A Study of the Acid Lability and Acute Toxicity of Dimethoxymethane in Rats

Green toxicological investigation for biofuel candidates

To avoid potential risks of biofuels on the environment and human, ecotoxicity investigation should be integrated into the early design stage for promising biofuel candidates. In the present study, a green toxicology testing strategy combining experimental bioassays with in silico tools was established to investigate the potential ecotoxicity of biofuel candidates. Experimental results obtained from the acute immobilisation test, the fish embryo acute toxicity test and the in vitro micronucleus assay (Chinese hamster lung fibroblast cell line V79) were compared with model prediction results by ECOSAR and OECD QSAR Toolbox. Both our experimental and model prediction results showed that 1-Octanol (1-Oct) and Di-n-butyl ether (DNBE) were the most toxic to Daphnia magna and zebrafish among all the biofuel candidates we investigated, while Methyl ethyl ketone (MEK), Dimethoxymethane (DMM) and Diethoxymethane (DEM) were the least toxic. Moreover, both in vitro micronucleus assay and OECD QSAR Toolbox evaluation suggested that the metabolites present higher genotoxicity than biofuel candidates themselves. Overall, our results proved that this green toxicology testing strategy is a useful tool for assessing ecotoxicity of biofuel candidates.

Testicular Toxicity of Candidate Fuel Additive 1,6-Dimethoxyhexane: Comparison with Several Similar Aliphatic Ethers

Previous studies of the toxicity of candidate fuel additives identified severe testicular toxicity in animals exposed to 1,6-dimethoxyhexane (DMH). A series of studies were conducted to characterize the effects of DMH on spermatogenesis and to compare the effects of DMH with responses to structural similar aliphatic ethers. In the first study, sexually mature male rats were administered a single dose (600 mg/kg) of DMH, and subsets of animals were sampled at intervals post exposure (PE). Both testis and thymus weight declined steadily after DMH exposure, both being significantly lower than control by 7 days PE. Treatment with DMH led, at 24 to 48 h PE, to an increase in dying primary spermatocytes in seminiferous tubule stages I-IV and stages XII-XIV, but not intervening stages. The affected cohort of germ cells was seen progressing through the developmental sequence of spermatogenesis as numbers of dying cells returned to control levels by 7 days PE, coincident with a significant decline in the proportion of round spermatids among germ cells as determined by flow cytometry. Resolution of round spermatids to control levels by day 21 PE coincided with a reduction in condensed spermatids (homogenization-resistant spermatid nuclei) and was followed at 28 days PE by a significant reduction in cauda epididymal sperm counts. Further studies of repeated exposures to DMH (200 mg.kg(-1).day(-1), 5 days per week for 4 weeks) confirmed the significant testis toxicity of this material. In contrast, similar treatment with any of a variety of structurally similar aliphatic ethers had little or no impact on testis function. Methoxyacetic acid, previously shown to cause rapid death of some meiotic germ cell stages, was found at high concentrations in the urine of DMH-treated rats but not in rats treated with other ethers, suggesting that DMH exerts its testis toxicity via metabolism to this substance. These results demonstrate that DMH selectively deletes germ cells from the testis At the very early or very late pachytene, diplotene, or M-phase spermatocyte stages, possibly through conversion to MAA.

Short-term oral toxicity of butyl ether, ethyl hexyl ether, methyl heptyl ether and 1,6-dimethoxyhexane in male rats and the role of 2-methoxyacetic acid

A 4-week oral study was conducted in male rats to characterize and compare the toxicity of four aliphatic ethers (butyl ether, BE; ethyl hexyl ether, EHxE; methyl heptyl ether, MHpE; and 1,6-dimethoxyhexane, DMH) which have been proposed as high-cetane diesel additives. Male Sprague-Dawley rats (280+/-20 g) were divided into groups of seven animals each and were administered by gavage low (2mg/kg body weight), medium (20mg/kg) or high (200mg/kg) doses of BE, EHxE, or MHpE, 5 days per week for 4 weeks. Another group of animals was administered DMH at 200mg/kg while the control group received the vehicle (corn oil at 1 ml/100g bw) only. At the end of the treatment period, relative testis weights and thymus weights were significantly decreased in the DMH group but not in animals receiving BE, EHxE, or MHpE. Microscopic examination revealed degeneration of the seminiferous tubules and reduction of sperm density in the epididymides in the DMH treatment group. Urinary creatine/creatinine ratio, a sensitive indicator of testicular damage, was markedly elevated in the DMH treated animals but not in those treated with BE, EHxE, or MHpE. In the bone marrow, DMH caused mild dyserythropoiesis and dysthrombopoiesis, while BE, EHxE, and MHpE produced mild increases in granulocytes and myelocyte/erythrocyte ratio. All four ethers at 200mg/kg caused mild histological changes in the thyroid but no significant modulation in the circulating thyroxin (T4) or triiodothyronine (T3) levels. All four ethers produced hepatic effects at 200mg/kg consisting of mild, adaptive histological changes, increased urinary ascorbic acid output, and elevation in the activities of one or more xenobiotic metabolizing enzymes (benzyloxyresorufin-O-dealkylase, UDP-glucuronosyltransferase, glutathione-S-transferases). The level of 2-methoxyacetic acid (MAA), a known testicular and developmental toxin, was significantly increased in the urine and plasma of animals treated with DMH but not in those administered the high dose BE, EHxE, or MHpE. Amomg the individual rats treated with DMH, the MAA level appeared to correlate with the severity of toxicity such as testicular and thymic weights, and urinary creatine/creatinine ratio. It is concluded that BE, EHxE, and MHpE differed from DMH in that they did not produce testicular or thymic toxicity. All four ethers at high dose caused changes to the thyroid, liver and bone marrows that were mild and adaptive in nature. MAA appeared to be the proximal toxicant in DMH treated animals but the route by which DMH is metabolized to MAA remains to be elucidated.