Abstract
The impact of reductive pulmonary inhalants on ultrafine particles (UFPs)-induced pulmonary oxidative stress remains a crucial consideration, yet the concentration-dependent effects of these inhalants have remained unexplored. Here we synthesized composite UFPs simulating atmospheric UFPs, primarily composed of metals and quinones. We subjected these UFPs to varying concentrations (0–7000 μM) of two reductive pulmonary inhalants, N-acetylcysteine and salbutamol, to assess their influence on oxidative potential, measured through the dithiothreitol assay (OPDTT). Simultaneously, we analysed the soluble metal content of UFPs to uncover potential relationships between oxidative potential and metal solubility. Our results unveil a dual role played by these inhalants in shaping the OPDTT of composite UFPs. Specifically, OPDTT generally increased as inhalant concentrations rose from 0 to 300 μM. However, an intriguing reversal occurred when concentrations exceeded 500 μM, resulting in a decline in OPDTT. Relative to untreated UFPs, these inhalants induced promotion and inhibition effects within concentration ranges of 100–500 and >1000 μM, respectively. While no significant correlation emerged between OPDTT and soluble metal content as inhalant concentrations ranged from 0 to 7000 μM, noteworthy positive correlations emerged at lower inhalant concentrations (e.g., N-acetylcysteine at 0–300 μM). These findings provide insights into the potential influence of reductive pulmonary inhalants on health risks associated with UFP exposure, further underscoring the need for continued research in this critical area.
Keywords: Concentration-dependent effects, Oxidative potential, Reductive pulmonary inhalants, Soluble metals, Simulated atmospheric ultrafine particles
Graphical abstract
Highlights
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Reductive inhalants dual-affect ultrafine particle (UFP)-induced oxidative stress.
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Reductive inhalants at lower levels promote UFP-induced oxidative stress.
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Reductive inhalants at higher levels inhibit UFP-induced oxidative stress.
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UFP oxidative will mutually affects metal dissolution at certain inhalant levels.
1. Introduction
Exposure to particulate matter (PM) correlates with millions of annual premature deaths globally [1]. Ultrafine particles (UFPs) are an important PM fraction, defined by their smaller diameter (≤100 nm) but larger specific surface area than PM2.5 or PM10 [2]. Anthropogenic UFPs in the environment are typically generated as by-products of fossil fuel combustion, the condensation of semi-volatile substances, and industrial emissions [3]. The negligible mass but substantial contribution of UFPs to the total number of atmospheric particles has been the focus of interest in recent years [4], given the threat of UFPs to human health. Moreover, UFPs can readily absorb toxic pollutants and deeply penetrate the lungs, resulting in prolonged retention and chronic lung damage [3,5,6].
Oxidative stress is an important mechanism of UFP-induced lung disease [3]. The chemical composition of PM has been shown to influence reactive oxygen species (ROS) generation in vitro and in vivo [[7], [8], [9]]. Once the PM is deposited in the lungs, redox-active PM components may interact with each other or the physiological components in lung fluid to generate ROS [10]. Redox-active PM components [11,12], such as polycyclic aromatic hydrocarbons (PAHs), PAH derivatives (e.g., quinones), and metals, have also been observed in UFPs and may contribute to the toxic effects of oxidative stress in lungs.
Antioxidant therapy to counteract oxidative stress has been investigated in the context of nutrition and epidemiology [13]. In treating respiratory disease, reductive pulmonary inhalants in lung fluid may act as antioxidants and reduce the pulmonary oxidative stress induced by PM [[14], [15], [16]]. In both in-vitro cellular and in-vivo murine models, Wang et al. [15] found that N-acetylcysteine (NAC), a commonly used inhalant, reduced ROS levels and the PM-induced inflammatory response. Lin et al. [16] conducted a murine model experiment in which NAC was similarly shown to decrease PM-mediated oxidative stress. However, there was no consistent conclusion regarding the effects of the reductive substances in lung fluid on PM-induced oxidative stress. Studies based on in-vitro acellular assays showed increased ROS generation mediated by redox-active PM components with the reductant (e.g., vitamin C) depleting in lung fluid [17,18]. The enhancement of oxidative stress by some antioxidants was reported by Childs et al. [19], who found that supplements of vitamin C (12.5 mg kg−1) and NAC (10 mg kg−1) resulted in a significant increase in the oxidative stress of healthy individuals after acute exercise. Another study suggested that the antioxidant concentration is an important determinant of antioxidant or pro-oxidant effects [20], as it influences the redox potential of the systems involved in ROS generation [[21], [22], [23]]. Accordingly, the concentration of reductive pulmonary inhalants in lung fluid may determine the level of lung oxidative stress induced by UFPs. However, this hypothesis has not been tested, although it has important implications regarding knowing pulmonary inhalants affect UFP-induced oxidative stress in the lung.
