Application of comprehensive gas chromatography (GCxGC) to measurements of volatile organic species in ambient air

The focus of this thesis was the in-situ application of the new analytical technique "GCxGC" in both the marine and continental boundary layer, as well as in the free troposphere. Biogenic and anthropogenic VOCs were analysed and used to characterise local chemistry at the individual measurement sites. The first part of the thesis work was the characterisation of a new set of columns that was to be used later in the field. To simplify the identification, a time-of-flight mass spectrometer (TOF-MS) detector was coupled to the GCxGC. In the field the TOF-MS was substituted by a more robust and tractable flame ionisation detector (FID), which is more suitable for quantitative measurements. During the process, a variety of volatile organic compounds could be assigned to different environmental sources, e.g. plankton sources, eucalyptus forest or urban centers. In-situ measurements of biogenic and anthropogenic VOCs were conducted at the Meteorological Observatory Hohenpeissenberg (MOHP), Germany, applying a thermodesorption-GCxGC-FID system. The measured VOCs were compared to GC-MS measurements routinely conducted at the MOHP as well as to PTR-MS measurements. Furthermore, a compressed ambient air standard was measured from three different gas chromatographic instruments and the results were compared. With few exceptions, the in-situ, as well as the standard measurements, revealed good agreement between the individual instruments. Diurnal cycles were observed, with differing patterns for the biogenic and the anthropogenic compounds. The variability-lifetime relationship of compounds with atmospheric lifetimes from a few hours to a few days in presence of O3 and OH was examined. It revealed a weak but significant influence of chemistry on these short-lived VOCs at the site. The relationship was also used to estimate the average OH radical concentration during the campaign, which was compared to in-situ OH measurements (1.7 x 10^6 molecules/cm^3, 0.071 ppt) for the first time. The OH concentration ranging from 3.5 to 6.5 x 10^5 molecules/cm^3 (0.015 to 0.027 ppt) obtained with this method represents an approximation of the average OH concentration influencing the discussed VOCs from emission to measurement. Based on these findings, the average concentration of the nighttime NO3 radicals was estimated using the same approach and found to range from 2.2 to 5.0 x 10^8 molecules/cm^3 (9.2 to 21.0 ppt). During the MINATROC field campaign, in-situ ambient air measurements with the GCxGC-FID were conducted at Tenerife, Spain. Although the station is mainly situated in the free troposphere, local influences of anthropogenic and biogenic VOCs were observed. Due to a strong dust event originating from Western Africa it was possible to compare the mixing ratios during normal and elevated dust loading in the atmosphere. The mixing ratios during the dust event were found to be lower. However, this could not be attributed to heterogeneous reactions as there was a change in the wind direction from northwesterly to southeasterly during the dust event.

Copper and zinc stable isotope ratios as tracers of biogeochemical processes, sources and transport of Cu and Zn in soils

