOAS<br />
measurements on a long-distance aircraft and taking<br />
into account the synergy of other CARIBIC<br />
measurements, e.g. of aerosol, water vapor, ozone<br />
or halocarbons.
2.1. TROPOSPHERIC RESEARCH GROUP 27<br />
2.1.9 Heidelberg ground-based network<br />
Participating scientists Barbara Dix, Udo Frieß, Thomas Wagner, Karin Kreher(1), Ulrich Platt;<br />
(1): National <strong>Institut</strong>e of Water and Atmosphere, Lauder, New Zealand<br />
Abstract The Heidelberg ground-based network consists of four instruments (see Figure 2.9) which<br />
are set up for long-term monitoring. The instruments provide valuable information on global atmospheric<br />
trends and contribute to scientific questions with respect to their individual location.<br />
Figure 2.9: Water vapor measurements at Paramaribo; location of ground-based instruments.<br />
Background The Heidelberg ground-based<br />
network started with measurements in Kiruna,<br />
Sweden, in 1996 and was soon followed by instruments<br />
in the Antarctic. The polar regions have<br />
always been of great scientific interest, since there<br />
the environment is almost free of anthropogenic<br />
influences. While the Artic has become more<br />
polluted, the Antarctic continent still provides<br />
a very clean troposphere, that enables accurate<br />
studies on stratospheric chemistry and transport.<br />
The polar DOAS (Differential Optical Absorption<br />
Spectroscopy) measurements focus on the influence<br />
of halogen compounds on the ozone budget,<br />
with the Antarctic (stratospheric) ozone hole in<br />
spring being its most prominent example. Yet the<br />
ozone hole phenomenon is not restricted to the<br />
southern hemisphere. Severe ozone destruction is<br />
also observed in the Arctic, but usually of smaller<br />
extent due to rather unstable dynamics. Both<br />
hemispheres show also tropospheric halogen activity:<br />
Autocatalytic processes on sea ice cause so<br />
called bromine explosions, which often lead to the<br />
complete destruction of near surface ozone (polar<br />
tropospheric ozone hole).<br />
In 2002 the DOAS instrument in Paramaribo,<br />
Suriname, was setup within a satellite validation<br />
project (Sciamachy validation). At the time of installation,<br />
this instrument was - to our knowledge<br />
- the first continuously operating DOAS instrument<br />
in the tropics. Measurements in the tropics<br />
allow to study global circulation since this is where<br />
most tropospheric air enters the stratosphere.<br />
Funding Sciamachy validation<br />
Methods and results Both Antarctic instruments<br />
and the one in Paramaribo use the Multi-<br />
Axis (MAX)-DOAS technique, where different<br />
viewing directions between zenith and horizon are<br />
scanned sequentially, thus yielding information in<br />
the vertical distribution of trace gases. With<br />
the MAX-DOAS setup many bromine explosion<br />
events were observed in detail. In contrast to measurements<br />
in the Arctic the data base of Arrival<br />
Heights shows no signs of a possible and suggested<br />
global BrO background.<br />
An example of MAX-DOAS measurements in<br />
Paramaribo show significant amounts of water vapor<br />
in the troposphere with rising columns at<br />
lower elevation angles indicating the presence of<br />
water in lower atmospheric layers (see Figure 2.9).<br />
Water has a major impact on radiative forcing and<br />
climate, therefore monitoring water trends is most<br />
valuable in understanding climate change.<br />
All stations contributed to the validation of<br />
satellite data (O3, NO2, BrO) with the Paramaribo<br />
data set adding one of the first BrO long<br />
term measurements in the tropics. The instrument<br />
at German Antarctic station Neumayer is<br />
also part of the international Network for the Detection<br />
of Stratospheric Change (NDSC).<br />
Outlook/Future work Future work will consist<br />
in continuous measurements, data analysis<br />
and interpretation.
28 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.10 Applicability of light-emitting diodes as light sources<br />
for active DOAS measurements<br />
Participating scientists Christoph Kern, Sebastian Trick, Ulrich Platt<br />
Abstract Light-emitting diodes (LEDs) were tested in respect to their applicability in long path<br />
DOAS (LP-DOAS) measurements. Measurements of NO2 and NO3 were conducted in Heidelberg<br />
using the novel method. Temperature stabilization of the LEDs was found to be essential.<br />
Figure 2.10: (a) Estimated spectral radiance distribution of the Osram 450 W/2 XBO xenon arc lamp,<br />
a Luxeon LXHL-LR3C high power 3W royal blue LED, and a conventional tungsten halogen lamp<br />
(20W). Note that the halogen lamp spectrum is multiplied by 10 in this figure. (b) Spectral radiance<br />
normalized to the electrical input power of the individual sources.<br />
Background To date, xenon arc lamps have established<br />
themselves as the most common light<br />
sources for active DOAS instruments. However,<br />
these have several disadvantages including poor<br />
power efficiency and low lifetime resulting in high<br />
maintenance costs. Modern LEDs potentially represent<br />
a very advantageous alternative. [Ball et al.<br />
, 2004] have already performed first cavity enhanced<br />
absorption spectroscopy (CEAS) measurements<br />
with LED light sources, and we conducted<br />
the first LP-DOAS measurements here.<br />
Funding Diplomarbeit therefore “not applicable”<br />
Methods and results The radiative properties<br />
of a variety of LEDs were characterized,<br />
and parameters such as spectral shape, spectral<br />
range, spectral stability, and how these could<br />
be influenced by environmental factors were analyzed.<br />
A study on the radiative properties of modern<br />
high-power LEDs revealed that despite their<br />
much lower power consumption, they posses spectral<br />
radiances comparable to those of xenon arc<br />
lamps at their peak wavelengths (see Figure 2.10).<br />
The spectra of several LEDs were found to contain<br />
Fabry-Perot etalon-induced spectral structures<br />
that interfered with the DOAS evaluation,<br />
in particular when a constant temperature was<br />
not maintained. It could be shown that LEDs<br />
can successfully be used as light sources in active<br />
DOAS experiments measuring NO2 and NO3<br />
around 450 and 630 nm, respectively. Average detection<br />
limits of 0.3 ppb and 16 ppt, respectively,<br />
were obtained using a 6 km light path in the open<br />
atmosphere.<br />
Outlook/Future work In future LED-DOAS<br />
experiments, emphasis must be put on achieving<br />
higher temperature stability. Also, LEDs are becoming<br />
brighter and more cost-effective, and there<br />
has been considerable recent interest in the development<br />
of UV-LEDs. Devices with emission wavelengths<br />
as low as 250 nm were already demonstrated<br />
in the laboratory. Soon, these will be<br />
available as DOAS light sources, thus enabling the<br />
measurement of many further trace gases such as<br />
BrO, SO2, HCHO, and aromatic hydrocarbons.<br />
Main publications [Kern, 2004],<br />
[Kern et al. , 2005]
2.1. TROPOSPHERIC RESEARCH GROUP 29<br />
2.1.11 Active DOAS measurements of trace gases in the free troposphere<br />
Participating scientist Katja Seitz<br />
Abstract The aim of this thesis was to establish a remote controlled active long–path Differential<br />
Optical Absorption Spectroscopy (DOAS) system with three spectrographs at the research station<br />
Schneefernerhaus on the Zugspitze to measure atmospheric trace gases.<br />
Figure 2.11: Umweltforschungsstation Schneefernerhaus (Zugspitze)<br />
Background Because of its remote location<br />
in the free troposphere the Environmental Research<br />
Station Schneefernerhaus is of special interest<br />
for the measurement of trace gases such as<br />
formaldehyde and ozone. As the Schneefernerhaus<br />
is hard to reach a remote-controlled longpath-<br />
DOAS-system with three spectrographs was established.<br />
Methods and results In order to make<br />
longterm measurements of trace gases such as<br />
ozone and formaldehyde a remote-contr olled<br />
longpath-DOAS (Differential Optical Absorption<br />
Spectroscopy) instrument was established. The<br />
lightbeam of a high pres sure xenon lamp is send<br />
to a retro reflector at a distance of two kilometers<br />
and then back to the Schneefernerhaus. As each<br />
trace gas has a characteristic absorp tion structure<br />
one can determine the concentration of different<br />
trace gases by comparing the reflected light with<br />
a lamp spectra.<br />
After several developements of the system first<br />
measurements were made. It was possible to detect<br />
o zone and formaldehyde. As two different<br />
types of spectrographs were used, their results<br />
were compared.<br />
Outlook/Future work An optical shortcut<br />
system has to be developed. Moreover light emitting<br />
diodes (LEDs) could be used instead of the<br />
xenon lamp, which would be much cheaper and<br />
less effort as the lifetime of a LED is a lot longer<br />
than that of a xenon lamp.<br />
Main publication [Seitz, 2005]
30 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.1.12 Long Term Observations of Urban Atmospheric Radical Chemistry<br />
(TURBAN)<br />
Participating scientists Jutta Zingler, Christoph Kern, Daniel Pedersen, Valeri Matveev, Mordechai<br />
Peleg, Ulrich Platt, Menachem Luria<br />
Abstract Using Long Path DOAS and MiniDOAS, seasonal and spatial patterns in the chemistry<br />
of NO3 in an arid urban location are investigated. Its contribution to the transformation and removal<br />
of atmospheric compounds is evaluated. Long term measurements are validated and complemented<br />
by a short term intensive measurement period.<br />
Figure 2.12: Vertical NO3 profiles: Measurement geometry for the MiniDOAS part of this study.<br />
Background The nitrate radical (NO3) is a<br />
key component of nighttime chemistry in the<br />
troposphere and is responsible for the nonphotochemical<br />
production of peroxy radicals and<br />
the transformation of important species such as<br />
nitrogen oxides, VOCs, and ozone. It can be comparable<br />
to the OH radical as a sink for nitrogen<br />
oxides and VOCs. Up to this project, the only<br />
two studies to provide long term nighttime measurements<br />
of NO3 in the boundary layer were conducted<br />
in Germany at a rural coastal site [Heintz<br />
et al. , 1996] and at a rural suburban site [Geyer<br />
et al. , 2001]. One short-term study reported daytime<br />
measurements of NO3 [Geyer et al. , 2003].<br />
Funding German Israeli Foundation for Scientific<br />
Research and Development (G.I.F.)<br />
Methods and results A long term monitoring<br />
station has been established by the Hebrew<br />
University of Jerusalem in the urban center of<br />
Jerusalem, including a Long Path DOAS system<br />
and several monitors for a variety of atmospheric<br />
trace gases and parameters. During an intensive<br />
one month joint field work campaign, IUP Heidelberg<br />
has set up a high end Long Path DOAS<br />
system aiming for quality control, high time resolution<br />
and enhancement of species investigated.<br />
A red LED as alternative light source and new<br />
technology was applied successfully during some<br />
days.<br />
Vertical profiles of NO3 have been measured<br />
using an advanced MiniDOAS system equipped<br />
with a VIS mini-spectrograph (MiniTURBAN).<br />
Stray light spectra acquired during sunrise give<br />
an idea on the concentration profiles in higher atmospheric<br />
layers.<br />
Information on photolytic rates is retrieved<br />
from solar radiation measurements with a spectral<br />
radiometer.<br />
Our long path measurements yielded positive<br />
results for NO3 during almost every night, with<br />
mixing ratios up to 300 ppt. NO3 was found during<br />
a period of very high humidity. Good agreement<br />
could be found comparing NO2 Long Path<br />
DOAS data with in situ monitor results.<br />
Outlook/Future work Evaluation improvement,<br />
intercomparison/correlation of data, quality<br />
control for long term data, profile modelling,<br />
investigation of photolysis parameters.<br />
Main publication in preparation
2.1. TROPOSPHERIC RESEARCH GROUP 31<br />
References<br />
Ball, S. M., Langridge, J. M., & Jones, R. L. 2004. Broadband cavity enhanced absorptions spectroscopy<br />
using light-emitting diodes. Chem. Phys. Lett., 398, 68–74.<br />
Barrie, L. A., & Platt, U. 1997. Arctic tropospheric chemistry. Overview to Tellus special issue, 49B,<br />
450–454.<br />
Bobrowski, N. 2005. Volcanic Gas Studies by MAX-DOAS. Dissertation, <strong>Universität</strong> Heidelberg.<br />
Bobrowski, N., & Filsinger, F. 2005. Mini-MAX-DOAS Manual. <strong>Universität</strong> Heidelberg.<br />
Bobrowski, N., Hönninger, G., Lohberger, F., & Platt, U. 2005. IDOAS: A new monitoring technique<br />
to study the 2D distribution of volcanic gas emissions. J. Volcanol. Geotherm. Res., Accepted for<br />
publishing.<br />
Burkholder, J. B., Curtius, J., Ravishankara, A. R., & Lovejoy, E. R. 2004. Laboratory studies of the<br />
homogeneous nucleation of iodine oxides. Atmos. Chem. Phys., 4, 19–34.<br />
Cauer, H. 2004. Schwankungen der Jodmenge der Luft in Mitteleuropa, deren Ursachen und deren<br />
Bedeutung <strong>für</strong> den Jodgehalt unserer Nahrung (Auszug). Angewandte Chemie 52, 11, 625–628.<br />
Cox, R. A., Bloss, W. J., Jones, R. L., & Rowley, D. M. 1999. OIO and the Atmospheric Cycle of<br />
Iodine. Geophys. Res. Lett., 26 (13), 1857–1860.<br />
Geyer, A., Ackermann, R., Dubois, R., Lohrmann, B., Müller, T., & Platt, U. 2001. Long-term<br />
observation of nitrate radicals in the continental boundary layer near Berlin. Atmos. Env., 35,<br />
3619–3631.<br />
Geyer, A., Alicke, B., Ackermann, R., Martinez, M., Harder, H., Brune, W., Carlo, Piero di, Williams,<br />
E., Jobson, T., Hall, S., Shetter, R., & Stutz, J. 2003. Direct observations of daytime NO3:<br />
Implications for urban boundary layer chemistry. J. Geosphys. Res., 108 (D17), 4368.<br />
Hak, C., Pundt, I., Trick, S., Kern, C., Platt, U., Dommen, J., Ordnez, C., Prvt, A. S. H., Junkermann,<br />
W., Astorga-Llorns, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle, B., Kleffmann,<br />
J., Lörzer, J. C., Braathen, G. O., & Volkamer, R. 2005. Intercomparison of four different in-situ<br />
techniques for ambient formaldehyde measurements in urban air. Atmos. Chem. Phys. Discuss., 5,<br />
2897–2945.<br />
Heintz, F., Platt, U., Flentje, H., & Dubois, R. 1996. Long-term observation of nitrate radicals at the<br />
Tor Station, Kap Arkona (Rügen). J. Geophys. Res., 101 (D17), 22891–22910.<br />
Hoffmann, T., O’Dowd, C. D., & Seinfeld, J. H. 2001. IO homogeneous nucleation. An explanation<br />
for coastal new particle formation. Geophys. Res. Lett., 28 (10), 1949–1952.<br />
Kern, C. 2004. Applicability of light-emitting diodes as light sources for long path DOAS measurements:<br />
A feasibility study. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />
Kern, C., Trick, S., Rippel, B., & Platt, U. 2005. Applicability of light-emitting diodes as light sources<br />
for active DOAS measurements. Appl. Opt., Accepted for publishing.<br />
Leck, C., & Bigg, E. K. 1999. Aerosol production over remote marine areas - A new route. Geophys.<br />
Res. Lett., 26, 3577–3580.<br />
Lee, J. S., Kim, Y. J., Kuk, B., Geyer, A., & Platt, U. 2005. Simultaneous Measurements of Atmospheric<br />
Pollutants and Visibility with a Long-Path DOAS System in Urban Areas. Environ. Monit.<br />
Assess., 104, 281–293.<br />
Lindberg, S., Brooks, S., Lin, C. J., Scott, K. J., Landis, M. S., Stevens, R. K., Goodsite, M., &<br />
Richter, A. 2002. Dynamic Oxidation of Gaseous Mercury in the Arctic Troposphere at Polar<br />
Sunrise. Environ. Sci. Technol., 36, 1245–1256.<br />
Louban, I. 2005. Zweidimensionale Aufnahmen von Spurenstoff-Verteilungen. Diplomarbeit, <strong>Universität</strong><br />
Heidelberg.<br />
O’Dowd, C., Jimenez, J. L., Bahreini, R., Flagan, R. C., Seinfeld, J. H., Hämeri, K., Pirjola, L., ans<br />
S. G. Jennings, M. Kulmala, & Hoffmann, T. 2002. Marine aerosol formation from biogenic iodine<br />
emissions. Nature, 417, 632–636.
32 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
Peters, C. 2005. Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal Boundary<br />
Layer by Active Longpath Differential Optical Absorption Spectroscopy. Dissertation, <strong>Universität</strong><br />
Heidelberg.<br />
Peters, C., Pechtl, S., Stutz, J., Hebestreit, K., Hönninger, G., Heumann, K. G., Schwarz, A., J.,<br />
Winterlik, & Platt, U. 2005. Reactive and organic halogen species in three different European<br />
coastal environments. Atm. Chem. and Phys. Disc., 5, 6077–6126.<br />
Platt, U. 1994. Differential optical absorption spectroscopy (DOAS). In: Sigrist, M. W. (ed), Air<br />
Monitoring by Spectroscopic Techniques. New York: John Wiley.<br />
Platt, U., & Hönninger, G. 2003. The Role of Halogen Species in the Troposphere. Chemosphere 52,<br />
2, 325–338.<br />
Platt, U., & Janssen, C. 1996. Observation and role of the free radicals NO3, ClO, BrO and IO in the<br />
Troposphere. Faraday Discuss., 100, 175–198.<br />
Platt, U., Allan, W., & Lowe, D. 2004. Hemispheric Average Cl Atom Concentration from 13 C/ 12 C<br />
Ratios in Atmospheric Methane. Atmos. Chem. Phys., 4, 2393–2399.<br />
Platt, U., Pfeilsticker, K., & Vollmer, M. 2005. Chapter 24: Atmospheric Optics. In: Träger, F. (ed),<br />
Springer Handbook of Lasers and Optics. Heidelberg: Springer.<br />
Pundt, I., Mettendorf, K. U., Laepple, T., Knab, V., Xie, P., Lösch, J., von Friedeburg, C., Platt,<br />
U., & Wagner, T. 2005. Measurements of trace gas distributions by Long-Path DOAS-Tomography<br />
during the motorway campaign BAB II: experimental setup and results for NO2 (BAB II special<br />
issue). Atmos. Environ., 39(5), 967–975.<br />
Roscoe, H.K., Kreher, K., & Friess, U. 2001. Ozone loss episodes in the free Antarctic troposphere,<br />
suggesting a possible climate feedback. Geophys. Res. Lett., 28, 2911–2914.<br />
Seitz, K. 2005. Spektroskopische Langzeitmessungen von Spurengasen in der freien Troposphäre.<br />
Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />
Sinreich, R., Frieß, U., Wagner, T., & Platt, U. 2005. Multi Axis Differential Optical Absorption<br />
Spectroscopy (MAX-DOAS) of Gas and Aerosol Distributions. Farady Discuss., 153 – 164.<br />
Stutz, J., Hebestreit, K., Alicke, B., & Platt, U. 1999. Chemistry of halogen oxides in the troposphere:<br />
comparison of model calculations with recent field data. J. Atmos. Chem., 34, 65–85.<br />
Tas, E., Peleg, M., Matveev, V., Zingler, J., & Luria, M. 2005. Frequency and extent of bromine oxide<br />
formation over the Dead Sea, Israel. J. Geosphys. Res., 110, D11304.<br />
Volkamer, R., Barnes, I., Platt, U., Molina, L. T., & Molina, M. J. 2004. Remote Sensing of Glyoxal<br />
by Differential Optical Absorption Spectrosocopy (DOAS): Advancements in Simulation Chamber<br />
and Field Experiments. In: Rudzinski, K., & Barnes, I. (eds), NATO Advanced Research Workshop<br />
of Environmental Simulation Chambers - Application to Atmospheric Chemical Processes, vol.<br />
NATO Sciences Series, IV. Earth and Environmental Sciences. Zakopane, Poland: Kluwer Academic<br />
Publishers.<br />
Volkamer, R., Spietz, P., Burrows, J. P., & Platt, U. 2005. High-resolution absorption cross-section of<br />
Glyoxal in the UV/vis and IR spectral ranges. J. Photoch. Photobio. A: Chemistry, 172, 35 – 46.<br />
von Friedeburg, C., Pundt, I., Mettendorf, K. U., Wagner, T., & Platt, U. 2005. Multi-AXis-(MAX)<br />
DOAS Measurements of NO2 during the BAB II Motorway Emission Campaign, (BAB II special<br />
issue). Atmos. Environ., 39(5), 977–985.<br />
von Glasow, R., & Crutzen, P.J. 2004. Model study of multiphase DMS oxidation with a focus on<br />
halogens. Atmos. Chem. Phys., 4, 589–608.<br />
von Glasow, R., von Kuhlmann, R., Lawrence, M. G., Platt, U., & Crutzen, P.J. 2004. Impact of<br />
reactive bromine chemistry in the troposphere. Atmos. Chem. Phys., 4, 2481 – 2497.<br />
Wagner, T., Dix, B., v. Friedeburg, C., Frieß, U., Sanghavi, S., Sinreich, R., & Platt, U. 2004.<br />
MAX-DOAS O4 measurements: A new technique to derive information on atmospheric aerosols -<br />
Principles and information content. J. Geophys. Res., 109, D22205.
2.1. TROPOSPHERIC RESEARCH GROUP 33<br />
Wenig, M., Jähne, B., & Platt, U. 2005. Operator Representation as a new differential optical absorption<br />
spectroscopy formalism. Appl. Opt., 44(16), 3246–3253.<br />
Wennberg, P.O., Hanisco, T. F., Jaegle, L., Jacob, D. J., Hintsa, E. J., Lanzendorf, E. J., Anderson,<br />
J.G., Gao, R. S., Keim, E. R., Donnelly, S. G., Negro, L. A. Del, Fahey, D. W., McKeen, S. A.,<br />
Salawitch, R. J., Webster, C. R., May, R. D., Herman, R. L., Proffitt, M. H., Margitan, J. J., Atlas,<br />
E. L., Schauffler, S. M., Flocke, F., McElroy, C. T., & Bui, T. P. 1998. Hydrogen radicals, nitrogen<br />
radicals, and the production of O3 in the upper troposphere. Science, 279, 49–53.<br />
Zingler, J., & Platt, U. 2005. Iodine Oxide in the Dead Sea Valley: Evidence for inorganic sources of<br />
boundary layer IO. J. Geosphys. Res., 110, D07307.
2.2. STRATOSPHERIC OZONE 35<br />
2.2 Stratospheric Ozone<br />
Participating scientists Pfeilsticker, K., A. Butz, M. Dorf, K. Grunow (*), L. Kritten, A. Lindner,<br />
U. Reichl, J. Schwärzle, B. Simmes, and F. Weidner, (*) also with FU-Berlin<br />
Abstract Stratospheric research at the IUP concentrates on an improved understanding of the<br />
photochemical processes controlling stratospheric ozone and its link to climate.<br />
Figure 2.13: Recent history of stratospheric organic (Brorg y = CH3Br, various man-made halones,<br />
and shorter lived organo-bromines) and inorganic (Brin y ) bromine. The open square denoted Brin y<br />
inferred from balloon-borne BrO measurements of the LPMA/DOAS balloon payload since 1996. Note<br />
that bromine is responsible for ∼ 35% of the recent stratospheric loss in ozone with an anticipated<br />
increasing fraction of the total in the future (adopted from M. Dorf, PhD thesis 2005).<br />
Scientific objectives of our stratospheric ozone research include investigation on:<br />
• the photochemistry and budget of upper tropospheric and stratospheric bromine (BrO, Bry)<br />
and its relevance to stratospheric ozone (see figures 2.13 and 2.2.1).<br />
• the photochemistry and budget of upper tropospheric and stratospheric iodine (IO, OIO, Iy)(see<br />
2.2.2 and 2.2.4)<br />
• the stratospheric chemistry and budget of odd nitrogen (NO, NO2, HNO3, ClONO2) (see<br />
2.2.2)<br />
• the partitioning and photochemistry of chlorine and bromine in the high latitude stratosphere<br />
and the assessment of the instantaneous in-situ ozone loss rate (see 2.2.2)<br />
• prominent natural and anthropogenic sources to the trace gas composition of the tropical<br />
tropopause and lowermost stratosphere (TTL/LMS) (see 2.2.4 and 2.2.5)<br />
• the temporal and spatial dependence of stratospheric radicals concentrations (e.g., NO2/N2O5,<br />
BrO/OClO, . . . ) (see 2.2.3)<br />
• the validation of remote sensing satellite instruments, such as ILAS/ADEOS, POAM II and<br />
III, SAGE II and III, ODIN/OSIRIS, GOME/ERS-2, and SCIAMACHY/ENVISAT satellite<br />
instruments (see 2.2.1 and 2.2.2)<br />
Methods The research objectives imply to probe the stratosphere by high altitude (∼ 40 km)<br />
balloon soundings. For that purpose the research group is operating (1) a lab-built two channel<br />
UV/vis spectrometer with which direct Sun measurements are made, and (2) a novel LIMB scanning<br />
UV/vis spectrometer. Both spectrometers are deployed on the joint French/German LPMA/DOAS<br />
(Laboratoire de Physique Moléculaire et Applications/Differential Optical Absorption Spectroscopy)<br />
balloon payload. Jointly with our direct Sun measurements, our French partner operates a near-IR<br />
Fourier Transform Spectrometer with which mid-IR absorbing gases are measured. Balloon flights<br />
are regularly performed at high (Kiruna/Sweden), mid (Aire sur l’Adour/France) and low latitudes
36 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
(Teresina/Brazil). Interpretation of the measurements also involves radiative transfer studies and 1-D<br />
photochemical modelling on air mass trajectories provided by our partner Meteorologisches <strong>Institut</strong>,<br />
FU-Berlin, Berlin, Germany. The model’s required initialisation is provided through outputs from a<br />
3-D chemistry model (CTM-SLIMCAT) run by the <strong>Institut</strong>e for Atmospheric Science, School of Earth<br />
and Environment, University of Leeds, Leeds, UK.<br />
Our scientific objectives are primarily achieved through measurements of stratospheric radicals (O3,<br />
NO2, BrO, OClO, IO, OIO, . . . ) and related trace gases (CH4, N2O, HCl, NO, HNO3, ClONO2,<br />
. . . ) and the interpretation of the results with respect to the photochemistry of stratospheric ozone.<br />
Major research objectives involve studies of the processes leading to the formation of the ozone hole<br />
in polar winter, the global decline in stratospheric ozone and since recently the photochemistry and<br />
transport of the tropical tropopause layer (TTL) and lowermost stratosphere (LMS). The research of<br />
the group is largely contributing to various international assessments on stratospheric ozone (WMO<br />
report in 1998, 2002, and 2006), organized by the World Meteorological Organisation (WMO).<br />
Field Campaigns & Studies<br />
1. March 04: a high latitude balloon campaign at Kiruna/Sweden (67.9 o N, 21.2 o W) within the<br />
ENVISAT/SCIAMACHY validation<br />
2. Nov./Dec. 2004: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the<br />
ENVISAT/SCIAMACHY validation<br />
3. June, 2005: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the EN-<br />
VISAT/SCIAMACHY validation<br />
International Cooperation The research group closely cooperates with the following institutions<br />
as e.g., documented in joint peer-reviewed publications.<br />
(1) Forschungszentrum Jülich GmbH, <strong>Institut</strong> <strong>für</strong> Chemie und Dynamik der Geosphare ICG-I: Stratosphäre,<br />
Jülich, Germany (2) Laboratoire de Physique Moléculaire pour l’Atmosphere et l’Astrophysique<br />
(LPMAA), Université Pierre et Marie Curie, Paris, France (3) Harvard-Smithsonian Center for Astrophysics,<br />
Cambridge, USA (4) <strong>Institut</strong>e for Atmospheric Science, School of Earth and Environment,<br />
University of Leeds, Leeds, UK (7) Meteorologisches <strong>Institut</strong>, Freie <strong>Universität</strong> Berlin, Berlin, Germany<br />
(6) Service d’Aeronomie du CNRS, Verrieres le Buisson, France (7) Belgian <strong>Institut</strong>e for Space<br />
Aeronomy (BIRA-IASB), Brussels, Belgium (8) Jet Propulsion Laboratory (JPL), Pasadena, USA<br />
(9) <strong>Institut</strong>e for Atmosphere and Environment, J.W. Goethe University Frankfurt, Frankfurt, Germany<br />
(10) European Space Agency (ESA), Nordwijk, Netherland, (11) <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und<br />
Fernerkundung, University of Bremen, Bremen, Germany (12) Chemistry Department, University of<br />
Cambridge, Cambdrige, UK, (13) <strong>Institut</strong> <strong>für</strong> Meterologie und Klima (IMK) Forschungszentrum <strong>Karls</strong>ruhe,<br />
<strong>Karls</strong>ruhe, Germany<br />
Outlook/Future work Future work will concentrate on (1) time resolved measurements of stratospheric<br />
radicals, and (2) to continue our budget and trend studies on stratospheric bromine and iodine.<br />
Future studies will also be devoted to the validation of existing (ENVISAT/SCIAMCHY) and future<br />
satellite instruments (Metop/GOME-2 and IASI).<br />
Funding comes through research contracts with European Community (EU-EVK2-CT-2000-00059,<br />
and 505390-GOCT-CT-2004), the BundesMinisteriumForschungs&Technologie (BMBF) through the<br />
DLR (DLR-50FE0017) and the Deutsche Forschungsgemeinschaft (DFG PF384/3-1).<br />
Publications<br />
Peer reviewed publications:<br />
1. Butz et al. [2005]<br />
2. Canty et al. [2005]<br />
3. Dufour et al. [2005]<br />
4. Hendrick et al. [2004]<br />
5. Vandaele et al. [2005]<br />
6. Weidner et al. [2005]
2.2. STRATOSPHERIC OZONE 37<br />
PhD theses:<br />
1. Dorf [2005]<br />
2. Weidner [2005]<br />
Diploma theses:<br />
1. Reichl [2005]<br />
2. Schwärzle [2005]<br />
Invited Talks<br />
1. Butz [2005]
38 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.2.1 Investigation of Inorganic Stratospheric Bromine<br />
Participating scientists Dorf, M., A. Butz, F. Weidner, and K. Pfeilsticker<br />
Abstract Balloon-borne DOAS (Differential Optical Absorption Spectroscopy) bromine monoxide<br />
(BrO) measurements and model simulations are used to investigate the inorganic stratospheric<br />
bromine chemistry and to validate BrO limb profiling from the new SCIAMACHY instrument on the<br />
European Envisat (ENVIronment SATellite) satellite.<br />
Morning Evolution Evening Evolution<br />
Time Time<br />
Figure 2.14: Colour-coded model concentration field of BrO as a function of height and SZA, for<br />
a DOAS balloon flight. Left and right panels show the morning and evening evolution of BrO<br />
respectively. The black lines in the left panel represent the line-of-sight of a SCIAMACHY limb<br />
scan. In the right panel the observation geometry of the DOAS measurements is shown. The thick<br />
black line represents the trajectory of the balloon and the thin black lines indicate the optical path<br />
from the Sun to the balloon instrument for measurements during ascent and solar occultation.<br />
Background Inorganic bromine (BrY) is the<br />
second most important halogen affecting stratospheric<br />
ozone. Although much less abundant than<br />
chlorine, stratospheric bromine currently contributes<br />
about 25 % to global ozone loss. During<br />
daylight the most abundant stratospheric bromine<br />
species is BrO, which accounts for 60 − 70 %<br />
of total BrY and is also the most feasible inorganic<br />
bromine species for detection. Balloonborne<br />
DOAS BrO measurements are used for validation<br />
of the SCIAMACHY satellite instrument.<br />
Funding This work was conducted within ESA<br />
contracts AO 146 and AO 465. Funding came<br />
from the BundesMinisterium <strong>für</strong> Bildung und<br />
Forschung (BMBF), contract DLR-50EE0017.<br />
Methods and results BrO is subject to considerable<br />
diurnal variation. Validation thus requires<br />
either perfect collocation of the validation<br />
observation with the satellite profiling, or other<br />
methods to account properly for temporal or spatial<br />
mismatches between both sets of observations<br />
and for their different viewing geometry (see<br />
figure 2.14). Photochemical modelling along air<br />
mass trajectories, which match the balloon with<br />
SCIAMACHY observations are used to account<br />
for these discrepancies and to generate a BrO<br />
profile validation set. First comparisons of SCIA-<br />
MACHY limb measurements with high precision<br />
DOAS BrO profiles show poor agreement, especially<br />
below 20 km, which is presently the most<br />
interesting region for bromine chemistry.<br />
Outlook/Future work<br />
• Investigation of the upper troposphere /<br />
lower stratosphere bromine budget<br />
• Investigation of the composition of organic<br />
bromine source gases<br />
• Bromine trend in the stratosphere<br />
• Coupling of bromine and chlorine chemistry<br />
Main publication Dorf, M., Investigation of<br />
Inorganic Stratospheric Bromine using Balloon-<br />
Borne DOAS Measurements and Model Simulations,<br />
PhD thesis at the University of Heidelberg,<br />
Heidelberg, Germany, 2005.
2.2. STRATOSPHERIC OZONE 39<br />
2.2.2 Stratospheric photochemistry of ozone, nitrogen and chlorine species<br />
Participating scientists at IUP Heidelberg Butz, A., M. Dorf, F. Weidner, and K. Pfeilsticker<br />
Abstract In the recent past the LPMA/DOAS balloon payload has conducted several stratospheric<br />
balloon flights at various locations and in different seasons. The inferred abundances of stratospheric<br />
ozone (O3) and nitrogen dioxide (NO2) are checked for internal consistency and compared to correlative<br />
data measured by the satellite borne instrument SCIAMACHY.<br />
Figure 2.15: Relative deviations between satellite (retrieved by IUP Bremen) and balloon borne measurements<br />
of O3 (left panel) and NO2 (right panel) vertical profiles. Observation sites and conditions are indicated in the<br />
legend. The mean deviation of all coincident data in the 20 km – 31 km altitude is 4.3% with 10.8% standard<br />
deviation for O3 and 1.8% with 12.4% standard deviation for NO2. The grey lines indicate the mean and the<br />
one and two times standard deviation boundaries with respect to the 20 km – 31 km altitude range. Note the<br />
broken abscissa.<br />
Background Nitrogen oxides dominate the catalytic<br />
destruction of stratospheric O3 between 25<br />
and 40 km altitude. Thus, NO2 and O3 measurements<br />
are of primary importance to study<br />
stratospheric photochemistry. Recent studies indicate<br />
that for selected geophysical conditions the<br />
agreement between measured and modeled O3 and<br />
NO2 is better than 10%. Accordingly, measurements<br />
of high accuracy are required to constrain<br />
or to be compared with photochemical models.<br />
Our study aims at estimating the accuracy of<br />
state-of-the-art remote sensing measurements of<br />
O3 and NO2.<br />
Funding The present work has been supported<br />
by ESA, BMBF, DLR and the European Union.<br />
Methods and results Abundances of stratospheric<br />
O3 and NO2 inferred from traditional<br />
solar occultation measurements of the<br />
LPMA/DOAS balloon payload are checked for internal<br />
consistency and subsequently compared to<br />
collocated observations of the SCanning Imaging<br />
Absorption spectroMeter for Atmospheric CHartographY<br />
(SCIAMACHY) onboard the European<br />
Envisat satellite. Our comparison scheme accounts<br />
for the temporal and spatial mismatch (airmass<br />
trajectory modell) as well as for the differing<br />
photochemical conditions (1D chemistry modell)<br />
between the balloon and the satellite borne observations.<br />
The internal agreement of the balloon borne<br />
measurements is 10% and 20% for O3 and NO2,<br />
respectively. Typical deviations between SCIA-<br />
MACHY and the balloon borne data amount to<br />
20% for both gases in the 20 to 30 km altitude<br />
range, see figure (2.15). Below 20 km the agreement<br />
worsens mainly due to lower sensitivity of<br />
the satellite retrieval.<br />
Outlook/Future work<br />
• Extension of the O3 and NO2 validation<br />
study to tropical latitudes<br />
• Case studies of the stratospheric nitrogen<br />
and chlorine budget/partitioning and implications<br />
for ozone loss<br />
• Abundance of iodine radicals in the tropical<br />
upper troposphere and stratosphere<br />
Main publication Butz, A. et al., Intercomparison<br />
of Stratospheric O3 and NO2 abundances<br />
retrieved from balloon borne direct sun observations<br />
and Envisat/SCIAMACHY limb measurements,<br />
Atmos. Chem. Phys. Disc. 5, 10747–<br />
10797, 2005.
40 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.2.3 Photolytic lifetime of stratospheric N2O5<br />
Participating scientists Kritten, L., F. Weidner, A. Butz, B. Simmes, M. Dorf, U. Reichl, and K.<br />
Pfeilsticker<br />
Abstract During one of the first international measurement campaigns in the tropics (Teresina,<br />
Brazil), balloon borne measurements of upper tropospheric and stratospheric trace gases were made<br />
using a recently developed UV/visible spectrometer which operates in limb viewing geometry and<br />
allows to infer time resolved (Weidner et al., 2005) vertical profiles.<br />
Background The amount and partitioning of<br />
stratospheric NOx (NO, NO2 and NO3) and<br />
NOy (NOx, N2O5, HNO3, ClONO2, HO2NO2<br />
and BrONO2) largely govern ozone (O3) photochemistry<br />
in the mid-stratosphere (25-40km).<br />
During daytime, NOx is supplied by the photochemical<br />
decay of the reservoir molecule N2O5.<br />
Monitoring the relative diurnal increase of NO2<br />
thus provides information on the photolytic lifetime<br />
of N2O5.<br />
Funding comes through ESA, BMBF, DLR,<br />
and the European Union.<br />
Methods and results In the framework of international<br />
measurement campaign dedicated to<br />
ENVISAT/SCIAMACHY validation three stratospheric<br />
balloon flights have been performed in<br />
tropical latitudes near Teresina, Northern Brazil,<br />
onboard the MIPAS, LPMA/DOAS and IASI balloon<br />
payloads. Our UV/vis spectrometer took<br />
spectra with scanning elevation angle (0 – -6 o )<br />
during balloon float. Slant column densities<br />
(SCDs) of O3 and NO2 were inferred from measurements<br />
conducted during IASI balloon flight.<br />
Using a Radiative Transport model (Tracy, developed<br />
at IUP Heidelberg) SCDs can be simulated<br />
according to our viewing geometry with an appro-<br />
priate trace gas profile as input.<br />
Figure 2.16 shows the inferred temporal<br />
change in measured stratospheric O3 and NO2 for<br />
the LPMA-IASI flight at Timon/Brazil on June<br />
30, 2005. As expected for the tropical stratosphere,<br />
while the inferred stratospheric ozone does<br />
not change much (< 10% ), NO2 largely increases<br />
(a factor of 2) over the course of the day, primarily<br />
due to the photolysis of the nighttime reservior<br />
species N2O5 into NO2 and NO3. The observed<br />
increase in NO2 can be used to test calculated<br />
N2O5 photolysis frequencies as a function of the<br />
actinic flux and the still uncertain temperature<br />
depndence of the N2O5 absorption cross section.<br />
Outlook/Future work<br />
• Analysis of all three balloon flights at<br />
Teresina for UV/vis absorbing gases such<br />
as O3, NO2, BrO, OClO, IO, OIO, and<br />
CH2O.<br />
• Preparation of and participation in future<br />
measurement campaigns (Kiruna, January<br />
2006)<br />
Main publication Kritten, L., et al., The photolytic<br />
lifetime of stratospheric N2O5, GRL, (in<br />
preparation), 2005.<br />
Figure 2.16: Inferred temporal change stratospheric O3 and NO2 concentrations as a function of<br />
time, solar zenith angle and height for the LPMA-IASI flight at Timon/Brazil on June 30, 2005.<br />
Note while the ozone field is almost constant with time and space, the NO2 concentrations increase<br />
at all altitudes with the largest increase seen in the 30 - 35 km range. Also shown are 2 collocated<br />
SCIAMCHY/ENVISAT observations on June 29, UT 12:16 (# orbit 17412) and on July 1, UT 12:53<br />
(# orbit 17441) which can be validated with the mini-DOAS observations.
2.2. STRATOSPHERIC OZONE 41<br />
2.2.4 Spectroscopic measurements of halogen oxides in the marine boundary<br />
layer in Alcântara/Brazil<br />
Participating scientists Schwärzle, J., A. Lotter, and K. Pfeilsticker<br />
Abstract Since the discovery of stratospheric ozone loss due to these species, the atmospheric<br />
photochemistry of reactive halogen species has become of particular concern. Their fate and behavior<br />
in the atmosphere is still uncertain. During a campaign carried out in Northeastern Brazil, IO was<br />
detected for the first time in a tropical coastal region.<br />
Figure 2.17: Mixing ratio of IO, measured at Alcântara/Brazil. Night time is indicated by grey<br />
background, tidal height is shown in blue in order to point out a possible correlation between tidal<br />
height, daylight and mixing ratios of IO<br />
Background Since reactive halogens have been<br />
detected at different sites all over the world (arctic,<br />
mid-latitudes), the global impact of halogen<br />
oxides on the chemistry of tropospheric ozone is<br />
an arising question. It is of special importance in<br />
the tropics as there is fast vertical convection of<br />
air from the boundary layer into the lower stratosphere.<br />
Funding came through Deutsche Forschungsgemeinschaft<br />
(DFG-PF 384/1-2 and 2-3).<br />
Methods and results The measurements were<br />
conducted by active long-path Differential Optical<br />
Absorption Spectroscopy (DOAS) near the<br />
ocean-surface during a field campaign held in<br />
Alcântara/Northeastern Brazil from December<br />
2004 until January 2005.<br />
Mixing ratios of up to 0.82 ppt of IO were determined<br />
within the IO-absorption-bands in the<br />
spectral range of 418–438 nm. Possible sources of<br />
the inorganic iodine in the marine boundary layer<br />
are the photochemical decay of short-lived organic<br />
iodine emitted from the biologically active oceanic<br />
shelf region (e.g. mangroves), or at lower concentrations<br />
by long-range transport of these species<br />
from the open ocean.<br />
Absorption structures in the range of 320–<br />
350 nm were analyzed for the absorption of<br />
bromine oxide, which could not be detected.<br />
Outlook/Future work<br />
• Identification of iodine source gases<br />
• Abundances of IO in the coastal and continental<br />
tropics<br />
• Determining possible impact of IO on tropospheric/stratospheric<br />
ozone<br />
Main publication Schwärzle, J., Spektroskopische<br />
Messung von Halogenoxiden in<br />
der marinen atmosphrischen Grenzschicht in<br />
Alcântara/Brasilien, Staatsexamensarbeit, University<br />
of Heidelberg, Heidelberg, Germany, 2005.
42 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.2.5 Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern<br />
Brazil: Comparison of tropospheric air mass pollution in the dry and<br />
wet season<br />
Participating scientists Reichl U., A. Butz, M. Dorf, L. Kritten, A. Lindner, B. Simmes, F.<br />
Weidner, and K. Pfeilsticker,<br />
Abstract: The impact of biomass burning on the concentration of tropospheric pollutants is investigated<br />
by comparisons of direct Sun UV/Vis DOAS measurements (Differential Optical Absorption<br />
Spectroscopy) at TIMON/North Eastern Brazil (5.1 o S, 42.9 o W) at the end of dry season in Nov<br />
2004 and after the rainy season in June 2005. Natural and anthropogenic contributions to pollutants<br />
(e.g. CH2O and NO2) to the tropical continental troposphere are assessed and corresponding species<br />
remotely sensed by the ENVISAT/SCIAMACHY instrument are validated. Biomass emission ratios<br />
for NO2 and CH2O are also inferred.<br />
Figure 2.18: Tropospheric vertical amount (VCD) of<br />
NO2 (upper two panels) and CH2O (lower two panels)<br />
during the dry season sunset (left panels) and end of<br />
the wet season (right panels) at TIMON/North Eastern<br />
Brazil (5.1 o S, 42.9 o W). The vertical lines marked<br />
by are (1) the average NO2 at the end-of wet season,<br />
(2) the average NO2 at the end-of dry season, (3) the<br />
average CH2O at the end-of wet season, and (4) the<br />
average CH2O at the end-of dry season. Considering<br />
the most likely emission scenario for TIMON, the<br />
difference of (2) - (1), and (4) - (3) can be ascribed<br />
to end-of the dry season biomass burning emissions.<br />
Accordingly, the baselines in the left panels are being<br />
due to either CH2O formed during hydrogen carbon<br />
related oxidation, or NOx related emission by anthropogenic<br />
emissions.<br />
Background In the tropics biomass burning is<br />
a prominent source of atmospheric pollutants. For<br />
further assessments on the potential impact of<br />
biomass burning on tropospheric ozone and air<br />
quality estimates of emission factors of certain<br />
pollutants, i.e. emitted pollutant mass per mass<br />
biomass burned, is of primary interest [Andreae<br />
& Merlet, 2001].<br />
Methods and results Ground-based direct<br />
sun spectroscopy of NO2 and CH2O<br />
were performed within the balloon-borne EN-<br />
VISAT/SCIAMACHY validation activities in<br />
Northeastern Brazil during the end of the dry season<br />
(Nov. 2004) and wet season (June 2005). The<br />
spectroscopic measurements indicate distinct features<br />
of biomass burning on the tropospheric composition<br />
(compare e.g. the left and right panels<br />
in Figure 2.18) in agreement with recent observations<br />
of ENVISAT/SCIAMACHY instrument (see<br />
section 2.5.12). Our observations indicate typical<br />
increases (∆) in the vertical column amounts<br />
of ∆NO2 = 4.8 · 10 15 /cm 2 and ∆CH2O =<br />
9.0 · 10 15 /cm 2 , respectively for the dry versus<br />
wet season tropical boundary layer. These imply<br />
emission ratios E(∆NOx/∆CH2O) = 1.6 ± 1,<br />
a result being in good agreement with recent<br />
estimates (0.64 to 1.64) for tropical forest fires<br />
(Andreae & Merlet [2001]). The elevated baseline<br />
concentrations (right panels in 2.18) for CH2O<br />
indicate the important role oxidation of naturally<br />
emitted hydrogen carbons plays and for NO2<br />
the influence of anthropogenic activity (traffic related<br />
fossil fuel consumption) related emissions<br />
on the photochemistry of tropospheric ozone and<br />
air quality.<br />
Funding came through research contracts with<br />
the BundesMinisteriumForschungs&Technologie<br />
(BMBF) through the DLR (DLR-50FE0017).<br />
Outlook/Future work will concentrate on a<br />
more thorough characterization of biomass and<br />
fossil fuel related emissions on the photochemistry<br />
of tropospheric ozone and air quality in the tropics.<br />
Validation of remotely sensed tropospheric<br />
pollution will also be conducted.<br />
Main publication Reichl, U., Groundbased<br />
direct Sun UV/vis spectroscopy in Timon/Northeastern<br />
Brazil: Comparison of tropospheric<br />
air mass pollution in the dry and wet<br />
season, Diploma thesis at the University of Heidelberg,<br />
Heidelberg, Germany, 2005.
2.2. STRATOSPHERIC OZONE 43<br />
References<br />
Andreae, M.O., & Merlet, P. 2001. Emission of trace gases and aerosols from biomass burning. Global<br />
Biochem. Cycles, 15, 4, 955 – 966.<br />
Butz, A. 2005. LPMA/DOAS: Balloon based SCIAMACHY validation example: O3 and NO2 vertical<br />
profiles. SCIAMACHY Science Advisory Group 32, Delft, Netherlands.<br />
Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />
P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />
Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 abundances retrieved<br />
from balloon borne direct sun observations and Envisat/SCIAMACHY limb measurements.<br />
Atmos. Chem. Phys. Disc., 5, 10747 – 10797.<br />
Canty, T., Salawitch, R.S., Renard, J.B., Reviere, E.D., Pfeilsticker, K., M., Dorf., Fitzenberger,<br />
R., Bösch, H., Stimpfle, R.M., Wilmouth, D.M., Anderson, J.G., Richard, E.C., Fahey, D.W., &<br />
Gao, R.S.and Bui, T.P. 2005. Analysis of BrO, ClO, and nighttime OClO in the arctic winter<br />
stratosphere. J. Geophys. Res., 110, D01301, doi:10.1029-/2004JD005035.<br />
Dorf, M. 2005. Investigation of inorganic stratospheric bromine by balloon-borne DOAS measurements<br />
and model simulations. PhD thesis, University of Heidelberg, Heidelberg, Germany.<br />
Dufour, G., Payan, S., Lefévre, F., Berthet, G., Eremenko, M., Butz, A., Jeseck, P., Té, Y., Pfeilsticker,<br />
K., & Camy-Peyret, C. 2005. 4D comparison method to study the NOy partitioning in summer<br />
polar stratosphere: Influence of aerosol burden. Atmos. Chem. Phys., 5, 919 – 926.<br />
Hendrick, F., Barret, B., Van Roozendael, M., Boesch, H., Butz, A., De Mazière, M., Goutail, F.,<br />
Lambert, J.-C., Pfeilsticker, K., & Pommereau, J.P. 2004. Retrieval of nitrogen dioxide stratospheric<br />
profiles from ground-based zenith-sky UV-visible observations: Validation of the technique through<br />
correlative comparisons. Atmos. Chem. Phys., 4, 2867 – 2904.<br />
Organization), WMO (World Meteorological. 2003. Scientific Assessment of Ozone Depletion: 2002,<br />
Global Ozone Research and Monitoring. Geneva, Project Report No. 47, 498 pp.<br />
Reichl, U. 2005. Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil: Comparison<br />
of tropospheric air mass pollution in the dry and wet season. Diploma thesis, University of<br />
Heidelberg, Heidelberg, Germany.<br />
Schwärzle, J. 2005. Spektroskopische Messung von Halogenoxiden in der marinen atmosphärischen<br />
Grenzschicht in Alcântara/Brasilien. Staatsexamensarbeit, University of Heidelberg, Heidelberg,<br />
Germany.<br />
Vandaele, A.C., Fayt, C., Hendrick, F., Hermans, C., Humbled, F., Van Roozendael, M., Gil, M.,<br />
Navarro, M., Puentedura, O., Yela, M., Braathen, G., Stebel, K., Tornkvist, K., Johnston, P.,<br />
Kreher, K., Goutail, F., Mieville, A., Pommereau, J.-P., Khaikine, S., Richter, A., Oetjen, H.,<br />
Wittrock, F., Bugarski, S., Frieß, U., Pfeilsticker, K., Sinreich, R., Wagner, T., Corlett, G., &<br />
Leigh, R. 2005. An intercomparison campaign of ground-based UV-Visible measurements of NO2,<br />
BrO, and OClO slant columns. Methods of analysis and results for NO2. J. Geophys. Res., 110,<br />
D08305, doi:10.1029/2004JD005423.<br />
Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />
skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />
Heidelberg, Germany.<br />
Weidner, F., Bösch, H., Bovensmann, H., Burrows, J.P., Butz, A., Camy-Peyret, C., Dorf, M.,<br />
Gerilowski, K., Gurlit, W., Platt, U., von Friedeburg, C., Wagner, T., & Pfeilsticker, K. 2005.<br />
Balloon-borne limb profiling of UV/vis skylight radiances, O3, NO2, and BrO: Technical set-up<br />
and validation of the method. Atmos. Chem. Phys., 5, 1409 – 1422.
2.3. RADIATIVE TRANSFER 45<br />
2.3 Radiative Transfer<br />
Participating scientists Pfeilsticker, K., A. Butz, M. Dorf, A. Lindner, A. Lotter, U. Reichl, T.<br />
Scholl, and F. Weidner<br />
Abstract Research on the radiative transfer (RT) in the Earth’s atmosphere at the IUP concentrates<br />
on an improved understanding of the UV/vis solar irradiance, its temporal variation and the deposition<br />
of solar radiation in the atmosphere. These studies include spectroscopic measurements from different<br />
platforms and sophisticated radiative transfer modelling.<br />
Figure 2.19: Upper panel: Comparison of measured (black) and simulated (red) oxygen A-band<br />
spectrum for the observation at Cabauw (NL) on May 11, 2003 at UT 14:59. The identification of the<br />
oxygen A-band and solar Fraunhofer lines is given next to the line. Middle panel: Residual spectrum<br />
taken as the natural log of the ratio of measured and simulated spectra, hence the natural units of<br />
vertically-integrated optical density (VOD) airmass. Lower panel: Inferred photon path-<strong>pdf</strong>, assuming<br />
a Gamma-distribution for the in-cloud transfer (adopted from Scholl et al. [2005])<br />
Background The transfer of solar radiation in the Earth’s atmosphere is one of the most complicated<br />
issues in environmental sciences, mostly owing due to the variety and complicated nature<br />
of atmospheric absorbers and scatters (e.g., gases, aerosols, liquid and solid cloud particles), their<br />
spectroscopic signatures and varying spatial arrangements. Accordingly it is found that, e.g., clear<br />
and cloudy sky RT is the major uncertainty in climate modelling and the validation of RT codes<br />
thus appears to be necessary. Also, RT codes find applications in photochemical investigations and<br />
in in-situ and remote sensing studies.<br />
Scientific objectives of radiative transfer studies include the following<br />
• the measurements of photon path length distributions of solar photons being transmitted to the<br />
ground (see 2.3.2)
46 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
• the absolute spectral solar irradiance (320 - 650 nm) and its temporal variation (see 2.3.3)<br />
• the measurement of UV/visible actinic fluxes (e.g., of JNO2) and of the limb radiance near<br />
horizon<br />
• the detection and characterization of unknown, overlooked, or yet poorly characterized atmospheric<br />
absorbers, such as the H2O continuum absorption, meta-stable and stable H2O − H2O<br />
dimers, or the collisional complex O2 − O2, .... (see 2.3.4)<br />
• the measurements of the stratospheric aerosol extinction and its relation to volcanic eruptions.<br />
• the validation of level 1 products (spectral solar irradiance, and limb radiances) of the SCIA-<br />
MACHY instrument deployed on the European research satellite ENVISAT (see 2.3.1).<br />
Arguably all these activities aim at a better understanding of the primary driving force of the<br />
climate system e.g., the solar radiation and its deposition in Earth’s atmosphere. The research thus<br />
contributes to better quantify and assess man’s impact on the past, present and future global climate.<br />
Methods used for the investigations of the radiative transfer involve (1) spectroscopic measurements<br />
of the absolute spectral solar irradiance in the UV/vis/near-IR and of corresponding near horizon<br />
skylight limb radiances from different spectrometers (grating and Fourier-Transform) deployed on<br />
high altitude (∼ 40 km) balloon platforms including on-side absolute radiometric calibration to NIST<br />
(National <strong>Institut</strong>e of Standard and Technology, USA) and PTB (Physikalische Technische Bundesanstalt)<br />
radiometric standards (2) ground-based high spectral resolution spectroscopic measurements<br />
of zenith scattered skylight around the oxygen A-band (767 - 771 nm) (see Figure 2.19, upper panel),<br />
that aim at the detection of photon path length distribution of solar photons for a variety of cloudy<br />
skies (see Figure 2.19, lower panel) and (3) long-path spectroscopic absorption measurements near<br />
surface in wavelength intervals ranging from the UV to the near-IR. All the different instruments<br />
are deployed on internationally organized field campaigns that address a wider range of scientific<br />
objectives (see below). The interpretation of these measurements also involves sophisticated radiative<br />
transfer modelling (ray-tracing, Monte Carlo, discrete ordinate models, DISORT) that e.g., account<br />
for the sphericity of the atmosphere, refraction, time and space dependent trace gas and aerosol<br />
concentrations and cloud cover. Activity (1) is performed within a French/German collaboration with<br />
the Laboratoire de Physique Moléculaire et Applications, Université Pierre et Marie Curie, Paris,<br />
France and (2) within a collaboration with the IUP at the University of Bremen, Germany.<br />
Field Campaigns & Studies<br />
1. March 04: a high latitude balloon campaign at Kiruna/Sweden (67.9 o N, 21.2 o W) within the<br />
ENVISAT/SCIAMACHY validation<br />
2. Nov./Dec./Jan. 2004/05: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within<br />
the ENVISAT/SCIAMACHY validation and at Alcantara/Sao Luis/Brazil (2.39 o S, 44.38 o W).<br />
3. June 2005: a tropical balloon campaign at Teresina/Brazil (5.1 o S, 42.9 o W) within the EN-<br />
VISAT/SCIAMACHY validation<br />
International Cooperation The research group closely cooperates with the following institutions<br />
as, e.g., documented in joint peer-review publications.<br />
(1) Laboratoire de Physique Moléculaire pour l’Atmosphere et l’Astrophysique (LPMAA), Université<br />
Pierre et Marie Curie, Paris, France, (2) Meteorologisches <strong>Institut</strong>, Freie <strong>Universität</strong> Berlin, Berlin,<br />
Germany, (3) European Space Agency (ESA), Nordwijk, The Netherlands, (4) <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong><br />
und Fernerkundung, University of Bremen, Bremen, Germany, (5) Los Alamos National Laboratory,<br />
Space and Remote Sensing Sciences Group, Los Alamos, USA, (6) Royal Netherlands Meteorological<br />
<strong>Institut</strong>e (KNMI), De Bilt, The Netherlands, (7) Meteorological <strong>Institut</strong>e, University of<br />
Bonn, Bonn, Germany, (8) Meteorological <strong>Institut</strong>e, University of Munich, Munich, Germany, (9)<br />
GKSS Research Centre, Geesthacht, Germany.<br />
Future work will concentrate on studies (1) of the inter annual variation of the spectral solar<br />
irradiance and its relation to climate change, (2) improved measurements of path length distribution<br />
of solar photons during the life-time of cloud systems, (3) high resolution spectroscopic studies of the<br />
visible and near-IR spectrum of water vapor and (4) 2-D imaging spectroscopy of radiative properties<br />
of the atmosphere.
2.3. RADIATIVE TRANSFER 47<br />
Funding comes through research contracts with the BundesMinisteriumForschungs&Technologie<br />
(BMBF), through the DLR (DLR-50FE0017) and GSF (GSF-07ATF24) and the Deutsche Forschungsgemeinschaft<br />
(DFG PF384/2-1 and PF384/2-3).<br />
Publications<br />
Peer reviewed publications:<br />
1. Crewell et al. [2004]<br />
2. Gurlit et al. [2005]<br />
3. Scholl et al. [2005]<br />
4. Weidner et al. [2005]<br />
PhD theses:<br />
1. Weidner [2005]<br />
Diploma theses:<br />
1. Lindner [2005]<br />
Invited Talks<br />
1. Pfeilsticker et al. [2004]<br />
2. Pfeilsticker [2005a]<br />
3. Pfeilsticker [2005b]
48 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.3.1 Development and Application of a Versatile Balloon-Borne DOAS<br />
Instrument for Skylight Radiance and Atmospheric Trace Gas Profile<br />
Measurements<br />
Participating scientists Weidner, F., H. Bösch, A. Butz, M. Dorf, U. Platt, C. von Friedeburg,<br />
T. Wagner, and K. Pfeilsticker<br />
Abstract A novel balloon-borne UV/vis DOAS instrument measuring limb scattered radiation was<br />
developed, characterized in the laboratory and employed during 5 stratospheric balloon flights. Skylight<br />
radiance and concentration profiles of O3, NO2, and BrO are retrieved and compared to radiative<br />
transfer simulations and measurements of the same parameters.<br />
Background In the past two decades remote<br />
sensing of the atmosphere by optical methods<br />
has evolved into a powerful tool for meteorology,<br />
atmospheric photochemistry and climate studies.<br />
Most recently, space-borne UV/vis limb observations<br />
have also become available, e.g., through<br />
the SME, SOLSE/LORE, Odin/OSIRIS, and EN-<br />
VISAT/SCIAMACHY instruments. Quasi in-situ<br />
UV/vis limb profiling from balloon may also offer<br />
a new method for time resolved spectroscopy of<br />
ozone harmful radicals in the stratosphere.<br />
Scientific questions that can be tackled by<br />
UV/vis limb measurements are:<br />
(1) measurements of near horizon limb radiance<br />
for different illumination conditions and validation<br />
of radiative transfer codes.<br />
(2) Monitoring profiles of stratospheric radical<br />
species, such as O3, NO2, BrO, OClO, IO, ....<br />
and studies of their photochemistry and budget,<br />
e.g., for the systems NO2/N2O5 (see 2.2.3) or<br />
BrO/OClO and its importance for ozone loss.<br />
Methods UV/visible skylight radiances (330 −<br />
550 nm) are measured from azimuth controlled<br />
balloon payloads which are flying into the middle<br />
stratosphere (∼ 32km). The spectra are analyzed<br />
for along-the-sights column densities of O3,<br />
NO2, BrO, H2O, and O4 by Differential Optical<br />
Absorption Spectroscopy (DOAS). Radiative<br />
Transfer (RT) calculations, e.g., with the lab programmed<br />
Monte Carlo RT Model TRACY, are<br />
used to (a) simulate the measured quantities and<br />
(b) infer vertical profiles of O3, NO2, BrO and<br />
OClO concentrations using the Maximum a Posteriori<br />
(MAP) inversion technique. Subsequent<br />
measurements of the profiles of these species allow<br />
us to draw information on the temporal or<br />
spatial variations (or both) of these species and<br />
the related photochemistry.<br />
Results Balloon-borne UV/vis limb scattered<br />
measurements is tested against simultaneous measurements<br />
of the same parameters available from<br />
in-situ, or UV/vis/near IR solar occultation observations<br />
performed on the same payload. Reasonable<br />
agreement is found between (a) measured and<br />
RT calculated limb radiances and (b) inferred limb<br />
O3, NO2, and BrO (see Figure 2.20) and correlative<br />
profile measurements when properly accounting<br />
for all relevant atmospheric parameters (temperature,<br />
pressure, aerosol extinction, and major<br />
absorbing trace gases).<br />
Figure 2.20: Comparison of retrieved BrO profiles<br />
from mini-DOAS limb measurements (black line)<br />
and direct sunlight DOAS measurements (red<br />
line) during balloon ascent for an LPMA/DOAS<br />
balloon flight in Kiruna, March 24 th , 2004 with a<br />
priori profile in green.<br />
Additionally, scanning limb observations provide<br />
time-resolved profile information of radicals<br />
during sunset.<br />
Future work should concentrate on the application<br />
of the method on photochemical studies addressing<br />
the loss in stratospheric ozone at high,<br />
middle, and low latitudes, including the tropical<br />
tropopause region.<br />
Main publication Weidner, F., Development<br />
and Application of a Versatile Balloon-Borne<br />
DOAS Instrument for Skylight Radiance and Atmospheric<br />
Trace Gas Profile Measurements, Ph.D.<br />
thesis, <strong>Universität</strong> Heidelberg, Heidelberg, 2005.
2.3. RADIATIVE TRANSFER 49<br />
2.3.2 Oxygen A-band measurements for solar photon path length distribution<br />
studies<br />
Participating scientists Scholl, T., and K. Pfeilsticker<br />
Abstract High resolution spectroscopy of the oxygen A-band (760-780 nm) in zenith scattered<br />
skylight is a powerful tool to infer path length distributions (PDF) of solar photons transmitted to<br />
the ground. The relation between the different moments of the PDF (〈L〉, 〈L 2 〉) and the rescaled<br />
cloud optical depth τ ∗ is a strong indicator for 3D-effects on the radiative transfer (RT).<br />
Height [m]<br />
10000<br />
8000<br />
6000<br />
4000<br />
2000<br />
0 :0<br />
12:<br />
:5 :10 :15 :20 :25 :30 :35 :40 :45 :50 :55<br />
Time [UTC]<br />
-60 -50 -40 -30 -20 -10 0 10 20<br />
Reflectivity [dBZ]<br />
Figure 2.21: left panel: Measured radar reflectivities from KNMI 35 GHz Radar for May 22, 2003 UT 12:00-<br />
13:00, right panel: Mean cloud photon paths 〈Lc〉 as a function of effective cloud optical depth τ ∗ c . The black<br />
lines are predictions for different values of the Lévy exponent α ≤ 2. The 3 data clusters (color-coded blue,<br />
red and green) correspond to the 3 different probed cloud situations.<br />
Background Modelling RT in cloudy skies is<br />
one of the most challenging tasks in climate modelling.<br />
Photon PDF is commonly a hidden property<br />
of standard RT models, controlled by the<br />
spatial distribution of scattering and absorption.<br />
The distribution in the near infrared region is<br />
very representative for the shortwave region as<br />
a whole. The principle of equivalence allows to<br />
draw conclusions about radiative properties of<br />
the atmosphere from a photon PDF measured in<br />
one wavelength band, since the scattering properties<br />
of clouds and aerosols vary slowly and predictably<br />
with wavelength. Here the first two moments<br />
of the photon PDF of solar photons transmitted<br />
through cloudy skies to the ground are<br />
investigated. Combining the spectroscopic measurements<br />
with other cloud properties measured<br />
simultaneously by in-situ techniques during two<br />
campaigns allows to test the theory of anomalous<br />
photon diffusion through clouds.<br />
Methods and Results The multiple of different<br />
line strengths offered by the oxygen A-band<br />
implicitly provide direct information on the PDF<br />
of the photons transmitted to the ground. The<br />
spectral retrieval is solved by forward modelling<br />
the measured spectra with a prescribed photon<br />
PDF (usually a Γ function) at high spectral resolution.<br />
The free parameters of the PDF are<br />
then iteratively calculated by using a Nonlinear<br />
Least Square Fit leading to the searched quantities<br />
〈L〉 and 〈L 2 〉. Davis & Marshak [2002]<br />
inferred for the first moment of photon PDF:<br />
〈Lc〉/∆H = (1/2 · [1 + C(ɛ)] · τ ∗ ) α−1 . α is the so<br />
called Lévy index which ranges between 1 and 2.<br />
In particular, the value α = 2 is attained for a homogenous<br />
slab and for α < 2 for inhomogeneous<br />
slab. In Figure 2.21 the enhancement of the mean<br />
photon path length in the cloud (as a function of<br />
τ ∗ = τ · (1 − g)) and the received Lévy index is<br />
shown.<br />
The findings confirm the theory of anomalous<br />
photon diffusion through clouds and the predictions<br />
for the values in the path length to optical<br />
depth relations. It also provides further evidence<br />
that cloudy sky photon path length require consideration<br />
of non-classical photon transport theory.<br />
Funding comes through the AFO-2000 4D<br />
Clouds project (BMBF-07ATF24).<br />
Outlook Photon PDFs are a central concept of<br />
cloud RT modelling. For further improvements<br />
imaging DOAS spectroscopy at high temporal and<br />
spatial resolution is required.<br />
Main publication Scholl, T., Photon path<br />
length distributions for cloudy skies: Their first<br />
and second-order moments inferred from high resolution<br />
oxygen A-Band spectroscopy, PhD-Thesis,<br />
<strong>Universität</strong> Heidelberg, Heidelberg, in preparation.
50 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.3.3 Absolutely calibrated solar irradiance measurements<br />
Participating scientists Lindner, A., H. Bösch, A. Butz, M. Dorf, F. Weidner, and K. Pfeilsticker<br />
Abstract Absolutely calibrated solar irradiance spectra are measured from aboard the LPMA/<br />
DOAS balloon gondola at around 30 to 35 km altitude. After accounting for residual atmospheric extinction<br />
the findings are compared to previous observations and discussed with respect to implications<br />
for atmospheric photochemistry and the Earth’s climate.<br />
Figure 2.22: Ratio of solar irradiance spectra referenced to the solar spectrum of Kurucz et al. [1984] with<br />
recent updates of Fontenla et al. [1999] (MODTRAN 3.7) with (a) the present balloon borne measurement,<br />
(b) SORCE/SIM Harder et al. [2000], (c) SCIAMACHY/ENVISAT in channel 1, 2, 3, and 4 using the revised<br />
IUP-Bremen calibration.<br />
Background Solar radiation is the driving force<br />
for climate and thus for life on Earth. Evidently,<br />
the extraterrestrial solar irradiance Eo and its<br />
temporal evolution is of primary interest for atmospheric<br />
spectroscopy, photochemistry, climate<br />
and the solar cell industry as well. Although Eo is<br />
monitored by a large number of space-borne, airborne<br />
and ground-based instruments, to date, a<br />
consensus on Eo could only be achieved within few<br />
percents in the UV-A and visible spectral wavelength<br />
ranges mainly due to given problems with<br />
the absolute calibration of the radiation measurements<br />
and long term drifts of the various sensors.<br />
Funding The present work has been supported<br />
by ESA, BMBF, DLR and the European Union.<br />
Methods and results Here, direct Sun observations<br />
from aboard the LPMA/DOAS balloon<br />
payload are used to absolutely infer Eo in<br />
two wavelength bands in the UV/visible spectral<br />
range. After an on-ground spectro-radiometrical<br />
calibration has been performed for each balloon<br />
flight, the solar irradiance measurements are conducted<br />
at about 30 to 35 km balloon float altitude<br />
where the remaining atmospheric extinction<br />
is minimal and can be accounted for easily. Thorough<br />
tracking and removal of systematic errors<br />
results in high-accuracy measurement of the extraterrestrial<br />
solar irradiance.<br />
Comparison of our balloon borne data set with<br />
previous studies yields excellent agreement, see<br />
Figure 2.22, and suggests that, to date, the integrated<br />
Eo is uncertain by as much as 5 W/m 2<br />
in the respective wavelength range Gurlit et al.<br />
[2005].<br />
Outlook/Future work<br />
• Quality check of the standard Eo recommendation<br />
by further refinement of the calibration<br />
procedure<br />
• Long term validation, monitoring and recalibration<br />
of satellite-borne Eo measurements<br />
• Monitoring of natural solar variability<br />
Main publications Lindner A., Ballongestütze<br />
Messungen der extraterrestrischen spektralen solaren<br />
Irradianz, Diploma thesis, University of Heidelberg,<br />
Germany, 2005.
2.3. RADIATIVE TRANSFER 51<br />
2.3.4 Atmospheric detection of water dimers and their contribution to<br />
solar shortwave absorption<br />
Participating scientists Lotter, A., C . Peters, J. Schwärzle, and K. Pfeilsticker<br />
Abstract The cause of the water vapor continuum and possible contributions to it by water dimers<br />
is one of the most challenging question in atmospheric spectroscopy. Field measurements by means<br />
of active long-path differential optical absorption spectroscopy (DOAS) were performed to probe the<br />
atmosphere for water vapor continuum and dimer absorption.<br />
Figure 2.23: Absorption cross section for water monomer (WM) and water dimer (WD). Due to the overlap,<br />
WD absorption is masked by strong WM absorption, except for the three marked regions, where detection<br />
may be possible.<br />
Background Disagreement in Earth’s radiation<br />
budget between observations and radiative transfer<br />
models has been a major concern for several<br />
decades, as there exists a significant level of solar<br />
shortwave (SW) cloudy-sky absorption, commonly<br />
referred to as excess absorption, beyond the<br />
ability of any model to predict. Many attempts<br />
have been made to explain the observed excess of<br />
solar SW absorption, but all potential mechanisms<br />
on their own fall far short of explaining a possible<br />
absorption deficit as much as 30 W/m 2 . One<br />
mechanism of the required additional absorption<br />
was suggested to come from a combined contribution<br />
of the water continuum and water dimers<br />
(WD). WDs may also play an important role in atmospheric<br />
physics by e.g., initiating homogeneous<br />
nucleation of water and photo-chemistry by catalyzing<br />
chemical reactions (e.g., in the formation<br />
of H2SO4).<br />
Methods Possible atmospheric WD absorption<br />
was investigated by extreme long path (up to<br />
29 km) near ocean surface absorption measurements<br />
during 3 field campaigns conducted in<br />
Northern Germany in May 2002, France in June<br />
2003, tropical Brazil in Dec./Jan. 2004. Since the<br />
near-IR absorption spectrum of WD is predicted<br />
to largely overlap with that of WM, 3 almost interference<br />
free WD lines were selected for the study<br />
(see Figure 2.23). Here, the dependance of WD<br />
absorption on the WM pressure squared is used<br />
as an indicator for WD detection.<br />
Results Although a WD absorption line at<br />
13340 cm −1 was tentatively identified to be due to<br />
WD absorption (Pfeilsticker et al. [2003]), subsequent<br />
campaigns involving a larger WM concentration<br />
(e.g., in Brazil) could not confirm its existence.<br />
However, the latter measurements indicate<br />
a possible WD absorption band at 16312 cm −1 .<br />
Uncertainties, however, still remain in WD identification<br />
due to uncertainties in the predicted WD<br />
line position (up to 200 cm −1 ) and width (10–<br />
200 cm −1 FWHM). The latter being a function<br />
as to whether WD are truly bound, meta-stable<br />
or simply free pair states. WD detection is also<br />
hindered by uncertainties in the WM data bases<br />
in particular for the WM weak lines.<br />
Funding comes through the Deutsche ForschungsGemeinschaft<br />
(PF 384/1-2 and 2-3).<br />
Outlook More sensitive detection of WD absorption<br />
will require higher quality WM and WD<br />
data than existing.<br />
Main publication Lotter A., Field measurements<br />
of water continuum and water dimer absorption<br />
by active long-path Differential Optical<br />
Absorption Spectroscopy (DOAS), PhD thesis,<br />
<strong>Universität</strong> Heidelberg, Heidelberg, Germany, in<br />
preparation.
