L’explosion de la nanotechnologie a permis l’intégration d’une multitude de nanoparticules dans des produits de consommation. Les nanoparticules d’argent (nAg) sont les plus utilisées à ces fins, selon les derniers recensements disponibles. La plupart des études toxicologiques, à ce jour, ont fait état de l’implication très évidente de l’ion Ag+ dans la toxicité aigüe des nAg; cependant, quelques études ont mis en évidence des effets toxicologiques dus aux nAg. Il y a un certain consensus à propos d’un risque de contamination des eaux douces via leur rejet par les effluents des réseaux d’aqueducs. Puisque les concentrations en Ag+ sont généralement très faibles dans les eaux douces (de l’ordre du pg L-1), de par la formation de complexes non-labiles avec des thiols (organiques et inorganiques) et des sulfures, la toxicité inhérente aux nAg pourrait ne pas être négligeable- comparativement aux tests en laboratoires. Cette étude s’intéressait donc aux mécanismes de bioaccumulation d’argent par l’algue verte C. reinhardtii suite à l’exposition à des nAg de 5 nm (enrobage d’acide polyacrylique). La bioaccumulation d’argent pour l’exposition à Ag+ servait de point de comparaison; également, les abondances de l’ARNm de l’isocitrate lyase 1 (ICL1) et de l’ARNm de Copper Transporter 2 (CTR2) étaient mesurées comme témoins biologiques de la bioaccumulation de Ag+. Les expériences ont été menées en présence d’un tampon organique (NaHEPES, 2 x 10-2 M; Ca2+, 5x 10-5 M) à pH de 7,00. Pour des expositions à temps fixe de 2 heures, la bioaccumulation d’argent pour nAg était supérieure à ce qui était prédit par sa concentration initiale en Ag+; cependant, il n’y avait pas de différence d’abondance des ARNm de ICL1 et de CTR2 entre nAg et Ag+. D’un autre côté, pour une exposition à temps variables, la bioaccumulation d’argent pour nAg était supérieure à ce qui était prédit par sa concentration initiale en Ag+ et une augmentation de l’abondance de l’ARNm de ICL1 était notée pour nAg. Cependant, il n’y avait aucune différence significative au niveau de l’abondance de l’ARNm de CTR2 entre nAg et une solution équivalente en Ag+. L’ajout d’un fort ligand organique (L-Cystéine; log K= 11,5) à une solution de nAg en diminuait radicalement la bioaccumulation d’argent par rapport à nAg-sans ajout de ligand. Par contre, l’abondance des ARNm de ICL1 et de CTR2 étaient stimulées significativement par rapport à une solution contrôle non-exposée à nAg, ni à Ag+. Les résultats suggéraient fortement que les nAg généraient des ions Ag+ au contact de C. reinhardtii. / The recent developments in nanotechnology have given rise to a new and increasing economical market where nanoparticles are at the forefront. Recent inventories of the nanoparticles-containing products have shown that silver nanoparticle- containing products are the most frequently used consumer nanomaterial. Due to the fear of a large scale contamination-and even pollution- of the aquatic environment from silver nanoparticles (nAg), studies have been conducted to assess their toxicities, which, in many cases, have been found to be mediated by the concomitant presence of Ag+. Notably, few studies have found evidence of toxicity due to the nAg, per se. Since numerous non-labile complexes are formed with Ag+ in freshwaters- especially with thiols and sulfides-, nAg toxicity might be more relevant in comparison to laboratory tests where the Ag+ tends to dominate toxicity studies. Therefore, this study investigated the mechanisms underlying silver bioaccumulation by the green alga, C. reinhardtii upon exposure to solutions of nAg (nominal size of 5 nm; poly-acrylate coating). Silver bioaccumulation upon exposures to the free ion alone served for comparison. In parallel, the abundance of two mRNAs- ICL1 and CTR2- were used to better understand the mechanisms underlying the bioaccumulation of Ag+ (and potentially nAg). The experiments were conducted in pH buffered solutions (NaHEPES, 2 x 10-2 M; Ca2+, 5x 10-5 M) at pH 7.00. For 2-hour exposures, the silver bioaccumulation for solutions of nAg exceeded what was expected from their Ag+ content only; however, no differences were noticed in the abundance of the expression of ICL1 and CTR2. For variable time exposures, the silver bioaccumulation for solutions of nAg exceeded what was expected from their Ag+ content only. Moreover, the expression of ICL1 was significantly higher for nAg than what was expected based upon an exposure to Ag+ only. When exposed to nAg, expression levels of CTR2 could be predicted from levels based solely on the Ag+ concentrations. The addition of a large excess of L-Cysteine, which is a very strong silver ligand (log K =11.5), to a nAg solution largely decreased silver bioaccumulation, however, bioaccumulation remained significant and the expression of both ICL1 and CTR2 were significantly higher than that of the control solutions (without Ag+). The results strongly suggest that nAg generated Ag+ ions when in contact with C. reinhardtii and that the nAg released to freshwaters might exert its toxicity through organism-contact-dependant release of Ag+.

