Team:Bielefeld-Germany/Theory

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Bisphenol A

Bisphenol A and its effects on mammals

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Bisphenol A degradation

There exist a lot of bacteria in nature that can degrade xenobiotic substances such as phenolic compounds or endocrine disruptors. In a lot of soil samples that were taken from contaminated soil to find organisms that do so, sphingomonads were extraordinarily often isolated (Stolz, 2009). In 2005, Sasaki et al. isolated a soil bacterium from the Sphingomonas genus which is able to degrade the endocrine disruptor bisphenol A (BPA) with a unique rate and efficiency compared to other BPA degrading organisms. This strain, called Sphingomonas bisphenolicum AO1, is able to completely decompose 120 mg BPA L^-1 in about 6 hours while other strains need days of cultivation (e.g. Sphingomonas strain BP-7 isolated by Sakai et al. (2007)). The full bisphenol degradation pathway which is found in nature is shown in the following figure (taken from KEGG database). All metabolites of the BPA degradation pathway can be found in BPA degrading S. bisphenolicum AO1 and these bacteria can grow on BPA as the only carbon source (Sasaki et al., 2005a).

Bisphenol A is mainly hydroxylated into the products 1,2-Bis(4-hydroxyphenyl)-2-propanol and 2,2-Bis(4-hydroxyphenyl)-1-propanol by some kind of oxidoreductase acting with NADH or NADPH. A total of three genes are responsible for this BPA hydroxylation: a cytochrome P450 (CYP, bisdB), a ferredoxin (Fd, bisdA) and a ferredoxin-NAD⁺ oxidoreductase (FNR) (Sasaki et al., 2005b). The three gene products act together to reduce BPA while oxidizing NADH + H⁺. The cytochrome P450 or BisdB reduces the BPA and is oxidized during this reaction. BisdB in its oxidized status is reduced by the ferredoxin BisdA so it can reduce BPA again. The oxidized BisdA is reduced by a ferredoxin-NAD⁺ oxidoreductase consuming NADH + H⁺ so the BPA degradation can continue (Sasaki et al., 2005b). This leeds to some kind of electron transport chain which is shown in the following figure:

ANIMATION FÜR BISPHENOL ABBAU

Further applications of bisphenol A degrading BioBricks and enzymes

S-layer

NAD⁺ detection

NAD⁺ in general

Nicotinamide adenine dinucleotide, abbreviated NAD⁺, is an ubiquitous and indispensable cofactor for all living organisms (Bi et al., 2011). The molecule has a wide range of physiological functions in cellular processes (fig. 2) and has a great impact on the cell integrity (Grahnert et al., 2011). It is integrated into the energy metabolism and determines the redox status of the cell due to its purpose as a reduction equivalent. This is strongly linked to the control of signaling and transcriptional events. For instance, NAD⁺ has been recently described as a modulator of immune functions (Grahnert et al., 2011) and a master regulator of transcription (Ghosh et al., 2010). Several enzymes are tightly regulated by the cellular balance between the oxidized and reduced form of NAD⁺ and therefore regarded as a potential target for therapeutics (Sauve, 2008). Indeed, NAD⁺ acts as a substrate for a wide range of proteins including NAD⁺-dependent protein deacetylases, poly(ADP-ribose) polymerases and several transcription factors (Houtcooper et al., 2010). A disorder of the cellular NAD⁺ level has usually relevance in symptoms and diseases like stroke, cardiac ischemia, epilepsy, huntington disease, wallerian degeneration, cancer, type two diabetes mellitus (T2DM), neutrophil survival, longevity, obesity as well as cardiovascular and neurodegenerative disease (Sauve, 2008; Houtcooper et al., 2010). The regulation of NAD⁺-dependent pathways may have a major contribution to oxidative metabolism and life span extension (Houtcooper et al., 2010). The biosynthetic pathways for NAD⁺ are proposed as promising novel antibiotics targets against pathogens (Bi et al., 2011).

Figure 2: NAD(P) physiological function (taken from Bi et al., 2011).