52 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
References<br />
Coheur, P.-F., Fally, S., Carleer, M., Clerbaux, C., Colin, R., Jenouvrier, A., Mérienne, M.-F., Hermans,<br />
C., & Vandaele, A. C. 2002. New water vapor line parameters in the 26000 - 13000 cm −1<br />
region. J. Quant. Spec. and Rad. Transf., 74, 493 – 510.<br />
Crewell, S., Bloemink, H., Feijt, A., García, S.G., Jolivet, D., Krasnov, O.A., van Lammeren, A.,<br />
Löhnert, U., van Meijgaard, E., Meywerk, J., Quante, M., Pfeilsticker, K., Schmidt, S., Scholl, T.,<br />
Simmer, C., Schröder, M., Trautmann, T., Venema, V., Wendisch, M., & Willén, U. 2004. The<br />
BALTEX Bridge Campaign - An integrated approach for a better understanding of clouds. Bull.<br />
Am. Met. Soc., 85, 1565 – 1584.<br />
Davis, A. B., & Marshak, A. 2002. Space-time characteristics of light transmitted by dense clouds: A<br />
Green function analysis. J. Atmos. Sci., 59, 2713 – 2727.<br />
Fally, S., Coheur, P.-F., Carleer, M., Clerbaux, C., Colin, R., Jenouvrier, A., Mérienne, M.-F., Hermans,<br />
C., & Vandaele, A. C. 2003. Water vapor line broadening and shifting by air in the 26000 -<br />
13000 cm −1 region. J. Quant. Spec. and Rad. Transf., 82, 119 – 131.<br />
Fontenla, J., White, O. R., Fox, P. A., Avrett, E. H., & Kurucz, R. L. 1999. Calculation of solar<br />
irradiances, I. Synthesis of the solar spectrum. Astrophys. J., 518, 480 – 500.<br />
Gurlit, W., Bösch, H., Bovensmann, H., Burrows, J. P., Butz, A., Camy-Peyret, C., Dorf, M., Gerilowski,<br />
K., Lindner, A., Noël, S., Platt, U., Weidner, F., & Pfeilsticker, K. 2005. The UV-A<br />
and visible solar irradiance spectrum: Inter-comparison of absolutely calibrated, spectrally medium<br />
resolved solar irradiance spectra from balloon-, and satellite-borne measurements. Atmos. Chem.<br />
Phys., 5, 1879 – 1890.<br />
Harder, J., Lawrence, G., Rottman, G., & Woods, T. 2000. The Spectral Irradiance Monitor (SIM)<br />
for the SORCE Mission. Proc. SPIE, 4135, 204 – 214.<br />
Kurucz, R. L., Furenlid, I., Brault, J., & Testerman, L. 1984. Solar Flux Atlas from 296 to 1300 nm.<br />
National Solar Observatory, Atlas No. 1. ftp://ftp.noao.edu/fts/fluxatl.<br />
Lindner, A. 2005. Ballongestütze Messungen der extraterrestrischen spektralen solaren Irradianz.<br />
Diploma thesis, University of Heidelberg, Heidelberg, Germany.<br />
Partridge, H., & Schwenke, D. W. 1997. The determination of an accurate isotope dependent potential<br />
energy surface for water from extensive ab initio calculations and experimental data. J. Chem. Phys.,<br />
106, 4618 – 4639.<br />
Pfeilsticker, K. 2005a. Collisional complexes, metastable, and stable complexes in the atmosphere, and<br />
their potential importance for the absorption of solar radiation. Gordon Research Conference on<br />
Radiation & Climate, Colby College, Waterville, ME, USA, July 24-29.<br />
Pfeilsticker, K. 2005b. Recent cloudy sky photon path <strong>pdf</strong> measurements from Heidelberg. 3rd I3RC<br />
Workshop, IFM Kiel, October 11-14.<br />
Pfeilsticker, K., Lotter, A., Peters, C., & Bösch, H. 2003. Atmospheric detection of water dimer via<br />
near-infrared absorption. Science, 300, 2078 – 2080.<br />
Pfeilsticker, K., Lotter, A., Boesch, H., & Peters, C. 2004. Collisional complexes, metastable and stable<br />
dimers in the atmosphere, and their potential importance for the absorption of solar radiation. 228th<br />
National ACS Meeting, Philadelphia, PA, USA, August 22-26.<br />
Rothman, L. S., Barbe, A., Benner, D. C., Brown, L. R., Camy-Peyret, C., Carleer, M. R., Chance,<br />
K., Clerbaux, C., Dana, V., Devi, V. M., Fayt, A., Flaud, J.-M., Gamache, R. R., Goldman, A.,<br />
Jacquemart, D., Jucks, K. W., Lafferty, W. J., Mandin, J.-Y., Massie, S. T., Nemtchinov, V.,<br />
Newnham, D. A., Perrin, A., Rinsland, C. P., Schroeder, J., Smith, K. M., Smith, M. A. H., Tang,<br />
K., Toth, R. A., Vander Auwera, J., Varanasi, P., & Yoshino, K. 2003. The HITRAN molecular<br />
spectroscopic database: edition of 2000 including updates through 2001. J. Quant. Spec. and Rad.<br />
Transf., 82, 5 – 44.
2.3. RADIATIVE TRANSFER 53<br />
Rothman, L. S., Jacquemart, D., Barbe, A., Benner, D. C., Birk, M., Brown, L. R., Carleer, M. R.,<br />
Chackerian Jr., C., Chance, K., Coudert, L. H., Dana, V., Devi, V. M., Flaud, J.-M., Gamache,<br />
R. R., Goldman, A., Hartmann, J.-M., Jucks, K. W., Maki, A. G., Mandin, J.-Y., Massie, S. T.,<br />
Orphal, J., Perrin, A., Rinsland, C. P., Smith, M. A. H., Tennyson, J., Tolchenov, R. N., Toth, R. A.,<br />
Vander Auwera, J., Varanasi, P., & Wagner, G. 2005. The HITRAN 2004 molecular spectroscopic<br />
database. J. Quant. Spec. and Rad. Transf., 96, 139 – 204.<br />
Scholl, T., Pfeilsticker, K., Davis, A.B., Klein Baltink, H., Crewell, S., Löhnert, U., Simmer, C.,<br />
Meywerk, J., & Quante, M. 2005. Path length distributions for solar photons under cloudy skies:<br />
Comparison of measured first and second moments with predictions from classical and anomalous<br />
diffusion theories. J. Geophys. Res., revised.<br />
Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />
skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />
Heidelberg, Germany.<br />
Weidner, F., Bösch, H., Bovensmann, H., Burrows, J.P., Butz, A., Camy-Peyret, C., Dorf, M.,<br />
Gerilowski, K., Gurlit, W., Platt, U., von Friedeburg, C., Wagner, T., & Pfeilsticker, K. 2005.<br />
Balloon-borne limb profiling of UV/vis skylight radiances, O3, NO2, and BrO: Technical set-up<br />
and validation of the method. Atmos. Chem. Phys., 5, 1409 – 1422.
2.4. DOAS TOMOGRAPHY GROUP 55<br />
2.4 DOAS Tomography Group<br />
Group members<br />
Dr. Irene Pundt, head of group<br />
Dipl. Met. Claudia Hak, PhD student<br />
Dipl. Phys. Andreas Hartl, PhD student<br />
Dipl. Phys. Klaus-Peter Heue, PhD student<br />
Dipl. Phys. Kai-Uwe Mettendorf, PhD student<br />
MPhys. Denis Pöhler, PhD student<br />
Bing-Chao Song, Research assistant<br />
Alexander Stelzer, Diploma Student<br />
Abstract The DOAS tomography group is a junior research group of the BMBF atmospheric research<br />
program 2000 (AFO 2000). The group started in August 2000 as part of the research group<br />
Atmospheric Physics of Prof. Dr. Ulrich Platt. DOAS Tomography is a novel technique developed<br />
for spatially resolved measurements of trace gas distributions. In the framework of the Tom-DOAS<br />
project, first tomographic measurements from ground and aircraft were carried out. New instruments<br />
were developed and the method was validated during an indoor campaign. In addition computer tools<br />
were developed to optimise instrumental configurations and to invert the measurements. The quality<br />
of the localization and quantification of atmospheric emission plumes was estimated by numerical<br />
studies.<br />
Figure 2.24: Left: Groundbased tomographic setup using Longpath DOAS instruments. From each<br />
telescope (houses) light beams are directed towards the four retro reflector arrays (yellow circles). The<br />
light travels back to the initial telescopes, where it is spectrally analysed. Right: Airborne tomographic<br />
measurements. Here the sunlight is captured by several telescopes from different directions. Using<br />
measurements from different aircraft positions, a large number of intersecting light paths can be<br />
achieved. The resulting trace gas column densities are subsequently inverted to obtain 2D-distributions<br />
of trace gas concentrations.<br />
Overarching topic and Background<br />
Air pollution due to anthropogenic trace gas emissions can cause serious environmental and medical<br />
problems. For example, for human beings air pollutants like ozone, nitrogen dioxide (NO2), sulphur<br />
dioxide (SO2) and benzene cause respiratory diseases. The predictability of their spatial distributions<br />
is subject to numerous uncertainties. For continuous concentration records some wide meshed networks<br />
of in situ measurement stations were installed. However, single-point measurements are often not<br />
sufficient in order to explain differences between models since small-scale characteristics of the models<br />
are not taken into account. In contrast, spatially resolved measurements can provide this type of<br />
information.<br />
Differential optical absorption spectroscopy (DOAS) is a path-integrating measurement technique<br />
for atmospheric trace gases like ozone, nitrogen oxides, SO2, halogen oxides (BrO, IO, OClO) and many<br />
hydrocarbons. For DOAS, a continuous artificial or natural light source (sun, moon, ) is used. Because<br />
of the characteristic absorption features it is possible to measure several trace gases simultaneously<br />
(e.g. NO2, SO2, HCHO, HONO, and ozone in the UV region). In a typical so-called long-path (LP)<br />
setup a beam of white light, emitted by a telescope, travels through the atmosphere to a retro-reflector<br />
and back to the telescope. Absorption patterns in the received light allow determining the column<br />
density (the integrated concentration) of the trace gases along the light path.<br />
Our DOAS tomography setups consist of a number of intersecting light paths (left figure). Column<br />
densities of one or several trace gases measured by the DOAS technique along the light paths are
56 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
inverted to obtain concentration distributions by tomographic techniques.<br />
In contrast, the Airborne Multi AXis (AMAX) DOAS instrument measures passively the sunlight<br />
which is scattered in the earths atmosphere and/or reflected on the ground (right figure). Several small<br />
telescopes are used which are directed in various directions and which capture the light simultaneously.<br />
Each measurement provides results from several different paths throughout the atmosphere. As the<br />
aircraft moves on from measurement to measurement, data of many intersecting light paths is recorded.<br />
First tomographic line-integrating indoor measurements of 2D trace gas distributions were realized<br />
in the 1990s by using open-path Fourier infrared absorption spectroscopy. There have been improvements<br />
in speed and spatial resolution since, but all experiments have been restricted to the laboratory<br />
environment so far.<br />
Main methods<br />
During the last five years, for the first time DOAS two-dimensional tomographic experiments using a<br />
larger number (10-90) of intersecting light paths have been carried out (e.g., Pundt [2005b]). At the<br />
ground, long path active instruments were used to measure 2D emission plumes from road traffic or<br />
horizontal distributions of trace gases (e.g. Pundt et al. [2005c], Lösch [2001], Kunz [2001], Bäuerle<br />
[2004], Rippel [2005], Poehler et al. [2005]). Instruments which are more suitable for tomographic<br />
applications were developed (Pundt & Mettendorf [2005], Mettendorf [2005]) and the reconstruction<br />
methods were validated during an indoor campaign (Mettendorf et al. [2005]). From aircraft, passive<br />
instruments were used to measure 2D distributions of a power plant emission plume (Pundt et al.<br />
[2005a], Heue et al. [2005]). The quality of the localization and quantification of atmospheric emission<br />
plumes has been estimated by means of numerical studies (Knab [2004], Laepple et al. [2004], Hartl<br />
et al. [2005a]). In addition, the group participated in two measurement campaigns in the Po-Valley<br />
region in the framework of the EU FORMAT project (e.g., Hak et al. [2005]).<br />
Subprojects<br />
Groundbased DOAS tomography<br />
Airborne DOAS tomography<br />
Theoretical studies<br />
FORMAT: Formaldehyde as a Tracer of Photo oxidation in the Troposphere (EU project)<br />
Funding<br />
BMBF (TomDOAS)<br />
EU (FORMAT)<br />
Cooperation<br />
University of Bremen<br />
FZK <strong>Karls</strong>ruhe (IMK <strong>Karls</strong>ruhe)<br />
IFU Garmisch-Partenkirchen (IMK <strong>Karls</strong>ruhe)<br />
NILU (Norway)<br />
IASB (Belgium)<br />
PSI (Switzerland)<br />
Anhui <strong>Institut</strong>e (Hefei, China)<br />
Publications<br />
Peer reviewed Publications<br />
1. Bruns et al. [2004]<br />
2. Fix et al. [2005]<br />
3. Hak et al. [2005]<br />
4. Heckel et al. [2005]<br />
5. Heue et al. [2005]<br />
6. Laepple et al. [2004]<br />
7. Pundt & Mettendorf [2005]
2.4. DOAS TOMOGRAPHY GROUP 57<br />
8. Pundt [2005b]<br />
9. Pundt et al. [2005c]<br />
10. von Friedeburg et al. [2005]<br />
11. Wang et al. [2005b]<br />
Other Publications<br />
1. Bruns et al. [2005]<br />
2. Hartl et al. [2005b]<br />
3. Hartl et al. [2005a]<br />
4. Heue et al. [2004]<br />
5. Poehler et al. [2005]<br />
6. Pundt et al. [2005b]<br />
7. Wang et al. [2005a]<br />
Doctoral Thesis<br />
1. Heue [2005]<br />
2. Mettendorf [2005]<br />
Diploma Thesis<br />
1. Stelzer [2005]<br />
2. Rippel [2005]<br />
3. Knab [2004]<br />
4. Bäuerle [2004]<br />
Invited talks<br />
1. Pundt [2005a]<br />
2. I. et al. [2005]
58 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.4.1 Intercomparison of ambient in-situ Formaldehyde Measurements in<br />
urban Air<br />
Participating scientist Claudia Hak et al.<br />
Abstract An intercomparison of in-situ formaldehyde (CH2O) measurements, including four different<br />
techniques, is presented. Formaldehyde levels between 1 and 13 ppbv were measured in an urban<br />
environment in Milano, Italy. By using only point measurement methods, it was ensured that all<br />
instruments probed the same air volume.<br />
Figure 2.25: Fractional difference histograms, calculated relative to a reference Hantzsch instrument<br />
Background Previous intercomparisons revealed<br />
significant disagreement among the techniques<br />
used. However, there was no general pattern<br />
in the deviations. Since formaldehyde is an<br />
important intermediate in the oxidation of VOCs<br />
and a source of HOx radicals, it was a major<br />
objective of the FORMAT (FORMAldehyde as<br />
a Tracer of photooxidation in the troposphere)<br />
project to intercompare the different available<br />
measurement techniques. These involved the wet<br />
chemical Hantzsch method (five instruments), the<br />
DNPH method with HPLC separation, DOAS<br />
and FTIR. For the optical methods DOAS and<br />
FTIR, White-multireflection systems were used.<br />
In contrast to long path integrating optical methods<br />
which average horizontally and vertically,<br />
they measure the absorption of trace gases along<br />
a short base path of a few metres.<br />
Funding FORMAT, European Union<br />
Methods and results Two methods were applied<br />
for the intercomparison of the measurement<br />
results. Firstly, an orthogonal regression analysis<br />
was performed, comparing the individual results<br />
of all instrument pairs with each other. The<br />
correlation analysis showed a very good agreement<br />
among the Hantzsch results, however the<br />
slopes and intercepts from the regression analysis<br />
revealed some systematic differences. The optical<br />
techniques showed larger scattering. The second<br />
method was the analysis of fractional differ-<br />
ences, i.e. the difference between the results of<br />
each instrument and an (arbitrarily chosen) reference<br />
instrument according to δ=([CH2O]instr.-<br />
[CH2O]ref.)/[CH2O]ref.. Because of its long and<br />
continuous time series, the BUW Hantzsch results<br />
were chosen as the reference. The figure depicts<br />
the results of the fractional difference analysis.<br />
The nearly collocation of mode, median and average<br />
for most distributions suggests symmetry<br />
in the distribution and therefore mostly random<br />
differences. In summary, a ±11% agreement was<br />
found among the Hantzsch results. The observed<br />
discrepancies were partly attributed to different<br />
calibration standards. The agreement of the two<br />
optical methods was within 5%, which is within<br />
the uncertainties of the UV and IR absorption<br />
cross-sections (both 5%). Hantzsch and spectroscopic<br />
techniques agreed within 15%. DNPH results<br />
were generally lower than the measurements<br />
of the continuous techniques by up to 25%. A<br />
more detailed description of the methods as well<br />
as the discussion of the problems and the uncertainties<br />
of the Hantzsch and the optical methods<br />
can be found in Hak et al. [2005].<br />
Outlook/Future work This work is finished.<br />
The discrepancies in liquid calibration standards<br />
of Hantzsch instruments form a task which is currently<br />
under investigation by other groups.<br />
Main publication Hak et al. [2005]
2.4. DOAS TOMOGRAPHY GROUP 59<br />
2.4.2 Trace gas distributions from long-path DOAS measurements<br />
Participating scientist Andreas Hartl<br />
Abstract The possibility to retrieve 2D trace gas concentration fields from a limited number of longpath<br />
DOAS measurements was studied theoretically. Using a discrete approach it was found that the<br />
reconstruction can be tremendously improved by using optimal parametrisation of the unknown field,<br />
but its resolution is restricted by the number of light paths.<br />
100<br />
y<br />
0<br />
x<br />
100<br />
1<br />
conc.<br />
0.5<br />
0<br />
50<br />
x<br />
100<br />
50 y<br />
100<br />
conc.<br />
0.5<br />
Figure 2.26: (Left) Geometric arrangement with 3 telescopes and 36 light paths, (centre) 2D test<br />
distribution of 4 Gaussian concentration peaks and (right) its reconstruction by averaging over several<br />
bilinear discretisation grids.<br />
Background Experiments designed to give information<br />
on the spatial distribution of concentration<br />
fields are limited to certain scales and, if there<br />
are not enough measurements, they are sometimes<br />
hard to interpret. Point measurements are subject<br />
to all sorts of flucuations, path integrating<br />
absorption measuremts only provide average concentrations.<br />
While special processes, like plume<br />
development from a single point source or pollution<br />
in a street canyon, have been studied intensively,<br />
there is only little data available for others,<br />
e.g. distributions over a city region.<br />
This work examines 2D retrieval of concentration<br />
fields from ground-based DOAS measurements<br />
with artificial light sources on scales of a<br />
few km by techniques very similar to the ones used<br />
in conventional computerised tomography. These<br />
experimental concentration maps eventually can<br />
be used for the validation of chemical transport<br />
models, escpecially in cases where different model<br />
scales play a role.<br />
Funding BMBF through project 07 ATC-03<br />
(Young researchers fellowship program for research<br />
groups, AFO 2000-C).<br />
Methods and results The unknown concentration<br />
field is expressed in terms of a limited<br />
number of “basis” functions with local support<br />
and the discrete set of parameters is fit to the<br />
measurement data using a least squares principle.<br />
For the box and bilinear basis considered here, the<br />
1<br />
0<br />
50<br />
x<br />
100<br />
50 y<br />
100<br />
parameters represent values in the boxes and on<br />
the nodes of the discretisation grid, respectively.<br />
In the simulations, Gaussian peaks of varying half<br />
width serve as test distributions, motivated by the<br />
semi-empirical approach that describes turbulent<br />
transport and advection in the atmosphere by a<br />
diffusion model.<br />
We found that formulation of the problem, i.e.<br />
its parametrisation in terms of type and number<br />
of basis functions, plays a paramount role for the<br />
reconstruction quality. It turns out that the narrower<br />
the peaks, the finer the discretisation grid<br />
can be chosen, leading to systems with as many as<br />
four times unknowns than knowns - provided additional<br />
(physical or ad hoc) information is added.<br />
Bilinear function allow not only better discretisation,<br />
but also improved inversion of the problem<br />
and taking into account different discretisation<br />
grids can further reduce reconstruction errors.<br />
Reconstruction quality strongly depends on<br />
the light path geometry, Fig. 2.26 shows an example<br />
for one of the geometries exmamined.<br />
Outlook/Future work Application to high<br />
resolution model data for a heavily polluted<br />
area over Hannover, reconstruction from measurements<br />
in Heidelberg, further theoretical work on<br />
the estimation of the reconstruction error field,<br />
the inclusion of point measurements and the 3D<br />
case.<br />
Main Publication Hartl et al. [2005a]
60 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.4.3 Airborne measurements of the CH2O and NO2 distributions in the<br />
Po basin<br />
Participating scientists Klaus-Peter Heue, Ping Wang 2 and Irene Pundt<br />
2 <strong>Institut</strong> <strong>für</strong> Umweltphysisk, <strong>Universität</strong> Bremen<br />
Abstract During two FORMAT campaigns the Airborne Multi AXis DOAS (AMAXDOAS) instrument<br />
was used to determine the two dimensional formaldehyde and nitrogen dioxide distributions<br />
around Milano. Vertical distributions were retrieved from observed slant column densities from the<br />
spectra of six telescopes directed at different viewing angles.<br />
Figure 2.27: Formaldehyde average mixing ratio at 0-1000 m altitude along the flight track<br />
Background One of the major aims of the<br />
FORMAT project (FORMAldehyde as a tracer<br />
of photooxidation in the Troposphere) was to<br />
observe the different sources of photooxidating<br />
traces gases in the atmosphere. Fossil fuel combustion<br />
is known to be a source of NOx and<br />
VOCs. Other source of VOCs are biogenic emissions<br />
and natural fires. Formaldehyde is an important<br />
intermediate in the oxidation of VOCs.<br />
The AMAXDOAS observation results in differential<br />
slant column densities (dSCDs) for each of<br />
the ten telescopes. For the reference location the<br />
observed dSCD vanishes. In total 20 flights were<br />
performed during two campaigns in 2002 and 2003<br />
and the slant column of HCHO, NO2, O4 and<br />
SO2 were retrieved.<br />
Funding FORMAT, DOAS Tomography,<br />
SCIAMACHY validation<br />
Methods and results The observed signal of<br />
passive DOAS systems like the AMAXDOAS is<br />
strongly influenced by the aerosol content. Based<br />
on the O4 observations of all ten telescopes the<br />
aerosol content can be approximated for several<br />
measurement locations including the reference.<br />
The different telescopes have different sensibilities<br />
for O4 absorptions if the aerosol content<br />
changes. Using a radiative transfer model we<br />
modelled the O4 SCDs for several aerosol contents<br />
and compared them with the observations.<br />
The aerosol content affects the sensitivity of the<br />
different lines of sight. Based on the observations<br />
form five downward directed lines of sight<br />
the CH2O vertical columns along the flight can<br />
be deduced. However, the measurement principle<br />
requires some approximations about the CH2O<br />
concentration at the reference location. Assuming<br />
a standard profile, based on independent measurements,<br />
an average mixing ratio for the lowest 1000<br />
m can be retrieved. Figure 2.27 shows the average<br />
CH2O mixing ratio distribution around Milano<br />
on 16/08/2002. On this day the wind blew<br />
from south east, therefore in the north west of the<br />
town an enhanced HCHO concentration is observed.<br />
The emission plume of Milano was found<br />
to be 20 km wide and the net CH2O production<br />
is estimated at 0.6 tons/hour.<br />
Outlook/Future work Publication is in<br />
preparation.<br />
Main publications Heue [2005]
2.4. DOAS TOMOGRAPHY GROUP 61<br />
2.4.4 Development of a Multibeam instrument for simultaneous measurements<br />
along multiple light paths<br />
Participating scientists Kai Uwe Mettendorf and Irene Pundt<br />
Abstract Long path DOAS tomography uses multiple Long path DOAS instruments and intersecting<br />
light paths to retrieve the concentration distributions of certain trace gases. For these measurements<br />
a new DOAS instrument was developed. Three instruments were build.<br />
Figure 2.28: Instrumental setup of the entire Multibeam system (including, A, telescope; B, lamp<br />
housing; C, mode mixer; D, spectrograph; E, CCD detector; F, stepper motor controller; G, mirror<br />
tower with four mirror units; H, rotating disk retroreflector; I, retroreflector array at a distance<br />
between 500 and 5000 m). The distance between the telescope and the mirror tower is usually 10-15<br />
m. The distance between the rotating retroreflector and the tower is also 10-15 m. The rotating disk<br />
can be placed close to the telescope.<br />
Background Conventional Long-path DOAS<br />
Instruments emit a single light beam. For two<br />
dimensional DOAS-tomographic-measurements,<br />
however at least 10-40 light paths are necessary.<br />
The Multibeam DOAS instrument, which emits<br />
one to six light paths was developed for this purpose.<br />
Funding DOAS Tomography (BMBF)<br />
Methods and results A novel long-path differential<br />
optical absorption spectroscopy (DOAS)<br />
apparatus for measuring tropospheric trace gases<br />
the ”Multibeam” instrument was developed. It is<br />
the first active DOAS device that emits several<br />
light beams simultaneously through only one telescope<br />
and with only one lamp as a light source,<br />
allowing simultaneous measurement along multiple<br />
light paths. In contrast to conventional<br />
DOAS instruments, several small mirrors are positioned<br />
near the lamp, creating multiple virtual<br />
light sources that emit one light beam each in one<br />
specific direction. The possibility of error due to<br />
scattering between the light beams is negligible.<br />
The trace-gas detection limits of NO2, SO2, O3,<br />
and H2CO are similar to those of the traditional<br />
long-path DOAS instrument. However, the received<br />
light intensity is reduced by a factor of 3<br />
compared to a traditional long-path DOAS instrument<br />
with a similar main mirror.<br />
Main publication Pundt & Mettendorf [2005],<br />
Mettendorf [2005]
62 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.4.5 An Indoor Test Campaign of the Tomography Long Path Differential<br />
Optical Absorption Spectroscopy (DOAS) Technique<br />
Participating scientists Kai Uwe Mettendorf, Andreas Hartl and Irene Pundt<br />
Abstract For the validation of the LP-DOAS-tomography method and the test of the Multibeam<br />
DOAS instrument an indoor validation campaign was performed. Known concentration distributions<br />
were successfully measured by 39 intersecting light paths and reconstructed using the SIRT-method.<br />
Figure 2.29: Reconstruction of a concentration distribution by SIRT on a 12×12 pixel grid and with<br />
additional grid shifting. The upper panel shows the original concentration distribution, the lower left<br />
panel the result from modelled column densities and the lower right panel the result from measured<br />
column densities.<br />
Background Long path DOAS tomography is<br />
a novel application of the DOAS-method which<br />
was not been validated before.<br />
Funding DOAS Tomography (BMBF)<br />
Methods and results In this study the twodimensional<br />
long path DOAS tomography measurement<br />
technique was validated by an indoor experiment<br />
with well-known concentration distributions.<br />
The experiment was conducted over an area<br />
of 10m×15m using one and two cylindrical containers<br />
of diameter 2 m, respectively, filled with<br />
NO2. The setup was realized with three of the recently<br />
developed Multibeam instruments (Pundt<br />
and Mettendorf, 2005), which allow the simultaneous<br />
measurement along at least four light paths<br />
each. The configuration consisted of twelve simultaneous<br />
light beams, 39 horizontal light paths in<br />
total, and 16 different cylinder positions inside the<br />
field. It was found that for the discretization and<br />
inversion technique shown here reconstructions of<br />
the concentration distributions from experimental<br />
data agree well with simulated reconstructions. In<br />
order to draw conclusions for atmospheric applications,<br />
numerical studies including instrumental errors<br />
were carried out. It was concluded that with<br />
the presented measurement setup it should be possible<br />
to measure and reconstruct one or two NO2<br />
plumes of 600 m diameter and average concentrations<br />
above 4.2 ppbv each, to a scale of 13.5 km 2 .<br />
Theoretical investigations show that it should be<br />
possible to localize and quantify 600 m diameter<br />
plumes of SO2 > 1.5 ppbv, H2CO > 6.3 ppbv,<br />
HONO > 3.2 ppbv, and O3 > 46.2 ppbv.<br />
Main publication Mettendorf [2005]
2.4. DOAS TOMOGRAPHY GROUP 63<br />
2.4.6 2D and 3D tomographic LP-DOAS measurements of trace gas distributions<br />
in Heidelberg over an area of 4 ∗ 4 km 2<br />
Participating scientists Denis Poehler, Alexander Stelzer, Irene Pundt<br />
Abstract A configuration of three Multibeam LP-DOAS Instruments and 20 different light paths<br />
to retro reflector arrays was established for long term 2D and 3D measurements of NO2, SO2, O3,<br />
HCHO, and HONO over an area of a 4 ∗ 4 km 2 above the city centre of Heidelberg.<br />
Figure 2.30: 3 Dimensional view on all light paths of the measurement over an area of 4 ∗ 4 km 2 with<br />
three telescope locations: IUP, SAS and HD-Druck.<br />
Background LP-DOAS (Long Path Differential<br />
Absorption Spectroscopy) is a well known<br />
technique for measuring average concentrations of<br />
tropospheric trace gases along a light path extending<br />
between a telescope and a retro reflector. But<br />
single path measurements are often not sufficient<br />
(as well as single point measurements), if smallscale<br />
variations exist or transport is important.<br />
To obtain informations of the dispersion, it is necessary<br />
to measure along a couple of light paths.<br />
The development of the ”Multibeam LP-DOAS<br />
telescope” (Pundt and Mettendorf, 2005), allows<br />
the measurement along up to 6 light paths simultaneously.<br />
With the suitable combination of<br />
two or more Multibeam LP-DOAS telescopes and<br />
the use of tomographic reconstruction techniques<br />
good quality 2D and 3D reconstructions of the<br />
measured trace gases can be achieved.<br />
Funding German Ministry of Research and Education<br />
, AFO 2000-C, project 07 ATC-03<br />
Methods and results The experimental setup<br />
consists of 3 Multibeam telescopes located on top<br />
of high buildings in the city (IUP, HD-Druck and<br />
SAS) and 20 retro reflector arrays. This work focuses<br />
on the one hand on the telescope location<br />
HD-Druck, where a Multibeam Instrument was<br />
installed and modified, to allow automatic measurements<br />
from this place.<br />
Each of the three telescopes uses a Xe-Arc lamp as<br />
light source, which creates up to 6 parallel light<br />
beams using different mirrors. Each light beam<br />
can be redirected to different retro reflector arrays<br />
which reflect parts of the light back into the<br />
telescope. The received light is measured with a<br />
Czerny Turner Spectrograph and contains information’s<br />
of the trace gas absorptions. With the<br />
measurement between 285 nm and 365 nm and<br />
the use of the DOAS technique reconstruction of<br />
NO2, SO2, O3, HCHO, and HONO are made<br />
along each light path.<br />
During the first measurements it was mostly impossible<br />
to run all three telescopes simultaneously,<br />
due to many breakdowns of the sensitive experimental<br />
setup. But since simultaneous measurements<br />
of all light paths are necessary for tomographic<br />
inversions, the hardware was modified and<br />
new controller software was coded to improve the<br />
stability. First simultaneous measurements were<br />
performed in September 2005, but are not completely<br />
analysed yet.<br />
Outlook/Future work The system will be run<br />
continuously over a time scale of several months.<br />
For the periods of simultaneous measurement<br />
data, 2 dimensional trace gas distributions will<br />
be reconstructed.<br />
Main publication Poehler et al. [2005]
64 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.4.7 Two-dimensional measurement of motorway emission plumes<br />
Participating scientist Irene Pundt, Kai Uwe Mettendorf<br />
Abstract A first Long-path Tom-DOAS experiment was carried out in April/May 2001 next to<br />
the German motorway A656 (between Heidelberg and Mannheim), as part of the BAB II campaign<br />
(Fiedler et al., 2001). From the measurements along 16 different light paths vertical profiles on both<br />
sides of the motorway as well as two-dimensional maps of the NO2, SO2 and ozone concentration<br />
distributions could be derived. Emission factors were calculated and compared to model simulations.<br />
Figure 2.31: Left: Tomographic setup used during a motorway emission campaign. From each telescope<br />
one light beam is directed successively towards the eight retro reflectors (circles). Right: NO2<br />
motor vehicle emission plume perpendicular to a motorway (in ppbv). Black bar: Location of the<br />
motorway, chequered area: Experiment towers, wind direction: coming from the left.<br />
Background Traffic emissions are among the<br />
major sources for anthropogenic air pollution.<br />
Volatile compounds and nitrogen oxides (NOx)<br />
are, besides others, important components of<br />
these emissions. Vehicle emission factors are generally<br />
estimated by means of dynamometric test<br />
measurements, but they may change under real<br />
world conditions. Therefore, a couple of field studies,<br />
mostly performed inside tunnels, have been<br />
conducted. However, the air flow through tunnels<br />
is influenced by the moving cars, causing an artificial<br />
wind, which changes the traffic emissions. A<br />
more realistic approach to evaluate emission factors<br />
is to carry out measurements at an open road.<br />
Knowledge of vertical profiles on both sides of the<br />
road is necessary to calculate emission rates (in<br />
molecules s −1 m −1 ). Taking 2D images of the<br />
emission plume perpendicular to the line source<br />
can provide even more information than emission<br />
rates. 2D images can be used to validate 2D<br />
dispersion models, or in the case of short lived<br />
species, to validate 2D chemical transport models.<br />
Funding TOMDOAS (BMBF)<br />
Methods and results The tomographic arrangement<br />
consisted of two long path telescope<br />
sites (one at each side of the motorway), and eight<br />
retro reflector arrays (four on each side at different<br />
heights). Each of the telescopes emitted<br />
one light beam, which was successively directed to<br />
the different retro-reflectors. Altogether 16 different<br />
light paths were realised. 2D NO2 concentration<br />
distributions perpendicular to the motorway<br />
were derived for several time spans (right figure).<br />
Concentrations on the left-hand side of the figure<br />
represent the NO2 background abundance and<br />
the right-hand side the background concentration<br />
plus emissions. For the inversion, an algebraic reconstruction<br />
technique was used in combination<br />
with bilinear basis functions describing the distribution.<br />
The derived emission plumes are, within<br />
the errors, in good agreement with model expectations.<br />
To our knowledge, these are the first measurements<br />
of two dimensional sections of an emission<br />
plume from a line source. Using multibeam<br />
telescopes will increase the time resolution of the<br />
images from hours to minute ranges in the future.<br />
Outlook/Future work SO2 and HCHO emission<br />
rates are currently evaluated and compared<br />
to model simulations. Ozone distributions seem to<br />
be not consistent with model expectations. Further<br />
work is needed to understand the discrepancies.<br />
Main publication Pundt et al. [2005c], Laepple<br />
et al. [2004], Mettendorf [2005]
2.4. DOAS TOMOGRAPHY GROUP 65<br />
2.4.8 Two dimensional concentration distributions of a NO2 Emission plume<br />
from a point source derived by Airborne DOAS Tomography<br />
Participating scientists Irene Pundt, Klaus-Peter Heue, Bing-Chao Song<br />
Abstract First airborne DOAS tomography measurements of two-dimensional concentration crosssections<br />
of a plume from a point source have been carried out. The measurements were performed<br />
with an AMAXDOAS (Airborne Multi-AXis Differential Optical Absorption Spectroscopy) instrument<br />
onboard a small aircraft during the second campaign of the European FORMAT project in August /<br />
September 2003.<br />
Figure 2.32: Left: Lines of sight of the flight track as function of the geographic position of the Sermide<br />
power plant plume. X is the latitudinal, y the longitudinal and z the vertical direction. For clearness,<br />
only the downward looking viewing directions are shown neglecting the scattering of light. The colors<br />
of the lines indicate the NO2 slant column densities along each of them. Right: NO2 2D mixing ratio<br />
distributions of the Sermide plume after tomographic inversion, first pass (distance from the plant: 5<br />
km).<br />
Background The focus of this study is the first<br />
application of the Airborne DOAS Tomography<br />
technique to provide concentration distributions<br />
of NO2 along cross sections of a plume from a<br />
point source. A technique to formulate a two dimensional<br />
inversion problem with weighting matrices<br />
from single scattering radiative transfer simulations,<br />
which can be used for tomographic inversions,<br />
is presented.<br />
Funding TomDOAS (BMBF), FORMAT (EU)<br />
Methods and results As part of the second<br />
campaign of the European FORMAT project<br />
(FORMAldehyde as a tracer of photo oxidation<br />
in the Troposphere), the instrument was installed<br />
on board a Partenavia PA 68 aircraft. During one<br />
occasion, on 26 September 2003, it was possible to<br />
derive the information for two-dimensional reconstructions<br />
of an emission plume of a point source.<br />
Three over flights were performed across the emission<br />
plume of the NO2 emitting Sermide power<br />
plant, located at 45.02 degree N 11.25 degree E.<br />
Three reconstructions have been performed, one<br />
for each overpass. It is assumed that the plume<br />
has not changed during the course of the measurement.<br />
Therefore 5, 6 and 9 aircraft positions, re-<br />
sulting in 50, 60 and 90 lines of sight were included<br />
for the 1st, 2nd and 3rd overpass, respectively (left<br />
figure). For each overpass, the area of interest<br />
is divided into rectangular boxes with 16 vertical<br />
segments of 133 m height and horizontal segments<br />
of 1.5 km length. For each inversion, the weighting<br />
matrix was calculated for the respective 2D<br />
grid. Then the inversion is performed using the<br />
Simultaneous Iterative Reconstruction Technique<br />
(SIRT) method. The right Figure presents the resulting<br />
NO2 mixing ratio maps for the first overpass.<br />
Interestingly the first and the third overpass,<br />
which were conducted very close by, show<br />
similar shapes, indicating only small changes of<br />
the plume during the 12 minutes flight interval.<br />
From this finding we conclude that the quality of<br />
the reconstruction is reproducible and consistent.<br />
NOX emissions of 4.1-9.6 10 24 molec s −1 were<br />
derived, in agreement with the information given<br />
by the power plant company.<br />
Outlook/Future work The analysis of the<br />
FORMAT flights is ongoing.<br />
Main publication Pundt et al. [2005a], Heue<br />
[2005]
66 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.4.9 Development of a computer tool for the inversion and optimization<br />
of airborne tomographic DOAS measurements (Tomolab2)<br />
Participating scientist Bing-Chao Song, Andreas Hartl and Irene Pundt<br />
Abstract The tomographic DOAS software project Tomolab [Laepple et al., 2004] is further developed<br />
for Airborne Multi Axis DOAS (AMAXDOAS) measurements. With its ability to include<br />
scattered light paths it can be used to optimize airborne measurements, optimize measurement geometries<br />
and for the reconstruction of 2D/3D concentration fields.<br />
Figure 2.33: Flight track with ground-reflected light paths (left), 2D single scattering light path<br />
geometry and reconstruction (right) in Tomolab2.<br />
Background The Tomolab software was originally<br />
created especially for ground-based active<br />
measurements, i.e. light paths clearly defined by<br />
source and reflector. While it is efficient for analyzing<br />
and displaying simple geometries, it does<br />
not include scattering processes, neither in its<br />
graphics nor in its inversion part. Tomolab was<br />
designed as a Windows project and runs on personal<br />
computers only. The enhanced version Tomolab2<br />
removes the dependency of the Windows<br />
system and, for intensive calculations, can be run<br />
on any UNIX workstation. Very flexible scripting<br />
support simplifies case studies for different geometric<br />
settings and atmospheric conditions.<br />
Funding DOAS Tomography, BMBF<br />
Method Single scattering processes, usually<br />
dominating the atmospheric radiative transfer,<br />
are simulated by defining a group of partial light<br />
paths which all enter the telescope and add up to<br />
the same measurement signal. Their individual<br />
contributions to the total absorption captured by<br />
the telescope are weighted by their relative light<br />
intensities from radiative transfer calculation for<br />
the layer where the scattering event took place.<br />
We finally obtain box air mass factors (AMFs)<br />
for cases where single scattering dominates. Measurements<br />
where multiple scattering is not negligi-<br />
ble can also be simulated and reconstructed, but<br />
the corresponding 2D or 3D box AMFs have to<br />
be calculated by suitable radiative transfer models.<br />
The modular structure of Tomolab2 makes<br />
exchange of platform dependent code easier. The<br />
visualization part is currently implemented for the<br />
Windows system. The scripting support layer for<br />
Windows is implemented using the so called COM<br />
technique. Essential and common functions are<br />
encapsulated into binary components to ensure<br />
the stability of the project. Varying case studies<br />
can be done by scripting components without<br />
modifying Tomolab2’s code.<br />
Results The Tomolab2 project was developed<br />
for passive airborne DOAS measurements and<br />
designed aiming at a flexible and platformindependent<br />
structure. 2D box AMFs have been<br />
calculated for lightly polluted scenarios and compare<br />
well with those from a radiative transfer<br />
model. The program also has been tested on<br />
UNIX platforms. Thanks to its modular structure,<br />
Tomolab2 can easily be updated and maintained.<br />
Outlook/Future work 3D reconstruction.<br />
Embedding of radiative transfer models for operational<br />
usage.
2.4. DOAS TOMOGRAPHY GROUP 67<br />
References<br />
Bäuerle, A. 2004. Messung von Spurenstoffverteilungen in Mailand mit Hilfe eines Multistrahl-<br />
Langpfad Teleskops. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Bruns, M., Buehler, S. A., Burrows, J. P., Heue, K.-P., Platt, U., Pundt, I., Richter, A., Rozanov, A.,<br />
Wagner, T., & Wang, P. 2004. Retrieval of profile information from Airborne Multi Axis UV/visible<br />
skylight absorption measurements. Appl.Opt., 43(22), 4415 – 4426.<br />
Bruns, M., Buehler, S. A., Burrows, J. P., Richter, A., Rozanov, A., Wang, P., Heue, K.-P., Platt, U.,<br />
Pundt, I., & Wagner, T. 2005. NO2 Profile retrieval using airborne multi axis UV-visible skylight<br />
absorption measurements over central Europe. Atmos. Chem. Phys. Discuss. accepted.<br />
Fix, A., Ehret, G., Flentje, H., Poberaj, G., Gottwald, M., Finkenzeller, H., Bremer, H., Bruns, M.,<br />
Burrows, J. P., Kleinbhl, A., Kllmann, H., Kuttippurath, J., Richter, A., Wang, P., Heue, K.-<br />
P., Platt, U., Pundt, I., & Wagner, T. 2005. SCIAMACHY validation by aircraft remote sensing:<br />
design, execution, and first measurement results of the SCIA-VALUE mission. Atmos. Chem. Phys.,<br />
5, 1273 – 1289.<br />
Hak, C., Pundt, I., Trick, S., Kern, C., Platt, U., Dommen, J., Ordóˆnez, C., Prévôt, A. S. H.,<br />
Junkermann, W., Astorga-Lloréns, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle,<br />
B., Kleffmann, J., Lörzer, J., Braathen, G. O., & Volkamer, R. 2005. Intercomparison of four<br />
different in-situ techniques for ambient formaldehyde measurements in urban air. Atmos. Chem.<br />
Phys., 5, 2881 – 2900.<br />
Hartl, A., Song, B.-C., & Pundt, I. 2005a. Reconstructing 2d-Concentration Peaks from Long Path<br />
DOAS-Tomographic measurements: Parametrisation and Geometry within a Discrete Approach.<br />
Atmos. Chem. Phys. Discuss., 5, 11781 – 11819.<br />
Hartl, A., Mettenorf, K. U., Song, B. C., & Pundt, I. 2005b. Reconstruction of 2D-Trace Gas<br />
Concentration Distributions from Long-path DOAS Measurements: General Approach, Validation<br />
and Simulations for an Experiment on an Urban Site. In: Proceedings of the 31st ”International<br />
Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />
ISPRS-publication(CD-ROM).<br />
Heckel, A., Richter, A., Tarsu, T., Wittrock, F., Hak, C., Pundt, I., Junkermann, W., & Burrows,<br />
J. P. 2005. MAX-DOAS measurements of formaldehyde in the Po-Valley. Atmos. Chem. Phys., 5,<br />
909 – 918.<br />
Heue, K.-P. 2005. Airborne Multi Axis DOAS instrument and measurements of two dimensional<br />
tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Heue, K.-P., Beirle, S., Bruns, M., Burrows, J. P., Platt, U., Pundt, I., Richter, A., Wagner, T., &<br />
P. Wang, P. 2004. SCIAMACHY validation using the AMAXDOAS instrument. In: Proceedings<br />
of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria. ESA-publication<br />
SP-572 (CD-ROM).<br />
Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., Friedeburg, C. von, Platt, U., Pundt, I., Wang,<br />
P., & Wagner, T. 2005. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />
measurements. Atmos. Chem. Phys., 5, 1039 – 1051.<br />
I., I. Pundt, Mettendorf, K.U., & v. Friedeburg, C. 2005. Emissionsmessung von NO2, SO2 und O2<br />
mittels DOAS Fernerkundung. Invited talk at the workshop ”Validierung von Kfz-Emissionsdaten:<br />
Das <strong>Karls</strong>ruher Autobahnprojekt BAB II”, <strong>Karls</strong>ruhe, 01.12.2005.<br />
Knab, V. 2004. Basic theory on DOAS tomography, Reconstruction of 2D trace gas distributions by<br />
discrete linear inversion techniques. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Kunz, C. 2001. Charakterisierung eines Multi-Strahl-Langpfad-DOAS-Systems zur Messung von<br />
Spurenstoff-Konzentrationen in der Atmosphre. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />
<strong>Universität</strong> Heidelberg, Germany.
68 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
Laepple, T., Knab, V., Mettendorf, K.-U., & Pundt, I. 2004. Longpath DOAS tomography on a<br />
motorway exhaust plume: Numerical studies and application to data from the BAB II campaign.<br />
Atmos. Chem. Phys., 4, 1323 – 1342.<br />
Lösch, J. 2001. Bestimmung von NO2 und SO2 Emissionen von Kraftfahrzeugen mittels DOAS-<br />
Tomographie. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Mettendorf, K. U. 2005. Aufbau und Einsatz eines Multibeam Instrumentes zur DOAStomographischen<br />
Messung zweidimensionaler Konzentrationsverteilungen. Ph.D. thesis, <strong>Institut</strong><br />
<strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Mettendorf, K. U., Hartl, A., & Pundt, I. 2005. An indoor test campaign of the Tomography Long<br />
Path Differential Absorption Spectroscopy (DOAS). J. Environ. Monit. accepted.<br />
Poehler, D., Rippel, B., Stelzer, A., Mettendorf, K. U., Hartl, A., Platt, U., & Pundt, I. 2005.<br />
Instrumental setup and measurement configuration for 2D-tomographic DOAS measurements of<br />
trace gas distributions over an area of a few square km. In: Proceedings of the 31st ”International<br />
Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />
ISPRS-publication(CD-ROM).<br />
Pundt, I. 2005a. DOAS (Differentielle Optische Absorptions- Spektroskopie)Messungen mit neuester<br />
Technologie. Invited talk at the DECHEMA/GDCH/DGB-Gemeinschaftsausschuss Chemie der<br />
Atmosphre, Frankfurt, 22.04.2005.<br />
Pundt, I. 2005b. DOAS tomography for the localisation and quantification of anthropogenic air<br />
pollution. Anal. Bioanal. Chem. accepted.<br />
Pundt, I., & Mettendorf, K. U. 2005. Multibeam long-path differential optical absorption spectroscopy<br />
instrument: a device for simultaneous measurements along multiple light paths. Appl. Opt., 44(23),<br />
4985 – 4994.<br />
Pundt, I., Heue, K.-P., Song, B.-C., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P.<br />
2005a. Airborne tomographic measurements of NO2 Plumes from point sources using the AMAX-<br />
DOAS instrument. J. Geophys. Res. submitted.<br />
Pundt, I., Hak, C., Hartl, A., Heue, K.-P., Mettendorf, K. U., Platt, U., Poehler, D., Rippel, B.,<br />
Song, B.-C., Stelzer, A., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P. 2005b.<br />
Mapping of tropospheric trace gas concentration distributions from ground and aircraft by DOAStomography<br />
(Tom-DOAS). In: Proceedings of the 31st ”International Symposium of Remote Sensing<br />
of the Environment”, June 20-24, 2005, in St. Petersburg, Russia. ISPRS-publication(CD-ROM).<br />
Pundt, I., Mettendorf, K. U., Laepple, T., Knab, V., Xie, P., Lösch, J., Friedeburg, C. von, Platt, U.,<br />
& Wagner, T. 2005c. Measurements of trace gas distributions using Long-path DOAS-Tomography<br />
during the motorway campaign BAB II: experimental setup and results for NO2. J. Atmos. Environ.,<br />
39(5), 967 – 975.<br />
Rippel, B. 2005. Vorarbeiten <strong>für</strong> Langpfad DOAS Tomographische Messungen über der Stadt Heidelberg.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Stelzer, A. 2005. Horizontale tomographische Langpfad-DOAS Spurengasmessungen in Heidelberg.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
von Friedeburg, C., Pundt, I., Mettendorf, K. U., Wagner, T., & Platt, U. 2005. Multi-axis-DOAS<br />
measurements of NO2 during the BAB II motorway emission campaign. J. Atmos. Environ., 39(5),<br />
977 – 985.<br />
Wang, P., Richter, A., Bruns, M., Burrows, J. P., Junkermann, W., Heue, K.-P., Wagner, T., Platt,<br />
U., & Pundt, I. 2005a. Airborne multi-axis DOAS measurements of tropospheric SO2 plumes in<br />
the Po-valley, Italy. Atmos. Chem. Phys. Discuss, 5, 2017 – 2045.<br />
Wang, P., Richter, A., Bruns, M., Rozanov, V., Burrows, J. P., Heue, K.-P., Wagner, T., Pundt, I., &<br />
Platt, U. 2005b. Measurements of tropospheric NO2 with an airborne multi-axis DOAS instrument.<br />
Atmos. Chem. Phys., 5, 337 – 343.
2.5. SATELLITE GROUP 69<br />
2.5 Satellite Group<br />
Participating scientist Steffen Beirle, Tim Deutschmann, Barbara Dix, Ossama Ibrahim, Christian<br />
Frankenberg, Michael Grzegorski, Klaus-Peter Heue, Jens Hollwedel, Muhammad Fahim Khokhar,<br />
Sven Kühl, Thiery Marbach, Janis Pukite, Suniti Sanghavi, Thomas Wagner, and Walburga Wilms-<br />
Grabe<br />
Abstract The Satellitegroup is part of the researchgroup Atmospheric Physics of Prof. Dr. Ulrich<br />
Platt. The satellite born remote sensing of the Earth’s atmosphere at the University of Heidelberg<br />
started in 1996 with the retrieval of atmospheric trace gases, namely NO2 and BrO. Today a wide variety<br />
of trace gases and other atmospheric parameters (Aerosols, Clouds, Radiative Transfer) from different<br />
satellite instruments are investigated at the IUP (see also http://satellite.iup.uni-heidelberg.de).<br />
Figure 2.34: Satellite measurement of the reflected and scattered sun light (yellow). The spectral<br />
signatures of several atmospheric trace gases are analysed in selected spectral ranges using the DOAS<br />
method. Displayed are the fitting results for various species analysed in the satellite group.<br />
Overarching topic and Background For about 10 years now, a new generation of UV/vis/NIR<br />
satellite instruments (GOME, SCIAMACHY, OMI) with moderate spectral resolution allows the<br />
retrieval of a large variety of atmospheric trace gases. In particular, global maps of several tropospheric<br />
trace gases like O3, BrO, NO2, CO, CH4, CO2, HCHO, SO2, H2O, O2, O4, and cloud properties can<br />
be analysed from observations in nadir viewing mode. The most important advantage of such satellite<br />
observations is their spatial (horizontal) coverage and resolution. The latest generation of nadir looking<br />
UV/vis satellite instruments (e.g. OMI) achieves global coverage within one day and has a horizontal<br />
resolution of about 13 x 24 km 2 . From such satellite observations, various individual sources like large<br />
cities can be identified. In addition, the observation of scattered sun light in limb geometry allows to<br />
retrieve vertical profiles of several stratospheric trace gases like O3, NO2, BrO and OClO.<br />
Funding The group activities are funded through various national and international projects, e.g.<br />
SCIAMACHY validation, FORMAT, STAR, Tropische Tropopause, NOXTRAM, EVERGREEN, AC-<br />
CENT<br />
Main methods From the measured spectra, the narowband absorption features of several trace<br />
gases are analysed using the DOAS method (see Figure). The result of the spectral analysis represents<br />
the trace gas absorption integrated along the absorption path. In addition, also the broad band<br />
spectral features are analysed; they yield information in particular on the cloud cover, aerosol load and<br />
ground albedo. Various algorithms for the analysis of satellite spectra were developed in the satellite<br />
group within the last years. For the detailed interpretation of the analysed spectral information,<br />
radiative transfer modelling is needed. A 3-D Monte-Carlo radiative transfer model (TRACY) was<br />
developed in our group, which allows to simulate various complex viewing geometries and atmospheric<br />
properties. The retrieved global data sets are further investigated using image sequence techniques.
70 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
Subprojects The various projects can be classified according to their spectral range, viewing geometry,<br />
and analysis method.<br />
UV/vis DOAS for Nadir viewing geometry: The main target is the determination of global maps of<br />
tropospheric trace gas distributions like NO2, BrO, H2O, HCHO, SO2. Curently measurements of<br />
GOME and SCIAMACHY are under investigation.<br />
NIR DOAS for Nadir viewing geometry: The main target is the determination of global maps of<br />
tropospheric trace gas distributions like CH4, CO2, and CO. Measurements in the near IR spectral<br />
range are caried out only by SCIAMACHY.<br />
Cloud retrieval for Nadir viewing geometry: The main target is the determination of global maps of<br />
cloud cover (effective cloud fraction) from broad band spectral measurements. From the combination<br />
with narow band absorption measurements of O4 and O2, also additional parameters like cloud top<br />
height can be retrieved.<br />
UV/vis DOAS for limb viewing geometry: The main target is the determination of vertical profiles of<br />
stratospheric trace gases like O3, NO2, BrO, and OClO. Measurements in limb viewing geometry are<br />
caried out only by SCIAMACHY.<br />
3-D radiative transfer modelling: Detailed radiative transfer modelling is the prerequisite for the corect<br />
interpretation of the results of the spectral analysis. The full spherical 3-dimensional Monte Carlo<br />
model is developed and operated in our group. Also a detailed scheme for the simulation of radiative<br />
properties of aerosols is developed.<br />
Validation of satellite data with independent DOAS observations are caried out from several ground<br />
based stations (Kiruna, Paramaribo, Neumayer) as well as from aircrafts and ships.<br />
Intensive interaction and cooperation exists with various international groups, e.g. Uni Bremen, IASB<br />
Brussels, Uni München, SRON Utrecht, KNMI Utrecht, EUMETSAT<br />
Publications<br />
Peer Reviewed Publications<br />
1. Frankenberg et al. [2005a]<br />
2. Frankenberg et al. [2005c]<br />
3. Frankenberg et al. [2005b]<br />
4. Heue et al. [2005]<br />
5. Hollwedel et al. [2004]<br />
6. Khokhar et al. [2005]<br />
7. Kühl et al. [2004]<br />
8. Richter et al. [2005]<br />
9. Wagner et al. [2005a]<br />
10. Wagner et al. [2004]<br />
11. Wagner et al. [2005b]<br />
Grey Publications<br />
1. Grzegorski et al. [2004]<br />
2. Heue et al. [2004]<br />
3. Marbach et al. [2004]<br />
4. ACCENT [2005]<br />
5. Wilms-Grabe et al. [2004]
2.5. SATELLITE GROUP 71<br />
PhD Theses<br />
1. Beirle [2004]<br />
2. Frankenberg [2005]<br />
3. Heue [2005]<br />
4. Hollwedel [2005]<br />
5. Kühl [2005]<br />
Diploma Theses<br />
1. Halasia [2004]<br />
Invited Talks<br />
1. Wagner [2004a]<br />
2. Wagner [2004b]<br />
3. Wagner [2004c]<br />
4. Wagner [2004d]<br />
5. Wagner [2005a]<br />
6. Wagner [2005c]<br />
7. Wagner [2005b]
72 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.1 Quantifying NOx from lightning using satellite data<br />
Participating scientists Steffen Beirle, Thomas Wagner, Ulrich Platt<br />
Abstract A strong lightning event in the Gulf of Mexico was investigated. Using satellite based<br />
measurements of NO2, combined with ground based flash counts, the direct observation of freshly<br />
produced lightning NOx could be demonstrated, and the amount of the produced NOx has been<br />
estimated.<br />
Figure 2.35: Lightning event on 30 August in the Gulf of Mexico. (a) NO2 TVCD from GOME (10 15<br />
molec/cm 2 ). (b) Time of flashes detected by NLDN<br />
Background Nitrogen oxides (NOx=<br />
NO+NO2) play an important role in tropospheric<br />
chemistry, in particular in catalytic ozone production.<br />
Lightning provides a natural source of<br />
nitrogen oxides, dominating the production in the<br />
tropical upper troposphere, with strong impact<br />
on tropospheric ozone and the atmosphere’s oxidizing<br />
capacity. Recent estimates of lightning<br />
produced NOx (LNOx) are of the order of 5 Tg<br />
[N] per year with still high uncertainties in the<br />
range of one order of magnitude. The Global<br />
Ozone Monitoring Experiment (GOME) on board<br />
the ESA–satellite ERS–2 allows the retrieval of<br />
tropospheric vertical column densities (TVCDs)<br />
of NO2 on a global scale. Here we present the<br />
GOME NO2 measurement directly over a large<br />
convective system over the Gulf of Mexico.<br />
Funding See satellite group overview.<br />
Methods and results A unique event of<br />
GOME capturing LNOx just produced is found<br />
on 30 August 2000 over the Gulf of Mexico: A<br />
sequence of about 14 pixels, measured at 16:47-<br />
16:48 UTC, shows high tropospheric NO2 TCDs<br />
(Fig. 1a) that by far exceed normal levels over<br />
ocean.<br />
These high TVCDs coincide with a strong convective<br />
system causing high lightning activity.<br />
Fig. 1b depicts the flashes detected by the U.S.<br />
National Lightning Detection Network (NLDN)<br />
on 30 August 2000 before the ERS–2 overpass,<br />
while the time of the flash occurence is colorcoded.<br />
This particular event is unprecedented as the<br />
lightning activity coincides perfectly with the<br />
GOME measurement both in space and in time.<br />
The enhanced NO2 TVCDs can not be explained<br />
with transport of anthropogenic emissions and<br />
must be thus due to freshly produced LNOx. As<br />
far as we know, such a clear and direct detection<br />
of LNOx from satellite has never been reported<br />
before.<br />
A quantitative analysis yields a LNOx production<br />
of 77 (27-230) moles of NOx, or 1.1 (0.4-3.2) kg<br />
[N], per flash. If simply extrapolated, this coresponds<br />
to a global LNOx production of 1.5 (0.5-<br />
4.5) Tg [N]/yr.<br />
Outlook/Future work The analysis of lightning<br />
NOx from satellite data will be continued<br />
with particular focus on radiative transfer in thunderstorm<br />
clouds.<br />
Main publication Beirle et al. [2005]
2.5. SATELLITE GROUP 73<br />
2.5.2 Evaluation of global tropospheric NO2 from SCIAMACHY<br />
Participating scientists Steffen Beirle, Thomas Wagner, Ulrich Platt<br />
Abstract Spectral measurements from the satellite instrument SCIAMACHY allow to determine<br />
tropospheric column densities of NO2 with improved spatial resolution compared to its predecessor<br />
GOME. The time series of global measurements provide valuable information on the spatial distribution<br />
of NOx pollution, allowing to identify and quantify the different sources of NOx.<br />
Figure 2.36: Mean NO2 TVCD (10 15 molec/cm 2 ) from SCIAMACHY (January 2003 - June 2004).<br />
Background Spectral measurements from<br />
satellite platforms allow to determine slant column<br />
densities of several trace gases, e.g. NO2,<br />
by applying Differential Optical Absorption Spectroscopy<br />
(DOAS). By estimating and subtracting<br />
the stratospheric column, and accounting for<br />
radiative transfer, tropospheric vertical column<br />
densities (TVCDs) can be retrieved. Time series<br />
of global NO2 TVCDs are available from the<br />
satellite instrument GOME since 1996, but the<br />
rather coarse spatial resolution of 320×40 km 2<br />
leads to a smoothed image of the spatial distribution<br />
of tropospheric NO2, often complicating<br />
the interpretation of the measurements. Since<br />
2002, spectral measurements with higher spatial<br />
resolution (60×30 km 2 ) are available from the<br />
SCanning Imaging Absorption SpectroMeter for<br />
Atmospheric CHartographY (SCIAMACHY), resolving<br />
several features of the spatial distribution<br />
of tropospheric NO2.<br />
Funding See satellite group overview.<br />
Methods and results The DOAS fit has been<br />
implemented for the evaluation of SCIAMACHY<br />
data. The processing of NO2 TVCDs is analogue<br />
to the GOME implementation.<br />
Fig. 1 shows the resulting mean of the global<br />
distribution of tropospheric NO2. Several hot<br />
spots, in particular several large cities, show up<br />
that have been smeared out in GOME data. The<br />
accurate measurement of spatial patterns allow<br />
the reliable identification of NOx sources and enables<br />
us to quantify NOx emissions as well as<br />
lifetime. Furthermore, the continuation of the<br />
GOME time series holds information on trends<br />
in emission strenghts, revealing a strong increase<br />
in China.<br />
Outlook/Future work Future improvements<br />
in DOAS fit, stratospheric estimation, radiative<br />
transfer modeling (in particular handling of<br />
clouds) will lead to high quality tropospheric data<br />
products that allow to assess several scientific<br />
questions.<br />
Main publication Beirle [2004]
74 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.3 Development of a radiative transfer model<br />
Participating scientist Tim Deutschmann, Suniti Sanghavi, Thomas Wagner<br />
Abstract A three-dimensional fully spherical Monte-Carlo model which provides realistic lightpath<br />
information in a scattering atmosphere is being implemented. The retrieved model data plays a keyrole<br />
in corect interpretation of spectroscopical measurements for estimation of spatially distributed tracegas<br />
concentrations.<br />
Figure 2.37: traced photons of λ = 411nm for a cloud layer with maximum extinction coefficient of<br />
3.5 in 3.0km altitude. Scattering events: air molecules (rayleigh, red), aerosols (mie, green) ground<br />
hits (isotropic, yellow), inter-voxel transitions (refraction, grey), TOA hit (turquoise).<br />
Background When using spectroscopy for the<br />
estimation of the amount of spatially distributed<br />
absorbing matter in the atmosphere, the information<br />
is needed, on which paths the photons of<br />
the measured spectrum propagated from the light<br />
source to the detector. The pathlengths through<br />
certain strongly absorbing regions of the atmosphere<br />
can susceptibly influence the observed intensity<br />
of the detecting instrument. Radiative<br />
transfer modelling can provide these key informations<br />
to inverting algorithms in order to retrieve<br />
spatially resolused tracegas concentrations.<br />
Existing models are limited under several points<br />
of view and cannot follow the progress in sensoring<br />
precision. Due to that the development of a new<br />
model is necessary and will also allow promising<br />
reprocessing of old data.<br />
Funding See satellite group overview.<br />
Methods and results Based on the work of<br />
Axel Morgner (2000) and mainly Christoph von<br />
Friedeburg (2003), the new program is being implemented<br />
under aspects of scalability, portability<br />
to different os and adaptability to various<br />
measurement geometries. The present algorithm<br />
uses a numerical method to generate realistic light<br />
paths in consideration of rayleigh scattering on<br />
air molecules, mie scattering on aerosols and so<br />
far isotropic ground scattering. The physically<br />
relevant properties air density, pressure, temperature,<br />
humidity, refractive index, tracegas and<br />
aerosol concentrations and ground albedo of the<br />
full spherical atmosphere are mapped into a 3D<br />
grid. Using the Backward Monte Carlo technique<br />
the simulated photons are emitted by the detector<br />
and traced through the grid until they leave the<br />
atmosphere (TOA, Figure 2.37). Then the generated<br />
paths are weighted for a certain sun position,<br />
by their possibility using a method called<br />
“forcing”.<br />
The flexibility of the new program allows the application<br />
of the model data in a wide range, not<br />
only in spectrosopy but also in atmospherical dynamics<br />
and chemistry by regarding forward traced<br />
photons, which is already possible.<br />
Outlook/Future work<br />
• more realistic mie scattering in clouds with<br />
droplet size distribution function<br />
• more realistic modellation of ground scattering<br />
by using BRDF<br />
• raman scattering and polarisation<br />
• investigation of the energy budget for certain<br />
conditions<br />
• web interface for remote model data retrieval<br />
• implementation of tomographic inversion<br />
• parallelisation<br />
Main publication von Friedeburg [2003]
2.5. SATELLITE GROUP 75<br />
2.5.4 Retrieval of methane from SCIAMACHY onboard ENVISAT<br />
Participating scientist Christian Frankenberg, Ulrich Platt, Thomas Wagner<br />
Abstract SCIAMACHY onboard ENVISAT features three near infrared spectrometers and thereby<br />
enables the retrieval of atmospheric methane with high sensitivity to the lowermost atmospheric layers.<br />
Using concurent retrievals of carbon dioxide and the application of atmospheric models, precise maps<br />
of the global distribution of column averaged methane mixing ratios are derived.<br />
Figure 2.38: Column averaged mixing ratio of methane averaged from August through November<br />
2003.<br />
Background Methane (CH4) is, after carbon<br />
dioxide, the second most important anthropogenic<br />
greenhouse gas, contributing directly 0.48 W m −2<br />
to the total anthropogenic radiative forcing of<br />
2.43 W m −2 by well-mixed greenhouse gases<br />
(IPCC, 2001). In addition, it exhibits an indirect<br />
effect of about 0.13 W m −2 through formation<br />
of other greenhouse gases, most notably<br />
tropospheric ozone and stratospheric water vapor<br />
(Lelieveld et al., 1998).<br />
A major limitation of present top-down methane<br />
emissions inventories is the limited number of atmospheric<br />
observation sites. SCIAMACHY now<br />
offers the unique possibility of sensing methane<br />
globally, retrieving methane abundances also in<br />
remote areas.<br />
Funding See satellite group overview.<br />
Methods and results An algorithm (IMAP-<br />
DOAS) was developed based on the principles<br />
of differential optical absorption spectroscopy<br />
(DOAS), that deals with the peculiarities of retrieving<br />
strong absorbers in the near infrared,<br />
thus allowing a precise retrieval of the respective<br />
trace gases. It was shown that nonlinear iterative<br />
schemes are necessary to account for saturation effects<br />
and to avoid interdependencies of spectrally<br />
overlapping strong absorbers.<br />
Global measurements of the total columns of<br />
methane with high precision were made possible<br />
by use of concurent retrievals of the relatively homogenously<br />
distributed carbon dioxide as proxy<br />
for the light path of the recorded photons. The<br />
highest abundances were found over areas of rice<br />
cultivation in South-East Asia and can be considered<br />
a direct proof of large scale methane emissions<br />
in Asia.<br />
In the time-period from August through November<br />
2003, large discrepancies between measurements<br />
and model were discovered over tropical<br />
rainforest areas. Measured abundances showed<br />
persistently higher abundances than those predicted<br />
by the model. This led to the conclusion<br />
that the tropical regions as methane source have<br />
been hitherto underestimated in curent emissions<br />
inventories.<br />
An extension of the analysis to the years 2003 and<br />
2004 showed that the discrepancies are highest<br />
during the months of August through October.<br />
The precision of these measurements now allows<br />
their use in inversion models to quantify the temporal<br />
and geographical distribution of methane<br />
sources.<br />
Main publications Frankenberg et al. [2005b],<br />
Frankenberg et al. [2005a]
76 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.5 Retrieval of carbon monoxide from SCIAMACHY onboard ENVISAT<br />
Participating scientist Christian Frankenberg, Ulrich Platt, Thomas Wagner<br />
Abstract SCIAMACHY onboard ENVISAT features three near infrared spectrometers and thereby<br />
enables the retrieval of atmospheric carbon monoxide which holds interest from several perspectives.<br />
Despite severe instrumental problems first global retrievals from SCIAMACHY have become feasible.<br />
Figure 2.39: Maximum CO vertical column densities as seen by SCIAMACHY.<br />
Background The global distribution of carbon<br />
monoxide (CO) holds interest from several perspectives:<br />
as a primary and secondary determinant<br />
of air quality, as the leading sink of hydroxyl<br />
radicals, and as an atmospheric tracer with<br />
a relatively long lifetime, that is, an indicator of<br />
how transport redistributes pollutants on a global<br />
scale. High CO concentrations can directly affect<br />
human health. Indirectly, CO plays a role in the<br />
catalytic production and destruction of ozone. In<br />
case of high NOx abundance, CO oxidation by<br />
OH radicals leads to ozone production. Global<br />
measurements with high sensitivity towards the<br />
ground are thus very valuable for the quantification<br />
of its impact on air quality and OH radical<br />
abundances.<br />
Funding See satellite group overview.<br />
Methods and results The IMAP-DOAS algorithm,<br />
which was developed at IUP Heidelberg,<br />
was applied to account for saturation effects and<br />
to avoid interdependencies of spectrally overlapping<br />
strong absorbers. Further, additional spectral<br />
calibrations for the SCIAMACHY instrument<br />
haven been elaborated to enable the retrieval from<br />
channel 8 spectra that are deteriorated due to an<br />
ice-layer and low signal to noise ratio.<br />
Since SCIAMACHY cannot be considered a dedicated<br />
greenhouse gas mission but a prototype with<br />
respect to near infrared spectroscopy, several instrumental<br />
shortcomings had to be solved. An<br />
extensive analysis of these effects enabled the retrieval<br />
of and carbon monoxide.<br />
In the retrievals, enhancements of carbon monoxide<br />
in biomass-burning regions could be clearly<br />
identified. In addition, the seasonal and geographical<br />
patterns of typical biomass burning regions<br />
could be observed. Only in the industrial regions<br />
of China, high carbon monoxide abundances were<br />
found to be persistent over the year.<br />
Main publications Frankenberg et al. [2005c],<br />
Frankenberg et al. [2005b]
2.5. SATELLITE GROUP 77<br />
2.5.6 Retrieval of cloud parameters using SCIAMACHY and GOME data<br />
Participating scientist Michael Grzegorski, Thomas Wagner, Christian Frankenberg, Mark Wenig 1 ,<br />
Nicolas Fournier 2 , Piet Stammes 2<br />
1 NASA Goddard Space Flight Center, Greenbelt, Maryland, USA<br />
2 Royal Meteorological <strong>Institut</strong>e of the Netherlands, KNMI, Utrecht, The Netherlands<br />
Abstract The retrieval of cloud parameters like cloud coverage, cloud top pressure or cloud optical<br />
thickness from satellite is an important issue both for climatology and the analysis of tropospheric<br />
trace gases. The HICRU algorithm improves retrieval of effective cloud fraction using data from<br />
SCIAMACHY on ENVISAT and GOME on ERS-2. HICRU also allows an accurate cloud retrieval<br />
over deserts, which is usually difficult for cloud algorithms.<br />
Figure 2.40: case study (08/27/2003): Results of HICRU compared with the corespondent image from<br />
Meteosat (2 hours after ENVISAT, taken from www.eumetsat.de, c○Eumetsat)<br />
Background The detection of cloud parameters<br />
like cloud coverage, cloud top pressure or<br />
cloud optical thickness from satellite is an important<br />
issue: 1.) for meteorology and the investigation<br />
of climate change and 2.) for the analysis of<br />
tropospheric trace gases from space relevant to environmental<br />
and climatological issues. Although<br />
the retrieval of different cloud parameters is useful<br />
for trace gas retrievals, especially the accurate<br />
identification of completely cloud free regions is<br />
crucial due to the shielding effect, which causes<br />
an underestimation of the vertical column density<br />
of tropospheric trace gases measured by satellite.<br />
Funding See satellite group overview.<br />
Methods and results The Heidelberg Iterative<br />
Cloud Retrieval Utilities (HICRU) retrieve effective<br />
cloud fraction by applying the widely used<br />
threshold method to the so-called Polarization<br />
Monitoring Devices (PMDs) with higher spatial<br />
resolution compared to the channels used for trace<br />
gas retrievals. The results are validated through<br />
intercomparison with different other cloud algorithms.<br />
The intercomparisons show the reliability<br />
of the HICRU algorithm. The sophisticated<br />
retrieval of the HICRU thresholds also allows an<br />
accurate retrieval over deserts, which is usually<br />
difficult for for GOME/SCIAMACHY cloud algorithms.<br />
Cloud fraction retrieved by HICRU using<br />
data both from SCIAMACHY and GOME is<br />
available free of charge on http://satellite.iup.uniheidelberg.de.<br />
Outlook/Future work The results of HICRU<br />
will be combined with the DOAS evaluation of O 2<br />
and O 4 and the results from the radiation transfer<br />
model TRACY to retrieve further cloud parameters,<br />
especially cloud top height.<br />
Main publication Grzegorski et al. [2004]
78 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.7 Satellite validation using the airborne multi axis DOAS instrument<br />
Participating scientists Klaus-Peter Heue, Thomas Wagner, Andreas Richter 2 , Marco Bruns 2<br />
Ping Wang 2 ( 2 <strong>Institut</strong> <strong>für</strong> Umweltphyisk, <strong>Universität</strong> Bremen)<br />
Abstract The Airborne Multi AXis DOAS instrument designed to separate the tropospheric from<br />
stratospheric absorptions of several Trace gases e.g. NO2. Due to the long range of the aeroplane<br />
it is ideal for validation measurements of tropospheric NO2 observed by the new satellite instrument<br />
SCIAMACHY on ENVISAT.<br />
Figure 2.41: AMAXDOAS measurements along the flight track on 19/02/2003 overlaid to SCIA-<br />
MACHY observations from the same day. The scientific SCIAMACHY data from the IUP in Bremen<br />
were taken.<br />
Background With the SCIAMACHY instruments<br />
slant and vertical columns of many trace<br />
gases can be measured. Here we concentrate on<br />
tropospheric NO2. Based on the observed spectra<br />
from SCIAMACHY several scientific DOAS<br />
products exist at different scientific groups (e.g.<br />
in Heidelberg, Bremen, Harvard). Nitrogen dioxide<br />
is known to be harmful and plays an important<br />
role in the tropospheric chemistry of ozone. Most<br />
of the tropospheric NO2 is produced by anthropogenic<br />
emissions.<br />
Funding See satellite group overview.<br />
Methods and results Tropospheric NO2 vertical<br />
and slant columns from the new satellite instrument<br />
SCIAMACHY on ENVISAT are validated<br />
by measurements of the AMAXDOAS instrument<br />
on board the DLR Falcon. The results<br />
presented here were obtained in February<br />
2003 on a flight over the Alps, the Po-Valley and<br />
the Mediterranean ( figure 2.41). Due to the<br />
similar measurement system of AMAXDOAS and<br />
SCIAMACHY both tropospheric slant and ver-<br />
tical columns can be compared. However, the<br />
stratospheric absorption has to be separated from<br />
the tropospheric signal first. In the Troposphere<br />
the local variation in the NO2 columns are very<br />
high caused by the anthropogenic emissions. The<br />
stratospheric signal shows rather smooth spatial<br />
variations. Different methods for the separation<br />
of tropospheric and stratospheric signal for both<br />
instruments were investigated. Independent information<br />
about aerosol optical thickness and mixing<br />
layer height were considered for the calculation of<br />
the AMF. The TVCD measured by AMAXDOAS<br />
varied between 16.2 and 35.2·10 15 molec/cm 2 over<br />
the Po-Valley where SCIAMACHY data resulted<br />
in 19.9 to 37·10 15 molec/cm 2 . Over less polluted<br />
areas a similarly good agreement was found. The<br />
linear correlation between the two datasets results<br />
in a slope of 0.93. The slight differences observed<br />
can be attributed to the different spatial resolution<br />
and the temporal mismatch between the measurements<br />
over the Po-Valley.<br />
Main publications Heue [2005], Heue et al.<br />
[2005]
2.5. SATELLITE GROUP 79<br />
2.5.8 Analysis of global long-term tropospheric and stratospheric BrO<br />
from GOME measurements<br />
Participating scientist Jens Hollwedel, Thomas Wagner, Roland von Glasow, Lars Kaleschke 2 ,<br />