When conspecific individuals are crossed, the ensuing hybridization creates a spectrum of phenotypes in the resulting offspring. Many of hybrid traits will be additive, similar to the parental phenotypes. In some cases however, transgressive phenotypes are formed, outside the range of that of the parental phenotypes. Transgressive phenotypes can either be restricted to the F1 generation or be heritable throughout the hybrid lineage. While the mechanism behind heritable transgressive phenotyped is yet to be determined, transgressive gene expression is thought to be the root cause of their formation. Epigenetics modifications, heritable variation separate to the DNA code, can alter gene expression, persist through generations, and vary between individuals and over time. This makes them ideal candidates to be involved in the formation of transgressive phenotypes. RNA silencing is an epigenetic mechanism of gene regulation relying on 20Q24nt single stranded small RNAs (sRNAs). Small RNAs, due to their ability to set up persistent epigenetic marks at a locus, have the potential to create heritable transgressive gene expression. For example, when genetic variation from one parental genome presents novel targets to the sRNAs of the other parental genome, new epigenetic marks such as DNA methylation or secondary sRNAs can be created at target sites. In order to understand the potential of small RNAs to influence hybrid phenotype, I designed crossing experiments with Chlamydomonas reinhardtii, choosing this unicellular alga due to the genetic tools available and the haploid nature of its vegetative cells. The specific aim of the experiment was to identify transgressively expressed sRNA populations. Crossing two geographically distinct strains of C. reinhardtii, and sequencing both the genomes and sRNAomes of parents and recombinants, I was able catalogue both genetic and epigenetic variation in the parental strains providing unique insight into the inheritance of small RNAs in this alga. In this thesis, I first compare the genomes of the parental strains, identifying polymorphisms and assessing genetic variation in RNA silencing pathway components. I then describe the sRNA profiles of the parental strains, identifying differentially expressed sRNA loci. I then describe my approach to identifying transgressively expressed sRNA loci in the hybrids. While many sRNA loci in the recombinants exhibit additive sRNA expression, I found multiple transgressively expressed sRNA loci. Using the available bioinformatics tools, I identified potential miRNAs and phased secondary sRNAs within the list of transgressively expressed loci. Target analysis of one of the transgressively expressed miRNAs linked it with the transgressive expression of certain phased loci, suggesting a potential for sRNAs to be able to set up heritable epigenetic marks in recombinant C. reinhardtii cells.

