Modulation of apoptosis by endogenously produced nitric oxide

Untersuchungen zur Expression der induzierbaren NO-Synthetase (NOS2) belegen eine häufige Expression dieses Enzyms in Tumoren unterschiedlicher Gewebe. Bislang ist jedoch ungeklärt, ob die Expression der NOS2 in Tumorzellen die apoptotische Eliminierung durch zytotoxische T-Zellen beeinflussen kann. In der vorliegenden Arbeit wurden die Folgen einer endogenen NO-Synthese auf die Apoptosesensitivität von HEK293-Zellen untersucht. Um primäre NO-Wirkungen von NO-induzierten, sekundären (kompensatorischen) Veränderungen zu trennen, wurde mit einem induzierbaren Vektorsystem gearbeitet. Die NOS2 wurde zunächst unter der Kontrolle eines Ecdyson-sensitiven Promoters in HEK293-Zellen kloniert. Es konnten regulierbare NOS2-Klone selektiert werden, die nach Ponasteronbehandlung dosisabhängig die NOS2 exprimieren und NO synthetisieren. Die NOS2-Expression wurde durch Western Blot Analyse und Immunfluoreszenzfärbung dargestellt und die NO-Produktion mit Hilfe der Griess-Reaktion gemessen. An den NOS2-induzierten Zellen wurde dann der Einfluss von NO auf die CD95-vermittelte Apoptose analysiert. Es zeigte sich nach Stimulation des CD95-Rezeptors eine deutliche Korrelation der Apoptoserate mit der NOS2-Expression. In Kokulturexperimenten mit Peptid-spezifischen zytotoxischen T-Zellen zeigte sich, dass NO-produzierende Zielzellen effektiver eliminiert werden konnten. Auch nach Behandlung der Zellen mit TRAIL ergab sich eine höhere Apoptoserate in NO-produzierenden Zellen. Die weitere Analyse der durch NO beeinflussten Signalwege ergab eine Beteiligung von ER-Stress-vermittelten Apoptosewegen. Dies zeigte sich an der Hochregulation des ER-Stress-Proteins Grp78 (BiP) nach NOS2-Expression und der Spaltung der am ER-lokalisierten Caspase-4. Darüber hinaus konnte der schnellere Verlust des mitochondrialen Membranpotentials in Abhängigkeit von der NOS2-Expression nachgewiesen werden. Weiterhin wurde die Wirkung einer dauerhaften NO-Exposition auf die Apoptosesensitivität der Zellen untersucht. Auch ohne zusätzliche CD95-Stimulation induzierte eine kontinuierliche NOS2-Expression nach wenigen Tagen in den EcR293-NOS2-Zellen Apoptose. Diese Dauerbehandlung führte zum nahezu vollständigen Absterben der Kulturen. Einige Zellen überlebten jedoch diese Behandlung und wuchsen zu Zellklonen. Diese NO-resistenten Klone konnten isoliert werden. Sie zeigten eine zusätzliche Resistenz für CD95-vermittelte Apoptosesignale und waren besser vor dem Angriff Peptid-spezifischer CTLs geschützt. Die Apoptoseresistenz blieb auch nach längerer Kultur erhalten und scheint auf NO-induzierter Genotoxizität zu beruhen. Anhand dieser Arbeit konnte gezeigt werden, dass allein durch chronische NO-Behandlung eine Selektion apoptoseresistenter Zellen stattfinden kann.

Soil biogenic emissions of nitric oxide from arid and semi-arid ecosystems

The biogenic production of NO in the soil accounts for between 10% and 40% of the global total. A large degree of the uncertainty in the estimation of the biogenic emissions stems from a shortage of measurements in arid regions, which comprise 40% of the earth’s land surface area. This study examined the emission of NO from three ecosystems in southern Africa which cover an aridity gradient from semi-arid savannas in South Africa to the hyper-arid Namib Desert in Namibia. A laboratory method was used to determine the release of NO as a function of the soil moisture and the soil temperature. Various methods were used to up-scale the net potential NO emissions determined in the laboratory to the vegetation patch, landscape or regional level. The importance of landscape, vegetation and climatic characteristics is emphasized. The first study occurred in a semi-arid savanna region in South Africa, where soils were sampled from 4 landscape positions in the Kruger National Park. The maximum NO emission occurred at soil moisture contents of 10%-20% water filled pore space (WFPS). The highest net potential NO emissions came from the low lying landscape positions, which have the largest nitrogen (N) stocks and the largest input of N. Net potential NO fluxes obtained in the laboratory were converted in field fluxes for the period 2003-2005, for the four landscape positions, using soil moisture and temperature data obtained in situ at the Kruger National Park Flux Tower Site. The NO emissions ranged from 1.5-8.5 kg ha-1 a-1. The field fluxes were up-scaled to a regional basis using geographic information system (GIS) based techniques, this indicated that the highest NO emissions occurred from the Midslope positions due to their large geographical extent in the research area. Total emissions ranged from 20x103 kg in 2004 to 34x103 kg in 2003 for the 56000 ha Skukuza land type. The second study occurred in an arid savanna ecosystem in the Kalahari, Botswana. In this study I collected soils from four differing vegetation patch types including: Pan, Annual Grassland, Perennial Grassland and Bush Encroached patches. The maximum net potential NO fluxes ranged from 0.27 ng m-2 s-1 in the Pan patches to 2.95 ng m-2 s-1 in the Perennial Grassland patches. The net potential NO emissions were up-scaled for the year December 2005-November 2006. This was done using 1) the net potential NO emissions determined in the laboratory, 2) the vegetation patch distribution obtained from LANDSAT NDVI measurements 3) estimated soil moisture contents obtained from ENVISAT ASAR measurements and 4) soil surface temperature measurements using MODIS 8 day land surface temperature measurements. This up-scaling procedure gave NO fluxes which ranged from 1.8 g ha-1 month-1 in the winter months (June and July) to 323 g ha-1 month-1 in the summer months (January-March). Differences occurred between the vegetation patches where the highest NO fluxes occurred in the Perennial Grassland patches and the lowest in the Pan patches. Over the course of the year the mean up-scaled NO emission for the studied region was 0.54 kg ha-1 a-1 and accounts for a loss of approximately 7.4% of the estimated N input to the region. The third study occurred in the hyper-arid Namib Desert in Namibia. Soils were sampled from three ecosystems; Dunes, Gravel Plains and the Riparian zone of the Kuiseb River. The net potential NO flux measured in the laboratory was used to estimate the NO flux for the Namib Desert for 2006 using modelled soil moisture and temperature data from the European Centre for Medium Range Weather Forecasts (ECMWF) operational model on a 36km x 35km spatial resolution. The maximum net potential NO production occurred at low soil moisture contents (<10%WFPS) and the optimal temperature was 25°C in the Dune and Riparian ecosystems and 35°C in the Gravel Plain Ecosystems. The maximum net potential NO fluxes ranged from 3.0 ng m-2 s-1 in the Riparian ecosystem to 6.2 ng m-2 s-1 in the Gravel Plains ecosystem. Up-scaling the net potential NO flux gave NO fluxes of up to 0.062 kg ha-1 a-1 in the Dune ecosystem and 0.544 kg h-1 a-1 in the Gravel Plain ecosystem. From these studies it is shown that NO is emitted ubiquitously from terrestrial ecosystems, as such the NO emission potential from deserts and scrublands should be taken into account in the global NO models. The emission of NO is influenced by various factors such as landscape, vegetation and climate. This study looks at the potential emissions from certain arid and semi-arid environments in southern Africa and other parts of the world and discusses some of the important factors controlling the emission of NO from the soil.

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