William Simpson 3 , Ulrich Platt ( 2 University of Bremen, 3 University of Alaska)<br />
Abstract BrO leads to ozone depletion, both in the stratosphere and troposphere. The global<br />
distribution and yearly cycle of stratospheric and tropospheric BrO has been analysed. Transport<br />
events and an increase in tropospheric source strength have been discussed.<br />
Figure 2.42: Global mean BrO distribution derived from GOME for the time period 1996 - 2001.<br />
Background The importance of BrO for the<br />
ozone depletion in the stratosphere is well known.<br />
BrO can also be liberated by heterogenous reactions<br />
on the surfaces of halogen rich aerosols, especially<br />
over the one year old sea ice. This mechanism<br />
is known as the Bromine explosion leading<br />
to the tropospheric ozone hole in polar spring.<br />
Funding See satellite group overview.<br />
Methods and results Column densities of<br />
bromine monoxide have been derived from GOME<br />
for the time period from 1996 to 2001 on a global<br />
scale. Two methods for the separation of the<br />
stratospheric and tropospheric fractions of the total<br />
column density have been used (a fixed SZA<br />
interval and a reference site method). The average<br />
stratospheric BrO load has increased slightly<br />
during the time period under investigation. Investigation<br />
of sources and source strengths of boundary<br />
layer BrO show that enhanced boundary layer<br />
BrO is released in bromine explosion events during<br />
polar spring leading to tropospheric ozone holes.<br />
The sea-ice and especially frost flowers are the<br />
sources for these events. The area covered by<br />
’clouds’ of enhanced BrO in the northern hemisphere<br />
has increased by about 10% per year from<br />
1996 to 2001. Thus the source strength has increased<br />
which is probably due to changes in the<br />
Arctic sea-ice cover. Strong evidence for a free<br />
tropospheric BrO background of about 2pptv BrO<br />
in the free troposphere with a lower boundary of<br />
its lifetime of about four days has been gathered.<br />
Transport events of polar tropospheric Bro towards<br />
mid-latitudes and into the free troposphere<br />
have been discovered.<br />
Outlook/Future work A corelation analysis<br />
of stratospheric BrO and NO2 will be performed<br />
discussing the stratospheric yearly cycle of BrO.<br />
Transport events from the polar troposphere towards<br />
mid-latitudes and into the free troposphere<br />
will be further investigated.<br />
Main publication Hollwedel et al. [2004],<br />
Hollwedel [2005]
80 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.9 Enhanced SO2 Column Densities Observed Over South East Asian<br />
Region: Consequence of El Niño<br />
Participating scientist M. F. Khokhar<br />
Abstract Changes in the global atmospheric circulation patterns caused by El Niño bring about<br />
weather extremes in various parts of the world. Especially, inhibiting rainfall over the western pacific<br />
equatorial region, resulting in a lot of biomass burning events and droughty conditions. GOME data<br />
showed enhanced SO2 column densities over South East Asian region which strongly corelate to the<br />
strong El Niño event in the year 1997-98.<br />
Figure 2.43: Comparison of monthly mean maps of fire data (ATSR fire counts /pixel), in the left<br />
panel, GOME SO2 SCDs (centre) and HCHO SCDs (right panel) for the month of September from<br />
1996 to 1998. The HCHO and SO2 emissions over S.E. Asia resulted from relatively enhanced Biomass<br />
burning events as consequences of strong El Niño 1997-98 in this region. The GOME observations are<br />
averaged on a 0.5 ◦ latitude/longitude grid.<br />
Background The satellite remote sensing provides<br />
information about various atmospheric trace<br />
gas emissions and their distribution on a global<br />
scale. Sulfur Dioxide (SO2) is an important trace<br />
gas in the atmosphere. It is released to the troposphere<br />
from both human activities and natural<br />
sources (mainly from volcanic eruptions and<br />
Biomass burning). We investigated the Biomass<br />
burning in S. E. Asia for the time period 1996-<br />
2001. We find an enhancement in the SO2 SCDs<br />
for the year 1997 and 98.<br />
Funding See satellite group overview.<br />
Methods and results GOME is a nadirscanning<br />
UV/Vis. spectrometer covering the<br />
wavelength range from 240nm to 790 nm. A key<br />
feature of GOME is its ability to detect, besides<br />
ozone, several chemically active atmospheric trace<br />
gases such as SO2, CH2O NO2, BrO etc. From the<br />
ratio of earthshine radiance and solar iradiance<br />
measurements, slant column densities (SCDs) of<br />
the respective absorbers can be derived by applying<br />
the technique of differential optical absorption<br />
spectroscopy (DOAS). Satellite remote sensing is<br />
a power full tool along with several advantages<br />
over the conventional measurement techniques.<br />
Especially, to monitor the volcanic eruptions and<br />
biomass burning events resulting from forest fire<br />
which very often occur in remote and inaccessible<br />
area. Biomass burnings are also an important<br />
source of tropospheric NO2 and HCHO, results<br />
compared with SO2 column densities showed a<br />
good agreement (see figure). Enhanced SO2 SCDs<br />
for 1997 and 98 over S. E Asian region are coupled<br />
to El Niño consequences. Satellites provide<br />
the best opportunity to quantify the impact of<br />
biomass burning on global atmospheric chemistry.<br />
Outlook/Future work Synergistic use of<br />
satellite observations for different trace gases e.g.<br />
HCHO and NO2 and CO, from biomass burning<br />
and to compare their results.<br />
Main publication Khokhar et al. [2005]
2.5. SATELLITE GROUP 81<br />
2.5.10 Retrieving vertical profiles of stratospheric trace gases from satellite<br />
observations<br />
Participating scientist Sven Kühl, Janis Pukite, Thomas Wagner, and Walburga Wilms-Grabe<br />
Abstract Vertical profiles of ozone, NO2, BrO and OClO were retrieved from measurements of<br />
SCIAMACHY in limb geometry. The retrieved profiles were compared to balloon measurements and<br />
SCIAMACHY products from other institutes.<br />
Figure 2.44: Averaging kernels for typical retrievals, revealing the altitude range for which information<br />
on the trace gas distribution can be retrieved.<br />
Background It is well established that the major<br />
cause for the ozone hole, the massive depletion<br />
of ozone in the polar lower stratosphere<br />
in springtime, is the heterogeneous processing of<br />
chlorine species during polar winter, the stratospheric<br />
chlorine activation. Despite their immense<br />
effect on the ozone layer, daily and global measurements<br />
of active chlorine compounds like ClO<br />
and ClOOCl are rare. On the other hand, chlorine<br />
dioxide (OClO), an important indicator for<br />
chlorine activation, can be measured by remote<br />
sensing methods more easily than ClO or ClOOCl.<br />
GOME measurements of OClO have been applied<br />
in the long term monitoring of stratospheric chlorine<br />
activation [Wagner et al. , 2001] as well as<br />
in case studies [Kühl et al. , 2004; Richter et al. ,<br />
2005]. However, the interpretation of column densities<br />
(obtained from observations in nadir geometry)<br />
in many cases has to remain on a qualitative<br />
level, while the knowledge about 3-dimensional<br />
trace gas distributions allows also quantitative<br />
studies. Thus, the vertical profiles of ozone, NO2,<br />
BrO and OClO, retrieved from the SCIAMACHY<br />
limb measurements, will lead to a better understanding<br />
of processes relevant for polar ozone loss<br />
and can be applied for investigating contemporary<br />
open questions of stratospheric chemistry.<br />
Funding See satellite group overview.<br />
Methods and results For the retrieval of the<br />
vertical trace gas profiles a two step approach is<br />
used: First, SCDs as function of tangent height<br />
are determined by DOAS, then inversion to profiles<br />
by applying the box AMFs calculated by<br />
RTM. This two step approach enables us to study<br />
separately the impact of spectroscopy and radiative<br />
transfer modeling on the retrieved profile.<br />
The retrieved profile is always a combination of<br />
the measured SCDs, the measurement eror, the<br />
applied AMFs, and the a priori. Therefore, the<br />
retrieved SCDs and the calculated AMFs should<br />
be of little uncertainty. Also, the a priori should<br />
describe the mean value and the variance of the<br />
state to be retrieved as good as possible. The last<br />
point is especially important for species with a<br />
strong annual or diurnal cycle, like e.g. OClO.<br />
First results are in good agreement with expectations<br />
from stratospheric chemistry, as well as<br />
the seasonal and latitudinal dependency of the respective<br />
trace gas abundances. Also, first comparisons<br />
with other profile retrievals from SCIA-<br />
MACHY limb measurements [Kühl et al. , 2005]<br />
and with balloon borne observations [Butz et al.<br />
, 2005] are very promising. The averaging kernels<br />
of our NO2, BrO and OClO retrieval algorithms<br />
(shown in 2.44) reveal that information about the<br />
vertical profile can be obtained for NO2 in the altitude<br />
range from 15-40 km, for BrO from 15-28<br />
km and for OClO from 15-25 km. The vertical<br />
resolution of the retrieved profile in this altitude<br />
range is 3 km.<br />
Outlook/Future work Improving the profile<br />
retrieval in terms of spectroscopy, radiative transfer<br />
simulation and inversion approach. Application<br />
of the retrived profiles in scientific studies on<br />
open questions of stratospheric chemistry.<br />
Main publication Kühl [2005]
82 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.11 Comparison of OClO nadir measurements from SCIAMACHY and<br />
GOME<br />
Participating scientist Sven Kühl, Walburga Wilms-Grabe, Thomas Wagner<br />
Abstract Total columns of OClO were retrieved from SCIAMACHY nadir observations and compared<br />
to the longterm dataset of GOME, the predecessor of SCIAMACHY. The retrieved SCDs are<br />
in good qualitative and quantitative agreement.<br />
Figure 2.45: Maximum OClO SCD at SZA = 90 ◦ for the southern hemisphere derived from SCIA-<br />
MACHY measurements during May to October 2003 and 2004 in comparison to the coresponding<br />
minimum and maximum values derived from GOME measurements during 1996 to 2001.<br />
Background In the polar winter, temperatures<br />
inside the polar vortex can drop below the threshold<br />
for formation of polar stratospheric clouds<br />
(PSCs) which is e.g. 195 K at an altitude of approx.<br />
19 km. Heterogeneous reactions on PSCparticles<br />
convert the ozone-inert chlorine reservoirs<br />
(mainly ClONO2 and HCl) into ozone destroying<br />
species (active chlorine, mainly Cl, ClO<br />
and ClOOCl), see e.g. Solomon [1999]. This<br />
chlorine activation is the prerequisite for massive<br />
ozone destruction by catalytic cycles. ClO (chlorine<br />
monoxide) absorbs strongly at wavelengths<br />
below 310 nm, which is in the region where also<br />
the strong ozone absorptions of the Hartley bands<br />
are situated. Therefore, the absorption by ClO<br />
is masked by the much stronger O3 absorption<br />
and unambiguous detection of stratospheric ClO<br />
by UV-Spectroscopy was not possible so far. On<br />
the other hand, OClO (chlorine dioxide) shows<br />
strong differential absorption features in the spectral<br />
range from 280 to 450 nm, and therefore can<br />
be detected by means of DOAS.<br />
Funding See satellite group overview.<br />
Methods and results For the OClO DOAS<br />
analysis of SCIAMACHY spectra we use the<br />
wavelength range from 363 to 391 nm, the same as<br />
for GOME. Included reference spectra are: OClO,<br />
NO2, O3, O4, Ring, and the Eta and Zeta Spectrum<br />
(from calbration key data) for corection of<br />
polarisation features. From various tests it turned<br />
out that the inclusion of the polarisation corection<br />
spectra is essential for a corect retrieval of OClO.<br />
Other parameters that were tested are the wavelength<br />
range used for the analysis, the degree of<br />
the polynomial, and the inclusion of the reciprocal<br />
of the Fraunhofer Reference (1/I0) in the fit.<br />
While the OClO fit converges for different wavelength<br />
ranges, we finally chose the same fit window<br />
as for GOME, for reason of consistency. The<br />
OClO SCDs derived from SCIAMACHY spectra<br />
by the DOAS method are consistent with expectations<br />
from stratospheric chlorine chemistry.<br />
Large OClO SCDs are observed only for regions<br />
inside the polar vortex, their magnitude is in good<br />
agreement with independent measurements from<br />
GOME, see Figure.<br />
Outlook/Future work Improvement of retrieval,<br />
monitoring of chlorine activation, case<br />
studies (e.g. mountain wave-induced chlorine activation).<br />
Investigating OClO photochemistry by<br />
combination of measurements in limb, nadir and<br />
occultation geometry.<br />
Main publication Kühl et al. [2005]
2.5. SATELLITE GROUP 83<br />
2.5.12 Identification of tropospheric emissions sources from satellite observations:<br />
Synergistic use of HCHO and NO2 trace gas measurements<br />
Participating scientist Thiery Marbach<br />
Abstract Many uncertainties remain in the distribution and characteristic of the tropospheric<br />
sources of trace gases. The satellites data sets allow to compare global trace gas maps providing<br />
unique opportunities to determine more precisely the tropospheric sources. We present case studies<br />
for combined HCHO and NO2 satellite observations, derived from GOME measurements.<br />
Figure 2.46: Case study of trace gas comparison: HCHO is produced from biogenic isoprenes and<br />
during biomass burning. Yellow box: HCHO only from isoprenes. Red box: Both, isoprenes and<br />
biomass burning. The HCHO biogenic isoprene emissions could be separated from the HCHO due to<br />
biomass burning using the NO2-fires corelation.<br />
Background We present case studies for the<br />
combined GOME observations for 1997 of HCHO<br />
SCDs and NO2 VCDs. Additional global data sets<br />
of quantities (forest fires) measured from ATSR<br />
have been compared to the tropospheric trace gas<br />
columns.<br />
Funding See satellite group overview.<br />
Methods and results The principal biomass<br />
burning areas (intense source of HCHO) can be<br />
observed in the Amazon basin region and in central<br />
Africa. Other high HCHO emissions can be<br />
corelated with climatic events like El Nino in 1997,<br />
which induced dry conditions in Indonesia causing<br />
many forest fires. Tree isoprene emissions contribute<br />
also to high HCHO concentrations especially<br />
in southeast United States, northern part<br />
of the Amazon basin, and in the African tropical<br />
rain forest region. The HCHO data can be compared<br />
with NO2 results to identify more precisely<br />
the tropospheric sources (biomass burning events,<br />
human activities). NO2 corelate with HCHO over<br />
Africa (grassland fires) but not over Indonesia<br />
(forest fires). In south America, an augmentation<br />
of the NO2 concentrations can be observed<br />
with the fire shift from the forest to grassland<br />
vegetation. So there seems to be a dependence<br />
between the NO2 emissions during biomass burning<br />
and the vegetation type (grassland or forest),<br />
which could influence the fire temperature (so the<br />
NO2 production) through parameters like vegetation<br />
density (oxidation capacity) or humidity. The<br />
NO2-fires corelation can also be an helpful tool to<br />
discriminate more precisely the part of the HCHO<br />
emissions coming from the biomass burning and<br />
the part issue from the tree isoprene emissions.<br />
This case studie is illustrated in the figure with an<br />
example over the Amazon basin (also illustrated<br />
by the work of Ulrike Reichl).<br />
Outlook/Future work The HCHO and NO2<br />
data can also be compared with SO2 results to<br />
identify more precisely the tropospheric sources<br />
(biomass burning events, human activities, additional<br />
sources like volcanoes emissions). Comparison<br />
with CH4 and CO will also be possible<br />
by using the SCIAMACHY data sets, and could<br />
contribute to the identification of sources due to<br />
biomass burning, fossil fuel combustion or agriculture.<br />
Main publication Marbach et al. [2004], Reichl<br />
[2005]
84 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.13 Trace gas profile retrieval from SCIAMACHY limb measurements<br />
Participating scientist Janis Pukite, Sven Kühl, Thomas Wagner, and Walburga Wilms-Grabe<br />
Abstract Trace gas profile retrieval of ozone, NO2, BrO and OClO is performed. This can be done<br />
in two successive steps. First, slant column densities (SCDs) of trace gas are retrieved by DOAS from<br />
SCIAMACHY measurements at different elevations. Second, profile is derived by inverting the SCDs.<br />
For that purpose radiative transfer modelling is performed.<br />
Figure 2.47: Latitudinal cross-sections of concentrations of ozone, NO2, BrO and OClO according to<br />
an orbit on 24.08.2004.<br />
Background The SCIAMACHY (Scanning<br />
Imaging Absorption Spectrometer for Atmospheric<br />
Chartography) on ENVISAT measures solar<br />
UV-VIS-NIR radiation transmitted, backscattered<br />
and reflected by the atmosphere and the<br />
ground. The limb-scanning mode (tangential<br />
view) is implemented by the instrument allowing<br />
to perform measurements at different elevation<br />
angles. In this way the atmosphere is probed<br />
at different geometrical configurations that make<br />
instrument more or less sensitive to substances located<br />
at different altitudes in the atmosphere. To<br />
connect the measurements with atmospheric profile<br />
of a trace gas the radiative transfer properties<br />
of the atmosphere should be applied.<br />
Funding See satellite group overview.<br />
Methods and results The retrieval of profiles<br />
is done in two successive steps. First, SCDs for<br />
the trace gases are derived from the SCIAMACHY<br />
limb measurements by DOAS method. In the second<br />
step the trace gases SCDs are converted into<br />
vertical concentration profiles by means of radiative<br />
transfer modelling (RTM). For the RTM the<br />
full spherical 3D model ”Tracy”, (von Friedeburg,<br />
2003) is used. Inversion is constrained by linear<br />
optimal estimation method (Rodgers, 2000).<br />
The method demonstrates possibility to retrieve<br />
trace gas concentrations for altitudes 15 - 28 km<br />
(BrO), 15 - 40 km (ozone and NO2), 15 - 25 km<br />
(OClO). There are still uncertainties in retrieval<br />
at polar regions probably caused by ozone absorption<br />
cross-section dependence from temperature<br />
or RTM shortages. Retrieved profiles of NO2 and<br />
BrO show good agreement with retrieval done by<br />
IUP Bremen and with balloon measurements for<br />
NO2.<br />
Outlook/Future work An improvement is<br />
necessary especially for measurements made at solar<br />
zenith angles ≥ 90 ◦ as well as for retrieval<br />
of BrO and OClO. Model studies should be performed.<br />
Improvement in RTM is required.<br />
Main publication Pukite et al. [2005], Butz<br />
et al. [2005]
2.5. SATELLITE GROUP 85<br />
2.5.14 Mie theory based characterization and modeling of atmospheric<br />
aerosols<br />
Participating scientist Suniti Sanghavi<br />
Abstract We have developed a Mie model to generate the single scattering properties of a particle<br />
given its size and complex refractive index. We put up a set of 24 aerosol scenarios to represent most<br />
aerosols in the atmosphere. The Mie theory can be used to simulate these scenarios and thus examine<br />
the optical behavior of most atmospheric aerosols.<br />
Figure 2.48: Phase functions of different aerosol particles<br />
Background Aerosols have gained increasing<br />
importance in atmospheric sciences due to the<br />
key role they play in regard to, amongst others,<br />
the earth’s radiative budget, convective processes<br />
and precipitation, and stratospheric chemistry<br />
leading, eg., to the formation of the ozone<br />
hole. They remain, however, difficult to quantify<br />
due to their varied sources, lifetimes and transport<br />
mechanisms. Thus they may occur over land or<br />
water surfaces and at different heights in the atmosphere.<br />
They also display inherent variations<br />
in size, shape and chemical composition, leading<br />
to different optical properties. We classify aerosols<br />
to represent most situations found in the atmosphere<br />
and characterize their optical properties<br />
using the Mie theory. This can be used to simulate<br />
the radiative properties of aerosols occuring in nature.<br />
We intend to use the TRACY MC RTM for<br />
this purpose. This should especially help quantify<br />
the radiative effects of aerosols on the retrieval of<br />
trace gas species from the satellite DOAS instrument<br />
SCIAMACHY. Work is ongoing for other<br />
applications that may include, in conjunction with<br />
aerosol climatologies now available at sites such<br />
as AERONET, aerosol inversion products from<br />
SCIAMACHY radiances.<br />
Funding See satellite group overview.<br />
Methods and results We have adapted a compilation<br />
of 24 distinct aerosol scenarios, consisting<br />
of 5 main aerosol types, viz. urban industrial,<br />
biomass burning, desert dust, marine and<br />
volcanic, each associated with a typical complex<br />
refractive index and vertical profile. Each is further<br />
subclassified according to coarseness, absorptivity,<br />
nonsphericity or height of occurence in the<br />
atmosphere(km a.s.l.).<br />
We obtain the optical properties, viz. extinction<br />
cross section, single scattering albedo and phase<br />
function of an aerosol particle of given size and<br />
complex refractive index, using the Mie theory<br />
(See figure). The Mie theory is a special case<br />
of the Maxwell equations with boundary conditions<br />
given by the interaction of electromagnetic<br />
radiation of given wavelength at the surface of a<br />
spherical particle.<br />
Using the characteristic complex refractive indices,<br />
size distributions and vertical profiles provided<br />
by the the scenarios mentioned above, we<br />
can use the Mie theory to determine bulk properties,<br />
e.g. the Aerosol Optical Thickness (AOT)<br />
at a given location. Adding surface reflection,<br />
Rayleigh scattering, and molecular absorption allows<br />
us to simulate fluctuations in radiances measured<br />
by satellite due to variations in the aerosol<br />
loading of the atmosphere.<br />
Outlook/Future work Implementing aerosols<br />
in TRACY RTM (Quantification of the effect<br />
of aerosols on SCDs/AMFs in different spectral<br />
regions), Aerosol retrieval/inversion from satellite/ground<br />
based measurements.<br />
Main publication Sanghavi [2003]
86 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.15 Satellite observations of the global water vapor distribution<br />
Participating scientist Thomas Wagner, Steffen Beirle, Michael Grzegorski<br />
Abstract From modern UV/vis satellite instruments, the integrated water vapor concentration<br />
(often refered to as vertical column density or total column precipitable water) can be observed on<br />
a global scale. In contrast to previous satellite observations in the infrared and microwave spectral<br />
range our observations include both ocean and land surfaces with similar sensitivity.<br />
Figure 2.49: Global anomalies of the water vapor distribution during the strong ENSO event in<br />
1997/98.<br />
Background Atmospheric water vapor is the<br />
most important greenhouse gas contributing<br />
about 2/3 of the natural greenhouse effect. In<br />
contrast to other greenhouse gases like CO2 and<br />
CH4 it has a much higher temporal and spatial<br />
variability. The corect understanding and assessment<br />
of atmospheric water vapor with respect to<br />
the Earths energy budget is further complicated<br />
by its role in cloud formation and transport of<br />
latent heat. Today, many details of how the hydrological<br />
cycle reacts to climate change (water<br />
vapor feedback) are still not understood. Especially<br />
for the tropics, which contribute strongest<br />
to the water vapor greenhouse effect, the strength<br />
of the water vapor feedback is under intense debate.<br />
In our studies we investigate the dependence<br />
of the global distribution of water vapor on surface<br />
temperature. Particular studies focussed on<br />
the response to the strong ENSO in 1997/98 and<br />
on the trends from 1996-2003.<br />
Funding See satellite group overview.<br />
Methods and results The GOME instrument<br />
is one of several instruments aboard the European<br />
research satellite ERS-2. It consists of a set of four<br />
spectrometers that simultaneously measure sunlight<br />
reflected from the Earth’s atmosphere and<br />
ground in total of 4096 spectral channels covering<br />
the wavelength range between 240 and 790 nm<br />
with moderate spectral resolutions. The satellite<br />
operates in a nearly polar, sun-synchronous orbit<br />
at an altitude of 780 km with an equator crossing<br />
time at approximately 10:30 local time. The<br />
Earth’s surface is totally covered within 3 days,<br />
and poleward from about 70 latitude within 1 day.<br />
Our water vapor algorithm is based on Differential<br />
Optical Absorption Spectroscopy (DOAS)<br />
performed in the wavelength interval 611-673 nm.<br />
It consists of three basic steps (described in detail<br />
in Wagner et al. [2003]): in the first step, the spectral<br />
DOAS fitting is caried out, taking into consideration<br />
cross sections of O2 and O4 in addition<br />
to that of water vapor. From the DOAS analysis,<br />
the water vapor slant column density (the<br />
concentration integrated along the light path) is<br />
derived. In the second step, the water vapor slant<br />
column density is corected for the non-linearity<br />
arising from the fact that the fine structure water<br />
vapor absorption lines are not spectrally resolved<br />
by the GOME instrument. In the last step, the<br />
corected water vapor slant column density is divided<br />
by a ’measured’ air mass factor which is<br />
derived from the simultaneously retrieved O4 or<br />
O2 absorptions [Wagner et al., 2003, 2005b,b].<br />
Outlook/Future work The work will be continued<br />
by applying the method to new satellite<br />
instruments like SCIAMACHY and the GOME-<br />
2-series. It can be expected that the time series<br />
can be continued until 2020.<br />
Main publication Wagner et al. [2003], Wagner<br />
et al. [2005a], Wagner et al. [2005b]
2.5. SATELLITE GROUP 87<br />
2.5.16 Analysis of MAXDOAS observations in various observing geometries<br />
Participating scientist Thomas Wagner, Nicole Bobrowski, Barbara Dix, Erna Frins, Ossama<br />
Ibrahim, Roman Sinreich<br />
Abstract MAX-DOAS measurements were caried out at various locations including ship borne<br />
measurements. Sophisticated analysis strategies were developed which can yield vertical profiles not<br />
only of the trace gases of interest, but also of aerosol properties. In addition, a new tomographic<br />
MAX-DOAS technique was developed which allows to determined three-dimensional trace gas fields.<br />
Figure 2.50: General dependence of the measured O4 absorption on various parameters of MAXDOAS<br />
observations. From MAXDOAS O4 measurements, the atmospheric aerosol properties can be derived<br />
(Wagner et al., 2004)<br />
Background The Multi AXis Differential Optical<br />
Absorption Spectroscopy (MAX-DOAS) technique<br />
allows to separate the absorptions taken<br />
place at different altitudes in the atmosphere by<br />
observing scattered sun light from a variety of<br />
viewing directions. This is possible because for<br />
most measurement conditions, the observed light<br />
is scattered in the free troposphere. Thus air<br />
masses located close to the ground are traversed<br />
on a slant absorption path determined by the<br />
viewing direction; in contrast, stratospheric air<br />
masses are traversed on a slant absorption path<br />
determined by solar zenith angle. In addition to<br />
the partial columns of various trace gases (like<br />
NO2, BrO, HCHO, etc.) also information on the<br />
aerosol profile can be retrieved (see figure).<br />
Funding See satellite group overview.<br />
Methods and results MAX-DOAS observations<br />
were caried out during coordinated compar-<br />
ison campaigns at Milano (September 2003) and<br />
Cabauw (July 2005). In addition, permanent instruments<br />
are installed at Paramaribo (Suriname)<br />
since 2002. MAXDOAS observations were also<br />
caried out during several cruises of the German research<br />
vessel Polarstern. Thes observations were<br />
used for the validation of the SCIAMACHY instrument<br />
on board of the European research satellite<br />
ENVISAT. In addition to the classical MAX-<br />
DOAS geometry, also MAX-DOAS observations<br />
of sun-illuminated targets were proposed (Frins<br />
et al., 2005). Thus measurements over well defined<br />
light paths are possible which will allow tomographic<br />
inversion of horizontal gradients.<br />
Outlook/Future work The full potential of<br />
the various MAXDOAS geometries will be further<br />
examined. Inversion schemes for trace gas<br />
and aerosol profiles will be optimised.<br />
Main publication Wagner et al. [2004]
88 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.17 Comparison of Radiative Transfer Models<br />
Participating scientist Thomas Wagner, Barbara Dix, Tim Deutschmann, Klaus-Peter Heue,<br />
Suniti Sanghavi<br />
Abstract For the interpretation of UV/vis remote sensing observations from different platforms<br />
(ground, aircraft, satellite) the atmospheric radiative transfer has to be numerically modeled. In June<br />
2005 a workshop was held at Heidelberg in order to compare the various models developed in different<br />
international research groups.<br />
Figure 2.51: MAXDOAS Box AMF for an elevation angle of 3 ◦ (360nm, no aerosol).<br />
Background During recent years the requirements<br />
on numerical models for the simulation of<br />
the atmospheric radiative transfer have been substantially<br />
increased. This is first, because complex<br />
measurement geometries have evolved, like<br />
e.g. Multi-Axis-(MAX-) DOAS observations or<br />
satellite observations over a large ground pixel.<br />
Since on the other hand, computer power has<br />
also largely increased, today’s radiative transfer<br />
models often include three dimensions and<br />
can describe complex geometries. The Heidelberg<br />
radiative transfer workshop compared Boxair<br />
mass factors (AMF) and normalised radiances<br />
for MAXDOAS geometries for various aerosol scenarios.<br />
Funding See satellite group overview.<br />
Methods and results The Heidelberg RTM<br />
workshop focused on the comparison of the results<br />
of curent RTM for DOAS observations of<br />
scattered radiation. The main focus was the modeling<br />
of various MAXDOAS geometries. Accurate<br />
modeling of MAXDOAS observations is important<br />
for satellite observations because of two<br />
main reasons: first, from the radiative transfer<br />
modeling of the rather complex MAXDOAS geometries,<br />
important and detailed conclusions on<br />
the quality of the different models can be drawn.<br />
These conclusions can be directly applied to the<br />
various satellite viewing geometries. Second, accurate<br />
atmospheric trace gas products are very<br />
important for the validation of satellite measurements,<br />
especially for tropospheric trace gases. Besides<br />
the normalise radiances, also Box-AMF for<br />
various altitudes were compared (see Figure). In<br />
general, good agreement was found. However, also<br />
discrepancies were detected, some of which could<br />
be related to the treatment of sphericity. More<br />
details on the selected comparison exercises and<br />
results can be found at http://satellite.iup.uniheidelberg.de/.<br />
Outlook/Future work Further improvements<br />
of the various model results is foreseen for the near<br />
future. Additional exercises were already selected<br />
to investigate specific dependencies like the influence<br />
of the aerosol phase function and the ground<br />
albedo. It is planned to publish the results.<br />
Main publication ACCENT [2005]
2.5. SATELLITE GROUP 89<br />
2.5.18 GOME observations of stratospheric trace gas distributions during<br />
the split vortex event in the Antarctic winter 2002<br />
Participating scientists: Walburga Wilms-Grabe, Steffen Beirle, Sven Kühl, Ulrich Platt, and<br />
Thomas Wagner<br />
Abstract In the austral winter/spring 2002, an unusual major stratospheric warming led to an early<br />
split of the south polar vortex, combined with a partly filling up of the Antarctic ozone hole. This<br />
study is dealing with distributions of ozone related trace gases (O3, NO2 and OClO) measured by<br />
GOME during the split vortex event.<br />
GOME O 3, 2002/09/27<br />
500 ><br />
DU<br />
450<br />
400<br />
350<br />
300<br />
250<br />
200<br />
150<br />
100<br />
ESA / DLR / IUP Bremen eichmann@iup.physik.uni-bremen.de <<br />
Figure 2.52: O3, NO2 and OClO-distributions above the south pole at 27 Sep. 2002, measured by<br />
GOME, retrievals of IUP Bremen (O3) and IUP Heidelberg (NO2, OClO).<br />
Background Unusual high activity of planetary<br />
waves in the southern hemisphere led to the<br />
early weakening and splitting of the south polar<br />
vortex in winter/spring 2002 and strongly affected<br />
also chemical conditions in the Antarctic atmosphere.<br />
This could be clearly seen from the premature<br />
break up of the ozone hole in the last third<br />
of September [Richter et al., 2005]. The stratospheric<br />
ozone chemistry is related to the nitrogen<br />
and to the halogene chemistry. Therefore, it<br />
is of interest to investigate the evolution of O3,<br />
NO2 and OClO during this abnormal situation,<br />
whereas OClO serves as indicator for the degree<br />
of stratospheric chlorine activation.<br />
Funding See satellite group overview.<br />
Methods and results The stratospheric ozone<br />
chemistry is closely connected to shape and<br />
strength of the vortex. Therefore, the polar<br />
ozone distribution reproduces precisely the actual<br />
state of the vortex. The break up starts at Sep.<br />
21st/22nd. Simultaneously with the weakening of<br />
the ozone hole NO2 is increasing inside the vortex.<br />
At 26/27 Sep. NO2 shows unusual high<br />
SCDs above the pole, although the ozone concentration<br />
is still relatively low in the same area<br />
(see figure). As well dynamical as chemical processes<br />
can be responsible for the increased NO2<br />
concentrations. One important aspect is the vertical<br />
misalignment and realignment of the vortex<br />
during the weakening period. Also thermal decay<br />
and rapid photolysis of NO2 reservoirs of warm<br />
mid-latitude air transported to polar regions may<br />
contribute to the NO2-enrichment. OClO evinces<br />
high chlorine activation inside the vortex at 20<br />
Sep. and is rapidly decreasing after 22 Sep. At 27<br />
Sep. GOME does not find OClO any more (figure).<br />
Even after the re-establishing of one vortex<br />
fragment by mid October over the pole no OClO<br />
was observed. The rapidity of the OClO reduction<br />
in the austral spring 2002 is anomalous. In<br />
contrary to the north pole where high yearly variability<br />
of OClO is typical, the chlorine activation<br />
above the south pole varies only slightly from year<br />
to year. In the year 2002 however the decrease of<br />
OClO starts about 10 days earlier as usual and<br />
continues for approximately 7 days only.<br />
Outlook/Future work Including measurements<br />
of polar stratospheric clouds (e.g. from<br />
ENVISAT-MIPAS) and limb observations of different<br />
trace gases by SCIAMACHY during the<br />
split vortex event can provide new insights in the<br />
chemical and dynamical interactions also with vertically<br />
resolved information.<br />
Main publication Wilms-Grabe et al. [2004],<br />
Richter et al. [2005]
90 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.5.19 Comparison of GOME NO2 retrievals analysed by different scientific<br />
groups<br />
Participating scientists: Walburga Wilms-Grabe, Steffen Beirle, Randall Martin, Andreas Richter,<br />
Michel van Roozendael, and Thomas Wagner<br />
Abstract In order to improve nonuniform GOME NO2 products of differing analysis tools applied<br />
at several institutes, NO2 SCDs have been compared for selected GOME orbits. The results show<br />
principal agreement between retrievals of IASB in Brussels, IUP Bremen and IUP Heidelberg, but in<br />
some extent clear discrepancies to retrievals of Dalhousie University in Halifax.<br />
Figure 2.53: NO2 SCDs of one GOME orbit crossing north-east of the United States and the Pacific,<br />
analysed for 03 February 1996 (left) and 06 February 2000 (right) by Heidelberg (blue), Bremen<br />
(black), Brussels (green) and Halifax (red)<br />
Background Several scientific groups are occupied<br />
with the analysis of GOME trace gas measurements.<br />
In dependence of the used retrieval<br />
tools, the resulting trace gas distributions differ<br />
from each other, though they were analyzed for<br />
the same location and time. Therefore, a comparison<br />
study is performed in order to assess the<br />
discrepancies and to evaluate the reliability of<br />
GOME products. The study is concentrated on<br />
NO2, an important trace gas for both the troposphere<br />
and stratosphere. The assessment of NO2<br />
retrievals can help all GOME data users to choose<br />
the most appropriate data set and particularly<br />
helps the provider of evaluated GOME data to<br />
unify the different existing analyzing algorithms.<br />
Funding See satellite group overview.<br />
Methods and results For the whole GOME<br />
measurement period, two GOME orbits per year<br />
have been selected as case studies: one orbit in<br />
the winter time (February) and one in the summer<br />
time (July). The chosen orbits are all located<br />
above nearly the same region, including high polluted<br />
areas in north-east of the United States and<br />
clean areas above the Pacific. This choice allows<br />
to compare NO2 retrievals for the complete orbit,<br />
but also to consider separately polluted and<br />
non-polluted parts of the orbit. In order to obtain<br />
really basic information about reasons for the<br />
variability of GOME NO2 products, in a first step<br />
pure SCDs were compared.<br />
The figure shows two examples of several NO2 retrievals.<br />
The principal agreement of all participating<br />
groups is existing. However, all selected<br />
orbits indicate better agreement between the NO2<br />
distributions of Bremen, Brussels and Heidelberg<br />
and more obvious deviations in the NO2 results<br />
of Halifax. The deviations of Halifax are related<br />
as well to the absolute SCD values (positive offset)<br />
as to the scattering of the data. In the figure,<br />
the differing scatter patterns of Halifax can<br />
be seen clearly in the region between −50 ◦ and<br />
−10 ◦ latitude. Correlations between NO2 results<br />
of Bremen, Brussels and Heidelberg lie around<br />
0.97 and 0.99 in both polluted and unpolluted regions.<br />
Correlations between data of one of these<br />
groups and data of Halifax are around 0.97 in<br />
polluted areas and about 0.55 in the less NO2enriched<br />
region between −50 ◦ and −10 ◦ latitude.<br />
Outlook/Future work Level 2 data of the<br />
DLR have to be included in the comparison study.<br />
Also VCDs and air mass factors have to be considered,<br />
the number of selected orbits has to be<br />
extended.<br />
Main publication Publication is planned later<br />
on in an advanced stage of the comparison study.
2.5. SATELLITE GROUP 91<br />
References<br />
ACCENT. 2005. Workshop on Radiative Transfer Modeling, Heidelberg.<br />
Beirle, S. 2004. Estimating source strengths and lifetime of Nitrogen Oxides from satellite data. Ph.D.<br />
thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Beirle, S., Spichtinger, N., Stohl, A., Cummins, K. L., Turner, T., Boccippio, D., Cooper, O. R.,<br />
Wenig, M., Grzegorski, M., Platt, U., & Wagner, T. 2005. Estimating the NOx produced by<br />
lightning from GOME and NLDN data: A case study in the (Gulf) of (Mexico). Atmos. Chem.<br />
Phys. Disc., 5, 11295 – 11329.<br />
Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />
P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />
Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 Abundances<br />
Retrieved from Balloon Borne Direct Sun Observations and Envisat/SCIAMACHY Limb Measurements.<br />
Atmos. Chem. Phys. Discuss., 5, 10747 – 10797. SRef-ID:1680-7375/acpd/2005-5-10747.<br />
Frankenberg, C. 2005. Retrieval of Methane and Carbon Monoxide using near infrared spectra recorded<br />
by SCIAMACHY onboard ENVISAT - Algorithm development and data analysis. Ph.D. thesis,<br />
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Frankenberg, C., Meirink, J. F., van Weele, M., Platt, U., & Wagner, T. 2005a. Assessing Methane<br />
Emissions from Global Space-Borne Observations. Science, 308(5724), 1010–1014.<br />
Frankenberg, C., Platt, U., & Wagner, T. 2005b. Iterative maximum a posteriori (IMAP)-DOAS for<br />
retrieval of strongly absorbing trace gases: Model studies for CH4 and CO2 retrieval from near<br />
infrared spectra of SCIAMACHY onboard ENVISAT. Atmos. Chem. Phys., 5, 9–22.<br />
Frankenberg, C., Platt, U., & Wagner, T. 2005c. Retrieval of CO from SCIAMACHY onboard<br />
ENVISAT: detection of strongly polluted areas and seasonal patterns in global CO abundances.<br />
Atmos. Chem. Phys., 5, 1639–1644.<br />
Grzegorski, M., Frankenberg, C., Platt, U., Wenig, M., Fournier, N., Stammes, P., & Wagner, T. 2004.<br />
Determination of cloud parameters from SCIAMACHY data for the correction of tropospheric trace<br />
gases. In: Proceedings of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria.<br />
ESA-publication SP-572, (CD-ROM).<br />
Halasia, M.-A. 2004. SMAX-DOAS observation of atmospheric trace gases on the Polarstern<br />
ANT/XX-expedition from October 2002 until February 2003. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />
<strong>Universität</strong> Heidelberg.<br />
Heue, K.-P. 2005. Airborne multi axis DOAS instrument and measurements of two dimensional<br />
tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Heue, K.-P., Beirle, S., Bruns, M., Burrows, J. P., Platt, U., Pundt, I., Richter, A., Wagner, T., &<br />
P. Wang, P. 2004. SCIAMACHY validation using the AMAXDOAS instrument. In: Proceedings<br />
of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria. ESA-publication<br />
SP-572 (CD-ROM).<br />
Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., v.Friedeburg, C., Platt, U., Pundt, I., Wang,<br />
P., & Wagner, T. 2005. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />
measurements. Atmos. Chem. Phys., 5, 1039–1051.<br />
Hollwedel, J. 2005. Observations of tropospheric and stratospheric Bromine Monoxide from satellite.<br />
Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Hollwedel, J., Wenig, M., Beirle, S., Kraus, S., Kühl, S., Wilms-Grabe, W., Platt, U., & Wagner, T.<br />
2004. Year-to-Year Variations of Spring Time Polar Tropospheric BrO as seen by GOME. Adv.<br />
Space Res., 34, 804–808. doi:10.1016/j.asr.2003.08.060.<br />
Khokhar, M.F., Frankenberg, C., Roozendael, M. Van, Beirle, S., Kühl, S., Richter, A., Platt, U.,<br />
& Wagner, T. 2005. Satellite observations of atmospheric SO2 from volcanic eruptions during the<br />
time period of 1996 to 2002. Adv. Space Res., 36, 879–887. doi:10.1016/j.asr.2005.04.114.
92 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
Kühl, S. 2005. Quantifying stratospheric chlorine chemistry by the satellite spectrometers GOME and<br />
SCIAMACHY. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Kühl, S., Dörnbrack, A., Sinnhuber, B.-M., Wilms-Grabe, W., Platt, U., & Wagner, T. 2004. Observational<br />
evidence of rapid chlorine activation by mountain waves above Northern Scandinavia. J.<br />
Geophys. Res., 109. doi:10.1029/2004JD004797.<br />
Kühl, S., Wilms-Grabe, W., Frankenberg, C., Grzegorski, M., Platt, U., & Wagner, T. 2005. Comparison<br />
of OClO Nadir measurements from SCIAMACHY and GOME. J. Adv. Space Res. in<br />
press.<br />
Marbach, T., Beirle, S., Hollwedel, J., Platt, U., & Wagner, T. 2004. Identification of tropospheric<br />
emission sources from satellite observations: Synergistic use of trace gas measurements of formaldehyde<br />
(HCHO), and nitrogen dioxide (NO2). In: Proceedings of the ENVISAT & ERS Symposium,<br />
6-10 September 2004, Salzburg, Austria. ESA publication SP-572, (CD-ROM).<br />
Pukite, J., Kühl, S., Wilms-Grabe, W., von Friedeburg, C., Deutschmann, T., Sanghavi, S., Hollwedel,<br />
J., Beirle, S., Frankenberg, C., Khokhar, M. F., Grzegorski, M., Marbach, T., Kirchof, B., Kraus, S.,<br />
Platt, U., & Wagner, T. 2005. SCIAMACHYLimb Measurements as a New Tool for Stratospheric<br />
Ozone Studies. Proceedings of the int. conference ”Integrative Approaches Towards Sustainability<br />
”Sharing””, May 11 - 14, 2005. in Jurmala, Latvia. in press.<br />
Reichl, U. 2005. Ground based spectroscopic direct Sun measurements at Timon/Northeast Brazil:<br />
Comparison of tropospheric air mass pollution during the dry and rainy season. M.Phil. thesis,<br />
University of Heidelberg, Heidelberg, Germany.<br />
Richter, A., Wittrock, F., Weber., M., Beirle, S., Kühl, S., Platt, U., Wagner, T., Wilms-Grabe, W., &<br />
Burrows, J.P. 2005. GOME observations of stratospheric trace gas distributions during the splitting<br />
vortex event in the Antarctic winter 2002 Part I: Measurements. J. Atmos. Sci., 62, 778 – 785.<br />
Sanghavi, S. 2003. An efficient Implementation of the Mie Theory to investigate the influence of<br />
Aerosols on Radiative Transfer. M.Phil. thesis, University of Heidelberg, Heidelberg, Germany.<br />
Solomon, S. 1999. Stratospheric ozone depletion: A review of concepts and History. Rev. Geophys.,<br />
37(3), 275 – 316.<br />
von Friedeburg, C. 2003. Derivation of Trace Gas Information combining Differential Optical Absorption<br />
Spectroscopy with Radiative Transfer Modelling. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />
<strong>Universität</strong> Heidelberg, Germany.<br />
Wagner, T. 2004a. Current status and future perspectives of atmospheric trace gas observations from<br />
space. Invited talk, <strong>Institut</strong>e Colloquium, MPI Mainz, Germany.<br />
Wagner, T. 2004b. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />
UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk, SO-<br />
LAS Science conference, Halifax, Canada.<br />
Wagner, T. 2004c. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />
UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk,<br />
WMO/GAW Expert Workshop, Tutzing, Germany.<br />
Wagner, T. 2004d. Moderne Methoden der Satellitenbildverarbeitung: Spektroskopie, Reflektions-,<br />
Streu-, und Absorptionsprozesse. Invited talk, WMO/GAW Expert Workshop, Tutzing, Germany.<br />
Wagner, T. 2005a. 7.5-year global trends in GOME cloud cover and humidity - a signal of climate<br />
change? Invited talk, KNMI, Utrecht, The Netherlands.<br />
Wagner, T. 2005b. Troposphärische Spurengasmessungen vom Satelliten aus. Invited talk,<br />
DECHEMA, Frankfurt, Germany.<br />
Wagner, T. 2005c. Wasserdampf-Fernerkundung mit dem ERS-2/GOME Sensor und seinen Nachfolgern.<br />
Invited talk, DWD, Offenbach, Germany.<br />
Wagner, T., Leue, C., Pfeilsticker, K., & Platt, U. 2001. Monitoring of the stratospheric chlorine<br />
activation by Global Ozone Monitoring Experiment GOME OClO measurements in the austral and<br />
boreal winters 1995 through 1999. J. Geophys. Res., 106, 4971–4986.
2.5. SATELLITE GROUP 93<br />
Wagner, T., Heland, J., M., Zöger, & U., Platt. 2003. A fast H2O total column density product from<br />
GOME - validation with in-situ aircraft measurements. Atmos. Chem. Phys., 3, 651 – 663.<br />
Wagner, T., Dix, B., von Friedeburg, C., Frieß, U., Sanghavi, S., Sinreich, R., & Platt, U. 2004.<br />
MAX-DOAS O4 measurements - a new technique to derive information on atmospheric aerosols:<br />
(I) Principles and information content. J. Geophys. Res., 109(D22205).<br />
Wagner, T., Beirle, S., Grzegorski, M., Sanghavi, S., & U., Platt. 2005a. El-Niño induced anomalies<br />
in global data sets of water vapour and cloud cover derived from GOME on ERS-2. J. Geophys.<br />
Res., 110(D15104).<br />
Wagner, T., Beirle, S., Grzegorski, M., & Platt, U. 2005b. Global trends (1996 to 2003) of total<br />
column precipitable water observed by GOME on ERS-2 and their relation to surface temperature.<br />
J. Geophys. Res. (accepted).<br />
Wilms-Grabe, W., Kühl, S., Beirle, S., Platt, U., & Wagner, T. 2004. GOME observations of stratospheric<br />
trace gas distributions during the split vortex event in the Antarctic winter 2002. Pages<br />
1053–1054 of: Proceedings Quadrennial Ozone Symposium, 1-8 June 2004, Kos, Greece.
2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 95<br />
2.6 MarHal - Modeling of marine and halogen chemistry<br />
MarHal is an independent Junior Research Group that is funded by the Deutsche Forschungsgemeinschaft<br />
in the Emmy-Noether program. The main research foci of our group are the investigation<br />
of photochemical and microphysical processes in the troposphere, especially in the marine boundary<br />
layer using numerical models.<br />
Group members<br />
Dr. Roland von Glasow, head of group<br />
Dr. Susanne Pechtl (b. Marquart), PostDoc<br />
Matthias Piot, DEA in oceanography and meteorology, PhD student<br />
Dipl. Met. Linda Smoydzin, PhD student<br />
Figure 2.54: Overview of the research topics of MarHal.<br />
Research field Seventy percent of the Earth’s surface is covered by oceans. Particles and gases are<br />
released from the ocean and have an influence on atmospheric chemistry and climate via changes of<br />
the oxidation power of the atmosphere. Furthermore, feedbacks between chemistry and, for example,<br />
cloud microphysical properties occur, that change the albedo and therefore alter the energy budget<br />
of the Earth (e.g. sulfate and sea salt aerosol particles and their role as cloud condensation nuclei).<br />
Measurements in the marine troposphere and in seawater have shown that exchanges of climatically<br />
relevant gases like dimethyl sulfide (DMS) and non-methane hydrocarbons occur which can have a<br />
significant impact on regional and even global photochemistry and climate. Furthermore, sea salt<br />
aerosol particles are produced that contain chlorine and bromine. Numerous aerosol samples have<br />
shown that marine aerosol is depleted in bromine compared to sea water. Once released to the gas<br />
phase bromine participates in ozone destruction cycles and also oxidizes dimethyl sulfide (DMS).<br />
Iodine is being released via biological processes in dramatic amounts from several coastal regions but<br />
also from the open ocean. Iodine is very efficient in destroying ozone and if concentrations of iodine<br />
oxides are high enough, new particle formation can occur.<br />
The role of halogens in tropospheric chemistry is not restricted to the marine environment. Very<br />
high mixing ratios of the radical bromine oxide have been measured during strong surface Ozone<br />
Depletion Events in polar regions in springtime and over saltlakes. In the Arctic BrO has also been<br />
implicated in so-called Mercury Depletion Events with an increase in the deposition of bioavailable,<br />
toxic mercury. Various measurements indicate that there is a significant background of the bromine
96 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
oxide radical in the troposphere, most likely in the free troposphere, which would significantly impact<br />
the background photochemistry in this sensitive environment (see 2.6.4).<br />
Although the mentioned domains appear to be very different they have striking similarities when<br />
halogen release and cycling are considered. This makes it feasible to address the associated research<br />
questions in one research group to benefit from synergies. Figure 2.54 shows schematically our research<br />
topics, making the interconnections more obvious.<br />
Methods Our research tools are numerical models. The main model is the one-dimensional model<br />
of the marine boundary layer MISTRA [von Glasow et al. , 2002a,b; von Glasow & Crutzen, 2004]<br />
that treats chemical processes in the gas phase, in and on aerosol particles, and cloud droplets. The<br />
microphysical module includes the growth of particles due to water vapor and uptake of other gases<br />
and a two-way feedback with radiation. Aqueous phase chemistry is calculated in sulfate and sea salt<br />
aerosol and - if a cloud is present - in cloud droplets that grew on each type of aerosol. The chemical<br />
mechanism comprises about 170 reactions in the gas phase and 270 reactions in and on aqueous<br />
particles for each of the four chemical bins. For some applications the model is run in Lagrangian box<br />
model mode where the relevant meteorological parameters (temperature, relative humidity, particle<br />
radius and liquid water content) are adjusted to the problem under investigation.<br />
We are developing an improved microphysical/microchemical module that will allow us to make<br />
more detailed studies of the microphysical (mainly growth) and chemical interactions of a particle<br />
population.<br />
Furthermore we have been using the global three-dimensional model MATCH-MPIC [Lawrence<br />
et al. , 1999; von Kuhlmann et al. , 2003] that uses meteorological data from numerical weather<br />
forecast reanalyses and allows to adjust the chemical mechanisms for the question in mind.<br />
Main activities All group members actively take part in model development and application.<br />
Polar halogen chemistry is being investigated by Matthias Piot (see 2.6.2) focusing on the effects<br />
of various chemical and meteorological parameters for the development of ozone depletion events.<br />
The effects of esp. organic surfactants on sea salt aerosol on particle growth and chemical processes<br />
like uptake or scavenging of gas phase compounds is the subject of Linda Smoydzin (see 2.6.3).<br />
Susanne Pechtl (b. Marquart) has developed and applied a parameterization for the nucleation of<br />
new aerosol particle from iodine vapors (see 2.6.1, Pechtl et al. [2005]). Data from a field campaign<br />
in Brittany (see C. Peters, Peters et al. [2005]) has been analysed with our model MISTRA. Together<br />
with Roland von Glasow she participated in a field campaign off the coast of New England on Appledore<br />
Island to collect data for the ongoing comparison and interpretation with numerical models.<br />
Currently, we are making comparisons focusing on iodine and chlorine chemistry and the effects on<br />
ozone and new particle formation (together with J. Stutz and O. Pikelnaya, Univ. of California, Los<br />
Angeles, W. Keene, Univ. Virginia, A. Pszenny, Univ. New Hampshire and other participants of the<br />
Appledore campaign). She is also developing the core routines of the new microphysical/microchemical<br />
model.<br />
The first global assessment of bromine chemistry in the free troposphere has been made by von<br />
Glasow et al. [2004] (see 2.6.4), showing that potentially very large sinks for ozone and DMS have<br />
been observed in previous studies. First comparisons with measurements are being made to help chose<br />
which model scenario fits best in the southern hemisphere (Schofield et al., in prep.).<br />
Effects of surface reactions on sea salt aerosol had been proposed in the literature to be of potentially<br />
great importance for the marine sulfur cycle, model results of Roland von Glasow showed,<br />
however, that the effects had been overestimated and are unlikely to be of importance (von Glasow<br />
2005, in prep.).<br />
A volcanic plume version of MISTRA was developed by Roland von Glasow and compared with<br />
measurements at Mt. Etna (see Bobrowski). With the help of Alessandro Aiuppa (Univ. of Palermo,<br />
Italy) several potential sets of initial plume conditions have been evaluated, showing that measurements<br />
of BrO and SO2 columns can very easily be reproduced by the model encouraging us to use<br />
the model to interpret the plume chemistry in this regard. The column densities of chlorine oxides,<br />
however, could not be reproduced satisfactorily, we did manage to reduce the mismatch from four<br />
orders of magnitude to a still very large factor of 30 (Bobrowski et al., submitted, von Glasow, in<br />
prep.).<br />
Colleagues from the National <strong>Institut</strong>e for Water and Atmospheric Research (NIWA) in Wellington,<br />
New Zealand, initiated a collaboration to investigate if observed seasonal variations in the δ 13 C concentrations<br />
as measured at their baseline station at Baring Head can be explained by known chlorine<br />
chemistry. Roland von Glasow has visited their group twice, the final model runs and a publication<br />
are in preparation.
2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 97<br />
Collaboration with the satellite group at the IUP include work of the detection of ship tracks in<br />
NO2 retrievals from GOME (Beirle et al. [2004]) and the spill-out of BrO from polar ODEs (Hollwedel<br />
et al., in prep., section 2.5.8).<br />
Collaborations<br />
Alfred-Wegener-<strong>Institut</strong>, Bremerhaven<br />
Cape Grim Baseline Air Pollution Station, Tasmanien, Australia<br />
Dipartimento CFTA, Università di Palermo, Italy<br />
Forschungszentrum <strong>Karls</strong>ruhe<br />
Max-Planck-<strong>Institut</strong> <strong>für</strong> Chemie, Mainz (MPI-C)<br />
National <strong>Institut</strong>e of Water and Atmospheric Research (NIWA), New Zealand<br />
National Oceanic and Atmospheric Administration, NOAA, Boulder, USA<br />
Scripps Inst. of Ocanography, University of California, San Diego (SIO), USA<br />
<strong>Universität</strong> Bremen<br />
University of California, Los Angeles (UCLA), USA<br />
University of New Hampshire, USA<br />
University of Virginia, USA<br />
Funding<br />
Deutsche Forschungsgemeinschaft, Emmy-Noether Junior Research Group MarHal<br />
Travel funds from National Science Foundation (USA), International Science and Technology<br />
Linkages Fund (New Zealand)<br />
Publications<br />
Peer Reviewed Publications<br />
1. Beirle et al. [2004]<br />
2. Fichter et al. [2005]<br />
3. Marquart et al. [2005]<br />
4. Peters et al. [2005]<br />
5. Ponater et al. [2005]<br />
6. von Glasow & Crutzen [2004]<br />
7. von Glasow et al. [2004]<br />
Grey Publications<br />
1. von Glasow [2005e]<br />
Invited Talks<br />
1. Piot & von Glasow [2005]<br />
2. von Glasow [2005f]<br />
3. von Glasow [2005d]<br />
4. von Glasow [2005c]<br />
5. von Glasow [2005b]<br />
6. von Glasow [2005g]<br />
7. von Glasow [2005h]<br />
8. von Glasow [2005i]<br />
9. von Glasow [2004a]
98 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
10. von Glasow [2004e]<br />
11. von Glasow [2004b]<br />
12. von Glasow [2004c]<br />
13. von Glasow [2004d]<br />
14. von Glasow [2005a]<br />
15. Pechtl [2005]
2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 99<br />
2.6.1 Modeling the possible role of iodine oxides in new particle formation<br />
Participating scientists Susanne Pechtl (b. Marquart), R. Lovejoy (NOAA), J. B. Burkholder<br />
(NOAA), and R. von Glasow<br />
Abstract The possible role of iodine oxides in new particle formation was investigated using the onedimensional<br />
marine boundary layer model MISTRA, extended by a parameterization for nucleation.<br />
While in a clean marine background atmosphere, OIO can be important for homogeneous nuclei<br />
formation, in a more polluted atmosphere it can only contribute to nuclei growth.<br />
Figure 2.55: Scetch of the scenarios: The model column is conditioned over different ennvironments<br />
and then moves over coastal regions with emissions of iodine compounds and later over the ocean.<br />
Background During the last years it became<br />
more and more evident that particle bursts observed<br />
in coastal regions were caused by iodine<br />
compounds that originate from marine alegae<br />
fields being exposed during low tide. It was suggested<br />
that nuclei may form via self-reaction of<br />
OIO, but the exact mechanism of particle formation<br />
and its atmospheric relevance is still uncertain.<br />
The 1D model MISTRA was used to exploit<br />
the nucleation potential of OIO under different environmental<br />
conditions, the importance compared<br />
to another nucleation mechanism, and the potential<br />
of OIO to contribute to the early growth of<br />
freshly nucleated particles.<br />
Funding DFG: Emmy Noether Junior Research<br />
Group MarHal Gl 353/1-1<br />
Methods and results The one-dimensional<br />
marine boundary layer model MISTRA includes<br />
chemistry in the gas and aerosol phase as well<br />
as aerosol microphysics. A two-step nucleation<br />
parameterization was implemented, where in the<br />
first step, the “real” nucleation process is parameterized,<br />
i.e., the formation of cluster-sized nuclei<br />
via condensation of gases. Both ternary sulfuric<br />
acid - ammonia - water nucleation and homomolecular<br />
homogeneous OIO nucleation were considered.<br />
For the latter, a parameterization was derived<br />
based on combined laboratory - model studies.<br />
The second step of the nucleation parameterization<br />
treats the “apparent” nucleation rate,<br />
i.e., the growth of clusters into the model’s lowest<br />
size bin by condensable vapors such as OIO.<br />
Different scenarios for a clean marine versus a<br />
polluted continental background atmosphere were<br />
compared. In every scenario, the air was assumed<br />
to move, independent of its origin, first over a<br />
coastal region (where it is exposed to fluxes of<br />
iodine compounds) and later over the open ocean<br />
(Figure 2.55).<br />
According to these sensitivity studies, in the<br />
clean marine background atmosphere OIO can be<br />
responsible for both homogeneous nuclei formation<br />
and the subsequent growth of the clusters to<br />
detectable sizes. In contrast to this, in the continental<br />
case with its higher levels of pollutants, gas<br />
phase OIO mixing ratios, and hence related nucleation<br />
rates, are significantly lower. Compared<br />
to ternary H2SO4-NH3-H2O nucleation, homogeneous<br />
OIO nucleation can be neglected for new<br />
particle formation in this case, but OIO can contribute<br />
to early particle growth, i.e., to apparent<br />
nucleation rates. In general, OIO was found to be<br />
more important for the growth of newly formed<br />
particles than for the formation of new nuclei itself.<br />
According to our studies, observations of particle<br />
“bursts” can only be explained by hot spotlike,<br />
not by homogeneously distributed emissions.<br />
Outlook/Future work The sensitivity studies<br />
were set up for ambient conditions encountered<br />
during the ICARTT 2004 field campaign. A detailed<br />
comparison with ICARTT results (regarding<br />
iodine oxides, nucleation, etc.) will be done in<br />
the future.<br />
Main publication Pechtl et al. [2005]
100 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.6.2 Ozone Depletion Events in the Polar Boundary Layer in Spring: A<br />
Model Study<br />
Participating scientists Matthias Piot and Roland von Glasow<br />
Abstract For more than 20 years, events with almost complete loss of ozone have been observed<br />
in the Arctic in spring. The importance of several species and meteorological parameters for these<br />
depletions have been investigated with sensitivity studies using a numerical box model.<br />
Figure 2.56: Schematic depiction of the most important processes included in the MISTRA model, applied<br />
for Arctic conditions. Fluxes over ice and sea salt production are switched ON/OFF, depending<br />
on the air composition we study.<br />
Background Reactive halogens play a major<br />
role in polar ozone depletion events (ODE): the<br />
reaction of bromine atoms with ozone, followed<br />
by the self-reaction of bromine oxides (BrO) represents<br />
a catalytic loss mechanism for ozone in the<br />
polar boundary layer (PBL). However, the triggering<br />
of the so-called ”bromine explosion” remains<br />
unclear. I present model results where prescribed<br />
bromine or chlorine fluxes are used to reproduce<br />
ODEs. I investigated the importance of several<br />
compounds for the chemistry of the PBL as well as<br />
meteorological parameters and focused on species<br />
which influence the occurrence of an ODE. This<br />
study allows us to better understand which species<br />
are important in the process of depleting ozone.<br />
Funding DFG: Emmy Noether Junior Research<br />
Group MarHal GL 353/1-1<br />
Methods and results I used the chemical and<br />
microphysical model MISTRA in the lagrangian<br />
box-model mode to study the mechanisms influencing<br />
these observed depletions in the polar<br />
boundary layer. My sensitivity studies consisted<br />
of a set of four-day runs where I changed initial<br />
mixing ratios or fluxes (or both) of 19 different<br />
species (including halogens, NOx, NOy,<br />
DMS, H2O2, HCHO...) and compared the results<br />
with base runs. The influence of temperature<br />
and humidity have also been examined. High<br />
HCHO concentrations result via increases in HO2<br />
in a redistribution of bromine species involving<br />
the aerosol phase, slowing ODEs down. Elevated<br />
DMS leads to an increase in HCHO, therefore also<br />
slowing ODEs down. By a similar production of<br />
HOx, hydrogen peroxyde (H2O2) also oxidizes Brx<br />
compounds inducing an ODE slow down. The<br />
presence of both Cl2 and Br2 in the air may lead<br />
to an unexpected decrease in the destruction process,<br />
depending on their relative mixing ratios. Increasing<br />
the mixing ratio of ethane by a factor of<br />
2 reduces the ozone mixing ratio from a partial<br />
ODE to a major ODE. For cases with low Br,<br />
ethene emphasizes the ozone loss. With high Br,<br />
it reduces the destruction process. An increase in<br />
HONO led to different eventual ozone mixing ratios,<br />
depending on its use by Brx-Clx compounds.<br />
A change in temperature or humidity modifies the<br />
liquid water content of aerosols and therefore the<br />
uptake coefficients. The recycling of halogens via<br />
the liquid phase is modified.<br />
Outlook/Future work This sensitivity study<br />
will help us investigate the potential triggers like<br />
frost flowers for the bromine explosion, using MIS-<br />
TRA in the lagrangian 1D mode.<br />
Main publication Piot and von Glasow, presentations<br />
at EGU, Vienna, 2005 and OASIS<br />
workshop, Toronto, 2005
2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 101<br />
2.6.3 Modeling Organic Films on Atmospheric Aerosol Particles and their<br />
Influence on Cloud Microphysics and Chemistry<br />
Participating scientists Linda Smoydzin, Roland von Glasow<br />
Abstract It is well known that organic material from the ocean’s surface can be incorporated into<br />
sea salt aerosols and that they often produce surface films. The relevance of these films for the gas<br />
phase and sea salt chemistry as well as for potential changes in the microphysical properties in cloud<br />
condensation nuclei is investigated.<br />
Figure 2.57: Daily course of aqueous phase concentration of HCl and HNO3 (black: organic free<br />
case, red: case with organics)<br />
Background In the last years more and more<br />
field experiments took place to characterize the<br />
chemical composition of sea salt aerosols but due<br />
to the large number and complexity of organic<br />
compounds it is only possible to determine functional<br />
groups present in the aerosol. Despite these<br />
uncertainties the measurements have shown that<br />
the organic mass fraction in fresh sea salt aerosols<br />
might be large enough to have a significant influence<br />
on cloud microphysics and atmospheric<br />
chemistry. It is assumed that surface-active organic<br />
matter of biogenic origin is enriched in the<br />
oceanic surface layer and gets into the atmosphere<br />
by bubble bursting. Surface active organic matter<br />
present in sea salt aerosols can lead to a decrease<br />
of the aerosol’s surface tension which reduces the<br />
mass transfer between the gas phase and liquid<br />
phase as well as water uptake into the aerosol.<br />
Funding DFG: Emmy Noether Junior Research<br />
Group MarHal GL 353/1-1<br />
Methods and results For studying the effect<br />
of organic surfactants a one-dimensional numerical<br />
model which contains a microphysics scheme<br />
and a detailed description of chemistry in the gas<br />
phase, in aerosol particles and in cloud droplets<br />
is used. Chemical composition and hygroscopic<br />
properties of aerosols are important aspects when<br />
regarding droplet formation and droplet growth.<br />
With simple assumptions simulating an organic<br />
film on the aerosol we tested how strong the influence<br />
of surfactants on cloud microphysics in<br />
our model is. The decrease in water uptake and<br />
a decreased solubility of the aerosol due to the<br />
organic mass fraction leads to an increase in the<br />
number of small aerosol particles. The observed<br />
changes in the aerosol size distribution, however,<br />
were small and might be negligible when considering<br />
droplet growth and cloud cover.<br />
Regarding the influence of organic matter on<br />
chemistry it is assumed that sea salt aerosols emitted<br />
from the ocean contain fatty acids which are<br />
known to be film forming compounds. The organic<br />
coating which hinders mass transfer between<br />
the gas and liquid phase is destroyed by reaction<br />
of the fatty acid with ozone. In fig. 2.57 the daily<br />
course of HNO3 and HCl for a three days model<br />
run is shown. Measurements have shown that an<br />
average organic mass fraction of 5-10% can be assumed.<br />
Although the organic mass fraction in this<br />
model run is less than 5% the uptake into the liquid<br />
phase is decreased as can be seen in lower<br />
concentrations in the case where organics were<br />
present in the aerosol. Coupled with the lower<br />
uptake into the liquid phase might be a change in<br />
the aerosol’s pH which also changes the chemical<br />
properties of the aerosol.<br />
Outlook/Future work Further investigation<br />
needs to be done to verify the uncertainties regarding<br />
the question of how strong the influence<br />
of organics really is and which chemical processes<br />
are affected exactly.
102 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.6.4 Impact of reactive bromine chemistry in the troposphere<br />
Participating scientists Roland von Glasow, R. von Kuhlmann (MPI-C), M. G. Lawrence (MPI-<br />
C), U. Platt, and P. J. Crutzen (MPI-C, SIO)<br />
Abstract The potential impact of 0.5 - 2 pmol mol −1 BrO on the photochemistry in the free<br />
troposphere was investigated with the help of a global three-dimensional transport model. Annual<br />
zonal mean ozone mixing ratios are reduced by up to 20 % pointing to a potentially very significant<br />
ozone loss process that has been ignored so far.<br />
Figure 2.58: Annually and zonally averaged ratio of O3 in a model run with bromine chemistry to O3<br />
in a run without bromine. The ordinate is the σ-level multiplied by 1000 which is approximately the<br />
pressure in hPa and the abscissa is latitude in degrees.<br />
Background Satellite observations suggest the<br />
widespread presence of BrO in the troposphere<br />
also outside the polar regions with global background<br />
vertical columns of about 1-3 × 10 13<br />
molec cm −2 , corresponding to BrO mixing ratios<br />
of 0.5-2 pmol mol −1 if uniformly mixed in the<br />
troposphere. The synopsis of the various measurmenets<br />
indicates that the tropospheric BrO<br />
was mainly located within the free troposphere<br />
(FT). The sources for reactive bromine in the free<br />
troposphere are thought to include the decomposition<br />
of organic bromine compounds, release from<br />
sea salt aerosol and upward transport, downward<br />
transport from the stratosphere, upward transport<br />
from ”ozone depletion events” in the polar<br />
boundary layers during spring (”spillout”), and<br />
release from slowly erupting volcanoes but a quantification<br />
of these processes remains to be made.<br />
Funding DFG: Emmy Noether Junior Research<br />
Group MarHal Gl 353/1-1<br />
Methods and results We used the global atmospheric<br />
chemistry transport model MATCH-<br />
MPIC and prescribed bromine sources to reproduce<br />
the observed BrO vertical columns taking<br />
inorganic gas phase chemistry and recycling on<br />
sulfate aerosol surfaces into account. Our vertical<br />
tropospheric columns are 0.3 - 2.4 x 10 13<br />
molec cm −2 corresponding to BrO mixing ratios<br />
of >0.1 to 2 pmol mol −1 . This amount of reactive<br />
bromine lead to a reduction in the zonal annual<br />
mean O3 mixing ratio of up to 18% in widespread<br />
areas, and regionally up to 40% compared to a<br />
model run without bromine chemistry. The lifetime<br />
of inorganic bromine was increased due to the<br />
recycling on sulfate aerosol and ranged from about<br />
ten days in the lower troposphere to 20 days in the<br />
upper troposphere. According to the model the<br />
changes in ozone were not only due to photochemical<br />
ozone destruction but also due to a reduction<br />
of ozone production as evident by changes in the<br />
HO2 : OH ratio that also affected the mixing ratios<br />
of NOx and PAN. Our lower limit estimate<br />
of the effect of BrO on dimethyl sulfide (DMS) in<br />
the marine boundary layer showed that the effect<br />
was even larger than on ozone, with up to 60%<br />
reduction of DMS tropospheric column. This is<br />
accompanied by dramatic changes in DMS oxidation<br />
pathways, reducing sulphate production and<br />
hence its cooling effect on climate. These results<br />
highlight a significant missing component in the<br />
tropospheric budgets of ozone and DMS.<br />
Outlook/Future work We will use our experience<br />
from the process modeling to developing<br />
parameterizations for the sources of inorganic<br />
bromine as well as a reduced reaction mechanism.<br />
Main publication von Glasow et al. [2004]
2.6. MARHAL - MODELING OF MARINE AND HALOGEN CHEMISTRY 103<br />
References<br />
Beirle, S., Platt, U., von Glasow, R., Wenig, M., & Wagner, T. 2004. Estimate of nitrogen<br />
oxide emissions from shipping by satellite remote sensing. Geophys. Res. Lett., 31, L18102,<br />
doi:10.1029/2004GL020312.<br />
Fichter, C., Marquart, S., Sausen, R., & Lee, D. S. 2005. The impact of cruise altitude on contrails<br />
and related radiative forcing. Met. Zeitsch., 14, 563 – 572.<br />
Lawrence, M. G., Crutzen, P. J., Rasch, P. J., Eaton, B. E., & Mahowald, N. M. 1999. A model<br />
for studies of tropospheric photochemistry: Description, global distributions, and evaluation. J.<br />
Geophys. Res., 104, 26245 – 26277.<br />
Marquart, S., Ponater, M., Ström, L., & Gierens, K. 2005. An upgraded estimate of the radiative<br />
forcing of cryoplane contrails. Met. Zeitsch., 14, 573 – 582.<br />
Pechtl, S. 2005. Halogenchemie in der Troposphäre: Überblick und Beispiele <strong>für</strong> Prozessstudien mit<br />
numerischen Modellen. Invited talk at the DLR, Oberpfaffenhofen, 15.11.2005.<br />
Pechtl, S., Lovejoy, E. R., Burkholder, J. B., & von Glasow, R. 2005. Modeling the possible role of<br />
iodine oxides in atmospheric new particle formation. Atmos. Chem. Phys. Discuss., 5, 9907 – 9952.<br />
Peters, C., Pechtl, S., Stutz, J., Hebestreit, K., Hönninger, G., Heumann, K. G., Schwarz, A., Winterlik,<br />
J., & Platt, U. 2005. Reactive and organic halogen species in three different European coastal<br />
environments. Atmos. Chem. Phys., 5, accepted.<br />
Piot, M., & von Glasow, R. 2005. Sensitivity studies of ODEs and frost flowers with a numerical<br />
model. Invited talk at the OASIS workshop, Toronto, Canada, 20.09.2005.<br />
Ponater, M., Marquart, S., Sausen, R., & Schumann, U. 2005. On contrail climate sensitivity. Geophys.<br />
Res. Lett., 32, L10706, doi: 10.1029/2005GL02258.<br />
von Glasow, R. 2004a. Halogenchemie in der Troposphäre - Untersuchungen mit numerischen Modellen.<br />
Invited talk at the Insitut <strong>für</strong> Meteorologie und Klimaforschung, <strong>Karls</strong>ruhe, 02.11.2004.<br />
von Glasow, R. 2004b. Links between sulfur and halogen chemistry and implications for our climate.<br />
Invited talk at the Afred-Wegener-<strong>Institut</strong> <strong>für</strong> Meeresforschung, Bremerhaven, 05.02.2004.<br />
von Glasow, R. 2004c. Modeling of halogen chemistry: Overview and impact on sulfur cycle. Invited<br />
talk at the EGU meeting, Nice, 2004.<br />
von Glasow, R. 2004d. Sea salt aerosol chemistry: Brief overview and recent modeling results. Invited<br />
talk at the AAAR meeting, Atlanta, 2004.<br />
von Glasow, R. 2004e. Tropospheric halogen chemistry and its implications for O3 and sulfur in<br />
the boundary layer and free troposphere. Invited talk at the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, Bremen,<br />
06.02.2004.<br />
von Glasow, R. 2005a. Invited talk at the AGU meeting, San Francisco, 2005.<br />
von Glasow, R. 2005b. Halogenchemie in der Troposphäre - Untersuchungen der Wechselwirkungen<br />
mit Ozon und Schwefel in Prozess- und globalen Modellstudien. Invited talk at the <strong>Institut</strong> <strong>für</strong><br />
Troposphärenforschung, Leipzig, 12.05.2005.<br />
von Glasow, R. 2005c. Impact of bromine on tropospheric photochemistry. Invited talk at the<br />
IGAC/SPARC workshop, Mainz, 19.05.2005.<br />
von Glasow, R. 2005d. Importance of the surface reaction OH + Cl- on sea salt aerosol for the<br />
chemistry of the MBL - a model study. Invited talk at the EMSI Workshop on Ions and Molecules<br />
at Aqueous Interfaces, Prague, Czech Republic, 27.06.2005.<br />
von Glasow, R. 2005e. Lead Essay - Research Front Iodine. Env. Chem., 2, in press.<br />
von Glasow, R. 2005f. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />
NIWA, Lauder, New Zealand, 15.09.2005.