Chlamydomonas reinhardtii can utilize CO2 for autotrophic growth (HSM plus 5% CO2) or acetate for mixotrophic growth (TAP). This study was to elucidate the differential regulation of methionine sulfoxide reductase (MSR) gene expression between HSM plus 5% CO2 and TAP cultured cells, and also to determine the difference of gene expression in response to high light (1,000 £gE m-2 s-1). The role of photosynthetic electron transport (PET) in the regulation of MSR gene expression was also examined by the use of PET inhibitors. High light inhibited PSII activity (Fv/Fm and Fv'/Fm') of HSM plus 5% CO2 and TAP cultured cells., while the responses of CrMSR gene expression in mixotrophically grown cells were different from autotrophically grown cells, High light increased the expression of CrMSRA1, CrMSRA2, CrMSRA3, CrMSRA5, CrMSRB1.2, and CrMSRB2.1, but inhibited the expression of CrMSRA4 and CrMSRB2.2 in autotrophically grown cells. The expression of CrMSRA3, CrMSRA5, and CrMSRB2.1 in mixotrophically grown cells was increased by high light but that of CrMSRA1, CrMSRA4, and CrMSRB2.2 was inhbited. The number of MSR isoform that was up-regulated by high light was greater in autotrophically grown cell than that in mixotrophically grown cells. Using the PET inhibitors (3-(3,4-dichlorophenyl)-1,1- dimethylurea (DCMU) and 2,5-dibromo-3-methyl-6-isopropyl-p-benzoquinone (DBMIB)), most of the CrMSRA expression was regulated by reduced QA for autotrophically grown cells while reduced PQ was the main site for mixotrophically grown cells by high light. The expression of CrMSRB in autotrophically grown cells was mainy modulated by QA (-) or Cytb6f (-), while that was not affected by PET, except a role of Cytb6f (-) on the high light-induced CrMSRB2.2 expression. We fouind that CrMSRB gene expression in autotrophically grown cells was highly affected by PET but not for micotrophically grtown cells. The present result that H2O2 did not accumulate in autotrophically and mixotrophically grown cells suggests that H2O2 may be not involved in the regulation of high light regulation of CrMSR gene expression. The present study shows that the mRNA expression of CrMSR isoforms in Chlamydomonas was diffrerentially regulated between autotrophically and mixttrophically grown cells. The relationship between the utilization of different C source and CrMSR gene expression will be discussed.

L’explosion de la nanotechnologie a permis l’intégration d’une multitude de nanoparticules dans des produits de consommation. Les nanoparticules d’argent (nAg) sont les plus utilisées à ces fins, selon les derniers recensements disponibles. La plupart des études toxicologiques, à ce jour, ont fait état de l’implication très évidente de l’ion Ag+ dans la toxicité aigüe des nAg; cependant, quelques études ont mis en évidence des effets toxicologiques dus aux nAg. Il y a un certain consensus à propos d’un risque de contamination des eaux douces via leur rejet par les effluents des réseaux d’aqueducs. Puisque les concentrations en Ag+ sont généralement très faibles dans les eaux douces (de l’ordre du pg L-1), de par la formation de complexes non-labiles avec des thiols (organiques et inorganiques) et des sulfures, la toxicité inhérente aux nAg pourrait ne pas être négligeable- comparativement aux tests en laboratoires. Cette étude s’intéressait donc aux mécanismes de bioaccumulation d’argent par l’algue verte C. reinhardtii suite à l’exposition à des nAg de 5 nm (enrobage d’acide polyacrylique). La bioaccumulation d’argent pour l’exposition à Ag+ servait de point de comparaison; également, les abondances de l’ARNm de l’isocitrate lyase 1 (ICL1) et de l’ARNm de Copper Transporter 2 (CTR2) étaient mesurées comme témoins biologiques de la bioaccumulation de Ag+. Les expériences ont été menées en présence d’un tampon organique (NaHEPES, 2 x 10-2 M; Ca2+, 5x 10-5 M) à pH de 7,00. Pour des expositions à temps fixe de 2 heures, la bioaccumulation d’argent pour nAg était supérieure à ce qui était prédit par sa concentration initiale en Ag+; cependant, il n’y avait pas de différence d’abondance des ARNm de ICL1 et de CTR2 entre nAg et Ag+. D’un autre côté, pour une exposition à temps variables, la bioaccumulation d’argent pour nAg était supérieure à ce qui était prédit par sa concentration initiale en Ag+ et une augmentation de l’abondance de l’ARNm de ICL1 était notée pour nAg. Cependant, il n’y avait aucune différence significative au niveau de l’abondance de l’ARNm de CTR2 entre nAg et une solution équivalente en Ag+. L’ajout d’un fort ligand organique (L-Cystéine; log K= 11,5) à une solution de nAg en diminuait radicalement la bioaccumulation d’argent par rapport à nAg-sans ajout de ligand. Par contre, l’abondance des ARNm de ICL1 et de CTR2 étaient stimulées significativement par rapport à une