Both quinones and metals contribute to the toxicity of anthropogenic UFPs [24]. UFPs generated by coal combustion can become enriched in metals such as Na, Fe, and Al [25], which, together with carbonaceous materials, increase their toxicity and reactivity. Hence, in the present study, composite UFPs, mainly consisting of metals and quinones as prepared in our recent work [26], were used to investigate the concentration-dependent effects of reductive pulmonary inhalants on UFP-induced oxidative stress in the lung. In-vitro acellular dithiothreitol (DTT) assays were conducted to measure the change in the oxidative potential (OP) of UFPs in response to changes in the concentrations of the reductive pulmonary inhalants. The correlation between the OP and the corresponding soluble metal concentration at the studied inhalant concentration range was then determined. Our findings provide further insights into UFP-induced pulmonary toxicity and the therapeutic safety of reductive pulmonary inhalants.
2. Materials and methods
2.1. Composite UFP preparation
Composite UFP samples were selected from the artificial UFPs prepared in our recent work [26] and shown to have a relatively high susceptibility to the effects of reducing agents in lung fluid. Briefly, the UFP samples were prepared by absorbing 1,4-naphthoquinone (NQ) or anthraquinone (AQ) on commercial nanoparticles of CuO, Fe2O3, and MnO2 (nCuO, nFe2O3, and nMnO2, respectively). The characteristics of the nCuO, nFe2O3, and nMnO2 are listed in Table 1. The infrared absorption spectra of the composite UFP samples resembled those of NQ and AQ, indicating the successful absorption of these compounds onto nCuO, nFe2O3, and nMnO2 (Fig. 1). The composite UFP samples consisting of nCuO, nFe2O3, and nMnO2 with NQ and AQ are referred to in the following sections as UFPCu/NQ, UFPFe/NQ, UFPMn/NQ, UFPCu/AQ, UFPFe/AQ, and UFPMn/AQ, respectively.
Table 1.
Physiochemical properties of the nanoparticles of CuO, Fe2O3, and MnO2.
| No. | Particles | Componentsa | Average particle size (nm)b | Specific surface area (m2 g−1)c |
|---|---|---|---|---|
| 1 | nCuO | 100% CuO | 20.0 | 1.55 |
| 2 | nFe2O3 | 100% Fe2O3 | 60.6 | 5.75 |
| 3 | nMnO2 | Mainly MnO2, subordinately quartz and birnessite, rarely goethite | 30.5 | 15.7 |
Components are analysed by X-ray diffraction.
Average particle size is calculated by the Scherrer equation based on X-ray diffraction analysis.
Specific surface area is analysed according to the BET method.
Fig. 1.
Fourier Transform Infrared (FTIR) spectra of composite ultrafine particles (UFPs) of nCuO, nFe2O3, and nMnO2 with NQ (a) or AQ (b). In panel a, composite UFPs of nCuO, nFe2O3, and nMnO2 with NQ were represented as UFPCu/NQ, UFPFe/NQ, and UFPMn/NQ, respectively. In panel b, composite UFPs of nCuO, nFe2O3, and nMnO2 with AQ were represented as UFPCu/AQ, UFPFe/AQ, and UFPMn/AQ, respectively.
2.2. Physiological buffer and reductive pulmonary inhalants
Phosphate-buffered saline (PBS) ( ×1; pH 7.4) was used as the physiological buffer. The studied reductive pulmonary inhalants were NAC and salbutamol (ALB), both employed in clinical settings. NAC and ALB were diluted with PBS to obtain final concentrations of 0, 100, 200, 300, 500, 1000, 2000, 3000, 5000, and 7000 μM to test their effects on the OP of UFPs in lung fluid.