104 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
von Glasow, R. 2005g. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />
Harvard Univ., Cambridge, MA, USA, 08.04.2005.<br />
von Glasow, R. 2005h. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />
the Univ. New Hampshire, Durham, USA, 07.04.2005.<br />
von Glasow, R. 2005i. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk at<br />
the Univ. of East Anglia, Norwich, UK, 28.02.05.<br />
von Glasow, R., & Crutzen, P. J. 2004. Model study of multiphase DMS oxidation with a focus on<br />
halogens. Atmos. Chem. Phys., 4, 589 – 608.<br />
von Glasow, R., Sander, R., Bott, A., & Crutzen, P. J. 2002a. Modeling halogen chemistry in the marine<br />
boundary layer. 1. Cloud-free MBL. J. Geophys. Res., 107, 4341, doi: 10.1029/2001JD000942.<br />
von Glasow, R., Sander, R., Bott, A., & Crutzen, P. J. 2002b. Modeling halogen chemistry in the<br />
marine boundary layer. 2. Interactions with sulfur and cloud-covered MBL. J. Geophys. Res., 107,<br />
4323, doi: 10.1029/2001JD000943.<br />
von Glasow, R., von Kuhlmann, R., Lawrence, M. G., Platt, U., & Crutzen, P. J. 2004. Impact of<br />
reactive bromine chemistry in the troposphere. Atmos. Chem. Phys., 4, 2481 – 2497.<br />
von Kuhlmann, R., Lawrence, M. G., Crutzen, P. J., & Rasch, P. J. 2003. A Model for Studies of<br />
Tropospheric Ozone and Non-Methane Hydrocarbons: Model Description and Ozone Results. J.<br />
Geophys. Res., 108, 4294, doi:10.1029/2002JD002893.
2.7. CARBON CYCLE GROUP 105<br />
2.7 Carbon Cycle Group<br />
Christel Facklam (Techn.), Samuel Hammer (PhD), Renate Heinz (Techn.), Ingeborg<br />
Levin (GL), Tobias Naegler (Post Doc), Christoph Schönherr (Dipl.), Cordelia Veidt<br />
(PhD, since Oct. 2005).<br />
High precision greenhouse gases observations (CO2, CH4, N2O, H2O), together with their isotope<br />
ratios as well as related tracer (CO, H2, SF6, 222 Radon) measurements are performed on the global,<br />
continental and regional scale. These measurements are used in combination with regional and trajectory<br />
models to study respective source and sink processes and with global box models to investigate<br />
their biogeochemical cycles.<br />
Figure 2.59: Map of monitoring stations and measurement platforms where trace gas and isotope<br />
samples are collected for analysis<br />
Overarching topic: Investigation of the regional and global biogeochemical cycles of CO2, CH4,<br />
N2O and H2<br />
Background: Increasing greenhouse gases in the atmosphere are a major player in Earth climate<br />
change; quantitatively understanding the causes of this increase is an indispensable pre-requisite for<br />
future climate prognoses. The most reliable information on the bio-geochemical cycles of greenhouse<br />
gases come from long term atmospheric observations combined with modelling. The Heidelberg Carbon<br />
Cycle Group is significantly contributing to this international effort by providing unique (isotopic)<br />
measurements as well as validation tracer techniques and budget modelling.<br />
Main methods: The Group is running a high-precision gas chromatography (GC) laboratory (see<br />
Hammer, article 2.7.3, this issue) and is responsible for the stable isotope ratio mass spectrometry<br />
(IRMS) laboratory of the <strong>Institut</strong>e. Deuterium measurements in atmospheric methane samples are<br />
made by IRMS and - in addition - by Tunable Laser Spectroskopy in co-operation with the MPI<br />
<strong>für</strong> Kernphysik, Heidelberg (Prof. T. Röckmann). A unique global network for continuous 14 CO2<br />
observations is maintained in collaboration with the Radiocarbon Laboratory [Levin & Hesshaimer,<br />
2000, see also article 2.7.1 from Levin & Kromer, this issue, and section 6.1, this issue]. Atmospheric<br />
transport tracers such as 222 Radon [Levin et al. , 2002] and SF6, analysed in collaboration with the<br />
Limnology group (Ilmberger, section 4.2, this issue) are measured at global and European sites for<br />
transport model validation and source estimates with the Radon-Tracer-Method [Levin et al. , 1999].<br />
A global box model for CO2 and its isotopes was developed in the last years (Naegler, article 2.7.2,<br />
this issue) which is currently adapted for other greenhouse gases budgets as well as tracers such as<br />
Beryllium isotopes in collaboration with the Glaciology Group (Wagenbach, section 3.2, this issue).<br />
Major activities of the year: As most of our work strongly relies on the precise measurement of<br />
mixing ratios by gas chromatography, and as there was no funding available for investment of a new
106 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
instrument (the GC for greenhouse gases has been purchased in 1994 and that for CO measurements<br />
is a permanent loan from Forschungszentrum Jülich (Dr. A. Volz-Thomas)) we made a special effort<br />
to modernise and couple these two systems including completely new hard- and software for data<br />
acquisition and evaluation. This work has been finalised in 2005 (see Hammer, article 2.7.3, this issue<br />
and Schönherr [2005]) and led to a significant improvement of measurement precision in addition to<br />
the capability to now also analyse atmospheric Hydrogen mixing ratios at high precision.<br />
The scientific highlight of the last year concerns a question on which the group has worked now<br />
since more than one decade, namely quantitatively closing the global budget of bomb radiocarbon<br />
in the carbon system. The problem of a serious mismatch in the budget was first presented by<br />
Hesshaimer et al. [1994] in Nature, suggesting an over-estimate of the bomb 14 C inventory of the<br />
world oceans. This problem was furtheron discussed in the scientific literature and has now finally<br />
come to a solution after new (reduced) oceanic 14 C inventories had been published in 2004 for two<br />
points in time [Peacock, 2004; Key et al. , 2004]. In his PhD thesis, Tobias Naegler was now able<br />
to derive a quantitatively consistent bomb 14 C budget with help of the GRACE model, and could<br />
estimate the total bomb 14 C inventory in the carbon system [Naegler, 2005]. This now serves as the<br />
main tool for future modelling of 14 CO2 in the global atmosphere on the basis of our unique highprecision<br />
world-wide 14 CO2 observations (Levin and Kromer, article 2.7.1, this issue) to use 14 C as a<br />
quantitative constraint to determine exchange rates and turnover times in the global carbon cycle.<br />
Besides the projects performed by individual scientists of the group we have been part of two<br />
EU-funded projects, MethMonitEUr and TCOS-Siberia. MethMonitEUr aimed at harmonising and<br />
evaluating continuous CH4 observations in Europe which are used to determine the European budget of<br />
CH4 emissions. MethMonitEUr also supported our CH4 isotope measurements at Alert (discontinued<br />
in 2004) and Neumayer station. TCOS-Siberia aims at determining the carbon budget of Western<br />
Russia and Siberia. Here we contribute with trace gas and CO2 stable isotope measurements of flask<br />
samples collected during regular aircraft profiling at Syktyvkar (Ural Mountains) and Cherskii (Polar<br />
Eastern part of Siberia). Both projects end in 2005 but extension is applied for at the EU.<br />
How are single projects linked? Projects are linked by common measurement techniques and<br />
monitoring stations (i.e. Heidelberg, Schauinsland, Neumayer, Alert etc.). Data evaluation and<br />
interpretation on different scales is naturally linked through common source and sink distributions<br />
of the different greenhouse gases, such as biospheric, anthropogenic, chemical oxidation/destruction.<br />
Common modelling techniques and using tracers such as 222 Radon or trajectories are applied in the<br />
different projects.<br />
External Collaborations:<br />
MPI for Biogeochemistry, Jena (Prof. Martin Heimann, Dr. Armin Jordan, Dr. Ute Karstens, Olaf<br />
Kolle, Prof. Detlef Schulze, Dr. Axel Steinhof), German Umweltbundesamt (Prof. <strong>Ruprecht</strong> Schleyer,<br />
Frank Meinhardt), Forschungszentrum Jülich (Dr. Andreas Volz-Thomas), MPI <strong>für</strong> Kernphysik, Heidelberg<br />
(Prof. Thomas Röckmann), AWI Bremerhaven (Dr. Rolf Weller), Univ. Frankfurt, Inst. <strong>für</strong><br />
Meteorologie (Dr. Andreas Engel), LSCE, Gif-sur-Yvette, France, (Dr. Philippe Ciais, Dr. Martina<br />
Schmidt), Royal Holloway, Univ. of London, Egham, UK (Prof. Euan Nisbet), Meteorological Service<br />
of Canada, Toronto (Douglas Worthy), Krakow University (Prof. Kazimierz Rozanski), and many<br />
others.<br />
Funding: The scientific work of the group is mainly funded by research grants from the EU (TACOS,<br />
MethMonitEUr, TCOS-Siberia and CarboEurope-IP) and DFG (Atmospheric Radiocarbon).<br />
Publications<br />
Peer Revied Publications<br />
1. Levin & Kromer [2004]<br />
2. Röckmann & Levin [2005]<br />
Doctoral Theses<br />
1. Naegler [2005]
2.7. CARBON CYCLE GROUP 107<br />
Diploma Theses<br />
1. Schönherr [2005]<br />
2. Schell [2004]<br />
Invited Talks<br />
1. Levin [2004b]<br />
2. Levin [2004a]<br />
3. Levin [2005a]<br />
4. Levin [2005b]
108 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.7.1 Global long-term observations of Radiocarbon in atmospheric CO2,<br />
revisited<br />
Participating scientist Ingeborg Levin, the Radiocarbon Laboratory, Bernd Kromer<br />
Abstract A global network of high-precision atmospheric 14 CO2 observations is maintained, providing<br />
an independent constraint for carbon cycle modelling. Apart from this innovative application<br />
important in research of the anthropogenic CO2 problematic also various modern dating techniques<br />
make use of our unique 14 C records [Mayorga et al. , 2005; Spalding et al. , 2005].<br />
Figure 2.60: Observed ∆ 14 C in atmospheric CO2 and tree rings<br />
Background Initiated by the late Karl Otto<br />
Münnich, Heidelberg was among the first laboratories<br />
involved in precise long-term observations of<br />
bomb 14 C perturbations in the global carbon system.<br />
Related atmospheric 14 CO2 monitoring extended<br />
globally and carried into the present time<br />
constitutes a world-wide unique exercise [Levin<br />
& Hesshaimer, 2000]. This long-term and sometimes<br />
painful effort of the Carbon Cycle Group at<br />
IUP now offers a wealth of intriguing applications<br />
which range from environmental issues like studying<br />
global carbon cycle dynamics to life science<br />
and forensic aspects.<br />
Methods and results Continuous bi-weekly<br />
integrated CO2 samples are collected at eight<br />
globally distributed background stations as well<br />
as in Germany in the Black Forest (Schauinsland)<br />
and in Heidelberg (Schönherr, article 2.7.4, this<br />
issue) and are analysed at high precision for their<br />
14 C activity by conventional radioactive counting<br />
(Kromer, section 6.1, this issue). The long term<br />
trend of ∆ 14 C in CO2 in the Northern Hemisphere<br />
troposphere from 1959 until 2005 is displayed in<br />
Figure 2.60 [Levin & Kromer, 2004]. Due to atmospheric<br />
nuclear weapon testing in the 1950s and<br />
early 1960s the atmospheric 14 CO2 level increased<br />
by about a factor of two (∆ 14 C≈1000�) compared<br />
to the natural reference level. The present<br />
steady decline which is mainly driven by the ex-<br />
change with oceanic CO2 and by input of 14 C-free<br />
fossil fuel CO2 into the atmosphere are underlain<br />
relatively weak perturbations. These secondary<br />
variations reflect interesting processes, for example<br />
the very regular seasonal cycle of 14 CO2 at mid<br />
latitude northern hemispheric sites today (inlay of<br />
Figure 2.60) are mainly caused by stratospheretroposphere<br />
exchange and by the seasonal release<br />
of bomb 14 C stored in the biosphere for the last<br />
50 years now re-entering the atmosphere (Naegler,<br />
article 2.7.2, this issue). This recent net source of<br />
bomb 14 C to the atmosphere is also reflected in<br />
a tropical 14 CO2 maximum while a relative minimum<br />
is observed in mid-to-high southern latitude<br />
which is caused by disequilibrium fluxes between<br />
ocean surface water and the atmosphere [Levin &<br />
Hesshaimer, 2000].<br />
Outlook/Future work The small but significant<br />
signals observed in atmospheric 14 CO2 are<br />
used in combination with the GRACE model<br />
(Naegler, article 2.7.2, this issue) and more sophisticated<br />
global 3-dimensional models to put independent<br />
constraints on carbon exchange on earth.<br />
Main publication: Levin & Kromer [2004]<br />
Funding Funding: CarboEurope-IP, DFG (Atmospheric<br />
Radiocarbon).
2.7. CARBON CYCLE GROUP 109<br />
2.7.2 Simulating Bomb Radiocarbon: Implications for the Global Carbon<br />
Cycle<br />
Participating scientist Tobias Naegler, Vago Hesshaimer, Ingeborg Levin, Philippe Ciais (LSCE,<br />
Gif-Sur-Yvette, France), Keith Rodgers (LODYC, Paris, France)<br />
Abstract With the help of the two-dimensional global (radio-)carbon cycle model GRACE, we<br />
estimated the total production of bomb 14 C and simulated bomb 14 C inventories in the main carbon<br />
cycle reservoirs. Furthermore, we exploited the constraints that observed bomb 14 C inventories impose<br />
on stratosphere-troposphere and air-sea gas exchange.<br />
Figure 2.61: Observed (symbols) and simulated<br />
(lines) bomb 14 C inventories in the troposphere,<br />
stratosphere, biosphere and ocean. The black<br />
line denotes the total simulated accumulated<br />
bomb 14 C production, the black symbols the<br />
”observation-based” total inventory.<br />
Background Bomb radiocarbon has been produced<br />
in atmospheric nuclear bomb tests. It<br />
is injected mainly into the stratosphere. Oxydised<br />
to 14 CO2, it takes part in the global carbon<br />
cycle. The production of bomb radiocarbon<br />
peaks sharply in the late 1950s and early 1960s.<br />
Due to this pulse-like injection, bomb radiocarbon<br />
acts like a one-time release of a dye-tracer<br />
into the stratosphere. The analysis of the subsequent<br />
distribution of bomb 14 C in the earth system<br />
allows to constrain exchange times between<br />
the main carbon reservoirs stratosphere, troposphere,<br />
biosphere and ocean, e.g. to quantify<br />
stratosphere-troposphere exchange (STE), the atmospheric<br />
interhemispheric exchange time, air-sea<br />
gas exchange and turnover times of biospheric carbon<br />
pools.<br />
Methods and results We simulated the<br />
global bomb radiocarbon cycle with the Global<br />
RAdioCarbon Exploration model GRACE, consisting<br />
of a 22-box zonally averaged twodimensional<br />
atmosphere coupled to a well-mixed<br />
4-reservoir biosphere. Radiocarbon exchange between<br />
atmosphere and the ocean was calculated<br />
according to observed tropospheric and ocean surface<br />
∆ 14 C . The model comprises all relevant<br />
sources of radiocarbon (natural, bomb and industrial<br />
production). The seasonal air mass exchange<br />
between model boxes was calibrated with stratospheric<br />
and tropospheric 14 CO2 observations as<br />
well as tropospheric observations of SF6 and the<br />
10 Be/ 7 Be ratio. The simulated air mass transport<br />
across the tropopause then gives an estimate<br />
of the effective STE necessary to reproduce the<br />
observed tracer distributions. The total radiocarbon<br />
production by atmospheric nuclear bomb<br />
tests was determined with the help of the model<br />
and available stratospheric and tropospheric radiocarbon<br />
observations. The model simulated<br />
the distribution of bomb radiocarbon among the<br />
carbon reservoirs stratosphere, troposphere, biosphere,<br />
and ocean. Simulated bomb radiocarbon<br />
inventories turned out to be in very good agreement<br />
with all available stratospheric and tropospheric<br />
radiocarbon observations as well as with<br />
the latest estimates of the ocean bomb radiocarbon<br />
inventories during the GEOSECS and WOCE<br />
surveys [Peacock, 2004; Key et al. , 2004]. For<br />
the very first time, the GRACE model is thus capable<br />
of closing the bomb radiocarbon budget in<br />
the global carbon system. Using the available latest<br />
atmospheric and oceanic (radio-) carbon data,<br />
we developed a new, improved parameterisation<br />
of air-sea gas exchange which is easily adaptable<br />
to new estimates of the ocean bomb 14 C inventory<br />
and the global wind speeds, two significant sources<br />
of uncertainty in this approach. Furthermore, we<br />
estimated an observation-based biospheric bomb<br />
14 C inventory which can be used to constrain the<br />
setup and parameterisation of biosphere models.<br />
Outlook/Future work We will analyse in detail<br />
bomb 14 C constraints on biospheric parameters.<br />
Furthermore, the GRACE model will be<br />
improved by adding an ocean module, allowing<br />
carbon isotope simulations in the coupled<br />
atmosphere-ocean-biosphere system.<br />
Main publication: Naegler [2005]<br />
Funding This PhD thesis was a close collaboration<br />
with the LSCE, Gif-sur-Yvette, France and<br />
has been funded by the EU projects AEROCARB<br />
and CarboEurope-IP and by the DFG.
110 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
2.7.3 Coupling and modernisation of the Heidelberg Greenhouse Gases<br />
and CO - GC systems for continuous measurements<br />
Participating scientists Samuel Hammer, Christoph Schönherr, Christl Facklam, Ingeborg Levin<br />
Abstract Two separate GC instruments were combined via one sample inlet system. The data<br />
acquisition and evaluation software was modernised. In addition, it is now possible to determine<br />
molecular hydrogen mixing ratios. The rebuilding led to higher measurement precision and a reduction<br />
of sample volume and analysis time, both by a factor of two, and the data output is now homogenised<br />
for all sample components.<br />
Background The radiative forcing due to anthropogenic<br />
Greenhouse Gases released into the<br />
atmosphere accounts for approximately 1.5 W/m 2<br />
and is therefore the main contributor to global<br />
warming [Hansen et al. , n.d.]. Long term greenhouse<br />
gas records of high quality are important<br />
to determine the temporal change of these trace<br />
gases. Combined with isotopic data and regional<br />
or global models, the respective budgets can be<br />
investigated. In combination with 222 Rn data, local<br />
source and sink studies for greenhouse gases<br />
can be carried out.<br />
Funding This PhD work is funded by the EU<br />
projects TCOS - Siberia and CarboEurope-IP.<br />
Methods and results In order to couple the<br />
GCs by connecting the sample loops of both GCs<br />
in series, it was necessary to rebuild the sample<br />
inlet system. In addition, the capacity for<br />
flask sample measurements was doubled using a<br />
separate flask valve. It is now possible to measure<br />
twelve flasks within one sequence. To improve<br />
the CO reproducibility, a dedicated system<br />
of a backflush valve and resistances was developed<br />
and successfully installed. Along with the installation<br />
of these additional valves, the electronics<br />
devices were improved. The two former separate<br />
data acquisition systems were replaced by a new,<br />
state of the art, ChemStation Chromatography<br />
software. The rebuilding led to reduced sample<br />
volume and analysis time, which is particularly<br />
important for flask measurements. For the semicontinuous<br />
measurements in Heidelberg we gained<br />
a homogenised dataset. Since the rebuilding of<br />
the GC it is possible to determine H2 mixing ratios<br />
without further needs. The combined instrument<br />
now performs measurements of CO2, CH4,<br />
CO, N2O, SF6 and H2 every five minutes. Outside<br />
air is measured semi-continuously via two separate<br />
air intake lines, each of which is sampled at least<br />
once every 30 minutes. An example of the time<br />
series and the correlations between the different<br />
gas species is given in Figure 2.62.<br />
Figure 2.62: Half hourly mixing ratios of CO2,<br />
CO, CH4, N2O and H2 in Heidelberg. SW and<br />
SE mark the south-west and south-east air intake<br />
lines. Additionally 222 Rn daughter concentration<br />
and meteorological parameters are shown.<br />
Outlook/Future work It is now planned to<br />
apply the radon tracer method to the continuous<br />
H2 data to assess the sink strength of local soils.<br />
Furthermore, a detailed study on the vertical H2<br />
profile in soil air is planned to be performed by<br />
a diploma student. The long and extensive N2O<br />
records from worldwide monitoring stations will<br />
be analysed in a simple 2D model (Naegler, article<br />
2.7.2 this issue) to improve our understanding<br />
of the global N2O budget.
2.7. CARBON CYCLE GROUP 111<br />
2.7.4 Investigating CO2, CO and Fossil Fuel CO2 in Heidelberg<br />
Participating scientists Christoph Schönherr, Samuel Hammer, Bernd Kromer, Ulrike Gamnitzer,<br />
Ingeborg Levin<br />
Abstract In order to calibrate CO as a proxy for fossil fuel CO2 (CO2(fossil)), atmospheric CO<br />
mixing ratios in Heidelberg are being related to (CO2(fossil)) mixing ratios derived from 14 CO2 measurements.<br />
For extension of these investigations to sites without continuous gas chromatographic<br />
measurements, a device for integrated air sampling in a large bag was set up and tested.<br />
Figure 2.63: Integrated samples of CO2, CO, and 14 CO2 taken in Heidelberg for determination of the<br />
ratio CO/CO2(fossil). Blue symbols represent winter months, red symbols summer months; dotted<br />
lines are background mixing ratios. (a) Average CO2(total) mixing ratios during the respective<br />
sampling periods. (b) Same as (a), but for CO mixing ratios. (c) 14 CO2 depletions of the integrated<br />
samples, relative to the continental background. (d) CO2(fossil) mixing ratio as calculated from the<br />
CO2(total) mixing ratio and the 14 CO2 depletion. (e) CO/CO2(fossil) ratios for each sample, and<br />
the average ratio for all samples (solid black line).<br />
Background The global atmospheric mixing<br />
ratio of CO2 has been rising from about 280 ppm<br />
at the beginning of the 19th century to 378 ppm<br />
by the end of 2004, mainly due to the combustion<br />
of fossil fuels. This influences the Earth’s climate<br />
at present and very likely in the future. In order<br />
to estimate fluxes of CO2 into the atmosphere,<br />
it is necessary to separate the share originating<br />
from fossil fuel combustion. This can be achieved<br />
by radiocarbon ( 14 C) observations [Levin et al. ,<br />
2003], or by observation of another proxy, like carbon<br />
monoxide [Gamnitzer, 2003]. This proxy then<br />
has to be calibrated first by parallel 14 C measurements.<br />
Methods and results In a first part of my<br />
Diploma Thesis, the local gas chromatographic<br />
system (GC) was modernised for easier operation<br />
and more convenient data output. Second, using<br />
CO and 14 CO2 data from the years 2001 to<br />
2005, the CO/CO2(fossil) ratio for Heidelberg was<br />
studied. Samples taken during atmospheric inver-<br />
sion situations (events) with high local emissions<br />
signals yielded CO/CO2(fossil)=(1.06±0.33)%.<br />
Weekly and two-weekly integrated 14 CO2 samples<br />
influenced by a larger catchment area yielded a<br />
mean CO/CO2(fossil) ratio of (1.33 ± 0.29) %.<br />
Both methods can be used to assess fossil fuel<br />
CO2 for differently sized catchment areas. For<br />
determination of CO/CO2(fossil) at sites without<br />
continuous GC measurements, a device for integrated<br />
air sampling was set up and tested. This<br />
device is suited for non-biased sampling of CO2,<br />
CO, CH4, N2O, and SF6 during one week.<br />
Outlook/Future work The devices for integrated<br />
air sampling will now be set up in Paris and<br />
Krakow in the frame of the CarboEurope-IP to be<br />
run in parallel to integrated 14 CO2 measurements,<br />
in order to determine the regional CO/CO2(fossil)<br />
ratio with different emission characteristics.<br />
Main publication: Schönherr [2005]
112 CHAPTER 2. ATMOSPHERE AND REMOTE SENSING<br />
References<br />
Gamnitzer, U. 2003. Bilanzierung der Kohlendioxidemissionen in der Region Heidelberg mit Hilfe<br />
atmosphärischer CO2-, 14 CO2- und CO-Messungen. Diploma thesis, University of Heidelberg.<br />
Hansen, J., Sato, M., Ruedy, R., Nazarenko, L., Lacis, A., Schmidt, G.A., Russell, G., Aleinov, I.,<br />
Bauer, M., Bauer, S., Bell, N., Cairns, B., Canuto, V., Chandler, M., Cheng, Y., Del Genio, A.,<br />
Faluvegi, G., Fleming, E., Friend, A., Hall, T., Jackman, C., Kelley, M., Kiang, N., Koch, D., Lean,<br />
J., Lerner, J., Lo, K., Menon, S., Miller, R., Minnis, P., Novakov, T., Oinas, V., Perlwitza, J.,<br />
Perlwitz, J., Rind, D., Romanou, A., Shindell, D., Stone, P., Sun, S., Tausnev, N., Thresher, D.,<br />
Wielicki, B., Wong, T., Yao, M., & Zhang, S. Efficacy of climate forcings), journal = JGR, year =<br />
2005, volume = 110, pages = doi:10.1029/2005JD005776,.<br />
Hesshaimer, V., Heimann, M., & Levin, I. 1994. Radiocarbon evidence for a smaller oceanic carbon<br />
dioxide sink than previously believed. Nature, 370, 201–203.<br />
Key, R. M., Kozyr, A., Sabine, C. L., Lee, K., Wanninkhof, R., Bullister, J. L., Feely, R. A., Millero,<br />
F. J., Mordy, C., & Peng, T.-H. 2004. A global ocean carbon climatology: Results from Global<br />
Data Analysis Project (GLODAP). Global Biogeoch. Cycl., 18(4), doi:10.1029/2004GB002247.<br />
Levin, I. 2004a. Greenhouse Gases Trends in Europe and at the German Antarctic Station. Invited<br />
talk, WMO WMO/GAW Expert Workshop on The Quality and Applications of European GAW<br />
Measurements. Tutzing, Germany.<br />
Levin, I. 2004b. Quantification of Exchange Rates in the Global Carbon Cycle by Radiocarbon Observations.<br />
Invited talk, Physical Colloquium. University of Groningen, The Netherlands.<br />
Levin, I. 2005a. Quantifying fossil fuel CO2 over Europe. Invited talk, Workshop on A Blueprint for<br />
a GHG monitoring system in Europe. Amsterdam, The Netherlands.<br />
Levin, I. 2005b. Recent Heidelberg Radiocarbon Observations in Atmospheric CO2. Invited talk,<br />
13th International WMO Experts Meeting on atmospheric CO2 and Related Tracer Measurement<br />
Techniques. Boulder (CO) USA.<br />
Levin, I., & Hesshaimer, V. 2000. Radiocarbon - a unique tracer of global carbon cycle dynamics.<br />
Radiocarbon, 42(1), 69–80.<br />
Levin, I., & Kromer, B. 2004. The tropospheric 14 CO2 level in mid-latitudes of the Northern Hemisphere<br />
(1959-2003). Radiocarbon, 46(3), 1 261–1 272.<br />
Levin, I., Glatzel-Mattheier, H., Marik, T., Cuntz, M., Schmidt, M., & Worthy, D.E. 1999. Verification<br />
of German methane emission inventories and their recent changes based on atmospheric<br />
observations. J. Geophys. Res., 104(D3), 3447–3456.<br />
Levin, I., Born, M., Cuntz, M., Langendörfer, U., Mantsch, S., Naegler, T., Schmidt, M., Varlagin,<br />
A., Verclas, S., & Wagenbach, D. 2002. Observations of atmospheric variability and soil exhalation<br />
rate of Radon-222 at a Russian forest site: Technical approach and deployment for boundary layer<br />
studies. Tellus, 54(5), 462–475.<br />
Levin, I., B. Kromer, M. Schmidt, & H. Sartorius. 2003. A novel approach for independent budgeting<br />
of fossil fuel CO2 over Europe by 14 CO2 observations. Geophysical Research Letters, 30(23), doi:<br />
10.1029/2003GL018477.<br />
Mayorga, E., Aufdenkampe, A. K., Masiello, C. A., Krusche, A. V., Hedges, J. I., Quay, P. D., Richey,<br />
J. E., & Brown, T. A. 2005. Young organic matter as a source of carbon dioxide outgassing from<br />
Amazonian rivers. Nature, 436, 538–541.<br />
Naegler, T. 2005 (June). Simulating Bomb Radiocarbon: Consequences for the Global Carbon Cycle.<br />
Ph.D. thesis, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg, Heidelberg, Germany.<br />
Peacock, S. 2004. Debate over the ocean bomb radiocarbon sink: Closing the gap. Global Biogeoch.<br />
Cycl., 18, GB2022, doi:10.1029/2003GB002211.<br />
Röckmann, T., & Levin, I. 2005. High-precision determination of the changing isotopic composition<br />
of atmospheric N2O from 1990 to 2002. J. Geophys. Res. accepted.
2.7. CARBON CYCLE GROUP 113<br />
Schell, S. 2004. 222 Radon-Profil-Messungen in Süd- und Ostdeutschland, Anwendung der Radon-<br />
Tracer-Methode zur Berechnung von CO2- und CH4-Flüssen. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>,<br />
University of Heidelberg. in German.<br />
Schönherr, C. 2005 (October). Investigating Carbon Dioxide, Carbon Monoxide and Fossil Fuel CO2<br />
in Heidelberg. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg.<br />
Spalding, K. L., Buchholz, B. A., Bergman, L.-E., Druid, H., & Frisén, J. 2005. Age written in teeth<br />
by nuclear tests. Nature, 437, 333–334.
Terrestrial Systems<br />
3.1 Soil Physics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 117<br />
3.2 Ice and Climate . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 137<br />
115
3.1. SOIL PHYSICS 117<br />
Overview<br />
We study the whole range of physical processes in near-surface land systems, including the land<br />
cryosphere, at spatial scales ranging from sub-millimeter to hundreds of kilometers. These processes<br />
are relevant for a spectrum of hot environmental issues including water resources in arid and semi-arid<br />
regions, contamination of groundwater by agrochemicals and waste disposal site, as well as past and<br />
present climate changes. Current main research fields are<br />
1. movement of water and contaminants through soils into groundwater<br />
2. geophysical near-surface exploration and monitoring<br />
3. thermal and hydraulic dynamics of permafrost in a changing environment<br />
4. climate and environmental archives of glaciers and ice shields<br />
The group is organized in two major subgroups: “Soil Physics” covering research fields 1. . . 3 and “Ice<br />
and Climate” covering research field 4. An overview of their current research activities is given on<br />
pages 118ff and 137ff, respectively.<br />
Future Work<br />
Important perspectives for the next reporting period include<br />
1. extension of the Grenzhof test site to include electrical resistivity tomography (ERT) and additional<br />
ground-penetrating radar (GPR) measurements,<br />
2. investigation of frequency-dependent dielectric properties of soils as a basis for accurate measurements<br />
of soil water content at the field scale,<br />
3. setup of several monitoring stations on the Qinghai-Tibet plateau (China) to study the dynamics<br />
low-latitude permafrost and the impact of climatic warming,<br />
4. participation in the EPICA project (European Ice Core Drilling in Antarctica) through 10 Beinvestigations<br />
at the deep DML (Dronning Maud Land) ice core,<br />
5. attempts to date the basal layer of Alpine glaciers.<br />
More details are again given in the respective summaries.<br />
3.1 Soil Physics<br />
Members<br />
Dr. Andreas Bayer, PhD student<br />
Cand. Phys. Alexandra Herzog, diploma student<br />
Angelika Gassama, lab technician<br />
Dipl. Phys. Holger Gerhards, PhD student<br />
Dr. Olaf Ippisch, postdoctoral researcher<br />
Cand. Phys. Patrick Leidenberger, student<br />
Dr. Ing. Benedikt Oswald, senior scientist<br />
Dipl. Phys. Fereidoun Rezanezhad, PhD student<br />
Prof. Dr. Kurt Roth, group leader<br />
Dr. Anatja Samouëlian, postdoctoral researcher<br />
Cand. Phys. Klaus Schneider, diploma student<br />
Dr. Nadiya Smoljar, postdoctoral researcher<br />
Dipl. Phys. Carolin Ulbrich, PhD student<br />
PD Dr. Hans-Jörg Vogel, senior scientist<br />
Dr. Ute Wollschläger, senior scientist
118 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
Background<br />
Transport of water, dissolved chemicals, and heat are intimately linked in soils and they are an important<br />
aspect of many environmental issues like quantity and quality of groundwater, irrigation and<br />
soil salinization, coupling of soil and atmosphere, and stability of permafrost soils. Major challenges<br />
are (i) the understanding of the physical basis of these highly nonlinear processes and (ii) the quantitative<br />
understanding of their manifestation at the scale of eventual interest. While the fundamental<br />
understanding typically refers to spatial scales of millimeters to meters, the scale of interest ranges<br />
from hundreds of meters, e.g., for optimized irrigation, to tens or hundreds of kilometers, e.g., for the<br />
impact of landuse changes on climate.<br />
Research Focus<br />
Our primary focus lies on understanding the physical basis of transport processes in soils, specifically<br />
the movement of water, of non-reactive solutes, and of thermal energy. We cover the range from<br />
detailed studies in the laboratory to monitoring at the field scale and from conceptual modeling to<br />
numerical simulation.<br />
A secondary focus is the development of novel approaches to (i) exploring subsurface structures<br />
and (ii) non-invasive measurements of state variables and material properties. Both are prerequisites<br />
for simulating large systems with time scales beyond reasonable experimentation and for monitoring<br />
transport processes.<br />
Project Clusters and Links<br />
Cluster A: Transport Processes<br />
At the lab scale, we study fundamentals of transport in porous media, currently water movement<br />
in coarse-textured media which may become unstable and lead to so-called flow fingers. These have<br />
been shown to be inconsistent with Richards’ equation which underlies most current models of water<br />
movement in soils. We study these instabilities in Hele-Shaw cells. Water saturation and dye<br />
distributions are determined by light transmission (project 3.1.3) which was previously calibrated by<br />
X-ray transmission (project 3.1.2). To improve the quality beyond that achieved with the white light<br />
transmission measurements, we look, with support from the image analysis group of Prof. Dr. Bernd<br />
Jähne, into near-infrared measurements within the absorption bands of water (project 3.1.4).<br />
Concurrent with our experimental studies, Sreejith Kuttanikkad in the parallel computing group<br />
of Prof. Dr. Peter Bastian at IWR develops a high-resolution solver for Stokes’ equation at the pore<br />
scale.<br />
At the small field scale, we investigate the impact of soil structures on water and solute movement.<br />
Of particular importance here are macropores – cracks and wormholes – which may lead to<br />
the bypassing of the biologically active layers. This has an impact on the availability of water for<br />
plants and on the decay of contaminants. An experimental study of so-called preferential flow was<br />
performed in cooperation with INRA at Orleans, Frankreich (Dr. Isabelle Cousin) (project 3.1.7) and<br />
successfully simulated numerically (project 3.1.8).<br />
At the large field scale, we operate test and monitoring sites at Grenzhof, Heidelberg, and near<br />
Ny-˚Alesund, Svalbard. Further sites are planned on the Qinghai-Tibet plateau, China.<br />
The Grenzhof site, located a few kilometers from Heidelberg, is dedicated to exploring transport<br />
processes in natural soils, eventually also the coupling between soil and atmosphere, and to developing<br />
and testing new measuring methods and instruments. Its primary advantages are easy access and<br />
vicinity to the institute.<br />
The site is 20 m × 10 m in size. It is equipped with an automated weather station (air temperature,<br />
humidity, and pressure, wind speed and direction, precipitation, radiation components), a profile of<br />
ground temperature sensors down to 1.6 m, and two profiles of time-domain reflectometry (TDR)<br />
probes for measuring liquid water content down to 1.4 m.<br />
During the installation of the ground instruments, large soil cores where extracted whose hydraulic<br />
properties are measured in the lab as described below on “Inverse Determination of Soil Hydraulic<br />
Properties”.<br />
Weekly measurements with ground-penetrating radar (GPR) yield novel information on the dynamics<br />
of soil water content at the field scale which is compared with the point measurements provided<br />
by TDR (project 3.1.9).
3.1. SOIL PHYSICS 119<br />
In November 2004, a tracer experiment was started and monitored with soil coring, TDR, GPR,<br />
and electrical tomography, the later by our cooperation partners from the Dresdner Grundwasserforschungszentrum<br />
(DGFZ). The experiment was sampled, in the classical destructive way, in April<br />
2005 (project 3.1.10).<br />
Funding for this site is provided primarily by DFG through a joint project with DGFZ (Dr. Frank<br />
Börner), and TU Freiberg (Prof. Dr. Bernhard Forkmann) and supplementary by IUP.<br />
Future The Grenzhof site is currently expanded to 200 m × 10 m to allow for large-scale<br />
measurements, primarily with GPR. In addition, we plan to install our own and permanent electrical<br />
resistivity tomography (ERT) equipment early 2006. This will be used to monitor a new tracer<br />
experiment with high temporal resolution. In addition, we want to explore the feasibility of monitoring<br />
the dynamics of soil water content with ERT.<br />
The two sites near Ny-˚Alesund, Svalbard are aimed at understanding the thermal and hydraulic<br />
dynamics of arctic permafrost. They are equipped with two-dimensional arrays of temperature- and<br />
TDR-sensors, some 30 of each at both sites, and Bayelva in addition has a weather station as already<br />
described for the Grenzhof site. The NP site is very near to the corresponding station at Ny-˚Alesund.<br />
Both sites were installed and are operated in cooperation with the Alfred Wegener <strong>Institut</strong>e (AWI),<br />
Potsdam (Dr. Julia Boike). They deliver data since September 1998, with some interruptions due to<br />
damage by reindeer.<br />
The original installation and operation of the sites was funded by DFG, the corresponding project<br />
was completed in 2001. The current operation and maintenance is covered by AWI and the stream of<br />
data is collected and processed at IUP. The original goal of understanding the thermal and hydraulic<br />
dynamics was achieved. The two stations are now oriented towards monitoring the response to climatic<br />
changes.<br />
Future We plan to set up four monitoring stations similar to those installed on Svalbard on the<br />
Qinghai-Tibet plateau, China. They will be aimed at understanding the dynamics of low-latitude<br />
permafrost, which is characteristically different from arctic permafrost due to the different radiation<br />
regime. Besides the local dynamics, we also want to study the impact of the current climatic warming<br />
on the decay of the permafrost. The major tool for this second aspect will be GPR explorations<br />
(project 3.1.13) on long lines in the vicinity of the stations.<br />
This project is funded by DFG and Chinese Academy of Sciences (CAS). Cooperation partners<br />
are Dr. Yu Qihao and Dr. Jin Huijun of the Cold and Arid Regions Environmental and Engineering<br />
Research <strong>Institut</strong>e (CAREERI) and CAS, Lanzhou.<br />
Cluster B: Geophysical Exploration and Monitoring<br />
Geophysical instruments are increasingly used for near-surface investigations of soils, permafrost,<br />
and glaciers and for the non-destructive semi-quantitative monitoring of transport processes. Our<br />
interest is currently focused on electromagnetic waves in the frequency range between 50 MHz and<br />
2 GHz which allow the mapping and monitoring of dielectric structures. These in turn are strongly<br />
influenced by the volume fraction of liquid water which has a dielectric number εw ≈ 80 that is<br />
about an order of magnitude larger than that of other relevant constituents. Since soil and geologic<br />
formations typically differ in texture, and thus in equilibrium water content, the dielectric structure<br />
of the subsurface typically also reveals its architecture. We employ two classes of instruments, timedomain<br />
reflectometry (TDR) which operates with guided waves and ground-penetrating radar (GPR)<br />
which is based on free waves. Our primary aim here is to develop a hierarchy of instruments and<br />
methods to measure the volumetric water content at scales from a few centimeters to a few kilometers.<br />
TDR has been developed and used for a long time to measure average volumetric water content<br />
within the sampling volume of the probe, typically a cylinder some 50 mm in diameter and 200 mm<br />
long [Roth et al. , 1990]. A new development is the use of much longer probes in conjunction with<br />
the inversion of the time-domain signal to obtain the spatial variation of the dielectric number along<br />
the probe instead of its average (project 3.1.11). Such an instrument is particularly attractive near<br />
the soil surface since the water content there changes very rapidly both in space and in time.<br />
GPR has the advantage that no installations are required – the antennas are just pulled across<br />
the soil surface – and thus facilitates measurements on long transects with lengths of hundreds of<br />
meters to a few kilometers. Two groups of waves may be distinguished in a typical GPR application,<br />
the ground wave which propagates as an evanescent wave along the soil-air interface, and the reflected<br />
waves that originate at dielectric discontinuities. Both yield valuable information on the water content<br />
and, to a limited degree, on solute distributions. Besides the heuristic analysis of GPR and comparison<br />
with TDR (project 3.1.9), we investigate the inversion of the signals. As a first step, semi-analytical<br />
(project 3.1.13) and numerical (project 3.1.12) forward solutions are developed and their performance<br />
is explored. The associated calculations are rather time-consuming and run on our Linux-cluster.
120 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
Future Activities at the Grenzhof site will be expanded along two lines: (i) We will explore the<br />
potential of GPR-trains (multiple coupled antennas) to yield concurrent information on the depth of<br />
reflectors and on soil water content. (ii) We want to perform a comparative study of different methods<br />
for measuring near-surface soil water content. Methods used will be soil sampling, vertical TDR, GPR<br />
groundwave, and GPR reflection. This study is a prerequisite for the accurate interpretation of data<br />
obtained satellite instruments (synthetic apperture radar (SAR) and radiometry as it will be available<br />
from SMOS after 2007).<br />
Cluster C: Effective Material Properties<br />
Soils contain relevant structures on many scales, from a few micrometers all the way up to the landscape.<br />
Effective material properties which summarize the impact of physical processes below some<br />
particular scale are a convenient approach to limit the complexity of models and simulations at scales<br />
of practical interest. These effective properties are of fundamental interest in their own right – under<br />
what circumstances do they exist and how can they be defined objectively? – but the immediate<br />
interest is typically to get hands on optimal estimates of their functional form and the corresponding<br />
parameters.<br />
Hydraulic properties, the soil water characteristic θ(ψm) and the hydraulic conductivity function<br />
K(θ) are prerequisites for the numerical simulation of water movement through soils. We employ<br />
the traditional multi-step outflow (MSO) method to (i) routinely estimate these functions and (ii) investigate<br />
effective properties of heterogeneous media (projects 3.1.2 and 3.1.1). In this method, an<br />
initially completely saturated soil column is drained by reducing the pressure at its lower end in a<br />
number of discrete steps. Pressure and outflow are recorded and inverted to obtain highly nonlinear<br />
functions θ(ψm) and K(θ).<br />
The MSO method is limited to rather high potentials – pressure cannot be reduced below the<br />
vapor pressure – and does not yield useful information for fine-textured soils. To obtain a much more<br />
extended range, we develop a new method where water is evaporated from the sample’s surface. This<br />
allows very low potentials by simply reducing the humidity of the incoming air. The vapor flux is<br />
measured spectroscopically (project 3.1.5) and again inverted numerically with a code developed by<br />
Olaf Ippisch (IWR and IUP).<br />
A crucial aspect of the inversion procedure, both for the traditional MSO and for the evaporation<br />
experiment, is the parameterization of θ(ψm) and K(θ). The current approaches are almost universally<br />
based on the Mualem-van Genuchten parameterization. In cooperation with IWR (Prof. Dr. Hans-<br />
Georg Bock) a free parameterization based on monotone spline functions is developed (project 3.1.6)<br />
and implemented in the inversion code by Olaf Ippisch (IWR and IUP).<br />
Funding for the projects on effective hydraulic properties is provided in part by BMBF (“Sickerwasserprognose”)<br />
and by DFG.<br />
Dielectric properties, the soil’s complex dielectric number ε, depend strongly on liquid water<br />
content and moderately on temperature, frequency, solute concentration, and soil composition. They<br />
provide the link between the electromagnetic measurements and the quantities of interest, primarily<br />
soil water content and secondarily solute concentration.<br />
The traditional approaches consists in identifying a regression relation between the quantities of<br />
interest [Topp et al. , 1980] or in postulating a dielectric mixing model εc = f({θi, εi}), where εc<br />
the measured (composite) dielectric number and {θi, εi} are volume fraction and (known) dielectric<br />
number of the set of constituents i [Roth et al. , 1990]. Both approaches are used for the direct analysis<br />
of the type of broadband signals used in TDR and GPR. In some earlier work in cooperation with<br />
Prof. Dr. Markus Flury, Washington State University, Pullman, USA, and Dr. Marco Bittelli, now<br />
at University of Bologna, Italy, we showed that narrow-band measurements (dielectric spectroscopy)<br />
yield more information on different soil constituents and in particular allow the distinction between<br />
liquid and frozen water [Bittelli et al. , 2004].<br />
For the next step, we developed a large coaxial cell for dielectric measurements of geologic samples<br />
for frequencies 0.3. . . 3’000 MHz using a network analyzer together with the required robust inversion<br />
code [Oswald et al. , 2006]. A first series of calibration runs with different liquids and partly saturated<br />
sands have been completed successfully.<br />
Future Preliminary studies of soil samples from the Grenzhof site revealed a rather strong<br />
frequency-dependence of dielectric properties. This has a strong impact on water content measurements<br />
with electromagnetic methods and requires further detailed investigation.
3.1. SOIL PHYSICS 121<br />
Major Achievements<br />
1. Demonstration that water content profiles can be obtained from GPR measurements and their<br />
accuracy rivals that of TDR (project 3.1.9).<br />
2. Modeling and numerical simulation of solute transport through a soil with macropores (projects 3.1.7<br />
and 3.1.8).<br />
Publications<br />
Peer Reviewed Publications<br />
1. Oswald et al. [2006]<br />
2. Roth et al. [2005]<br />
3. Stöhr & Roth [2005]<br />
4. Bayer et al. [2005]<br />
5. Yu et al. [2005]<br />
6. Vogel et al. [2005a]<br />
7. Vogel et al. [2005d]<br />
8. Vogel et al. [2005e]<br />
9. Wollschläger & Roth [2005]<br />
10. Braun et al. [2005]<br />
PhD Theses<br />
1. Bayer [2005]<br />
Diploma Theses<br />
1. Herzog [2005]<br />
2. Ulbrich [2005]<br />
3. Herzog [2005]<br />
Invited Talks<br />
1. Vogel [2005b]<br />
2. Vogel et al. [2005c]<br />
3. Vogel [2005c]<br />
4. Vogel [2005a]<br />
5. Oswald & Roth [2005c]<br />
6. Roth & Wollschläger [2005]<br />
7. Roth [2005a]<br />
8. Roth [2005b]<br />
9. Roth [2005c]
122 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.1 Estimation of effective hydraulic parameters for heterogeneous porous<br />
media<br />
Participating scientist Anatja Samouëlian, Hans Jörg Vogel<br />
Abstract Through numerical simulations and experimentations, the influence of small scale heterogeneity<br />
on large scale hydraulic properties of soil was investigated. The effective water capacity<br />
is directly related to the probability densities function for the texture of the composites, while the<br />
hydraulic conductivity additionally depends on its topology.<br />
Figure 3.1: a) Three types of heterogenous media where the grey value corresponds to characteristic length<br />
of subscale porous medium, b) effective water retention curve for the three fields (predicted in yellow, grey<br />
area represents the small scale heterogeneity), c) the regression between hydraulic conductivity exponent and<br />
topological variable.<br />
Background Soil hydraulic properties can be<br />
estimated using multi-step-outflow experiments<br />
(MSO) in combination with inverse modeling.<br />
One assumption implied, is that the sample is<br />
large enough to contain all microscopic heterogeneities<br />
in the sense of a representative elementary<br />
volume (REV). Hence, the measured properties<br />
are considered as an ‘effective‘ description.<br />
However these ideal conditions are rarely met,<br />
since soil is typically heterogeneous at various hierarchical<br />
scales.<br />
The question for this project is: Given the<br />
measured effective properties together with the<br />
entire 3D structure of the composites (measured<br />
by X-ray tomography) is it possible to estimate<br />
the properties of each single component?<br />
As a first step we investigate the functional<br />
relation between structural features and the effective<br />
hydraulic properties through numerical simulations<br />
using well defined random fields.<br />
Funding DFG project 2004-2005 VO 566/5-1<br />
Methods and results Numerical experiments<br />
were performed on heterogeneous media: (i) a<br />
standard Gaussian field, (ii) a field where the fine<br />
textured material is highly connected and (iii) a<br />
field where the coarse textured material is connected<br />
(fig.1a). The hydraulic properties are described<br />
assuming Miller-similarity. Their topol-<br />
ogy, quantified by the Euler number is different,<br />
however, the first two moments, mean and covariance,<br />
are identical for the three random fields.<br />
The simulated water retention curves for the<br />
three fields are identical and can be directly calculated<br />
from the histogram of the components by<br />
θeff (ψ) = �<br />
i [ωiθi(ψ)] for i materials and their<br />
probability density ωi (fig. 1b).<br />
Concerning the hydraulic conductivity, the<br />
topology of the structure is a key to predict the<br />
effective behaviour. It can be approached by<br />
Keff (ψ) q = �<br />
i [ωiKi(ψ) q ] with q an exponent<br />
related to the topology of the conductivity field.<br />
The first results indicate a polynomial regression<br />
between the calculated exponent q and the measured<br />
topology (fig. 1c).<br />
Outlook/Future work The quantitative link<br />
between structural quantities and effective hydraulic<br />
properties, both accessible through direct<br />
measurement, will greatly facilitate the estimation<br />
of the subscale parameter field. Based on this information<br />
the phenomenology of water flow and<br />
solute transport can be predicted for natural heterogeneous<br />
soil.<br />
Main publication Samouëlian et al., Averaging<br />
of hydraulic properties in heterogeneous<br />
porous media (to be submited)
3.1. SOIL PHYSICS 123<br />
3.1.2 X-ray attenuation techniques to study the dynamics of water in<br />
porous media<br />
Participating scientist Andreas Bayer, Hans-Jörg Vogel, Kurt Roth<br />
Abstract X-ray attenuation was used as non-invasive method to monitore the distribution of water<br />
in samples of porous media during a multistep-outflow experiment. Differences between the data and<br />
a numerical inversion that aimed at effective material properties reveal the impact of soil structures<br />
at different scales.<br />
0 1<br />
40 50 60 70<br />
time [h]<br />
0<br />
−20<br />
−15<br />
cumulative outflow [cm]<br />
1<br />
−10<br />
2<br />
−5<br />
boundary condition [cmWC]<br />
0<br />
3<br />
−0.5<br />
5<br />
diff. [cm]<br />
0<br />
0.5<br />
sample height [cm]<br />
10<br />
8<br />
6<br />
4<br />
2<br />
0<br />
0 0.1 0.2 0.3 0.4<br />
water content [-]<br />
sample height [cm]<br />
10<br />
8<br />
6<br />
4<br />
2<br />
0<br />
0 0.1 0.2 0.3 0.4<br />
water content [-]<br />
Figure 3.2: Left: Measured cumulative outflow (black circles) and results of inverse modeling (black<br />
lines). Red lines shows predicted outflow assuming layered material model. Green symbols and lines<br />
represent outflow obtained for layered material model turned upside down with effective properties<br />
again obtained by inversion. Center: Measured (symbols) and simulated (solid lines) vertical water<br />
distribution at hydrostatic equlibrium for different outflow steps assuming uniform sample. Right:<br />
Same as the center but simulation based on layered model.<br />
Background The description of the dynamics<br />
of water in soil leads to the introduction of effective<br />
properties. For large scales, order of 1 m and<br />
beyond, soils and aquifers have a distinctive heterogeneous<br />
architecture of soil layers and sedimentary<br />
units, respectively. These units are presumed<br />
to be uniform and are represented by a set of effective<br />
material properties which in turn are measured<br />
in the lab, typically by multistep-outflow<br />
experiments. This approach does not explicitly<br />
address the well-documented multiscale heterogeneity<br />
of natural porous media which extends to<br />
scales much smaller than 1 m. In this project, the<br />
impact of heterogeneity on the typical analysis of<br />
a multistep-outflow experiment is explored.<br />
Funding BMBF (“Sickerwasserprognose”)<br />
Project 02WP0261<br />
Methods and results A non-invasive method<br />
to obtain information about the assumed sample<br />
structure is X-ray attenuation and tomography.<br />
It was combined with a multistep-outflow setup<br />
to assess the sample’s structure and to monitor<br />
the distribution of water during the experiment.<br />
Vertical water content profiles extraxted from<br />
X-ray attenuation data were compared with<br />
profiles simulated based on Richards equation<br />
(fig. 3.2, middle). The simulation used hydraulic<br />
parameters estimated from the inversion of measured<br />
outflow data (fig. 3.2, left). The dramatic<br />
differences between measured and predicted profiles<br />
are typically not observed because the corresponding<br />
instrumentation is not available. The<br />
origin of the difference is a weak layering produced<br />
during sample preparation and is representative<br />
for a rather uniform natural porous medium. Inversion<br />
of the data did not hint at this complication:<br />
the fit represents the outflow data very well.<br />
To investigate the issue, we set up a layered<br />
model based on the X-ray attenuation profiles<br />
and hydraulic parameters obtained from forward<br />
simulations. The modeled outflow fits both, the<br />
measured outflow and the vertical water content<br />
distribution, reasonably well. Notice that there<br />
was no inversion used in this approach. This illuminates<br />
the difficulties to estimate effective hydraulic<br />
properties in a “blind experiment” where<br />
the internal structure is not represented. We<br />
demonstrated that X-ray measurements provide<br />
the crucial additional information required for<br />
a faithful model of the hydraulic behavior of a<br />
porous material, at least for the simple case studied<br />
here.<br />
Main publication Bayer, A., PhD thesis 2005;<br />
Bayer et al. [2004]; Bayer et al. [2005]
124 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.3 Fingered Flow Through Initially Dry Porous Hele-Shaw cell<br />
Participating scientist Fereidoun Rezanezhad, Hans-Jörg Vogel, Kurt Roth<br />
Abstract Fingered flow is an instability that occurs during infiltration into dry, coarse-textured,<br />
and uniform porous media. We study the dynamics of such fingers in porous Hele-Shaw cells with<br />
dimensions 1.6 × 0.6 × 0.003 [m]. High-resolution measurements of the water saturation are obtained<br />
from light transmission images that have been calibrated by X-ray transmission.<br />
Background Unstable flow of water during infiltration<br />
into unsaturated porous media belongs<br />
to the class of preferential flow. It has been studied<br />
for many years and we have a quite complete<br />
description of the general phenomena. Glass and<br />
Nicholl (1996) reviewed the classical understanding<br />
and DiCarlo (2004) summarizes the newer<br />
developments which focus on the nature of the<br />
saturation overshoot in the finger tip. Fingered<br />
flow is important for some practical issues, e.g.,<br />
for rapid contaminant transport with irrigation in<br />
many arid regions. However, it also illuminates<br />
our very understanding of the physics of multiphase<br />
flow in porous media. Indeed, the current<br />
theory – Richards equation – cannot explain the<br />
existence of such fingers.<br />
Funding DFG RO 1080/9-1&2<br />
Methods and Results The key to understanding<br />
fingered flow are rapid high-resolution measurements<br />
of the water saturation. To facilitate<br />
this, we work with Hele-Shaw cells – two parallel<br />
glass plates separated by a few millimeters –<br />
that are filled with sand. Light transmission is<br />
the used as a proxy for water saturation. A simple<br />
digital camera then yields the required rapid measurements.<br />
Since the relation between transmission<br />
and saturation is nonlinear, it is calibrated<br />
with X-ray transmission which is accurate but too<br />
slow and also too expensive for routine measurements.<br />
In our experiments, fingers are initiated<br />
at the transition from a fine-textured layer, where<br />
the flow is very uniform, to a coarse-textured<br />
Figure 3.3: Experimental setup for X-ray and<br />
light transmission measurements. The front<br />
view shows the highly localized flow paths that<br />
originate from the flow instability in the uniform<br />
part of the medium.<br />
layer. They eventually disappear into the simulated<br />
groundwater at the lower end of the cell. At<br />
different stages, a dye tracer is added to the flow in<br />
order to study the flow field behind the finger tip.<br />
Finally, pressure sensors are installed to monitor<br />
the potential energy of the water.<br />
First, a number of experimental findings of<br />
other groups were reproduced. These are in particular<br />
(i) the maximum saturation that occurs in<br />
the finger tip, (ii) the stability of the resulting flow<br />
channel on short time scales and its diffusive decay<br />
on very long time scales, and (iii) the existence of a<br />
mobile core and an immobile fringe. Some newer<br />
findings include (i) the demonstration that flow<br />
channels are destroyed when they encounter heterogeneous<br />
layers, (ii) the detection of pressure<br />
drops in the overlaying fine-textured layer upon<br />
initialization of a new finger, and (iii) the detection<br />
of correlated intermittency between different<br />
fingers.<br />
Outlook/Future Work The future work will<br />
concentrate on the theoretical understanding of<br />
the experiments. This necessitates a still higher<br />
spatial resolution, however, which in turn requires<br />
a more detailed representation of the light transmission<br />
through the porous medium. Measurements<br />
of the point spread function in the nearinfrared<br />
as well as in the visible region are under<br />
way (project 3.1.4). On another route, a microscope<br />
was installed that allows the resolution of<br />
the pore space and the detailed observation of the<br />
water phase during the passage of a finger tip.
3.1. SOIL PHYSICS 125<br />
3.1.4 Near Infrared Imaging Spectroscopy of Water States in Porous Silicate<br />
Media<br />
Participating scientist Nadiya Smolyar, Kurt Roth, Bernd Jähne<br />
Abstract We have examined capillary and adsorbed water in porous silicates (quartz sand, clay,<br />
silica gel) by using of Near Infrared Image Spectroscopy, NIRIS. The interaction of water with the<br />
porous media, the spatial distribution of water content, and the physics of different water states, as<br />
well as their transformation will be studied.<br />
Figure 3.4: Spectral transmission images of capillary water in sand at different times t1(a) < t2(b),<br />
showing the distribution of water content and state.<br />
Background NIRIS examinations are important<br />
for understanding the molecular mechanisms<br />
of water interacting with porous silicate media.<br />
Even today, the role water plays in the quality of<br />
soils and in further environmental effects is not<br />
unterstood in many aspects.<br />
Methods and results Capillary and adsorbed<br />
water is examined spectrally in both dry and<br />
saturated silica specimens. The frequency spectra<br />
are measured in near infrared (ν = 3300 −<br />
11000cm −1 ; λ = 700 − 3000nm) with a UV-NIR<br />
spectrometer Scan 500 (Varian,USA).<br />
The frequency values, the characteristic intensities,<br />
and appearance of new spectral bands of water<br />
in SiO2 media yield numerous data as elasticity<br />
constants, bond geometries, and adsorption<br />
mechanisms. The analysis of OH vibration<br />
modi permits the determination of water content<br />
along with changes of water states in the silicate<br />
medium. We have found that the water content<br />
can be determined best by using the intensive<br />
bands 2νOH and νOH + ν2, and the water state<br />
according to the bands 3νOH and 2νOH+ν2.<br />
A new innovative NIRIS method has been developed<br />
for investigations on the spectral optical<br />
qualities of water in porous specimens with spatial<br />
resolution. To this end, an imaging multispectral<br />
32-channel CCD spectrometer has been set up.<br />
The corresponding CCD camera takes sequences<br />
of spectral images at certain wavelengths using<br />
band pass filters. The images are by spectral digital<br />
image processing analyzed.<br />
Outlook/Future work The NIRIS concept<br />
permits the determination of molecular interaction<br />
forces of water on solid boundaries and micro<br />
pores together with the physics of water states and<br />
measuring the water distribution on porous silicates.<br />
The results will aid in gaining deeper understanding<br />
of the thermodynamical, structural,<br />
and dynamic characteristics of water in silicate<br />
media. We are planning the following investigations<br />
of water in porous silicate media:<br />
-Relation of multiple light scattering for determination<br />
of true values of water absorption; -<br />
Investigation of different water states, their spatial<br />
distribution and concentration; -Investigation<br />
of the stationary and dynamic water regimes; -<br />
Spectral analysis of the influence of physical factors<br />
on the interaction of water and medium; -<br />
Investigation of multi-phase systems with various<br />
kinds of intermolecular interaction.<br />
Main publication Smolyar N., M. Korniyenko<br />
and K. Roth (2005) Near Infrared imaging spectroscopy:<br />
A new tool for studying water states<br />
and movement in porous media, ’Geophysical Research<br />
Abstracts’, EGU05-A-07910.<br />
Smolyar N. (2003) Bildgebende Spektroskopie<br />
an Pflanzenblättern. Dissertation, <strong>Universität</strong><br />
Heidelberg, Interdisziplinäres Zentrum <strong>für</strong> Wissenschaftliches<br />
Rechnen (IWR), 195 S.<br />
Garbe C., N. Smolyar, M. Korniyenko and<br />
U. Schurr (2003) Water relations in plant leaves,<br />
Springer Verlag. Lecture Notes in Computer Science,<br />
LNCS 19: 377-401.
126 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.5 Evaporation Experiment to determine Soil Hydraulic Properties<br />
Participating scientist Klaus Schneider, Kurt Roth<br />
Abstract A new enhanced evaporation experiment has been set up to measure soil hydraulic properties.<br />
The water flux and the potential at the upper boundary are measured precisely using infrared<br />
absorption. Hydraulic properties are determined by inverse numeric modelling, thereby explicitely<br />
simulating the diffusive water transport at the surface.<br />
air conditioning<br />
pressure sensor<br />
capillary<br />
vacuum pump<br />
IR gas analyser evaporation chamber<br />
Cell A<br />
Cell B<br />
temperature sensor<br />
TDR<br />
soil<br />
pressure sensor<br />
Figure 3.5: Schematic of the experimental setup of the evaporation experiment. IR spectroscopy<br />
allows precise potential and water flux measurement at the upper boundary.<br />
Background An important issue in soil physics<br />
is the determination of the hydraulic parameters<br />
of soils. If the soil water characteristic θ(ψm)<br />
and the conductivity function K(θ) of a soil are<br />
known, its hydraulic dynamics can be simulated<br />
using Richard’s equation.<br />
Several methods exist to determine the hydraulic<br />
properties in the laboratory. As these<br />
are highly non-linear functions, numeric simulation<br />
and inverse modelling provide a flexible tool<br />
to determine them with reasonable accuracy.<br />
It is generally desireable to know the hydraulic<br />
properties in a wide range of potential and water<br />
content. However, methods are always limited to<br />
a certain range, and hydraulic properties normally<br />
are not valid outside the measured range.<br />
For the wet range with potentials up to about<br />
ψm = −1.8 · 10 4 J/m 3 (corresponding to a water<br />
column of −1.8 m), the multistep-outflow (MSO)<br />
method is already well established. To obtain<br />
valid hydraulic properties also for the dry range,<br />
an evaporation method is developed. It will be<br />
used after an MSO experiment. Ideally this allows<br />
to obtain the desired functions in one run.<br />
Problems of traditional experiments The<br />
traditional setup for evaporation method uses a<br />
balance to measure the cumulative outflow at<br />
the upper boundary and tensiometers at different<br />
heights to measure potentials. The soil is initally<br />
saturated and free evaporation is allowed to start<br />
(Wendroth et al 1993).<br />
The major drawbacks of this setup are:<br />
• With free evaporation, the boundary condition<br />
at the upper boundary is not well defined.<br />
• The potential at the upper boundary is not<br />
known.<br />
• The range is limited, because tensiometers only<br />
work until ψm ≈ −5 · 10 4 J/m 3<br />
• Weighting to determine the flow at the upper<br />
boundary is problematic in the dry region, because<br />
water content change is very small.<br />
Methods and results To avoid these problems,<br />
a new design of experimental setup was<br />
used, which is shown schematically in figure 3.5. A<br />
gas-tight chamber is placed on top of the soil sample,<br />
and air with defined water vapour contents is<br />
flowing through the chamber. As the potential<br />
of the air is determined by its relative humidity,<br />
the upper boundary condition can be controlled<br />
precisely. The water vapour content of the air<br />
is measured before and after the chamber by infrared<br />
absorption. This allows very precise flux<br />
and potential measurements, while at the same<br />
time abandoning the usage of tensiometers and<br />
balance. The method is thus applicable even in<br />
the very dry region.<br />
Additionally, numerical simulation allows explicit<br />
modelling of the diffusive water transport in<br />
the boundary layer, enhancing the results and the<br />
insight into the physical processes.<br />
Outlook / Future work The setup is currently<br />
in its test phase, but first data look promising.<br />
The numerical inversion must still be completed.<br />
Main publication Diplomarbeit planned for<br />
December 2005.<br />
evaporation
3.1. SOIL PHYSICS 127<br />
3.1.6 Free Parameterisation of Soil Hydraulic Properties<br />
Participating scientists A. Herzog, O. Ippisch, S. Körkel, E. Kostina, K. Roth, J. Schlöder<br />
Abstract In order to cope with multi-modal soil water characteristic and permeability functions a<br />
local parameterisation based on piecewise cubic Hermite polynomials is used.<br />
volumetric water content<br />
Mualem−van Genuchten parametrisation<br />
original bimodal soil water characteristic<br />
applied suction pressure [Pa]<br />
Figure 3.6: Sketch of a bimodal soil water characteristic together with Mualem-van Genuchten<br />
parametrisation.<br />
Background It is expected that soils with<br />
multi-modal hydraulic functions (i.e. soil water<br />
characteristic and permeability function) exist in<br />
nature. As the hydraulic functions are mainly<br />
obtained by inverse modelling and not by direct<br />
measurement a parameterisation is needed that is<br />
flexible enough to handle all cases. Specifically,<br />
the widely-used Mualem-van Genuchten parameterisation<br />
is too restrictive to describe the actual<br />
functions satisfactorily. With these problem specifications<br />
water transport through these materials<br />
cannot be described accurately.<br />
Different approaches have been proposed in<br />
the last ten years. Among those are a piecewise<br />
linear parameterisation introduced by Chardaire-<br />
Riviere et al. (1990) and a piecewise cubic Hermite<br />
parameterisation introduced by Knabner et<br />
al. (Aug. 2004).<br />
Also in this thesis piecewise cubic Hermite<br />
parametrisation is investigated in the context<br />
of a simulation programme for water transport<br />
through soil.<br />
Funding Diplomarbeit<br />
Methods and results In this thesis a simulation<br />
programme for water transport is used (Ippisch,<br />
2001). The deviation between model response<br />
and measured values is to be minimised.<br />
The hydraulic functions are part of the model response<br />
in parameterised form.<br />
The simulation programme includes a minimisation<br />
routine for solving for the unknown soil parameters.<br />
The hydraulic functions are parameterised<br />
by piecewise cubic Hermite polynomials.<br />
This parameterisation guarantees C 1 continuity.<br />
Mainly, two different modifications of the parameterisation<br />
of Knabner et al. are tested:<br />
1. A piecewise cubic Hermite parameterisation<br />
using approximated derivatives according to the<br />
formulas of Butland and Brodlie. This parameterisation<br />
is local, in contrast to the one of Knabner<br />
et al..<br />
2. The derivatives themselves are not approximated<br />
but also treated as parameters. parameterisation.<br />
This approach leads to the best results<br />
when started with rather good initial values,<br />
which are gained by solving the inverse problem<br />
with the parameterisation described in (1). However,<br />
this parameterisation is again non-local.<br />
For bimodal hydraulic functions it could be<br />
demonstrated that the used piecewise Hermite parameterisation<br />
is much more convenient than the<br />
Mualem-van Genuchten parameterisation.<br />
With the derivatives as additional parameters<br />
a new problem arises: Some plateaus appeare in<br />
the hydraulic functions where, physically, they are<br />
not expected. They might be artefacts of the revision<br />
of derivatives.<br />
Outlook/Future work In order to avoid these<br />
plateaus it is intended to create a parameterisation<br />
that has still the C 1 continuity but resembles<br />
more closely a piecewise linear interpolation. This<br />
can be achieved by a much more restrictive selection<br />
of the allowed derivatives.<br />
Main publication Herzog, Alexandra, Diplomarbeit,<br />
Interdisziplinäres Zentrum <strong>für</strong> wissenschaftliches<br />
Rechnen/<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />
<strong>Universität</strong> Heidelberg, 2005
128 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.7 Modelling water flow and solute transport in heterogeneous soil<br />
Participating scientist Hans-Jörg Vogel, Isabelle Cousin, Olaf Ippisch<br />
Abstract Flow and transport in soil is governed by the heterogeneous structure of the material.<br />
In this project we consider the structure using different concepts: direct measurement, statistical<br />
description and modelling structure formation. Based on this rough representation we estimate water<br />
flow and solute transport. This is possible because the processes are dissipative.<br />
A<br />
B<br />
C<br />
Figure 3.7: Soil profile with three horizons (A, B, C) and the distribution of a dye tracer (left),<br />
modelled structural components: correlated random fields and earthworm burrows (middle), and<br />
predicted tracer distribution (right).<br />
Background The quantitative understanding<br />
of flow and transport in soil is hampered by<br />
the heterogeneous structure of the material which<br />
cannot be represented by a meaningful average<br />
value. This is typically true at any spatial scale.<br />
To predict the movement of chemicals between the<br />
soil surface and groundwater this structure has to<br />
be represented adequately.<br />
Funding Deutscher Akademische Auslandsdienst<br />
(DAAD, PROCOPE project).<br />
Methods and results In this project we used<br />
a dye tracer in a field experiment on arable soil to<br />
visualize the tracer distribution after a cumulative<br />
infiltration of 50 mm of water. To model this experiment,<br />
the structure of the soil was represented<br />
using three different approaches: i) direct measurement<br />
of the soil horizons in the field (A,B,and<br />
C in the figure) and the measurement of the related<br />
hydraulic properties in lab experiments; ii)<br />
description of the mesoscopic heterogeneity inside<br />
the horizons by an estimated covariance function<br />
in the A and C horizon; iii) modelling earthworm<br />
burrows in the middle, compacted horizon (B)<br />
by a model which mimics the formation of these<br />
macropores.<br />
As a result we obtain the continuous parameter<br />
field (hydraulic properties) of the entire<br />
experimental domain. Hence, the 3D velocity<br />
field of water could be calculated by<br />
solving Richards’ Equation numerically. Subsequently,<br />
solute transport was simulated assuming<br />
a convection-dispersion type of transport locally.<br />
Our model predicted the main characteristics<br />
of the experiment. It demonstrates that a rough<br />
description of the structure together with a rough<br />
measurement/estimation of the related material<br />
properties can be sufficient to come up with reliable<br />
predictions.<br />
Outlook/Future work The further development<br />
of non-invasive techniques to measure the<br />
heterogeneous structure of the subsurface, together<br />
with an better understanding of structure<br />
forming processes will improve our ability to quantitatively<br />
understand water flow and solute transport<br />
in soil.<br />
Main publication Vogel et al. [2005b]
3.1. SOIL PHYSICS 129<br />
3.1.8 Unsaturated Flow in Strongly Heterogeneous Porous Media<br />
Participating scientist Olaf Ippisch, Interdisciplinary Center for Scientific Computing<br />
Abstract Numerical models for the simulation of flow and transport in strongly heterogeneous<br />
porous media have been developed and optimized for speed, robustness and usability. The models<br />
were used to simulate laboratory and field experiments and were used for parameter estimation from<br />
multi-step outflow experiments.<br />
Figure 3.8: Simulation of water infiltration in a macroporous soil<br />
Background Natural porous media are often<br />
strongly heterogeneous. This can influence the<br />
flow patterns considerably, resulting in preferential<br />
flow or macropore flow which have to be taken<br />
into account to get reliable predictions of solute<br />
transport. One way to handle this problem is the<br />
use of homogenization approaches to get a set of<br />
effective parameters for the porous medium as a<br />
whole. However, if the heterogeneous structures<br />
are large in comparison to the scale of interest this<br />
is no longer possible. An alternative strategy is<br />
the determination of the soil structure (e.g. with<br />
x-ray tomography, geoelectrics, georadar) and the<br />
direct simulation of the flow field. Special numerical<br />
problems arise for parameter fields changing on<br />
a very small scale with sometimes highly nonlinear<br />
parameter functions resulting in poor convergence<br />
of the linear and nonlinear solvers.<br />
Funding <strong>Institut</strong>e for Informatics, University of<br />
Heidelberg<br />
Methods and results The developed model<br />
µϕ uses the Levenberg-Marquardt-Algorithm for<br />
parameter estimation with sensitivities derived by<br />
external numerical differentiation. The forward<br />
model solves Richards’ equation or twophaseflow<br />
equations using a cell-centered finite-volume<br />
scheme with full-upwinding in space and an implicit<br />
Euler scheme in time. Linearization of the<br />
nonlinear equations is done by an inexact Newton-<br />
Method with line search. The linear equations are<br />
solved with an algebraic multigrid solver. For the<br />
time solver the time step is adopted automatically.<br />
Brooks-Corey and van Genuchten parametrizations<br />
as well as cubic splines can be used for the<br />
hydraulic functions. Solute transport was discretized<br />
using a higher-order Godonov method<br />
with a minmod slope limiter for the convective<br />
part and a finite-volume scheme for the diffusive<br />
term. It is currently limited to steady-state flow<br />
conditions.<br />
Outlook/Future work The model will be<br />
ported to the new base library Dune which facilitates<br />
the parallelization and the use of different<br />
grid types. Parameter estimation is currently expanded<br />
to evaporation experiments. The stability<br />
and usability of the twophase will be improved<br />
and the solute transport model expanded to nonsteady-state<br />
flow conditions.<br />
Main publications Vogel et al. [2005b]
130 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.9 Assessing temporal changes in volumetric soil water content from<br />
ground-penetrating radar profiles<br />
Participating scientists Ute Wollschläger, Kurt Roth<br />
Abstract We investigated the applicability of ground-penetrating radar (GPR) to estimate temporal<br />
changes of volumetric soil water content at the field scale. Water contents calculated from a time series<br />
of GPR reflections are compared to values derived independently from time domain reflectometry<br />
(TDR) measurements. We found that the results of both methods are well comparable.<br />
volumetric water content<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0<br />
-0.1<br />
-0.2<br />
-0.3<br />
-0.4<br />
2<br />
1<br />
Feb. March April May June July August Sept.<br />
50 100 150<br />
day of year 2004<br />
200 250<br />
0 m...0.8 m, calc. GPR<br />
0 m...0.8 m, calc. TDR<br />
0.8 m...1.65 m, calc. GPR<br />
0.8 m...1.65 m, calc. TDR<br />
1 0 m...0.8 m, meas. mean TDR<br />
2 0.8 m...1.65 m, meas. mean TDR<br />
Figure 3.9: Mean volumetric water contents of the sections 0...0.80 m (1) and 0.80...1.65 m (2)<br />
calculated from TDR data and temporal changes calculated from GPR and TDR measurements for a<br />
1D soil profile. Changes in water content derived from both methods coincide well for both soil sections<br />
demonstrating the potential of the GPR method to estimate volumetric water contents non-invasively<br />
at much larger scales.<br />
Background Measurements of volumetric soil<br />
water content are essential for many scientific,<br />
agricultural and economic questions since it is an<br />
important parameter for plant growth, groundwater<br />
recharge calculations and the local climate. In<br />
contrast to classical methods like TDR or thermogravimetric<br />
measurements, GPR surveys are noninvasive<br />
and can easily be applied on scales of a<br />
few hundreds of meters.<br />
Funding DFG, project RO 1080/8-2<br />
Methods and results At the Grenzhof Test<br />
Site, a time series of GPR reflection measurements<br />
was taken along a fixed transect to determine temporal<br />
changes in volumetric soil water content at<br />
the field scale. For one single trace volumetric<br />
water contents were calculated from the two-way<br />
travel times of two reflections at known depths<br />
of 0.80 m and 1.65 m using the Complex Refractive<br />
Index Method (CRIM). The measurements<br />
were compared to volumetric water contents derived<br />
from independent TDR measurements from<br />
several depths at nearby soil profiles (fig. 1). During<br />
summer 2004 several wetting and drying cycles<br />
were observed in the upper soil section. The corresponding<br />
changes in volumetric soil water content<br />
were detected equally well by both methods.<br />
In the lower soil section water content remains<br />
quite stable which is again shown by both methods.<br />
This investigation demonstrates the power<br />
of GPR to determine volumetric water contents<br />
in soils at the field scale down to a depth of several<br />
meters.<br />
Outlook/Future work GPR time series will<br />
be measured at a scale of a few 100 m. We will use<br />
an array of two GPR antennas which allows to determine<br />
the depth of occuring reflections without<br />
the necessity of ground-truth information from<br />
soil profiles or drillings. The gained data will be<br />
used as important information for the modelling<br />
of the water dynamics in the vadose zone.<br />
Main publication Wollschläger & Roth [2005]
3.1. SOIL PHYSICS 131<br />
3.1.10 Monitoring Field Tracer Experiment with Ground Penetrating Radar<br />
and Time Domain Reflectometry<br />
Participating scientist Carolin Ulbrich, Ute Wollschläger, Kurt Roth<br />
Abstract We explored the feasibility of Ground Penetrating Radar to non-destructively monitor<br />
solute movement in natural soils at the field scale. In a weekly radar time series the displacement<br />
of a CaCl2-tracer was monitored. The test site was instrumented with Time Domain Reflectometry<br />
probes in several depths to measure soil water content and electric conductivity.<br />
Background On its way down from the soil surface<br />
to aquifers, water passes through soil that<br />
acts as a filter. The transport and decomposition<br />
of fertilizers and contaminants determines the<br />
quality of groundwater.<br />
The interaction of this complex system cannot<br />
be calculated exactly. So appropriate restrictions<br />
have to be chosen and abstract models developed<br />
in order to get a quantitative description of a<br />
few important aspects which can be used for estimations.<br />
To assess the applicability of a certain<br />
model one has to verify its predictions with experiments.<br />
At small scales (O(1 m)) there exist numerous validation<br />
methods, but most of them cannot be<br />
implemented at larger scales (O(100 m)) because<br />
they are destructive or too time-consuming.<br />
The aim of this work was to test Ground Penetrating<br />
Radar (GPR) as a new technique to<br />
non-destructively monitor subsurface solute transport<br />
processes. It was compared with Time Domain<br />
Reflectometry (TDR) measurements and<br />
with data from soil sampling. Model predictions<br />
of solute transport on this scale were applied.<br />
Methods and results At the Grenzhof Test<br />
Site, a conservative tracer fluid that absorbs the<br />
radar wave was spread on a streak that crosses<br />
GPR transects vertically. The transport of the<br />
absorbing fluid was monitored weekly with a GPR<br />
antenna along these transects. At the end of the<br />
experiment a trench was excavated and sampled<br />
along the streak. The samples were analyzed with<br />
traditional methods to verify the radar data set.<br />
In addition, a TDR time series was acquired in<br />
the same area in three depths. The comparison to<br />
the excavation samples showed that TDR can be<br />
used to monitor tracer concentration at the instru-<br />
Figure 3.10: GPR radargram. Amplitudes of<br />
single radar pulses are plotted versus their travel<br />
times at the distances where they have been<br />
acquired. The recorded signals before ≈ 15 ns<br />
originate from air- and ground-waves that travel<br />
through the air and along the soil surface, respectively.<br />
The salt tracer was applied between<br />
5.8 m and 7.8 m. It absorbs the radar signal.<br />
mented depth in a semi-quantitative approach.<br />
The absorption effect of the highly concentrated<br />
salt tracer was clearly visible in the GPR surveys.<br />
Figure 3.10 shows a radargram acquired<br />
one month after the application of the tracer. Reflections<br />
at layer borders, visible in the GPR surveys<br />
that were taken before the application of the<br />
tracer, disappeared when the signal was absorbed<br />
by the tracer pulse. The reflections could be detected<br />
again when the tracer pulse passed the reflector.<br />
Obviously, the spatial resolution and accuracy is<br />
much better in traditional sampling experiments,<br />
but the effort there is enormous and the destructive<br />
manner impedes large scale surveys. TDR<br />
provides point measurements with good accuracy<br />
and excellent temporal resolution. GPR holds the<br />
promise to large scale experiments with good temporal<br />
resolution but coarse spatial resolution. A<br />
significant further effort is required to make it<br />
quantitative, however.<br />
Outlook/Future work A solute transport experiment<br />
is planned to be performed on the Grenzhof<br />
Test Site. At a scale of about 300 m tracer<br />
will be applied on small areas and the displacement<br />
will be monitored with GPR and TDR. The<br />
tracer distribution will be tracked in addition by<br />
permanent electric resistivity measurements. This<br />
will help to achieve a better understanding of<br />
transport processes and to further develop the<br />
methods of GPR and TDR monitoring of tracer<br />
movement.<br />
Main publication Ulbrich, Carolin, Diplomarbeit,<br />
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong><br />
Heidelberg, October 2005
132 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.11 Efficient reconstruction of dispersive dielectric profiles using TDR<br />
Student assistant Patrick Leidenberger, Benedikt Oswald, Kurt Roth<br />
Abstract Time Domain Reflectometry (TDR) has become an indispensable technique for measuring<br />
the water content of soils. We use a numerical model for TDR signal propagation in dispersive dielectric<br />
materials. We couple this model with a genetic algorithm to invert measured TDR traces. To make<br />
this approach more efficient we use hierarchical spatial resolution.<br />
Figure 3.11: Reconstruction of a measured TDR trace (Grenzhof test site, Heidelberg; 30cm three-rod<br />
probe); reflection coefficient ρ vs. time. The ohmic and dispersive dielectric profiles (spatial resolution<br />
3.75cm) for the calculated trace are generated with a hierarchical genetic algorithm.<br />
Background A TDR instrument transmits a<br />
fast rise time pulse on a TDR probe. The probe<br />
usually consists of parallel conductors. Variations<br />
of impedance along the probe causes a partial<br />
reflection of the signal, which is measured.<br />
Furthermore the conductivity and the frequencydependent<br />
dielectric properties between the conductors<br />
of the probe have an affect on the measured<br />
signal.<br />
In this study we want to extract the dielectric<br />
parameters from TDR traces measured at the<br />
Grenzhof test site at Heidelberg to get the water<br />
content. Therefore we reconstruct hierarchical the<br />
spatial distributed dielectric parameters along the<br />
probe with a genetic algorithm.<br />
Funding Deutsche Forschungsgemeinschaft<br />
(Project No. 1080-8/2)<br />
Methods and results We have implemented<br />
a explicite time domain solver for the transmission<br />
line equations (3.3) and (3.4) that uses Debye<br />
model for dispersive media.<br />
∂v<br />
∂x<br />
∂i<br />
∂x<br />
�<br />
= − R ′ �<br />
′ ∂<br />
+ L i (3.3)<br />
∂t<br />
�<br />
= − G ′ �<br />
′ ∂<br />
+ C v (3.4)<br />
∂t<br />
The transmission line equations with piecewise<br />
constant parameters describes a TDR probe. We<br />
couple this solver with a genetic algorithm, in order<br />
to reconstruct the dispersive dielectric and<br />
ohmic profiles along the TDR probe. The genetic<br />
algorithm generates a population with different individuals<br />
(a number of different sets of profiles).<br />
For every individual we calculate a synthetic TDR<br />
trace and compare it with the measured trace.<br />
Then the new population is created from the old<br />
one by crossing the best individuals and random<br />
mutation. We use the genetic approach here, because<br />
the error landscape contains a lot of local<br />
minima.<br />
We implement a hierarchical spatial reconstruction<br />
of the profiles for more efficiency. Therefor<br />
we start with a coarse spatial resolution of the<br />
parameter profile. If the calculated TDR traces<br />
from new individuals do not match better to the<br />
measured trace for a while we increase the spatial<br />
resolution, by cutting old intervals into halves.<br />
This method does not only speed up the profile reconstruction<br />
process but also leads to a smoother<br />
parameter profile.<br />
Outlook/Future work The code will be tested<br />
on TDR traces measured with long probes (1m or<br />
more). Such a long, vertical installed TDR probe<br />
will provide a lot of informations about grounds<br />
properties in a simple way.<br />
Main publication Leidenberger, P., Oswald,<br />
B. and Roth, K. (2005). Efficient reconstruction<br />
of dispersive dielectric profiles using time domain<br />
reflectometry (TDR). Hydrology and Earth System<br />
Sciences Discussions, 2 (4), 1449-1502.