solution contrôle non-exposée à nAg, ni à Ag+. Les résultats suggéraient fortement que les nAg généraient des ions Ag+ au contact de C. reinhardtii. / The recent developments in nanotechnology have given rise to a new and increasing economical market where nanoparticles are at the forefront. Recent inventories of the nanoparticles-containing products have shown that silver nanoparticle- containing products are the most frequently used consumer nanomaterial. Due to the fear of a large scale contamination-and even pollution- of the aquatic environment from silver nanoparticles (nAg), studies have been conducted to assess their toxicities, which, in many cases, have been found to be mediated by the concomitant presence of Ag+. Notably, few studies have found evidence of toxicity due to the nAg, per se. Since numerous non-labile complexes are formed with Ag+ in freshwaters- especially with thiols and sulfides-, nAg toxicity might be more relevant in comparison to laboratory tests where the Ag+ tends to dominate toxicity studies. Therefore, this study investigated the mechanisms underlying silver bioaccumulation by the green alga, C. reinhardtii upon exposure to solutions of nAg (nominal size of 5 nm; poly-acrylate coating). Silver bioaccumulation upon exposures to the free ion alone served for comparison. In parallel, the abundance of two mRNAs- ICL1 and CTR2- were used to better understand the mechanisms underlying the bioaccumulation of Ag+ (and potentially nAg). The experiments were conducted in pH buffered solutions (NaHEPES, 2 x 10-2 M; Ca2+, 5x 10-5 M) at pH 7.00. For 2-hour exposures, the silver bioaccumulation for solutions of nAg exceeded what was expected from their Ag+ content only; however, no differences were noticed in the abundance of the expression of ICL1 and CTR2. For variable time exposures, the silver bioaccumulation for solutions of nAg exceeded what was expected from their Ag+ content only. Moreover, the expression of ICL1 was significantly higher for nAg than what was expected based upon an exposure to Ag+ only. When exposed to nAg, expression levels of CTR2 could be predicted from levels based solely on the Ag+ concentrations. The addition of a large excess of L-Cysteine, which is a very strong silver ligand (log K =11.5), to a nAg solution largely decreased silver bioaccumulation, however, bioaccumulation remained significant and the expression of both ICL1 and CTR2 were significantly higher than that of the control solutions (without Ag+). The results strongly suggest that nAg generated Ag+ ions when in contact with C. reinhardtii and that the nAg released to freshwaters might exert its toxicity through organism-contact-dependant release of Ag+.

Intraflagellar transport (IFT), the bi-directional movement of particles along the length of flagella, is required for flagellar assembly. The IFT particles are moved by kinesin II from the base to the tip of the flagellum, where flagellar assembly occurs. The IFT particles are then moved in the retrograde direction by cytoplasmic dynein 1b/2 to the base of the flagellum. The IFT particles of Chlamydomonas are composed of ~16 proteins, organized into complexes A and B. Alhough IFT is believed to transport cargoes into flagella, few cargoes have been identified and little is known about how the cargos are transported. To study the mechanism of IFT and how IFT is involved in flagellar assembly, this thesis focuses on two questions. 1) In addition to a heavy chain, DHC1b, and a light chain, LC8, what other proteins are responsible for the retrograde movement of IFT particles? 2) What is the specific function of an individual IFT-particle protein? To address these two questions, I screened for Chlamydomonas mutants either defective in retrograde IFT by immunofluorescence microscopy, or defective in IFT-particle proteins and D1bLIC, a dynein light intermediate chain possibly involved in retrograde IFT, by Southern blotting. I identified several mutants defective in retrograde IFT and one of them is defective in the D1bLIC gene. I also identified several mutants defective in several IFT-particle protein genes. I then focused on the mutant defective in D1bLIC and the one defective in IFT46, which was briefly reported as an IFT complex B protein. My results show that as a subunit of the retrograde IFT motor, D1bLIC is required for the stability of DHC1b and is involved in the attachment of IFT particles to the retrograde motor. The P-loop in D1bLIC is not necessary for the function of D1bLIC in retrograde IFT. My results also show that as a complex B protein, IFT46 is necessary for complex B stability and is required for the transport of outer dynein arms into flagella. IFT46 is phosphorylated in vivo and the phosphorylation is not critical for IFT46’s function in flagellar assembly.

