Oral exposure to tire rubber-derived contaminant 6PPD and 6PPD-quinone induce hepatotoxicity in mice

Tire rubber derivative 6PPD and 6PPD-Q induce lipid accumulation in hepatocytes through ERRγ pathway

N-phenyl-N'-(1,3-dimethylbutyl)-p-phenylenediamine (6PPD) is a tire rubber antioxidant that can be oxidized to form derivative 6PPD-quinone (6PPD-Q). 6PPD and 6PPD-Q have been detected in human urine with concentrations reaching nanomolar levels. However, their human adverse effects and toxic mechanisms are not explicit. This study elucidated their lipid metabolism disruption effects on hepatic cells (HepG2) and revealed a potential molecular mechanism via estrogen-related receptor γ (ERRγ) pathway. The results of fluorescence competitive binding assay showed that 6PPD and 6PPD-Q could bind to ERRγ with an IC50 (the concentration of a ligand competing 50 % probe from ERRγ) of 9 nmol/L and 6 nmol/L, respectively. The reporter gene assay indicated that 6PPD-Q activated ERRγ in a concentration-dependent mode with the lowest observable effective concentration (LOEC) of 100 nmol/L and the maximum induction rate of 320 %, while 6PPD displayed weak ERRγ activity. The molecular docking showed that the binding energies of 6PPD/6PPD-Q with agonistic ERRγ were much lower than those with antagonistic ERRγ, implying that 6PPD/6PPD-Q tended to display ERRγ agonistic binding mode. The BODIPY fluorescence staining and triglyceride (TG) assay revealed that 6PPD and 6PPD-Q promoted lipid accumulation and TG production in HepG2 cells with LOEC of 10 nmol/L and 100 nmol/L, respectively. The ERRγ antagonist (GSK5182) co-exposure reversed the lipid induction effects of 6PPD/6PPD-Q, which confirmed the regulatory roles of ERRγ. Overall, our study revealed a novel endocrine disruption mechanism of 6PPD and 6PPD-Q via ERRγ and their hepatic lipid-inducing risks, providing novel information for their health hazard evaluation.

Toxicity of 6PPD-quinone in European seabass (Dicentrarchus labrax) under baseline and Vibrio alginolyticus challenge conditions: Protective insights from astaxanthin mitigation

6PPD-quinone, a widespread pollutant from tire wear, exhibits species-specific toxicity in aquatic organisms. This study examines the effects of 6PPD-quinone on European seabass (Dicentrarchus labrax) at an environmentally relevant concentration (2.85 μg/L, static renewal for five days) under both unchallenged conditions and bacterial challenge with Vibrio alginolyticus. The study also evaluates the hepatoprotective and immunomodulatory potential of astaxanthin supplementation (150 mg/kg diet for 30 days), derived from non-GMO Haematococcus pluvialis microalgae. While 6PPD-quinone exposure (up to 250 μg/L for 72 h) did not cause mortality, it induced neurological symptoms, including erratic swimming and respiratory distress. At 2.85 μg/L, biochemical analyses showed increased albumin, altered creatine kinase and blood urea nitrogen levels, and disrupted glucose homeostasis. Significant hepatic and gill lesions, such as diffuse hepatic necrosis and lamellar fusion, were observed. Astaxanthin mitigated liver necrosis, reduced inflammation, restored albumin/globulin ratios, and maintained glucose and triglyceride homeostasis. It improved gill integrity, reduced blood urea nitrogen, and enhanced lysozyme activity while preventing excessive immune activation. 6PPD-quinone disrupted immune gene expression in the head-kidney and spleen, which astaxanthin modulated. This study highlights 6PPD-quinone's physiological impact on seabass and astaxanthin's potential in mitigating pollutant toxicity, emphasizing that balanced immune responses are essential for maintaining health under environmental stressors.

Environmental concentrations of TCEP and TDCIPP induce dysbiosis of gut microbiotal and metabolism in the honeybee (Apis mellifera L.)

Organophosphorus flame retardants (OPFRs) have emerged as significant global pollutants, yet their harmful effects on pollinating insects remain largely unexplored. This study explored the toxicological effects of tri(2-chloroethyl) phosphate (TCEP) and tri(1,3-dichloro-2-propyl) phosphate (TDCIPP) on the gut microbiota and metabolic pathways of honeybees (Apis mellifera L.). Exposure to TCEP led to a 35 % reduction in intestinal wall thickness and significantly suppressed the expression of pyrimidine metabolism-associated enzymes, including CAD, DHODH, and ODCase (p < 0.05). In contrast, TDCIPP exposure increased the relative abundance of Snodgrassella and Lactobacillus by 40 % and 25 %, respectively, while exerting more extensive toxicity by disrupting nucleotide metabolism, oxidative stress responses, and microbial diversity. Histological assessments revealed that both chemicals compromised intestinal wall integrity and induced crypt loss in the midgut epithelium. Multi-omics analyses underscored distinct toxicity mechanisms: TCEP primarily inhibited pyrimidine biosynthesis, impairing nucleotide synthesis and DNA repair processes, whereas TDCIPP caused broader metabolic disturbances, likely attributed to its greater hydrophobicity. Notably, the enhanced prevalence of certain microbial taxa suggests potential microbial adaptations to TDCIPP-induced stress. This comparative analysis highlighted the detrimental effects of TCEP and TDCIPP on gut health and metabolism, critical factors for honeybee survival and ecological function. These findings underscored the urgent need for further investigation into the ecological hazards posed by OPFRs and provided a basis for developing mitigation strategies to address the impacts of persistent organic pollutants (POPs) on pollinators.

Child exposure to N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) and its derived quinone (6PPDQ) in e-waste areas: Urinary concentrations, sources, and health effect assessment

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6PPDQ) and its parent 6PPD are ubiquitous in the environment and may induce multi-endpoint toxicity. Electronic waste (e-waste) dismantling is an under-recognized source of 6PPD and 6PPDQ emissions, and there is a lack of epidemiological investigations into their presence and health effects in local populations. This study aimed to determine the urinary concentrations of 6PPD and 6PPDQ in children aged 2-7 years from e-waste dismantling areas and evaluate their potential risk to physical growth. We found that children from the e-waste area had significantly elevated urinary concentrations of 6PPD and 6PPDQ (median: 0.073 and 2.34 ng/mL) compared to those in the reference area (0.020 and 0.24 ng/mL, respectively). The estimated urinary excretions of 6PPDQ in the e-waste exposure group were considerably higher than that in the reference group (p < 0.001). Furthermore, a borderline significant association of co-exposure to high levels of 6PPD and 6PPDQ with lower BMI z-score (OR = 1.99, 95% Cl: 1.04, 3.82) was observed in the crude model and the model adjusted for age and gender. In conclusion, our study first reported the urinary 6PPD and 6PPDQ concentrations in children from e-waste dismantling areas. The result indicated that e-waste recycling activities contribute to significantly elevated body burdens of 6PPD and 6PPDQ in children, which may be a potential risk factor for physical growth. Further epidemiological and toxicological studies are needed to investigate the exposure and health risks, especially in vulnerable populations.

Identification of cell-surface receptors associated with 6-PPD quinone-induced reproductive toxicity in Caenorhabditis elegans after long-term and low-dose exposure: A primordial response including sword effect and shield effect

6-PPD quinone (6-PPDQ) has been frequently detected in different environmental matrices and widely identified as causing reproductive toxicity. However, the molecular initiation events of the reproductive toxicity induced by 6-PPDQ exposure, the primordial response, remain largely unknown. This study focused on investigating the primordial response induced by cell-surface receptors localized in the epidermis and intestine of 6-PPDQ exposure on reproductive toxicity. 7 cell-surface receptors were recognized to control the 6-PPDQ-induced reproductive toxicity. The epidermal cell-surface receptors (DCAR-1 and DAF-4) mainly mediated the primordial response by enhancing epidermal innate immune response or reproductive aging, and the intestinal cell-surface receptors (SER-5, FSHR-1, GON-2, DAF-2, and EGL-15) mainly mediated the primordial response by inducing oxidative stress or intestinal innate immune response. In epidermis, DAF-4 mediated "sword effect" and DCAR-1 mediated "shield effect" in response to the primordial response of the 6-PPDQ-induced reproductive toxicity. In intestine, SER-5, DAF-2, EGL-15, and GON-2 mediated "sword effect" and FSHR-1 mediated "shield effect" in response to the primordial response of the 6-PPDQ-induced reproductive toxicity. This study provides the "first station" of the effect of long-time 6-PPDQ exposure at environmentally relevant concentrations on reproductive capacity in organisms.

Comparative effects of 6PPD and 6PPD-Quinone at environmentally relevant concentrations on hepatotoxicity, glucolipid metabolism and ferroptotic response in adult zebrafish

The antioxidant 6PPD and its oxidized product 6PPD-Quinone (6PPDQ) have attracted considerable attention due to their various acute toxicities to aquatic organisms. However, the chronic toxicity of two compounds in aquatic animals is still unknown. Here, adult zebrafish were exposed to 6PPD and 6PPDQ at environmentally relevant concentrations (20 μg/L) for 28 days, and histological analysis showed that 6PPD caused more severe hepatic vacuolization than 6PPDQ. Meanwhile, 6PPD induced more serious lipid accumulation and a higher increase in triglyceride and total cholesterol levels than 6PPDQ, suggesting higher hepatotoxicity of 6PPD. Furthermore, transcriptomic analysis revealed that both compounds disturbed glucolipid metabolism to different degrees by altering the expression of different peroxisome proliferator-activated receptors (PPARs), in which 6PPD inhibited gene expressions in glucolipid metabolism possibly by PPARα, PPARβ and RXR, while 6PPDQ disrupted the expressions of partial genes in similar pathways probably via PPARγ. Additionally, 6PPD but not 6PPDQ increased Fe2+ content, decreased the protein levels of ferroportin 1, ferritin and glutathione peroxidase 4, accompanied with the increase of malondialdehyde level and the decrease of glutathione content, suggesting ferroptotic response by 6PPD. Overall, our data deepened the understanding of 6PPD- and 6PPDQ-induced hepatotoxicity association with glucolipid metabolism disorders and ferroptotic responses.