2.3. UFP extraction
For each treatment, 20 mg of a UFP sample was resuspended in 20 mL of PBS containing different concentrations (0–7000 μM) of reductive pulmonary inhalant (ALB or NAC) and incubated for 4 h in a thermostatic box at 37 °C on a reciprocating shaker (SHA-B; Saidelisi, Shanghai, China). The suspensions were then filtered through a 0.22-μm cellulose microporous membrane; the filtrates were used for DTT assay and dissolved metal analysis. Each treatment was tested in triplicate.
2.4. Chemical analysis
2.4.1. DTT assay
In this study, the OP of UFPs was measured using the DTT assay, a widely used acellular method sensitive to metals and quinones [27]. The analytical procedures were modified from previous studies [27,28]. Briefly, 50–100 μL of the filtrate was incubated at 37 °C with 1.0 mL of 0.1 M potassium phosphate and 100 μL of 0.5 mM DTT for 0, 5, 10, 15, or 20 min, after which 100 μL of 1.0 mM 5,5′-dithiobis-(2-nitrobenzoic acid) was added. The yellow reaction products were detected using an ultramicro ultraviolet–visible (UV–vis) spectrophotometer (NanoDrop One; Thermo Fisher Scientific, Waltham, MA, USA) at 412 nm. The OP of each UFP sample was expressed as the DTT consumption rate (OPDTT), determined from the linear regression slope of the data points, and normalized to the mass of the UFPs. The R2 values derived from linear regression analysis were all >0.9. Blank controls were included with each batch.
2.4.2. Metal analysis
Metals dissolved from UFPs into extracts were determined using inductively coupled plasma-mass spectrometry (Agilent 780; Agilent Technologies, Santa Clara, CA, USA). The detection limit was 0.02–0.22 μg L−1, and the recovery rate was 85–105%.
2.5. Statistical analysis
The data are presented as the mean ± standard deviation. A two-way analysis of variance and Tukey's multiple comparison tests were performed using GraphPad Prism 8.0 software (GraphPad Software Inc., San Diego, CA, USA). Statistical differences were defined at p < 0.05, p < 0.01, and p < 0.001. Associations among quantitative variables were assessed based on Pearson's product moment correlation coefficient (r), calculated using Microsoft Office Excel 2016 (Microsoft Corp., Redmond, WA, USA). Illustrations were drawn using GraphPad Prism 8.0 and Adobe Illustrator CC 2015.3 (Adobe Systems Inc., San Jose, CA, USA).
3. Results
3.1. OPDTT of composite UFPs of nCuO with quinones (UFPCu)
In general, the OPDTT of UFPCu increased, either significantly or non-significantly, at lower concentrations and decreased at higher concentrations (>500 μM) of reductive pulmonary inhalants (Fig. 2). For example, the OPDTT of UFPCu/NQ increased significantly at ALB concentrations of 200–300 μM (p < 0.01), whereas a non-significant increase was measured at NAC concentrations of 0–500 μM (p > 0.05) (Fig. 2a); the increase in OPDTT of UFPCu/AQ was not significant at NAC and ALB concentrations of 0–200 μM (p > 0.05) (Fig. 2b).
Fig. 2.
OPDTT of the UFPCu/NQ (a) and UFPCu/AQ (b) in physiological buffer with different concentrations of reductive pulmonary inhalants. OPDTT: oxidative potential analysed by the dithiothreitol assay; UFPCu/NQ and UFPCu/AQ: the composite UFPs of nCuO with 1,4-NQ and AQ, respectively; NAC: N-acetylcysteine; ALB: salbutamol.
Compared with treatments consisting of UFPCu/NQ without added reductive pulmonary inhalants, the OPDTT was significantly higher in treatments containing 300 or 500 μM ALB (p < 0.001) (Fig. 2a). For UFPCu/AQ, the OPDTT increased following the addition of NAC or ALB at a concentration of 100 μM (p < 0.05) and 200 μM (p < 0.001) (Fig. 2b). By contrast, reductive pulmonary inhalant concentrations >1000 μM caused a decrease in the OPDTT of UFPCu.