The first type of dynein identified, axonemel dynein (Gibbons and Rowe, 1965), slides adjacent microtubules within the axoneme, generating the force necessary for ciliary and flagellar beating. The outer dynein arm is an important component of the flagellar axoneme, providing up to 60% of the force for flagellar motility. In the absence of the outer arm, cells swim with a slow-jerky motion at about 1/3rd the speed of wild-type cells, and the flagellar beat frequency is markedly reduced. Sixteen genes (ODA1-ODA16) have been identified that are required for outer arm assembly in Chlamydomonas reinhardtii. In addition, PF13, PF22, and FLA14 are required for outer dynein arm assembly, but their phenotypes are pleiotropic, suggesting that they affect additional flagellar components. Of the uncloned genes, ODA5, ODA8, and ODA10 are of particular interest because they do not encode subunits of the outer arm or the outer dynein arm-docking complex (ODA-DC). Mutant alleles of these genes are unable to complement in temporary dikaryons, suggesting that the gene products interact with each other (Kamiya, 1988). Since the genes encoding all of the known components of the outer dynein arm and the ODA-DC have been characterized, it is of great interest to identify the gene products of these additional, uncloned ODA alleles. The first chapter provides an introduction to the Chlamydomonasflagellum, the dyneins in general, the outer dynein arm in particular, and mutations that impinge on the assembly and regulation of this important axonemal structure. The second chapter addresses the identification and isolation of genomic DNA containing the ODA5 gene. Utilizing a NIT1-tagged oda5-insertional mutant, I identified sequences flanking the site of the inserted NIT1 gene. These sequences were used to isolate wild-type genomic clones spanning the ODA5 gene. When transformed into the oda5 mutant, the wild-type clones rescued the mutant phenotype. These results demonstrated the successful isolation of the ODA5 gene. The third chapter describes the identification of the ODA5 gene and its corresponding cDNA. The rescuing genomic fragments were sequenced. Gene modeling was used to predict intron-exon splice sites. Primers to predicted exons were designed and used to obtain the ODA5 cDNA. The gene structure of Oda5 was analyzed and its predicted amino acid sequence deduced. Secondary structure predictions indicate that Oda5p is likely to contain a series of coiled-coil domains, followed by a poly-glycine sequence and a short, highly charged region. Northern analysis demonstrated that ODA5 gene expression is upregulated by deflagellation, a hallmark of many flagellar mRNAs. Data in CHAPTER IV further characterize the Oda5 protein and its association with the axoneme. Oda5p localizes to the flagellum, consistent with the enhancement in mRNA levels in response to deflagellation. Within the flagellum, Oda5p is an axonemal component that is released from the axoneme upon high salt extraction, as are the ODA-DC and the outer dynein arm. However, Oda5p does not associate with this super-complex in the high salt extract as determined by sucrose gradient sedimentation. Oda5p assembles onto the axoneme independently of the outer dynein arm and the ODA-DC,demonstrating it does not require these complexes for localization. Furthermore, Oda5p assembles onto the axoneme in the oda8, but not the oda10 mutant, demonstrating a role for the Oda10 protein in localization of Oda5p. These data provide the first biochemical evidence for an interaction between Oda5p and Oda10p. CHAPTER V reveals the discovery of a previously unrecognized phenotype exhibited in both oda5 and oda10 mutant strains: a defect in the assembly of a previously unknown flagellar adenylate kinase (AK). The protein levels of this flagellar AK are reduced in oda5 mutant axonemes, as determined by quantitative mass spectrometry. Direct enzymatic assays confirmed a reduction in AK activity in both oda5 and oda10 mutant axonemes, providing a second line of biochemical evidence supporting a complex containing Oda5p and OdalOp. The sequence of the flagellar AK gene and its cDNA were determined. CHAPTER VI details our efforts to identify the ODA10 gene. Genomic clones were isolated, which contain sequences at, or near, the ODA10 locus. Analysis of the genomic clones yielded no insights into the identity of the ODA10 gene. The inability of these clones to rescue the Oda10-motility phenotype indicates that these clones most likely do not contain an intact ODA10 gene. And lastly, CHAPTER VII discusses future experimentation that can be done based on the data provided by the current study.

No description available.

京都大学 / 0048 / 新制・課程博士 / 博士(生命科学) / 甲第22021号 / 生博第418号 / 新制||生||55(附属図書館) / 京都大学大学院生命科学研究科統合生命科学専攻 / (主査)教授 福澤 秀哉, 教授 河内 孝之, 教授 荒木 崇 / 学位規則第4条第1項該当 / Doctor of Philosophy in Life Sciences / Kyoto University / DFAM

No description available.

