INDUCTION OF DNA STRAND BREAKS AND CROSS-LINKS BY THE NEW ANTICANCER AGENT 3,6-DIAZIRIDINYL-2,5-BIS(CARBOETHOXYAMINO) -1,4-BENZOQUINONE

The DNA breakage effect of the anticancer agent 3,6-diaziridinyl-2,5-bis(carboethoxyamino)-1,4-benzoquinone (AZQ, NSC-182986) on bacteriophage PM2 DNA was investigated using agarose gel electrophoresis. AZQ caused both single-stranded and double-stranded breaks after reduction with NaBH(,4), but it was not active in the native state. At 120 (mu)M, it degraded 50% of the closed circular form I DNA into 40% form II DNA (single-stranded break) and 10% form III DNA (double-stranded break). It produced a dose-response breakage between 1 (mu)M and 320 (mu)M. The DNA breakage exhibited a marked pH dependency. At 320 (mu)M, AZQ degraded 80% and 60% of form I DNA at pH 4 and 10 respectively, but none between pH 6 to 8. The DNA breakage at physiologic pH was greatly enhanced when 10 (mu)M cupric sulfate was included in the incubation mixture. The DNA strand scission was inhibited by catalase, glutathione, KI, histidine, Tiron, and DABCO. These results suggest that the DNA breakage may be caused by active oxygen metabolites including hydroxyl free radical. The bifunctional cross-linking activity of reduced AZQ on isolated calf thymus DNA was investigated by ethidium fluorescence assay. The cross-linking activity exhibited a similar pH dependency; highest in acidic and alkaline pH, inactive under neutral conditions. Using the alkaline elution method, we found that AZQ induced DNA single-stranded breaks in Chinese hamster ovary cells treated with 50 (mu)M of AZQ for 2 hr. The single-stranded break frequencies in rad equivalents were 17 with 50 (mu)M and 140 with 100 (mu)M of AZQ. In comparison, DNA cross-links appeared in cells treated with only 1 to 25 (mu)M of AZQ for 2 hr. The cross-linking frequencies in rad equivalents were 39 and 90 for 1 and 5 (mu)M of AZQ, respectively. Both DNA-DNA and DNa-protein cross-links were induced by AZQ in CHO cells as revealed by the proteinas K digestion assay. DNA cross-links increased within the first 4 hr of incubation in drug-free medium and slightly decreased by 12 hr, and most of the cross-links disappeared after cells were allowed to recovered for 24 hr.^ By electrochemical analysis, we found that AZQ was more readily reduced at acidic pH. However, incubation of AZQ with NaBH(,4) at pH 7.8 or 10, but not at 4, produced superoxide anion. The opening of the aziridinyl rings of AZQ at pH 4 was faster in the presence of NaBH(,4) than in its absence; no ring-opening was detected at pH 7.8 regardless of the inclusion of NaBH(,4). . . . (Author's abstract exceeds stipulated maximum length. Discontinued here with permission of author.) UMI ^

Zur Erklärung der Mischna Erubin 2, 5

S. Friedmann

Clara Ziegler, Hüftbild, 2,5 Jahre alt - Clara Ziegler, Geburtshaus

Signatur des Originals: S 36/F07406

The role of beta-arrestin 2 in lysophosphatidic acid-induced NF-kappaB activation

Lysophosphatidic acid (LPA) is a bioactive phospholipid and binds to its receptors, a family of G protein-coupled receptors (GPCR), which initiates multiple signaling cascades and leads to activation of several transcription factors, including NF-κB. NF-κB critically regulates numerous gene expressions, and is persistently active in many diseases. In our previous studies, we have demonstrated that LPA-induced NF-κB activation is dependent on a novel scaffold protein, CARMA3. However, how CARMA3 is recruited to receptor remains unknown. β-Arrestins are a family of proteins involved in desensitization of GPCR signaling. Additionally, β-arrestins function as signaling adaptor proteins, and mediate multiple signaling pathways. Therefore, we have hypothesized that β-arrestins may link CARMA3 to LPA receptors, and facilitate LPA-induced NF-κB activation. ^ Using β-arrestin-deficient MEFs, we found that β-arrestin 2, but not β-arrestin 1, was required for LPA-induced NF-κB activation. Also, we showed that the expression of NF-κB-dependent cytokines, such as interlukin-6, was impaired in β-arrestin 2-deficient MEFs. Mechanistically, we demonstrated the inducible association of endogenous β-arrestin 2 and CARMA3, and we found the CARD domain of CARMA3 interacted with 60-320 residues of β-arrestin 2. To understand why β-arrestin 2, but not β-arrestin 1, mediated NF-κB activation, we generated β-arrestin mutants. However, some mutants degraded quickly, and the rest did not rescue NF-κB activation in β-arrestin-deficient MEFs, though they had similar binding affinities with CARMA3. Therefore, it indicates that slight changes in residues may determine the different functions of β-arrestins. Moreover, we found β-arrestin 2 deficiency impaired LPA-induced IKK kinase activity, while it did not affect LPA-induced IKKα/β phosphorylation. ^ In summary, our results provide the genetic evidence that β-arrestin 2 serves as a positive regulator in NF-κB signaling pathway by connecting CARMA3 to LPA receptors. Additionally, we demonstrate that β-arrestin 2 is required for IKKα/β activation, but not for the inducible phosphorylation of IKKα/β. Because the signaling pathways around the membrane-proximal region of LPA receptors and GPCRs are quite conserved, our results also suggest a possible link between other GPCRs and CARMA3-mediated NF-κB activation. To fully define the role of β-arrestins in LPA-induced NF-κB signaling pathways will help to identify new drug targets for clinical therapeutics.^

Characterization of the East Houston particulate matter <2.5 atmosphere; a novel method for desorbing organic constituents from airborne particulates

I have developed a novel approach to test for toxic organic substances adsorbed onto ultra fine particulate particles present in the ambient air in Northeast Houston, Texas. These particles are predominantly carbon soot with an aerodynamic diameter (AD) of <2.5 μm. If present in the ambient air, many of the organic substances will be absorbed to the surface of the particles (which act just like a charcoal air filter), and may be adducted into the respiratory system. Once imbedded into the lungs these particles may release the adsorbed toxic organic substances with serious health consequences. I used a Airmetrics portable Minivol air sampler time drawing the ambient air through collection filters samples from 6 separate sites in Northeast Houston, an area known for high ambient PM 2.5 released from chemical plants and other sources (e.g. vehicle emissions).(1) In practice, the mass of the collected particles were much less than the mass of the filters. My technique was designed to release the adsorbed organic substances on the fine carbon particles by heating the filter samples that included the PM 2.5 particles prior to identification by gas chromatography/mass spectrometry (GCMS). The results showed negligible amounts of target chemicals from the collection filters. However, the filters alone released organic substances and GCMS could not distinguish between the organic substances released from the soot particles from those released from the heated filter fabric. However, an efficacy tests of my method using two wax burning candles that released soot revealed high levels of benzene. This suggests that my method has the potential to reveal the organic substances adsorbed onto the PM 2.5 for analysis. In order to achieve this goal, I must refine the particle collection process which would be independent of the filters; the filters upon heating also release organic substances obscuring the contribution from the soot particles. To obtain pure soot particles I will have to filter more air so that the soot particles can be shaken off the filters and then analyzed by my new technique. ^