Environmental fate, toxicity, and mitigation of 6PPD and 6PPD-Quinone: Current understanding and future directions

N'-(1,3-Dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), a widely used antioxidant in the rubber industry, has garnered global attention due to the high toxicity and ecological-health risks posed by its environmental oxidation product, 6PPD-quinone (6PPD-Q). With the continuous release of tire wear particles (TWPs), 6PPD-Q is ubiquitously distributed in atmospheric, aquatic, and terrestrial environments, as well as within organisms, where it bioaccumulates through food chains. Notably, 6PPD-Q has been detected in human urine, serum, and cerebrospinal fluid, and its association with abnormal α-synuclein aggregation in the brains of Parkinson's patients further underscores its neurotoxic risks. This review systematically examines the environmental occurrence and migration patterns of 6PPD and 6PPD-Q, their multisystem toxicity, highly sensitive detection technologies, and pollution control strategies, while highlighting critical gaps in current research, such as chronic exposure mechanisms, combined pollution effects, and environmental safety thresholds. By synthesizing existing knowledge, this review provides a scientific foundation for elucidating the ecological and health risks of 6PPD-Q, offering critical insights to advance environmental regulatory policies, promote green transformation in the rubber industry, and safeguard global ecological security. Future research should prioritize long-term toxicity studies, refined detection techniques, and sustainable regulatory frameworks to mitigate the ecological and health risks posed by these emerging contaminants.

Low-dose tire wear chemical 6PPD-Q exposure elicit fatty liver via promoting fatty acid biosynthesis in ICR mice

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine-quinone (6PPD-Q) as a major metabolite of tire wear chemical 6PPD has been demonstrated to be an emerging burden of exposure in human populations, via contamination from drinking water, air particulate matter and food sources. Whilst increasing attention has been moved toward its adverse effect, the potential hepatotoxicity of 6PPD-Q in mammals at realistic dose remains unknown. Here, the toxic effects of 6PPD-Q at environmentally relevant dose on the liver of adult mice and its underlying mechanism were investigated through an integrative approach combining transcriptomic and lipidomic analyses. We found that 6PPD-Q exposure induced excessive lipid deposition following three weeks of exposure, ultimately contributing to the pathogenesis of fatty liver disease. Mechanistically, 6PPD-Q exposure caused a remarkable increase in the contents of fatty acids within the hepatic tissue of mice by enhancing their biosynthesis, thereby facilitating lipid deposition. In summary, this study provides a new understanding on the endocrine disrupting effects of 6PPD-Q on hepatic lipid metabolism and how it may contribute to elevated risk of fatty liver disease. Our findings call for a potential public health attention on the risk assessment of 6PPD-Q, particularly towards the risk of chronic metabolic diseases.

Exploring the fate of 6PPD in zebrafish (Danio rerio): Understanding toxicokinetics, biotransformation mechanisms, and metabolomic profiling at environmentally relevant levels

In recent years, N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) has attracted significant attention in environmental science, yet its behavior in biological systems remains poorly understood. This study involved a 28-day zebrafish exposure experiment at three concentrations (2, 20, and 200 μg/L), to investigate its physiologically based toxicokinetic (PBTK) properties, the formation of biotransformation products, and the metabolic characteristics of liver tissue. The results indicated that the liver and intestines are key organs for 6PPD accumulation, with tissue-specific distribution patterns. The biotransformation of 6PPD in the liver involves various phase I and phase II metabolic reactions, including hydroxylation, N-dealkylation, and sulfation processes. Furthermore, Metabolomics analysis revealed substantial changes in both the diversity and abundance of liver metabolites with increasing 6PPD concentrations, particularly in key biological processes such as lipid metabolism, amino acid metabolism, and redox balance. Notably, significant disruptions in sphingolipid and glycerophospholipid pathways suggest 6PPD may impair membrane fluidity and stability, potentially leading to membrane damage and dysfunction. Overall, this study provides crucial insights into the biological behavior of 6PPD in zebrafish, contributing essential knowledge for its ecotoxicological evaluation.

Polystyrene microplastics and cypermethrin exposure interfered the complexity of antibiotic resistance genes and induced metabolic dysfunction in the gut of adult zebrafish

Environmental pollutants such as microplastics (MPs) and pesticides are becoming prevalent in aquatic ecosystems, posing risks to wildlife and human health. This study investigated the toxicological effects of polystyrene microplastics (PS-MPs) and cypermethrin (CYP) on adult female zebrafish (Danio rerio), focusing on intestinal microenvironment. Adsorption kinetics experimental results showed that PS-MPs can adsorb a certain amount of CYP on its surface, thereby forming a new type of composite pollutant. After exposure to red fluorescent PS-MPs for 4 days, it was found that the PS-MPs could enter the zebrafish and accumulate in the intestines. Five-month-old female zebrafish were exposed to PS-MPs, CYP, and a mixture of both for 21 days. After exposure, feces were collected and analyzed using metagenomic sequencing to determine microbial composition and functional changes. Metagenomic sequencing of naturally excreted feces showed that co-exposure synergistically reduced α-diversity and shifted community structure, with marked losses of beneficial Fusobacteriota, Firmicutes and Cetobacterium somerae and enrichment of pathogenic Preplasmiviricota. Functional annotation indicated that PS-MPs alone up-regulated glycoside hydrolases and glycosyl-transferases, whereas CYP and the co-exposure group suppressed a great number of the top 50 carbohydrate-active enzymes and decreased secondary metabolic pathways linked to amino-acid, lipid and carbohydrate metabolism pathways. Antibiotic-resistance gene (ARGs) profiling identified 57 ARG types (such as sul1, adeF, lnuC and mphA) after co-exposure. Finally, key genes related to amino acid metabolism, carbohydrate metabolism, and lipid metabolism in intestinal tissue were significantly altered. Collectively, our data demonstrated that PS-MPs and CYP exposure amplified gut dysbiosis, metabolic dysfunction and ARG complexity in zebrafish. Overall, the study highlighted the potential risks of combined environmental pollutants on intestinal microbiota, with implications for ecosystem health.

Combined Analysis of Network Toxicology and Multiomics Revealed the Potential Mechanism of 6PPDQ-Induced Hepatotoxicity in Mice

6PPDQ, a rubber tire-derived environmental pollutant, exhibits significant hepatotoxicity. However, its hepatotoxic mechanisms remain insufficiently studied and systematically evaluated. This study integrated network toxicology, transcriptomics, and metabolomics to investigate its toxicity mechanisms. ADMETlab 3.0 was used to predict physicochemical properties and multiorgan toxicity. The targets related to 6PPDQ and liver injury were obtained from public databases, and a protein-protein interaction (PPI) network was constructed to identify key targets. Meanwhile, molecular docking was performed to assess 6PPDQ's binding affinity to core proteins. Transcriptomics and differential gene expression analysis were performed on the livers of Kunming mice exposed to 4 mg/kg 6PPDQ to explore transcriptomic alterations, while metabolomic profiling identified disrupted metabolic pathways. Network toxicology results reveal that 6PPDQ primarily induces hepatotoxicity through apoptosis, inflammation, and lipid metabolic disturbances. Key targets, including P53, Mapk1, Mapk14, Casp8, Traf6, Ripk1, and Tnf, are identified, with strong binding affinities suggesting direct interactions. Transcriptomic and metabolomic analyses further confirms disruptions in TNF, NF-kappa B, oxidative phosphorylation, autophagy pathways, and glycerolipid metabolism. Overall, this study provides a comprehensive mechanistic framework for 6PPDQ-induced liver injury in mice and provides a new perspective for subsequent studies on the mechanism of 6PPDQ hepatotoxicity.

Enantioselectivity in human urinary excretion of N-(1,3-dimethylbutyl)-N'-phenyl-1,4-benzenediamine (6PPD) and 6PPD-quinone

Human exposure to of N-(1,3-dimethylbutyl)-N'-phenyl-1,4-benzenediamine (6PPD) has raised global concerns due to its documented toxic effects, including hepatotoxicity, metabolic disruption, and potential contributions to organ damage. 6PPD-quinone (6PPD-Q), a ubiquitous transformation product of 6PPD, has been identified as a major toxicant linked to acute mortality in aquatic species, underscoring its ecological and human health risks. While these compounds exist as enantiomers with demonstrated differences in environmental behavior and toxicity, their enantiomer-specific distribution and excretion patterns in humans remain unknown limiting accurate risk assessments. This study analyzed 6PPD and 6PPD-Q in 109 pairs of whole blood and urine from general Chinese adults at the enantiomer-specific level. Results showed that 6PPD (range < LOD-0.60 ng/mL) and 6PPD-Q ( Collapse

Key Words

• Enantioselectivity
• Human behavior
• Human exposure
• Renal clearance
• Rubber additives

Collapse

MESH Headings Collapse

Grants Collapse

Affiliation(s)

Hanfeng Chen Department of Neurology, The First Affiliated Hospital, School of Medicine, Zhejiang University, Hangzhou, Zhejiang, 324000, PR China
Hangbiao Jin Key Laboratory of Microbial Technology for Industrial Pollution Control of Zhejiang Province, College of Environment, Zhejiang University of Technology, Hangzhou, Zhejiang, 310014, PR China
Fangfang Ren Key Laboratory of Microbial Technology for Industrial Pollution Control of Zhejiang Province, College of Environment, Zhejiang University of Technology, Hangzhou, Zhejiang, 310014, PR China
Ruyue Guo Key Laboratory of Microbial Technology for Industrial Pollution Control of Zhejiang Province, College of Environment, Zhejiang University of Technology, Hangzhou, Zhejiang, 310014, PR China
Jianqiang Zhu Department of Environmental Engineering, Taizhou University, Taizhou, Zhejiang, 318000, PR China
Kaiyuan Huang Department of Neurosurgery, The First Affiliated Hospital, School of Medicine, Zhejiang University, Zhejiang, 310003, PR China.