3.2. OPDTT of composite UFPs of nFe2O3 with quinones (UFPFe)
When the concentration of NAC and ALB was raised from 200 to 300 μM, the OPDTT of UFPFe/NQ increased significantly, from 3.39 ± 0.47 to 6.17 ± 0.66 pmol min−1 μg−1 (p < 0.001) and from 4.71 ± 0.37 to 6.44 ± 0.63 pmol min−1 μg−1 (p < 0.01), respectively (Fig. 3a). By contrast, the OPDTT decreased significantly at NAC and ALB concentrations >300 μM (p < 0.05) and 500 μM (p < 0.001), respectively. For UFPFe/AQ, the increase in the OPDTT was not significant (p > 0.05) at NAC and ALB concentrations of 100–500 μM and 300–500 μM, respectively (Fig. 3b). However, the OPDTT decreased significantly when the reductive pulmonary inhalant concentration was >500 μM (p < 0.01).
Fig. 3.
OPDTT of the UFPFe/NQ (a) and UFPFe/AQ (b) in physiological buffer with different concentrations of reductive pulmonary inhalants. OPDTT: oxidative potential analysed by the dithiothreitol assay; UFPFe/NQ and UFPFe/AQ: the composite UFPs of nFe2O3 with 1,4-NQ and AQ, respectively; NAC: N-acetylcysteine; ALB: salbutamol.
Compared with untreated UFPFe/NQ, the OPDTT was enhanced when the particles were incubated with NAC or ALB at concentrations of 300–500 μM but reduced at concentrations >1000 μM (Fig. 3a). For UFPFe/AQ, the addition of 0–7000 μM of either NAC or ALB inhibited their OPDTT (Fig. 3b).
3.3. OPDTT of composite UFPs of nMnO2 with quinones (UFPMn)
The OPDTT of UFPMn/NQ and UFPMn/AQ increased significantly when the NAC and ALB concentration increased from 0 to 100 μM (p > 0.05) (Fig. 4), whereas the OPDTT of UFPMn/NQ decreased significantly at NAC and ALB concentrations >500 μM and >200 μM, respectively (p < 0.001) (Fig. 4a). The OPDTT of UFPMn/AQ also decreased significantly (p < 0.05) at NAC and ALB concentrations of <300 μM and <200 μM, respectively (Fig. 4b).
Fig. 4.
OPDTT of the UFPMn/NQ (a) and UFPMn/AQ (b) in physiological buffer with different concentrations of reductive pulmonary inhalants. OPDTT: oxidative potential analysed by the dithiothreitol assay; UFPMn/NQ and UFPMn/AQ: the composite UFPs of nMnO2 with 1,4-NQ and AQ, respectively; NAC: N-acetylcysteine; ALB: salbutamol.
For both UFPMn/NQ and UFPMn/AQ, compared with the untreated controls, the OPDTT increased in response to NAC concentrations <2000 μM and decreased at NAC concentrations >2000 μM (Fig. 4). Similarly, the OPDTT of UFPMn/NQ and UFPMn/AQ increased in response to ALB at concentrations <500 μM (Fig. 4a) and <300 μM (Fig. 4b), respectively, but for both UFPs the OPDTT was inhibited by higher ALB concentrations.
3.4. Relationship between OPDTT and the soluble metal concentration of composite UFPs
The soluble metal concentrations of the composite UFPs at different concentrations of NAC and ALB (0–7000 μM) are reported in Table 2. Correlation analyses were performed between the OPDTT and the soluble metal concentration of each composite UFP treated with NAC or ALB in the studied concentration range (0–7000 μM) (Table 3). Overall, with the NAC or ALB varied at 0–7000 μM, there was no significant correlation between the OPDTT and the soluble metal concentration of the composite UFPs (p > 0.05). However, for some composite UFPs, a significantly positive correlation was determined between the OPDTT and the soluble metal concentration when the OPDTT increased in response to an increase in the ALB concentration. Specifically, the OPDTT of UFPCu/NQ was significantly positively correlated with the soluble Cu concentration as the ALB concentration increased from 0 to 500 μM (r = 0.8932, p < 0.05). Similarly, a correlation between the OPDTT and the soluble Mn concentration of UFPMn/NQ was positive notably as the ALB concentration varied from 0 to 300 μM (r = 0.9970, p < 0.01). However, there was no significant relationship between the OPDTT and the soluble metal concentration of any of the studied composite UFPs when the OPDTT decreased in response to further increases in the concentration of either reductive pulmonary inhalant (p > 0.05).