3.1. SOIL PHYSICS 133<br />
3.1.12 3D Full-wave, electromagnetic model of ground penetrating radar<br />
systems<br />
Participating scientist Benedikt Oswald<br />
Abstract Ground penetrating radar (GPR) has been increasingly used in hydrological applications<br />
for subsurface structure investigation. The size of structures that can be resolved is intimately related<br />
to the relevant wavelength of the GPR signal. A finite element time domain 3-dimensional<br />
electrodynamics code has been implemented for studying GPR signal propagation.<br />
+Y[m]<br />
+Y[m]<br />
3<br />
3<br />
2<br />
2<br />
1<br />
1<br />
+Z[m]<br />
2<br />
1<br />
0 0<br />
+Z[m]<br />
2<br />
1<br />
0 0<br />
1<br />
1<br />
2<br />
2<br />
3<br />
+X[m]<br />
-6.08<br />
-12.83<br />
-19.59<br />
-26.34<br />
-33.10<br />
+X[m]<br />
3 -39.85<br />
-46.61<br />
-53.36<br />
pdelta_310_340tsno1400.job.cmp<br />
Figure 3.12: An electromagnetic wave is launched<br />
from a horizontal dipole antenne on the soil surface<br />
(upper side of green regon) and scattered<br />
off 2 dielectric objects (2 yellow regions) buried<br />
in the underground (inside green region); lower<br />
plot: dielectric parameter distribution modeling<br />
two spheres; upper plot: contour plot of the normalized<br />
electric field intensity [dB] for timestep<br />
1400 of the simulation.<br />
Background Increasing GPR resolution requires<br />
shorter wavelength λ which demands higher<br />
frequency f. Due to attenuation of the GPR signal<br />
proportional to frequency, there is a tradeoff<br />
between resolution and penetration depth. For<br />
increasing resolution a full-wave electromagnetic<br />
analysis of GPR signal propagation is essential.<br />
There is evidence that sub-wavelength structures<br />
may be manifest in the radargram. We will use<br />
a 3-dimensional, full-wave model of a simplified<br />
GPR system. We adopt a near field electromag-<br />
8.99<br />
7.86<br />
6.74<br />
5.61<br />
4.49<br />
3.36<br />
2.24<br />
1.11<br />
[dB]<br />
[-]<br />
netic approach, originally [Ohtsu & Kobayashi,<br />
2004] employed in scanning near field optical microscopy<br />
(SNOM). We study the GPR’s response<br />
to sub-wavelength sized objects and investigate<br />
the capability of GPR to resolve those structures.<br />
Funding IUP<br />
Methods and results We have implemented a<br />
3-dimensional finite element code to solve the electric<br />
field vector wave equation (3.5) in the time<br />
domain [Oswald & Roth, 2005a].<br />
∇ × 1<br />
µ ∇ × E + σ ∂E<br />
∂t + ɛ∂2 E<br />
∂2 = −∂J<br />
t ∂t<br />
(3.5)<br />
Locally refined, tetrahedral grids are used to describe<br />
the geometry of the GPR configuration;<br />
this allows for detailed models of delicate geometrical<br />
features. In order to model open region<br />
problems we employ an absorbing boundary<br />
condition (ABC). The code has been validated<br />
on a Hertzian dipole radiating into free space.<br />
We study a simplified GPR configuration of two<br />
spherical objects separated by a sub-wavelength<br />
distance, 0.3 m in the shown example, buried in<br />
the subsurface. The distance between the sphericals<br />
is small with respect to the dominang wavelength<br />
λ. The dielectric structure of the buried<br />
spheres is mapped into the electric field observed<br />
on the surface.<br />
Outlook/Future work The code will be used<br />
in order to study more complicated underground<br />
structures; in particular we want to investigate<br />
synthetical radargram generation in order to compare<br />
those to measured radargrams. We will use<br />
dielectric material properties measured from real<br />
soil [Oswald et al. , 2006] to obtain a realistic<br />
model. This will be one of the first steps towards<br />
the challenge of GPR full-wave inversion.<br />
Main publication Oswald et al. [2006]
134 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.1.13 Simulation and Observation of an Evanescent Wave in Ground Penetrating<br />
Radar Applications<br />
Participating scientist Holger Gerhards, Benedikt Oswald<br />
Abstract A radiating dipole near a single boundary layer was simulated to observe air and ground<br />
wave occurring in Ground Penetrating Radar applications. A semi-analytical approach to solve<br />
Maxwell’s equations in frequency domain with Green’s functions was used. The evanescent characteristic<br />
of the ground wave in air was demonstrated theoretically and experimentally.<br />
x<br />
air<br />
soil<br />
(4)<br />
(3)<br />
(1)<br />
antenna<br />
z<br />
(2)<br />
Background Ground Penetrating Radar<br />
(GPR) is a fast and nondestructive electromagnetic<br />
method to do near subsurface explorations<br />
to estimate soil water content. Reflections are<br />
measured, which occur at boundaries with a dielectric<br />
contrast. Because the relative dielectric<br />
permittivity (εw ≈ 81) of water is much higher<br />
than the soil matrix (εs ≈ 3) in the used frequency<br />
range between 0.1 to 1.0 GHz and assuming that<br />
high water content changes coincides with soil<br />
layers, temporal changes of water content can be<br />
easily detected analyzing travel times.<br />
As shown in Fig. 3.13 for a two layer (air/soil)<br />
model a direct wave from transmitter to receiver<br />
in air and another in the soil can be observed. The<br />
measured ground wave in the air has an evanescent<br />
character, which means, that its amplitude<br />
decays exponentially with the height of the receiving<br />
antenna over the soil. The knowledge about<br />
this phenomena can help to separate the interfering<br />
air and ground waves or to obtain information<br />
about the dielectric properties of the soil surface.<br />
Funding DFG RO 1080 / 10-1<br />
Methods and results A radiating dipole<br />
within a two layer medium was modeled using a<br />
semi-analytical approach based on a spectral decomposition<br />
of the Green’s functions in frequency<br />
domain. The obtained electric field components<br />
were transformed into time domain to be able to<br />
compare the simulation with field measurements.<br />
Figure 3.13: Propagation modes at a single<br />
boundary layer; (1) and (2) spherical wave like<br />
propagation modes in the according material,<br />
(3) ground wave coupling in air (evanescent<br />
wave), (4) air wave coupling in soil (lateral/head<br />
wave)<br />
The exponential decay and its frequency dependence<br />
can be shown by analyzing the amplitudes<br />
of the ground wave wavelet and its shape with<br />
increasing height above the soil.<br />
Analogous to the simulation experiments were<br />
arranged, where the evanescent behavior of the<br />
ground wave was verified and therefore validates<br />
the semi-analytical approach. Furthermore, it was<br />
shown, how far the ground wave interferes with<br />
the air wave.<br />
To obtain insight on the parameters that determine<br />
the attenuation, an equation was derived<br />
from the plane wave approach used in optics. The<br />
dependency on frequency and dielectric contrast<br />
was obtained, which can be qualitatively shown<br />
with the simulated and measured time signals.<br />
Outlook/Future work A frequency analysis<br />
must be applied to check the derived frequency<br />
dependence for experimental data. If air and<br />
ground waves interfere with each other, a quantitative<br />
separation must be developed, such as using<br />
a wavelet analysis. Furthermore, the semianalytical<br />
approach will be extended to simulated<br />
multilayered models, which may help to understand<br />
the depth-dependency of the ground wave<br />
when a near subsurface water content gradient exists.<br />
Main publication Gerhards, Holger, Diplomarbeit,<br />
<strong>Universität</strong> Jena, 2004
3.1. SOIL PHYSICS 135<br />
References<br />
Bayer, A. 2005. X-ray attenuation techniques to explore the dynamics of water in porous media. PhD<br />
thesis, University of Heidelberg.<br />
Bayer, A., Vogel, H.-J., & Roth, K. 2004. Direct measurement of the soil water retention curve<br />
using X-ray absorption. Hydrology and Earth System Sciences Discussion, 8(1), 2–7, SRef–ID:<br />
1607–7938/hess/2004–8–2.<br />
Bayer, A., Vogel, H.-J., Ippisch, O., & Roth, K. 2005. Do effective properties for unsaturated weakly<br />
layered porous media exist? An experimental study. Hydrology and Earth System Sciences Discussion,<br />
2, 1087–1105, SRef–ID: 1812–2116/hessd/2005–2–1087.<br />
Bittelli, M., Flury, M., & Roth, K. 2004. Use of dielectric spectroscopy to estimate ice content in<br />
frozen porous media. Water Resour. Res., 40, W04212, doi:10.1029/2003WR002343.<br />
Braun, H., Christl, M., Rahmstorf, S., Ganopolski, A., Mangini, A., Kubatzki, C., Roth, K., &<br />
Kromer, B. 2005. Possible solar origin of the 1,470-year glacial climate cycle demonstrated in a<br />
coupled model. Nature, in press, doi: 10.1038/nature04121.<br />
Herzog, A. 2005. Free Parameterisation of Soil Hydraulic Properties. Diplomarbeit, University of<br />
Heidelberg.<br />
Leidenberger, P., Oswald, B., & Roth, K. 2005. Efficient Reconstruction of dispersive dielectric profiles<br />
using Time Domain Reflectometry (TDR). Hydrology and Earth System Sciences Discussion, 1449–<br />
1502.<br />
Ohtsu, M, & Kobayashi, K. 2004. Optical Near Fields. 1 edn. Advanced Texts in Physics. Berlin -<br />
Heidelberg: Springer.<br />
Oswald, B., & Roth, K. 2005a. Electromagnetic full wave analysis of sub-wavelength sized objects in<br />
ground penetrating radar (GPR). Page 04437 of: Geophysical Research Abstracts, vol. 7. European<br />
Geosciences Union, EGU, Vienna.<br />
Oswald, B., & Roth, K. 2005b. A full-wave numerical model for the interaction of L-band electromagnetic<br />
radiation with a simplified forest-like vegetation. Page 06741 of: Geophysical Research<br />
Abstracts, vol. 7. European Geosciences Union, EGU, Vienna.<br />
Oswald, B., Doetsch, J., & Roth, K. 2006. A new computational technique for procesing transmission<br />
line measurements to determine dispersive dielectric properties. Geophysics. accepted for<br />
publication.<br />
Oswald, Benedikt, & Roth, Kurt. 2005c. Parallel 3D Finite Element Time Domain Maxwell Solver<br />
- Investigation of Ground Penetrating Radar Sub-Wavelength Resolution. Paul Scherrer <strong>Institut</strong>,<br />
Villigen. 2005, August, 25.<br />
Roth, K. 2005a. Bodenwasser: Bedeutung – Herausforderung – Messung. Eröffnungsvortrag, Soil<br />
Moisture Group, <strong>Universität</strong> <strong>Karls</strong>ruhe, 8. Juni.<br />
Roth, K. 2005b. GPR zur Quantifizierung von Transportprozessen in Böden? <strong>Institut</strong> <strong>für</strong> Geophysik,<br />
<strong>Universität</strong> Kiel, 20. Mai.<br />
Roth, K. 2005c. Measurement and Modeling of Thermal and Hydraulic Dynamics of Permafrost Soils.<br />
Dept. of Earth Sciences, Uppsala University, March 31.<br />
Roth, K., & Wollschläger, U. 2005. Field-Scale Measurement of Soil Water Content. Plenary Session<br />
at International Conference on Human Impacts on Soil Quality Attributes, Isfahan, Iran, September<br />
12–16.<br />
Roth, K., Schulin, R., Flühler, H., & Attinger, W. 1990. Calibration of time domain reflectometry<br />
for water content measurement using a composite dielectric approach. Water Resour. Res., 26(10),<br />
2267–2273.<br />
Roth, K., Wollschläger, U., Cheng, Z., & Zhang, J. 2004. Exploring Soil Layers and Water Tables<br />
with Ground-Penetrating Radar. Pedosphere, 14(3), 273–282.
136 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
Roth, K., Boike, J., & Vogel, H.-J. 2005. Quantifying Permafrost Patterns using Minkowski Densities.<br />
Permafrost and Periglacial Processes, 16, 277–290, doi: 10.1002/ppp.531.<br />
Stöhr, M., & Roth, K. 2005. Gradient-based estimation of local parameters for flow and transport in<br />
heterogeneous porous media. Water Resour. Res., 41, 1–14, W08401, doi:10.1029/2004WR003768.<br />
Topp, G. C., Davis, J. L., & Annan, A. P. 1980. Electromagnetic determination of soil water content:<br />
Measurement in coaxial transmission lines. Water Resour. Res., 16, 574–582.<br />
Ulbrich, C. 2005. Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />
Domain Reflectometry. Diplomarbeit, University of Heidelberg.<br />
Vogel, H.-J. 2005a. From Pore- to Continuum-Scale Understanding of Flow and Transport Processes<br />
in Porous Media. Keynote paper, SSSA-Annual Meeting, November 7-11, 2005, Salt Lake City,<br />
USA.<br />
Vogel, H.-J. 2005b. Hierarchies of flow and transport in soil. Keynote paper, GFHN, 29emes journees,<br />
November 24-25, 2004, Grenoble, France.<br />
Vogel, H.-J. 2005c. Modeling the heterogeneous structure of soil to predict flow and transport. SIAM<br />
Conference on Mathematical and Computational Issues in the Geosciences, June 7-10, 2005, Avignon,<br />
France.<br />
Vogel, H.-J., Tölke, J., Schulz, V. P., Krafczyk, M., & Roth, K. 2005a. Comparison of a Lattice-<br />
Boltzmann Model, a Full-Morphology Model, and a Pore Network Model for Determining Capillary<br />
Pressure-Saturation Relationships. Vadose Zone J., 4, 380–388, doi: 10.2136/vzj2004.0114.<br />
Vogel, H.-J., Cousin, I., Ippisch, O., & Bastian, P. 2005b. The dominant role of structure for<br />
solute transport in soil: Experimental evidence and modelling of structure and transport in a<br />
field experiment. Hydrology and Earth System Sciences Discussion, 2, 2153–2181, SRef–ID: 1812–<br />
2116/hessd/2005–2–1.<br />
Vogel, H.-J., Samouelian, A., & Ippisch, O. 2005c. Modeling structure to predict flow and transport.<br />
Gesellschaft <strong>für</strong> Angewandte Mathematik und Mechanik, 76th Annual Scientific Conference, March<br />
28 - April 1, 2005, Luxembourg.<br />
Vogel, H.-J., Hoffmann, H., & Roth, K. 2005d. Studies of crack dynamics in clay soil. I. Experimental<br />
methods, results, and morphological quantification. Geoderma, 125, 203–211.<br />
Vogel, H.-J., Hoffmann, H., Leopold, A., & Roth, K. 2005e. Studies of crack dynamics in clay soil.<br />
II. A physically based model for crack formation. Geoderma, 125, 213–223.<br />
Wollschläger, U., & Roth, K. 2004. Estimating the three-dimensional hydraulic structure of soils from<br />
ground-penetrating radar measurements. Pages 501–504 of: Proceedings of the 10th International<br />
Conference on Ground Penetrating Radar, Delft.<br />
Wollschläger, U., & Roth, K. 2005. Estimation of temporal changes of volumetric soil water content<br />
from ground-penetrating radar reflections. Subsurf. Sens. Technol. Appl., 6(2), doi: 10.1007/s11220–<br />
005–0007–y.<br />
Yu, Q., Shi, C., Niu, F., He, N., & Roth, K. 2005. Analysis of temperature controlled ventilated<br />
embankment. Cold Reg. Sci. Technol., 42, 17–24, doi:10.1016/j.coldregions.2004.11.004.
3.2. ICE AND CLIMATE 137<br />
3.2 Ice and Climate<br />
Names of group members<br />
Isabel Bengel, diploma student<br />
Felix Jahn, diploma student<br />
Barbara May, diploma student<br />
Christine Offermann, diploma student<br />
Dipl.Phys. Markus Pettinger, PhD student<br />
Dipl.Phys. Martin Schock, PhD student<br />
Dr. Dietmar Wagenbach, head of group<br />
Overarching topic, main methods and specific objectives Among all paleo-archives, only<br />
non-temperated glaciers basically allow the reconstruction of climate as well as of environmental<br />
records. Appropriate ice core studies may thus allow to tackle the crucial problem about the mutual<br />
relationships between changes of climate and bio-geochemical cycles through a retrospective approach.<br />
Figure 3.14: Drilling down to bedrock at Colle Gnifetti (Monte Rosa 4500m a.s.l.) September 2005.<br />
View on the exposed situation of the drill camp near the ice-cliff (dome drilling tent at upper right<br />
rim). Picture: Olaf Eisen<br />
In this context, the ’Ice and Climate’ group concentrates on ice core investigations by deploying the<br />
following species, backed up by standard physical ice properties:<br />
• water-isotopomeres δ 18 O- δD (thermometry)<br />
• various particulate key species as mineral dust, major ions, organic carbon (bio-geochemical<br />
cycles),<br />
• natural radionuclides as terrestrial 210 Pb, cosmogenic 10 Be, 3 H, 36 Cl (solar variability)and on<br />
3 He, 4 He isotopes (basal layer dynamics).<br />
Apart from joint activities within polar ice core studies, emphasis is thereby on the independent<br />
exploration of non-temperated alpine glaciers. Such small scale drill sites are unique in supplementing<br />
high latitude ice core findings, though reliable atmospheric signals would be much more difficult<br />
to elucidate here (Preunkert et al., 2000). In addition to ice core analyses, deserving application<br />
of novel techniques and species (Ruth et al., 2003), also process-oriented field studies are regularly<br />
performed. These specific activities are aimed at understanding the transfer of the atmospheric signals<br />
into the glacier archive as well as at constraining their basic glaciological embedding conditions (as e.g.
138 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
controlled by the near surface and near bed-rock glacier dynamics). Based on external collaborations,<br />
dedicated atmospheric observations are deployed here at various alpine (Preunkert and Wagenbach,<br />
1998) and Antarctic sites (Wagenbach et al. 1998, Piel et al. 2005, which also include isotopic<br />
fingerprints of aerosol samples ( 15 N, 14 C, 26 Al). Within the glaciological issue, joint efforts range<br />
from ground penetrating radar soundings of the internal stratigraphy in alpine glaciers (Eisen et al.<br />
2003) and related glacio-meterological and glacio-chemical surveys, to the prospection of novel dating<br />
techniques ( 3 He/ 4 He (Friedrich, 2003), 14 C, 26 Al/ 10 Be).<br />
Overview on principal activities and achievements<br />
Alpine research<br />
a) EU- ALP-IMP related: Long term isotope records from two deep Mt. Blanc cores could be added<br />
to the already existing array of respective Monte Rosa records, enhancing the significance in the<br />
reconstruction of climate related changes (see 3.2.4). Site selection study of ideal drill site for high<br />
resolution records back to 1000 years by radar tracking of the internal layering by University Zürich<br />
(Böhlert, 2005) and drilling there to bedrock in collaboration with KUP of University Bern could be<br />
successfully achieved. First estimates indicate a net surface accumulation of the new site, significantly<br />
lower than 15 cm water per year, which may offer a relatively high time resolution in the bottom<br />
core section. A further intensive field campaign for sampling a special non-temperated ice cap at<br />
lower altitude was performed in collaboration with university Zürich, in order to prospect the basic<br />
stratigraphycal properties of this ice body (see 3.2.1) .<br />
b) EU-CARBOSOL project related: The first continuous records into the pre-industrial area of dissolved<br />
organic carbon (DOC) could be established (partly in seasonal resolution) (see 3.2.5). Also<br />
aimed at the long term change of the organic fraction of the aerosol body, the first radiocarbon investigations<br />
on european wide aerosol samples could be accomplished after final revision of the sample<br />
preparation line (see 3.2.2).<br />
Antarctica<br />
a) Related to EPICA: Field sampling of bottom core for He-isotope analyses could be accomplished<br />
at Berkner Island and at EPICA Dome C (actually the oldest ice available) drill sites. Respective<br />
mass spectrometric analyses by the ”Groundwater and Paleoclimate” group, along with noble gas ice<br />
core samples obtained from the previous campaigns are expected to come up in the near future.<br />
Investigation of the air firn transfer of 10 Be (and associated host particles) were extended from investigations<br />
at the central EPICA DML drill site(Piel et al. 2005) by a bi-annual record from a recent<br />
firn core obtained from coastal Berkner Island. In this context long term observations of atmospheric<br />
radionuclides at Neumayer Station were regularly continued (see 3.2.3).<br />
b)The Lake Vostok: Additional ice samples of the Vostok bottom ice core (accreted from Lake Vostok)<br />
as well as meteoric reference ice were obtained from LGGE-CRNS. Grenoble and analysed for dissolved<br />
organic Carbon, confirming the outstanding low DOC level, already obtained in previous pilot analyses<br />
(Bulat et al.2004) (see 3.2.5)<br />
c) New developments focussed on the extension of automatic aerosol sampling in central Antarctica<br />
and on the prospection of the 26 Al/ 10 Be dating tool, to be deployed for very old ice. (see 3.2.6)<br />
Novel activities envisaged in the following year Launching a radiocarbon dating project focussing<br />
on various non-temperated Alpine ice bodies (with VERA and University Zürich).<br />
Supplementing continuous flow ice core analyses by a screening method for the total gas content, as<br />
to infer the melt-layer stratigraphy (with Groundwater and Paleoclimate Group)<br />
Pilot studies on the Little Ice Age variability of 10 Be possibly archived in a new sediment core recovered<br />
from the well explored high alpine Schwarzsee ob Sölden (with University Innsbruck and Heidelberg<br />
Academy of Sciences)<br />
Re-designing of the Air Chemistry Observatory at the Antarctic Neumayer Station III (with AWI and<br />
the Carbon Cycle Group)<br />
Funding and major cooperations Funding relayed on the EU-projects CARBOSOL (Anthropogenic<br />
change of organic carbon aerosol in West- Europe)and ALP-IMP (Climate variability in the<br />
greater Alpine region), the AWI-Cooperation contract (Investigation of ice cores and aerosol of polar
3.2. ICE AND CLIMATE 139<br />
regions) and on an Austrian Research Fund project jointly with VERA ( 26 Al- 10 Be investigations). Important<br />
logistical support was obtained from the ESF-EU core project EPICA (European Ice Drilling<br />
in Antarctica).<br />
Vital long term collaborations (also operating outside funding projects) comprised joint activities<br />
with:<br />
• Alfred Wegener <strong>Institut</strong>e for Polar and Marine Research (various polar investigations),<br />
• Laboratoire de Glaciolocique et Geophisique-CRNS, Grenoble (alpine ice cores and Lake Vostok),<br />
• Geographical <strong>Institut</strong>e of the University Zürich (alpine glaciology and glacio-meteorology)<br />
• Klima und <strong>Umweltphysik</strong>, University Bern (ice core drilling and analyses),<br />
• VERA-laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik der <strong>Universität</strong> Wien (AMSanalyses)<br />
• <strong>Institut</strong>e for Zoology and Limnology, University Innsbruck (ice biology and high alpine lake<br />
sediments),<br />
• British Antarctic Survey, Cambridge (Berkner Island Project)<br />
• <strong>Institut</strong>e for Environmental Geochemistry, University Heidelberg (trace element analyses)<br />
Internal collaboration concentrates on: the Neumayer Observatory, 14 C and radon investigations<br />
(Carbon Cycle Group), noble gas and tritium analyses (Groundwater and Paleoclimate Group) as<br />
well as on long term marine 10 Be sediment records (Heidelberger Academy of Sciences).<br />
Publications<br />
Peer Reviewed Publications<br />
1. Bulath et al. [2004]<br />
2. Legrand et al. [2005]<br />
3. Piel et al. [accepted]<br />
Other Publications<br />
1. Auer et al. [2005]<br />
2. Bigler et al. [2005]<br />
3. Dombrowski-Etchevers et al. [2005]<br />
4. Pettinger et al. [2005]<br />
5. Schock et al. [2005]<br />
6. Steier et al. [2005]<br />
7. Wegner et al. [2005]<br />
Diploma Theses<br />
1. Bengel [2005]<br />
2. May [2005]<br />
Invited Talks<br />
1. Schock et al. [2005]<br />
2. Pettinger et al. [2005]<br />
3. Wagenbach [2004]
140 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.2.1 Glaciological pilot studies on a cold miniature ice cap<br />
Participating scientist Isabel Bengel and Wilfried Haeberli ∗<br />
∗ Glaciology and Geomorphodynamics Group, Geography Department, University of Zürich<br />
Abstract The study deals with the glacio-chemical characterisation of a high alpine miniature ice<br />
cap (Piz Murtèl, 3433 m a.s.l., Oberengadin). Inside an ice tunnel the 210 Pb and 3 H point to<br />
ice, surprisingly less than 50 years old. On the whole, the ice body of Piz Murtèl exhibits a dust<br />
stratigraphy and distinct age distribution, but less regular than in sedimentary ice.<br />
Figure 3.15: Above: Northwest flank of Piz<br />
Murtèl (3300 m a.s.l.) seen after an intense summer<br />
ablation period with indicated 2004 samplings.<br />
Below: Shallow profile of 3 H (T 1/2 =<br />
10.3 a) and 210 Pb (T 1/2 = 22 a) obtained in the<br />
interior tunnel floor, showing surprisingly modern<br />
ice conditions.<br />
Background Different to high alpine cold<br />
glaciers (above 4000 m a.s.l.) the environmental<br />
information, which maybe contained in lower elevation<br />
miniature ice caps remained virtually unknown.<br />
Because of a small mass turnover and low<br />
ice motions in such ice caps a relatively high age<br />
in the order of some 1000 years may be expected<br />
(Haeberli et al., 2004). An alpine prime example<br />
for a miniature ice cap provides the Piz Murtèl<br />
(Oberengadin, Suisse) which is analysed in this<br />
study. Being non-temperate despite its low elevation,<br />
the ice cap might be used as an archive<br />
containing the history of past minimum glacier<br />
extend. The primary aim of this study was to<br />
gather basic information on the internal stratigraphy,<br />
age structure and accumulation processes<br />
by screening the isotope and chemical ice properties.<br />
Methods and results In October 2004, a continous<br />
50 m profile at the northwest flank and a<br />
shallow ice core in an artifical ice tunnel were sampled<br />
in collaboration with University of Zürich.<br />
First measurements of the variability of ice impurities<br />
have been carried out based on fast standard<br />
methods including continous profiling of particles,<br />
liquid conductivity and electrical ice conductivity.<br />
Thereby it turned out, that the mineral dust variability<br />
in the samples – although partly consisting<br />
of superimposed ice and containing ablation<br />
dirt– could be measured without essential modifications.<br />
Also the electrical method generated<br />
reproducible profiles, allowing to record the ice<br />
stratigraphy at a sub-cm resolution. Exemplary<br />
radionuclide analyses gave (as expected) a 210 Pb<br />
down slope increase but surprisingly young ice<br />
of less than 50 years ( 210 Pb and 3 H) inside the<br />
calotte. Although soluble ion components appeared<br />
to be strongly affected by elution, a DOC<br />
level around 200 ppb was found, making dating by<br />
14 C analyses possible. On the whole, the ice of<br />
Piz Murtèl exhibits a dust stratigraphy and spatial<br />
age distribution which is, however, modified<br />
by the untypical properties of the miniature ice<br />
cap, governed by complicated ablation / accumulation<br />
processes.<br />
Outlook/Future work Drilling into and dating<br />
of the basal layer.<br />
Main publication Bengel [2005]
3.2. ICE AND CLIMATE 141<br />
3.2.2 Constraining the anthropogenic fraction of carbonaceous aerosol by<br />
14 C-analysis<br />
Participating scientists Barbara May, Samuel Hammer and Peter Steier ∗<br />
∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />
Abstract A sample preparation line for 14 C analysis of aerosol filters for AMS has been revised<br />
and characterised. First analyses revealed that the European carbonaceous aerosol is of mainly recent<br />
origin, while the free tropospheric clean air condition indicates a more fossil contribution.<br />
Figure 3.16: Range of the relative contribution of<br />
fossil carbon seen in aerosol sampled during winter<br />
and summer half years at various mountain sites<br />
(Sonnblick, Austria; Schauinsland, Germany; Puy<br />
de Dôme, France). Note the significantly higher<br />
fossil carbon fraction during the relatively clean<br />
winter conditions.<br />
Background While inorganic aerosols, like sulphate,<br />
are relatively well understood regarding<br />
their anthropogenic sources and related radiative<br />
forcing implications, anthropogenic change of carbonaceous<br />
aerosol and its radiative influence are<br />
virtually unknown. Therefore, we attempted to<br />
quantify the recent versus fossil fraction of total<br />
organic carbon from European wide sampled<br />
aerosol filters by the 14 C approach. Here, 14 C<br />
measurements may allow to quantitatively distinguish<br />
between the fossil fraction, completely free<br />
of 14 C, and the recent one, carrying the present<br />
day 14 C signature of biogenic carbon. The low<br />
carbon mass and various fractionation processes<br />
associated with aerosol sample combustion make<br />
however thorough experimental efforts necessary<br />
to achieve reliable 14 C results.<br />
Funding EU CARBOSOL-project: Present<br />
and retrospective state of organic versus inorganic<br />
aerosol over Europe: Implications for climate<br />
Methods and results For analysing the 14 C<br />
signature of aerosol filters, a pilot system for controlled<br />
sample combustion in a gas stream and<br />
subsequent purification and extraction of the CO2<br />
(designed by Hammer (2003)) for δ 13 C and AMS<br />
14 C analysis (Steier et al, 2004) was optimised and<br />
characterised. It was shown, that the combustion<br />
process efficiency increases when pure oxygen is<br />
used as combustion gas. Furthermore a water cold<br />
trap is necessary in excess as well as a second combustion<br />
step (assuring the total combustion of the<br />
organic matter). The system allows to reasonably<br />
quantify a minimal carbon amount of 65 µgC<br />
with an accuracy of 10 %. The typical blank level<br />
of the entire process is found to be 63 µgC with<br />
a 14 C content close to 80 pmC (percent modern<br />
Carbon).<br />
A first systematic investigation of CARBOSOL<br />
aerosol filters, specifically selected by 210 Pb data,<br />
indicated: (1) Around 75 % of the carbonaceous<br />
aerosol is released by non-fossil sources, which appear<br />
to be rather uniformly distributed over Western<br />
Europe. (2) Under free tropospheric clean air<br />
conditions nearly one third of the carbonaceous<br />
aerosol may be ascribed to fossil sources (see Figure).<br />
An attempt to interpret these results in<br />
terms of anthropogenic emissions, considering the<br />
variable amount of bomb 14 C added by biomass<br />
burning, proved to be difficult.<br />
Outlook/Future work The system basically<br />
allows the separation of BC (black carbon) and<br />
OC (organic carbon), which may improve the interpretation<br />
in terms of anthropogenic emissions.<br />
Furthermore, upcoming ice core based CAR-<br />
BOSOL results of pre-industrial organic aerosol<br />
concentrations may allow an independent comparison<br />
of the anthropogenic contribution to present<br />
day organic aerosol levels.<br />
Main publication May [2005]
142 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.2.3 Recent variability of the cosmogenic nuclides 10 Be and 7 Be in coastal<br />
Antarctica<br />
Participating scientists Christine Offermann, Matthias Auer ∗ and Robert Mulvaney ∗∗<br />
∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />
∗∗ British Antarctic Survey, Cambridge<br />
Abstract The solar activity proxy 10 Be is investigated in a firn core of coastal Antarctica (Berkner<br />
Island) along with the 10 Be and 7 Be activities, obtained from aerosol filters at Neumayer station.<br />
Data evaluation is aimed at assessing the air-firn transfer of 10 Be.<br />
Background Cosmogenic 10 Be archived in polar<br />
ice sheets provides an unique tool in reconstructing<br />
solar activity changes. Dueto various<br />
glacio-meteorological noise, the interpretation of<br />
those, latitude dependant, records remained however<br />
ambiguous . Moreover only very few 10 Be ice<br />
core findings are available from the recent (preinstrumental)<br />
era. In this context IUP started investigating<br />
10 Be in relatively recent ice-cores from<br />
different Antarctic drill sites, focussing on the 11year<br />
solar cycle and the outstanding solar minima<br />
of the last 500 years.<br />
As the influence of meteorological noise on 10 Be<br />
is barely understood and strongly depends on the<br />
drill site, investigations at the central Antarctic<br />
EPICA-DML drill site (Wegner 2003, Wegner<br />
et al. 2005) were extended to a coastal site at<br />
Berkner Island (BI) (Rohlfs, 2004). In the coastal<br />
area, also atmospheric long term observations of<br />
7 Be and 10 Be are performed by IUP at Neumayer<br />
(NM) Station, allowing comparison with concurrent<br />
10 Be firn core data with respect to the 11-year<br />
cycle.<br />
Methods and results In this thesis the still<br />
missing high resolution 10 Be firn record from<br />
coastal Antarctica should be provided by establishing<br />
a continuous bi-annual 10 Be profile from a<br />
firn core drilled for this purpose at BI. To study<br />
the glacio-meteorological influence on the air-firn<br />
transfer of 10 Be, the aerosol time series from NM<br />
was extended by the 2004 values of 7 Be concentrations<br />
and completed by missing 10 Be data of<br />
the previous years. The challenge to gain an absolute<br />
core chronology was accomplished by combining<br />
δ 18 O and Electric Conductivity Measurement(ECM)<br />
based acidity profiling, taking advantage<br />
of the seasonal variation of the data. Moreover,<br />
to employ the VERA (AMS) facility, our<br />
10 Be target-preparation procedure has been revised<br />
with respect to the final BeO handling.<br />
∆ 7 Be [fCi/scm]<br />
100<br />
50<br />
0<br />
-50<br />
7 Be at Neumayer Station, Antarctica<br />
1985 1990 1995 2000 2005<br />
year<br />
Figure 3.17: Deviation of monthly mean atmospheric<br />
7 Be activity from the total mean of 112<br />
fCi/m 3 . Note the regular variation related to the<br />
seasonal cycle. Black line: SSA derived extraction<br />
of the underlying Schwabe cycle.<br />
While inspection of the atmospheric 7 Be record<br />
reveals the expected Schwabe cycle, also found<br />
at EPICA-DML, very recently obtained 10 Be raw<br />
data from BI does not show such prominent regular<br />
changes for the first 30 years. The reason for<br />
this discrepancy is not elucidated yet.<br />
Final work Correction for interannual snow accumulation<br />
and revision of the core chronology is<br />
envisaged to gain a useful record of the short term<br />
10 Be variability at BI. Only then comparison with<br />
concurrent changes at EPICA-DML, NM and neutron<br />
monitor data would be possible. Thus, subsequent<br />
analysis for recent trends may show if the<br />
expected decrease (Solanki et al, 2004) due to high<br />
solar activity can be found in the 10 Be record.<br />
Main publications Upcoming diploma thesis
3.2. ICE AND CLIMATE 143<br />
3.2.4 Climatic significance of stable water isotope records from Alpine ice<br />
cores.<br />
Participating scientists Markus Pettinger, Susanne Preunkert ∗ , Ralph Böhlert ∗∗ and Reinhard<br />
Böhm ∗∗∗<br />
∗ LGGS - CNRS, Grenoble<br />
∗∗ Glaciology and Geomorphodynamics Group, Department of Geography, University of Zürich<br />
∗∗∗ ZAMG, Wien<br />
Abstract Upstream effects associated with local variations in snow deposition that influence long<br />
term isotopic trends recorded in Alpine ice cores were investigated. Isotope records of two Mont Blanc<br />
ice show the recent warming trend with high isotope sensitivity, whereas long term records show only<br />
weak correlation with instrumental temperature data.<br />
Figure 3.18: δ 18 O- records of a low<br />
(0.2 m w.e./yr, middle) and a high<br />
(1.1 m w.e./yr, bottom) accumulation core<br />
from the Mont Blanc summit range.<br />
Background Isotope δ 18 O and δD records from<br />
high Alpine cold glaciers may provide complementary<br />
records to polar cores, including the unique<br />
possibility to extend the 250 years instrumental<br />
climate time series only available from western<br />
Europe (Schöner et al., 2002). On the other<br />
side various glaciological constrains hamper the<br />
straightforward interpretation of alpine isotope<br />
records in terms of temperature changes. A multicore<br />
study was therefore set up to partly compensate<br />
for this basic shortcoming.<br />
Funding EU-project ALP-IMP (Multicentennial<br />
climate variability in the Alps based on<br />
Instrumental data, Model simulations and Proxy<br />
data)<br />
Methods and results To determine systematic<br />
upstream effects in the cachment area of<br />
Monte Rosa deep ice cores three shallow firn cores<br />
have been drilled along their flow line down to a<br />
reflection layer determined by radio echo sounding<br />
(as to guarantee an common time span). The<br />
systematic change in the core mean δ 18 O value<br />
along the flow line has been used to improve the<br />
overall upstream corrections. The new data exhibit<br />
in the upper region of the flowline a linear<br />
δ 18 O-accumulation relation of 1.9 � per m water<br />
equivalent. Thus, additional corrections up to<br />
0.4� to those of Keck (2001) are necessary for<br />
the long term trends recorded in Monte Rosa ice<br />
cores. A different approach was chosen for the<br />
Mont Blanc ice core in flank position. In this case,<br />
the changes with depth of the winter snow fraction<br />
induced by wind erosion was determined, but<br />
only an insignificant dependance with depth could<br />
be found.<br />
In the time span of 1920 to 1995 both new Mont<br />
Blanc ice cores show no clear correlation with instrumental<br />
temperature, wich may be due to poor<br />
dating. In contrast the recorded recent warming<br />
trend (1980-2000) exhibits ∆δ 18 O/∆T relations<br />
between 1.5 and 3 �/ ◦ C with high significance<br />
in all ice cores. Previous studies show a relation<br />
of 1.7 �/ ◦ C in the period of 1920 to 1995. Different<br />
to existing Monte Rosa records showing an<br />
odd long term trend towards lower isotope values<br />
into the medieval era, the new Mont Blanc ice divide<br />
core exhibits no such trend, but, if any, only<br />
a weak δ 18 O increase by 0.6�. The respective<br />
ice core chronology as based on a flow only model<br />
(Raymond, 1983) is however still uncertain.<br />
Future work Dating and isotopic analysis of<br />
the new Monte Rosa ice core, drilled to get high<br />
resolution records. In addition the model based<br />
dating of the low accumulation Mont Blanc ice<br />
core has to be improved by matching with known<br />
dust and volcanic horizons.<br />
Main publication Pettinger et al. [2005]
144 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
3.2.5 Analyses of dissolved organic carbon (DOC) at low levels in Alpine<br />
and polar glaciers<br />
Participating scientists Martin Schock, Steffen Greilich ∗ and Jean-Robert Petit ∗∗<br />
∗ Heidelberger Akademie der Wissenschaften, Forschungsstelle Archaeometrie<br />
∗∗ LGGE-CNRS, Grenoble<br />
Abstract Deploying a novel method for ultra-low DOC analysis, DOC in high Alpine precipitation<br />
was found to be increased by a factor of 2-4 (to up to 4 · 10 −7 gC/g) since preindustrial times, wheras<br />
DOC level less than about 10 −8 gC/g are seen in Antarctic ice cores.<br />
Background The bulk quantity DOC constitutes<br />
an important part of the impurity content<br />
of non-temperated glaciers. Related retrospective<br />
studies would be highly relevant therefore in terms<br />
of radiative forcing, past atmospheric carbon cycles<br />
and englacial microbial activity. However no<br />
systematic ice core analyses of DOC were available,<br />
yet, due to unsolved contamination problems<br />
and insufficient sensitivity of conventional TOC<br />
analysers. In this context a dedicated flow injection<br />
system, based on UV induced DOC degregation<br />
has been developed (along with an appropriate<br />
decontamination procedure as to cope with the<br />
challenge to analyse ice cores, drilled in kerosene<br />
filled bore holes).<br />
Funding EU-CARBOSOL project : ”Present<br />
and Retrospective State of Organic versus Inorganic<br />
Aerosol over Europe : Implications for Climate”<br />
Methods and results Sample decontamination,<br />
(deploying partial melting or a melting<br />
probe) is shown to control the precision and<br />
quantitative detection limit (presently around<br />
5 · 10 −9 gC/g). Extensive comparison with a high<br />
temperature combustion method revealed that the<br />
UV degradation efficiency for most of the relevant<br />
DOC species seems to be close to 90% .<br />
Various high Alpine ice cores have been systematically<br />
analysed for DOC (partly in seasonal resolution),<br />
indicating a significant change by typically<br />
a factor of 2 to 4 since the pre industrial era.<br />
This presumably anthropogenic effect is however<br />
clearly lower, compared to concurrent changes of<br />
man made inorganic species, like sulphate (Preunkert<br />
et al., 2001).<br />
DOC-surveys of a cold, low elevation Alpine ice<br />
cap (Bengel, 2005), in view of radiocarbon dating<br />
of the ice body genesis via DOC indicated, that<br />
about 1 kg ice would be needed for this purpose.<br />
Most difficult in terms of reliable measurements<br />
have been Antarctic ice cores, where DOC levels<br />
approach the limit of detection. Including polar<br />
ice cores, no big difference is seen in the pre<br />
industrial DOC level between Alpine and Greenland<br />
sites, wheras an interhemispheric difference<br />
by one order of magnitude shows up with respect<br />
to Antarctica. Here, DOC analyses in accreted ice<br />
from Lake Vostok gave a mean DOC level lower<br />
by roughly a factor of 50, than previously reported<br />
by Priscu et al., (1999), giving much less room for<br />
viable micro biological activities, than hitherto assumed<br />
(Bulat et al 2004).<br />
Figure 3.19: Range of dissolved organic carbon<br />
(DOC) content in various ice bodies (including accreted<br />
ice from Lake Vostok), displayed by median<br />
as well as by 25% and 75% percentils, respectively<br />
Outlook/Future work Radiocarbon dating of<br />
the DOC fraction in Alpine ice.<br />
Main publication J.-R. Petit , J. Flückiger, M.<br />
Leuenberger, W. Haeberli, R. Psenner , Dissolved<br />
organic carbon (DOC) in ice samples from nontemperated,<br />
polar and Alpine glaciers. Geophysical<br />
Research Abstracts, Vol. 7, 08671, 2005<br />
Schock et al. [2005]
3.2. ICE AND CLIMATE 145<br />
3.2.6 Novel tools in ice core research<br />
Participating scientists Dietmar Wagenbach, Rolf Weller ∗ and Matthias Auer ∗∗<br />
∗ AWI-Bremerhaven<br />
∗∗ VERA Laboratory, <strong>Institut</strong> <strong>für</strong> Isotopenforschung und Kernphysik, <strong>Universität</strong> Wien<br />
Abstract New developments on automatic aerosol sampling in central Antarctica and on the prospection<br />
of the 26 Al/ 10 Be dating tool are reported along with their futur application.<br />
Figure 3.20: Seasonal cycle of biogenic sulfate in central Antarctica obtained by automatic aerosol<br />
samplings (left), first tropospheric 26 Al/ 10 Be ratios derived from Antarctica Neumayer (Ant), alpine<br />
Sonnblick (SBO) and Schauinsland (SIL) Station (right).<br />
Background Among various shortcomings in<br />
the interpretation of Antartic ice core records,<br />
the air-firn transfer of aerosol species as well as<br />
the age and stratigraphical properties of the basal<br />
core sections continue to provide outstanding challenges.<br />
On the one hand, this is mainly due to<br />
missing year round atmospheric aerosol observations<br />
at central Antartic drill sites and on the<br />
other, due to the missing of appropriate dating<br />
tools reaching back beyond several 100ka. a) In<br />
order to reduce the first deficit IUP developed an<br />
autonomous aerosol sampling device (ROBERTA)<br />
(Preunkert and Wagenbach 1998) to be deployed<br />
year round at the EPICA-DML drill site in the<br />
Atlantic sector of east Antartica. b) In close collaboration<br />
with the University of Vienna AMS facility<br />
(VERA) the dating deficit of very old ice<br />
samples has been tackled by exploring the feasibility<br />
of the 26 Al/ 10 Be ratio (apparent T 1/2 =1.3<br />
10 −6 a) as a radiometric chronometer.<br />
Fundings a) AWI-Cooperation Contract, b)<br />
joint project within the Austrian Research<br />
Fund(FWF).<br />
First results a) Year round, unattended running<br />
of the aerosol sampling system could be successfully<br />
achieved in close collaboration with AWI-<br />
Bremnerhaven, providing first records on the seasonal<br />
change of major ion in central Antarctica.<br />
26 Al/ 10 Be<br />
3x10 -3<br />
2x10 -3<br />
1x10 -3<br />
0<br />
ANT<br />
SBO<br />
Adding ion concentration data in sub-seasonal resolution<br />
from concurrent firn deposits along with<br />
automatic snow hight recordings may now allow to<br />
elucidate the drill site specific air-firn transfer of<br />
the ionic aerosol species. A second sampler version<br />
substantially improved with respect to the<br />
consecutive activation of the sampling units has<br />
been put in operation.<br />
b) After establishing and optimizing the 26 Alanalysis,<br />
first tropospheric 26 Al/ 10 Be ratios could<br />
be obtained from Antarctic and mid-latitude<br />
aerosol samples. The reasonable constant ratios<br />
indicate a control by atmospheric production,<br />
rather than by terrestrial or cosmic dust inputs<br />
(which is a pre-requisite for the dating application).<br />
Future work a) Possibly deploying one of the<br />
two devices at a high altitude drill site in the western<br />
Himalayans (Pamir).<br />
b) 26 Al/ 10 Be analyses will be extended to recent<br />
polar snow and glacial ice core samples and supplemented<br />
by 53 Mn (solely derived from interplanatary<br />
dust) as to obtain a quantative estimate<br />
of the IPD influence on the 26 Al variability in polar<br />
ice cores. If successful 26 Al/ 10 Be dating might<br />
be applied the first time on ice core samples (e.g.<br />
on the basal section of the EPICA Dome C core,<br />
which comprises the oldest ice recovered so far).<br />
Main publication Auer et al. [2005]<br />
SIL
146 CHAPTER 3. TERRESTRIAL SYSTEMS<br />
References<br />
Auer, M., Kutschera, W., Priller, A., Wagenbach, D., Wallner, A., & Wild, E. M. 2005 (September<br />
5-10). Atmospheric 26 Al and 10 Be as a dating tool for climate archives (Abstract). vol. The 10th<br />
International Conference on Accelerator Mass Spectrometry Berkeley, California.<br />
Bengel, I. 2005. Spurenstoffglaziologische Pilotuntersuchungen an einer kalten Miniatureiskappe.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Bigler, M., Röthlisberger, R., Ruth, U., Siggaard-Andersen, M.-L., Steffensen, J. P., Hansson, M. E.,<br />
Goto-Azuma, K., Fischer, H., & Wagenbach, D. 2005. A new high-resolution chemical ice core<br />
record over the last glacial period from NGRIP. Geophysical Research Abstracts, Vol 7, 05616.<br />
Böhlert, R. 2005. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> Geographie, <strong>Universität</strong> Zürich.<br />
Böhm, R., Brunetti, M., Maugeri, M., Nanni, T., & Schöner, W. 2001. Regional temperature variability<br />
in the European Alps: 1760-1998 from homogenized instrumental time series. International<br />
Journal of Climatology, 21, 1779 – 1801.<br />
Bulath, S., Alekhina, I., Blot, M., Petit, J.-R., de Angelis, M., Wagenbach, D., Lipenkov, V., Valilyeva,<br />
L., Wloch, D., Raynaud, D., & Lukin, V. 2004. DNA singature of thermophilic bacteria from the<br />
aged accretion ice of Lake Vostok, Antarctica: implications for searching for life in extreme icy<br />
environments. International Journal of Astrobiology, 3(1), 1–12.<br />
Dombrowski-Etchevers, I., Peuch, V.-H., Wagenbach, D., & Legrand, M. 2005. Validation of concentrations<br />
of lead-210 in high altitude simulated by MOCAGE. Geophysical Research Abstracts, Vol<br />
7, 09009.<br />
Eisen, O., Nixdorf, U., Keck, L., & Wagenbach, D. 2003. Alpine Ice Cores and Ground Penetrating<br />
Radar: Combined Investigations for Glaciological and Climatic Interpretations of a Cold Alpine Ice<br />
Body. Tellus, 55B(5), 1007–1017.<br />
Friedrich, R. 2003. Helium in polaren Eisschilden. Diplomarbeit, Instiut <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong><br />
Heidelberg.<br />
Haeberli, W., Frauenfelder, R., Kääb, A., & Wagner, S. 2004. Characteristics and potential climatic<br />
significance of ”miniature ice caps” (crest- and cornice-type low-altitude ice archives. Journal of<br />
Glaciology, 50(168), 129–136.<br />
Hammer, S. 2003. Einsatz von Radioisotopen zur Interpretation der raum-zeitlichen Variabilität von<br />
organischem Aerosol. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Keck, L. 2001. Climate significance of stable isotope records from Alpine ice cores. Ph.D. thesis,<br />
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Legrand, M., Preunkert, S., Galy-Lacaux, C., Liousse, C., & Wagenbach, D. 2005. Atmospheric yearround<br />
records of dicarboxylic acids and sulfate at three French sites located between 630 and 4360<br />
m elevation. Journal of Geophysical Research, 110, D13302, doi:10.1029/2004JD005515.<br />
May, B. 2005. Quantification of the fossile fraction of carbonaceous aerosol by radiocarbon analysis.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Pettinger, M., Keck, L., Fischer, H., Wagenbach, D., Preunkert, S., Böhm, R., Hoelzle, M., & Hoffmann,<br />
M. Leuenbergerand G. 2005. Cenntennial scale isotope thermometry from Alpine ice core<br />
records: shortcomings and challenge. Geophysical Research Abstracts, Vol 7, 07941.<br />
Piel, C., Weller, R., M.Huke, & Wagenbach, D. accepted. Atmospheric methane sulfonate and non-sea<br />
salt sulfate records at the EPICA deep-drilling site in Dronning Maud Land. Journal of Geophysical<br />
Research, 2005JD006213.<br />
Preunkert, S., & Wagenbach, D. 1998. An automatic recorder for air/firn transfer studies of chemical<br />
aerosol species at remote glacier sites. Atmospheric Environment, 23, 4021–4030(10).<br />
Preunkert, S., Wagenbach, D., Legrand, M., & Vincent, C. 2000. Col du Dome (Mont Blanc Massif,<br />
French Alps) suitability for ice core studies in relation with past atmospheric chemistry over Europe.<br />
Tellus, 52B, (3), 993–1012.
3.2. ICE AND CLIMATE 147<br />
Preunkert, S., Legrand, M., & Wagenbach, D. 2001. Sulfate trends in a Col du Dome (French Alps) ice<br />
core : A record of anthropogenic sulfate levels in the European midtroposphere over the twentieth<br />
century. Journal of Geophysical Research, 106, 31991–32004.<br />
Priscu, J., Adams, E., Lyons, W., Voytek, M., Mogk, D., Brown, R., McKay, C., Takacs, C., Welch,<br />
K., Wolf, C., Kirshtein, J., & Avci, R. 1999. Geomicrobiology of Subglacial Ice Above Lake Vostok,<br />
Antarctica.<br />
Raymond, C. F. 1983. Deformation in the vicinity of divides. Journal of Glaciology, 34, 357–373.<br />
Rohlfs, J. 2004. Zeitliche Variation von 10 Be in der Küstenantarktis - Eine Eiskernzeitreihe von<br />
Berkner Island. Diplomarbeit. <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Schock, M., Greilich, S., Wagenbach, D., Preunkert, S., Legrand, M., Petit, J. R., Flückiger, J.,<br />
Leuenberger, M., Haeberli, W., & Psenner, R. 2005. Dissolved organic carbon (DOC) in ice samples<br />
from non-temperated, polar and Alpine glaciers. Geophysical Research Abstracts, Vol. 7, 08671.<br />
Schöner, W., Auer, I., Böhm, R., Keck, L., & Wagenbach, D. 2002. Spatial representativity of air<br />
temperature information from instrumental and ice core based isotope records in the European<br />
Alps. Annals of Glaciology, 35, 157–161.<br />
Solanki, S. K., Usoskin, I. G., Kromer, B., Schüssler, M., & Beer, J. 2004. Unusual activity of the<br />
Sun during recent decades compared to the previous 11,000 years. Nature.<br />
Steier, P., Dellinger, F., Kutschera, W., Rom, W., & Wild, E. M. 2004. Pushing the precision limit<br />
of C14 measurements with AMS. Radiocarbon, 46, 969–978.<br />
Steier, P., Drosg, R., Kutschera, W., Wild, E. M., Fedi, M., Wagenbach, D., & Schock, M. 2005.<br />
Radiocarbon determination of particulate organic carbon (POC) in non-temperated, Alpine glacier<br />
ice (Abstract). The 10th International Conference on Accelerator Mass Spectrometry Berkeley,<br />
California, September 5-10, 2005.<br />
Wagenbach, D. 2004. Potential and restrictions of Alpine (mid-latitude) ice cores. Invited talk, SCIEM<br />
2000 (The synchronisation of civilization in the eastern Mediterranean in the 2nd Millenium BC)<br />
Workshop: Ashes and Ice, Vienna.<br />
Wagenbach, D., Ducroz, F., Mulvaney, R., Keck, L., Minikin, A., Legrand, M., Hall, J. S., & Wolff,<br />
E. W. 1998. Sea-salt aerosol in coastal Antarctic regions. Journal of Geophysical Research, 103(D9),<br />
10961–10974, 10.1029/97JD01804.<br />
Wegner, A. 2003. Die Geschichte der Sonnenaktivität im Antarktischen Eis Nachweis produktionsbedingter<br />
10 Be - Schwankungen. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Wegner, A., Rohlfs, J., Huke, M., Stanzick, A., Wagenbach, D., Oerter, H., Sommer, S., Mulvaney,<br />
R., & Kubik, P. 2005. Bi-annual to decadal 10 Be variability in firn cores from Dronning Maud Land<br />
(DML) and Berkner Island (BI), Antarctica. Geophysical Research Abstracts, Vol 7, 08396.
Aquatic Systems<br />
4.1 Groundwater and Paleoclimate . . . . . . . . . . . . . . . . . . . . . . . . 151<br />
4.2 Lake Research (Limnophysics) . . . . . . . . . . . . . . . . . . . . . . . . 161<br />
149
4.1. GROUNDWATER AND PALEOCLIMATE 151<br />
Overview<br />
The research group ”Aquatic Systems” investigates freshwater systems, in particular lakes and groundwater,<br />
using direct measurements of physical parameters as wells as tracer and isotope methods. The<br />
fundamental goal of this research is to obtain a better understanding of the physical processes in these<br />
systems. Examples of studied processes are vertical turbulent mixing, currents, and tracer transport<br />
in stratified lakes, or recharge, flow, dispersion and contaminant transport in aquifers. A further important<br />
field is the use of aquifers as paleoclimate archives. The wider context of our research includes<br />
the issues of water resources protection and management, and assessment of past and present climate<br />
change.<br />
The group is divided in two subgroups: ”Groundwater and Paleoclimate” and ”Limnophysics”.<br />
4.1 Groundwater and Paleoclimate<br />
Names of group members<br />
Prof. Werner Aeschbach-Hertig, head of group<br />
Dr. Reinhold Bayer, administration<br />
Dr. Hany El-Gamal, PhD-student (completed June 2005)<br />
Dipl. Phys. Ronny Friedrich, PhD-student<br />
Dipl. Phys. Rainer Klement, diploma student (completed February 2005)<br />
Dipl. Phys. Tobias Kluge, PhD-student<br />
Dipl. Phys. Andreas Kreuzer, PhD-student<br />
Dr. Laszlo Palcsu, postdoc<br />
M. Sc. Sarah Rice, master student (completed December 2004)<br />
Dipl. Phys. Katja Träumner, diploma student (completed November 2005)<br />
Martin Wieser, diploma student<br />
Dipl. Ing. Gerhard Zimmek, technician<br />
Abstract The research group ”Groundwater and Paleoclimate” deals with applications of isotope<br />
and environmental tracers, in particular noble gases, in groundwater (and lakes in collaboration with<br />
the Limnophysics group). With theses methods, the group pursues two main aims: 1. To provide foundations<br />
for a sustainable management of groundwater resources, 2. Reconstruction of the paleoclimate<br />
since the last ice age.<br />
Background The overarching topic of our research may be summarized as ”isotope hydrology and<br />
climatology”, more specifically the use of isotopes and other environmental tracers (in particular noble<br />
gases) to study the functioning of groundwater systems and to extract paleoclimatic information from<br />
them.<br />
Isotope and tracer techniques have a long tradition in environmental physics. In addition to the widely<br />
used stable isotopes, dissolved noble gases in groundwater have been established as a reliable paleotemperature<br />
proxy. Furthermore, 3 H, He isotopes and other transient gas tracers are important tools<br />
in groundwater dating and recharge assessment [e.g. Kipfer et al. , 2002]. Groundwaters constitute<br />
by far the largest global reservoir of available fresh water. For the sustainable management of these<br />
resources, particularly in arid and semi-arid regions, it is essential to understand on what time-scales<br />
these resources are renewed and how they react to global climate change. Climate change and the<br />
limited availability of water resources are interrelated issues of increasing global importance. Isotopic<br />
studies of groundwaters yield information on both past climatic conditions such as temperature or<br />
aridity and on physical parameters such as residence time or recharge rate. Thus, issues of past climatic<br />
conditions and future availability of groundwater resources can be addressed in an integrated<br />
approach.<br />
Methods A central facility of the group is the newly built mass spectrometric system for the analysis<br />
of noble gases dissolved in water. It is currently becoming operational and will allow measurements<br />
of all stable noble gases from groundwaters for paleotemperature studies as well as the analysis of<br />
He isotopes for 3 H- 3 He dating. This facility is also being used to study new sample types such as<br />
stalagmites. It is complemented by an older system for He isotope analysis and a radiometric 3 H<br />
lab. Furthermore, the group conducts gas chromatographic SF6 analyses in cooperation with the<br />
limnophysics group, and uses the stable isotope and 14 C laboratories of the institute.
152 CHAPTER 4. AQUATIC SYSTEMS<br />
Main activities Projects of the group are related either to questions of water resources or paleoclimate,<br />
or both. Some projects are mainly applications of established methods, whereas others intend<br />
to develop new methods and approaches.<br />
The main goal of a project studying groundwater in the North China Plain is to obtain a noble gas<br />
paleotemperature record from a formerly little studied part of the world (see section 4.1.1). However,<br />
it also involves an investigation of the current recharge to the heavily exploited groundwater resources<br />
of this semi-arid area. Preliminary results of this study showing a clear paleoclimatic signal are being<br />
published in the framework of the IAEA isotope hydrology series [Kreuzer et al. , in press 2005].<br />
Similarly, a project on groundwater in Egypt focusses on the renewal rate of these resources that are<br />
used to sustain new agricultural developments outside the Nile Delta (see section 4.1.2). The study<br />
clearly shows that the regional groundwater originates from the Nile water, but the renewal is very<br />
slow. This project has been a cornerstone of the thesis of Hany El-Gamal [El-Gamal, 2005]. A paper<br />
is in preparation.<br />
Recharge rates and processes are also central to a project focussing on groundwater in the nearby<br />
Odenwald region (see section 4.1.3). However, the main problem in this case is not the overexploitation<br />
of the resource but the incomplete understanding of the connection between recharge in the mountains<br />
and water levels in the valley, where large water works are operating. Progress in this project has<br />
been and will again be reported at meetings of the hydrogeology section of the German Geological<br />
Society [Friedrich et al. , 2004].<br />
A new idea is to try and use microscopic water inclusions in speleothems (stalagmites and other<br />
carbonate sinters) to extract noble gas concentrations and temperatures (see section 4.1.4). After<br />
some preliminary studies in the form of diploma theses [Rice, 2004; Träumner, 2005], this issue is now<br />
studied in the framework of a DFG research unit in collaboration with the Radiometry Group of the<br />
”Heidelberger Akademie der Wissenschaften” (see section 5.1.8). The issue of the analysis of noble<br />
gases on very small samples and in new archives is also central to the project of our Marie Curie<br />
fellow Laszlo Palcsu (see section 4.1.5). However, the scope of this project is wider, trying to advance<br />
our general understanding of the ways in which noble gases in different archives can help us to gain<br />
paleoclimatic information.<br />
Another area of research that is currently developed is the study of interactions between groundwater<br />
and lakes, where a strong link between the two subgroups of the aquatic systems section becomes<br />
apparent (see section 4.1.6). A just completed diploma thesis investigated and validated the use of<br />
Radon as a tracer to study this interaction [Kluge, 2005].<br />
Funding The China project is funded by the DFG and its Chinese counterpart NSFC. The speleothem<br />
project is part of a DFG research unit (”Dated speleothems as archives of the paleo-environment”).<br />
The Odenwald project is a collaboration with the ”Hessisches Landesamt <strong>für</strong> Umwelt und Geologie”<br />
and the tracer analyses are funded by the State of Hessen. Hany El-Gamal was supported by a longterm<br />
mission fellowship of the Egyptian government. Laszlo Palcsu is supported by a Marie Curie<br />
EIF fellowship of the EU (project ”ADNOGAPALIN”).<br />
Cooperations In the above mentioned projects we cooperate with other groups of the institute,<br />
in particular with the carbon cycle group for stable isotope analyses on groundwaters and with the<br />
radiometry group for the preparation of 14 C samples for AMS analysis as well as on the study of<br />
fluid inclusions in speleothems. There exists also a cooperation with the ice and climate group on<br />
the analysis of He isotopes in ice. Cooperations outside the institute include local project partners<br />
in China, Egypt and Hessen. Furthermore, close links exist to the noble gas and AMS labs at ETH<br />
Zurich, where some of our samples are analysed, as well as to the isotope hydrology group at the<br />
University of Bern. Several links exist to scientists at the UFZ in Leipzig and Halle, and many new<br />
national and international cooperations will be forged in the framework of the upcoming DFG research<br />
unit.<br />
The institutions of our main cooperation partners are listed in the following (with shortcuts as used<br />
for author affiliations in the project reports):<br />
<strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese academy of geological sciences, Zhengding,<br />
China (IHEG),<br />
Geology Department, Faculty of Science, Minufiya University, Shebin El-Kom, Egypt (MINUF),<br />
Hessisches Landesamt <strong>für</strong> Umwelt und Geologie, Wiesbaden, Germany (HLUG),<br />
<strong>Institut</strong> <strong>für</strong> Isotopengeologie und Mineralische Rohstoffe, ETH Zürich, Switzerland (ETHZ).