Collapse

Collaborators Collapse

Associations of human exposure to 6PPD and 6PPDQ with colorectal cancer: A mixture analysis

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) and its oxidation product, 6PPD-quinone (6PPDQ), are widely present in the environment. Toxicological studies have demonstrated that they can induce adverse health effects on the intestinal system. However, epidemiological studies examining the association between human 6PPD and 6PPDQ exposure and colorectal cancer (CRC) risk remain scarce. In this study, human urinary 6PPD and 6PPDQ concentrations were analyzed in 329 controls and 367 CRC cases from Quzhou, China. A combination of analyses, including unconditional logistic regression, Bayesian kernel machine regression (BKMR), and restricted cubic spline analysis, was employed to evaluate associations between urinary 6PPD and 6PPDQ levels and CRC risk, adjusting for demographic and lifestyle variables. The median concentration of 6PPDQ in CRC cases (0.94 vs 0.14 μg/g creatinine) was significantly higher than that in controls (Mann-Whitney U test, p = 0.001), while the median concentration of 6PPD showed no significant (p = 0.061) difference between the two groups (0.31 vs 0.38 μg/g creatinine). Higher urinary 6PPDQ concentrations were significantly associated with increased CRC risk, especially among participants with third (adjusted OR = 2.79, 95 % CI: 1.76-4.47; p for trend <0.001) and fourth (adjusted OR = 7.13, 95 % CI: 4.31-12.0; p for trend <0.001) quartiles of exposure. Additionally, the joint effects of 6PPD and 6PPDQ exposure, assessed using the BKMR model, indicated a positive association with CRC risk, suggesting a cumulative risk from co-exposure. This study provides the first epidemiological evidence linking human 6PPDQ exposure to CRC risk, highlighting its potential role in colorectal carcinogenesis.

p-Phenylenediamines and their derived quinones: A review of their environmental fate, human exposure, and biological toxicity

p-Phenylenediamines (PPDs) are widely used as antioxidants in numerous rubber products to prevent or delay oxidation and corrosion. However, their derived quinones (PPD-Qs), generated through reactions with ozone, are ubiquitous in the environment and raise significant health and toxicity concerns. This review summarizes the current state of knowledge on environmental distribution and fate, human exposure, and biological toxicity of PPDs and PPD-Qs, and makes recommendations for future research directions. Although PPDs and PPD-Qs have been monitored in a variety of environmental matrices, studies on soil, sediment, and organisms remain limited. This shortcoming hinders our understanding of their distribution patterns and migration mechanisms in these specific environments. These contaminants can enter the human body through various exposure routes, but toxicological studies have not yielded sufficient results to derive risk thresholds for the assessment of human health. Most studies examining biological and toxicological effects have focused on acute exposure scenarios, which do not accurately reflect the long-term interactions that occur in natural settings. The toxic effects of PPDs and PPD-Qs on zebrafish, nematodes, and mammals include neurobehavioral changes, reproductive dysfunction, and digestive damage, which are linked to mitochondrial stress, DNA adduct formation, and disrupted lipid metabolism, respectively. However, the underlying toxicological mechanisms remain poorly understood. Future research should prioritize the investigation of the impacts of PPDs and PPD-Qs on various organizational levels within biota to provide a scientific basis for developing effective risk management measures.

Correlation between 6PPD-Q and immune along with metabolic dysregulation induced liver lesions in outdoor workers

Outdoor workers who are exposed to traffic-derived pollutants often suffer from a range of diseases, with liver disease being particularly notable. Recently, a rubber stabilizing additive antioxidant N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) and its transformed-quinone product 6PPD-quinone (6PPD-Q) attracted attention. However, their implication for human health remains inadequately elucidated. In this study, outdoor and indoor workers were recruited to analyze 6PPD and 6PPD-Q distribution in their serum and urine. Simultaneously, blood cell counts, liver function, renal function, blood glucose level, and lipid profile were evaluated by 23 physiological parameters. For the first time, we found that the concentrations of 6PPD (0.54 - 1.66 μg L-1) and 6PPD-Q (0.58 - 4.04 μg L-1) in outdoor group serum were two- and three-fold in the indoor group, respectively. Compared with indoor workers, 18 biochemical parameters, notably total bilirubin and indirect bilirubin, were elevated in outdoor workers (p < 0.05). A computed tomography scan showed liver lesions in 60% of the outdoor group, whereas only 30% of the indoor group. The statistical analysis exhibited that significant positive correlations exist between the serum 6PPD-Q and immune cell counts, total bilirubin, indirect bilirubin, and triglycerides in human beings (p < 0.05). The logistic regression implied that for each 1 μg L-1 increase of 6PPD-Q in serum, the risk of human liver lesions increased by 2.31 times. Our results suggest that outdoor exposure is associated with increased concentrations of 6PPD-Q in serum, which could potentially influence glucose and lipid metabolism, immune cell regulation, and liver health.

Molecular insight on conformational alterations and functional changes of acetylcholinesterase induced by an emerging environmental pollutant 6PPD-quinone

The emerging pollutant N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6PPD-quinone) has attracted broad attention because of its widespread presence and harmful impacts, including hepatotoxicity and neurotoxicity. Acetylcholinesterase (AChE) is commonly used as a classical biomarker for assessing toxicity in the nervous system. Here, the interaction mechanism between AChE and 6PPD-quinone was investigated using a combination of multispectral and computational approaches, including enzyme activity assay, fluorescence thermodynamic titration, circular dichroism (CD) spectroscopy, molecular dynamics (MD) simulation, computational alanine scanning (CAS), and free energy landscape (FEL) analysis, among others. The result indicates that 6PPD-quinone spontaneously binds into the active site of AChE, thereby competitively inhibiting enzyme's activity. The interaction is primarily facilitated by hydrogen bonds and van der Waals forces, exhibiting a binding constant (Kb) of 1.044 × 104 M-1 at 298 K. The introduction of 6PPD-quinone causes a reduction in the α-helix content of AChE, making the structure less stable and more relaxed. Furthermore, the FEL analysis of AChE revealed that, with the presence of 6PPD-quinone, the number of global minima of AChE increased from 2 to 2-3. Additionally, Molecular docking outcomes exhibit that 6PPD-quinone interacted with tyrosine (TYR) 337, TYR124, tryptophan (TRP) 86, serine (SER) 203, glycine (GLY) 120 and other residues of AChE. CAS analysis shows binding free energy changes (ΔΔGbinding) of TRP86, TYR337 were 5.17 and 2.57 kcal mol-1, respectively, highlighting their key roles in the binding process of 6PPD-quinone with AChE. The interactions of 6PPD-quinone with the TRP86 and TYR337 may be the reason for the decrease in AChE activity.

Development of a quantitative analytical method for 6PPD, a harmful tire antioxidant, in biological samples for toxicity assessment

This study developed and validated a high-sensitivity analytical method for the quantification of N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), a hazardous antioxidant used in tires, to support the effective management of its environmental exposure. Using an HPLC-UV system with acetonitrile and deionized water as the mobile phase, the method did not require salts or acids. The calibration curve exhibited excellent linearity (R2 = 0.9999) with detection limits of 0.17 pg μL-1 (LOD) and 5.51 pg μL-1 (MDL), underscoring its ultra-trace detection capability. A pretreatment protocol was developed to quantify 6PPD in mouse liver samples. The protocol achieved a relative recovery rate of 71.89 % and high precision across all spiking concentrations (mean RSD = 2.20 ± 0.92 %). The validated methods were applied to analyze 6PPD residues in mouse liver following intratracheal instillation exposure. At 9 h post-exposure, residual 6PPD concentrations increased significantly in a dose-dependent manner (R2 = 0.9906), with a relative distribution of 0.06 ± 0.01 %. This cost-effective and reliable method provides a practical tool for quantifying 6PPD in environmental and biological matrices. The findings enhance the understanding 6PPD exposure dynamics and support the establishment of regulatory guidelines for managing its ecological and human health risks.

The endoplasmic reticulum-mitochondrial crosstalk involved in nanoplastics and di(2-ethylhexyl) phthalate co-exposure induced the damage to mouse mammary epithelial cells

With the extensive use of plastic products, significant amounts of microplastics, nanoplastic particles (NPs), and plasticizers such as Di(2-ethylhexyl) phthalate (DEHP) are continuously released into the environment. However, the toxic effects of NPs alone or in combination with DEHP on mammary glands remain unreported. This study investigates the impacts of NPs and DEHP on the structure and function of mouse mammary epithelial cells and elucidates the underlying molecular mechanisms. We found that co-exposure to NPs and DEHP induced severe pyroptosis, inflammation and oxidative stress in HC11 cells. Co-exposure also caused mitochondrial damage, as evidenced by changes in mitochondrial membrane potential, increase in mitochondrial ROS and inhibition of ATP production. Moreover, NPs and DEHP co-exposure increased the transcriptional levels of endoplasmic reticulum (ER) stress-related genes, activated the inflammation-related NLRP3 signaling pathway, and damaged the cell membrane integrity. Notably, Co-exposure enhanced the ER-mitochondria crosstalk in HC11 cells, as evidenced by the upregulated transcriptional levels of ER Ca2+ channel proteins (Ip3r1, Grp75 and Vdac1), increased mitochondrial Ca2+ levels, and expanded mitochondrial-ER contact areas. In summary, this study revealed that NPs and DEHP co-exposure had the potential to induce pyroptosis and inflammation by enhancing the ER-mitochondria crosstalk, ultimately resulting in injury to mammary glands. These findings would provide some new insights into the molecular mechanisms underlying the toxic effects of NPs and DEHP to mammary glands.