Table 2.
Soluble metal concentrations of UFPs at different concentrations of N-acetylcysteine (NAC) and salbutamol (ALB) (μM).a
| Reductive pulmonary inhalants | Concentration (μM) | UFPCu/NQ |
UFPCu/AQ |
UFPFe/NQ |
UFPFe/AQ |
UFPMn/NQ |
UFPMn/AQ |
||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| AVE | SD | AVE | SD | AVE | SD | AVE | SD | AVE | SD | AVE | SD | ||
| NAC | 0 | 181.19 | 3.06 | 225.25 | 6.42 | 306.07 | 4.91 | 258.57 | 18.29 | 1152.26 | 146.51 | 1313.93 | 308.78 |
| 100 | 226.20 | 33.87 | 340.23 | 46.19 | 284.47 | 22.66 | 231.37 | 17.19 | 1409.63 | 81.49 | 1376.33 | 192.47 | |
| 200 | 246.97 | 17.99 | 355.28 | 5.56 | 297.53 | 10.55 | 244.13 | 21.76 | 1586.21 | 200.75 | 1306.69 | 212.67 | |
| 300 | 252.97 | 11.84 | 312.43 | 54.51 | 354.40 | 17.60 | 243.57 | 7.80 | 1760.93 | 173.25 | 1329.57 | 98.83 | |
| 500 | 256.63 | 6.05 | 338.83 | 13.54 | 364.27 | 11.02 | 230.57 | 19.93 | 1800.87 | 96.44 | 1586.23 | 55.77 | |
| 1000 | 251.27 | 10.38 | 342.47 | 12.23 | 372.67 | 8.49 | 229.90 | 2.16 | 1806.43 | 91.42 | 1448.27 | 65.97 | |
| 2000 | 241.50 | 17.56 | 360.67 | 8.99 | 381.87 | 8.92 | 248.27 | 12.17 | 1894.90 | 34.30 | 1256.90 | 46.80 | |
| 3000 | 238.73 | 17.56 | -b | -b | 366.83 | 15.40 | -b | -b | 1693.13 | 124.14 | 1296.37 | 101.19 | |
| 5000 | -b | -b | -b | -b | 366.00 | 25.83 | -b | -b | 1738.73 | 85.06 | 1287.13 | 25.71 | |
| 7000 | -b | -b | -b | -b | 362.30 | 7.88 | -b | -b | 1741.33 | 53.17 | -b | -b | |
| ALB | 0 | 181.19 | 6.42 | 125.25 | 6.42 | 256.07 | 4.91 | 258.57 | 18.29 | 1018.92 | 47.41 | 1480.59 | 85.60 |
| 100 | 187.03 | 6.15 | 166.47 | 4.82 | 244.62 | 14.58 | 233.24 | 26.93 | 1216.51 | 136.54 | 1801.82 | 26.33 | |
| 200 | 225.92 | 9.34 | 294.63 | 7.99 | 212.09 | 17.83 | 244.08 | 37.28 | 1261.22 | 63.07 | 1772.46 | 213.25 | |
| 300 | 242.47 | 12.44 | 301.70 | 8.36 | 228.70 | 17.49 | 224.07 | 8.09 | 1360.87 | 54.11 | 1924.77 | 117.81 | |
| 500 | 264.73 | 14.03 | 299.70 | 7.23 | 231.57 | 20.13 | 236.90 | 17.27 | 1393.57 | 14.01 | 1980.90 | 42.69 | |
| 1000 | 251.10 | 8.25 | -b | -b | 205.50 | 6.90 | 218.77 | 10.97 | 1298.80 | 49.30 | 1859.07 | 53.91 | |
| 2000 | 260.67 | 4.33 | -b | -b | 207.93 | 8.20 | -b | -b | 1345.83 | 67.74 | 1894.57 | 51.32 | |
| 3000 | 253.83 | 6.79 | -b | -b | 216.73 | 6.73 | -b | -b | 1341.57 | 53.10 | 1965.63 | 58.03 | |
| 5000 | 249.00 | 4.83 | -b | -b | 207.33 | 10.27 | -b | -b | 1176.40 | 110.34 | 2006.27 | 52.70 | |
| 7000 | -b | -b | -b | -b | 178.00 | 3.83 | -b | -b | 1295.83 | 6.63 | -b | -b | |
Analysing the concentration of the dissolved Cu, Fe, and Mn from the UFPCu, UFPFe, and UFPMn, respectively, and the N-acetylcysteine and salbutamol were the studied reductive pulmonary inhalants.