4.1. GROUNDWATER AND PALEOCLIMATE 153<br />
Publications<br />
Peer reviewed<br />
1. Aeschbach-Hertig [2005a]<br />
2. Corcho Alvarado et al. [2004]<br />
3. Peeters et al. [2004]<br />
Other publications<br />
1. Kreuzer et al. [in press 2005]<br />
Doctoral theses<br />
1. El-Gamal [2005]<br />
Diploma theses<br />
1. Klement [2005]<br />
2. Kluge [2005]<br />
3. Rice [2004]<br />
4. Träumner [2005]<br />
Invited Talks<br />
1. Aeschbach-Hertig [2005b]<br />
2. Aeschbach-Hertig [2004c]<br />
3. Aeschbach-Hertig [2004a]<br />
4. Aeschbach-Hertig [2004d]<br />
5. Aeschbach-Hertig [2004b]
154 CHAPTER 4. AQUATIC SYSTEMS<br />
4.1.1 A tracer study of paleoclimate and groundwater recharge in the<br />
North China Plain<br />
Participating scientists Andreas M. Kreuzer, Christoph v. Rohden, Werner Aeschbach-Hertig,<br />
Chen Zongyu (IHEG), Rolf Kipfer (ETHZ)<br />
Abstract Noble gas temperatures (NGTs), stable isotope ratios and 14 C-ages from old groundwater<br />
in the North China Plain (NCP) are used to reconstruct a paleoclimate record. This is the first NGT<br />
record from East Asia. Preliminary results indicate a glacial cooling of about 4 ◦ C .<br />
NGT (°C)<br />
15.5<br />
15.0<br />
14.5<br />
14.0<br />
13.5<br />
13.0<br />
12.5<br />
12.0<br />
11.5<br />
11.0<br />
10.5<br />
10.0<br />
9.5<br />
9.0<br />
8.5<br />
8.0<br />
7.5<br />
2.6<br />
Noble Gas Temperatures of different wells<br />
Avg. 12.8°C<br />
7<br />
15.5<br />
13<br />
10<br />
12<br />
0 50 100 150 200 250 300 350 400<br />
12<br />
18<br />
11<br />
Avg. 9.0°C<br />
Approx. distance from well #1 (km)<br />
Numbers below points<br />
indicate age of<br />
specific well in ka.<br />
(Data from Zongyu, 2003)<br />
Figure 4.1: The figure shows the noble gas temperatures for the samples from 2004. There are warm temperatures<br />
of about 13 ◦ C in the infiltration area (on the left end), which correspond to the local annual air temperatures. The<br />
transition from the holocene to the last glacial occurs at about 100 km from well no.1 accompanied by a clear signal in<br />
temperature.<br />
Background Noble gas concentrations in water<br />
vary with temperature as the solubilities are temperature<br />
dependent. Measurements of noble gases<br />
in paleo-groundwater can therefore be used to calculate<br />
paleo-recharge temperatures [Kipfer et al.<br />
, 2002]. The importance of this method lies in<br />
reliable determination of glacial-interglacial temperature<br />
differences. The age of the groundwater<br />
in the NCP reaches from very young water to<br />
20 kyr old water in the deeper parts of the aquifers<br />
[Zongyu et al. , 2003].<br />
The goal of this study is to complement isotope<br />
data from this aquifer system with NGTs in order<br />
to quantify the climatic signal of the transition<br />
from the last glacial maximum (LGM) to the<br />
holocene.<br />
Methods and results Last years measurements<br />
showed a clear temperature signal at about<br />
100 km from well #1 as shown in the figure. This<br />
year a second sampling campaign was conducted<br />
in April to sample a short distance where the transition<br />
from the last glacial to the holocene was<br />
expected.<br />
A clear climatic signal is also present in the sta-<br />
ble isotope data corroborating previous results of<br />
Zongyu et al. [2003].<br />
For radiocarbon dating of groundwater a new<br />
extraction-line was developed and built. A total<br />
amount of about 200ml of water is needed, which<br />
is then acidified under vacuum to release the dissolved<br />
inorganic carbon from the water. The carbon<br />
dioxide is then trapped in a special volume<br />
in liquid nitrogen and is further treated and prepared<br />
for accelerator mass spectrometry.<br />
Funding This work is financially supported by<br />
the DFG (DFG grant AE 93/1) and by the<br />
National Natural Science Foundation of China<br />
(NSFC grant No. 40472125)<br />
Outlook/Future work The dating with 14 C<br />
will be done by the end of this year and also the<br />
measurement of the new noble gas samples will be<br />
finished this year. It is planned to present the results<br />
at international conferences and to prepare<br />
publications.<br />
Main publication Kreuzer et al. [in press<br />
2005]
4.1. GROUNDWATER AND PALEOCLIMATE 155<br />
4.1.2 A multi-tracer study of groundwater in reclamation areas south-west<br />
of the Nile Delta, Egypt<br />
Participating scientists Werner Aeschbach-Hertig, Hany El-Gamal, Kamal Dahab (MINUF), Rolf<br />
Kipfer (ETHZ)<br />
Abstract The origin and renewal rate of groundwater used for irrigation in Egypt was investigated<br />
using a variety of isotope and tracer techniques ( 2 H, 18 O, 14 C, SF6, 3 H- 3 He, noble gases). The main<br />
result is that the groundwater is recharged from the Nile river, albeit at a slow rate. Water younger<br />
than 50 yr is found only in the vicinity of surface water features in the Nile Delta.<br />
� � ���per mil�<br />
20<br />
0<br />
-20<br />
-40<br />
-60<br />
-80<br />
GMWL<br />
A<br />
Paleowater<br />
Pre-1969 Nile water<br />
Precipitation<br />
-12 -10 -8 -6 -4 -2 0 2 4<br />
�<br />
� 18<br />
O [per mil]<br />
Figure 4.2: Mixing trend lines in stable isotope data. Squares A, B, and C indicate endmembers, dots<br />
represent precipitation data, and triangles represent data from the wells. The latter lie on mixing lines<br />
(dashed) between regional paleogroundwater and Nile water from before and after the completion of<br />
the Aswan High Dam in 1969. These data clearly show that the groundwater is mainly recharged<br />
from the surface water, but at a slow rate, such that most of the water infiltrated before 1969.<br />
Background Egypt develops new agricultural<br />
areas outside the overpopulated Nile Delta and<br />
Valley. Such so-called reclamation areas depend<br />
almost exclusively on groundwater as water resource.<br />
For the long-term sustainability of these<br />
developments it is of central importance to understand<br />
the processes and rates of recharge of the<br />
groundwater resources.<br />
Methods and results The transient environmental<br />
tracers SF6 and 3 H- 3 He have been used<br />
to date the shallow groundwater, whereas dating<br />
of the old groundwater by 14 C is currently<br />
in progress. Noble gases and stable isotopes have<br />
been analysed to obtain information on the conditions<br />
during recharge. The results of the SF6<br />
and 3 H- 3 He dating show that only the wells that<br />
are located within a few kilometers of the artificial<br />
irrigation canals in the delta have young ages of<br />
between 1 and 25 years, indicating direct recharge<br />
by water derived from the river. At larger distance<br />
from the surface water, the age of the groundwater<br />
exceeds the detection limit of these methods<br />
B<br />
C<br />
Recent<br />
Nile<br />
water<br />
(30 - 50 yr). The 14 C-analyses will provide information<br />
on the age of the groundwater in the<br />
reclamation areas, some tens of kilometers apart<br />
from the surface water. The stable isotope data<br />
provide clear indications of the on origin and age<br />
of the groundwater, due to the change (enrichment<br />
by evaporation) of the isotopic signature of<br />
the Nile water resulting from the construction of<br />
the Aswan High Dam in 1969 (see figure). Only<br />
groundwater samples from the vicinity of the river<br />
lie close to the the recent Nile water composition.<br />
Most of the data lie close to the former Nile composition<br />
but not the local precipitation, indicating<br />
paleo-recharge derived from the river.<br />
Outlook/Future work The 14 C ages should<br />
enable us to further constrain the renewal rate<br />
of the groundwater and thus to contribute crucial<br />
information for a sustainable management of this<br />
resource. A publication is in preparation.<br />
Main publication El-Gamal [2005]
156 CHAPTER 4. AQUATIC SYSTEMS<br />
4.1.3 A multi tracer study to investigate the groundwater in the Odenwald<br />
region<br />
Participating scientists Ronny Friedrich, Werner Aeschbach-Hertig, Bernhard Leßmann (HLUG),<br />
Guido Vero (HLUG)<br />
Abstract Three sampling campaigns where performed during 2003, 2004 and 2005 in the Odenwald<br />
region. With this multi tracer study (noble gases, 3 H, δ 18 O, δ 2 H, SF6, CFCs) we want to investigate<br />
the age structure, mixing ratios and recharge areas of the groundwater in this region. First results<br />
show groundwater ages of a few years up to older than 40 years.<br />
Figure 4.3: Stable isotope data (δ 18 O, δ 2 H) of the campaign in 2003. Isotopic signatures of samples<br />
from the crystalline part (1), the sandstone part (2) and from the ”Hanau-Seeligenstädter-Senke” (4)<br />
are concentrated in separate groups, whereas samples from ”Hessisches Ried” (3) scatter over the<br />
whole range.<br />
Background The Odenwald region is one of<br />
the main recharge areas for groundwater of<br />
the surrounding areas (Hessisches Ried, Hanau-<br />
Seligenstädter Senke). These areas are very important<br />
for freshwater extraction. Therefore we<br />
want to investigate the groundwater in the Odenwald<br />
to study residence times and mixing ratios<br />
of the groundwater, define regions of groundwater<br />
recharge and understand the groundwater inflow<br />
from the Odenwald to the surrounding areas.<br />
Funding This work is done in cooperation with<br />
the ”Hessisches Landesamt <strong>für</strong> Umwelt und Geologie”<br />
Wiesbaden.<br />
Methods and results To study the groundwater<br />
we use different stable and radioactive gasand<br />
isotope tracers summarized as ”environmental<br />
tracers” such as 2 H, 18 O, 3 H, noble gases and<br />
SF6. Noble gases (He, Ne, Ar, Kr, Xe) can be<br />
used in principle to calculate recharge temperatures<br />
or the infiltration altitudes (above sea level)<br />
of recharge areas. Furthermore noble gases give<br />
important information to correct other gas tracers<br />
for so called ”excess air” that oversaturates<br />
gases in groundwater (see Kipfer et al. [2002] for<br />
a review of the methods). SF6 and 3 H- 3 He are<br />
used to date the groundwater.<br />
Comparing the results of these two independent<br />
dating methods we see that dating with SF6 is not<br />
possible in the crystalline region of the Odenwald.<br />
We assume that SF6 is influenced by a natural<br />
source in the subsurface. Data from the 3 H- 3 He<br />
method give robust groundwater ages in the range<br />
of some years to values higher than 40 years. By<br />
using the stable isotope data it is possible to distinguish<br />
between groundwater from different areas<br />
of the Odenwald. That will help us to define flow<br />
paths of the groundwater from the Odenwald to<br />
the surrounding areas. Additionally the isotopic<br />
signatures show that the groundwater was formed<br />
by ”annual” precipitation and not only in winteror<br />
summertime.<br />
Outlook/Future work Until today we have<br />
analyzed all samples from the campaign in 2003.<br />
Measuring the samples from 2004 and 2005 should<br />
give us information about seasonal changes in<br />
groundwater flow.<br />
Main publication Friedrich et al. [2004]
4.1. GROUNDWATER AND PALEOCLIMATE 157<br />
4.1.4 A new mass spectrometric system for measurement of noble gases<br />
and first applications to perform measurements of fluid inclusions in<br />
speleothems<br />
Participating scientists Katja Träumner, Werner Aeschbach-Hertig, Ronny Friedrich, Laszlo Palcsu<br />
and Gerhard Zimmek<br />
Abstract A new mass spectrometric system for purification and measurement of noble gases from<br />
groundwater and stalagmite samples was put into operation and tested for its behavior. The first<br />
application was a successful testing of a new extraction method for stalagmite samples.<br />
Desorption<br />
120%<br />
100%<br />
80%<br />
60%<br />
40%<br />
20%<br />
Desorption characteristic charcoal trap<br />
0%<br />
0 20 40 60 80 100 120 140<br />
-20%<br />
Temperature [K]<br />
Helium<br />
Neon<br />
Figure 4.4: The desorption of helium and neon from the charcoal trap as a function of temperature is<br />
shown. The decrease of the Helium-signal is a result of the gas consumption of the Quadrupol mass<br />
spectrometer which was used for measurement. On account of this characteristic curves a separation<br />
of helium and neon is possible, which is necessary for an exact measurement in the mass spectrometer.<br />
Background The characteristic temperature<br />
dependence of the solubility of noble gases and<br />
their property of being chemically and biologically<br />
inert, make noble gases an ideal proxy for<br />
paleotemperatures [Kipfer et al. , 2002]. By measuring<br />
noble gas concentrations of small fluid inclusions<br />
in stalagmite samples, we try to combine<br />
this thermometer with the possibility to precisely<br />
date the speleothem archive.<br />
Methods and results After first experiences<br />
with the extraction of fluid inclusions in the institute<br />
by a master thesis in the last year [Rice,<br />
2004], now the development of a new mass spectrometric<br />
system was the next step. This system<br />
consists of an inlet part to attach several kinds<br />
of samples, a system of cold traps for purification<br />
and separation (one trap cooled by dry ice<br />
for removal of water, one nude metal trap to condense<br />
all gases except helium and neon and a charcoal<br />
trap for separating helium and neon) and a<br />
commercial mass spectrometer, which is especially<br />
designed for measuring noble gases (see section<br />
4.1.5).<br />
During the diploma thesis the software to control<br />
all valves and to supervise the pressure in the line<br />
was written; software, tests and the parameters<br />
for temperature control of the traps were developed<br />
and several volumes (pipettes, standards, expansion<br />
and splitting volumes) of the system were<br />
determined. The new system was tested for the<br />
temporal behavior of the cool down processes and<br />
the desorption properties of the cold traps.<br />
The results of these tests were used to develop a<br />
new measurement routine. To continue the work<br />
with fluid inclusions in speleothems a new crushing<br />
method was tested. First measurements show<br />
that good results depend on the kind of samples.<br />
The composition of noble gases from stalagmites<br />
is a mixture of gases from air and from water.<br />
Outlook/Future work An automated measurement<br />
of samples will soon be possible. We<br />
will obtain a sample throughput of at least two to<br />
three samples a day. The work with the stalagmite<br />
samples will be continued by a Ph.D. thesis.<br />
Main publication Träumner [2005]
158 CHAPTER 4. AQUATIC SYSTEMS<br />
4.1.5 Advancing the use of noble gases as palaeoclimate indicators<br />
Participating scientists Laszlo Palcsu, Werner Aeschbach-Hertig<br />
Abstract A better understanding of gas partitioning during groundwater infiltration is a prerequisite<br />
for the reliable use of noble gases as palaeoclimate proxies. The primary goal of the present project<br />
is to obtain a detailed understanding of the physical mechanisms linking climate and soil parameters<br />
to the noble gas patterns imprinted during groundwater recharge.<br />
Figure 4.5: Results of stability tests of the new noble gas system, showing the deviation of different<br />
noble gas measurements from the average (X-axis: number of measurements, Y-axis: deviation in %).<br />
Background The analysis of dissolved noble<br />
gas concentrations in groundwater has proven to<br />
be a reliable method to determine quantitative<br />
palaeotemperatures [Kipfer et al. , 2002]. Noble<br />
gas studies in semi-arid regions have shown that<br />
in addition to recharge temperatures, the ”excess<br />
air” phenomenon may be useful as a proxy for<br />
the important climate parameter humidity [Beyerle<br />
et al. , 2003]. The present project aims at<br />
advancing and broadening the scope and applicability<br />
of noble gases in palaeoclimatology and hydrology,<br />
in particular at establishing the palaeoclimatic<br />
significance of excess air. This objective<br />
shall be achieved by careful analysis of noble gas,<br />
climate, and soil data from several semi-arid regions,<br />
complemented by experiments on the scale<br />
of laboratory soil columns and test-fields.<br />
Methods and results To interpret the dissolved<br />
noble gases in water as noble gas temperature<br />
and excess air component with low error it is<br />
necessary to achieve a very precise measurement<br />
of noble gases. Therefore, the accuracy of each<br />
noble gas measurement should be around 1 % or<br />
better. Noble gas measurents are performed by a<br />
new GV 5400 noble gas mass spectrometer which<br />
was purchased and installed in 2004. The GV<br />
5400 is an all-metal, statically operated, double focused,<br />
90 ◦ sector field mass spectrometer with 57<br />
cm extended geometry. So far, sensitivities and reproducibilities<br />
were determined. According to the<br />
acceptance specification, the achieved sensitivities<br />
are 7.52·10 −4 Amps/Torr for 40 Ar, and 3.47·10 −4<br />
Amps/Torr for 4 He, respectively. Stability and<br />
reproducibility measurements were performed on<br />
normal air samples. An individual sample could<br />
be measured within a few permil relative error,<br />
while the results of several measurements differed<br />
from each other by 1-2 %. The standard deviation<br />
of the 4 He and 3 He measurement were 0.6 %<br />
and 1.2 %, whilst the measured data were varying<br />
within the range of ±1 % and ±3 % around the<br />
average (see Figure). The standard deviation of<br />
the heavier noble gases were 0.3 % for neon, 0.5 %<br />
for argon, 1.0 % for krypton, and 0.9 % for xenon.<br />
These accuracies allow us to determine noble gas<br />
temperatures with an error of about 0.5 ◦ C and<br />
very precise excess air components.<br />
Outlook/Future work Laboratory and field<br />
experiments will be started in the next months<br />
in order to investigate the mechanisms which are<br />
responsible for the excess air formation. Furthermore,<br />
using the ability for precise noble gas measurements,<br />
the potential of fluid inclusions in stalagmites<br />
and other carbonate deposits from caves<br />
as palaeoclimate archives will also be investigated<br />
(see section 4.1.4).<br />
Funding This project is supported by the Marie<br />
Curie Intra-European Fellowships program (reference<br />
number: 009562).
4.1. GROUNDWATER AND PALEOCLIMATE 159<br />
4.1.6 Radon as tracer for lake - groundwater interaction<br />
Participating scientists Tobias Kluge, Werner Aeschbach-Hertig, Christoph v. Rohden, Johann<br />
Ilmberger<br />
Abstract Using the radioactive noble gas radon-222, the groundwater inflow into a lake is calculated<br />
from vertical profiles. With the aid of a newly developed sensitive technique, a clear groundwater signal<br />
has been detected in the lake.<br />
depth (m)<br />
0<br />
5<br />
10<br />
15<br />
epilimnion<br />
thermocline<br />
hypolimnion<br />
typ. error<br />
0 5 10 15 20 25 30<br />
Bq/m 3<br />
20.June<br />
4.July<br />
12.July<br />
19.July<br />
26.July<br />
Figure 4.6: Vertical radon profile in Lake Willersinnweiher, a lake with significant groundwater inflow<br />
in the upper part. This inflow produces a radon maximum in the thermocline. In the epilimnion,<br />
outgassing into the atmosphere reduces the radon activity.<br />
Background In this study we investigated the<br />
lake - groundwater interaction at a lake in the<br />
Rhine-Valley without surface inflow from rivers.<br />
One focus was to quantify the groundwater inflow.<br />
This inflow is used to calculate the replacement<br />
time of the lake water, which is of great ecological<br />
and hydrological significance.<br />
Rn-222 is a suitable tool to detect even a very<br />
small amount of groundwater inflow, because the<br />
activity difference between groundwater and lake<br />
- or surface water is very high. In the study area<br />
the activity concentration of radon in the groundwater<br />
is between 5 000 and 10 000 Bq/m 3 and in<br />
the lake water it is < 50 Bq/m 3 .<br />
Methods and results The measurements are<br />
done with an alpha-spectrometer (RAD7). This<br />
spectrometer detects the decay products of radon<br />
in the gas phase. To evaluate the radon activity<br />
of water, radon in sample water is brought into<br />
equilibrium with radon in a closed air loop. The<br />
activity in the air loop is only controlled by the<br />
amount of radon in water and its solubility. A new<br />
technique with large (12 l) water samples was de-<br />
veloped to reduce the detection limit.<br />
To explain the results, the sources of radon have<br />
to be known. The first possibility is the dissolved<br />
radium, that can decay directly into radon. Another<br />
source is the emanation from the lake sediments<br />
and the inflow of dissolved radon with the<br />
groundwater. Loss is caused by decay and outgassing<br />
into the atmosphere. The vertical profile<br />
can only be explained by a strong groundwater<br />
inflow in the epilimnion and a negligible inflow in<br />
the hypolimnion.<br />
By dividing the lake in different boxes according<br />
to the structure of stratification, a water balance<br />
was calculated. The replacement time for the epilimnion<br />
is (4.7 ± 1.2) years, for the hypolimnion<br />
ca. 21 years. In addition to previous studies,<br />
statements about depth-dependent groundwater<br />
inflow are possible. Due to the large number of<br />
constraints an exact calculation of the smallest<br />
and greatest possible groundwater inflow can be<br />
made.<br />
Main publication Kluge [2005]
160 CHAPTER 4. AQUATIC SYSTEMS<br />
References<br />
Aeschbach-Hertig, W. 2004a. Climate of the Past as a Basis for an Assessment of the Future. Invited<br />
talk, GSI-Kolloquium, Darmstadt, Germany.<br />
Aeschbach-Hertig, W. 2004b. Environmental Tracers in Groundwater Studies - Water Resources and<br />
Paleoclimate. Invited talk, <strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese Academy<br />
of Geological Sciences, Zhengding, China.<br />
Aeschbach-Hertig, W. 2004c. Excess Air in Groundwater: Problems and Opportunities. Invited<br />
keynote presentation, Annual Meeting of the Geological Society of America (GSA), Denver, USA.<br />
Aeschbach-Hertig, W. 2004d. Noble Gases and Excess Air in Groundwater: Review and Outlook.<br />
Invited talk, KUP-Seminar, University of Bern, Switzerland.<br />
Aeschbach-Hertig, W. 2005a. A comment on ”Helium sources in passive margin aquifers-new evidence<br />
for a significant mantle 3 He source in aquifers with unexpectedly low in situ 3 He/ 4 He production”<br />
by M. C. Castro [Earth Planet. Sci. Lett. 222 (2004) 897-913]. Earth Planet. Sci. Lett., in press.<br />
Aeschbach-Hertig, W. 2005b. Surface and Subsurface Waters. Invited lecture, WE-Heraeus summerschool<br />
”Physics of the Environment”, Bad Honnef, Germany.<br />
Beyerle, U., Rüedi, J., Leuenberger, M., Aeschbach-Hertig, W., Peeters, F., Kipfer, R., & Dodo, A.<br />
2003. Evidence for periods of wetter and cooler climate in the Sahel between 6 and 40 kyr BP<br />
derived from groundwater. Geophys. Res. Lett., 30(4), 1173, doi:10.1029/2002GL016310.<br />
Corcho Alvarado, J. A., Purtschert, R., Hinsby, K., Troldborg, L., Hofer, M., Kipfer, R., Aeschbach-<br />
Hertig, W., & Synal, H.-A. 2004. 36 Cl in modern groundwater dated by a multi tracer approach<br />
( 3 H/ 3 He, SF6, CFC-12 and 85 Kr): A case study in quaternary sand aquifers in the Odense Pilot<br />
River Basin, Denmark. Appl. Geochem., 20, 599–609.<br />
El-Gamal, H. 2005. Environmental tracers in groundwater as tools to study hydrological questions in<br />
arid regions. PhD thesis, University of Heidelberg.<br />
Friedrich, R., Aeschbach-Hertig, W., Vero, G., & Leßmann, B. 2004. Einsatz von Umwelttracern zur<br />
Erkundung des Grundwassers der Odenwald-Region. Page 35 of: Schiedek, T., Kaufmann-Knoke,<br />
R., & Ebhardt, G. (eds), Hydrogeologie regionaler Aquifersysteme (FH-DGG-Tagung). Schriftenreihe<br />
der Deutschen Geologischen Gesellschaft, vol. 32. Darmstadt: Deutsche Geologische Gesellschaft.<br />
Kipfer, R., Aeschbach-Hertig, W., Peeters, F., & Stute, M. 2002. Noble gases in lakes and ground waters.<br />
Pages 615–700 of: Porcelli, D., Ballentine, C., & Wieler, R. (eds), Noble gases in geochemistry<br />
and cosmochemistry. Rev. Mineral. Geochem., vol. 47. Washington, DC: Mineralogical Society of<br />
America, Geochemical Society.<br />
Klement, R. 2005. Optimierung von SF6-Grundwasserprobenahme-Methoden. Diplomarbeit, <strong>Universität</strong><br />
Heidelberg.<br />
Kluge, T. 2005. Radon als Tracer in aquatischen Systemen. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />
Kreuzer, A. M., Zongyu, C., Kipfer, R., & Aeschbach-Hertig, W. in press 2005. Environmental Tracers<br />
in Groundwater of the North China Plain. In: IAEA (ed), International Conference on Isotopes in<br />
Environmental Studies - Aquatic Forum 2004. Monte-Carlo, Monaco: IAEA.<br />
Peeters, F., Beyerle, U., Aeschbach-Hertig, W., Brennwald, M. S., & Kipfer, R. 2004. Response to<br />
the comment by G. Favreau, A. Guero, and J. Seidel on Improving noble gas based paleoclimate<br />
reconstruction and groundwater dating using 20 Ne/ 22 Ne ratios (2003) Geochim. Cosmochim. Acta,<br />
67, 587 - 600. Geochim. Cosmochim. Acta, 68(6), 1437–1438.<br />
Rice, S. 2004. The development of a method for the extraction and measurement of noble gases from<br />
fluid inclusions in samples of calcium carbonate. Master thesis, University of Heidelberg.<br />
Träumner, K. 2005. Inbetriebnahme, Tests und erste Anwendung einer neuen Aufbereitungslinie zur<br />
massenspektrometrischen Messung von Edelgasen aus Grundwasser - und Stalagmitproben. Diplomarbeit,<br />
<strong>Universität</strong> Heidelberg.<br />
Zongyu, C., Jixiang, Q., Jianming, X., Jiaming, X., Hao, Y., & Yunju, N. 2003. Paleoclimatic<br />
interpretation of the past 30 ka from isotopic studies of the deep confined aquifer of the North<br />
China plain. Appl. Geochem., 18, 997–1009.
4.2. LAKE RESEARCH (LIMNOPHYSICS) 161<br />
4.2 Lake Research (Limnophysics)<br />
Names of group members<br />
Dr. Johann Ilmberger, head of group<br />
Dr. Christoph von Rohden, postdoc<br />
Dipl. Phys. Karl Wunderle, diploma student (completed April 2005)<br />
Abstract Water quality of lake waters is, among other factors, affected by mixing and transport<br />
processes in the interior, as well as by the exchange with the ambient ground water. These internal<br />
processes and the ground water exchange are the main subjects of our investigations.<br />
Figure 4.7: Schematic diagramm of transport processes in lakes.<br />
Background Transport processes in lakes are important for the lake water quality. Especially<br />
mining lakes tend to have a poor quality because of the disturbed landscape due to the mining<br />
activities.<br />
Methods The investigations are based on tracers and direct measurements. Mainly we are using<br />
the tracer SF6, but also stable isotopes and now upcoming Radon (see section 4.1.6).<br />
The background level of SF6 can be used to study the interaction of ground water with lake water.<br />
This is based on the equilibration of rain and surface waters with atmospheric gases and the increase<br />
of the atmospheric level of the man made SF6 during the last decades. Therefore ground water -as it<br />
normally infiltrated a few decades ago- has a low SF6 content, while the lake water SF6 concentration<br />
is, at least during overturn, close to the (higher) atmospheric concentration. This difference of the<br />
signals can be used to study ground water - lake water exchange. We will try to apply this method<br />
to the mining lake RL117.<br />
We use SF6 spike experiments to investigate vertical mixing and ground water exchange. There we<br />
inject a small amount SF6 (few hundred mg) into the (hypolimnic) water body and trace the vertical<br />
spread and the balance by profile measurements (see section 4.2.1). We applied this method to Lake<br />
Constance, Lake Hufeisensee, Lake Merseburg Ost 1a and 1b. We will apply it at Lake Waldsee.<br />
Direct measurements include the profile measurements of temperature and electrical conductivity with<br />
a CTD-probe at a vertical resolution of ∼2cm (see section 4.2.2), continuous temperature measurements<br />
at different water depths using logging temperature probes and measurements of water currents<br />
with an Acoustic Doppler Current Profiler (see section 4.2.3).<br />
Lakes in investigation: Mining lake Merseburg Ost 1a, Mining lake Merseburg Ost 1b, Lake Willersinnweiher,<br />
Lake Waldsee, Lake RL117.<br />
The tracer methods, especially the spike experiments, are very well suited for the transport investigations.<br />
Projects and funding<br />
Our work at Willersinnweiher, where we did current measurements, continuous temperature and CTD-
162 CHAPTER 4. AQUATIC SYSTEMS<br />
profile measurements, was funded by the SFB 359: ”Reaktive Strömungen, Diffusion und Transport”,<br />
Teilprojekt D2 (see section 4.2.3).<br />
The SF6 spike measurements at the mining lakes Merseburg 1a and 1b were funded by the Centre<br />
of Environmental Research Leipzig-Halle and performed in close collaboration with B. Böhrer (UFZ-<br />
Leipzig/Halle, Section Gewässerforschung, Magdeburg).<br />
In the future we will intensify the research using radon as limnic tracer, as the work of Tobias Kluge<br />
has shown its potential as tracer for the groundwater exchange of gravel lakes (see section 4.1.6).<br />
In a joined project, funded by the German Research Foundation, we will investigate vertical transport<br />
and groundwater exchange at two mining lakes (Lake Waldsee and Lake RL117).<br />
Collaborations<br />
UFZ Leipzig-Halle, Dept. of Lake Research Magdeburg and Dept. of Isotope Hydrology<br />
BTU Cottbus, Lehrstuhl Gewässerschutz<br />
<strong>Institut</strong>e for Biodiversity and Ecosystem Dynamics / Aquatic Microbiology, University of Amsterdam<br />
Limnologisches <strong>Institut</strong>, <strong>Universität</strong> Konstanz<br />
<strong>Institut</strong> <strong>für</strong> Seenforschung, Langenargen, LfU<br />
Publications<br />
Other publications<br />
1. Ilmberger & von Rohden [2005]<br />
2. Ilmberger et al. [2005]<br />
3. von Rohden et al. [2005]<br />
Diploma theses<br />
1. Wunderle [2005]
4.2. LAKE RESEARCH (LIMNOPHYSICS) 163<br />
4.2.1 Sulfurhexaflourid (SF6) as tracer for transport and mixing processes<br />
in mining lakes<br />
Participating scientists Johann Ilmberger, Christoph von Rohden<br />
Abstract To study transport and mixing processes in the monimolimnion of mining lakes we released<br />
a small quantity of the trace gas in the monimolimnion of two mining lakes. The vertical spread and<br />
the mass balance were used to gain information about the vertical diffusion and the ground water<br />
exchange.<br />
Figure 4.8: SF6 - quantity in the monimolimnion (the water mass below 56.55 m asl) of the mining<br />
lake Merseburg-Ost 1a versus time. The experiment was started in 1997 and today we still can balance<br />
the trace gas by measuring a vertical profile. The SF6 decreases at a rate of 0.12 yr −1 , which is mainly<br />
due to ground water exchange.<br />
Background Because of their geometry, which<br />
is the result of the mining activities, mining lakes<br />
tend to have a water body which is not involved<br />
in the yearly cycle of mixing, a monimolimnion.<br />
These monimolimnia usually have a very poor water<br />
quality and might be enriched by heavy metals<br />
and other toxicities. Therefore one would like to<br />
know how persistent they are, or how high the<br />
risk is to contaminate the lake water and/or the<br />
ambient ground water.<br />
Funding This work was funded by the Centre<br />
of Environmental Research Leipzig-Halle.<br />
Methods and results The man made and industrially<br />
used gas sulfur hexaflouride (SF6) is<br />
very well suited to trace transport processes in<br />
strongly stratified waters, because it is chemically<br />
inert much as a noble gas. So far no other than<br />
the (very slow) degradation in the higher atmosphere<br />
is reported. And, because of its high electronegativity,<br />
it can be detectet very sensitively<br />
by an ECD detector after separation by gas chromatography.<br />
Our detection limit is ∼ 10 −17 Mol<br />
(10 aMol). For comparison: water, in equilibrium<br />
with the modern atmosphere ( 6 pptv), has a concentration<br />
of 2 fMol/l (= 2 · 10 −15 Mol/l). In<br />
1997 we started a tracer experiment in the monimolimnion<br />
of the open pit mining lake Merseburg-<br />
Ost 1a [von Rohden & Ilmberger, 2001]. To investigate<br />
the transport processes we injected 0.1<br />
mMol (15 mg) of SF6 into the interior of the monimolimnion.<br />
The monimolimnion has a salinity of<br />
about 40�, is about 2 m high and within a distance<br />
of 20 cm it changes to the hypolimnic salinity<br />
of 4�. The figure shows the total SF6 content<br />
of the monimolimnion calculated from profiles<br />
sampled at a vertical distance of 20 cm. The<br />
SF6 content of the monimolimnion changed from<br />
the initial 100 Mol down to 45 Mol at the beginning<br />
of 2004. A logarithmic fit to the values<br />
leads to a loss rate of 0.12 yr −1 . So 12% of the<br />
content leaves the monimolimnion per year. As<br />
we find only very little SF6 escaping into the hypolimnion<br />
and even a decrease in concentration<br />
directly above the lake floor, the loss is mainly<br />
due to ground water exchange.<br />
Outlook/Future work Though we do not<br />
have further funding for this research we will try<br />
to continue these very interesting investigations.<br />
Main publication Ilmberger & von Rohden<br />
[2005]
164 CHAPTER 4. AQUATIC SYSTEMS<br />
4.2.2 Vertical transport in stratified lakes<br />
Participating scientists Christoph von Rohden<br />
Abstract Based on measurements of the environmental tracers temperature and sulfur hexafluoride,<br />
effective vertical exchange coefficients Kz in density stratified lakes were calculated using budget<br />
methods. The heat transport in summer stratification can be limited to conduction. Molecular<br />
diffusion was found to be the only exchange process in lakes with strong chemical stratification.<br />
height [m asl]<br />
88<br />
86<br />
84<br />
s u r f a c e<br />
82<br />
80<br />
78<br />
76<br />
74<br />
72<br />
70<br />
68<br />
5 10 15 20 25 10 -5<br />
10 -4<br />
10 -3<br />
2004<br />
t h e r m o c l i n e<br />
05.11.<br />
22.10.<br />
24.09.<br />
14.09.<br />
03.09.<br />
25.08.<br />
10.08.<br />
30.07.<br />
16.07.<br />
06.07.<br />
25.06.<br />
07.06.<br />
08.06.<br />
27.05.<br />
a)<br />
17.05.<br />
07.05.<br />
b o t t o m<br />
b)<br />
temperature [°C]<br />
stratification stability N 2 [s -1 stability N<br />
]<br />
2<br />
10 -2<br />
heat conduction<br />
10 -7<br />
10 -6<br />
c)<br />
10 -5<br />
diffusion coefficient K z [m 2 /s]<br />
Figure 4.9: a) Temperature profiles during the summer stratification, b) mean stability (acting against<br />
vertical exchange) due to temperature gradients, c) calculated parameter Kz (average) representing<br />
the intensity of exchange.<br />
Background In density stratified lakes, the extent<br />
of the redistribution of geochemically relevant<br />
species caused by the wind driven internal<br />
dynamics is of interest. On time scales of weeks<br />
to months, the vertical transport during stratification<br />
is a result of small scale turbulent motions.<br />
It can be quantified by calculating Kz as effective<br />
vertical exchange coefficients.<br />
Funding The work was supported by the SFB<br />
359 “Reaktive Strömungen, Diffusion und Transport”,<br />
University of Heidelberg and the Centre<br />
for Environmental Research (UFZ) Leipzig-Halle,<br />
Department of Lake Research, Magdeburg.<br />
Methods and results The investigations are<br />
based on high resolution profiles of temperature<br />
and conductivity (taken with an automatic probe)<br />
and gas chromatographic measurements of the artificial<br />
tracer sulfur hexafluoride. Assuming horizontal<br />
homogeneity, which is reasonable in small<br />
lakes, the experimental setup was one dimensional<br />
taking into account the morphology of the lakes.<br />
The transport intensity was quantitatively estimated<br />
by budgeting of these tracers. The flux<br />
gradient method connects changes in the tracer<br />
concentrations in distinct lake layers (budgeting)<br />
to the vertical fluxes. Turbulent diffusion coefficients<br />
are calculated from the fluxes using Fick’s<br />
law.<br />
The results show that the vertical exchange is suppressed<br />
by the stratification. In a small quarry<br />
pond, the heat fluxes are reduced to the conduction<br />
level (∼ 10 −7 m 2 /s) during summer in the<br />
stratified region (high temperature gradients, see<br />
figure). This gives room for even lower transport<br />
rates of solutes.<br />
In a mining lake with a strong permanent salt<br />
stratification we found the molecular diffusion<br />
(∼ 10 −9 m 2 /s) to be the dominant transport process<br />
within the stratified region.<br />
Outlook/Future work A new project will<br />
start in 2006 to investigate the interaction of<br />
groundwater connection, vertical transport and<br />
stratification in a mining lake with a permanent<br />
density gradient maintained by hydrochemical<br />
processes.<br />
Main publication von Rohden [2002]
4.2. LAKE RESEARCH (LIMNOPHYSICS) 165<br />
4.2.3 Investigation of Water Currents in Lake Willersinnweiher using Acoustic<br />
Doppler Current Profiler<br />
Participating scientists Karl Wunderle, Christoph von Rohden, Johann Ilmberger<br />
Abstract In a small stratified lake currents were measured with a bottom mounted 1200 kHz Acoustic<br />
Doppler Current Profiler, ADCP. Currents are measured with an accuracy of ∼1 mm/s and a<br />
vertical resolution of 20-40 cm. Typical current speeds in Lake Willersinnweiher are very low in the<br />
range of several mm/s (especially in the hypolimnion), occasionally reaching a few cm/s during wind<br />
incidents.<br />
Figure 4.10: Short Time Fourier Transformation (STFT) of the east - west component of water<br />
currents at a depth of 10 m. The time series, used for these calculations, startet at the 6th July 2004.<br />
The window for the individual spectrum is 21 h (256 5-minute values) at an overlap of 80%. The color<br />
indicates the spectral intensity of the signal on a logarithmic scale from high (red) to low (blue).<br />
Background Transport and mixing in the interior<br />
of lakes is due to wind driven internal motion.<br />
To investigate the internal dynamics, fluctuations<br />
of water temperature as indirect indicator of motion<br />
and direct water current measurements can<br />
be used.<br />
Funding The work was supported by the SFB<br />
359 “Reaktive Strömungen, Diffusion und Transport”,<br />
University of Heidelberg.<br />
Methods and results Current measurements<br />
were performed with the ADCP (RD Instruments)<br />
mounted at the bottom of the lake. 800 pings were<br />
averaged and recorded every 5 minutes. To keep<br />
the inclination angles below 2 ◦ , it was mounted<br />
in a cardanic suspension. The ADCP was powered<br />
through a cable from ashore, using low cost<br />
rechargeable 60 V battery pack. The cable was<br />
also used to check the operation and <strong>download</strong> the<br />
stored data once a week. In addition to the current<br />
measurements weekly vertical profiles of temperature<br />
and electrical conductivity were taken<br />
and temperature data were continuosly recorded<br />
at several depths at different sites in the lake.<br />
Long term Fourier transform does not show significant<br />
peaks in the spectra i.e. there are no distinct<br />
eigenfrequencies on a longer timescale. In order to<br />
resolve the dynamics of the watercurrents Short<br />
Time Fourier Transform (STFT) was used. Figure<br />
1 shows an example of a STFT calculation<br />
of the east-west component of the watercurrent<br />
from 6th to 13th July 2004 using a window of 21h<br />
(256 5min values) and an overlap of 80The STFT<br />
computations reveal the transient character of the<br />
currents with peaks at ∼3h.<br />
Main publication Wunderle [2005]
166 CHAPTER 4. AQUATIC SYSTEMS<br />
References<br />
Ilmberger, J., & von Rohden, C. 2005. Abschlußbericht zum Forschungsvorhaben: ”SF6 als Tracer<br />
<strong>für</strong> Transport- und Mischungsprozesse in Tagebaurestseen.<br />
Ilmberger, J., von Rohden, C., & Wunderle, K. 2005. Observation of Multilayer Structures in a Small<br />
Lake. In: In A. Folkard and I. Jones,editors, 9th workshop on physical processes in natural waters.<br />
von Rohden, C. 2002. Tracerstudie zur Quantifizierung des Vertikaltransports in meromiktischen Seen.<br />
PhD thesis, University of Heidelberg.<br />
von Rohden, C., & Ilmberger, J. 2001. Tracer experiment with sulfur hexafluoride to quantify the<br />
vertical transport in a meromictic pit lake. aquatic sciences, 63, 417–431.<br />
von Rohden, C., Hauser, A., Wunderle, K., Ilmberger, J., Wittum, G., & Roth, K. 2005. Lake<br />
dynamics: observation and high-resolution numerical simulation. In Rannacher editor. Springer.<br />
Wunderle, K. 2005. Untersuchungen der Strömungen im Willersinnweiher mit einem akustischen<br />
Strömungsmessgerät. Diplomarbeit, University of Heidelberg.
Small-Scale Air-Sea Interaction<br />
5.1 Small-Scale Air-Sea Interaction . . . . . . . . . . . . . . . . . . . . . . . . 169<br />
167
5.1. SMALL-SCALE AIR-SEA INTERACTION 169<br />
5.1 Small-Scale Air-Sea Interaction<br />
Names of group members<br />
Prof. Dr. B. Jähne, head of group<br />
Dr. G. Balschbach, staff<br />
Dipl.Phys. K. Degreif, PhD student<br />
Dipl.Chem. A. Falkenroth, PhD student<br />
Dr. C. S. Garbe, Postdoc<br />
Dipl.Phys. M. Jehle, PhD student<br />
Dipl.Phys. M. Klar, PhD student<br />
Dipl.Phys. C. Popp, PhD student<br />
R. Rocholz, diploma student<br />
Dipl.Phys. M. Schmidt, PhD student<br />
Dr. U. Schimpf, Postdoc<br />
T. Schwarz, diploma student<br />
Abstract Research in small-scale air-sea interaction at the IUP concentrates on air-sea gas exchange<br />
and the dynamics of wind waves. The basic mechanisms are studied in laboratory experiments in a<br />
unique annular wind-wave facility (The Heidelberg Aeolotron) and field experiments using imaging<br />
techniques for quantitative visualization of the water surface structure (wind waves), the flow field,<br />
concentration fields by laser-induced fluorescence, and the water surface temperature by passive and<br />
active thermography.<br />
Scientific Objectives The basic scientific objective is a better physical understanding of air-sea<br />
gas transfer, the dynamics of short wind waves, and the micro turbulence at the ocean surface.<br />
Currently the following topics are investigated:<br />
1. The influence of the diffusion coefficient (or the Schmidt number Sc) on the transfer velocity<br />
of gases. Together with the transfer velocity itself, this is a sensitive measure to distinguish<br />
different models.<br />
2. The influence of wind waves on air-sea gas transfer by enhancing the turbulence near the water<br />
surface.<br />
3. The influence of chemical reactivity on gas transfer. Here the hydration reaction of CO2 is<br />
currently of most interest, because today only some model computations but no detailed measurements<br />
are available.<br />
4. Analysis of the spatial and temporal structure of the turbulence in the water-sided viscous<br />
boundary layer as the driving force for air-water gas exchange.<br />
Overarching topic is the study of small-scale air-sea interaction, especially the mechanisms of<br />
air-sea gas exchange and the dynamics of wind waves.<br />
Background Despite intensive research, knowledge about air-sea interaction processes has not been<br />
significantly improved during the last decade. Many basic questions are still open. The relation of<br />
the air-sea gas exchange rate with wind speed is discussed controversial. Both field and laboratory<br />
experiments show large deviations up to a factor of two from a simple relation between the wind<br />
speed and the gas transfer velocity [Jähne & Haußecker, 1998; Jähne, 2001]. It is obvious that<br />
other parameters, especially wave-induced near-surface turbulence and surface active films are of<br />
importance, but detailed modeling of these processes is still lacking. Therefore, despite their known<br />
significant limitations, semi-empirical relations between the wind speed and the gas transfer velocity,<br />
as established by Liss & Merlivat [1986] or Wanninkhof [1992], are still the state of the art.<br />
Another uncertainty in the estimation of transfer velocity is the dependence on the Schmidt number<br />
Sc. It is common to assume that the transfer velocity k is proportional to Sc −1/2 . However, for quite<br />
some time it has been known [Jähne, 1980] that the exponent is about 2/3 for a smooth water surface<br />
at low wind speeds and gradually decreases to 1/2 for a rough and wavy water surface. The exact<br />
shape of this transition, and especially how it is influenced by surface films in coastal zones and on<br />
which parameters it depends, is not known. This lack of knowledge causes a considerable uncertainty<br />
in estimating the transfer velocity. A change of the exponent from 2/3 to 1/2 without a change of<br />
other parameters causes an increase of the transfer velocity by about a factor of two.
170 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
Recently, the intermittent nature of the gas exchange process has come into the focus of research.<br />
Of particular interest is the microscale wave breaking, a process that causes enhanced near-surface<br />
turbulence. It is known that microscale wave breaking enhances gas transfer. Zappa et al. [2001]<br />
found, e. g., a good correlation between the measured transfer velocity and the fraction of the water<br />
surface at which surface renewal occurred by microscale wave breaking. Details of the mechanisms<br />
that allow a physically-based parameterization are, however, not yet known. The intermittency of the<br />
gas transfer is of much importance when integrating gas transfer rates form short time and spatial<br />
scales as determined by active thermography to larger scales. Because the relation between wind<br />
speed and the transfer velocity and possible other parameters is certainly nonlinear, not only the<br />
mean values but also the variations must be known for a proper integration.<br />
A particularly difficult and interdisciplinary problem is the influence of organic films on air-sea gas<br />
transfer [Frew, 1997]. Surfactants attenuate short wind waves and thus changes the hydrodynamic<br />
boundary conditions at the water surface. In effect, the gas transfer rate is significantly reduced.<br />
Interestingly this complex process can be modeled by simply relating the gas transfer rate to the<br />
mean square wave slope [Frew, 1997; Bock et al. , 1999; Frew et al. , 2004]. This close correlation<br />
between the mean square slope and the gas transfer rate was already pointed out by Jähne et al.<br />
[1987] long before systematic studies of the influence of surface films on gas transfer were performed.<br />
However, a more detailed modeling is still lacking.<br />
Main methods By using novel visualization techniques and image sequence processing techniques,<br />
the complex small-scale air-sea interaction processes can be tackled experimentally for the first time<br />
in both laboratory and field experiments. Equally important are spectroscopic techniques that allow<br />
simultaneous gas exchange measurements with many tracer. The techniques are briefly described in<br />
the following.<br />
UV-spectroscopy for volatile species dissolved in water UV-spectroscopy in contrast to IRspectroscopy<br />
offers the significant advantage that it is not required to degas water samples in<br />
order to measure gases and volatile species dissolved in water, because water is transparent in<br />
the required wavelength range from 200–300 nm. Thus this technique can be used to measure<br />
concentrations both the water and air space. The technique adds a number of volatile species for<br />
gas exchange measurements, especially species containing aromatic rings, such as fluorobenzenes,<br />
thiophenes, and pyrenes. For further details see section 5.1.3.<br />
Wave slope and height imaging A detailed investigation of the dynamics of short wind waves<br />
required simultaneous imaging of the wave height and slope. This is because the energy of<br />
gravity waves is contained in the wave height whereas the energy of the capillary waves is<br />
proportional to the wave slope. Therefore a novel instrumentation was developed that is capable<br />
to measure the wave slope and height simultaneously by making use of the fact that light at<br />
different wavelengths in the near infrared shows significant differences in absorption. In this way<br />
the imaging wave slope gauge could be extended for simultaneous wave height measurements<br />
(section 5.1.7 and Jähne et al. [2005c]).<br />
Active thermography Using heat as a proxy tracer for gases has two significant advantages. Firstly,<br />
the concentration of the tracer at the water surface can directly be measured with infrared cameras.<br />
Secondly, the heat flux can be controlled by applying infrared radiation onto the water<br />
surface. Periodically varying infrared radiation was applied to the water surface to create a corresponding<br />
variation in the surface temperature of the water. For slow variations of the infrared<br />
radiation - slower than the time constant for the exchange process - the transfer velocity can be<br />
measured directly by dividing the known flux density by the measured temperature variation.<br />
If the heat flux is switched off, the temperature increase will decay with the characteristic time<br />
constant t⋆ (surface renewal time) for the transport process across the aqueous heat boundary<br />
layer. From this time constant the transfer velocity k can be computed directly using the relation<br />
t⋆ = D/k 2 , where D is the diffusion coefficient for heat [Jähne et al. , 1989]. By measuring<br />
the phase shift and amplitude damping of the thermal boundary to periodically changing IR<br />
radiation, it is also possible to distinguish between different models for the exchange process<br />
and to investigate the intermittency of the process. Because the infrared image sequences contain<br />
significant contrast, the surface flow field including its vorticity and local convergence and<br />
divergence zones can also be computed from image sequences [Garbe et al. , 2003]. Moreover,<br />
the spatial structure of the micro-turbulence at the water surface can be studied [Schimpf et al.<br />
, 2004].
5.1. SMALL-SCALE AIR-SEA INTERACTION 171<br />
Fluorescence imaging of gas tracer concentration fields The fluorescence spectrum of dissolved<br />
dyes generally shows a bandwidth between 30 and 100 nm. A second dye is used to attenuate<br />
the emitted fluorescent light in this wavelength range differently for different wavelengths. With<br />
this double-dye technique, the shape of the observed fluorescence spectrum depends on the path<br />
length the light travels through the water before it is measured. Because the fluorescence is<br />
excited from the air space, the path length directly corresponds to the distance from the water<br />
surface.<br />
For a given wavelength, the fluorescent light received is then integrated over a characteristic<br />
depth ˆz = α −1 (λ), where α(λ) is the wavelength-dependent absorption coefficient of the absorbing<br />
dye solution. If α(λ) is known, the depth-dependent concentration can be computed from<br />
the measured spectra as a linear inverse problem.<br />
This technique is investigated for the quenching of the fluorescence of a organic rutheniumcomplex<br />
by oxygen (section 5.1.6) and pH-dependent fluorescent dyes (section 5.1.8).<br />
3-D flow measurements close to and at the water surface The aqueous viscous boundary layer<br />
at a wind-driven water surface has a thickness of at most a millimeter. Therefore almost no flow<br />
measurements are available from this layer at a free water surface. We try to tackle this difficult<br />
experimental problem with two techniques. First, thermal image sequences from the water surface<br />
contain enough structures to computed 2-D flow fields (section 5.1.2). Secondly, a modified<br />
particle tracking technique is used for depth-resolved flow measurements. Again an absorbing<br />
dye is used to code the depth of the tracked particles and to measure the velocity component<br />
perpendicular to the water surface from the brightness change of the particle (section 5.1.5).<br />
Main activities Our current main activities include<br />
1. the development of a novel optic technique for simultaneous imaging of the height and slope of<br />
short wind waves (section 5.1.7),<br />
2. the development of depth-resolving imaging technique to measure concentration fields of gases<br />
close to the water surface by using a double dye laser induced fluorescence techniques (sections<br />
5.1.6 and 5.1.8),<br />
3. detailed studies of the Schmidt number dependency of air-water gas transfer (section 5.1.3),<br />
4. investigations of the air-sea gas exchange by active thermography (section 5.1.1),<br />
5. analysis of flow fields by passive and active thermography thermography (section 5.1.2),<br />
6. 3-D flow measurements within the aqueous viscous boundary layer (section 5.1.5), and<br />
7. 3-D flow measurements within porous gravel layers (section 5.1.4).<br />
Funding<br />
1. DFG-Schwerpunktprogramm 1114 “Mathematische Methoden der Zeitreihenanalyse und digitalen<br />
Bildverarbeitung”<br />
2. DFG-Schwerpunktprogramm 1147 “Bildgebende Strömungsmesstechnik”<br />
3. Graduiertenkolleg 1114 “Optische Messtechniken <strong>für</strong> die Charakterisierung von Transportprozessen<br />
an Grenzflächen” (TU Darmstadt and U Heidelberg)<br />
4. DFG Ja395/10: ”Mechanismen des Gasaustausches zwischen Atmosphäre und Ozean: Laborversuche<br />
und Modellierung”<br />
5. DFG Ja395/13: ”Impact of Wind, Rain, and Surface Slicks on Air-Sea CO2 Transfer Velocity -<br />
Tank Experiments”<br />
6. Bundesanstalt <strong>für</strong> Wasserbau
172 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
Cooperation<br />
1. Prof. T. Aach, <strong>Institut</strong> <strong>für</strong> Signalverarbeitung und Prozessrechentechnik, <strong>Universität</strong> Lübeck<br />
2. Prof. Dr. Klaus Affeld, Dr. Ulrich Kertzscher, Labor <strong>für</strong> Biofluidmechanik, <strong>Universität</strong>sklinikum<br />
Charite Berlin, Humboldt <strong>Universität</strong> Berlin<br />
3. Dr. Erhardt Barth, <strong>Institut</strong> <strong>für</strong> Neuro- und Bioinformatik, <strong>Universität</strong> Lübeck<br />
4. Dr. Volker Beushausen, Laser-Laboratorium Göttingen e.V.<br />
5. Dr. Nelson M. Frew, Marine Chemistry and Geochemistry, Woods Hole Oceanographic <strong>Institut</strong>ion<br />
(WHOI), USA<br />
6. Prof. Dr. Tetsu Hara, Graduate School of Oceanography (GSO), University of Rhode Island,<br />
USA<br />
7. Dr. V. Kudryavtsev, Marine Hydrophysical <strong>Institut</strong>e, Sebastopol, Ukraine<br />
8. Dr. V. K. Makin, Royal Netherlands Meteorological <strong>Institut</strong>e, de Bilt, Niederlande<br />
9. Prof. R. Mester, Digitale Bildverarbeitung, <strong>Institut</strong> <strong>für</strong> Angewandte Physik, <strong>Universität</strong> Frankfurt<br />
10. Dr. Bernd Schneider, Dr. Joachim Kuss, <strong>Institut</strong> <strong>für</strong> Ostseeforschung, Warnemünde<br />
11. Prof. Dr. Detlef Stammer, Dr. Martin Gade, <strong>Institut</strong> <strong>für</strong> Meeresforschung, <strong>Universität</strong> Hamburg<br />
12. Prof. Christoph Schnörr, Bildverarbeitung, Mustererkennung & Computergrafik <strong>Universität</strong><br />
Mannheim<br />
13. Prof. Jürgen Wolfrum, PD Dr. Volker Ebert, Physikalische Chemie, <strong>Universität</strong> Heidelberg<br />
Future Work Future work in the coming year will include extension laboratory measurements in the<br />
Heidelberg Aeolotron and the Hamburg wind-wave facility that combine gas exchange, wave imaging<br />
and flow measurements.<br />
The second focus will be further development of the depth-resolving measurements of concentration<br />
fields and 3-D flow fields within the aqueous viscous boundary layer.<br />
Publications<br />
Peer Reviewed Publications<br />
1. Frew et al. [2004]<br />
2. Garbe et al. [2004a]<br />
3. Jähne et al. [2005c]<br />
4. Schimpf et al. [2004]<br />
5. Zhang & Garbe [2004]<br />
Other Publications<br />
1. Jähne [2004]<br />
2. Jähne [2005a]<br />
3. Jähne [2005b]<br />
Doctoral Theses<br />
1. Fuß [2004]<br />
2. Hilsenstein [2004]<br />
3. Klar [2005]<br />
4. Nielsen [2004]
5.1. SMALL-SCALE AIR-SEA INTERACTION 173<br />
Diploma Theses<br />
1. Rocholz [2005]<br />
2. Schwarz [2005]<br />
Invited Talks<br />
1. Jähne [2004]<br />
2. Jähne [2004]<br />
3. Jähne & Garbe [2004]<br />
4. Jähne et al. [2005]
174 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
5.1.1 Investigation of transport processes across the sea-surface microlayer<br />
by active thermography<br />
Participating scientist Uwe Schimpf and Christopher Popp<br />
Abstract The thermal boundary layer is considered as a black box in linear system theory. The<br />
input is a periodically varying heat flux forced onto the water surface by a carbon dioxide laser, the<br />
output is the amplitude and phase shift of the water surface temperature measured by an infrared<br />
camera.<br />
100 Watts CO 2 laser (10.6 µm)<br />
IR camera<br />
(3-5 µm)<br />
240 cm<br />
100 cm<br />
Paddle<br />
temperature probe<br />
humidity probe<br />
temperature probe<br />
62 cm<br />
X-Y scan unit<br />
flow meter<br />
wind direction<br />
wind speed 1.4 m/s<br />
wind speed 3.2 m/s<br />
wind speed 8.2 m/s<br />
Figure 5.1: Setup of the controlled flux technique in the AEOLOTRON wind-wave facility. A carbon<br />
dioxide laser forces a periodic heat flux onto the water surface. The temperature response of the water<br />
surface is measured by an infrared imager. From the image sequences the amplitude damping and the<br />
phase shift of the temperature signal is calculated.<br />
Background In order to improve the parameterizations<br />
and the models of air-gas exchange,<br />
the transport mechanisms in the boundary layer<br />
and their space and time scales have to be understood<br />
in detail. The active controlled flux technique<br />
[Jähne et al. , 1989] gives a detailed insight<br />
into the turbulent processes controlling the transport<br />
across the sea surface microlayer.<br />
Funding Aktives Thermografie System, HBFG-<br />
125-667 (Hardware), DFG Ja395/13-1 (Joint<br />
project with Detlef Stammer, Insitut <strong>für</strong><br />
Meereskunde, <strong>Universität</strong> Hamburg)<br />
Methods and results Heat is used as a proxy<br />
tracer for gases. The heat flux is controlled by<br />
forcing infrared radiation onto the water surface<br />
and the temperature variation is directly measured<br />
with an infrared imager. For slow temporal<br />
variations of the infrared radiation the transfer velocity<br />
is given by the ratio of the heat flux density<br />
and the temperature variation at the water surface.<br />
If the heat flux is switched off, the temperature<br />
increase will decay with a characteristic time<br />
constant of the transport across the thermal sublayer.<br />
The measured phase shifts clearly indicate<br />
that the transfer process is strongly intermittent.<br />
Outlook/Future work The developed system<br />
will be deploy in the DFG project ”Impact of<br />
Wind, Rain, and Surface Slicks on Air-Sea CO2<br />
Transfer Velocity - Tank Experiments” in cooperation<br />
with the <strong>Institut</strong>e of Oceanography, University<br />
of Hamburg. The goal is to improve the<br />
understanding of the parameterization of air-sea<br />
gas exchange with emphasis on CO2.<br />
Main publication Schimpf et al. [2004]
5.1. SMALL-SCALE AIR-SEA INTERACTION 175<br />
5.1.2 Water flow measurements in environmental and biological systems<br />
Participating scientist Christoph S. Garbe<br />
Abstract Novel measurement techniques are developed for accurately determining water flows in<br />
biological and environmental systems. These techniques are closely linked to the development of refined<br />
image processing techniques, making temporally and spatially highly resolved field measurements<br />
feasible.<br />
a) b) c)<br />
Figure 5.2: In a) a thermal image of the air-water interface is shown with the extracted motion field.<br />
In b) the motion of a microfluidic application is shown, and in c) the flow velocity of Xylem in a plant<br />
leaf can be seen.<br />
Background For a number of exchange processes<br />
both in environmental and life sciences, the<br />
transport of water plays a fundamental role. Systems<br />
of interest are turbulent transport at water<br />
surfaces for air sea heat and gas exchange, water<br />
flow in plant leaves, and microfluids. Density<br />
distributions of tracers are visualized with modern<br />
cameras and their motion as well as density<br />
changes estimated from digital image processing<br />
techniques. Examples of such tracers are heat<br />
which can be applied with lasers and visualized<br />
with highly resolved thermographic imagers or<br />
caged dyes for microfluidic applications. Results<br />
of these flow measurements can be used for modelling<br />
physical transport processes, deepening our<br />
understanding of the systems analyzed.<br />
Funding Research Centre Jülich (Forschungszentrum<br />
Jülich), Jülich<br />
DFG SPP 1147, “Bildgebende Messverfahren <strong>für</strong><br />
die Strömungsanalyse”<br />
DFG SPP 1114, “Mathematische Methoden<br />
der Zeitreihenanalyse und digitalen Bildverarbeitung”<br />
Methods and results A fluid is visualized using<br />
density distributions as tracers. These can be<br />
heat or dyes. At the air-water interface, usually<br />
a net heat flux is present which allows visualizing<br />
turbulences directly without additional tracers.<br />
The motion of density distributions is then<br />
modelled as a linear partial differential equation<br />
(PDE). These PDEs can be solved from the image<br />
sequences with techniques developed in digital<br />
image processing. This allows to estimate the<br />
motion as well as density changes in the image<br />
sequences. Through estimating motion as well as<br />
other parameters of the transport model, a deeper<br />
understanding of the transport processes involved<br />
can be reached. Through this technique, the net<br />
heat flux at the air-water interface was estimated<br />
directly for the first time, both temporally and<br />
spatially highly resolved. Furthermore, the flow<br />
of water in plant leaves was also measured in a<br />
relatively simple set-up.<br />
Outlook/Future work The developed techniques<br />
will be used for studying transport processes<br />
for shear driven as well as convective driven<br />
exchange of heat and mass at the air-water interface.<br />
Furthermore, the transport of Xylem in<br />
plant leaves will be measured under varying environmental<br />
forcings. This will make spatially resolved<br />
measurements of water flows in plant leaves<br />
possible for the first time, closing a missing link<br />
in the understanding of water relations in plants.<br />
The low Reynolds number flows in microfluidic<br />
mixing machines will also be measured, allowing<br />
to improve the design and mixing capabilities for<br />
such devices.<br />
Main publication Garbe et al. [2004a]; Zhang<br />
& Garbe [2004]; Garbe et al. [2004b]
176 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
5.1.3 Time resolved Measurements of Air Water Gas Exchange<br />
Participating scientist Kai Degreif<br />
Abstract Laboratory measurements are performed to determine the influence of short wind waves<br />
on air-sea gas exchange. UV-spectroscopy is introduced as a powerful method for tracking the fate<br />
of gaseous and volatile tracers simultaneously both in the gas and water phase. The “controlled<br />
leakage technique”, a new measurement technique that permits the calculation of time resolved flux<br />
rates exclusively from the air-side concentration, could be validated within the scope of the UVmeasurements.<br />
Reliable gas flux measurements of dissolved trace gases for a broad range of species<br />
without the need for extraction are now feasible.<br />
a b<br />
d e<br />
wind speed [m/s]<br />
relative concentration<br />
5<br />
4<br />
3<br />
2<br />
1<br />
0<br />
0 1 2 3<br />
time[h]<br />
4 5 6<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
measured concentration<br />
calculated concentration<br />
0<br />
0 1 2 3<br />
time [h]<br />
4 5 6<br />
c<br />
f<br />
relative concentration<br />
transfer velocity k [cm/h]<br />
0.14<br />
0.12<br />
0.1<br />
0.08<br />
0.06<br />
0.04<br />
0.02<br />
0 1 2 3<br />
time [h]<br />
4 5 6<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
0 1 2 3<br />
time [h]<br />
4 5 6<br />
Figure 5.3: Time resolved gas exchange measurements at the small Heidelberg Wind Wave Facility. a<br />
Experiments are performed in a small circular water channel of 1.2 m diameter. b Rotating windpaddles<br />
produce controlled wind speeds. c The investigated trace gases are dissolved in the water phase.<br />
The air-volume being constantly flushed with fresh air, the air-side concentration of the released tracers<br />
is proportional to the gas transfer and the water concentration. d Concentration measurements of<br />
volatile aromatics are performed using UV-spectroscopy simultaneously in the air and water phase. e<br />
The calculated water concentration is in good agreement with the measured water concentration. f<br />
Gas transfer velocities are achieved with a high time resolution.<br />
Background The oceans can act as a source<br />
or sink for climate relevant gases such as carbon<br />
dioxide, methane or dimethylsulphide. As hydrodynamics<br />
at the free oceans surface is not well<br />
understood yet, the estimation of total flux rates<br />
of those gases has to rely on empiric parameterizations.<br />
Precise and systematic laboratory measurements<br />
can help us to get a better understanding<br />
of the gas transfer rates dependence on tracer<br />
parameters like Schmidt number and solubility or<br />
hydrodynamic parameters like wind stress, waviness<br />
of the water surface and turbulence intensity.<br />
Methods and results Conventional gas exchange<br />
measurements rely on the knowledge of<br />
concentration gradients across the water surface.<br />
Therefore the information about the concentration<br />
of the dissolved species is indispensable. UVspectroscopy<br />
provides the possibility for direct<br />
and fast measurement of multiple tracer concentrations<br />
both in the water and the atmosphere.<br />
Volatile aromatic hydrocarbons such as benzene,<br />
thiophene, pyridine and derivates, and some other<br />
species can be measured.<br />
The “controlled leakage technique” permits the reconstruction<br />
of the water concentration from gases<br />
that are released by the water body only by measuring<br />
the air concentration. Therefore flux rates<br />
of tracers with a wide range of physicochemical<br />
parameters, i.e. Schmidt number and solubility<br />
can be measured simultaneously so that a detailed<br />
experimental study of the influence of these parameters<br />
on air-water gas exchange has now become<br />
feasible and will be presented within the<br />
work.<br />
Funding Project funded by the DFG<br />
Main publication Degreif, Kai, Doktorarbeit,<br />
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong> und Interdisziplinäres<br />
Zentrum <strong>für</strong> Wissenschaftliches Rechnen, <strong>Universität</strong><br />
Heidelberg, 01/2006
5.1. SMALL-SCALE AIR-SEA INTERACTION 177<br />
5.1.4 3-D flow measurements within a porous gravel layer<br />
Participating scientist Michael Klar<br />
Abstract A novel technique for 3-D flow measurements within a permeable gravel layer is developed.<br />
Two fiberoptic endoscopes are used in a stereoscopic arrangement to acquire image sequences of<br />
the flow field within a single gravel pore. The images are processed by a 3-D Particle-Tracking<br />
Velocimetry (3-D PTV) algorithm, which yields the three-dimensional reconstruction of Lagrangian<br />
particle trajectories.<br />
Figure 5.4: Left: Experimental setup with two fiberoptic endoscopes observing the flow field within a<br />
specially prepared artificial gravel pore. Right: 3-D flow trajectories of the pore flow, obtained from<br />
the recorded stereo image sequences.<br />
Background Bed stability of rivers and waterways<br />
is one of the major issues of geotechnical and<br />
hydraulic engineering. The design of erosion protection<br />
structures, e.g. filter layers of noncohesive<br />
gravel, is based on empirical design criteria and<br />
numerical, analytical and phenomenological models<br />
for flow and sediment transport. There is a<br />
lack of experimental data that can be used to validate<br />
and improve these models. A detailed examination<br />
of the hydrodynamic processes that cause<br />
instability of single grains requires flow measurements<br />
with a high temporal and spatial resolution.<br />
Funding Federal Waterways Engineering and<br />
Research <strong>Institut</strong>e (Bundesanstalt <strong>für</strong> Wasserbau,<br />
BAW), <strong>Karls</strong>ruhe.<br />
Methods and results The core of the experimental<br />
setup is an artificial gravel pore made up<br />
of grains fixed to each other. Optical access to the<br />
pore volume is given by two flexible fiberoptic endoscopes.<br />
The artificial pore is embedded within a<br />
gravel bed at the bottom wall of an open-channel<br />
flow. Tracer particles are added to visualize the<br />
pore flow, and image sequences of the flow field<br />
inside the artificial pore are recorded.<br />
Analysis of the image sequences by digital image<br />
processing techniques, namely a 3-D PTV algorithm,<br />
yields the Lagrangian flow velocities of the<br />
tracer particles along their trajectories. The algorithm<br />
is based on stereo correlation of the particle<br />
trajectories. The 3-D coordinates are calculated<br />
by triangulation of corresponding optical<br />
rays. Correlating 2-D trajectories instead of the<br />
positions of single particles allows for a simple<br />
setup with a minimum number of two cameras<br />
resp. endoscopes.<br />
Experiments have been conducted in cooperation<br />
with the Federal Waterways Engineering and Research<br />
<strong>Institut</strong>e (Bundesanstalt <strong>für</strong> Wasserbau,<br />
BAW) in Karlruhe and the <strong>Institut</strong>e for Hydromechanics<br />
of the University of <strong>Karls</strong>ruhe. Extensive<br />
flow measurements under different flow conditions<br />
have been carried out in an experimental flume located<br />
at the BAW. The impact of the turbulent<br />
free surface flow on the pore flow inside the gravel<br />
bed is clearly reflected in the measurement results.<br />
These studies are part of an international research<br />
project initiated by the BAW, with the objective<br />
to quantify the influence of turbulent velocity and<br />
pressure fluctuations on the stability of river beds.<br />
Outlook/Future work The main subject of<br />
further work will be the comprehensive hydromechanic<br />
analysis of the flow data obtained in the<br />
experiments at the BAW.<br />
Main publication Klar [2005]
178 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
5.1.5 3D fluid flow measurement close to surfaces<br />
Participating scientist Markus Jehle<br />
Abstract A novel measurement technique for 3D reconstruction of Eulerian velocity vector fields<br />
and Lagrangian trajectories at water-side boundary layers in wavy free surfaces is developed. In a<br />
first step, the method is applied in a falling film with known velocity profile.<br />
intensity [arbitrary units]<br />
1<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0<br />
absorption of dye (tartracine)<br />
emission of LED 1 ("royal blue")<br />
emission of LED 2 ("blue")<br />
380 400 420 440 460 480 500 520 540<br />
wavelength [nm]<br />
Figure 5.5: Top: Experimental setup. Bottom:<br />
The emitted light of the two types of LEDs<br />
(“blue” and “royal blue”) is absorbed by the dye<br />
(tartracine acid yellow) unequally. Thus, with<br />
known penetration depths, a reconstruction of the<br />
depth of the observed particle is possible.<br />
Background In order to examine the air-water<br />
gas exchange, a detailed knowledge of the waterside<br />
flow-field is needed. Therefore important<br />
quantities like wall-shear stresses, velocity profiles,<br />
dissipation rates and Lagrangian trajectories,<br />
have to be determined. Because the flow<br />
is 3D, instationary and close to the wave-driven<br />
(curved and moving) water-surface, conventional<br />
techniques like Particle Imaging Velocimetry using<br />
laser light sections are not applicable. A technique<br />
that is similar to the one proposed here is<br />
applied in the field of biofluidmechanics succesfully,<br />
where it is important to get knowledge about<br />
the flow in (artificial) blood vessels.<br />
Methods and results A fluid volume is illuminated<br />
by LEDs. Small glas hollow spheres (mean<br />
diameter 30µm) are added to the fluid, working as<br />
tracer. A high speed camera pointing to the water<br />
surface from above records the image sequences.<br />
The depth of an individual fluid particle is coded<br />
by a supplemented dye, which absorbs the light of<br />
the LEDs obeying Beer-Lambert’s law. By using<br />
LEDs flashing with two different wavelengths it is<br />
possible to use particles variable in size:<br />
The depth of a particle, which appears to the camera<br />
under the intensities (gray values) g1 and g2<br />
is calculated according to<br />
z(g1, g2) = z∗1z∗2<br />
z∗1 − z∗2<br />
�<br />
ln<br />
� g1<br />
g2<br />
�<br />
+ ln<br />
� g02<br />
g01<br />
��<br />
,<br />
where z∗1 and z∗2 are the penetration depths of<br />
LED-light of two distinct wavelengths into the<br />
dyed fluid, and g01/g02 is the ratio of the intensities<br />
of the two light sources. All of these quantities<br />
can be obtained by means of calibration.<br />
The velocity vectors of the flow are obtained using<br />
an extension of the method of optical flow,<br />
allowing for exponential brightness changes.<br />
First results obtained in a laminar falling film<br />
with known hydrodynamics show the feasibility<br />
of this measurement technique: the measurement<br />
reproduces the theoretical velocity profile in good<br />
agreement.<br />
Outlook/Future work The method will be extended<br />
to higher particle densities, coping with<br />
the problem of overlapping of the motion of individual<br />
particles. Further, the technique will be<br />
applied both at curved and at moving free surfaces.<br />
Simultaneous measurements using active<br />
thermography and imaging slope gauge will be<br />
conducted.<br />
Funding DFG-Schwerpunktprogramm 1147
5.1. SMALL-SCALE AIR-SEA INTERACTION 179<br />
5.1.6 Imaging concentration profiles of water boundary layer by Double-<br />
Dye LIF<br />
Participating scientist Achim Falkenroth<br />
Abstract Laser-Induced Fluorescence (LIF) is applied to directly observe and understand the mechanism<br />
of gas exchange in the upper 500 µm boundary layer. The luminescent dye used (Ru-complex)<br />
is sensitive to a given in-situ oxygen concentration that quenches the phosphorescence. The new<br />
Double-Dye LIF technique strives for a 2-D spatial resolution of 200x50 µm 2 .<br />
Figure 5.6: The camera looks through a prism on the surface to measure a wavelength spectrum for<br />
every point of a laser line. Spectra with and without the second dye are shown on the left.<br />
Background The difficulty in studying the<br />
inter-phase exchange processes is due to the small<br />
interacting thickness of approximately 30 µm to<br />
1 mm on both sides of a boundary layer z∗. Therefore,<br />
none of the traditional fixed sampling methods<br />
are applicable.<br />
A non invasive optical method using luminescent<br />
dyes is chosen to determine the gas concentration.<br />
Especially phosphorescent dyes are advantageously<br />
sensitive to quenching because of the long<br />
live time of their excitation states. In regions of<br />
high oxygen concentration, the amount of light<br />
emitted will be significantly lower.<br />
Fluorescent pH indicators may also be used, as<br />
they are able to quantitatively visualise acid or<br />
basic gases like HCl, NH3, or CO2. In former<br />
studies, the boundary layer of the water was monitored<br />
sideways. This way, it is difficult to get a<br />
high resolution with a wavy and agitated surface.<br />
Methods and results The idea of this work is<br />
to reconstruct the concentration profile by looking<br />
from the top on the surface using the spectral<br />
information of all points illuminated by a visible<br />
laser system. The light emitted by the luminescent<br />
dye travels back to the surface through the<br />
water body.<br />
A second dye is dissolved which absorbs certain<br />
wavelengths of the emission spectrum. Therefore,<br />
the deepness information is concealed in the light<br />
spectra. By applying an inverse modelling approach,<br />
the concentration depths can be evaluated<br />
over the whole depth profile.<br />
The time resolution aimed for is naturally predetermined<br />
by the demanding task to catch the<br />
micrometer waves and turbulence events like, for<br />
example, surface renewal. Finally, a temporal resolution<br />
of 30 − 100 Hz should be reached.<br />
First results are luminescence spectra of about 300<br />
pixels acquired with a low noise camera. The signal<br />
appears to be adequate as an input for the<br />
inverse calculation in order to gain the concentration<br />
profiles.<br />
Outlook/Future work The consistent next<br />
steps will be to improve the resolution and stability<br />
of the reconstruction. The application of this<br />
method for measurements in a water tank with<br />
wind generated waves lies ahead.<br />
Funding DFG-Research-Training-Group<br />
(Graduiertenkolleg 1114)
180 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
5.1.7 Combined slope/height measurements of short wind waves : ISHG<br />
Participating scientists Roland Rocholz, Martin Schmidt<br />
Abstract A new technique for the simultaneous measurement of wave height and wave slope of<br />
water surface waves has been developed. The Imaging Slope/Height Gauge (ISHG) is an imaging<br />
system that is designed to measure waves at different length scales. Using a high speed camera, the<br />
high spatiotemporal resolution provides an insight into hydrodynamic processes such as microscale<br />
wave breaking and small scale wave-wave interaction.<br />
f 2<br />
high speed camera<br />
(lens set to infinity)<br />
lens (L 2 ) for telecentric<br />
imaging (f 2 = 50 cm)<br />
water body<br />
lens (L 1 ) for telecentric<br />
illumination (f 1 = 25 cm)<br />
diffusing screen<br />
rays are only<br />
for illustration<br />
(entrance pupil of the<br />
camera lies at the focal<br />
point of lens L 2 )<br />
f 2 (mean water height is at<br />
focal distance to L 2 )<br />
water height<br />
(6 to 16 cm)<br />
f 1 (diffusing screen is at<br />
focal distance to L 1 )<br />
programmable LED-array<br />
(320x1W, λ = 880nm)<br />
Figure 5.7: Sketch of the wave imaging system<br />
for the simultaneous measurement of waves height<br />
and slope.<br />
Background Since water surface waves<br />
strongly influence transfer velocities due to the<br />
induced turbulence, such wave measurements are<br />
used for monitoring the conditions in gas exchange<br />
experiments. Unfortunately, the slope calibration<br />
of typical imaging wave measurement techniques<br />
like the color imaging slope gauge used at the<br />
Heidelberg Aeolotron so far is depending on the<br />
wave height of larger waves. To overcome this<br />
source of systematic errors, a new technique is<br />
under development with the following aims:<br />
• The slope of the waves should be measured<br />
without biases due to the wave height<br />
• The image size should not change with wave<br />
height<br />
• The wave slope and height should be measured<br />
simultaneously<br />
• Simple set-up with a single camera<br />
Funding DFG, Ja395/13: ”Mechanismen des<br />
Gasaustausches zwischen Atmosphäre und Ozean:<br />
Laborversuche und Modellierung”<br />
Methods and results Like the color imaging<br />
slope gauge the slope measurement of the new<br />
Imaging Slope/Height Gauge (ISHG) is based on<br />
light refraction (shape from refraction) and makes<br />
use of an area-extended light source with defined<br />
spatial variation of radiance, produced by a programmable<br />
LED array. This Imaging Slope Gauge<br />
gives a 2-D slope map of the water surface. The<br />
Imaging Height Gauge gives the 2-D height map.<br />
This is also used to correct the slope map for<br />
height dependencies. The method is based on<br />
light absorption and works with light in the near<br />
infrared range. The optical setup provides a telecentric<br />
imaging. The camera is virtually located<br />
at infinity so that height variations of the water<br />
surface do not affect the image scaling.<br />
Outlook/Future work The ISHG system at<br />
our small wind wave flume is still under construction.<br />
The calibration and first wave measurements<br />
are expected to take place at the end of year 2005.<br />
It is planned to assemble the same system at the<br />
wind-wave tank of the University of Hamburg and<br />
at the wind-wave facility AEOLOTRON, University<br />
of Heidelberg. Combining the ISHG with infrared<br />
imaging will be the next step of extending<br />
the system.<br />
Main publication Jähne et al. [2005c]
5.1. SMALL-SCALE AIR-SEA INTERACTION 181<br />
5.1.8 Development of a depth resolving boundary layer visualization for<br />
gas exchange at free water surfaces<br />
Participating scientist Tobias Schwarz<br />
Abstract To directly visualize gas concentration transport in the water-sided boundary layer, a<br />
combined LIF-measurement system consisting of a laser scanning unit and a confocal microscope has<br />
been developed and constructed. Furthermore, methods to reconstruct a 2-D depth profile had been<br />
investigated.<br />
Figure 5.8: An example of the fluorescence intensity changes through local gas concentrations, illuminated<br />
with the laser scanning system.<br />
Background As detailed knowledge of gas exchange<br />
between atmosphere and ocean is of great<br />
importance for predicting and modeling future<br />
climate situations, this diploma thesis aimed at<br />
the development of a measurement system for improved<br />
gas exchange measurements.<br />
Funding Graduiertenkolleg 1114 “Optische<br />
Messtechniken <strong>für</strong> die Charakterisierung von<br />
Transportprozessen an Grenzflächen” (TU Darmstadt<br />
and U Heidelberg)<br />
Methods and results A measurement setup<br />
is introduced which makes it possible to directly<br />
measure two-dimensional, vertical concentration<br />
profiles of gases in the water sided boundary layer<br />
using Laser-Induced Fluorescence (LIF). While it<br />
is impossible to gain knowledge of the physical<br />
processes involved in gas exchange using measurements<br />
of transfer rates and mass balances, the introduced<br />
method makes it possible to directly visualize<br />
the physical processes of matter transport<br />
in the layer. The measurement method is based on<br />
two basic principles: First, a fluorescence indicator<br />
is used, whose fluorescence intensity is proportional<br />
to the local pH-value, thus allowing a spa-<br />
tial resolved measurement of the concentrations of<br />
dissolved alkaline or acidic gases. Second, to create<br />
a depth resolution, a second, absorbing dye is<br />
added, whose absorption maximum lies inside the<br />
fluorescence spectrum, so that spectra from different<br />
depths show changes in their spectral shape<br />
due to the different light path lengths through the<br />
absorber. Thus the measured spectrum is the superposition<br />
of all depth spectra, which provide the<br />
basis of a linear inverse problem. Models for the<br />
reconstruction of the depth information will be introduced<br />
in the course of this thesis, and the solvability<br />
will be analyzed. As the stability of the<br />
solution of the inverse problem is almost exclusively<br />
determined by the invertibility of the basis<br />
function matrix, a confocal microscope was constructed,<br />
which allowed the direct measurement of<br />
depth spectra. Thereby it was made possible to<br />
numerically analyze and evaluate the conditioning<br />
of the matrix invertibility.<br />
Outlook/Future work Work to be continued<br />
within Graduiertenkolleg 1114<br />
Main publication Schwarz [2005]
182 CHAPTER 5. SMALL-SCALE AIR-SEA INTERACTION<br />
References<br />
Bock, E. J., Hara, T., Frew, N. M., & McGilles, W. R. 1999. Relationship between air-sea gas transfer<br />
and short wind waves. J. Gephys. Res., 104, 25 821–25 831.<br />
Frew, N. M. 1997. The role of organic films in air-sea gas exchange. Pages 121–172 of: Liss, Peter S., &<br />
Duce, Robert S. (eds), The Sea Surface and Global Change. Cambridge, UK: Cambridge University<br />
Press.<br />
Frew, N. M., Bock, E. J., Schimpf, U., Hara, T., Haußecker, H., Edson, J. B., McGillis, W. R., Nelson,<br />
R. K., McKeanna, B. M., Uz, B. M., & Jähne, B. 2004. Air-sea gas transfer: its dependence on wind<br />
stress, small-scale roughness and surface films Small-Scale Air-Sea Interaction with Thermography.<br />
Journal of Geophysical Research, C8(109). C08S17, doi:10.1029/2003JC002131.<br />
Fuß, D. 2004. Kombinierte Höhen- und Neigungsmessung von winderzeugten Wasserwellen am Heidelberger<br />
Aeolotron. PhD Thesis, <strong>Universität</strong> Heidelberg.<br />
Garbe, C. S., Spies, H., & Jähne, B. 2003. Estimation of Surface Flow and Net Heat Flux from<br />
Infrared Image Sequences. J. Mathematical Imaging and Vision, 19, 159–174.<br />
Garbe, C. S., Schimpf, U., & Jähne, B. 2004a. A Surface Renewal Model to Analyze Infrared Image<br />
Sequences of the Ocean Surface for the Study of Air-Sea Heat and Gas Exchange. Journal of<br />
Geophysical Research, C8(109). C08S15, doi:10.1029/2003JC001802.<br />
Garbe, C. S., Smoljar, N., Korniyenko, M., & Schurr, U. 2004b. Water relations in plant leaves. Chap.<br />
19 of: Image Sequence Analysis to Investigate Dynamic Processes. Lecture Notes in Computer<br />
Science. Springer.<br />
Hilsenstein, V. 2004. Design and Implementation of a Passive Stereo-Infrared Imaging System for the<br />
Surface Reconstruction of Water Waves. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Jähne, B. 1980. Zur Parameterisierung des Gasaustausches mit Hilfe von Laborexperimenten. Diss.,<br />
Univ. Heidelberg. D-200.<br />
Jähne, B. 2001. Air-Sea Interaction: Gas Exchange. In: Steele, J., Thorpe, S., & Turekian, K. (eds),<br />
Encyclopedia of Ocean Sciences. Academic Press, London.<br />
Jähne, B. 2004. Exchange Processes at the Ocean Surface: Their Role in Coupling Atmosphere and<br />
Ocean, A Contribution to the SOLAS Project. Invited talk, Hauptvortrag Fachverband <strong>Umweltphysik</strong>,<br />
DPG Frühjahrstagung München, 22. Mrz 2004.<br />
Jähne, B. 2004. Handbook of Digital Image Processing for Scientific and Technical Applications. 2nd<br />
edn. Boca Raton: CRC Press.<br />
Jähne, B. 2004. New Insight into the Mechanisms of Air-Sea Gas Transfer. Invited talk, IOW-<br />
Kolloquium, Leibniz-<strong>Institut</strong> fr Ostseeforschung, Warnemünde, Januar 2004.<br />
Jähne, B. 2005a. Digital Image Processing. 6th edn. Berlin: Springer.<br />
Jähne, B. 2005b. Digitale Bildverarbeitung. 6th edn. Berlin: Springer.<br />
Jähne, B., & Garbe, C. S. 2004. Spatiotemporal Active Thermography. Invited talk, 7th International<br />
Conference on Quantitative Infrared Thermography, von Karman <strong>Institut</strong>e for Fluid Dynamics in<br />
Rhode Saint Genèse, Belgium, 08. July 2004.<br />
Jähne, B., & Haußecker, H. 1998. Air-Water Gas Exchange. Annual Rev. Fluid Mech., 30, 443–468.<br />
Jähne, B., Münnich, K. O., Bösinger, R., Dutzi, A., Huber, W., & Libner, P. 1987. On the parameters<br />
influencing air/water gas exchange. J. Geophys. Res, 92, 1937–1949.<br />
Jähne, B., Libner, P., Fischer, R., Billen, T., & Plate, E. J. 1989. Investigating the transfer processes<br />
across the free aqueous viscous boundary layer by the controlled flux method. Tellus, 41B, 177–195.<br />
Jähne, B., Nielsen, R., Popp, C., Schimpf, U., & Garbe, C. S. 2005. Air-Sea Gas Transfer: Schmidt<br />
Number Dependency and Intermittency. Invited talk, 37th International Liège Colloquium on Ocean<br />
Dynamics Gas Transfer at Water Surfaces, 2–6 May 2005.