Biosynthesis of NAD⁺

NAD⁺ is embedded in the cellular metabolism and has a great impact on essential cellular processes. The biosynthesis in most bacteria and plants starts with the anaerobic conversion of the amino acid aspartate to quinoline. Alternatively, in yeast, humans and some bacterial microbes the quinoline derives from tryptophan in an aerobic pathway (fig 3). This is a crucial step that leads under consumption of nicotinic acid to the nicotinate ring system via formation of nicotinic acid monoculeotide (NAMN), respectively (Sauve, 2008). After conjugation of adenosine mononucleotide (AMP) the NAD synthetase forms nicotinamide adenine dinucleotide (NAD). Recently, it has been reported that in humans also exists an nicotinic acid-independent catalysed enzymatic reaction (nampt/PBEF) for NAD biosynthesis by directly using nicotinamide (Rongvaux, 2002). Nicotinamide or nicotinic acid can be taken from diet or medicine. If the NAD occurs in its oxidized (NAD⁺) or reduced form (NADH) depends basically on fundamental processes as the cellular energy meabolism.

Figure 3: Principle of de novo NAD⁺ biosynthesis of organisms that use tryptophan as a source. Bottom: paths of metabolism for human nicotinamide, nicotinic acid and nicotinamide riboside that lead to formation of NAD⁺ (taken from Sauve, 2008).

Applications for Molecular Beacons

Bacterial NAD⁺ dependent DNA ligase

Further applications for the NAD⁺ bioassay

The reviewed molecular beacon based NAD⁺ bioassay can be applied to biochemical and biomedical studies (Tang et al., 2011). Accordingly, it can be utilized to detect NAD⁺/NADH-dependent enzymatic processes. The low limit of detection, its reliability and manageability provides a practical alternative to present colorimetric, fluorometric, chemiluminescent, electrochemical or mass spectrometric methods detecting NAD⁺ or NADH. In context of clinical applications and therapeutics the NAD⁺ bioassay can be useful to monitor cellular NAD⁺ levels during treatments of tissues or cell cultures for identification of drug targets, for instance. It may also be applied in the field of diagnostics. Finally, the principle of the proposed NAD⁺ bioassay can be used for cell-free optical biosensors by taking molecular beacons either immobilized on the sensor surface or being present in the reaction medium (Tang et al., 2011).

References

Bi J, Wang H, Xiel J (2011) Comparative genomics of NAD(P) biosynthesis and novel antibiotic drug targets, Journal of Cellular Physiology 226(2):331-340.

Ghosh S, George S, Roy U, Ramachandran D, Kolthur-Seetharam U (2010) NAD: A master regulator of transcription, Biochimica et Biophysica Acta 1799(10-12):681-693.

Grahnert A, Grahnert A, Klein C, Schilling E, Wehrhahn J, Hauschildt S (2011) NAD⁺: A modulator of immune functions, Innate Immunity 17(2):212-233.

Houtkooper RH, Cantó C, Wanders RJ, Auwerx J (2010) The Secret Life of NAD⁺: An Old Metabolite Controlling New Metabolic Signaling Pathways, Endocrine Reviews 31(2):194-223.

Rongvaux

Sakai K, Yamanaka H, Moriyoshi K, Ohmoto T, Ohe T (2007) Biodegradation of Bisphenol A and Related Compounds by Sphingomonas sp. Strain BP-7 Isolated from Seawater, Bioscience, Biotechnology, and Biochemistry 71(1):51-57.

Sauve AA (2008) NAD⁺ and Vitamin B3: From Metabolism to Therapies, The Journal of Pharmacology and Experimental Therapeutics 324(3):883-893.

Sasaki M, Maki J, Oshiman K, Matsumura Y, Tsuchido T (2005a) Biodegradation of bisphenol A by cells and cell lysate from Sphingomonas sp. strain AO1, Biodegradation 16(5):449-459.

Sasaki M, Akahira A, Oshiman K, Tsuchido T, Matsumura Y (2005b) Purification of Cytochrome P450 and Ferredoxin, Involved in Bisphenol A Degradation, from Sphingomonas sp. Strain AO1, Appl Environ Microbiol 71(12):8024-8030.

Stolz A (2009) Molecular characteristics of xenobiotic-degrading sphingomonads, Appl Microbiol Biotechnol 81:793-811.