Die in dieser Arbeit durchgeführten Untersuchungen dienten dazu, die Eigenschaften und Grundlagen zur Regulation der chloroplastidären NAD(P)(H)-GAPDH im Wechsel zwischen Licht- und Dunkelmetabolismus aufzuklären. Dazu wurden Untersuchungen mit dem System ‘isoliertes Enzym’ und dem System ‘isolierte Chloroplasten’ durchgeführt. Durch die Herstellung proteolysierter NAD(P)(H)-GAPDH und rekombinanter Untereinheiten GapAM, GapBM und GapBMDC, sowie gleichzeitig exprimierter GapAMBM und GapAMBMDC war die Möglichkeit geschaffen, die Funktion der CTE bei der Regulation zu untersuchen. Eigenschaften von NAD(H)-abhängiger plastidärer GapCp konnten mit angereinigtem und rekombinant hergestelltem Enzym aus roter Paprikafrucht ermittelt werden. Regulation von NAD(P)(H)-GAPDH im isolierten intakten Chloroplasten aus Spinat Durch Reduktion von NAD(P)(H)-GAPDH in belichteten isolierten intakten Spinatplastiden, vermutlich durch Thioredoxinf, ist das Enzym sensitiver gegenüber 1,3bisPGA, da der Ka-Wert von 17-21 µM auf ca. 1-2 µM gesenkt wird. Die gleichzeitig steigende Konzentration von 1,3bisPGA auf ca. 0,8 µM im Chloroplasten führt zur Aktivierung und damit verbundener Dissoziation des Enzyms. Die Aktivierung betrifft ausschließlich die NADPH-abhängigen Aktivitäten. NADPH, NADP und ATP scheiden als Aktivatoren in vivo aus, da sie bei im Chloroplasten im Licht und im Dunkeln herrschenden Konzentrationen von 140 µM NAD das Enzym nicht aktivieren und unphysiologisch hohe Konzentrationen der Effektoren zur Aktivierung des Enzyms benötigt würden. Die Inaktivierung im Dunkeln erfolgt durch Absenkung der 1,3bisPGA-Konzentration, und das Enzym wird durch ein bislang nicht bekanntes Oxidationsmittel oxidiert. NAD, sowie möglicherweise auch GAP und NADH sind an der Inaktivierung und gleichzeitigen Aggregation beteiligt. Die CTE der Untereinheit B ist für die Aggregation/Dissoziation von NAD(P)(H)-GAPDH verantwortlich Im Vergleich von NAD(P)(H)-GAPDH-Isoenzymen besitzt ausschließlich GapB aus Chloroplasten höherer Pflanzen eine CTE von 28-32 Aminosäuren Länge. Sie ist gekennzeichnet durch zwei konservierte Cysteine, zwischen denen sich acht Aminosäuren befinden. In der Mitte dieser acht Aminosäuren befindet sich ein Prolin, welches u.a. für den Richtungswechsel bei der Faltung eines Proteins verantwortlich ist, so dass sich zwischen den beiden Cysteinen eine Disulfidbrücke ausbilden könnte. Die CTE aus Spinat besitzt außerdem einen hohen Anteil von sieben negativ geladenen Aminosäuren. In Rahmen dieser Arbeit wurde ein Modell enwickelt, welches beinhaltet, dass die Aggregation von vier (A2B2)-Tetrameren über Salzbrückenbindung negativ geladener Aminosäuren der CTE und nach außen exponierten positiv geladenen Aminosäuren von GapA vermittelt wird. Ergebnisse mit NAD(P)(H)-GAPDH, der die CTE fehlt, d.h. proteolysierte NAD(P)(H)-GAPDH und rekombinant hergestellte GapAM, GapBMDC und GapAMBMDC bestätigen das Modell. Die drei tetrameren Formen, sowie die gleichzeitig exprimierte GapAMBMDC sind nicht fähig, zu aggregieren. Ausschließlich GapB und die gleichzeitig exprimierte GapAMBMC aggregieren in eine hochmolekulare Form von ca. 470 kDa, bzw. eine Mischung von 470 und 300 kDa. Die CTE der Untereinheit B ist für die Redoxmodulation von NAD(P)(H)-GAPDH verantwortlich. NAD(P)(H)-GAPDH