5.1. SMALL-SCALE AIR-SEA INTERACTION 183<br />
Jähne, B., Schmidt, M., & Rocholz, R. 2005c. Combined optical slope/height measurements of short<br />
wind waves: principle and calibration. Meas. Sci. Technol., 16, 1937–1944.<br />
Klar, M. 2005. Design of an endoscopic 3-D Particle-Tracking Velocimetry system and its application<br />
in flow measurements within a gravel layer. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Liss, P. S., & Merlivat, L. 1986. Air-sea gas exchange rates: introduction and synthesis. Pages 113–127<br />
of: Buat-Menard, P. (ed), The Role of Air-Sea Exchange in Geochemical Cycling. Dordrecht, The<br />
Netherlands: Reidel.<br />
Nielsen, R. 2004. Hochgenaue Messung der Schmidtzahlabhängigkeit des Gasaustausches an einer<br />
wind- und wellenbewegten Wasseroberfläche. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Rocholz, R. 2005. Bildgebendes System zur simultanen Neigungs- und Höhenmessung an kleinskaligen<br />
Wind-Wasser-Wellen. diploma thesis, <strong>Universität</strong> Heidelberg.<br />
Schimpf, U., Garbe, C. S., & Jähne, B. 2004. Investigation of transport processes across the seasurface<br />
microlayer by infrared imagery. Journal of Geophysical Research, C8(109). C08S13,<br />
doi:10.1029/2003JC001803.<br />
Schwarz, T. 2005. Development of a depth resolving boundary layer visualization for gas exchange at<br />
free water surfaces. diploma thesis, <strong>Universität</strong> Heidelberg.<br />
Wanninkhof, R. 1992. Relationship between wind speed and gas exchange over the ocean. J. Gephys.<br />
Res., 97, 7373–7382.<br />
Zappa, C. J., Asher, W. E., Jessup, A. T., Klinke, J., & Long, S. R. 2001. Effect of microscale wave<br />
breaking on air-water gas transfer. Pages 23–29 of: Donelan, M. A., Drennan, W. M., Saltzman,<br />
E. S., & Wanninkhof, R. (eds), Gas Transfer at Water Surfaces. Geophysical Monograph, vol. 127.<br />
Washington, DC: American Geophysical Union.<br />
Zhang, X., & Garbe, C. S. 2004. Studying dynamical processes of air-sea exchanges with air-water inerface<br />
image techniques. Chap. 3, pages 57–88 of: Recent Research Developments in Fluid Dynamics,<br />
vol. 5. Transworld Research Network.
Forschungsstelle “Radiometrie” of<br />
the Heidelberger Akademie der<br />
Wissenschaften<br />
6.1 Radiometric Dating of Water and Sediments . . . . . . . . . . . . . . . . 187<br />
185
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 187<br />
6.1 Radiometric Dating of Water and Sediments<br />
The Forschungsstelle is an independent research unit funded by the Heidelberger Akademie der Wissenschaften.<br />
Funding began in the year 1958 and will run until the end of 2010.<br />
Personnel :<br />
Prof. Dr. Augusto Mangini<br />
Dr. Bernd Kromer<br />
Dr. Marcus Christl<br />
Dr. Denis Scholz<br />
René Eichstätter, Technician<br />
Maleen Gillmann, Technician<br />
Sebastian Welk, Technician<br />
Karoline Thomas, Secretary<br />
Additional funding from the DFG, BMBF and EU (CarboEurope-IP):<br />
Scientists: Pablo Verdes, Marcus Christl, Denis Scholz, Andrea Schröder-Ritzrau, Sahra Talamo,<br />
Michael Friedrich,<br />
PhD-students: Frank Bernsdorff, Holger Braun, Nicolas Latuske, Jörg Lippold, Marga-rita Koroleva,<br />
Ingmar Unkel,<br />
Technicians: Helga Baus, Maleen Gillmann, Sabine Kühr, Eva Gier and 4 student assistants<br />
Master-students: Kerstin Bohn, Daniel Schimpf, Boris Schulze, Nicole Vollweiler, Patrick Wenderoth<br />
The task of the Forschungsstelle ”Radiometrie”of the Heidelberger Akademie der Wissenschaften is<br />
the dating and interpretation of climate archives. The research unit consists of two groups, the 14 C<br />
Lab (Bernd Kromer) and the Th/U-Lab (Augusto Mangini).<br />
14 C Lab The focus of the 14 C Lab are highly precise 14 C-dating and the construction of a calibration<br />
curve for radiocarbon that reaches far back into the last Glacial. Furthermore this Lab delivers 14 Cdatings<br />
for several archeological groups.<br />
Methods We use both the conventional gas-counting technique and AMS. The gas counters were<br />
developed to highest precision (better than 2 �). For AMS we prepare graphite targets, to be<br />
measured at one of the European AMS facilities.<br />
Extension of tree-ring based 14 C calibration into the Late Glacial In collaboration with<br />
the tree-ring laboratories of the University Stuttgart-Hohenheim and the University of Zürich/WSL<br />
Birmensdorf we extend the tree-ring based 14 C calibration into the past. Presently, the absolutely<br />
(annually) dated oak and pine chronology starts at 12.400 years BP (before AD 1950) [Friedrich et<br />
al., 2004; Reimer et al. 2004]. In the Late Glacial two independent chronologies were built in the two<br />
tree-ring labs, assisted by numerous 14 C predating in our laboratory [Kromer et al., 2004; Schaub et<br />
al., 2005]. Based on a comparison to the marine 14 C of [Hughen et al., 2004] the chronologies cover<br />
the mid-Bølling, all of the Allerød and the initial 150 years of Younger Dryas (ca. 14,100 to 12,800<br />
cal BP). The trees were recovered from gravel pits at the Danube river and its tributaries, the lignite<br />
area south-east of Berlin, and construction sites in Zürich. Beyond the range of these chronologies we<br />
assembled several floating 14 C sections from trees found in Northern Italy and Romania.<br />
The 14 C data sets are evaluated to infer solar activity variability [Bond et al., 2001; Solanki et al.<br />
2004, Usoskin et al., 2005] as well as ocean thermohaline circulation changes. Combined with 10 Be<br />
time series from Greenland they may serve to link tree-ring and ice-core time-scales. From dendroclimatological<br />
parameters of tree-rings, such as ring-widths, frost damage and growth patterns climate<br />
anomalies can be reconstructed.<br />
14 C dating, archaeology and geosciences We maintain extensive collaborations with archaeologists<br />
to date key sites, such as Troy [Kromer et al. 2002] or the Nasca sites in Peru [Eitel et al.<br />
2005], and to anchor floating tree-ring sections by 14 C wiggle-matching to the absolute scale. In the<br />
’Roman Gap Project’ (http://www.arts.cornell.edu/dendro/2004News/ADP2004.html) we assist in<br />
the extension of the Eastern Mediterranean chronologies into the first millennium AD, to link the<br />
absolute part to the 2300-year long Bronze Age chronology [Manning et al., 2003]. The date of the<br />
eruption of Thera remains a crucial and still controversial time marker of the Late Bronze Age in the<br />
Eastern Mediterranean. In long-standing collaborations with colleagues in archaeology we contribute<br />
to a high-precision 14 C date of this event [Manning et al., 2001].
188 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
14 C in the present-day carbon cycle The present-day 14 C level is largely determined by the<br />
re-equilibration of the atmosphere following strong 14 C input during the bomb testing up to 1962,<br />
and the dilution of the natural 14 C level by anthropogenic, 14 C free, CO2 emissions (see contribution<br />
by I. Levin in this report). In our laboratory continuous 14 C times series from several sites around<br />
the globe have been measured up to today, now covering more than 40 years [Levin & Kromer, 2004].<br />
Recently, 14 C has become an important marker to determine the ratio of fossil to present-day sources<br />
of carbon, e.g. in the emissions trading. Here we are involved in pilot studies to establish legislative<br />
procedures.<br />
Th/U-Lab The Th/U-Lab works on continental archives, such as speleothems and travertines, as<br />
well as on marine samples, such as deep sea sediments, Mn-nodules and corals.<br />
One principal focus is the determination of the natural variations of Holocene and Late Pleistocene<br />
climate using the stable isotopic composition of speleothems. Furthermore, we determine the magnitude,<br />
timing, and duration of past sea level fluctuations from the position and age of fossil coral reefs<br />
as well as the intensity of the Earths magnetic field during the past 350,000 years from 10 Berecords.<br />
These studies deliver a precise time scale for the variations of past climate. This is a basic requirement<br />
for the understanding of the causal relationships and the complex interplay between the forcing and<br />
feedback mechanisms in the climate system during the past 350,000 years and during the Holocene. We<br />
work in close cooperation with climate modelers from Hamburg and Berlin in the DEKLIM program<br />
(through 5/2006). With modelers from Potsdam we apply their CLIMBER2 model to study the<br />
abrupt climate changes that occurred during the Last Glacial (Dansgaard/Oeschger events).<br />
Methods We use dating methods, relying on the disequilibrium of the natural decay chains (TIMS-<br />
230 Th/U and 231 Pa/U). In addition, we use the decay of 10 Be, a radioactive product of cosmic rays.<br />
Speleothems, an archive of paleoclimate Speleothems are an excellent climate archive because<br />
they can be dated very precisely with the Th/U method. Stable isotope signals recorded in these<br />
stalagmites can be measured at a resolution of 100 µm and hence provide a climate signal of one-yearresolution.<br />
Most isotope signals in stalagmites display significant kinetic effects. These kinetic signals have been<br />
related to the intensity of precipitation within the last ten years. For example, periods of enhanced<br />
kinetic were ascribed to periods of less intense precipitation in speleothems from Oman and from<br />
Central Germany [Burns et al.,2002; Fleitmann et al., 2003; Neff et al., 2001; Niggemann et al,2003].<br />
The combination of this high resolution proxy for precipitation and the precise Th/U dating lead to<br />
a number of internationally regarded publications. For example, we found a very good correlation<br />
between the intensity of precipitation in Oman and the intensity of solar irradiation [Neff, 2001].<br />
This relationship has been confirmed by a number of following studies [e.g. Holzkämper et al., 2004;<br />
Mangini et al., 2005].<br />
In November 2005 we were granted by the DFG for a Forschergruppe (www.fg-Daphne.de) to study the<br />
basic processes affecting speleothem formation as well as the isotopic and the chemical signals. These<br />
studies will establish and improve the applicability of speleothems as archives for past precipitation<br />
and temperature. The DAPHNE project is funded for the next three years, with an option for funding<br />
for three additional years. We will work in close collaboration with groups from Bochum, Trento (Italy)<br />
and Innsbruck (Austria).<br />
Reconstruction of Sea level from fossil corals Reconstructions of past sea level allow to determine<br />
the magnitude, timing and duration of interglacial periods. which are essential for the understanding<br />
of the causal relationships and the complex interplay between the forcing and feedback<br />
mechanisms in the climate system.<br />
Some reef coral genera grow in upper 5m below sea surface only and record past sea level fluctuations.<br />
Thus, the determination of accurate U-series ages provides a direct method for sea level reconstruction.<br />
Unfortunately, many fossil reef corals show clear evidence for post-depositional open-system behaviour.<br />
There-fore, conventional Th/U-ages obtained from such corals cannot be considered as strictly reliable.<br />
We dealt with this problem (i) by identifying corals that have not been altered [Scholz and Mangini,<br />
in press] and (ii) by developing an appropriate correction technique [Scholz et al., 2004]. The results<br />
enabled to reconstruct sea level during Marine Isotope Substage 6.5 (∼175,000 years before present).<br />
The intensity of the Earth’s magnetic field in the past Accumulating evidence suggests that<br />
solar activity is responsible for at least some climatic variability. These include correlations between
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 189<br />
solar activity and either direct climatic variables or indirect climate proxies over time scales ranging<br />
from days to millennia [Eddy, 1976; Labitzke & van Loon, 1992; Svensmark & Friis-Christensen, 1997;<br />
Soon et al., 1996, 2000; Beer et al., 2000; Hodell et al., 2001]. A very notable correlation was that<br />
obtained in our group in Heidelberg [Neff et al., 2001]. However, the climatic variability attributable<br />
to solar activity is larger than could be expected from the typical 0.1% changes in the solar irradiance<br />
observed over the decadal to centennial time scale [Beer et al., 2000; Soon et al., 2000]. Thus, an<br />
amplifier is required unless the sensitivity to changes in the radiative forcing is uncomfortably high.<br />
The first suggestion for an amplifier of solar activity was suggested by Ney [1959], who pointed out<br />
that if climate is sensitive to the amount of tropospheric ionization, it would be sensitive the intensity<br />
of the Earth’s magnetic field as well as to solar activity since the solar wind modulates the cosmic ray<br />
flux (CRF), and with it, the amount of tropospheric ionization.<br />
We are studying 10 Be in marine sediments to determine the timing and the intensity of the Earth’s<br />
magnetic field in the past. The cosmogenic nuclide 10 Be is mainly produced in the lower stratosphere<br />
by interaction of galactic cosmic rays with oxygen and nitrogen atoms, and its production is known<br />
to be strongly anti-correlated with the solar- and/or geomagnetic field strength. In addition, highly<br />
resolved profiles of 10 Be in marine sediments may be used to synchronize the marine to the ice core<br />
ones.<br />
Cooperations The Forschungsstelle Radiometrie of the Heidelberger Akademie der Wissenschaften<br />
cooperates in the following projects with these institutions.<br />
Germany: Research Centre Ocean Margins, University of Bremen; Geosciences, University of Trier;<br />
<strong>Institut</strong>e for Paleontology, University of Erlangen; <strong>Institut</strong>e of Mineralogy, University of Frankfurt<br />
a.M.; <strong>Institut</strong>e of Environmental Geochemistry, University of Heidelberg; Potsdam <strong>Institut</strong>e for Climate<br />
Impact Research, Potsdam; Alfred-Wegener <strong>Institut</strong>e, Bremerhaven; ICG-V, Research-Centre<br />
Jülich; Faculty of Natural Sciences, University of Hohenheim, Stuttgart<br />
Foreign Countries: Paul-Scheerer <strong>Institut</strong>, ETH-Zürich, Switzerland Geology and Paleontology, University<br />
of Innsbruck, Austria<br />
Publications<br />
Peer Reviewed Publications<br />
1. Braun [in press]<br />
2. Christl et al. [2004]<br />
3. Eitel et al. [2005]<br />
4. Felis et al. [2004]<br />
5. Fleitmann et al. [2004]<br />
6. Friedrich et al. [2004]<br />
7. Holzkämper et al. [2004]<br />
8. Holzkämper et al. [2005]<br />
9. Hughen et al. [2004a]<br />
10. Hughen et al. [2004b]<br />
11. Kromer et al. [2004]<br />
12. Levin & Kromer [2004]<br />
13. Mangini et al. [2005]<br />
14. McHargue & Donahue [2005]<br />
15. McManus et al. [2004]<br />
16. Reimer et al. [2004]<br />
17. Schaub et al. [2005]
190 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
18. Scholz et al. [2004]<br />
19. Solanski et al. [2004]<br />
20. Usoskin & Kromer [2005]<br />
21. Verdes et al. [in pressa]<br />
22. Verdes et al. [in pressb]<br />
23. Wurth et al. [2004]<br />
Other Publications<br />
1. Christl et al. [2005]<br />
2. Scholz & Mangini [in press]<br />
3. Schröder Ritzrau et al. [2005]<br />
4. Spötl et al. [2004]<br />
Doctoral Theses<br />
1. Scholz [2005]<br />
Diploma Theses<br />
1. Bohn [2005]<br />
2. Schimpf [2005]<br />
3. Schulze [2005]<br />
4. Wenderoth [2005]
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 191<br />
6.1.1 Reconstruction of the geomagnetic field strength over the past 300,000<br />
years derived from 10 Be data of deep sea sediments from the North<br />
and South Atlantic Ocean<br />
Participating scientists Frank Bernsdorff, M. Christl, P. Wenderoth, B. Schulze, A. Mangini, D.<br />
Wagenbach, G. Brey (Frankfurt), P. Kubik (Zürich)<br />
Abstract In this project we use the anti correlation between the 10 Be production in the Earth’s<br />
stratosphere via galactic cosmic rays and the strength of the geomagnetic field to determine its variation<br />
over a time period of 300,000 years. Two deep sea sediment cores (ODP) from the Atlantic<br />
Ocean, which act as 10 Be archives are investigated.<br />
Background The cosmogenic nuclide 10 Be is<br />
mainly produced in the lower stratosphere by interaction<br />
of galactic cosmic rays with oxygen and<br />
nitrogen atoms, and its production is known to<br />
be strongly anti-correlated with the solar- and/or<br />
geomagnetic field strength. After a short atmospheric<br />
residence time of about 1 year 10 Be is<br />
removed from this part of the atmosphere and<br />
deposited onto land, ice sheets and (mainly) the<br />
ocean surface. Therefore, it should be possible<br />
to extract a record of geomagnetic paleointensity<br />
(GPI) from depositional profiles of these radionuclides<br />
in marine, terrestrial and ice core archives.<br />
In this study we are investigating two deep sea<br />
sediment cores from the North and South Atlantic<br />
Ocean (ODP-Site 983 and ODP-Site 1089)<br />
for highly resolved 10 Be profiles. The application<br />
of a special correction procedure (involving uranium<br />
and thorium measurements) is indispensable<br />
to quantify the transport of 10 Be in the ocean, so<br />
that the global 10 Be-production can be extracted<br />
from marine records. Based on these profiles, a<br />
marine 10 Be stratigraphy will be developed that<br />
can be matched with 10 Be records from Greenland<br />
(GRIP, GISP II) and Antarctic (EPICA) ice cores.<br />
In particular, enhanced global 10 Be-production<br />
during geomagnetic events (Lachamp, Blake, Jamaica)<br />
can be used as global time marker for the<br />
synchronization of marine and ice core chronologies.<br />
Based on the 10 Be stratigraphy a record of<br />
relative paleointensity will be calculated independently<br />
from the magnetization data<br />
Funding DFG Schwerpunktprogramm: Antarktisforschung<br />
mit vergleichenden Untersuchungen<br />
in arktischen Eisgebieten (SPP 1158)<br />
Methods and results Besides the measurement<br />
of 10 Be in Zürich, we are implementing the<br />
new technique of ICPMS for the precise determination<br />
of thorium and uranium isotopes in sediments.<br />
During initial tests we analyzed a number<br />
of different standard solutions and deep sea<br />
sediment samples of known isotopic composition.<br />
First samples of ODP 983 sediments are presently<br />
studied.<br />
Outlook/Future work According to the goals<br />
of this project, the future work will mainly comprise<br />
10 Be measurements of the deep sea sediments<br />
from ODP site 983, its normalization to<br />
230 T hxs(0) and comparison to the data set of ODP<br />
site 1089 (South Atlantic).<br />
Main publication Christl et al. [2005]
192 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.2 Possible solar origin of the glacial 1,470-year climate cycle demonstrated<br />
in a coupled climate model<br />
Participating scientists H.Braun, M.Christl, A.Mangini, B.Kromer (AdW Heidelberg), K.Roth<br />
(IUP Heidelberg), S.Rahmstorf, A.Ganopolski (PIK Potsdam), C.Kubatzki (AWI Bremerhaven)<br />
Abstract It is shown that an intermediate-complexity climate model reproduces abrupt glacial<br />
warmings (Dansgaard-Oeschger events) with a spacing of 1470 years when forced by freshwater cycles<br />
of about 87 and 210 years, i.e. with periods close to known solar cycles. Thus, the glacial 1470-year<br />
climate cycle could be caused by the Sun despite the lack of a 1470-year solar period.<br />
Figure 6.1: Forcing and model response. The applied freshwater forcing (left panel, in mSv [1 Sv =<br />
106 m 3 /s]) is the sum of two sinusoidal cycles with periods of 210 years and 86.5 years, respectively.<br />
These periods are close to well-known solar cycles. In response to this forcing, the applied climate<br />
model can show abrupt warm events in Greenland (Dansgaard-Oeschger events) with a period of 1470<br />
years (right panel, in ◦ C). The dashed lines in both panels are spaced by 1470 years.<br />
Background Many paleoclimatic archives show<br />
a quasi-cycle of about 1470 years in the Last<br />
Glacial. This pattern is manifested in rapid<br />
climate shifts, the so-called Dansgaard-Oeschger<br />
(DO) events. To explain these, various concepts<br />
have been proposed, including internal oscillations<br />
in the climate system and external (e.g. solar)<br />
forcing. However, while pronounced solar cycles<br />
of about 87 and 210 years are well-known [Peristykh<br />
and Damon 2003, Wagner et al. 2001], a<br />
1470-year cycle has not been found [Stuiver and<br />
Braziunas 1993]. This has been considered as a<br />
main argument against solar origin of the glacial<br />
1470-year climate cycle.<br />
Funding This work was funded by the Heidelberg<br />
Academy of Sciences.<br />
Methods and results To test if the lack of<br />
a 1470-year solar cycle indeed argues against solar<br />
origin of the DO events, we used the climate<br />
system model CLIMBER-2 of the Potsdam <strong>Institut</strong>e<br />
for Climate Impact Research (PIK). In earlier<br />
simulations with the model, abrupt glacial warming<br />
events were already simulated which reproduce<br />
many features of the observed DO events<br />
[Ganopolski and Rahmstorf 2001, Ganopolski and<br />
Rahmstorf 2002]. In the model, DO events represent<br />
rapid transitions between a stadial (cold)<br />
and an interstadial (warm) mode of the North Atlantic<br />
thermohaline circulation (THC), triggered<br />
by a threshold process.<br />
In our model study, a freshwater forcing was applied<br />
which is the sum of two sinusoidal components<br />
with periods 1470/7 (=210) and 1470/17<br />
(about 86.5) years (left panel in figure 1). The amplitudes<br />
of both forcing components are small (10<br />
mSv, i.e 10.000 m 3 /s), that is, about 5 cm/year<br />
in the surface freshwater flux. Although the total<br />
forcing does not explicitly have a spectral component<br />
of 1470 years, it repeats with this period due<br />
to the combined effect of the applied cycles.<br />
The forcing can excite DO-like events in the North<br />
Atlantic region (right panel in 6.1). Within a large<br />
forcing-parameter range, these events are spaced<br />
by 1470 years. This timescale is robust when<br />
the phases, amplitudes, and periods of the two<br />
forcing cycles are changed over some range. If<br />
instead of two sinusoidal cycles a more realistic<br />
forcing is applied with spectral properties close<br />
to that observed in solar proxies, a regular 1470year<br />
model response is still found. The stability<br />
of the simulated 1470-year cycle results from two<br />
well-known properties of the THC: its long characteristic<br />
timescale, and the non-linearity (i.e. the<br />
threshold character) inherent in the transitions<br />
between the two modes of the THC. For Holocene<br />
conditions, DO events do not occur in the model.<br />
To conclude, our results show that the lack of<br />
a 1470-year solar cycle does not by itself argue<br />
against a solar origin of the glacial 1470-year climate<br />
cycle.<br />
Main publication Braun et al. [in press]
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 193<br />
6.1.3 Solar variability and rapid climate change on decadal to centennial<br />
scales<br />
Participating scientist Michael Friedrich (<strong>Universität</strong> Hohenheim), Bernd Kromer, Nicolas Latuske,<br />
Sabine Remmele (<strong>Universität</strong> Hohenheim), Gerd Schleser (Forschungszentrum Jülich)<br />
Abstract The relation between solar variability and climate variations in the Holocene was investigated.<br />
The heliomagnetic variations were derived from fluctuations of the production of 14 C,<br />
calculated from the atmospheric 14 C activity using a carbon box model. Statistical parameters obtained<br />
from tree ring widths were correlated with the 14 C production at two intervals of low solar<br />
activity where previously cooling in the North Atlantic has been documented. Generally only weak<br />
correlations were found, probably pointing to a low climate sensitivity of riverine oaks in the Holocene.<br />
Figure 6.2: Spectral features in the detrended ∆ 14 C data (upper curve); and band-pass-filtered ∆ 14 C.<br />
Center band-pass wavelength are of 88, 210, 500 and 950 years (top to bottom).<br />
Background The sun is the most important<br />
driving force in the climate system, but only little<br />
is know how the climate system reacts to changes<br />
of the solar magnetic activity on decadal to multicentennial<br />
scales. It is known that the Little Ice<br />
Age coincided with the decrease of solar activity<br />
in the Maunder Minimum (1645-1715) but the<br />
mechanism remains unclear. To investigate how<br />
the variation of the climate system responses to<br />
the variability of solar activity, we used the atmospheric<br />
14 C signal (∆ 14 C) recorded in tree rings<br />
as proxy of solar activity.<br />
In this study we investigated the variation of<br />
∆ 14 C changes in the time period of the Holocene<br />
on time scales from decades to centennial and<br />
correlated statistic parameters as calculated from<br />
tree rings with selected maxima of 14 C production<br />
(minima of solar activity).<br />
Funding Deutsches Klimaforschungsprogramm<br />
(DEKLIM)<br />
Methods and results The fluctuations in<br />
the 14 C production were calculated from the<br />
atmospheric 14 C (∆ 14 C) using a Oeschger-<br />
Siegenthaler-type box-diffusion model of the carbon<br />
cycle. Model experiments were done to investigate<br />
the influence of changes in diffusive deepocean<br />
ventilation, air-sea gas exchange rate and<br />
14 C production. Furthermore, the atmospheric<br />
14 C was spectrally analyzed with various methods<br />
(Singular Spectrum Analysis, Maximum Entropy<br />
Method and Multi Taper Method, Digital Filters<br />
(IIR) and Wavelets) to obtain solar variability periods<br />
(Fig. 6.2). Finally, statistical parameters of<br />
tree ring chronologies in southern Germany were<br />
calculated, and they were correlated to the 14 C<br />
production changes at intervals of low solar activity<br />
(∆ 14 C maximum).<br />
In two intervals of low solar activity, centered<br />
at 2800 BC and 800 BC, respectively, the treering<br />
parameters (derived from the ring widths) are<br />
weakly correlated with the 14 C production. The<br />
tree-ring parameters indicate that in these intervals<br />
the precipitation increased and the temperature<br />
decreased at times of solar minimum, pointing<br />
to a role of solar forcing of climate variability.<br />
Model experiments to explain instances and observed<br />
decrease of ∆ 14 C about 10 � over 20 years<br />
are compatible with an increase of the ocean circulation<br />
and gas exchange rate at a factor of 2 and<br />
a decrease at 25 % for the 14 C production.<br />
The results of spectral analysis ∆ 14 C are shown<br />
in Figure 6.2.<br />
Outlook/Future work none in this case<br />
Main publication in preparation
194 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.4 Establishment of a method for measuring 231 Pa in deep-sea sediments<br />
via ICP-MS<br />
Participating scientist Jörg Lippold, M. Christl, A. Mangini, G. Brey (Frankfurt).<br />
Abstract Using ICP-MS, the 231 Pa / 230 Th ratio of deep-sea sediments can be estimated more<br />
efficiently and precisely than by α-spectrometry. The measurement of the tracers 231 Pa and 230 Th<br />
allows a high resolution for paleoproductivity and ocean circulation studies on glacial to interglacial<br />
timescales.<br />
Background 231 Pa and 230 Th are natural radionuclides,<br />
which are continously produced in<br />
seawater by in situ decay of their dissolved progenitors<br />
234 U and 235 U. As a result, both are produced<br />
at a constant rate with an initial 231 Pa and<br />
230 Th activity ratio of 0.093. Variable 231 Pa and<br />
230 Th ratios in sediments indicate that both radionuclides<br />
follow different pathways of removal<br />
from the water column. The flux of 230 Th to<br />
the seafloor is nearly identical to its rate of production.<br />
In contrast, the longer oceanic residence<br />
time for dissolved 231 Pa due to lower particle reactivity<br />
allows a large scale diffusive transport over<br />
basin-wide distances prior to scavenging, resulting<br />
in its preferential removal in high particle flux<br />
regions.<br />
Particularly in the North Atlantic region radioisotope<br />
signals may be significantly influenced by<br />
changes in Ocean circulation. Up to now, the<br />
231 Pa and 230 Th-ratio is the best kinematic proxy<br />
to quantify the strength of the meridional overturning<br />
circulation. A high resolution study of<br />
the sedimentary 231 Pa and 230 Th-ratio showed<br />
that North Atlantic meridional overturning was<br />
highly variable, switching very fast from an offmode<br />
(during Heinrich Event H1) to almost modern<br />
conditions (Bølling-Allerød) during the past<br />
20 kyr. Thus, 231 Pa and 230 Th-data, that provide<br />
the best estimate of ocean circulation in the<br />
past, can be used as input for model calculations<br />
to quantify the transport of other tracers (e.g. 10<br />
Figure 6.3: Planktonic foraminifera δ 18 O (upper<br />
curve) plotted with sedimentary 231 Pa and<br />
230 Th (lower curve) against age, sediment core<br />
at 33 ◦ N, 57 ◦ W, [McManus et al., 2004].<br />
Be) in the North Atlantic Ocean. Because of the<br />
32.5 kyr half life of 231 Pa, this method is restricted<br />
to the last about 90 kyr [McManus et al., 2004],<br />
[Walter, 1998].<br />
Funding DFG Schwerpunktprogramm 527 and<br />
1158.<br />
Methods and results The accurate and precise<br />
determination of the very low 231 Pa content<br />
in marine sediments requires the application of<br />
a new analytical technique. ICP-MS is currently<br />
the most suitable analytical tool for high precision<br />
measurements of heavy isotope ratios. A cooperation<br />
with the <strong>Institut</strong>e of Mineralogy at the University<br />
of Frankfurt to develop the appropriate analytical<br />
techniques for the determination of Th/U,<br />
and Pa- isotope-ratios with Inductively Coupled<br />
Plasma Mass Spectrometry (ICP-MS) was initiated.<br />
Outlook/Future work In combination with<br />
published 231 Pa and 230 Th-data from the North<br />
Atlantic region, these records will help to greatly<br />
improve our understanding of past Ocean circulation<br />
in this region. Once established, the 231 Pa<br />
measurement method can be applied to further<br />
paleoclimate records, e.g. corals.<br />
Main publication in preparation
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 195<br />
6.1.5 Modelling of stable isotope records of stalagmites<br />
Participating scientist Christian Mühlinghaus, D. Scholz, D. Schimpf, A. Mangini<br />
Abstract Speleothems can be precisely dated with the Th/U method. Climate variations are<br />
recorded in the δ 18 O and δ 13 C of their calcium carbonate. We are developing models to evaluate<br />
drip rates (and other parameters) at the time of growth from the isotopic enrichment of δ 13 C from<br />
the stable isotope records of close-by stalagmites.<br />
1200<br />
1000<br />
Tropfabstand dT [s]<br />
800<br />
600<br />
400<br />
200<br />
T: 6.5<br />
Ma2<br />
0<br />
0 0.5 1 1.5 2 2.5<br />
Alter [ka]<br />
3 3.5 4 4.5<br />
Figure 6.4: Drip rate of stalagmites from Chile calculated by the I model.<br />
Background The isotopic composition of stalagmites<br />
growing under kinetic conditions has<br />
barely been interpretable. Only under equilibrium<br />
formation a temperature signal of δ 18 O could<br />
be deduced. Understanding of the process of kinetic<br />
fractionation, would deliver information on<br />
the drip rate and, therefore, precipitation.<br />
Funding Diplomarbeit, therefore ”not applicable”<br />
Methods and results Drip rate, cave temperature,<br />
calcium concentration, the isotopic composition<br />
of the drop as well as mixing parameters<br />
affect the stable isotope composition of<br />
speleothems.<br />
Three different models were developed to determine<br />
past drip rates. And the sensitivity to these<br />
parameters was tested.<br />
A-Model The age-height-model is based upon<br />
the considerations of W. Dreybrodt [1999] and G.<br />
Kaufmann [2003]. Through a comparison of ages<br />
and heights of different growth layers, drip rates,<br />
calcium concentration and mixing parameter can<br />
be obtained. Hence, the outer form of a stalagmite<br />
can be modeled by given parameters.<br />
I-Model The isotopic model is based on isotopic<br />
enrichment of δ 13 C along the growth axis of<br />
Ma1<br />
a stalagmite due to kinetic fractionation. By comparing<br />
the intersections of modeled drip rate and<br />
isotopic curves of two close-by stalagmites, drip<br />
rates, the isotopic composition of the drop and the<br />
mixing parameter can be determined. Calibrating<br />
the A-Model with these results yields more<br />
information about the calcium concentration of<br />
the drop. This has been done for two close-by<br />
stalagmites from a cave in South Chile.<br />
H-Model The Hendy-Model uses measured<br />
Hendy tests to determine drip rates more accurately.<br />
It is similar to the I-Model, but it is coupled<br />
with an additional box model. Using isotopic<br />
fractionation, one can obtain the range of<br />
drip rate and temperature from the isotopic enrichment<br />
along a growth layer. The correlation<br />
between the drip rate and ∆δ 18 O/∆δ 13 C was constructed.<br />
Outlook/Future work Aim of this work is to<br />
correct for the kinetic effect using the slope of<br />
∆δ 18 O/∆δ 13 C and to determine temperatures in<br />
the cave from the δ 18 O signals of speleothems.<br />
These models are used in the DFG-Project<br />
Forschergruppe 668 (www.FG-daphne.de).<br />
Main publication in preparation
196 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.6 Reconstruction of the 10 Be-production based on deep sea sediments<br />
from the North Atlantic<br />
Participating scientist Boris Schulze, M. Christl, F. Bernsdorff, A. Mangini, D. Wagenbach, P.<br />
W. Kubik (Zürich)<br />
Abstract The 10 Be-production is inversely related with the Earth‘s magnetic field strength. A<br />
highly resolved record of 10 Be-production is produced based on highly accumulating deep sea sediments<br />
from Bermuda Rise. The data support the idea of using 10 Be as a global matching-tool and as<br />
a proxy for geomagnetic paleointensity.<br />
Figure 6.5: 10 Be deposition rate, transport corrected by 230 Th-normalization. Compared are data from<br />
ODP Sites 1063 (North Atlantik; red) and 1089 (South Atlantic; blue).<br />
Background Cosmogenic 10 Be is produced by<br />
the interaction of galactic cosmic rays with oxygen<br />
and nitrogen atoms in the upper atmosphere<br />
of the Earth. Thus, 10 Be-production is inversely<br />
related with the Earth‘s magnetic field strength.<br />
After different processes of transport, the variations<br />
of the 10 Be-production eventually are conserved<br />
as varying 10 Be-deposition fluxes in different<br />
archives (ice cores, marine and terrestrial<br />
sediments). Knowing the past production rate<br />
of 10 Be, it should be possible to synchronize<br />
chronologies of different archives by comparison<br />
of the reconstructed 10 Be-deposition fluxes.<br />
Funding DFG Schwerpunktprogramm: Antarktisforschung<br />
mit vergleichenden Untersuchungen<br />
in arktischen Gebieten (SPP 1158)<br />
Methods and results A high-resolution record<br />
of 10 Be-production is produced based on highly<br />
accumulating deep sea sediments from Bermuda<br />
Rise (ODP Site 1063). To correct for marine<br />
transport signals, the 230 T hexcess normalisation<br />
technique is applied. The 10 Be -concentration<br />
(measured at the ETH-Zürich) and the activity of<br />
Th/U-isotopes (by alpha-spectroscopy) were determined<br />
in sediments of the past 100 kyr. The<br />
comparison of the 230 T h-normalized 10 Be-flux at<br />
Site 1063 with other records ( 10 Be-fluxes, atmospheric<br />
∆ 14 C, and paleointensity) revealed a very<br />
good interhemispheric correlation. Thus, the results<br />
of this work strongly support the idea of using<br />
10 Be as a global matching-tool for the synchronisation<br />
of marine, terrestrial, and ice-core<br />
chronologies and as a proxy for geomagnetic paleointensity.<br />
Outlook/Future work The 10 Be and U/Thdataset<br />
of the deep sea sediments from ODP Site<br />
1063 will be further expanded and compared to<br />
the data from ODP Sites 983 (North Atlantic) and<br />
1089 (South Atlantic).<br />
Main publication Schulze [2005]; Christl et al.<br />
[2005]
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 197<br />
6.1.7 U/Th dating of deep-water corals from the North Atlantic<br />
Participating scientist Andrea Schröder-Ritzrau, A. Mangini, A. Freiwald (Tübingen), G. Hoffman<br />
(Zürich)<br />
Abstract Coupled uranium-series and radiocarbon measurements on deep-water corals are a proxy<br />
to estimate intermediate water ages. 17 intermediate water ages were estimated on deep-water corals<br />
from the eastern North Atlantic. These data give strong evidence for periodic reduced ventilation in<br />
the North Atlantic during the LGM/Holocene transition.<br />
600<br />
400<br />
� 14 C ‰<br />
200<br />
0<br />
� C Cariaco Basin; Hughen et al. 2004<br />
14<br />
� 14<br />
C model/atm; Laj et al. 2002<br />
� 14<br />
C atm INTCAL; Reimer et al. 2004<br />
� 14<br />
C marin INTCAL; Hughen et al. 2004<br />
-200<br />
0 4000 8000 12000 16000 20000 24000<br />
age (years BP)<br />
Figure 6.6: ∆ 14 Cintermediate water (red data points) compared to various ∆ 14 C records and models (see<br />
references in the Fig.). Data are plotted without error bars for clarity - except for the deep-water coral<br />
data.<br />
Background Thermohaline circulation in the<br />
world ocean has a major influence on climate.<br />
Hence, changes of thermohaline circulation and<br />
water mass distribution especially in the North<br />
Atlantic during climate transitions are of major<br />
interest for paleoceanographic and climatic reconstructions.<br />
It is suggested that at terminations<br />
the intermediate water has a larger component of<br />
poorly ventilated SSW (Southern Source Water)<br />
compared to interglacials and full glacials.<br />
The 14 C/ 12 C ratio of dissolved inorganic carbon<br />
is a powerful tracer for reconstructing the<br />
pathways of deep- and intermediate water in the<br />
ocean. Coupled AMS- 14 C- and Th/U- (TIMS)<br />
measurements on coral carbonate, deliver a snapshot<br />
of the 14 C-concentration of deep- or intermediate<br />
water at the time and place the coral lived<br />
[Mangini et al. 1998].<br />
Funding DFG and EU<br />
Methods and results Intermediate water ages<br />
were calculated via the method of 14 C projection<br />
ages [Adkins and Boyle, 1997]. Radiocarbon<br />
dates (measured at the ETH-Zurich and at<br />
the Leibniz-Laboratory in Kiel) and uranium series<br />
ages (via TIMS in HD) were used to calculate<br />
the ∆ 14 Cintermediate water of the former sur-<br />
rounding intermediate water the coral lived in.<br />
Assuming closed system radiocarbon decay and<br />
no further exchange with atmospheric radiocarbon,<br />
the calculated ∆ 14 Cintermediate water of the<br />
coral (Fig. 6.6) can be backtracked to the crossover-point<br />
with the (∆ 14 C past/atm) [Reimer et al.,<br />
2004]. This ratio (∆ 14 C past/coral) is the ratio of<br />
the water that had equilibrated with the past atmosphere.<br />
This value was applied in the equation<br />
for the ventilation age [Mangini et al., 1998] where<br />
non-reservoir-corrected ventilation ages (intermediate<br />
water ages) are determined.<br />
A total of 69 deep-water corals were investigated<br />
and 17 intermediate water ages were calculated.<br />
Our data document short periods of reduced conveyor<br />
circulation associated with increasing influence<br />
of SSW at intermediate water depth at the<br />
end of Heinrich I and the end of the Younger Dryas<br />
event. These periods are associated with meltwater<br />
discharge (MPIA and B). A similar event in<br />
the early Holocene has to be verified.<br />
Outlook/Future work none in this case, the<br />
project is finished<br />
Main publication Schröder-Ritzrau et al.<br />
[2003]; Schröder-Ritzrau et al. [2005]
198 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.8 Isochron dating of fossil reef corals and the reconstruction of past<br />
sea level fluctuations<br />
Participating scientist Denis Scholz, A. Mangini, K. Bohn, T. Felis (Bremen), D. Meischner<br />
(Göttingen)<br />
Abstract We developed an isochron dating approach that enables to derive reliable ages for fossil<br />
reef corals that cannot be dated by the conventional Th/U-method. Isochron dating was applied to<br />
Porites corals from Aqaba and Baja California. In addition, we reconstructed magnitude,timing, and<br />
duration of the Marine Isotope Substage (MIS) 6.5 ( 175,000 years before present) sea level peak by<br />
U-series dating of fossil Acropora palmata corals from Barbados.<br />
Figure 6.7: Isochron dating of coral AQB 3A from<br />
Aqaba. The isochron age is calculated from the intersection<br />
point, the age error is estimated from<br />
the intersection points of the confidence bands.<br />
Background Reconstructions of past sea level<br />
fluctuations allow to determine the magnitude,<br />
timing and duration of glacial/interglacial periods.<br />
This is essential for the understanding of the<br />
causal relationships and the complex interplay between<br />
the forcing and feedback mechanisms in the<br />
climate system.<br />
Some reef coral genera grow in upper 5m below<br />
sea surface only and record past sea level fluctuations.<br />
Thus, the determination of accurate<br />
U-series ages provides a direct method for sea<br />
level reconstruction. Unfortunately, many fossil<br />
reef corals show elevated ( 234 U/ 238 U) activity ratios<br />
which are clear evidence for post-depositional<br />
open-system behaviour. Therefore, conventional<br />
Th/U-ages obtained from such corals cannot be<br />
considered as strictly reliable. There are two possibilities<br />
to deal with this problem: (i) to identify<br />
corals that have not been altered and (ii)<br />
to develop and apply appropriate correction techniques.<br />
Funding BMBF (DEKLIM project)<br />
Methods and results We analysed five fossil<br />
Porites corals from Aqaba, Jordan, by<br />
thermal ionisation mass spectrometry (TIMS).<br />
( 234 U/ 238 U) and ( 230 T h/ 238 U) activity ratios of<br />
Figure 6.8: Sea level reconstruction for MIS 6.5.<br />
Black squares are our coral data from Barbados.<br />
Red and yellow symbols are coral data from other<br />
studies, straight curves are based on oxygen isotopes.<br />
different sub-samples from one coral specimen<br />
show a high linear correlation (Fig. 6.7). This<br />
can be explained by a model assuming different<br />
degree of U addition and subsequent loss for different<br />
sub-samples. The model predicts that the<br />
true coral age can be calculated from the intersection<br />
point of the isochron with the seawater<br />
evolution curve (Fig. 6.7). Isochron dating was<br />
also successfully applied to corals from Baja California,<br />
Mexico [Bohn, 2005].<br />
Detailed investigation of Acropora palmata corals<br />
from Barbados, West Indies, showed that<br />
these corals suffered U-redistribution [Scholz and<br />
Mangini, in press]. Thus, isochron dating cannot<br />
be applied. Careful selection of reliable Th/Uages<br />
by application of strict reliability criteria<br />
suggests that MIS 6.5 sea level ranged from -<br />
50±11 to -47±11 m relative to present sea level<br />
between 176,100±2,800 and 168,900±1,400 years<br />
before present (Fig. 6.8). At present, this reconstruction<br />
is one of the most accurate for MIS 6.5.<br />
Outlook/Future work publication of results<br />
Main publication Scholz et al. [2004], Felis et<br />
al. [2004], Scholz [2005], Bohn [2005], Scholz and<br />
Mangini [in press]
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 199<br />
6.1.9 Dating and interpretation of the carbon and oxygen isotopes of two<br />
Holocene stalagmites from the South of Chile (Patagonia)<br />
Participating scientist Daniel Schimpf, C. Mühlinghaus, D. Scholz, A. Schröder-Ritzrau, A.<br />
Mangini, R. Kilian (Trier), C. Spötl (Innsbruck)<br />
Abstract Two Holocene stalagmites (MA-1 and MA-2) from the Marcelo-Arevalo cave, which is<br />
located in the South of Chile (53 ◦ S) in the vicinity of the Pacific coast, were dated with the 230 T h/ 234 U<br />
method and analyzed with respect to their oxygen and carbon isotopes. We find that the Westwind<br />
drift, which controls precipitation, is strongly influenced by the El Nino Southern Oscillation.<br />
age (ka BP)<br />
5<br />
4<br />
3<br />
2<br />
1<br />
Stalagmite MA-1<br />
Akima fit<br />
0<br />
0 50 100 150 200 250<br />
distance from top (mm)<br />
Background For the first time stalagmites<br />
from a cave of the southernmost Andes were analyzed<br />
at high resolution. The intensity of precipitation<br />
at this location reflects the shifts of the<br />
position of the Westwind drift.<br />
Funding Diploma thesis, therefore not applicable.<br />
Methods and results The 230 T h/ 234 U dating<br />
method was used to establish a depth-age model<br />
for the two stalagmites (MA-1 and MA-2). The<br />
measurements were performed with a Thermal<br />
Ionization Mass Spectrometer (TIMS). Figure 6.9<br />
shows the depth-age model for stalagmite MA-1<br />
including all reliable data points. An Akima fit<br />
was implemented to get a continuous depth-age<br />
Figure 6.9: Depth-age model of stalagmite MA-1.<br />
relation. It shows an almost linear relation between<br />
age and depth.<br />
The comparison of the dated δ 13 C and δ 18 O profiles<br />
with a record of the ENSO intensity, derived<br />
from a sediment record off the coast of Peru, reveals<br />
that the ENSO strongly influenced the intensity<br />
of precipitation, probably causing North-<br />
South-shifts of the Southern Westerlies.<br />
Outlook/Future work Further stalagmites<br />
from the Marcelo-Arevalo cave will be analysed.<br />
The stable isotope profiles are modeled by C.<br />
Mühlinghaus. We have applied for a DFG -<br />
Project to continue this study.<br />
Main publication Schimpf [2005]
200 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.10 Chronostratigraphy of the Nasca culture and palaeoclimate reconstruction<br />
of the Palpa region (Peru) by AMS- 14 C dating<br />
Participating scientist Ingmar Unkel, B. Kromer, G. Wagner, B. Eitel, L. Wacker (Zürich)<br />
Abstract Research on the enigmatic Nasca culture in South-Peru is driven by two major questions:<br />
when did the Nasca people live, and did changing climate have an influence on the rise and fall of this<br />
Pre-Columbian civilisation? AMS- 14 C-dating and investigations in an multi-disciplinary project help<br />
to get the first answers.<br />
Figure 6.10: (left) Preparation line for AMS- 14 C-targets built at the IUP during this project. (right)<br />
A trapezoid, one of the famous Nasca-geoglyphs, in the research area near Palpa (S-Peru).<br />
Background The chronology of the Nasca culture,<br />
which created the world famous geoglyphs<br />
(giant diagrams etched into the desert ground)<br />
and spanning from approximately 200 BC to 600<br />
AD, in the plain between the Peruvian Andes and<br />
the Pacific Ocean, is presently based almost exclusively<br />
on a ceramic typology without any extensive<br />
chronometric dating. An absolute chronology<br />
of this culture had to be created via radiocarbon<br />
dating on organic samples from settlement and<br />
tomb relics as well as on organic material derived<br />
from geoglyph sites in the Nasca/Palpa region.<br />
Furthermore, the question is under investigation,<br />
if changing climate had influence on the rise and<br />
fall of the Pre-Columbian cultures in South-Peru.<br />
Funding BMBF focus programme ”New technologies<br />
in humanities”, project No. 03WAX3VP<br />
- title: ”Nasca: development and adaptation of<br />
archaeometric techniques for the investigation of<br />
the cultural history of the Palpa region, S-Peru”<br />
Methods and results The main focus of the<br />
archaeological investigations was on the Nascaperiod<br />
settlement centres near Palpa, Los Molinos<br />
und La Mua. In co-operation with the geomorphological<br />
investigations within the parent<br />
project, palaeoclimatic reconstruction of the re-<br />
spective region was undertaken. The material to<br />
be dated consisted mainly of loess molluscs and<br />
charred plant remains, sampled from river terraces<br />
and debris flows which originated in more humid<br />
phases in this presently hyper-arid area.<br />
During the course of the project a semi-automated<br />
AMS-target preparation line was built in the<br />
radiocarbon laboratory. Using AMS (Accelerator<br />
Mass Spectrometry), dating of extremely<br />
small amounts of archaeological material is possible.<br />
For the first time in Peruvian archaeology<br />
straw fragments found within adobes (clay<br />
bricks), which do not provide a sufficient amount<br />
of material for conventional measurement, have<br />
been dated.<br />
The dating of the samples appears to confirm so<br />
far the archaeological timeframe of the Nasca culture.<br />
The chronology will be completed and statistically<br />
analysed towards the end of this year.<br />
Some surprising new evidence of climate change<br />
has been found in the studies of the river sediments,<br />
showing a pronounced wet phase from 15 th<br />
to 17 th century in that region. The analysis is still<br />
in progress.<br />
Outlook/Future work none in this case<br />
Main publication in preparation
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 201<br />
6.1.11 Nonlinear time-series analysis of nonstationary signals<br />
Participating scientists Pablo Verdes, A. Mangini<br />
Abstract The purpose of my research is to develop new tools for the analysis of nonstationary<br />
complex systems. I explore them using a natural decomposition into intrinsic dynamics and external<br />
component, using a previously developed technique to estimate the latter from measured data. In<br />
particular, I investigate how modeling and forecasting can be improved in this framework.<br />
Background One of the main goals of Physics<br />
has always been prediction. The most satisfactory<br />
situation arises when the system of interest<br />
can be completely understood and modeled from<br />
first principles, so that its equations of motion<br />
can be derived and solved for all times. However,<br />
real-world dynamical systems have often so many<br />
degrees of freedom that the traditional approach<br />
proves intractable. In such a case, an alternative<br />
path is to measure the evolution of any given<br />
system property by recording time series, which<br />
are a set of observations collected at regular intervals<br />
of time, and then recurr to the theory of<br />
time-series analysis. The vast literature on this<br />
subject mostly rely on the condition of stationarity,<br />
because a solid mathematical foundation can<br />
be built in this case. As a result, nonstationary<br />
time-series analysis is an almost unexplored<br />
branch of science. However, the stationarity condition<br />
is very stringent because most real-world<br />
time series have some degree of nonstationarity<br />
due to external perturbations acting on the observed<br />
system.<br />
Funding Alexander von Humboldt postdoctoral<br />
fellowship.<br />
Methods and results I have investigated the<br />
problem of modeling and forecasting of nonstationary<br />
time series. More precisely, I have studied<br />
an over-embedding method that constitutes a general<br />
framework for modeling nonstationary systems,<br />
basically enlarging the standard time-delay<br />
embedding space by inclusion of the unknown slow<br />
driving signal. I have developed a variant in which<br />
this external driving force can be estimated simultaneously<br />
with the intrinsic stationary dynamics.<br />
This method is general and can be implemented<br />
with any modeling tool; using in particular artificial<br />
neural networks, I have found that it is highly<br />
efficient both on synthetic and real-world time series.<br />
In particular, in noiseless artificial cases this<br />
approach is more than one order of magnitude<br />
better than the second best method. As a realworld<br />
application, I have considered the problem<br />
of modeling the sunspot number record. In this<br />
case a 30% error reduction was obtained, which is<br />
a remarkable number within the vast literature on<br />
this benchmark, particularly for an already very<br />
competitive modeling methodology like ensembles<br />
of artificial neural networks. In the case of nstep-ahead<br />
predictions, this approach also leads<br />
to much more accurate results and longer prediction<br />
horizons than other existing overembedding<br />
methods in the literature.<br />
We have also studied a time series of temperatures<br />
in the Central Alps during the past 2000 years reconstructed<br />
from a δ 18 O stalagmite record. The<br />
isotopic composition of this stalagmite could be<br />
precisely dated and translated into a highlyresolved<br />
record of temperature during the last 2<br />
millenia. The variability of this time series was<br />
analysed and compared to other reconstructions<br />
of past temperatures in the literature, and the role<br />
of the solar signal as a possible driver of its dynamics<br />
was assessed in comparison with carbon<br />
dioxide. The fractions of temperature variance<br />
that are explained by each of these forcing factors<br />
were analysed in a nonlinear framework, by studying<br />
the relevance of the solar and greenhouse gas<br />
inputs in a feed-forward neural network model of<br />
the temperature behaviour.<br />
I have also participated in a time series prediction<br />
competition organised by the International Joint<br />
Conference on Neural Networks. The goal of this<br />
competition was to provide a new benchmark for<br />
the problem of time series prediction and to compare<br />
the different methods or models that can be<br />
used for the prediction. An artificial time series<br />
with 5000 data was given and, within those, 100<br />
values were missing and had to be predicted. Selected<br />
papers were considered for publication in<br />
Neurocomputing.<br />
Main publications Verdes et al. [pub.];<br />
Mangini et al. [2005]; Verdes et al. [in press]
202 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
6.1.12 The authigenic 10 Be/ 9 Be ratio in deep sea sediments as a proxy for<br />
the Earth‘s magnetic field intensity<br />
Participating scientists Patrick Wenderoth, M. Christl, F. Bernsdorff, A. Mangini, P. Kubik<br />
(Zürich)<br />
Abstract We tested if the authigenic 10 Be/ 9 Be ratio in deep sea sediments could be used for the<br />
reconstruction of the relative Earth’s magnetic field.<br />
Reconstruction of the relative Earth’s magnetic field strength for the last 580 ka<br />
relative Earth magnetic field,<br />
determined with 10 Be Titan corrected / 9 Be(auth.)/g sed<br />
from 10 Be Titancorrected / 9 Be(auth.)/g sed<br />
Relative Paleointensity from Sint800<br />
2,5<br />
2,0<br />
1,5<br />
1,0<br />
0,5<br />
0,0<br />
1 2 3 4 5 6 7 8<br />
Relative Paleointensity<br />
1,4<br />
1,2<br />
1,0<br />
0,8<br />
0,6<br />
0,4<br />
9 10 11 12 13 14 15 16 0,2<br />
0 0 100 200 200 300 400 400 500 600<br />
600<br />
Age (ka)<br />
Figure 6.11: The Relative Earth’s magnetic field, determined with 10 BeT itan corrected/ 9 Be(auth.)/gsed<br />
(blue curve) compared with the relative intensity derived from paleomagnetic data (SINT 800), (black<br />
curve).<br />
Background The production rate of the radionuclide<br />
10 Be in the stratosphere, induced by<br />
interaction of cosmic rays with atmospheric O<br />
and N, depends on the intensity of the Earth’s<br />
magnetic field. The production rate of 10 Be increases<br />
when the Earth’s magnetic field strength<br />
decreases and vice versa. Therefore, the 10 Beflux<br />
in the deep sea sediments is a proxy for the<br />
longterm variation of the relative Earth’s magnetic<br />
field. However, the 10 Be-flux into sediments<br />
has to be normalized with 230 T h to account for<br />
processes that redistribute the sediments on the<br />
sea floor. This normalization is limited to the last<br />
350 ky. Here, a new method was investigated,<br />
based on the normalization to the stable isotope<br />
9 Be. The 10 Be/ 9 Be ratio depends only on the<br />
half life of 10 Be (1.5 Ma). Deep sea sediments<br />
have a detritic and an authigenic (i.e sea water signature)<br />
component. Both 10 Be and 9 Be detritic<br />
fluxes may be influenced by climate [McHargue et<br />
al., 2005], whereas the normalization of 10 Be on<br />
authigenic 9 Be is not.<br />
Funding Diplomathesis, non in this case.<br />
1,6<br />
Methods and results In this study a procedure<br />
based on sequential extraction steps was developed<br />
to separate the authigenic and the terrigenous<br />
components of sediments from ODP Leg<br />
177 Site 1089. In addition, Ti in the authigenic<br />
fraction was measured to quantify the amount of<br />
extracted detritic fraction.<br />
The 10 Be-flux normalized to the 10 Be/ 9 Be ratio<br />
was compared with that derived from the 230 T h<br />
normalization. Best matching was obtained when<br />
the 10 Be-flux was normalized to authigenic 9 Be<br />
and additionally using a ”Ti-correction”. The<br />
magnetic field reconstruction determined by the<br />
”Ti corrected” authigenic 10 Be/ 9 Be ratio correlates<br />
well with the record from paleomagnetic data<br />
(SINT 800) for the last 580ka (Fig. 6.11). Furthermore,<br />
we could show that the signal of paleomagnetic<br />
intensity of Site 1089 is partially an artifact<br />
of supply of terrigenuos material and, therefore,<br />
not as appropriate as the 10 Be-flux for reconstructing<br />
the Earth’s magnetic field<br />
Main publication Wenderoth [2005]
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 203<br />
References<br />
Adkins, J.F., & Boyle, E.A. 1997. Changing atmospheric ∆ 14 C and the record of deep water paleoventilation<br />
ages. Paleoceanography, 12(3), 337–344.<br />
Beer, J., Mende, W., & Stellmacher, R. 2000. The role of the sun in climate forcing. Quaternary<br />
Science Reviews, 19, 403–415.<br />
Bohn, K. 2005. Datierung von fossilen Riffkorallen aus Baja California mit der 230 Th/ 234 U-Methode.<br />
unpublished Master Thesis, University of Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />
Bond, G., Kromer, B., Beer, J., Muscheler, R., Evans, M.N., Showers, W., Hoffmann, S., Lotti Bond,<br />
R., Hajdas, I., & Bonani, G. 2001. Persistent solar influence on North Atlantic climate during the<br />
Holocene. Science, 294(5549).<br />
Braun, H. in press. Possible solar origin of the glacial 1,470-year climate cycle demonstrated in a<br />
coupled model. Nature.<br />
Burns, S.J., Fleitmann, D., Mudelsee, M., Neff, U., Matter, A., & Mangini, A. 2002. A 780-year<br />
annually resolved record of Indian Ocean monsoon precipitation from a speleothem from south<br />
Oman. Journal of Geophysical Research, 107(D20), doi:10.1029/2001JD001281.<br />
Christl, M., Mangini, A., Holzkämper, S., & Spötl, C. 2004. Evidence for a link between the flux<br />
of galactic cosmic rays and Earths climate during the past 200,000 years. J. Atmospheric and<br />
Solar-Terrestrial Physics, 66, 313–322.<br />
Christl, M., Schulze, B., Wenderothr, P., Bernsdorff, F., & Mangini, A. 2005. Geomagnetic variability<br />
over the past 300,000 years from cosmogenic beryllium-10 in deep-sea sediments - a potential global<br />
matching tool. 22. Internationale Polartagung, 18.24.09.2005, Poster.<br />
Dreybrodt, W. 1999. Chemical kinetics, speleothem growth and climate. Boreas, 28, 347–356.<br />
Eddy, J. 1976. The mounder minimum. Science, 192, 1189–1202.<br />
Eitel, B., Hecht, S., Mächtle, B., Schukraft, G., Kadereit, A., Wagner, G.A., Kromer, B., Unkel, I., &<br />
Reindel, M. 2005. Geoarchaeological evidence from desert loess in the Nazca/Palpa region, Southern<br />
Peru: Palaeoenvironmental changes and their impact on Pre-Columbian cultures. Archaeometry,<br />
47(1), 137–158.<br />
Felis, T., Lohmann, G., Kuhnert, H., Lorenz, S.J., Scholz, D., Pätzold, J., Al Rousan, S.A., & Al<br />
Moghrabi, S.M. 2004. Increased seasonality in Middle East temperatures during the last interglacial<br />
period. Nature, 429, 164–168.<br />
Fleitmann, D., Burns, S.J., Mudelsee, M., Neff, U., Kramers, J., Mangini, A., & Matter, A. 2003.<br />
Holocene Forcing of the Indian Monsoon Recorded in a Stalagmite from Southern Oman. Science,<br />
300(5626), 1737–1739.<br />
Fleitmann, D., Burns, S.J., Neff, U., Mudelsee, M., Mangini, A., & Matter, A. 2004. Palaeoclimatic interpretation<br />
of high-resolution oxygen isotope profiles derived from annually laminated speleothems<br />
from Southern Oman. Quaternary Science Reviews, 23, 935–945.<br />
Friedrich, M., Remmele, S., Kromer, B., Hofmann, J., Spurk, M., Kaiser, K.F., Orcel, C., & Küppers,<br />
M. 2004. The 12,460-Year Hohenheim Oak and Pine Tree-Ring Chronology from Central Europe<br />
- a Unique Annual Record for Radiocarbon Calibration and Paleoenvironment Reconstructions.<br />
Radiocarbon, 46(3), 1111–1122.<br />
Ganopolski, A., & Rahmstorf, S. 2001. Rapid changes of glacial climate simulated in a coupled climate<br />
model. Nature, 409, 153–158.<br />
Ganopolski, A., & Rahmstorf, S. 2002. Abrupt glacial climate changes due to stochastic resonance.<br />
Physical Review Letters, 88(3), 038501.<br />
Hodell, D.A., Brenner, M., Curtis, J.H., & Guilderson, T. 2001. Solar Forcing of Drought Frequency<br />
in the Maya Lowlands. Science, 292, 1367–1370.<br />
Holzkämper, S., Mangini, A., Spötl, C., & Mudelsee, M. 2004. Timing and progression of the Last<br />
Interglacial derived from a high alpine stalagmite. Geophysical Research Letters, 31(L07201), 1–4.