6PPD induces apoptosis and autophagy in SH-SY5Y cells via ROS-mediated PI3K/AKT/mTOR pathway: In vitro and in silico approaches

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), an extensively employed antioxidant in rubber materials, is considered as an emerging contaminant. 6PPD was proven to have potential neurotoxicity, which poses risks to human health. However, the research on its neurotoxicity is still limited. This work explored the neurotoxicity of 6PPD to SH-SY5Y cells and in-depth mechanisms with a combination of in vitro and in silico approaches. Our results indicated that 6PPD could reduce cell viability and cause oxidative damage by increasing reactive oxygen species (ROS) accumulation and altering the levels of glutathione (GSH), catalase (CAT), superoxide dismutase (SOD), and malondialdehyde (MDA). 6PPD induced neuronal apoptosis of mitochondrial pathway and autophagy dysfunction, as characterized by the increased expressions of Cleaved caspase-3, Bax/Bcl-2, Beclin-1, LC3-II/I, and P62. 6PPD downregulated the expression of PI3K, p-AKT, and p-mTOR, while the PI3K inhibitor suppressed PI3K/AKT/mTOR pathway and promoted both apoptosis and autophagy, indicating that PI3K/AKT/mTOR pathway was involved in 6PPD-induced apoptosis and autophagy. The inhibition of this pathway was attributed to ROS accumulation in SH-SY5Y cells. Molecular docking analysis further revealed that 6PPD exhibits strong binding affinity to PI3K, AKT, and mTOR protein molecules, which could effectively interfere with downstream signaling pathways. These findings enrich the understanding of 6PPD-induced neurotoxicity and contribute to the evaluation of ecological risks associated with 6PPD.

Assessment of tire-derived additives and their metabolites into fruit, root and leafy vegetables and evaluation of dietary intake in Swiss adults

Tire wear particles, released at an estimated 6 million tons annually worldwide, introduce various chemical substances into agricultural environments through atmospheric deposition, road runoff, and reclaimed wastewater. These tire-derived compounds are known to impact ecosystem health. This study investigates the transfer of such additives and their metabolites into vegetables, assessing human dietary intake. Using UPLC-MS/MS, eleven tire-related compounds were analyzed in 100 vegetable samples from nine Swiss retailers, including leafy (lettuce, cabbage, spinach), root (onion, potato, carrot), and fruit (tomato, bell pepper, zucchini, pumpkin) vegetables. Contamination was detected in all vegetable varieties. 31 % of the 100 samples contained benzothiazole (BTH), 1,3-diphenylguanidine (DPG), 6-PPD, or 1,3-dicyclohexylurea (DCU) at levels exceeding the limit of quantification (LOQ) whereas blank values remained below LOD. DPG was most frequently detected (18 %, n = 100), followed by 6-PPD (15 %, n = 100), DCU (10 %, n = 100), and BTH (3 %, n = 100). Spinach comprised 78 % of DPG-positive leafy samples. Daily intakes of 6-PPDQ, DCU, 6-PPD, and DPG from vegetables were estimated at 0-18.7, 0-57.7, 0-42.3, and 0-42.4 ng/person/day, respectively. While current toxicological data suggest no immediate health concerns, significant knowledge gaps remain regarding long-term toxicity. This study offers critical insights into the presence of tire-derived substances in agriculture and underscores the need for further research to better assess environmental and human health risks.

Review of Health Effects of Automotive Brake and Tyre Wear Particles

Non-exhaust emissions from brakes and tyres are becoming the major transport-related contributor of particulate matter (PM) pollution in cities. Furthermore, tyre microplastics are the major contributor of unintentionally released microplastics in all environmental compartments. The European Union introduced for the first time worldwide limits for brakes (PM10) and tyres (total abrasion mass) with the Euro 7 regulatory step. Thus, the interest in brake and tyre particles regarding health and environmental impacts has significantly increased in recent years. In this review, we summarise studies that assessed the impact of brake and tyre particles on human, mammalian, aquatic, and terrestrial cells and organisms. Furthermore, we summarise the studies that compared the impact of brake and tyre particles to other sources. We also critically examine the sampling methodologies of brake and tyre particles for health and environmental impact studies.

Prediction of p-phenylenediamine antioxidant concentrations in human urine using machine learning models

p-phenylenediamine antioxidants (PPDs) are extensively used in rubber manufacturing for their potent antioxidative properties, but PPDs and 2-anilino-5-[(4-methylpentan-2yl)amino]cyclohexa-2,5-diene-1,4-dione (6PPDQ) pose potential environmental and health risks. Existing biomonitoring methods for assessing human exposure to PPDs are labor-intensive, costly, and provide limited data. Thus, there is a critical need to develop predictive models for evaluating PPDs and 6PPDQ exposure levels to facilitate health risk assessments. In this study, machine learning (ML) models were developed to predict the concentration of three PPDs and 6PPDQ in human urine samples. A total of 759 participants from three cities in Zhejiang Province, China, provided urine samples, which were analyzed for PPDs and 6PPDQ concentrations using liquid chromatography-tandem mass spectrometry. Eight ML models were employed to predict PPDs and 6PPDQ concentrations based on demographic and environmental exposure factors such as age, gender, body mass index (BMI), and occupation. N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) was the most frequently detected PPD (mean 3.03 ng/mL, range < LOD-18.65 ng/mL), followed by 6PPDQ (mean 2.76 ng/mL, range < LOD-20.85 ng/mL) and N-phenyl-N'-cyclohexyl-p-phenylenediamine (mean 2.04 ng/mL, range < LOD-10.22 ng/mL). Random forest model demonstrated the highest accuracy in predicting PPDs and 6PPDQ concentrations in human urine among the ML models evaluated. Through the application of these models, age, BMI, and occupation emerged as significant predictors of urinary PPDs and 6PPDQ concentrations. This research significantly contributes by using ML models to enhance exposure assessment accuracy and efficiency, providing a novel framework for future studies on environmental health risks related to PPDs and 6PPDQ.

Inhalation exposure to tire rubber particle-sourced pollutant 6PPD-quinone involving basolateral amygdala impairment in male ICR mice

INTRODUCTION

The extensive use of 6PPD in tire rubber has led to its increase in atmospheric tire wear particles. 6PPD reacts with ozone to form 6PPD-quinone (6PPD-Q), a respiratory toxicant enriched in tire and road wear particles.

OBJECTIVES

The aim of this study is to decipher the potential sensitive target organs and toxic actions by inhalation exposure to atmospheric 6PPD-Q.

METHODS

This study employed a mouse inhalation exposure model to simulate environmental levels of 6PPD-Q at three concentrations of 0, 0.14, and 14 mg/m3. Using a 28-day exposure period followed by an equivalent recovery phase, we systematically evaluated the toxicological targets and effects of subacute exposure.

RESULTS

The findings revealed that, compared to pulmonary, cardiovascular, and metabolic organ damage, 6PPD-Q-induced neurotoxicity was more persistent and irreversible, particularly characterized by prolonged anxiety-like behaviors. Histopathological analyses of the basolateral amygdala, using Nissl staining and markers of neuronal aging, indicated substantial neuronal degeneration linked to elevated oxidative stress, identifying this region as a critical target of 6PPD-Q neurotoxicity. Transcriptomic analysis uncovered that the expression of Egr1, a transcription factor crucial for neuronal plasticity, was markedly dysregulated. Findings of significant downregulation at the gene level and an upward trend in protein expression suggest thatEgr1expression is influenced by translational efficiency, epigenetic modifications, and post-translational regulatory mechanisms. Egr1dysregulation disrupted downstream networks involving solute carrier proteins and calcium-binding proteins, contributing to aberrant neurobehavioral outcomes. Notably, the elevation ofEgr1protein levels in the basolateral amygdala but not in the cerebral cortex highlights the region-specific nature of 6PPD-Q's neurotoxic effects.

CONCLUSION

This study provides the first insights into the neurotoxicity and irreversibility of inhaled 6PPD-Q exposure, paving the way for future research into the long-term neurological consequences and regulatory mechanisms of 6PPD-Q.

Exposure to 6PPD-Q induces dysfunctions of ovarian granulosa cells: Its potential role in PCOS

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine-quinone (6PPD-Q), an environmental pollutant derived from the ozonolysis of the widely used tire rubber antioxidant 6PPD, has been found to accumulate in air, dust, and water, posing significant health risks. While its reproductive toxicity in male organisms has been established, its effects on female reproductive health remain unclear. Polycystic ovary syndrome (PCOS), a common endocrine disorder in premenopausal women, is known to be influenced by environmental pollutants. In this study, we exposed BALB/c mice intraperitoneally to 6PPD-Q, and they exhibited PCOS-like changes after 40 days, including alterations in hormone levels, estrous cycle arrest, and polycystic ovarian morphology. Then we identified significantly elevated levels of 6PPD-Q in the follicular fluid of PCOS patients compared to those with tubal infertility, and these levels were associated with clinical parameters. In the human ovarian granulosa cell line (KGN) studies, we demonstrated that 6PPD-Q induced granulosa cell apoptosis by inhibiting the PI3K/AKT/FOXO1 pathway, leading to ovarian damage and fertility decline. To our knowledge, this is the first study to report 6PPD-Q levels in human follicular fluid and its detrimental effects on female reproductive health, underscoring the need for further research on environmental impacts on PCOS.