Copper and Zn are essential micronutrients for plants, animals, and humans; however, they may also be pollutants if they occur at high concentrations in soil. Therefore, knowledge of Cu and Zn cycling in soils is required both for guaranteeing proper nutrition and to control possible risks arising from pollution.rnThe overall objective of my study was to test if Cu and Zn stable isotope ratios can be used to investigate into the biogeochemistry, source and transport of these metals in soils. The use of stable isotope ratios might be especially suitable to trace long-term processes occurring during soil genesis and transport of pollutants through the soil. In detail, I aimed to answer the questions, whether (1) Cu stable isotopes are fractionated during complexation with humic acid, (2) 65Cu values can be a tracer for soil genetic processes in redoximorphic soils (3) 65Cu values can help to understand soil genetic processes under oxic weathering conditions, and (4) 65Cu and 66Zn values can act as tracers of sources and transport of Cu and Zn in polluted soils.rnTo answer these questions, I ran adsorption experiments at different pH values in the laboratory and modelled Cu adsorption to humic acid. Furthermore, eight soils were sampled representing different redox and weathering regimes of which two were influenced by stagnic water, two by groundwater, two by oxic weathering (Cambisols), and two by podzolation. In all horizons of these soils, I determined selected basic soil properties, partitioned Cu into seven operationally defined fractions and determined Cu concentrations and Cu isotope ratios (65Cu values). Finally, three additional soils were sampled along a deposition gradient at different distances to a Cu smelter in Slovakia and analyzed together with bedrock and waste material from the smelter for selected basic soil properties, Cu and Zn concentrations and 65Cu and 66Zn values.rnMy results demonstrated that (1) Copper was fractionated during adsorption on humic acid resulting in an isotope fractionation between the immobilized humic acid and the solution (65CuIHA-solution) of 0.26 ± 0.11‰ (2SD) and that the extent of fractionation was independent of pH and involved functional groups of the humic acid. (2) Soil genesis and plant cycling causes measurable Cu isotope fractionation in hydromorphic soils. The results suggested that an increasing number of redox cycles depleted 63Cu with increasing depth resulting in heavier 65Cu values. (3) Organic horizons usually had isotopically lighter Cu than mineral soils presumably because of the preferred uptake and recycling of 63Cu by plants. (4) In a strongly developed Podzol, eluviation zones had lighter and illuviation zones heavier 65Cu values because of the higher stability of organo-65Cu complexes compared to organo-63Cu complexes. In the Cambisols and a little developed Podzol, oxic weathering caused increasingly lighter 65Cu values with increasing depth, resulting in the opposite depth trend as in redoximorphic soils, because of the preferential vertical transport of 63Cu. (5) The 66Zn values were fractionated during the smelting process and isotopically light Zn was emitted allowing source identification of Zn pollution while 65Cu values were unaffected by the smelting and Cu emissions isotopically indistinguishable from soil. The 65Cu values in polluted soils became lighter down to a depth of 0.4 m indicating isotope fractionation during transport and a transport depth of 0.4 m in 60 years. 66Zn values had an opposite depth trend becoming heavier with depth because of fractionation by plant cycling, speciation changes, and mixing of native and smelter-derived Zn. rnCopper showed measurable isotope fractionation of approximately 1‰ in unpolluted soils, allowing to draw conclusions on plant cycling, transport, and redox processes occurring during soil genesis and 65Cu and 66Zn values in contaminated soils allow for conclusions on sources (in my study only possible for Zn), biogeochemical behavior, and depth of dislocation of Cu and Zn pollution in soil. I conclude that stable Cu and Zn isotope ratios are a suitable novel tool to trace long-term processes in soils which are difficult to assess otherwise.rn

Global simulated soil biogenic nitric oxide (NO) emissions: Impact, improvement and innovation

rnNitric oxide (NO) is important for several chemical processes in the atmosphere. Together with nitrogen dioxide (NO2 ) it is better known as nitrogen oxide (NOx ). NOx is crucial for the production and destruction of ozone. In several reactions it catalyzes the oxidation of methane and volatile organic compounds (VOCs) and in this context it is involved in the cycling of the hydroxyl radical (OH). OH is a reactive radical, capable of oxidizing most organic species. Therefore, OH is also called the “detergent” of the atmosphere. Nitric oxide originates from several sources: fossil fuel combustion, biomass burning, lightning and soils. Fossil fuel combustion is the largest source. The others are, depending on the reviewed literature, generally comparable to each other. The individual sources show a different temporal and spatial pattern in their magnitude of emission. Fossil fuel combustion is important in densely populated places, where NO from other sources is less important. In contrast NO emissions from soils (hereafter SNOx) or biomass burning are the dominant source of NOx in remote regions.rnBy applying an atmospheric chemistry global climate model (AC-GCM) I demonstrate that SNOx is responsible for a significant part of NOx in the atmosphere. Furthermore, it increases the O3 and OH mixing ratio substantially, leading to a ∼10% increase in the oxidizing efficiency of the atmosphere. Interestingly, through reduced O3 and OH mixing ratios in simulations without SNOx, the lifetime of NOx increases in regions with other dominating sources of NOx

Räumliche und jahreszeitliche Verteilung von OH- und HO 2-Radikalen in der Troposphäre über Europa

