PubMed · 5467400
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1970-05-11. The DDT muddlement.. https://pubmed.ncbi.nlm.nih.gov/5467400/
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Unresolved DNA lesions trigger replication stress, forcing cancer cells to hijack DNA damage tolerance (DDT) networks, specifically translesion synthesis (TLS) and template switching, to sustain replication. While DDT prevents lethal fork collapse, error-prone TLS drives mutagenesis, tumor evolution, chemoresistance and radioresistance. Proliferating cell nuclear antigen post-translational modifications dynamically govern pathway selection. Cancer cells exploit this plasticity, creating actionable vulnerabilities such as postreplicative single-stranded DNA gaps. Emerging inhibitors targeting TLS polymerases, upstream regulators such as ubiquitin-specific peptidase 1 (USP1), and critical protein-protein interactions offer unprecedented opportunities for precision oncology. By integrating DDT inhibition with biomarkers such as homologous recombination deficiency and tumor mutational burden, we can drive synthetic lethality, sensitize tumors to genotoxic agents, suppress treatment-induced mutagenesis, and potentially enhance responses to immunotherapy.
Organochlorine pesticides (OCPs) were quantified by GC-ECD in tomato (Lycopersicon esculentum) during a vegetation period. Plants were harvested at 15, 60, and 151 days after seed germination. Leaves, stem, roots, and fruit (peel and flesh) were analyzed separately. The results showed that tomato plants were able to accumulate OCPs from soils, and a trend to reach the equilibrium among tissues at mature stages was also observed. Endosulfans comprised the main OCP group, probably due to its spray during summer months in the surrounding areas. Banned pesticides such as DDTs, heptachlor, and dieldrin were found. OCPs levels in the fruit were below the maximum residues limits (MRL) considered by the Codex Alimentarius. DDE/DDT and alpha-/gamma-HCH ratios of <1 would indicate recent inputs of DDT and lindane in the environment. The occurrence of OCPs in the study farm, where agrochemicals have never been used, is a result of atmospheric deposition of those pesticides.
Sediment samples of the Teltow Canal (Berlin, Germany) were analyzed with respect to extractable and nonextractable organic compounds. The study focused on the identification and quantitation of bound 2,2-bis(chlorophenyl)-1,1,1-trichlorethane (DDT) residues in order to obtain further information about the fate of DDT-derived compounds within the particulate matter of the aquatic environment. Various chemical degradation techniques and a complementary online pyrolysis-GC/MS method were applied to the pre-extracted sediment residues. Generally, the distribution of the bound DDT-related compounds was found to differ distinctly from the substances distribution within the extractable fraction. The main metabolite of the anaerobic degradation pathway (2,2-bis(chlorophenyl)-1,1-dichlorethane, DDD) is most abundant in the sediment extracts but occurred only in insignificant concentrations in the degradation products of all procedures applied. The most abundant DDT-metabolites released after the degradation procedures were 4,4'-DBP, 4,4'-DDA, and 4,4'-DDM. In addition, 4,4'-DDM was detected at rather high concentrations by pyrolytic analysis. The results imply a weak association to the nonextractable particulate matter based on noncovalent interactions for the observed DDT-related contaminants. The release of these compounds was initiated by the modification and degradation of the organic macromolecular matrix as well as of the inorganic material. Furthermore, numerous methoxychlor-related compounds were detected not only in the extracts but also in parts of the hydrolysis products.