höherer Pflanzen besitzt fünf konservierte Cysteine: 18, 149, 153, 274 und 285, wovon sich Cystein 149 und Cystein 153 im aktiven Zentrum befinden. Cystein 153 in nicht an der Katalyse beteiligt. In der CTE von GapB sind zusätzlich zwei Cysteine 355 und 364 konserviert. Im Rahmen dieser Arbeit konnte gezeigt werden, dass die lange Zeit prognostizierte intramolekulare Disulfidbrücke zwischen Cystein 18 und 285 nicht vorhanden ist. Dies ergibt sich aus der Tatsache, dass in Algen, deren NAD(P)(H)-GAPDH als redoxmoduliert beschrieben ist, Cystein 285 nicht vorkommt. Weiterhin zeigen eigene Ergebnisse, dass NAD(P)(H)-GAPDH, der die CTE fehlt, d.h. proteolysierte NAD(P)(H)-GAPDH, rekombinant hergestellte GapAM und GapBMDC, weder durch DTTred noch in Kombination mit 1,3bisPGA aktiviert werden. Die tetrameren Formen sind nicht redoxmoduliert. Daraus wird gefolgert, dass die für die Redoxmodulation verantwortliche Disulfidbrücke sich in der CTE von GapB befindet. Die CTE der Untereinheit B ist für die Nucleotidspezifität von NAD(P)(H)-GAPDH verantwortlich Die Bindung von NADPH, bzw. NADH in den verschiedenen Isoenzymen von NAD(P)(H)-GAPDH hängt von der Aminosäurezusammensetzung in den Positionen 32, 33, 187 und 188 ab. Die Aminosäuren 187 und 188 befinden sich auf einem S-loop, der in das aktive Zentrum eines benachbarten Monomers hineinreicht und mit ihm eine funktionelle Einheit bildet. NAD(H) wird in den Positionen 32 und 33 gebunden; eine Bindung von NADP(H) ist durch sterische Hinderung und Ladung des Prolins 188, welches in cytosolischer NAD(H)-GAPDH vorkommt, nicht möglich. Da chloroplastidäre NAD(P)(H)-GAPDH in der Position 188 ein Serin besitzt, kann die Phosphatgruppe von NADP(H) binden. Aufgrund der Affinitäten der inaktiven 600 kDa- und aktiven 150 kDa-NAD(P)(H)-GAPDH für NADPH, bzw. der in Chloroplasten im Licht wie im Dunkeln herrschenden NADPH-Konzentrationen, wäre es theoretisch möglich, dass das Coenzym sowohl bei Belichtung als auch im Dunkeln umgesetzt wird. Während des Licht-Dunkel-Übergangs wechselt das Enzym jedoch zwischen dem Coenzym NADPH und NAD. In dieser Arbeit konnte anhand eines Modells aufgezeigt werden, dass im Dunkel-adaptierten Chloroplasten die Bindung von NADPH an der Aminosäure 188 unterbunden ist, da der S-loop um einige A aus dem aktiven Zentrum gezogen wird. Ursache dafür ist mit großer Wahrscheinlichkeit die CTE, die in der 600 kDa-Form an positiv geladenen Aminosäuren des S-loops bindet. Die Aktivierung von NAD(P)(H)-GAPDH in struktureller Hinsicht. Die 600 kDa-Form von NAD(P)(H)-GAPDH ist mit dem Coenzym NADPH inaktiv, da sich innerhalb der CTE eine Disulfidbrücke gebildet hat. Die strukturelle Änderung der CTE erlaubt es, dass negativ geladenene Aminosäuren der CTE an nach außen exponierten positiv geladenen Aminosäuren eines S-loops von GapA binden können. Dadurch ist eine Bindung von NADPH im aktiven Zentrum an den S-loop nicht möglich. NAD kann ungehindert binden. Bei einsetzender Belichtung wird die Disulfidbrücke der CTE aufgebrochen, ohne dass das Enzym dissoziert. Mit steigenden Konzentrationen von dreifach negativ geladenem 1,3bisPGA wird die Salzbrückenbindung zwischen der CTE und dem S-loop gelöst, so dass NAD(P)(H)-GAPDH in vier Tetramere dissoziiert und gleichzeitig NADPH umsetzen kann.