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L H Thompson

Publications and source records attributed to L H Thompson.

168 records · Page 10Linked to original sources

DNA-ligase activities appear normal in the CHO mutant EM9.

The Chinese hamster ovary (CHO) mutant strain EM9 was previously shown to be hypersensitive to killing by ethyl methanesulfonate (EMS) and methyl methanesulfonate (MMS), to have a 12-fold increased baseline incidence of sister-chromatid exchanges (SCE), and to be defective in rejoining DNA strand breaks after treatment with EMS, MMS, or X-rays. A study was performed to determine if the primary biochemical defect might be a DNA ligase. DNA-ligase activities were assayed and compared after separation of the multiple forms of ligase by AcA 34 gel-filtration chromatography of total cellular extracts. In EM9 cells the levels of the presumptive replicative forms, DNA ligase Ia (480 kd) and ligase Ib (240 kd) were about 50% and 60%, respectively, of those in the parental AA8 cells, whereas DNA ligase II (80 kd) was unaltered in EM9 . In a phenotypic revertant line ( 9R1 ) ligases Ia, Ib and II levels were 35%, 37% and 100%, respectively, of those in AA8 . The reduced levels of ligases Ia and Ib in EM9 and 9R1 cells are apparently not related directly to the mutant phenotype and may be attributable to the somewhat slower growth rates of these strains compared with those of AA8 . To determine if the repair defect in EM9 might reside in the ability to induce DNA-ligase activity after treatment with a DNA-damaging agent, AA8 and EM9 cells were treated with MMS at 30 micrograms/ml for 60 min before preparing fractions for ligase assays. Under these conditions the activities of ligases Ia and Ib decreases 70-80% in both cell lines, but ligase II increased 2.0- and 2.6-fold, respectively, in AA8 and EM9 . As a further test of defective ligase activities in EM9 , assays were performed in the presence of 0.1 M NaCl or after heating the fractions for 10 min at 50 degrees C. Although all 3 forms of ligase showed altered activity under both of these conditions, there were no significant differences between EM9 and AA8 cells. These data combined with the above results provide strong evidence that the site of the primary defect in EM9 is not in either of the DNA ligases .

Animals↗

DNA-strand breaks associated with halogenated pyrimidine incorporation.

The alkaline elution of bromodeoxyuridine-containing (BrdUrd) DNA and chlorodeoxyuridine-containing ( CldUrd ) DNA was studied in two CHO lines, the parental AA8 and a mutant line, EM9 , which has a defect in repairing strand breaks and a 12-fold elevated baseline frequency of SCE. BrdUrd-DNA was found to have alkali-labile sites as well as direct breaks, neither of which were increased significantly by prior treatment of AA8 cells with an inhibitor (benzamide) or poly(adenosine diphosphoribose) polymerase. CldUrd -DNA, which gives higher frequencies of SCEs than BrdUrd-DNA, had more strand breaks than BrdUrd-DNA in AA8 cells after treatment with benzamide, while without benzamide there was no difference. The accumulation of breaks in CldUrd -DNA by benzamide was shown to occur rapidly, to reach a maximum by 90 min, and to be readily reversible after benzamide removal. Under all conditions, EM9 cells had more strand breaks than AA8 . These observed differences in strand breaks were not due to differences in incorporation efficiencies. For the different halogenated pyrimidines and cell types, there was a good correlation between the number of strand breaks and reduction in plating efficiencies.

Animals↗

The contribution of homologous recombination in preserving genome integrity in mammalian cells.

Although it is clear that mammalian somatic cells possess the enzymatic machinery to perform homologous recombination of DNA molecules, the importance of this process in mitigating DNA damage has been uncertain. An initial genetic framework for studying homologous recombinational repair (HRR) has come from identifying relevant genes by homology or by their ability to correct mutants whose phenotypes are suggestive of recombinational defects. While yeast has been an invaluable guide, higher eukaryotes diverge in the details and complexity of HRR. For eliminating DSBs, HRR and end-joining pathways share the burden, with HRR contributing critically during S and G2 phases. It is likely that the removal of interstrand cross-links is absolutely dependent on efficient HRR, as suggested by the extraordinary sensitivity of the ercc1, xpf/ercc4, xrcc2, and xrcc3 mutants to cross-linking chemicals. Similarly, chromosome stability in untreated cells requires intact HRR, which may eliminate DSBs arising during DNA replication and thereby prevent chromosome aberrations. Complex regulation of HRR by cell cycle checkpoint and surveillance functions is suggested not only by direct interactions between human Rad51 and p53, c-Abl, and BRCA2, but also by very high recombination rates in p53-deficient cells.

Amino Acid Sequence↗

Mutagenic and toxic activity of environmental effluents from underground coal gasification experiments.

Using bacterial bioassays, we have screened for the presence of mutagens and toxins in extracts from groundwater, and in tar from product gas, at the sites of two Lawrence Livermore National Laboratory (LLNL) in situ experiments: Hoe Creek II and Hoe Creek III. The sites exhibited different potential biological hazards, suggesting that different gasification processes may represent different human health concerns. We found that mutagens are present in groundwater, persist for at least 2 yr after gasification has been terminated, and show a change in activity with time-possibly in parallel with changes in chemical composition. Preliminary evidence suggests that the mutagens in groundwater are quinoline and aniline derivatives, while the toxins in groundwater may be phenolic compounds. In tar from the product gas, the organic bases and neutrals were found to be genotoxic in both bacterial and mammalian cells; the neutral compounds appear to be the major mutagenic health hazards. Neutral compounds constitute most of the tar (85-97 wt%) and were mutagenic in both the bacterial and mammalian cell assays. Tar in the gas stream may be a problem for the aboveground environment if gas escapes through fractures in the overburden. Because it is mutagenic and induces chromosomal damage to mammalian cells, the tar may represent a disposal problem as well. However, it is difficult to assess tar quantitatively as a health hazard because its mutagenic activity is low, possibly due to contaminants in the neutral fraction that act to suppress mutagenicity.

Animals↗