Environmental factors ultraviolet a and ozone exacerbate the repeated inhalation toxicity of 6PPD in mice via accelerating the aging reaction

The burden of N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) and its oxidized products on human health can no longer be ignored due to the detection types and concentrations in the environment continue to increase. Environmental ozone (O3) and ultraviolet A (UVA) may induce ozonation and photoaging of 6PPD to produce toxic products. However, the impact of specific environmental conditions on the aging and toxic effects of 6PPD is unclear. This study investigated the aging effects of O3 and UVA on 6PPD, and compared the repeated inhalation toxicity of differently aging 6PPDs in C57BL/6 male mice. The result showed that UVA and O3 accelerated 6PPD aging, and the aging products varied depending on the O3 and irradiation conditions. After 10 weeks of inhalation intoxication at human comparable level, mice exhibited significant neurobehavior alterations, respiratory dysfunction, and DNA damage in the blood, showing significant heterogeneity among groups. Notably, 6PPD treated with perozonation and UVA aging may be the most toxic. The study suggests inhalation health risks of transportation derived tire pollutants under the influence of ground-level ozone and ultraviolet light need more attention, and provides new insights into risk assessment and pollution control of 6PPD and other pollutants from the perspective of environmental factors.

Mass Spectrometry Imaging Unveils the Metabolic Effect of 6PPD-Quinone in Exposed Mice

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6PPD-Q) has gained widespread attention as an emerging significant environmental contaminant, but its biochemical toxicity in mammals remains inadequately explored. In this study, the systemic toxicological effects of 6PPD-Q in mouse models exposed to both high and low doses were investigated. Matrix-assisted laser desorption/ionization mass spectrometry imaging (MALDI MSI) was applied to evaluate its effects on major organs, including the liver, kidneys, spleen, and testes. Notably, both high and low doses caused similar multiorgan metabolic disturbances, with significant changes in antioxidant levels, highlighting oxidative stress as a key factor in 6PPD-Q-induced damage. Further results revealed that 6PPD-Q disrupts critical metabolic pathways, including glutathione metabolism, ascorbic acid metabolism, energy metabolism, and amino acid metabolism, which are associated with systemic oxidative stress, immune dysfunction, and disruptions in liver, kidney and testis. This study provides important insights into the mechanisms of 6PPD-Q toxicity and underscores the need for further research to assess its potential health risks, which could guide future environmental policies and human health risk assessments.

6-PPD triggered lipid metabolism disorder and inflammatory response in larval zebrafish (Danio rerio) by regulating PPARγ/NF-κB pathway

As a synthetic rubber antioxidant, the environmental monitoring concentrations of N-(1,3-Dimethylbutyl)-N'-phenyl-p-phenylenediamine (6-PPD) have exceeded the risk threshold, attracting widespread attention. Although investigations into the harmful effects on zebrafish have commenced, a comprehensive exploration of its toxicological impacts and underlying molecular mechanisms remains to be conducted. By using zebrafish as a model, this study systematically evaluated 6-PPD-induced lipid metabolism disorders and inflammation response following environmental exposure. Bioinformatics analysis revealed that 6-PPD target genes enriched in the hepatitis B pathway, indicating potential hepatic toxicity via inflammatory pathways. Therefore, we hypothesize that 6-PPD could trigger hepatotoxicity through the crosstalk between lipid metabolism and inflammation. Further experiments substantiated this hypothesis by showing lipid accumulation in the liver following 6-PPD exposure, along with elevated triglyceride (TG) and total cholesterol (TC) levels, and imbalanced expression of lipid metabolism-related marker genes. Additionally, 6-PPD exposure induced the accumulation of reactive oxygen species (ROS) and inhibited the differentiation and maturation of immune cells, resulting in immune evasion. Most of these abnormalities were exacerbated in a dose-dependent manner with increasing concentrations of 6-PPD. The addition of the PPARγ pathway agonist puerarin (PUE) or NF-κB pathway inhibitor quinazoline (QNZ) to 6-PPD exposure group mitigated these toxic effects, validating our conjecture that lipid metabolism disorder and inflammatory responses may result from the regulation of the PPARγ/NF-κB pathway.

Acute cardiorespiratory effects of 6PPD-quinone on juvenile rainbow trout (Oncorhynchus mykiss) and arctic char (Salvelinus alpinus)

N-(1,3-Dimethylbutyl)-N'-phenyl-p-phenylenediamine-quinone (6PPD-quinone) is an environmental transformation product of the widely used rubber tire antioxidant, 6PPD. Found in stormwater runoff, 6PPD-quinone has been reported to cause acute lethality at ≤1 μg/L in salmonids like coho salmon, rainbow trout, and brook trout. Conversely, other species such as Arctic char and brown trout are insensitive, even when exposed to significantly greater concentrations (3.8-50 μg/L). Sensitive species exhibit symptoms such as gasping, spiraling, increased ventilation, and loss of equilibrium, suggesting a possible impact on cardiorespiratory physiology. This study investigated sublethal 6PPD-quinone toxicities, focusing on cardiovascular and metabolic effects in two salmonids of varying sensitivity: a sensitive species, rainbow trout (Oncorhynchus mykiss) and a tolerant species, Arctic char (Salvelinus alpinus). Fish were exposed to measured concentrations of 0.59 or 7.15 μg/L 6PPD-quinone, respectively, in respirometry chambers for 48 h to assess temporal changes in resting oxygen consumption compared to unexposed controls. Following exposure, cardiac ultrasound and electrocardiography characterized cardiac function in vivo, while blood gas analysis examined blood composition changes. In both species, changes in resting oxygen consumption were observed. In rainbow trout only, a decrease in end systolic volume and an increase in passive ventricular filling, cardiac output, and PR interval length were observed, indicating cardiac stimulation. Cardiorespiratory symptoms observed following rainbow trout exposure might partly be driven by a significant increase in methemoglobin, resulting in an impaired ability to oxygenate tissues. This study is the first to examine the effects of 6PPD-quinone exposure on the cardiorespiratory system of salmonid fishes and provides information invaluable to a better understanding of the mechanism of 6PPD-quinone toxicity.

Elucidating the size distribution of p‑Phenylenediamine-Derived quinones in atmospheric particles

Transformed from p-phenylenediamines (PPDs) antioxidant, PPD-derived quinones (PPD-Qs) have recently been recognized as emerging contaminants due to their potential negative impacts on the environment and human health. While there have been measurements of airborne PPD-Qs, the size distribution of PPD-Qs and the impact of particle size on PPD transformation chemistry remain largely unknown. Here, through the measurements of atmospheric particles in three megacities in China (Beijing, Xi'an, and Hefei), we find that PPD-Qs are widely distributed in these cities. Further analysis of the size-fractioned particles in Hefei indicates that 48 % of PPD-Qs reside in coarse particles. Given that previous studies mainly focus on the measurement of PPD-Qs in fine particles, the previously reported PPD-Q concentrations and the corresponding human exposure dosages are likely to be significantly underestimated. Furthermore, the ratio of PPD-Q to PPD concentration (PPD-Q/PPD) for particles with size range of 0.056 - 0.1 μm is up to 3 times higher than that with size range of 10 - 18 μm, highlighting the key role of particle size in determining the atmospheric oxidation reactivity of PPDs. Model simulations reveal a size-dependent pattern for the estimated concentration of particulate PPD-Qs in human body. In addition, we also demonstrate that PPD-Qs can induce the formation of cellular reactive oxygen species, suggesting that they may pose risks to human health. Overall, our results emphasize the importance of considering the particle size effect when evaluating the reaction potential and exposure risk of airborne PPD-Qs.

Exploring potential targets and mechanisms of renal tissue damage caused by N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6-PPDQ) through network toxicology and animal experiments: A case of chronic kidney disease

6-PPDQ is a new type of environmental contaminant contained in tire rubber. No studies have been reported on the potential targets and mechanisms of action of 6-PPDQ on renal tissue damage. In the present study, we used CKD as an example to explore the potential targets and biological mechanisms of renal injury caused by 6-PPDQ using Network toxicology and animal experiments. A total of 1361 6-PPDQ-related target genes were obtained from the CTD database. 17,296 CKD-related target genes were obtained through the GeneCards database. After intersecting the two, a total of 908 intersecting genes were obtained. Next, we constructed a PPI protein interaction network. Using different algorithms in Cytoscape software and "Logistic regression analysis", five key target genes were finally identified as NOTCH1, TP53, TNF, IL1B and IL6. We constructed a diagnostic model using five key target genes, and the ROC curves, calibration curves and DCA curves proved that the model has good diagnostic value. Molecular docking demonstrated high affinity between 6-PPDQ and five key target gene proteins. In animal experiments, repeated intraperitoneal injections of 6-PPDQ using different concentration gradients for 28 days revealed that the expression levels of five key target genes in renal tissues increased progressively with the increase of the concentration, and the damage to renal tissues was also aggravated. ssGSEA and animal experiments revealed a key role for activation of the MAPK signaling pathway. Finally, we also identified a significant correlation between five key target genes and the level of infiltration of multiple immune cells. In conclusion, these findings suggest that 6-PPDQ can cause damage to renal tissue and that the level of damage progressively increases with increasing concentration. Among them, NOTCH1, TP53, TNF, IL1B and IL6 may be its potential targets of action. Activation of the MAPK signaling pathway is a potential mechanism of action.