204 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
Holzkämper, S., Spötl, C., & Mangini, A. 2005. High-precision constrains on timing of Alpine warm<br />
periods during the middle to late Pleistocene using speleothem growth. Earth and Planetary Science<br />
Letters, 236, 751–764.<br />
Hughen, K., Lehman, S., Southon, J., Overpeck, J., Marchal, O., & Herring, C. 2004a. 14C activity<br />
and Global Carbon Cycle changes over the last 50,000 years. Science, 303, 202–207.<br />
Hughen, K.A., Baillie, M.G.L., Bard, E., Beck, J.W., Bertrand, C.J.H., J.H., Chanda, Blackwell, P.G.,<br />
Buck, C.E., Burr, G.S., Cutler, K.B., Damon, P.E., Edwards, R.L., Fairbanks, R.G., Richard, G.,<br />
Friedrich, M., Guilderson, T.P., Kromer, B., McCormac, G., Manning, S., Ramsey, C.B., Reimer,<br />
P.J., Reimer, R.W., Remmele, S., Southon, J.R., Stuiver, M, Talamo, S., Taylor, F.W., van der<br />
Plicht, J., & Weyhenmeyer, C.E. 2004b. Marine04 Marine Radiocarbon Age Calibration, 0-26 Cal<br />
Kyr BP. Radiocarbon, 46(3), 1059–1086.<br />
Kaufmann, G. 2003. Stalagmite Growth and palaeo-climate: the numerical perspective. Earth and<br />
Planetary Science Letters, 214, 251–266.<br />
Kromer, B., Korfmann, M., & Jablonka, P. 2002. Heidelberg radiocarbon dates for Troia I to VIII<br />
and Kumtepe. Pages 43–54 of: Wagner, G. (ed), Troia and the Troad. Heidelberg: Springer.<br />
Kromer, B., Friedrich, M., Hughen, K.A., Kaiser, F., Remmele, S., Schaub, M., & Talamo, S. 2004.<br />
Late Glacial 14C ages from a floating 1382-ring pine chronology. Radiocarbon, 46(3), 1203–1209.<br />
Labitzke, K., & Loon, H. 1992. Association between the 11-Year Solar Cycle and the Atmosphere.<br />
Part V: Summer. Journal of Climate, 5, 240–251.<br />
Laj, C., Kissel, C., Mazaud, A., Michel, E., Muscheler, R., & Beer, J. 2002. Geomagnetic field<br />
intensity, North Atlantic Deep Water circulation and atmospheric ∆ 14 C during the last 50kyr.<br />
Earth and Planetary Science Letters, 200, 177–190.<br />
Levin, I., & Kromer, B. 2004. The tropospheric 14 CO2 level in Mid-Latitudes of the Northern Hemisphere<br />
(1959-2003). Radiocarbon, 46(3), 1261–1272.<br />
Mangini, A., Lomitschka, M., Eichstädter, R., Frank, N., Vogler, S., Bonani, G., Hajdas, I., & Pätzold,<br />
J. 1998. Coral provides way to age deep water. Nature, 392, 347–348.<br />
Mangini, A., Spötl, C., & Verdes, P.F. 2005. Reconstruction of temperature in the Central Alps<br />
during the past 2,000 years from a δ 18 O stalagmite record. Earth and Planetary Science Letters,<br />
235, 741–751.<br />
Manning, S.W., Kromer, B., Kuniholm, P.I., & Newton, M.W. 2001. Anatolian tree-rings and a new<br />
chronology for the east Mediterranean Bronze-Iron Ages. Science, 295, 2532–2535.<br />
Manning, S.W., Kromer, B., Kuniholm, P.I., & Newton, M.W. 2003. Confirmation of near-absolute<br />
dating of east Mediterranean Bronze-Iron Dendrochronology. Antiquity, 77, 295.<br />
McHargue, L.R., & Donahue, D.J. 2005. Effects of climate and the cosmic-ray flux on the 10 Be content<br />
of marine sediment. Earth and Planetary Science Letters, 232, 193–207.<br />
McManus, J.F., Francois, R., Keigwin, L.D., & Brown Leger, S. 2004. Collapse and rapid resumption<br />
of Atlantic meridional circulation linked to deglacial climate changes. Nature, 428, 834–837.<br />
Neff, U., Burns, S.J., Mangini, A., Mudelsee, M., Fleitmann, D., & Matter, A. 2001. Strong coherence<br />
between solar variability and the monsoon. Nature, 411, 290–293.<br />
Ney, E.P. 1959. Cosmic radiation and weather. Nature, 183, 451.<br />
Niggemann, S., Mangini, A., Mudelsee, M., Richter, D.K., & Wurth, G. 2003. Sub-Milankovitch<br />
climatic cycles in Holocene stalagmites from Sauerland, Germany. Earth and Planetary Science<br />
Letters, 6844, 1–9.<br />
Peristykh, A.N., & Damon, P.E. 2003. Persistence of the Gleissberg 88-year solar cycle over the last<br />
12,000 years: Evidence from cosmogenic isotopes. Journal of Geophysical Research, 108(A1), 1003,<br />
doi:10.1029/2002JA009390.
6.1. RADIOMETRIC DATING OF WATER AND SEDIMENTS 205<br />
Reimer, P.J., Baillie, M.G.L., Bard, E., Bayliss, A., Beck, J.W., Bertrand, C.J.H., Blackwell, P.G.,<br />
Buck, C.E., Burr, G.S., Cutler, K.B., Damon, P.E., Edwards, R.L., Fairbanks, R.G., Friedrich, M.,<br />
Guilderson, T.P., Hogg, A.G., Hughen, K.A., Kromer, B., McCormac, G., Manning, S., Ramsey,<br />
C.B., Reimer, R.W., Remmele, S., Southon, J.R., Stuiver, M., Talamo, S., Taylor, F.W., van der<br />
Plicht, J., & Weyhenmeyer, C.E. 2004. INTCAL04 terrestrial radiocarbon age calibration, 0-26 cal<br />
kyr BP. Radiocarbon, 46(3), 1029–1058.<br />
Schaub, M., Kaiser, K.F., Kromer, B., & Talamo, S. 2005. Extension of the Swiss Lateglacial tree-ring<br />
chronologies. Dendrochronologia, doi:10.1016.<br />
Schimpf, D. 2005. Datierung und Interpretation der Kohlenstoff- und Sauerstoffisotopie zweier<br />
holozäner Stalagmiten aus dem Süden Chiles (Patagonien). unpublished Master Thesis, University<br />
of Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />
Scholz, D. 2005. U-series dating of diagenetically altered fossil reef corals and the application for sea<br />
level reconstruction. unpublished PhD Thesis, University of Heidelberg, Heidelberger Akademie der<br />
Wissenschaften.<br />
Scholz, D., & Mangini, A. in press. U-redistribution in fossil reef corals from Barbados, West Indies,<br />
and sea level reconstruction for MIS 6.5. In: Sirocko, F., Litt, T., Claussen, M., & Sanchez Goni,<br />
M.-F. (eds), The climate of past interglacials.<br />
Scholz, D., Mangini, A., & Felis, T. 2004. U-series dating of diagenetically altered fossil reef corals.<br />
Earth and Planetary Science Letters, 218, 163–178.<br />
Schröder Ritzrau, A., Lomitschka, M., & Mangini, A. 2003. Deep-sea corals evidence periodic reduced<br />
ventilation in the North Atlantic during LGM/Holocene transition. Earth and Planetary Science<br />
Letters, 216, 399–410.<br />
Schröder Ritzrau, A., Freiwald, A., & Mangini, A. 2005. U/Th dating of deep-water corals from the<br />
eastern North Atlantic and the western Mediterranean Sea. In: Freiwald, A., & Roberts, J.M.<br />
(eds), Cold-water corals and ecosystems. Berlin Heidelberg: Springer-Verlag.<br />
Schulze, B. 2005. Hochaufgelöste Rekonstruktion der 10Be-Produktionsrate aus Tiefseesedimentkernen<br />
des Bermuda Rise über die letzten 70.000 Jahre. unpublished Master Thesis, University of<br />
Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />
Solanski, S.K., Usoskin, I.G., Kromer, B., Schüssler, M., & Beer, J. 2004. Unsusual activity of the<br />
sun during recent decades compared to the previous 11,000 years. Nature, 431, 1084–1087.<br />
Soon, W.H., Posmentier, E.S., & Baliunas, S.L. 2000. Climate hypersensitivity to solar forcing?<br />
Annales Geophysicae, 18, 583–588.<br />
Spötl, C., Mangini, A., Burns, S.J., Frank, N., & Pavuza, R. 2004. Speleothems from high alpine<br />
Spannagel Cave, Zillertal Alps (Austria). Page 329 of: Sasowsky, I., & MyIroie, J. (eds), Studies of<br />
Cave Sediments. New York: Kluwer Academic.<br />
Stuiver, M., & Braziunas, T.F. 1993. Sun, ocean, climate and atmospheric 14 CO2: an evaluation of<br />
causal and spectral relationships. The Holocene, 3(4), 289–305.<br />
Svensmark, H., & Friis Christensen, E. 1997. Variation of cosmic ray flux and global cloud coverage-a<br />
missing link in solar-climate relationships. J. Atmos. Terr. Phys, 59, 1225–1232.<br />
Usoskin, I.G., & Kromer, B. 2005. Reconstruction of the 14 C production rate from measured relative<br />
abundance. Radiocarbon, 47(1), 31–37.<br />
Verdes, P.F., Granitto, P.M., & Ceccatto, H.A. in pressa. An overembedding method for modeling<br />
nonstationary systems. Physical Review Letters.<br />
Verdes, P.F., Granitto, P.M., Szeliga, M. I., Rebola, A., & Ceccatto, H.A. in pressb. Symmetric-<br />
Embedding Prediction of the CATS Benchmark. Neurocomputing.<br />
Wagner, G. 2001. Presence of the solar de Vries cycle (∼205 years) during the last ice-age. Geophysical<br />
Research Letters, 28(2), 303–306.<br />
Walter, H.J. 1998. Scavening of 231 Pa and 230 Th in the South Atlantic: Implications for the use of<br />
the 231Pa/230Th ratio as a paleoproductivity proxy. Berichte zur Polarforschung, 282, 1–82.
206 CHAPTER 6. FORSCHUNGSSTELLE “RADIOMETRIE”<br />
Wenderoth, P. 2005. Untersuchung der Anwendbarkeit des authigenen 10 Be/ 9 Be-Verhältnisses in Tiefseesedimenten<br />
als Proxy zur Rekonstruktion der Erdmagnetfeldstärke. unpublished Master Thesis,<br />
University of Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />
Wurth, G., Niggemann, S., Richter, D.K., & Mangini, A. 2004. The Younger Dryas and Holocene<br />
climate record of a stalagmite from Hölloch Cave (Bavarian Alps, Germany). Journal of Quaternary<br />
Science, 19, 291–298.
Bibliography<br />
Peer Reviewed Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 209<br />
Grey Publications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 215<br />
PhD Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 217<br />
Diploma Theses . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 219<br />
Invited Talks . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 221<br />
207
7.1. PEER REVIEWED PUBLICATIONS 209<br />
Peer Reviewed Publications<br />
Aeschbach-Hertig, W. 2005. A comment on ”Helium sources in passive margin aquifers-new evidence<br />
for a significant mantle 3 He source in aquifers with unexpectedly low in situ 3 He/ 4 He production”<br />
by M. C. Castro [Earth Planet. Sci. Lett. 222 (2004) 897-913]. Earth Planet. Sci. Lett., in press.<br />
Bayer, A., Vogel, H.-J., Ippisch, O., & Roth, K. 2005. Do effective properties for unsaturated weakly<br />
layered porous media exist? An experimental study. Hydrology and Earth System Sci., 9, 517–522,<br />
SRef–ID: 1607–7938/hess/2005–9–517.<br />
Beirle, S., Platt, U., von Glasow, R., Wenig, M., & Wagner, T. 2004. Estimate of nitrogen<br />
oxide emissions from shipping by satellite remote sensing. Geophys. Res. Lett., 31, L18102,<br />
doi:10.1029/2004GL020312.<br />
Bobrowski, N., Hönninger, G., Lohberger, F., & Platt, U. 2005. IDOAS: A new monitoring technique<br />
to study the 2D distribution of volcanic gas emissions. J. Volcanol. Geotherm. Res., Accepted for<br />
publishing.<br />
Braun, H. in press. Possible solar origin of the glacial 1,470-year climate cycle demonstrated in a<br />
coupled model. Nature.<br />
Braun, H., Christl, M., Rahmstorf, S., Ganopolski, A., Mangini, A., Kubatzki, C., Roth, K., &<br />
Kromer, B. 2005. Possible solar origin of the 1,470-year glacial climate cycle demonstrated in a<br />
coupled model. Nature, 438, doi: 10.1038/nature04121.<br />
Bruns, M., Buehler, S. A., Burrows, J. P., Heue, K.-P., Platt, U., Pundt, I., Richter, A., Rozanov, A.,<br />
Wagner, T., & Wang, P. 2004. Retrieval of profile information from Airborne Multi Axis UV/visible<br />
skylight absorption measurements. Appl.Opt., 43(22), 4415 – 4426.<br />
Bulath, S., Alekhina, I., Blot, M., Petit, J.-R., de Angelis, M., Wagenbach, D., Lipenkov, V., Valilyeva,<br />
L., Wloch, D., Raynaud, D., & Lukin, V. 2004. DNA singature of thermophilic bacteria from the<br />
aged accretion ice of Lake Vostok, Antarctica: implications for searching for life in extreme icy<br />
environments. International Journal of Astrobiology, 3(1), 1–12.<br />
Butz, A., Bösch, H., Camy-Peyret, C., Chipperfield, M., Dorf, M., Dufour, G., Grunow, K., Jeseck,<br />
P., Kühl, S., Payan, S., Pepin, I., Pukite, J., Rozanov, A., von Savigny, C., Sioris, C., Wagner, T.,<br />
Weidner, F., & Pfeilsticker, K. 2005. Inter-comparison of Stratospheric O3 and NO2 abundances retrieved<br />
from balloon borne direct sun observations and Envisat/SCIAMACHY limb measurements.<br />
Atmos. Chem. Phys. Disc., 5, 10747 – 10797.<br />
Canty, T., Salawitch, R.S., Renard, J.B., Reviere, E.D., Pfeilsticker, K., M., Dorf., Fitzenberger,<br />
R., Bösch, H., Stimpfle, R.M., Wilmouth, D.M., Anderson, J.G., Richard, E.C., Fahey, D.W., &<br />
Gao, R.S.and Bui, T.P. 2005. Analysis of BrO, ClO, and nighttime OClO in the arctic winter<br />
stratosphere. J. Geophys. Res., 110, D01301, doi:10.1029-/2004JD005035.<br />
Christl, M., Mangini, A., Holzkämper, S., & Spötl, C. 2004. Evidence for a link between the flux<br />
of galactic cosmic rays and Earths climate during the past 200,000 years. J. Atmospheric and<br />
Solar-Terrestrial Physics, 66, 313–322.<br />
Corcho Alvarado, J. A., Purtschert, R., Hinsby, K., Troldborg, L., Hofer, M., Kipfer, R., Aeschbach-<br />
Hertig, W., & Synal, H.-A. 2004. 36 Cl in modern groundwater dated by a multi tracer approach<br />
( 3 H/ 3 He, SF6, CFC-12 and 85 Kr): A case study in quaternary sand aquifers in the Odense Pilot<br />
River Basin, Denmark. Appl. Geochem., 20, 599–609.<br />
Corsmeier, U., Kohler, M., Vogel, B., Vogel, H., & Fiedler, F. 2005. BAB II: a project to evaluate the<br />
accuracy of real-world traffic emissions for a motorway. Atmos. Environ., 39, 5627–5641.<br />
Crewell, S., Bloemink, H., Feijt, A., García, S.G., Jolivet, D., Krasnov, O.A., van Lammeren, A.,<br />
Löhnert, U., van Meijgaard, E., Meywerk, J., Quante, M., Pfeilsticker, K., Schmidt, S., Scholl, T.,<br />
Simmer, C., Schröder, M., Trautmann, T., Venema, V., Wendisch, M., & Willén, U. 2004. The<br />
BALTEX Bridge Campaign - An integrated approach for a better understanding of clouds. Bull.<br />
Am. Met. Soc., 85, 1565 – 1584.<br />
Dufour, G., Payan, S., Lefévre, F., Berthet, G., Eremenko, M., Butz, A., Jeseck, P., Té, Y., Pfeilsticker,<br />
K., & Camy-Peyret, C. 2005. 4D comparison method to study the NOy partitioning in summer<br />
polar stratosphere: Influence of aerosol burden. Atmos. Chem. Phys., 5, 919 – 926.
210 CHAPTER 7. BIBLIOGRAPHY<br />
Eitel, B., Hecht, S., Mächtle, B., Schukraft, G., Kadereit, A., Wagner, G.A., Kromer, B., Unkel, I., &<br />
Reindel, M. 2005. Geoarchaeological evidence from desert loess in the Nazca/Palpa region, Southern<br />
Peru: Palaeoenvironmental changes and their impact on Pre-Columbian cultures. Archaeometry,<br />
47(1), 137–158.<br />
Felis, T., Lohmann, G., Kuhnert, H., Lorenz, S.J., Scholz, D., Pätzold, J., Al Rousan, S.A., & Al<br />
Moghrabi, S.M. 2004. Increased seasonality in Middle East temperatures during the last interglacial<br />
period. Nature, 429, 164–168.<br />
Fichter, C., Marquart, S., Sausen, R., & Lee, D. S. 2005. The impact of cruise altitude on contrails<br />
and related radiative forcing. Met. Zeitsch., 14, 563 – 572.<br />
Fix, A., Ehret, G., Flentje, H., Poberaj, G., Gottwald, M., Finkenzeller, H., Bremer, H., Bruns, M.,<br />
Burrows, J. P., Kleinbhl, A., Kllmann, H., Kuttippurath, J., Richter, A., Wang, P., Heue, K.-<br />
P., Platt, U., Pundt, I., & Wagner, T. 2005. SCIAMACHY validation by aircraft remote sensing:<br />
design, execution, and first measurement results of the SCIA-VALUE mission. Atmos. Chem. Phys.,<br />
5, 1273 – 1289.<br />
Fleitmann, D., Burns, S.J., Neff, U., Mudelsee, M., Mangini, A., & Matter, A. 2004. Palaeoclimatic interpretation<br />
of high-resolution oxygen isotope profiles derived from annually laminated speleothems<br />
from Southern Oman. Quaternary Science Reviews, 23, 935–945.<br />
Frankenberg, C., Meirink, J. F., van Weele, M., Platt, U., & Wagner, T. 2005a. Assessing Methane<br />
Emissions from Global Space-Borne Observations. Science, 308(5724), 1010–1014.<br />
Frankenberg, C., Platt, U., & Wagner, T. 2005b. Iterative maximum a posteriori (IMAP)-DOAS for<br />
retrieval of strongly absorbing trace gases: Model studies for CH4 and CO2 retrieval from near<br />
infrared spectra of SCIAMACHY onboard ENVISAT. Atmos. Chem. Phys., 5, 9–22.<br />
Frankenberg, C., Platt, U., & Wagner, T. 2005c. Retrieval of CO from SCIAMACHY onboard<br />
ENVISAT: detection of strongly polluted areas and seasonal patterns in global CO abundances.<br />
Atmos. Chem. Phys., 5, 1639–1644.<br />
Frew, N. M., Bock, E. J., Schimpf, U., Hara, T., Haußecker, H., Edson, J. B., McGillis, W. R., Nelson,<br />
R. K., McKeanna, B. M., Uz, B. M., & Jähne, B. 2004. Air-sea gas transfer: its dependence on wind<br />
stress, small-scale roughness and surface films Small-Scale Air-Sea Interaction with Thermography.<br />
Journal of Geophysical Research, C8(109). C08S17, doi:10.1029/2003JC002131.<br />
Friedrich, M., Remmele, S., Kromer, B., Hofmann, J., Spurk, M., Kaiser, K.F., Orcel, C., & Küppers,<br />
M. 2004. The 12,460-Year Hohenheim Oak and Pine Tree-Ring Chronology from Central Europe<br />
- a Unique Annual Record for Radiocarbon Calibration and Paleoenvironment Reconstructions.<br />
Radiocarbon, 46(3), 1111–1122.<br />
Garbe, C. S., Schimpf, U., & Jähne, B. 2004. A Surface Renewal Model to Analyze Infrared Image<br />
Sequences of the Ocean Surface for the Study of Air-Sea Heat and Gas Exchange. Journal of<br />
Geophysical Research, C8(109). C08S15, doi:10.1029/2003JC001802.<br />
Gurlit, W., Bösch, H., Bovensmann, H., Burrows, J. P., Butz, A., Camy-Peyret, C., Dorf, M., Gerilowski,<br />
K., Lindner, A., Noël, S., Platt, U., Weidner, F., & Pfeilsticker, K. 2005. The UV-A<br />
and visible solar irradiance spectrum: Inter-comparison of absolutely calibrated, spectrally medium<br />
resolved solar irradiance spectra from balloon-, and satellite-borne measurements. Atmos. Chem.<br />
Phys., 5, 1879 – 1890.<br />
Hak, C., Pundt, I., Trick, S., Kern, C., Platt, U., Dommen, J., Ordonez, C., Prevot, A. S. H.,<br />
Junkermann, W., Astorga-Llorens, C., Larsen, B. R., Mellqvist, J., Strandberg, A., Yu, Y., Galle,<br />
B., Kleffmann, J., Lörzer, J. C., Braathen, G. O., & Volkamer, R. 2005. Intercomparison of four<br />
different in-situ techniques for ambient formaldehyde measurements in urban air. Atmos. Chem.<br />
Phys. Discuss., 5, 2897–2945.<br />
Heckel, A., Richter, A., Tarsu, T., Wittrock, F., Hak, C., Pundt, I., Junkermann, W., & Burrows,<br />
J. P. 2005. MAX-DOAS measurements of formaldehyde in the Po-Valley. Atmos. Chem. Phys., 5,<br />
909 – 918.
7.1. PEER REVIEWED PUBLICATIONS 211<br />
Hendrick, F., Barret, B., Van Roozendael, M., Boesch, H., Butz, A., De Mazière, M., Goutail, F.,<br />
Lambert, J.-C., Pfeilsticker, K., & Pommereau, J.P. 2004. Retrieval of nitrogen dioxide stratospheric<br />
profiles from ground-based zenith-sky UV-visible observations: Validation of the technique through<br />
correlative comparisons. Atmos. Chem. Phys., 4, 2867 – 2904.<br />
Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., Friedeburg, C. von, Platt, U., Pundt, I., Wang,<br />
P., & Wagner, T. 2005a. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />
measurements. Atmos. Chem. Phys., 5, 1039 – 1051.<br />
Heue, K.-P., Richter, A., Bruns, M., Burrows, J. P., v.Friedeburg, C., Platt, U., Pundt, I., Wang, P.,<br />
& Wagner, T. 2005b. Validation of SCIAMACHY tropospheric NO2-columns with AMAXDOAS<br />
measurements. Atmos. Chem. Phys., 5, 1039–1051.<br />
Hollwedel, J., Wenig, M., Beirle, S., Kraus, S., Kühl, S., Wilms-Grabe, W., Platt, U., & Wagner, T.<br />
2004. Year-to-Year Variations of Spring Time Polar Tropospheric BrO as seen by GOME. Adv.<br />
Space Res., 34, 804–808. doi:10.1016/j.asr.2003.08.060.<br />
Holzkämper, S., Mangini, A., Spötl, C., & Mudelsee, M. 2004. Timing and progression of the Last<br />
Interglacial derived from a high alpine stalagmite. Geophysical Research Letters, 31(L07201), 1–4.<br />
Holzkämper, S., Spötl, C., & Mangini, A. 2005. High-precision constrains on timing of Alpine warm<br />
periods during the middle to late Pleistocene using speleothem growth. Earth and Planetary Science<br />
Letters, 236, 751–764.<br />
Hughen, K., Lehman, S., Southon, J., Overpeck, J., Marchal, O., & Herring, C. 2004a. 14C activity<br />
and Global Carbon Cycle changes over the last 50,000 years. Science, 303, 202–207.<br />
Hughen, K.A., Baillie, M.G.L., Bard, E., Beck, J.W., Bertrand, C.J.H., J.H., Chanda, Blackwell, P.G.,<br />
Buck, C.E., Burr, G.S., Cutler, K.B., Damon, P.E., Edwards, R.L., Fairbanks, R.G., Richard, G.,<br />
Friedrich, M., Guilderson, T.P., Kromer, B., McCormac, G., Manning, S., Ramsey, C.B., Reimer,<br />
P.J., Reimer, R.W., Remmele, S., Southon, J.R., Stuiver, M, Talamo, S., Taylor, F.W., van der<br />
Plicht, J., & Weyhenmeyer, C.E. 2004b. Marine04 Marine Radiocarbon Age Calibration, 0-26 Cal<br />
Kyr BP. Radiocarbon, 46(3), 1059–1086.<br />
Jähne, B., Schmidt, M., & Rocholz, R. 2005c. Combined optical slope/height measurements of short<br />
wind waves: principle and calibration. Meas. Sci. Technol., 16, 1937–1944.<br />
Kern, C., Trick, S., Rippel, B., & Platt, U. 2005. Applicability of light-emitting diodes as light sources<br />
for active DOAS measurements. Appl. Opt., Accepted for publishing.<br />
Khokhar, M.F., Frankenberg, C., Roozendael, M. Van, Beirle, S., Kühl, S., Richter, A., Platt, U.,<br />
& Wagner, T. 2005. Satellite observations of atmospheric SO2 from volcanic eruptions during the<br />
time period of 1996 to 2002. Adv. Space Res., 36, 879–887. doi:10.1016/j.asr.2005.04.114.<br />
Kromer, B., Friedrich, M., Hughen, K.A., Kaiser, F., Remmele, S., Schaub, M., & Talamo, S. 2004.<br />
Late Glacial 14C ages from a floating 1382-ring pine chronology. Radiocarbon, 46(3), 1203–1209.<br />
Kühl, S., D”ornbrack, A., Sinnhuber, B.-M., Wilms-Grabe, W., Platt, U., & Wagner, T. 2004. Observational<br />
evidence of rapid chlorine activation by mountain waves above Northern Scandinavia.<br />
J. Geophys. Res., 109. doi:10.1029/2004JD004797.<br />
Laepple, T., Knab, V., Mettendorf, K.-U., & Pundt, I. 2004. Longpath DOAS tomography on a<br />
motorway exhaust plume: Numerical studies and application to data from the BAB II campaign.<br />
Atmos. Chem. Phys., 4, 1323 – 1342.<br />
Lee, J. S., Kim, Y. J., Kuk, B., Geyer, A., & Platt, U. 2005. Simultaneous Measurements of Atmospheric<br />
Pollutants and Visibility with a Long-Path DOAS System in Urban Areas. Environ. Monit.<br />
Assess., 104, 281–293.<br />
Legrand, M., Preunkert, S., Galy-Lacaux, C., Liousse, C., & Wagenbach, D. 2005. Atmospheric yearround<br />
records of dicarboxylic acids and sulfate at three French sites located between 630 and 4360<br />
m elevation. Journal of Geophysical Research, 110, D13302, doi:10.1029/2004JD005515.<br />
Levin, I., & Kromer, B. 2004. The tropospheric 14 CO2 level in mid-latitudes of the Northern Hemisphere<br />
(1959-2003). Radiocarbon, 46(3), 1 261–1 272.
212 CHAPTER 7. BIBLIOGRAPHY<br />
Mangini, A., Spötl, C., & Verdes, P.F. 2005. Reconstruction of temperature in the Central Alps<br />
during the past 2,000 years from a δ 18 O stalagmite record. Earth and Planetary Science Letters,<br />
235, 741–751.<br />
Marquart, S., Ponater, M., Ström, L., & Gierens, K. 2005. An upgraded estimate of the radiative<br />
forcing of cryoplane contrails. Met. Zeitsch., 14, 573 – 582.<br />
McHargue, L.R., & Donahue, D.J. 2005. Effects of climate and the cosmic-ray flux on the 10 Be content<br />
of marine sediment. Earth and Planetary Science Letters, 232, 193–207.<br />
McManus, J.F., Francois, R., Keigwin, L.D., & Brown Leger, S. 2004. Collapse and rapid resumption<br />
of Atlantic meridional circulation linked to deglacial climate changes. Nature, 428, 834–837.<br />
Oswald, B., Doetsch, J., & Roth, K. 2006. A new computational technique for procesing transmission<br />
line measurements to determine dispersive dielectric properties. Geophysics, in print.<br />
Peeters, F., Beyerle, U., Aeschbach-Hertig, W., Brennwald, M. S., & Kipfer, R. 2004. Response to<br />
the comment by G. Favreau, A. Guero, and J. Seidel on Improving noble gas based paleoclimate<br />
reconstruction and groundwater dating using 20 Ne/ 22 Ne ratios (2003) Geochim. Cosmochim. Acta,<br />
67, 587 - 600. Geochim. Cosmochim. Acta, 68(6), 1437–1438.<br />
Peters, C., Pechtl, S., Stutz, J., Hebestreit, K., Hönninger, G., Heumann, K. G., Schwarz, A., Winterlik,<br />
J., & Platt, U. 2005. Reactive and organic halogen species in three different European coastal<br />
environments. Atmos. Chem. Phys., 5, accepted.<br />
Piel, C., Weller, R., M.Huke, & Wagenbach, D. accepted. Atmospheric methane sulfonate and non-sea<br />
salt sulfate records at the EPICA deep-drilling site in Dronning Maud Land. Journal of Geophysical<br />
Research, 2005JD006213.<br />
Platt, U., Allan, W., & Lowe, D. 2004. Hemispheric Average Cl Atom Concentration from 13 C/ 12 C<br />
Ratios in Atmospheric Methane. Atmos. Chem. Phys., 4, 2393–2399.<br />
Ponater, M., Marquart, S., Sausen, R., & Schumann, U. 2005. On contrail climate sensitivity. Geophys.<br />
Res. Lett., 32, L10706, doi: 10.1029/2005GL02258.<br />
Pundt, I. 2005. DOAS tomography for the localisation and quantification of anthropogenic air pollution.<br />
Anal. Bioanal. Chem. accepted.<br />
Pundt, I., & Mettendorf, K. U. 2005. Multibeam long-path differential optical absorption spectroscopy<br />
instrument: a device for simultaneous measurements along multiple light paths. Appl. Opt., 44(23),<br />
4985 – 4994.<br />
Pundt, I., Mettendorf, K. U., Laepple, T., Knab, V., Xie, P., Lösch, J., von Friedeburg, C., Platt,<br />
U., & Wagner, T. 2005. Measurements of trace gas distributions by Long-Path DOAS-Tomography<br />
during the motorway campaign BAB II: experimental setup and results for NO2 (BAB II special<br />
issue). Atmos. Environ., 39(5), 967–975.<br />
Reimer, P.J., Baillie, M.G.L., Bard, E., Bayliss, A., Beck, J.W., Bertrand, C.J.H., Blackwell, P.G.,<br />
Buck, C.E., Burr, G.S., Cutler, K.B., Damon, P.E., Edwards, R.L., Fairbanks, R.G., Friedrich, M.,<br />
Guilderson, T.P., Hogg, A.G., Hughen, K.A., Kromer, B., McCormac, G., Manning, S., Ramsey,<br />
C.B., Reimer, R.W., Remmele, S., Southon, J.R., Stuiver, M., Talamo, S., Taylor, F.W., van der<br />
Plicht, J., & Weyhenmeyer, C.E. 2004. INTCAL04 terrestrial radiocarbon age calibration, 0-26 cal<br />
kyr BP. Radiocarbon, 46(3), 1029–1058.<br />
Richter, A., Wittrock, F., Weber., M., Beirle, S., Kühl, S., Platt, U., Wagner, T., Wilms-Grabe, W., &<br />
Burrows, J.P. 2005. GOME observations of stratospheric trace gas distributions during the splitting<br />
vortex event in the Antarctic winter 2002 Part I: Measurements. J. Atmos. Sci., 62, 778 – 785.<br />
Röckmann, T., & Levin, I. 2005. High-precision determination of the changing isotopic composition<br />
of atmospheric N2O from 1990 to 2002. J. Geophys. Res. accepted.<br />
Roth, K., Boike, J., & Vogel, H.-J. 2005. Quantifying Permafrost Patterns using Minkowski Densities.<br />
Permafrost and Periglacial Processes, 16, 277–290, doi: 10.1002/ppp.531.<br />
Schaub, M., Kaiser, K.F., Kromer, B., & Talamo, S. 2005. Extension of the Swiss Lateglacial tree-ring<br />
chronologies. Dendrochronologia, doi:10.1016.
7.1. PEER REVIEWED PUBLICATIONS 213<br />
Schimpf, U., Garbe, C. S., & Jähne, B. 2004. Investigation of transport processes across the seasurface<br />
microlayer by infrared imagery. Journal of Geophysical Research, C8(109). C08S13,<br />
doi:10.1029/2003JC001803.<br />
Scholl, T., Pfeilsticker, K., Davis, A.B., Klein Baltink, H., Crewell, S., Löhnert, U., Simmer, C.,<br />
Meywerk, J., & Quante, M. 2005. Path length distributions for solar photons under cloudy skies:<br />
Comparison of measured first and second moments with predictions from classical and anomalous<br />
diffusion theories. J. Geophys. Res., revised.<br />
Scholz, D., Mangini, A., & Felis, T. 2004. U-series dating of diagenetically altered fossil reef corals.<br />
Earth and Planetary Science Letters, 218, 163–178.<br />
Sinreich, R., Frieß, U., Wagner, T., & Platt, U. 2005. Multi Axis Differential Optical Absorption<br />
Spectroscopy (MAX-DOAS) of Gas and Aerosol Distributions. Farady Discuss., 153 – 164.<br />
Solanski, S.K., Usoskin, I.G., Kromer, B., Schüssler, M., & Beer, J. 2004. Unsusual activity of the<br />
sun during recent decades compared to the previous 11,000 years. Nature, 431, 1084–1087.<br />
Stöhr, M., & Roth, K. 2005. Gradient-based estimation of local parameters for flow and transport in<br />
heterogeneous porous media. Water Resour. Res., 41, 1–14, W08401, doi:10.1029/2004WR003768.<br />
Tas, E., Peleg, M., Matveev, V., Zingler, J., & Luria, M. 2005. Frequency and extent of bromine oxide<br />
formation over the Dead Sea, Israel. J. Geosphys. Res., 110, D11304.<br />
Usoskin, I.G., & Kromer, B. 2005. Reconstruction of the 14 C production rate from measured relative<br />
abundance. Radiocarbon, 47(1), 31–37.<br />
Vandaele, A.C., Fayt, C., Hendrick, F., Hermans, C., Humbled, F., Van Roozendael, M., Gil, M.,<br />
Navarro, M., Puentedura, O., Yela, M., Braathen, G., Stebel, K., Tornkvist, K., Johnston, P.,<br />
Kreher, K., Goutail, F., Mieville, A., Pommereau, J.-P., Khaikine, S., Richter, A., Oetjen, H.,<br />
Wittrock, F., Bugarski, S., Frieß, U., Pfeilsticker, K., Sinreich, R., Wagner, T., Corlett, G., &<br />
Leigh, R. 2005. An intercomparison campaign of ground-based UV-Visible measurements of NO2,<br />
BrO, and OClO slant columns. Methods of analysis and results for NO2. J. Geophys. Res., 110,<br />
D08305, doi:10.1029/2004JD005423.<br />
Verdes, P.F., Granitto, P.M., & Ceccatto, H.A. in pressa. An overembedding method for modeling<br />
nonstationary systems. Physical Review Letters.<br />
Verdes, P.F., Granitto, P.M., Szeliga, M. I., Rebola, A., & Ceccatto, H.A. in pressb. Symmetric-<br />
Embedding Prediction of the CATS Benchmark. Neurocomputing.<br />
Vogel, H.-J., Tölke, J., Schulz, V. P., Krafczyk, M., & Roth, K. 2005a. Comparison of a Lattice-<br />
Boltzmann Model, a Full-Morphology Model, and a Pore Network Model for Determining Capillary<br />
Pressure-Saturation Relationships. Vadose Zone J., 4, 380–388, doi: 10.2136/vzj2004.0114.<br />
Vogel, H.-J., Hoffmann, H., & Roth, K. 2005b. Studies of crack dynamics in clay soil. I. Experimental<br />
methods, results, and morphological quantification. Geoderma, 125, 203–211.<br />
Vogel, H.-J., Hoffmann, H., Leopold, A., & Roth, K. 2005c. Studies of crack dynamics in clay soil.<br />
II. A physically based model for crack formation. Geoderma, 125, 213–223.<br />
Volkamer, R., Spietz, P., Burrows, J. P., & Platt, U. 2005. High-resolution absorption cross-section of<br />
Glyoxal in the UV/vis and IR spectral ranges. J. Photoch. Photobio. A: Chemistry, 172, 35 – 46.<br />
von Friedeburg, C., Pundt, I., Mettendorf, K. U., Wagner, T., & Platt, U. 2005. Multi-AXis-(MAX)<br />
DOAS Measurements of NO2 during the BAB II Motorway Emission Campaign, (BAB II special<br />
issue). Atmos. Environ., 39(5), 977–985.<br />
von Glasow, R., & Crutzen, P. J. 2004. Model study of multiphase DMS oxidation with a focus on<br />
halogens. Atmos. Chem. Phys., 4, 589 – 608.<br />
von Glasow, R., von Kuhlmann, R., Lawrence, M. G., Platt, U., & Crutzen, P. J. 2004. Impact of<br />
reactive bromine chemistry in the troposphere. Atmos. Chem. Phys., 4, 2481 – 2497.<br />
Wagner, T., Dix, B., von Friedeburg, C., Frieß, U., Sanghavi, S., Sinreich, R., & Platt, U. 2004.<br />
MAX-DOAS O4 measurements - a new technique to derive information on atmospheric aerosols:<br />
(I) Principles and information content. J. Geophys. Res., 109(D22205).
214 CHAPTER 7. BIBLIOGRAPHY<br />
Wagner, T., Beirle, S., Grzegorski, M., Sanghavi, S., & U., Platt. 2005a. El-Niño induced anomalies<br />
in global data sets of water vapour and cloud cover derived from GOME on ERS-2. J. Geophys.<br />
Res., 110(D15104).<br />
Wagner, T., Beirle, S., Grzegorski, M., & Platt, U. 2005b. Global trends (1996 to 2003) of total<br />
column precipitable water observed by GOME on ERS-2 and their relation to surface temperature.<br />
J. Geophys. Res. (accepted).<br />
Wang, P., Richter, A., Bruns, M., Rozanov, V., Burrows, J. P., Heue, K.-P., Wagner, T., Pundt, I., &<br />
Platt, U. 2005. Measurements of tropospheric NO2 with an airborne multi-axis DOAS instrument.<br />
Atmos. Chem. Phys., 5, 337 – 343.<br />
Weidner, F., Bösch, H., Bovensmann, H., Burrows, J.P., Butz, A., Camy-Peyret, C., Dorf, M.,<br />
Gerilowski, K., Gurlit, W., Platt, U., von Friedeburg, C., Wagner, T., & Pfeilsticker, K. 2005.<br />
Balloon-borne limb profiling of UV/vis skylight radiances, O3, NO2, and BrO: Technical set-up<br />
and validation of the method. Atmos. Chem. Phys., 5, 1409 – 1422.<br />
Wenig, M., Jähne, B., & Platt, U. 2005. Operator Representation as a new differential optical absorption<br />
spectroscopy formalism. Appl. Opt., 44(16), 3246–3253.<br />
Wollschläger, U., & Roth, K. 2005. Estimation of temporal changes of volumetric soil water content<br />
from ground-penetrating radar reflections. Subsurf. Sens. Technol. Appl., 6(2), doi: 10.1007/s11220–<br />
005–0007–y.<br />
Wurth, G., Niggemann, S., Richter, D.K., & Mangini, A. 2004. The Younger Dryas and Holocene<br />
climate record of a stalagmite from Hölloch Cave (Bavarian Alps, Germany). Journal of Quaternary<br />
Science, 19, 291–298.<br />
Yu, Q., Shi, C., Niu, F., He, N., & Roth, K. 2005. Analysis of temperature controlled ventilated<br />
embankment. Cold Reg. Sci. Technol., 42, 17–24, doi:10.1016/j.coldregions.2004.11.004.<br />
Zhang, X., & Garbe, C. S. 2004. Studying dynamical processes of air-sea exchanges with air-water inerface<br />
image techniques. Chap. 3, pages 57–88 of: Recent Research Developments in Fluid Dynamics,<br />
vol. 5. Transworld Research Network.<br />
Zingler, J., & Platt, U. 2005. Iodine Oxide in the Dead Sea Valley: Evidence for inorganic sources of<br />
boundary layer IO. J. Geosphys. Res., 110, D07307.
7.2. GREY PUBLICATIONS 215<br />
Grey Publications<br />
ACCENT. 2005. Workshop on Radiative Transfer Modeling, Heidelberg.<br />
Auer, M., Kutschera, W., Priller, A., Wagenbach, D., Wallner, A., & Wild, E. M. 2005 (September<br />
5-10). Atmospheric 26 Al and 10 Be as a dating tool for climate archives (Abstract). vol. The 10th<br />
International Conference on Accelerator Mass Spectrometry Berkeley, California.<br />
Bigler, M., Röthlisberger, R., Ruth, U., Siggaard-Andersen, M.-L., Steffensen, J. P., Hansson, M. E.,<br />
Goto-Azuma, K., Fischer, H., & Wagenbach, D. 2005. A new high-resolution chemical ice core<br />
record over the last glacial period from NGRIP. Geophysical Research Abstracts, Vol 7, 05616.<br />
Christl, M., Schulze, B., Wenderothr, P., Bernsdorff, F., & Mangini, A. 2005. Geomagnetic variability<br />
over the past 300,000 years from cosmogenic beryllium-10 in deep-sea sediments - a potential global<br />
matching tool. 22. Internationale Polartagung, 18.24.09.2005, Poster.<br />
Dombrowski-Etchevers, I., Peuch, V.-H., Wagenbach, D., & Legrand, M. 2005. Validation of concentrations<br />
of lead-210 in high altitude simulated by MOCAGE. Geophysical Research Abstracts, Vol<br />
7, 09009.<br />
Grzegorski, M., Frankenberg, C., Platt, U., Wenig, M., Fournier, N., Stammes, P., & Wagner, T. 2004.<br />
Determination of cloud parameters from SCIAMACHY data for the correction of tropospheric trace<br />
gases. In: Proceedings of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria.<br />
ESA-publication SP-572, (CD-ROM).<br />
Hartl, A., Mettenorf, K. U., Song, B. C., & Pundt, I. 2005. Reconstruction of 2D-Trace Gas Concentration<br />
Distributions from Long-path DOAS Measurements: General Approach, Validation and<br />
Simulations for an Experiment on an Urban Site. In: Proceedings of the 31st ”International Symposium<br />
of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia. ISPRSpublication(CD-ROM).<br />
Heue, K.-P., Beirle, S., Bruns, M., Burrows, J. P., Platt, U., Pundt, I., Richter, A., Wagner, T., &<br />
P. Wang, P. 2004. SCIAMACHY validation using the AMAXDOAS instrument. In: Proceedings<br />
of the ENVISAT & ERS Symposium, 6-10 September 2004, Salzburg, Austria. ESA-publication<br />
SP-572 (CD-ROM).<br />
Ilmberger, J., & von Rohden, C. 2005. Abschlußbericht zum Forschungsvorhaben: ”SF6 als Tracer<br />
<strong>für</strong> Transport- und Mischungsprozesse in Tagebaurestseen.<br />
Ilmberger, J., von Rohden, C., & Wunderle, K. 2005. Observation of Multilayer Structures in a Small<br />
Lake. In: In A. Folkard and I. Jones,editors, 9th workshop on physical processes in natural waters.<br />
Jähne, B. 2004. Handbook of Digital Image Processing for Scientific and Technical Applications. 2nd<br />
edn. Boca Raton: CRC Press.<br />
Jähne, B. 2005a. Digital Image Processing. 6th edn. Berlin: Springer.<br />
Jähne, B. 2005b. Digitale Bildverarbeitung. 6th edn. Berlin: Springer.<br />
Kreuzer, A. M., Zongyu, C., Kipfer, R., & Aeschbach-Hertig, W. in press 2005. Environmental Tracers<br />
in Groundwater of the North China Plain. In: IAEA (ed), International Conference on Isotopes in<br />
Environmental Studies - Aquatic Forum 2004. Monte-Carlo, Monaco: IAEA.<br />
Marbach, T., Beirle, S., Hollwedel, J., Platt, U., & Wagner, T. 2004. Identification of tropospheric<br />
emission sources from satellite observations: Synergistic use of trace gas measurements of formaldehyde<br />
(HCHO), and nitrogen dioxide (NO2). In: Proceedings of the ENVISAT & ERS Symposium,<br />
6-10 September 2004, Salzburg, Austria. ESA publication SP-572, (CD-ROM).<br />
Pettinger, M., Keck, L., Fischer, H., Wagenbach, D., Preunkert, S., Böhm, R., Hoelzle, M., & Hoffmann,<br />
M. Leuenbergerand G. 2005. Cenntennial scale isotope thermometry from Alpine ice core<br />
records: shortcomings and challenge. Geophysical Research Abstracts, Vol 7, 07941.<br />
Platt, U., Pfeilsticker, K., & Vollmer, M. 2005. Chapter 24: Atmospheric Optics. In: Träger, F. (ed),<br />
Springer Handbook of Lasers and Optics. Heidelberg: Springer.
216 CHAPTER 7. BIBLIOGRAPHY<br />
Poehler, D., Rippel, B., Stelzer, A., Mettendorf, K. U., Hartl, A., Platt, U., & Pundt, I. 2005.<br />
Instrumental setup and measurement configuration for 2D-tomographic DOAS measurements of<br />
trace gas distributions over an area of a few square km. In: Proceedings of the 31st ”International<br />
Symposium of Remote Sensing of the Environment”, June 20-24, 2005, in St. Petersburg, Russia.<br />
ISPRS-publication(CD-ROM).<br />
Pundt, I., Hak, C., Hartl, A., Heue, K.-P., Mettendorf, K. U., Platt, U., Poehler, D., Rippel, B., Song,<br />
B.-C., Stelzer, A., Wagner, T., Bruns, M., Burrows, J. P., Richter, A., & Wang, P. 2005. Mapping of<br />
tropospheric trace gas concentration distributions from ground and aircraft by DOAS-tomography<br />
(Tom-DOAS). In: Proceedings of the 31st ”International Symposium of Remote Sensing of the<br />
Environment”, June 20-24, 2005, in St. Petersburg, Russia. ISPRS-publication(CD-ROM).<br />
Schock, M., Greilich, S., Wagenbach, D., Preunkert, S., Legrand, M., Petit, J. R., Flückiger, J.,<br />
Leuenberger, M., Haeberli, W., & Psenner, R. 2005. Dissolved organic carbon (DOC) in ice samples<br />
from non-temperated, polar and Alpine glaciers. Geophysical Research Abstracts, Vol. 7, 08671.<br />
Scholz, D., & Mangini, A. in press. U-redistribution in fossil reef corals from Barbados, West Indies,<br />
and sea level reconstruction for MIS 6.5. In: Sirocko, F., Litt, T., Claussen, M., & Sanchez Goni,<br />
M.-F. (eds), The climate of past interglacials.<br />
Schröder Ritzrau, A., Freiwald, A., & Mangini, A. 2005. U/Th dating of deep-water corals from the<br />
eastern North Atlantic and the western Mediterranean Sea. In: Freiwald, A., & Roberts, J.M.<br />
(eds), Cold-water corals and ecosystems. Berlin Heidelberg: Springer-Verlag.<br />
Spötl, C., Mangini, A., Burns, S.J., Frank, N., & Pavuza, R. 2004. Speleothems from high alpine<br />
Spannagel Cave, Zillertal Alps (Austria). Page 329 of: Sasowsky, I., & MyIroie, J. (eds), Studies of<br />
Cave Sediments. New York: Kluwer Academic.<br />
Steier, P., Drosg, R., Kutschera, W., Wild, E. M., Fedi, M., Wagenbach, D., & Schock, M. 2005.<br />
Radiocarbon determination of particulate organic carbon (POC) in non-temperated, Alpine glacier<br />
ice (Abstract). The 10th International Conference on Accelerator Mass Spectrometry Berkeley,<br />
California, September 5-10, 2005.<br />
Volkamer, R., Barnes, I., Platt, U., Molina, L. T., & Molina, M. J. 2004. Remote Sensing of Glyoxal<br />
by Differential Optical Absorption Spectrosocopy (DOAS): Advancements in Simulation Chamber<br />
and Field Experiments. In: Rudzinski, K., & Barnes, I. (eds), NATO Advanced Research Workshop<br />
of Environmental Simulation Chambers - Application to Atmospheric Chemical Processes, vol.<br />
NATO Sciences Series, IV. Earth and Environmental Sciences. Zakopane, Poland: Kluwer Academic<br />
Publishers.<br />
von Glasow, R. 2005. Lead Essay - Research Front Iodine. Env. Chem., 2, in press.<br />
von Rohden, C., Hauser, A., Wunderle, K., Ilmberger, J., Wittum, G., & Roth, K. 2005. Lake<br />
dynamics: observation and high-resolution numerical simulation. In Rannacher editor. Springer.<br />
Wegner, A., Rohlfs, J., Huke, M., Stanzick, A., Wagenbach, D., Oerter, H., Sommer, S., Mulvaney,<br />
R., & Kubik, P. 2005. Bi-annual to decadal 10 Be variability in firn cores from Dronning Maud Land<br />
(DML) and Berkner Island (BI), Antarctica. Geophysical Research Abstracts, Vol 7, 08396.<br />
Wilms-Grabe, W., Kühl, S., Beirle, S., Platt, U., & Wagner, T. 2004. GOME observations of stratospheric<br />
trace gas distributions during the split vortex event in the Antarctic winter 2002. Pages<br />
1053–1054 of: Proceedings Quadrennial Ozone Symposium, 1-8 June 2004, Kos, Greece.
7.3. PHD THESES 217<br />
PhD Theses<br />
Bayer, A. 2005. X-ray attenuation techniques to explore the dynamics of water in porous media. PhD<br />
thesis, University of Heidelberg.<br />
Beirle, S. 2004. Estimating source strengths and lifetime of Nitrogen Oxides from satellite data. Ph.D.<br />
thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Bobrowski, N. 2005. Volcanic Gas Studies by MAX-DOAS. Dissertation, <strong>Universität</strong> Heidelberg.<br />
Dorf, M. 2005. Investigation of inorganic stratospheric bromine by balloon-borne DOAS measurements<br />
and model simulations. PhD thesis, University of Heidelberg, Heidelberg, Germany.<br />
El-Gamal, H. 2005. Environmental tracers in groundwater as tools to study hydrological questions in<br />
arid regions. PhD thesis, University of Heidelberg.<br />
Frankenberg, C. 2005. Retrieval of Methane and Carbon Monoxide using near infrared spectra recorded<br />
by SCIAMACHY onboard ENVISAT - Algorithm development and data analysis. Ph.D. thesis,<br />
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Fuß, D. 2004. Kombinierte Höhen- und Neigungsmessung von winderzeugten Wasserwellen am Heidelberger<br />
Aeolotron. PhD Thesis, <strong>Universität</strong> Heidelberg.<br />
Heue, K.-P. 2005a. Airborne Multi Axis DOAS instrument and measurements of two dimensional<br />
tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Heue, K.-P. 2005b. Airborne multi axis DOAS instrument and measurements of two dimensional<br />
tropospheric trace gas distributions. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Hilsenstein, V. 2004. Design and Implementation of a Passive Stereo-Infrared Imaging System for the<br />
Surface Reconstruction of Water Waves. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Hollwedel, J. 2005. Observations of tropospheric and stratospheric Bromine Monoxide from satellite.<br />
Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Klar, M. 2005. Design of an endoscopic 3-D Particle-Tracking Velocimetry system and its application<br />
in flow measurements within a gravel layer. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Kühl, S. 2005. Quantifying stratospheric chlorine chemistry by the satellite spectrometers GOME and<br />
SCIAMACHY. Ph.D. thesis, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Mettendorf, K. U. 2005. Aufbau und Einsatz eines Multibeam Instrumentes zur DOAStomographischen<br />
Messung zweidimensionaler Konzentrationsverteilungen. Ph.D. thesis, <strong>Institut</strong><br />
<strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Naegler, T. 2005 (June). Simulating Bomb Radiocarbon: Consequences for the Global Carbon Cycle.<br />
Ph.D. thesis, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg, Heidelberg, Germany.<br />
Nielsen, R. 2004. Hochgenaue Messung der Schmidtzahlabhängigkeit des Gasaustausches an einer<br />
wind- und wellenbewegten Wasseroberfläche. Ph.D. thesis, <strong>Universität</strong> Heidelberg.<br />
Peters, C. 2005. Studies of Reactive Halogen Species (RHS) in the Marine and mid-Latitudinal Boundary<br />
Layer by Active Longpath Differential Optical Absorption Spectroscopy. Dissertation, <strong>Universität</strong><br />
Heidelberg.<br />
Schimpf, D. 2005. Datierung und Interpretation der Kohlenstoff- und Sauerstoffisotopie zweier<br />
holozäner Stalagmiten aus dem Süden Chiles (Patagonien). unpublished Master Thesis, University<br />
of Heidelberg, <strong>Institut</strong>e of Environmental Physics.<br />
Scholz, D. 2005. U-series dating of diagenetically altered fossil reef corals and the application for sea<br />
level reconstruction. unpublished PhD Thesis, University of Heidelberg, Heidelberger Akademie der<br />
Wissenschaften.<br />
Schulze, B. 2005. Hochaufgelöste Rekonstruktion der 10Be-Produktionsrate aus Tiefseesedimentkernen<br />
des Bermuda Rise über die letzten 70.000 Jahre. unpublished Master Thesis, University of<br />
Heidelberg, <strong>Institut</strong>e of Environmental Physics.
218 CHAPTER 7. BIBLIOGRAPHY<br />
Weidner, F. 2005. Development and application of a versatile balloon-borne DOAS instrument for<br />
skylight radiance and atmospheric trace gas measurements. PhD thesis, University of Heidelberg,<br />
Heidelberg, Germany.<br />
Wenderoth, P. 2005. Untersuchung der Anwendbarkeit des authigenen 10 Be/ 9 Be-Verhältnisses in Tiefseesedimenten<br />
als Proxy zur Rekonstruktion der Erdmagnetfeldstärke. unpublished Master Thesis,<br />
University of Heidelberg, <strong>Institut</strong>e of Environmental Physics.
7.4. DIPLOMA THESES 219<br />
Diploma Theses<br />
Bäuerle, A. 2004. Messung von Spurenstoffverteilungen in Mailand mit Hilfe eines Multistrahl-<br />
Langpfad Teleskops. Staatsexamensarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Bengel, I. 2005. Spurenstoffglaziologische Pilotuntersuchungen an einer kalten Miniatureiskappe.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Bobrowski, N., & Filsinger, F. 2005. Mini-MAX-DOAS Manual. <strong>Universität</strong> Heidelberg.<br />
Halasia, M.-A. 2004. SMAX-DOAS observation of atmospheric trace gases on the Polarstern<br />
ANT/XX-expedition from October 2002 until February 2003. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>,<br />
<strong>Universität</strong> Heidelberg.<br />
Herzog, A. 2005. Free Parameterisation of Soil Hydraulic Properties. Diplomarbeit, University of<br />
Heidelberg.<br />
Kern, C. 2004. Applicability of light-emitting diodes as light sources for long path DOAS measurements:<br />
A feasibility study. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />
Klement, R. 2005. Optimierung von SF6-Grundwasserprobenahme-Methoden. Diplomarbeit, <strong>Universität</strong><br />
Heidelberg.<br />
Kluge, T. 2005. Radon als Tracer in aquatischen Systemen. Diplomarbeit, <strong>Universität</strong> Heidelberg.<br />
Knab, V. 2004. Basic theory on DOAS tomography, Reconstruction of 2D trace gas distributions by<br />
discrete linear inversion techniques. Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg,<br />
Germany.<br />
Lindner, A. 2005. Ballongestütze Messungen der extraterrestrischen spektralen solaren Irradianz.<br />
Diploma thesis, University of Heidelberg, Heidelberg, Germany.<br />
Louban, I. 2005. Zweidimensionale Aufnahmen von Spurenstoff-Verteilungen. Diplomarbeit, <strong>Universität</strong><br />
Heidelberg.<br />
May, B. 2005. Quantification of the fossile fraction of carbonaceous aerosol by radiocarbon analysis.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg.<br />
Reichl, U. 2005. Ground-based direct Sun UV/vis spectroscopy in Timon/Northeastern Brazil: Comparison<br />
of tropospheric air mass pollution in the dry and wet season. Diploma thesis, University of<br />
Heidelberg, Heidelberg, Germany.<br />
Rice, S. 2004. The development of a method for the extraction and measurement of noble gases from<br />
fluid inclusions in samples of calcium carbonate. Master thesis, University of Heidelberg.<br />
Rippel, B. 2005. Vorarbeiten <strong>für</strong> Langpfad DOAS Tomographische Messungen über der Stadt Heidelberg.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Rocholz, R. 2005. Bildgebendes System zur simultanen Neigungs- und Höhenmessung an kleinskaligen<br />
Wind-Wasser-Wellen. diploma thesis, <strong>Universität</strong> Heidelberg.<br />
Schell, S. 2004. 222 Radon-Profil-Messungen in Süd- und Ostdeutschland, Anwendung der Radon-<br />
Tracer-Methode zur Berechnung von CO2- und CH4-Flüssen. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>,<br />
University of Heidelberg. in German.<br />
Schönherr, C. 2005 (October). Investigating Carbon Dioxide, Carbon Monoxide and Fossil Fuel CO2<br />
in Heidelberg. Diplomarbeit, Insititut <strong>für</strong> <strong>Umweltphysik</strong>, University of Heidelberg.<br />
Schwarz, T. 2005. Development of a depth resolving boundary layer visualization for gas exchange at<br />
free water surfaces. diploma thesis, <strong>Universität</strong> Heidelberg.<br />
Schwärzle, J. 2005. Spektroskopische Messung von Halogenoxiden in der marinen atmosphärischen<br />
Grenzschicht in Alcântara/Brasilien. Staatsexamensarbeit, University of Heidelberg, Heidelberg,<br />
Germany.<br />
Seitz, K. 2005. Spektroskopische Langzeitmessungen von Spurengasen in der freien Troposphäre.<br />
Diplomarbeit, <strong>Universität</strong> Heidelberg.
220 CHAPTER 7. BIBLIOGRAPHY<br />
Stelzer, A. 2005. Horizontale tomographische Langpfad-DOAS Spurengasmessungen in Heidelberg.<br />
Diplomarbeit, <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, <strong>Universität</strong> Heidelberg, Germany.<br />
Träumner, K. 2005. Inbetriebnahme, Tests und erste Anwendung einer neuen Aufbereitungslinie zur<br />
massenspektrometrischen Messung von Edelgasen aus Grundwasser - und Stalagmitproben. Diplomarbeit,<br />
<strong>Universität</strong> Heidelberg.<br />
Ulbrich, C. 2005. Monitoring Field Tracer Experiment with Ground Penetrating Radar and Time<br />
Domain Reflectometry. Diplomarbeit, University of Heidelberg.<br />
Wunderle, K. 2005. Untersuchungen der Strömungen im Willersinnweiher mit einem akustischen<br />
Strömungsmessgerät. Diplomarbeit, University of Heidelberg.
7.5. INVITED TALKS 221<br />
Invited Talks<br />
Aeschbach-Hertig, W. 2004a. Climate of the Past as a Basis for an Assessment of the Future. Invited<br />
talk, GSI-Kolloquium, Darmstadt, Germany.<br />
Aeschbach-Hertig, W. 2004b. Environmental Tracers in Groundwater Studies - Water Resources and<br />
Paleoclimate. Invited talk, <strong>Institut</strong>e of Hydrogeology and Environmental Geology, Chinese Academy<br />
of Geological Sciences, Zhengding, China.<br />
Aeschbach-Hertig, W. 2004c. Excess Air in Groundwater: Problems and Opportunities. Invited<br />
keynote presentation, Annual Meeting of the Geological Society of America (GSA), Denver, USA.<br />
Aeschbach-Hertig, W. 2004d. Noble Gases and Excess Air in Groundwater: Review and Outlook.<br />
Invited talk, KUP-Seminar, University of Bern, Switzerland.<br />
Aeschbach-Hertig, W. 2005. Surface and Subsurface Waters. Invited lecture, WE-Heraeus summerschool<br />
”Physics of the Environment”, Bad Honnef, Germany.<br />
Bobrowski, N. 2004. The DOAS (Differential Optical Absorption Spectroscopy) principle - experimental<br />
setups and mathematical description of the DOAS problem and Development of the Mini-MAX-<br />
DOAS (Multi-AXis Differntial Optical Absorption Spectroscopy) and examples of applications at<br />
three Italian volcanoes - Stromboli, Vulcano, Etna. Invited talk, Seminar INGV Palermo.<br />
Bobrowski, N. 2005a. DOAS evaluation basics. Invited talk, IAVCEI Gas workshop 9th, Nicolosi.<br />
Bobrowski, N. 2005b. The DOAS technique and the analyses of gas emissions of active volcanoes.<br />
Invited talk, Seminar ”Stoffbestand und Entwicklung von Mantel und Kruste”, Mainz.<br />
Bobrowski, N. 2005c. Volcanic research carried out with the DOAS technique - an overview. Invited<br />
talk, Seminar at CAI Pedara.<br />
Butz, A. 2005. LPMA/DOAS: Balloon based SCIAMACHY validation example: O3 and NO2 vertical<br />
profiles. Invited talk, SCIAMACHY Science Advisory Group 32, Delft, Netherlands.<br />
Jähne, B. 2004a. Exchange Processes at the Ocean Surface: Their Role in Coupling Atmosphere and<br />
Ocean, A Contribution to the SOLAS Project. Invited talk, Hauptvortrag Fachverband <strong>Umweltphysik</strong>,<br />
DPG Frühjahrstagung München, 22. Mrz 2004.<br />
Jähne, B. 2004b. New Insight into the Mechanisms of Air-Sea Gas Transfer. Invited talk, IOW-<br />
Kolloquium, Leibniz-<strong>Institut</strong> fr Ostseeforschung, Warnemünde, Januar 2004.<br />
Jähne, B., & Garbe, C. S. 2004. Spatiotemporal Active Thermography. Invited talk, 7th International<br />
Conference on Quantitative Infrared Thermography, von Karman <strong>Institut</strong>e for Fluid Dynamics in<br />
Rhode Saint Genèse, Belgium, 08. July 2004.<br />
Jähne, B., Nielsen, R., Popp, C., Schimpf, U., & Garbe, C. S. 2005. Air-Sea Gas Transfer: Schmidt<br />
Number Dependency and Intermittency. Invited talk, 37th International Liège Colloquium on Ocean<br />
Dynamics Gas Transfer at Water Surfaces, 2–6 May 2005.<br />
Levin, I. 2004a. Greenhouse Gases Trends in Europe and at the German Antarctic Station. Invited<br />
talk, WMO WMO/GAW Expert Workshop on The Quality and Applications of European GAW<br />
Measurements. Tutzing, Germany.<br />
Levin, I. 2004b. Quantification of Exchange Rates in the Global Carbon Cycle by Radiocarbon Observations.<br />
Invited talk, Physical Colloquium. University of Groningen, The Netherlands.<br />
Levin, I. 2005a. Quantifying fossil fuel CO2 over Europe. Invited talk, Workshop on A Blueprint for<br />
a GHG monitoring system in Europe. Amsterdam, The Netherlands.<br />
Levin, I. 2005b. Recent Heidelberg Radiocarbon Observations in Atmospheric CO2. Invited talk,<br />
13th International WMO Experts Meeting on atmospheric CO2 and Related Tracer Measurement<br />
Techniques. Boulder (CO) USA.<br />
Oswald, Benedikt, & Roth, Kurt. 2005. Parallel 3D Finite Element Time Domain Maxwell Solver<br />
- Investigation of Ground Penetrating Radar Sub-Wavelength Resolution. Paul Scherrer <strong>Institut</strong>,<br />
Villigen. 2005, August, 25.
222 CHAPTER 7. BIBLIOGRAPHY<br />
Pechtl, S. 2005. Halogenchemie in der Troposphäre: Überblick und Beispiele <strong>für</strong> Prozessstudien mit<br />
numerischen Modellen. Invited talk, the DLR, Oberpfaffenhofen, 15.11.2005.<br />
Pfeilsticker, K. 2005a. Collisional complexes, metastable, and stable complexes in the atmosphere,<br />
and their potential importance for the absorption of solar radiation. Invited talk, Gordon Research<br />
Conference on Radiation & Climate, Colby College, Waterville, ME, USA, July 24-29.<br />
Pfeilsticker, K. 2005b. Recent cloudy sky photon path <strong>pdf</strong> measurements from Heidelberg. Invited talk,<br />
3rd I3RC Workshop, IFM Kiel, October 11-14.<br />
Pfeilsticker, K., Lotter, A., Boesch, H., & Peters, C. 2004. Collisional complexes, metastable and stable<br />
dimers in the atmosphere, and their potential importance for the absorption of solar radiation. 228th<br />
National ACS Meeting, Philadelphia, PA, USA, August 22-26.<br />
Piot, M., & von Glasow, R. 2005. Sensitivity studies of ODEs and frost flowers with a numerical<br />
model. Invited talk, the OASIS workshop, Toronto, Canada, 20.09.2005.<br />
Platt, U. 2004a. Atmospheric Chemistry and Global Change. Invited talk, Reading, United Kingdom.<br />
Platt, U. 2004b. German SCIAMACHY Validation. Invited talk, SCIAMACHY Validation project<br />
final workshop, Bremen.<br />
Platt, U. 2004c. Reactive Halogen Species in the Troposphere. Invited talk, AFO-2000 Abschluß<br />
Workshop, Bad Tölz, 22.-2. März.<br />
Platt, U. 2004d. Spectroscopic Mapping of Trace Gases by Differential Optical Absorption Spectroscopy<br />
(DOAS). Invited talk, Massachusetts <strong>Institut</strong>e of Technology, Boston, Mass, USA.<br />
Platt, U. 2005a. Atmospheric Chemistry and Global Change. Invited talk, Advanced Environmental<br />
Monitoring Research Center, K-JIST, Kwangju, S. Korea.<br />
Platt, U. 2005b. Atmospheric Gas Phase Reactions. Invited talk, SOLAS Summer School, Cargese,<br />
Corsica, France.<br />
Platt, U. 2005c. The Determination of Reactive Halogen Species in the Troposphere and their Relevance<br />
for Atmospheric Chemistry. Invited talk, Workshop des DFG-Graduiertenkollegs 826,<br />
Elementspeziation: Methodenentwicklung und ihre Anwendung in den Umwelt- und Lebenswissenschaften,<br />
Mainz.<br />
Platt, U. 2005d. Neue Entwicklungen der atmosphärischen Spektroskopie - wie BERLIOZ II aussehen<br />
könnte. Invited talk, Seminar, Bergische <strong>Universität</strong> Wuppertal.<br />
Platt, U. 2005e. Observation of Spatial Distributions of Air Pollutants. Plenary lecture, Royal Meteorological<br />
Society Conference 2005, 12th-16th Sept. 2005, at the University of Exeter.<br />
Platt, U. 2005f. Ocean - Atmosphere Exchanges and Interactions. Invited talk, IGAC/WMO WORK-<br />
SHOP: From Chemical Weather Forecast to Climate Change in South America: the challenges and<br />
opportunities of integration and collaboration, Centro de Modelamiento Matemático, Universidad<br />
de Chile, Santiago de Chile.<br />
Platt, U. 2005g. Probing the Atmosphere with Differential Optical Absorption Spectroscopy - DOAS.<br />
Invited talk, Advanced Environmental Monitoring Research Center, K-JIST, Kwangju, S. Korea.<br />
Platt, U., & Burrows, J. P. 2005. The Remote Sensing of Atmospheric Constituents From Space,<br />
ACCENT-TROPOSAT-2 (AT2): An ACCENT Integration Task. Invited talk, ACCENT General<br />
Assembly, Clermont Ferrant, 9-11 Februar.<br />
Platt, U., & Zingler, J. 2006. Spatial Distribution of Halogen Oxides in the Dead Sea Basin, Israel<br />
Society for Ecology and Environmental Quality Sciences. Invited talk, Conference on ”Living with<br />
Global Change: Challenges in Environmental Sciences”, May 30 - June 1, 2005, Weizmann <strong>Institut</strong>e<br />
of Science, Israel.<br />
Platt, U., Sinreich, R., Friesß, U., & Wagner, T. 2005. Multi Axis Differential Optical Absorption Spectroscopy<br />
(MAX-DOAS) of Gas and Aerosol Distributions. Invited talk, 130th Faraday Discussion<br />
Meeting ”Atmospheric Chemistry”, Leeds, United Kingdom.
7.5. INVITED TALKS 223<br />
Pundt, I. 2005. DOAS (Differentielle Optische Absorptions- Spektroskopie) Messungen mit neuester<br />
Technologie. Invited talk, DECHEMA/GDCH/DGB-Gemeinschaftsausschuss Chemie der Atmosphre,<br />
Frankfurt, 22.04.2005.<br />
Pundt, I., Mettendorf, K.U., & v. Friedeburg, C. 2005. Emissionsmessung von NO2, SO2 und O3<br />
mittels DOAS Fernerkundung. Invited talk, workshop ”Validierung von Kfz-Emissionsdaten: Das<br />
<strong>Karls</strong>ruher Autobahnprojekt BAB II”, <strong>Karls</strong>ruhe, 01.12.2005.<br />
Roth, K. 2005a. Bodenwasser: Bedeutung – Herausforderung – Messung. Eröffnungsvortrag, Soil<br />
Moisture Group, <strong>Universität</strong> <strong>Karls</strong>ruhe, 8. Juni.<br />
Roth, K. 2005b. GPR zur Quantifizierung von Transportprozessen in Böden? <strong>Institut</strong> <strong>für</strong> Geophysik,<br />
<strong>Universität</strong> Kiel, 20. Mai.<br />
Roth, K. 2005c. Measurement and Modeling of Thermal and Hydraulic Dynamics of Permafrost Soils.<br />
Dept. of Earth Sciences, Uppsala University, March 31.<br />
Roth, K., & Wollschläger, U. 2005. Field-Scale Measurement of Soil Water Content. Plenary Session<br />
at International Conference on Human Impacts on Soil Quality Attributes, Isfahan, Iran, September<br />
12–16.<br />
Vogel, H.-J. 2005a. From Pore- to Continuum-Scale Understanding of Flow and Transport Processes<br />
in Porous Media. Keynote paper, SSSA-Annual Meeting, November 7-11, 2005, Salt Lake City,<br />
USA.<br />
Vogel, H.-J. 2005b. Hierarchies of flow and transport in soil. Keynote paper, GFHN, 29emes journees,<br />
November 24-25, 2004, Grenoble, France.<br />
Vogel, H.-J. 2005c. Modeling the heterogeneous structure of soil to predict flow and transport. SIAM<br />
Conference on Mathematical and Computational Issues in the Geosciences, June 7-10, 2005, Avignon,<br />
France.<br />
Vogel, H.-J., Samouelian, A., & Ippisch, O. 2005. Modeling structure to predict flow and transport.<br />
Gesellschaft <strong>für</strong> Angewandte Mathematik und Mechanik, 76th Annual Scientific Conference, March<br />
28 - April 1, 2005, Luxembourg.<br />
von Glasow, R. 2004a. Halogenchemie in der Troposphäre - Untersuchungen mit numerischen Modellen.<br />
Invited talk, the Insitut <strong>für</strong> Meteorologie und Klimaforschung, <strong>Karls</strong>ruhe, 02.11.2004.<br />
von Glasow, R. 2004b. Links between sulfur and halogen chemistry and implications for our climate.<br />
Invited talk, the Afred-Wegener-<strong>Institut</strong> <strong>für</strong> Meeresforschung, Bremerhaven, 05.02.2004.<br />
von Glasow, R. 2004c. Modeling of halogen chemistry: Overview and impact on sulfur cycle. Invited<br />
talk, the EGU meeting, Nice, 2004.<br />
von Glasow, R. 2004d. Sea salt aerosol chemistry: Brief overview and recent modeling results. Invited<br />
talk, the AAAR meeting, Atlanta, 2004.<br />
von Glasow, R. 2004e. Tropospheric halogen chemistry and its implications for O3 and sulfur in<br />
the boundary layer and free troposphere. Invited talk, the <strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong>, Bremen,<br />
06.02.2004.<br />
von Glasow, R. 2005a. Invited talk, the AGU meeting, San Francisco, 2005.<br />
von Glasow, R. 2005b. Halogenchemie in der Troposphäre - Untersuchungen der Wechselwirkungen<br />
mit Ozon und Schwefel in Prozess- und globalen Modellstudien. Invited talk, the <strong>Institut</strong> <strong>für</strong><br />
Troposphärenforschung, Leipzig, 12.05.2005.<br />
von Glasow, R. 2005c. Impact of bromine on tropospheric photochemistry. Invited talk, the<br />
IGAC/SPARC workshop, Mainz, 19.05.2005.<br />
von Glasow, R. 2005d. Importance of the surface reaction OH + Cl- on sea salt aerosol for the<br />
chemistry of the MBL - a model study. Invited talk, the EMSI Workshop on Ions and Molecules at<br />
Aqueous Interfaces, Prague, Czech Republic, 27.06.2005.<br />
von Glasow, R. 2005e. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk,<br />
NIWA, Lauder, New Zealand, 15.09.2005.
224 CHAPTER 7. BIBLIOGRAPHY<br />
von Glasow, R. 2005f. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk,<br />
Harvard Univ., Cambridge, MA, USA, 08.04.2005.<br />
von Glasow, R. 2005g. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk, the<br />
Univ. New Hampshire, Durham, USA, 07.04.2005.<br />
von Glasow, R. 2005h. Reactive halogen chemistry in the troposphere - Using numerical models for<br />
detailed process studies of the marine boundary layer and a first global assessment. Invited talk, the<br />
Univ. of East Anglia, Norwich, UK, 28.02.05.<br />
Wagenbach, D. 2004. Potential and restrictions of Alpine (mid-latitude) ice cores. Invited talk, SCIEM<br />
2000 (The synchronisation of civilization in the eastern Mediterranean in the 2nd Millenium BC)<br />
Workshop: Ashes and Ice, Vienna.<br />
Wagner, T. 2004a. Current status and future perspectives of atmospheric trace gas observations from<br />
space. Invited talk, <strong>Institut</strong>e Colloquium, MPI Mainz, Germany.<br />
Wagner, T. 2004b. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />
UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk, SO-<br />
LAS Science conference, Halifax, Canada.<br />
Wagner, T. 2004c. Global monitoring of atmospheric trace gases, clouds and aerosols from<br />
UV/vis/NIR satellite instruments: Currents status and near future perspectives. Invited talk,<br />
WMO/GAW Expert Workshop, Tutzing, Germany.<br />
Wagner, T. 2004d. Moderne Methoden der Satellitenbildverarbeitung: Spektroskopie, Reflektions-,<br />
Streu-, und Absorptionsprozesse. Invited talk, WMO/GAW Expert Workshop, Tutzing, Germany.<br />
Wagner, T. 2005a. 7.5-year global trends in GOME cloud cover and humidity - a signal of climate<br />
change? Invited talk, KNMI, Utrecht, The Netherlands.<br />
Wagner, T. 2005b. Troposphärische Spurengasmessungen vom Satelliten aus. Invited talk,<br />
DECHEMA, Frankfurt, Germany.<br />
Wagner, T. 2005c. Wasserdampf-Fernerkundung mit dem ERS-2/GOME Sensor und seinen Nachfolgern.<br />
Invited talk, DWD, Offenbach, Germany.<br />
Zingler, J. 2005. Eine kurze Geschichte von Messungen zur Halogenchemie am Toten Meer, Israel.<br />
Invited talk, Seminar über aktuelle Forschungsthemen der Meteorologie, <strong>Institut</strong> <strong>für</strong> Meteorologie<br />
und Klimaforschung, Forschungszentrum <strong>Karls</strong>ruhe, <strong>Karls</strong>ruhe, Germany.
<strong>Institut</strong> <strong>für</strong> <strong>Umweltphysik</strong><br />
Im Neuenheimer Feld 229<br />
69120 Heidelberg<br />
Germany<br />
Tel. + 49 6221 54-63 50<br />
Fax + 49 6221 54-64 05<br />
email: sekretariat@iup.uni-heidelberg.de<br />
www.iup.uni-heidelberg.de<br />
Board of Directors<br />
Prof. Dr. Ulrich Platt<br />
Prof. Dr. Kurt Roth