The results of this study indicated that administering 1.6 mg/kg/day of DEG for 30 days in rats did not appear to produce readily detectable detrimental effects on higher cognitive brain functions, including exploratory, spatial, and avoidance capabilities. Anxiety-related behaviors also appeared unaffected by DEG exposure. Diethylene glycol is recognized as a hazardous substance; ingestion can lead to mortality and severe complications across various organ systems, including the renal and nervous systems (
1). While the precise mechanisms of damage remain incompletely understood, toxicity is likely dose-dependent (
14). Given suggestions that DEG poisoning can symmetrically affect the basal ganglia, thalamus, amygdala, hippocampus, brainstem, and white matter, it is plausible that DEG could indirectly influence learning and memory processes. Hasbani et al. reported a case of encephalopathy and rapid quadriplegia in an individual following consumption of a DEG-containing solution. Data suggest that DEG poisoning may induce acute primary axonal sensorimotor polyneuropathy (
4). Sosa et al. also characterized DEG poisoning resulting from contaminated cough syrup distributed in Panama in 2006 (
15). In addition to acute kidney damage, most patients with DEG poisoning also exhibited progressive neurological signs and symptoms (
16). A 2015 study reported that exposure to di-(2-ethylhexyl) phthalate (DEHP) at concentrations of 50,200 mg/kg/d reduced NR1 and NR2B subunit levels of the N-methyl-D-aspartate (NMDA) receptor in the hippocampus of juvenile mice, leading to learning and memory deficits (
17). While DEHP is a different compound, this finding highlights that environmental chemicals can indeed modulate critical synaptic components like NMDA receptors, which are well-known for their essential role in synaptic plasticity, learning, and memory. Although our current behavioral study at a low DEG dose did not reveal cognitive deficits, it is plausible that DEG, particularly at higher exposure levels or through different mechanisms not captured by our behavioral tests, could also interfere with such neurochemical pathways. Therefore, future molecular investigations are crucial. For instance, examining the expression levels of NMDA receptor subunits, such as NR2B, in key brain regions like the hippocampus following DEG exposure, as suggested by the reviewer, could provide valuable insights into its potential neurochemical impact. Such studies, alongside electrophysiological assessments of synaptic function, would help to elucidate whether DEG can alter neuronal excitability or plasticity even in the absence of overt behavioral changes at low doses, or at doses approaching a toxic threshold.
These established neurotoxic effects at high doses are in stark contrast to the findings of the current study. Here, using a DEG dose of 1.6 mg/kg/day – representing the maximal safe human daily intake level according to EU guidelines – administered for 30 days, we did not observe impairments in the assessed measures of memory, learning, or anxiety-like behavior in rats. Diethylene glycol dose of 1.6 mg/kg/day used in our study, considered a safe reference for human intake by the EU based on kidney, liver, and brain effects, is substantially lower than the No observed adverse effect levels (NOAELs) typically reported for renal toxicity in rats exposed to a related compound, ethylene glycol (which are often in the range of 50 - 200 mg/kg/day in subchronic studies). This highlights differing potencies even among related glycols, though a detailed comparative toxicological review is beyond our current scope.
5.1. Conclusions
In conclusion, while it is well-established in the literature, including reports of significant neurotoxicity such as spinal cord demyelination at high doses (e.g., 4 - 6 g/kg in rats), the findings from the present study suggest that sub-chronic oral administration of a comparatively very low dose of DEG (1.6 mg/kg/day for 30 days) did not result in detectable impairments in the specific cognitive functions (object recognition, spatial learning and memory, passive avoidance) or anxiety-like behaviors assessed in male Wistar rats. This underscores the critical importance of dose in determining DEG’s toxicological profile. Nevertheless, these findings should be interpreted within the scope of the behavioral paradigms employed and the exposure duration. Further investigations, potentially employing molecular and electrophysiological techniques, as well as examining longer exposure periods or more sensitive neurological endpoints, are warranted to provide deeper insights into the full spectrum of potential effects of chronic low-level DEG exposure on neuronal physiology and complex behaviors.
5.2. Study Limitations
While the quantitative MWM data (e.g., time in target quadrant, platform crossings) indicated no impairment in spatial memory, the study would have been strengthened by the inclusion of qualitative data such as heatmaps or path traces from the probe trial to visually confirm search strategies; however, these detailed raw tracking outputs were not available from the original dataset. Additionally, while swim speed in the MWM was unaltered, indicating no gross motor impairments that would confound cognitive testing in that apparatus, the study did not include a dedicated test of fine motor coordination and balance, such as the rotarod. Future studies could incorporate such measures for a more comprehensive assessment of potential neuromotor effects.
A consideration in interpreting the uniform lack of statistically significant findings in this study is statistical power. Post-hoc power analyses revealed that with the current sample sizes, the study was adequately powered to detect large effect sizes (e.g., Cohen’s d > ~1.1 - 1.3 depending on the test) for the primary outcome measures. However, the observed effect sizes for the differences between the DEG and saline groups were generally in the small to moderate range. Consequently, the achieved power to detect these specific observed differences was low. While the consistent pattern of non-significance across multiple cognitive domains suggests that DEG at 1.6 mg/kg/day for 30 days does not exert a strong, readily detectable influence, the possibility of a true, but very subtle, type II error cannot be entirely excluded. Future studies employing larger sample sizes would be beneficial to more definitively assess potential effects of very small magnitudes.
It is crucial to emphasize that the findings of this study, which indicate a lack of detectable cognitive impairment, are specific to the low dose of DEG administered (1.6 mg/kg/day) and the 30-day sub-chronic exposure period in adult male Wistar rats. These results cannot and should not be generalized to scenarios involving higher doses or more prolonged, chronic exposures. As discussed, DEG exhibits clear dose-dependent toxicity, with severe neurological and renal effects documented at high exposure levels. Similarly, the potential for cumulative effects or different toxicological profiles to emerge with truly chronic low-level exposure warrants distinct investigation. Therefore, further research is required to understand the potential risks associated with higher acute or sub-chronic doses of DEG, as well as the consequences of long-term, continuous exposure, even at levels currently considered safe for shorter durations. Such studies should also consider different developmental stages and potentially more sensitive or diverse neurological endpoints.
A further limitation is the absence of histopathological analysis (e.g., assessment of neuronal integrity or cell counts in brain regions like the hippocampus) to provide structural correlates for our behavioral findings. While no overt behavioral deficits were detected at the low dose of DEG used, such analyses would be essential in future studies, particularly if investigating higher doses or longer exposure periods, to more comprehensively evaluate DEG’s potential impact on brain structure.
An important consideration, particularly for the SOR tasks, was the notable inter-individual variability observed in some parameters, as reflected by relatively large standard errors of the mean (SEMs) compared to the group means (e.g., for tactile and standard SOR in the control group,
Table 1). Such variability is not uncommon in tests relying on spontaneous exploratory behavior, which can be influenced by intrinsic individual differences in temperament or subtle environmental factors. This high variability inherently reduces the statistical power to detect subtle differences between experimental groups and underscores the need for cautious interpretation of non-significant findings in these specific SOR paradigms. While our power analyses (discussed elsewhere) considered overall study power, this task-specific variability further emphasizes that any potential subtle effects of DEG in these SOR tests might have been obscured.