6-PPD quinone causes lipid accumulation across multiple generations differentially affected by metabolic sensors and components of COMPASS complex in Caenorhabditis elegans

The toxicity of 6-PPD quinone (6-PPDQ) has been frequently detected. However, the possible transgenerational effects of 6-PPDQ remain largely unclear. Due to short life cycle and high sensitivity to environmental exposure, Caenorhabditis elegans is useful for study of transgenerational toxicology. In C. elegans, we observed the transgenerational increase in lipid accumulation after parental generation (P0-G) exposure to 6-PPDQ at 0.1-10 μg/L. Accompanied with this, transgenerational increase in expressions of genes governing fatty acid synthesis and monounsaturated fatty acyl-CoAs synthesis and decrease in genes governing fatty acid β-oxidation were induced by 6-PPDQ exposure. Moreover, 6-PPDQ exposure at P0-G caused transgenerational activation of mdt-15 and sbp-1 encoding lipid metabolic sensors. Meanwhile, exposure to 6-PPDQ induced transgenerational activation of set-2 and inhibition in rbr-2, two genes encoding components of COMPASS complex. The 6-PPDQ induced transgenerational lipid accumulation could be strengthened by RNAi of set-2 and suppressed by RNAi of rbr-2. Additionally, 6-PPDQ induced transgenerational neurotoxicity could be increased by RNAi of mdt-15, sbp-1, and rbr-2, and inhibited by RNAi of set-2. Therefore, our results demonstrated the possibility in resulting in transgenerational lipid accumulation by exposure to 6-PPDQ.

Long-Term Exposure to Tire-Derived 6-PPD Quinone Causes Neurotoxicity and Neuroinflammation via Inhibition of HTR2A in C57BL/6 Mice

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6-PPDQ), a novel contaminant derived from tire wear, has raised concerns due to its potential neurotoxicity, yet its long-term effects on mammalian neurological health remain poorly understood. This study investigates the neurotoxic and neuroinflammatory impacts of prolonged 6-PPDQ exposure using male C57BL/6 mice. Behavioral assessments revealed significant cognitive deficits, while biochemical analyses demonstrated increased levels of reactive oxygen species, apoptosis, and blood-brain barrier (BBB) disruption. Elevated pro-inflammatory cytokines (TNF-α, IL-6, IL-1β) and activation of microglial cells were observed, indicating a robust neuroinflammatory response. Network pharmacology and molecular docking identified serotonin receptor HTR2A as a key target through which 6-PPDQ mediates its toxic effects. Activation of HTR2A by the agonist DOI (2,5-dimethoxy-4-iodoamphetamine) mitigated these effects, suggesting a potential therapeutic strategy. These findings provide the first evidence of 6-PPDQ-induced neurotoxicity in mammals, underscoring the need for preventive measures to protect neurological health.

Tire rubber-derived contaminants 6PPD and 6PPD-quinone reduce attachment and outgrowth of trophoblast spheroids onto endometrial epithelial cells

N-(1,3-Dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), a synthetic additive widely used in the rubber industry, and its oxidized product 6PPD-quinone (6PPDQ), have garnered widespread attention as an emerging hazardous chemicals owing to their potential detrimental effects on aquatic ecosystem and human health. The effects of 6PPD and 6PPDq on the female reproductive tract, especially embryo implantation, remain unknown and were investigated in this study. We used the spheroid attachment and outgrowth models of BeWo trophoblastic spheroids and Ishikawa cells as surrogates for the human blastocyst and endometrial epithelium, respectively. Treatment with the chemicals for up to 48 h decreased the viability of the cells in a dose- and cell line-dependent manner (20-100 μM 6PPD and 10-100 μM 6PPDQ for both the cell lines). At a noncytotoxic concentration, exposure of Ishikawa cells to 1 and 10 μM 6PPD reduced the attachment of BeWo spheroids and further inhibited their invasion and outgrowth on the endometrial epithelial monolayer. A similar result was observed in 1 μM 6PPDQ-exposed groups. Gene expression profiling of 6PPD- and 6PPDQ-exposed endometrial epithelial cells revealed that both 6PPD and 6PPDQ differentially regulated a panel of transcript markers toward overall downregulation of receptivity and invasion. The study provides the first proof of the adverse effects of 6PPD and 6PPDQ on human endometrial receptivity and trophoblast invasion during the window of implantation, warranting the need for further in vivo and clinical studies.

High-resolution observation per 1.5 h revealed prominent time-dependent daily contamination variations of p-phenylenediamine (PPD) antioxidants and their quinone derivatives PPDQs in PM2.5 from central China

p-Phenylenediamine (PPD) antioxidants and their quinone derivatives (PPDQs), as hot-spot novel contaminants in recent years, have been detected in air fine particulate matters (PM2.5) in multiple regions. However, current research all discussed the pollution of PPDs and PPDQs based on the collected PM2.5 samples at least in one day (23.5 h). In this work, an innovative study was conducted to investigate their precise daily pollution characteristics and health risks based on high-resolution collected PM2.5 samples every 1.5 hours in one week in Zhengzhou, a megacity continuously suffers from serious air contamination in central China. The composition patterns and sources of PPDs and PPDQs were discovered and more serious contamination of them were both found at the day-time (07:00-19:00). Almost all daily time intervals with relatively high pollution levels of PPDs and PPDQs were commuting time for majority of workers, which was possibly because of increased rubber tire abrasion induced by huge traffic volume. The highest daily adults' inhalation risks were also found in 11:30-13:00 and 16:00-17:30 for PPDs and PPDQs in PM2.5, respectively. Current study builds the relationship between pollution status of such novel pollutants and human activities, and possibly guides people in central China to take precautions to protect themselves from environmental toxicants at special daily time.

Tire rubber-derived contaminant 6PPD had the potential to induce metabolism disorder in early developmental stage of zebrafish

The increasing release of tire-derived particles, particularly those containing N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), into the environment has raised concerns regarding their ecological impact. This study aims to elucidate the toxicological effects of 6PPD on the metabolism in early developmental stage of zebrafish. Larval zebrafish were exposed to 10 and 100 μg/L 6PPD, and some endpoints in biochemical parameters, gene expression, and metabolism were analyzed. The results showed that 6PPD exposure disrupted glucolipid metabolism in zebrafish larvae, evidenced by increased triglyceride (TG) levels and decreased glucose content. Nile red staining indicated significant lipid accumulation in the liver and intestines. Additionally, RT-qPCR analysis revealed the upregulation of genes involved in lipid synthesis and metabolism, such as ppar-γ and fas, and downregulation of glycolysis-related genes like pk and gk. Furthermore, the untargeted metabolomics technique was used to identify a total of 220 differentially expressed metabolites (DEMs) with changes in amino acid metabolism, lipid metabolism, and the TCA cycle. KEGG pathway enrichment analysis highlighted disruptions mainly in Taurine and hypotaurine metabolism, Arginine and proline metabolism, and Histidine metabolism, which played very important roles on energy metabolism in zebrafish. The results provided some critical insights into the ecological risks associated with 6PPD.

Environmental occurrence, fate, human exposure, and human health risks of p-phenylenediamines and their quinones

P-phenylenediamine antioxidants (PPDs) are widely used in the rubber industry and their release and transformation in the environment has become one of the current environmental research hotspots. PPDs are readily oxidized in the environment to form quinone transformation products (PPD-Qs), some of which (e.g. 6PPD-Q) have been shown to be highly toxic and persistent in the environment, posing a potential threat to aquatic organisms and ecosystems. The present study provides an overview of the physicochemical properties, environmental distribution, and potential human exposure and toxicological effects of PPDs and PPD-Qs. PPDs and PPD-Qs are found in water, air, dust and soil around the world, and humans are inevitably exposed to them by inhaling, ingesting and through dermal contact. There is growing evidence indicates that PPDs and PPD-Qs are present in human body fluids and tissues, where they are subject to metabolic and transformational processes in the liver and blood. Furthermore, PPDs and PPD-Qs have the potential to induce adverse health effects, including digestive, respiratory, neurotoxic and reproductive toxicity. Nevertheless, there is a paucity of evidence concerning the direct effects of PPDs and PPD-Qs on human health. Consequently, future research should concentrate on this area in order to provide quantitative support for the assessment of the risk posed by PPDs and PPD-Qs to human health.

Transgenerational intestinal toxicity of 6-PPD quinone in causing ROS production, enhancement in intestinal permeability and suppression in innate immunity in C. elegans

Toxicity of 6-PPD quinone (6-PPDQ) on organisms at various aspects has been frequently observed at parental generation (P0-G). In contrast, we know little about its possible transgenerational toxicity and underlying mechanisms. In Caenorhabditis elegans, exposure to 6-PPDQ (0.1-10 μg/L) at P0-G induced transgenerational reactive oxygen species (ROS) production in intestine. Accompanied with this, transgenerational increase in intestinal permeability and decrease in expressions of genes governing intestinal function were observed. Exposure to 6-PPDQ (1 and 10 μg/L) at P0-G caused transgenerational suppression in expressions of antimicrobial genes (lys-7 and spp-1) and LYS-7::RFP. Meanwhile, intestinal ROS production could be enhanced by RNAi of acs-22, hmp-2, pkc-3, lys-7, and spp-1. Moreover, acs-22, hmp-2, and pkc-3 RNAi could inhibit innate immune response induced by 6-PPDQ. Additionally, lys-7 and spp-1 RNAi could strengthen intestinal permeability in 6-PPDQ exposed nematodes. Therefore, 6-PPDQ caused transgenerational intestinal toxicity, which was associated with both enhanced intestinal permeability and suppressed innate immunity.

Untargeted metabolomic analysis reveals a time-course hepatic metabolism disorder induced by short-term 6PPD exposure in rats

The tire antioxidant 6PPD has garnered extensive attention due to its widespread presence in the environment and the harmful effects of its transformation products on aquatic organisms. 6PPD has been detected in airborne dust, and it can enter mammals through inhalation exposure. While the toxic effects of 6PPD exposure have been reported in mammals, its effects on hepatic metabolism still remain poorly understood. Here, we collected the serum and liver samples at 1, 6, and 72 h following a single oral exposure of 100 mg/kg body weight (bw) 6PPD, respectively. We also investigated changes in serum and hepatic physiological indicators and metabolites, correspondingly. Results indicated that single time oral exposure a high dose of 6PPD did not significantly affect the physiological indexes of rats within a short time frame. However, untargeted metabolomics analysis of the metabolites in the liver at 1, 6, and 72 h revealed that the number of differential expression metabolites gradually increased over time and the most affected substances were lipids and lipid-like molecules. Interestingly, the KEGG pathway enrichment analysis indicated that 6PPD disrupted the riboflavin metabolism, leading to a significant decrease in FMN levels at all time points. In addition, the hepatic glucose metabolism was significantly affected at 6 and 72 h after oral administration. Taken together, short-term exposure to 6PPD disturbed lipid and riboflavin metabolism and gradually affected glucose metabolism in the liver of rats. These findings revealed the impacts of 6PPD on the hepatic metabolism in animals, and also offered some important insights into its toxicology and health risk.