Durch geologische Prozesse freigesetzte sowie biogen und anthropogen emittierte Gase werden hauptsächlich von der untersten Atmosphärenschicht, der Troposphäre, aufgenommen und abgebaut. Durch in die Troposphä¬re einfallende solare Strahlung wird ein Abbau des Großteils der emittierten Spurengase durch reaktive Radikale initiiert. Der wichtigste Vertreter dieser reaktiven Radikale in der Troposphäre ist das Hydroxylradikal (OH-Radikal), welches im schnellen Gleichgewicht mit Hydroperoxyradikalen (HO2-Radikal) vorliegt, sodass die Summe aus OH- und HO2-Radikalen oft als HOx zusammengefasst wird. HOx-Radikale bilden tagsüber den Hauptteil der Oxidationskapazität der Troposphäre und sind somit verantwortlich für den oxidativen Abbau vieler, auch chemisch und photolytisch stabiler, Spurengase. Daher wird die Oxidationskapazität als Selbstreinigungskraft der Troposphäre verstanden. rnIm Rahmen meiner Arbeit wurde die wissenschaftliche Fragestellung auf die Oxidationskapazität der Troposphäre über Europa fokussiert. Die Höhen- und Breitenverteilung der OH- und HO2-Mischungsverhältnisse und ihre jahreszeitliche Variation wurde während der flugzeuggestützten HOOVER-Kampagnen (HOOVER 1 & 2) charakterisiert, wobei ein Fokus auf der oberen Troposphäre lag. Es wird gezeigt, welchen Einfluss die einfallende Strahlung, die Variation von HOx-Vorläufersubstanzen (wie z. B. Ozon) und die Variation von Substanzen, die das HOx-Gleichgewicht beeinflussen (z. B. Stickstoffmonoxid), auf das HOx-Budget haben. rnEs wird beispielhaft für den Höhenbereich zwischen 8 und 9.5 km gezeigt, dass die Oxidationskapazität in der oberen Troposphäre des Sommers im Ver¬gleich zu der des Herbstes aufgrund von einer verstärkten HO2-Zyklierung im Mittel deutlich erhöht ist (500 %). rnDurch konvektiven Transport werden im Sommer im Gegensatz zum Herbst regelmäßig Luftmassen aus der planetaren Grenzschicht in die obere Troposphäre eingemischt. Daher wurden der konvektive Luftmassentransport und der Einfluss der eingemischten Spurengase auf die Oxidationskapazität der oberen Troposphäre anhand eines konvektiven Elements über Südostdeutschland untersucht. Wie in dieser Arbeit berichtet wird, wurden in den Luftmassen der Ausströmregion mit bis zu 3.5 pmol/mol (Maximum 10 s-Mittelwert) sehr hohe OH-Mischungsverhältnisse gefunden, die aus der HO2-Konversion mit NO gebildet wurden. Das modellierte HOx-Budget zeigt, dass die HOx-Chemie - unter den beobachteten Bedingungen in der Ausströmregion - durch HOx-Zyklierungsreaktionen beherrscht wird. rnDie gemessenen OH-Mischungsverhältnisse in der Ausströmregion liegen etwa um einen Faktor fünf höher, als die während dieses Fluges in der konvektiv unbeeinflussten oberen Troposphäre gemessenen OH-Mischungsverhältnisse. Am Beispiel der NO2- und CH4-Lebensdauer wird ein schnellerer Abbau von Spurengasen aufgrund der erhöhten Oxidationskapazität nachgewiesen. Aus der NO2-Lebensdauer wird abgeschätzt, wie lange die Oxidationskapazität aufgrund des konvektiven Transports von NOx in den Luftmassen des Ausströmgebietes erhöht ist.rnDie während den Kampagnen durchgeführten Messungen wurden genutzt, um Modellberechnungen des vertikalen HOx-Budgets (über Südschweden) und des meridionalen HOx-Budgets zwischen Nordeuropa und Korsika durchzuführen. Es wurde gezeigt, dass das Modell die OH- und HO2-Mischungsverhältnisse im Allgemeinen gut reproduziert (Modell/Messung: OH im Sommer 94 %, HO2 im Sommer 93 % im Herbst 95 %), wohingegen die vergleichsweise kleinen OH-Mischungsverhältnisse im Herbst aufgrund von einer überschätzten H2O2 abhängigen OH-Produktion stark überschätzt wurden (Modell/Messung: 147 %). rnZur Charakterisierung der Oxidationskapazität innerhalb der planetaren Grenzschicht wurden die DOMINO-Kampagnen durchgeführt. Dabei wurde die Zusammensetzung unterschiedlicher Luftmassen untersucht, die aus verschiedenen Herkunftsorten zum Messort transportiert wurden und aufgrund ihres Ursprungs kaum prozessierte bis prozessierte anthropogen emittierte Spurengase enthielten. Zusätzlich enthielt ein Teil der Luftmassen biogen emittierte Spurengase. Komplementäre Messungen ermöglichen die Berechnung der totalen OH-Produktion und den Vergleich mit den bekannten OH-Quellen. Der Vergleich zeigt, dass offenbar wichtige OH-Produktionskanäle durch die gemessenen Spurengase oder die durchgeführten Berechnungen nicht abgebildet werden. Es wird gezeigt, dass die Stärke der unbekannten OH-Quellen, vor allem unter niedrigen NO-Bedingungen, groß ist und mit den Isopren-, RO2- und HO2-Mischungsverhältnissen korreliert.rn