Abstract

Dinitrotoluenes (DNTs) are byproducts of the explosive trinitrotoluene (TNT), and exist as a mixture of 2 to 6 isomers, with 2,4-DNT and 2,6-DNT being the most significant. The main route of human exposure at ammunition facilities is inhalation. The primary targets of DNTs toxicity are the hematopoietic system, cardiovascular system, nervous system and reproductive system. In factory workers, exposure to DNTs has been linked to many adverse health effects, including: cyanosis, vertigo, headache, metallic taste, dyspnea, weakness and lassitude, loss of appetite, nausea, and vomiting. Other symptoms including pain or parasthesia in extremities, abdominal discomfort, tremors, paralysis, chest pain, and unconsciousness have been documented. An association between DNTs exposure and increased risk of hepatocellular carcinomas and subcutaneous tumors in rats, as well as renal tumors in mice, has been established. This research was therefore designed targeting the liver to assess the cellular and molecular responses of human liver carcinoma cells following exposure to 2,4-DNT and 2,6-DNT. Cytotoxicity was evaluated using the MTT assay. Upon 48 hrs of exposure, LC50 values of 245 +/- 14.724 microg/mL, and 300 +/- 5.92 microg/mL were recorded for 2,6-DNT and 2,4-DNT respectively, indicating that both DNTs are moderately toxic, and 2,6-DNT is slightly more toxic to HepG2 cells than 2,4-DNT. A dose response relationship was recorded with respect to the cytotoxicity of both DNTs. Western blot analysis resulted in a significant expression (p<0.05) of the 70-kDa heat shock protein in 2,6-DNT-treated cells compared to the control cells and at the 200 microg/mL dose for 2,4-DNT. A statistically significant expression in c-fos was also observed at the 200 and 250 microg/mL treatment level for 2,4- and 2,6-DNT, respectively. However, no statistically significant expression of this protooncogene-related protein was observed at the doses of 0, 100, or 300 microg/mL or within the dose range of 0-200 microg/mL for 2,6-DNT. The 45-kDa growth arrest and damage protein was significantly expressed at the dose range of 200 - 250 microg/mL for 2,6-DNT and at the dose range of 200 - 400 microg/mL for 2,4-DNT. Expression of 153-kDa growth arrest and DNA damage protein was significant at the 100, 200, and 250 microg/mL doses for 2,6-DNT and at the 200 microg/mL dose for 2,4-DNT. Overall, these results indicate the potential of DNTs to induce cytotoxic, proteotoxic (HSP70), and genotoxic (GADD45/153) effects, as well as oxidative stress and pro-inflammatory reactions (c-fos).

Highlights

  • Dinitrotoluenes (DNTs) [CH3C6H3(NO2)2] are nitroaromatic compounds that are produced industrially and released into the environment as a result of human activities

  • A classical dose-response pattern was demonstrated with respect to the cytotoxicity of 2,4dinitrotoluene

  • Data obtained from this research clearly demonstrate that under similar exposure conditions, the cytotoxicity of the dinitrotoluenes is dose-dependent with LD50 values of 300 + 5.92μg/mL for 2,4-DNT and 245 + 14.72μg/mL for 2,6-DNT

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Summary

Introduction

Dinitrotoluenes (DNTs) [CH3C6H3(NO2)2] are nitroaromatic compounds that are produced industrially and released into the environment as a result of human activities. They are soluble in alcohol, ether, acetone, and benzene, but only slightly soluble in water – 270 parts per million (ppm) at 22°C (2,4-DNT) and 180 ppm at 20°C (2,6-DNT) [2,3,4,5] Both 2,4-DNT and 2,6-DNT are transformation products of 2,4,6-trinitrotoluene [4], the main pathway of their production is through the dinitration of toluene with nitric acid in the presence of sulfuric acid. Dinitrotoluenes are used in the manufacture of dyes, in munitions as smokeless propellant powder, and as gelatinizing and plasticizing agents in both commercial and military explosive compositions [6] Their major use is in the synthesis of toluenediamine, the organic intermediate used in the production of polyurethane [7]. In the United States, about 500 persons are estimated to be potentially exposed yearly to 2,4-DNT and 2,6-DNT during the production of munitions and explosives

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