Occurrence, sources, and human exposure assessment of amine-based rubber additives in dust from various micro-environments in South China

Despite the ubiquitous use and potential health effects of amine-based rubber additives, information regarding their occurrences in indoor environments remains scarce and is basically investigated in traffic-related environments. In this study, a total of 140 dust samples collected from eight indoor micro-environments were analyzed for twelve amine-based rubber additives. Overall, 1,3-diphenylguanidine (DPG), dicyclohexylamine (DCHA), N-(1,3-dimethylbutyl)-N'-phenyl-p-penylenediamine (6PPD), 6PPD-quinone (6PPDQ), and hexa(methoxymethyl)melamine (HMMM) were frequently detected across all micro-environments with detection frequencies of 97 %, 51 %, 71 %, 99 %, and 77 %, respectively. The highest total concentration of amine-based rubber additives was found in parking lots (median 10,300 ng/g), indicating heavier emission sources of these compounds in vehicle-related indoor environments. Despite this, amine-based rubber additives were also frequently detected in various non-vehicle-related environments, such as markets, cinemas, and hotels, probably due to the widespread use of consumer products and more frequent air exchanges with outdoor environments. Further tracking of tire rubber products and paint particles from flooring materials in parking lots revealed that paint particles might be an overlooked contributor to amine-based rubber additives in indoor environments. Finally, the highest estimated daily intakes (EDIs) of all amine-based rubber additives via dust ingestion at home were observed for toddlers (3.48 ng/kg bw/d). This research provides a comprehensive overview of human exposure to a variety of amine-based rubber additives in various indoor environments. ENVIRONMENTAL IMPLICATION: This study highlights the presence of high concentrations of amine-based additives in indoor dust from both traffic-related and non-traffic-related indoor environments. Additional efforts are needed to identify potential sources of amine-based rubber additives indoors, beyond just tire rubber. This is critical because the widespread presence of rubber products in indoor settings could pose a risk to human health.

Phytotoxicity of 6PPD and its uptake by Myriophyllum verticillatum: Oxidative stress and metabolic processes

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), a widely utilized antioxidant in automobile tires and rubber goods, is frequently detected in aquatic ecosystems and poses a potential threat to aquatic organisms. However, research on the impact of 6PPD on aquatic plants is still scarce. Here, we investigated the bioaccumulation of 6PPD in Myriophyllum verticillatum (M. verticillatum) (watermilfoil), and its impacts on biochemical characteristics and metabolomics. 6PPD (10,100 mg/L) significantly inhibited the growth and photosynthetic pigment content of M. verticillatum. After 14 days of exposure to 100 μg/L 6PPD, accumulation levels of 6PPD and its metabolite 6PPDQ in M. verticillatum reached 0.52 mg/kg and 0.09 mg/kg, respectively. Moreover, 6PPD significantly induced the activities of superoxide dismutase (SOD), peroxidase (POD), catalase (CAT) enzymes and glutathione (GSH), reducing the levels of reactive oxygen species (ROS) and malondialdehyde (MDA), thereby mitigating oxidative damage in M. verticillatum. Furthermore, metabolic pathway analysis revealed that 6PPD has remarkable effects on amino acid and sugar metabolism. This study provides data support for understanding the toxic effects of 6PPD on aquatic plants and evaluating its potential risks.

p-phenylenediamines (PPDs) and PPD-quinones (PPD-Qs) in human urine and breast milk samples: Urgent need for focus on PPD-Qs and the establishment of health threshold criteria

PPDs and their oxidation products, PPD-Qs, are emerging environmental contaminants arising from the addition and oxidation of rubber products. Although numerous studies have been conducted to elucidate their risks, the primary focus has been on 6PPD and 6PPD-Q, with limited attention given to other PPDs and especially other PPD-Qs. This study comprehensively examines the occurrences of frequently used PPDs and their degradation products, PPD-Qs, in human urine and breast milk samples. The average concentrations of ΣPPDs and ΣPPD-Qs in urine were 27 ± 78 ng/mL and 16 ± 12 ng/mL, respectively. IPPD and DNPD were the predominant PPDs, while DPPD-Q, CPPD-Q, and IPPD-Q were the predominant PPD-Qs. Notably, the concentrations of 6PPD, CPPD, and DPPD were significantly lower than their oxidized quinone products. Weak or no correlations were observed between most PPDs and their corresponding PPD-Qs, suggesting that PPD-Qs in the human body are primarily derived from direct environmental intake rather than in vivo conversion of PPDs. PPDs and PPD-Qs were widely detected in breast milk, exhibiting concentrations and patterns similar to those found in urine, with comparable major pollutants. Estimated daily intakes of PPDs + PPD-Qs for infants were several μg/(kg·day), with the 95th percentile intake approaching 10 μg/(kg·day).

Accurate and stable detection of p-phenylenediamine antioxidants and their transformation products in aquatic products using antioxidant protection - Analysis of actual aquatic products

Given the high toxicity of N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) derivatives, such as 6PPD quinone (6PPDQ) to salmon, as well as their ubiquitous presence in the environment, the contaminant of aquatic food products has drawn significant attention. However, analytical methods for p-Phenylenediamines (PPDs) and their transformation products (TPs) in aquatic products remain underdeveloped. In particular, the degradation of some compounds and strong matrix effects complicate detection. In this study, we present a stable, rapid, and sensitive method combining salt-out assisted extraction, antioxidant protection, and multi-plug filtration clean-up (m-PFC) to detect two PPDs and five TPs in aquatic products. Crucially, the appropriate selection of antioxidants prevented the degradation of the easily oxidized target compounds. Further, the m-PFC method significantly enhanced the purification efficiency, achieving satisfactory recoveries (62.1-115 %), and method detection limits (MDLs) ranging from 0.00300 to 0.400 μg/kg. Subsequently, the method was applied to monitor PPDs and their TPs in aquatic products systematically, revealing the presence of 6PPD and N-isopropyl-N'-phenyl-1,4-phenylenediamine (IPPD) in white shrimp from aquafarms, whereas none of the seven target analytes were detected in fish and crab samples. These findings contribute to the detection of PPDs, their TPs and other unstable chemicals in aquatic products, thereby providing insights into their concentrations in these products.

Environmental concentrations of 6PPD and 6PPD-quinone induce hepatic lipid metabolism disorders in male black-spotted frogs

Aquatic environments are generally contaminated with N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD) and its oxidation product 6PPD-quinone (6PPD-Q). Recently, 6PPD-Q was found lethally toxic to some specific species, especially salmonid silverfish. This study investigated male black-spotted frogs (Pelophylax nigromaculatus) exposed to 6PPD and 6PPD-Q with different environmental concentrations (0, 1, and 10 μg/L) for 21 days, after which biochemical, metabolomic, gene expression analyses, and molecular docking were conducted. 6PPD and 6PPD-Q were both found to bioaccumulate in frogs' livers in a dose-dependent manner and produce a significant reduction of the hepatosomatic index. Metabolomics data showed that 6PPD and 6PPD-Q induced distinct alterations in metabolite expression, predominantly within pathways associated with the biosynthesis of unsaturated fatty acids as well as the metabolism of arachidonic and linoleic acids. Exposure to 10 μg/L 6PPD and 6PPD-Q increased the cholesterol level by 2.22 and 4.35 folds, and the triglyceride level by 1.90 and 2.25 folds, respectively. 6PPD-Q inhibited the enzyme activity and gene expression involved in lipolysis, and promoted the lipid synthesis. Moreover, 6PPD and 6PPD-Q bound to peroxisome proliferators-activated receptors of α and γ. In conclusion, 6PPD and 6PPD-Q with environmental concentrations induced frogs' lipid metabolism disorders. These findings contribute to our understanding of 6PPD and 6PPD-Q health risks in amphibians.

Stress of soil moisture and temperature exacerbates the toxicity of tire wear particles to soil fauna: Tracking the role of additives through host microbiota

Tire wear particles (TWPs) are considered as an emerging threat to soil fauna. However, how TWP toxicity to soil fauna responds to the stress of soil moisture and temperature remains unclear. We assessed the toxicity of environmentally relevant TWPs to the soil model species Enchytraeus crypticus under three soil moisture and two temperature gradients. Typical thermoplastic polypropylene (PP) was selected for comparison. Results showed that compared with PP, TWPs exerted stronger toxicity, including decreasing the worm growth, survival and reproduction rates, disturbing the soil and worm gut microbiota, and leaching more diverse and higher contents of additives. Stress of soil moisture and temperature exacerbated TWP toxicity mainly through affecting the leaching and transformation of additives. Fourteen mediated additives significantly contributed to the shift of the gut microbiota under soil moisture and temperature stress, among which 1,3-diphenylguanidine, N,N'-bis(methylphenyl)-1,4-benzenediamine quinone, N-tert-butyl-2-benzothiazolesulfenamide, and 2-aminobenzothiazole were identified as the main drivers. In addition, this study provided the first clear evidence that increased soil moisture and temperature promoted the transformation of additives in the soil. Our study revealed the non-negligible aggravated toxicity of TWPs to soil fauna under stress of soil moisture and temperature, providing novel insights into the environmental behavior of additives.

Fractional extraction phenolics from C. oleifera seed kernels exhibited anti-inflammatory effect via PI3K/Akt/NF-κB signaling pathway under Caco-2/RAW264.7 co-culture cell model

Camellia oleifera Abel (C. oleifera) is a multifunctional oilseed, which is rich in many biological active substances with health-promoting properties, especially polyphenols. Previous research revealed that camellia oil phenolics exhibited anti-inflammatory effect, which originated from seed. Thus, we aimed to explore the components of camellia seed phenolics and its potential mechanism of anti-inflammation. Initially, fractional extraction was processed to prepare the phenolics from camellia seed kernels, and we compare four different fractions of phenolics under the LPS-induced Caco-2/RAW264.7 coculturing model. Results showed that free phenolics (FP) had best effect on alleviating pro-inflammatory cytokines (IL-1β, IL-6, IL-8 and TNF-α) compared to esterified-bound phenolics (EP), glycosylated-bound phenolics (GP) and insoluble-bound phenolics (IP). Furthermore, FP reduced inflammation by suppressing the PI3K/Akt/NF-κB signaling pathway and effectively inhibited LPS-induced intestinal permeability increase, tight junction related proteins loss (ZO-1, claudin-1). Same results obtained, as the transepithelial electrical resistance (TEER) and alkaline phosphatase (AKP) activity of high-dose FP treated group was high than model group. Finally, molecular docking was used for evaluating the anti-inflammatory effect for phenolic monomer. KGRG (kaempferol -3-O-(2-O-glucopyranosyl-6-O-rhamnopyranosyl)-glucopyranoside), KXR (kaempferol 3-O-(2''-xylopyranosyl)-rutinoside) and leucoside (kaempferol 3-O-sambubioside) show lower binding energy docking with NF-κB, PI3K and Akt protein, indicating better interactions, which might be effective constituents against inflammation. Subsequently, five major polyphenols were obtained to validate the docking results, especially, indicating the best anti-inflammatory activities of KGRG. Overall, this research sheds insights on the therapy of phenolics from C. oleifera seed towards LPS-induced intestinal inflammation model in vitro and its related mechanism.

Comparative toxic effect of tire wear particle-derived compounds 6PPD and 6PPD-quinone to Chlorella vulgaris

N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), a widely used antioxidant in rubber products, and its corresponding ozone photolysis product N-(1,3-Dimethylbutyl)-N'-phenyl-p-phenylenediamine-quinone (6PPD-Q), have raised public concerns due to their environmental toxicity. However, there is an existing knowledge gap on the toxicity of 6PPD and 6PPD-Q to aquatic plants. A model aquatic plant, Chlorella vulgaris (C. vulgaris), was subjected to 6PPD and 6PPD-Q at concentrations of 50, 100, 200, and 400 μg/L to investigate their effects on plant growth, photosynthetic, antioxidant system, and metabolic behavior. The results showed that 6PPD-Q enhanced the photosynthetic efficiency of C. vulgaris, promoting growth of C. vulgaris at low concentrations (50, 100, and 200 μg/L) while inhibiting growth at high concentration (400 μg/L). 6PPD-Q induced more oxidative stress than 6PPD, disrupting cell permeability and mitochondrial membrane potential stability. C. vulgaris responded to contaminant-induced oxidative stress by altering antioxidant enzyme activities and active substance levels. Metabolomics further identified fatty acids as the most significantly altered metabolites following exposure to both contaminants. In conclusion, this study compares the toxicity of 6PPD and 6PPD-Q to C. vulgaris, with 6PPD-Q demonstrating higher toxicity. This study provides valuable insight into the risk assessment of tire wear particles (TWPs) derived chemicals in aquatic habitats and plants.

Paeoniflorin alleviates toxicity and accumulation of 6-PPD quinone by activating ACS-22 in Caenorhabditis elegans

6-PPD quinone (6-PPDQ) is extensively existed in various environments. In Caenorhabditis elegans, exposure to 6-PPDQ could cause multiple toxic effects. In the current study, we further used C. elegans to investigate the effect of paeoniflorin (PF) treatment on 6-PPDQ toxicity and accumulation and the underlying mechanism. Treatment with PF (25-100 mg/L) inhibited 6-PPDQ toxicity on reproduction capacity and locomotion behavior and in inducing reactive oxygen species (ROS) production. Additionally, PF (25-100 mg/L) alleviated the dysregulation in expression of genes governing oxidative stress caused by 6-PPDQ exposure. Moreover, PF (25-100 mg/L) inhibited the enhancement in intestinal permeability caused by 6-PPDQ exposure and the accumulation of 6-PPDQ in the body of nematodes. In 6-PPDQ exposed nematodes, PF (25-100 mg/L) increased expression of acs-22 encoding a fatty acid transporter. RNAi of acs-22 could inhibit the beneficial effect of PF against 6-PPDQ toxicity in decreasing reproductive capacity and locomotion behavior, in inducing intestinal ROS production, and in enhancing intestinal permeability. RNAi of acs-22 could also suppress the PF beneficial effect against 6-PPDQ accumulation in the body of nematodes. Therefore, our results demonstrate the function of PF treatment against 6-PPDQ toxicity and accumulation in nematodes by activating the ACS-22.

Potential human health risk of the emerging environmental contaminant 6-PPD quinone

The tire antioxidant 6-PPD has been widely used to enhance tire performance and extend tire lifespan. 6-PPD quinone (6-PPDQ), a quinone derivative derived from 6-PPD in the presence of ozone, has been recognized an emerging environmental contaminant. In addition to causing acute lethality to coho salmon, 6-PPDQ exhibits toxic effects on other aquatic species and mammals. Based on the existing evidence, we provide a critical overview on the human internal exposure, potential adverse effects on health, and prediction of human health risk of 6-PPDQ. 6-PPDQ could be detected in human samples, including human urine, blood, and cerebrospinal fluid. Human exposure to 6-PPDQ in the environment is inevitable and may lead to adverse health effects, including hepatotoxicity, enterotoxicity, pulmonary toxicity, neurotoxicity, reproductive toxicity, and cardiotoxicity. Additionally, potential human health risk to 6-PPDQ through exposure routes and human samples were predicted. This review is helpful to identify the existing knowledge gaps and future research directions regarding the human health effects of 6-PPDQ.

Transgenerational response of glucose metabolism in Caenorhabditis elegans exposed to 6-PPD quinone

In Caenorhabditis elegans, 6-PPD quinine (6-PPDQ) could cause several aspects of toxicity together with alteration in glucose metabolism. However, transgenerational alteration in glucose metabolism remains still unknown after 6-PPDQ exposure. In the current study, we further observed transgenerational increase in glucose content induced by 6-PPDQ (1-10 μg/L). After 1-10 μg/L 6-PPDQ exposure, although expressions of genes controlling gluconeogenesis were not changed in the offspring, expressions of hxk-1, hxk-3, pyk-1, and pyk-2 controlling glycolysis could be decreased in the offspring. Meanwhile, transgenerational decrease in expressions of daf-16 encoding FOXO transcriptional factor and aak-2 encoding AMPK was detected in the offspring of 6-PPDQ (1-10 μg/L) exposed nematodes. RNAi of daf-16 and aak-2 led to more severe transgenerational increase in glucose content and reduction in expressions of hxk-1 and hxk-3 induced by 6-PPDQ. Moreover, RNAi of daf-16, aak-2, hxk-1, hxk-3, pyk-1, and pyk-2 caused susceptibility to transgenerational 6-PPDQ toxicity on locomotion and reproduction. Additionally, 6-PPDQ induced activation of SOD-3 and HSP-6 reflecting anti-oxidation and mitochondrial UPR responses could be inhibited by RNAi of daf-16, aak-2, hxk-1, hxk-3, pyk-1, and pyk-2. Therefore, exposure to 6-PPDQ potentially resulted in transgenerational alteration in glucose metabolism, which provided the possible link to induction of transgenerational 6-PPDQ toxicity in organisms.

P-phenylenediamine antioxidants and their quinone derivatives: A review of their environmental occurrence, accessibility, potential toxicity, and human exposure

Substituted p-phenylenediamines (PPDs), a class of antioxidants, have been widely used to extend the lifespan of rubber products, such as tires and pipes. During use, PPDs will generate their quinone derivatives (PPD-Qs). In recent years, PPDs and PPD-Qs have been detected in the global environment. Among them, N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine quinone (6PPD-Q), the oxidation product of N-(1,3-dimethylbutyl)-N'-phenyl-p-phenylenediamine (6PPD), has been identified as highly toxic to coho salmon, with the lethal concentration of 50 % (LC50) being 95 ng/L, highlighting it as an emerging pollutant of great concern. This review summarizes the physicochemical properties, global environmental distribution, bioaccessibility, potential toxicity, human exposure risk, and green measures of PPDs and PPD-Qs. These chemicals exhibit lipophilicity, bioaccumulation potential, and poor aqueous stability. They have been found in water, air, dust, soil, and sediment worldwide, indicating their significance as emerging pollutants. Notably, current studies have identified electronic waste (e-waste), such as discarded wires and cables, as a non-negligible source of PPDs and PPD-Qs, in addition to tire wear. PPDs and PPD-Qs exhibit strong bioaccumulation in aquatic organisms and mammals, with a tendency for biomagnification within the food web, posing health threats to humans. Available toxicity data indicate that PPDs and PPD-Qs have negative effects on aquatic organisms, mammals, and invertebrates. Acute exposure leads to death and acute damage, and long-term exposure can cause a series of adverse effects, including growth and development toxicity, reproductive toxicity, neurotoxicity, intestinal toxicity, and multi-organ damage. This paper discusses current research gaps and offers recommendations to understand better the occurrence, behavior, toxicity, and environmental exposure risks of PPDs and PPD-Qs.