Not analysed due to the not detectably corresponding OPDTT.
Table 3.
Pearson's product moment correlation coefficients (r) between OPDTT and soluble metal concentration of UFPs.a
| No. | UFP type | N-acetylcysteine | Salbutamol |
|---|---|---|---|
| 1 | UFPCu/NQ | 0.0047 | 0.2999 |
| 2 | UFPCu/AQ | −0.0848 | −0.1244 |
| 3 | UFPFe/NQ | −0.0071 | 0.5782 |
| 4 | UFPFe/AQ | 0.2980 | 0.7485 |
| 5 | UFPMn/NQ | 0.0203 | −0.0069 |
| 6 | UFPMn/AQ | 0.3985 | −0.5918 |
Correlation analysis was performed between the OPDTT and the soluble metal concentration of each composite UFP in the studied concentration range of N-acetylcysteine (NAC) and salbutamol (ALB) of 0–7000 μM.
4. Discussion
Knowledge concerning the effect of reductive agents in lung fluid on PM-induced oxidative stress is inconclusive. While the reductive pulmonary inhalant concentration plays an important role in determining PM-induced ROS levels in the lung, to our knowledge, the concentration-dependent effects of the reductive pulmonary inhalants in lung fluid on the OP of the UFPs remained unknown. This study demonstrated the dual effects of two reductive pulmonary inhalants (NAC and ALB) on the OPDTT of composite UFPs as the concentrations of those agents increased from 0 to 7000 μM. Specifically, the OPDTT of some composite UFPs increased at lower NAC and ALB concentrations, especially in the range of 0–300 μM. However, at NAC and ALB concentrations >500 μM, the OPDTT of most composites decreased. Correspondingly, the reductive pulmonary inhalants exhibited stimulatory effects at concentrations of 100–500 μM but inhibitory effects at concentrations >1000 μM.
Various PAHs and quinones have been identified in UFPs and served as important contributors to PM-induced ROS generation and oxidative stress [11,12]. The potential mechanisms may involve enzymatic conversion and redox cycling of these redox-active compounds. For example, the oxidative damage of PAHs has been partly attributed to their metabolic process by cytochrome P450 in lung tissues. Specifically, it is generally believed that cytochrome P450 metabolism converts PAHs to their oxidized form, such as quinones [29]. These converted and original quinones in UFPs can generate O2•− by redox cycling of quinoids and their semiquinone radicals (reactions (1)–(4)) [30,31]. The subsequent production of H2O2 in aqueous environment in the presence of O2 (reaction (5)) and HO• generation catalyzed by the redox-active metal elements bound to PM through Fenton or Fenton-like reactions (reaction (6)) [3,32]. In addition, reducing substances in lung fluid may promote ROS generation during quinone redox cycling by donating electrons (reactions (1)–(3)) and by maintaining Fenton or Fenton-like reactions by reducing oxidized metal elements (reaction (7)) [18,31,33]. However, reducing substances that lose their electrons may behave as free radicals and thus exert pro-oxidant effects [34]. For example, the transformation of ascorbic acid into ascorbyl radicals and of β-carotene into carotenoid radicals in the presence of oxygen and ferrous ions has been reported [18,35,36]. Thus, the sulfhydryl groups (-SH) in NAC and the phenolic hydroxyl groups (Ph-OH) in ALB may be transformed into sulfhydryl radicals (-S·) [37] and phenolic hydroxyl radicals (Ph-O⋅) [38], respectively. Similar reactions would link the increased OPDTT of UFPs to the generation of ROS and other radicals in the presence of low concentrations of reductive pulmonary inhalants, whereas high concentrations would lower the OPDTT of UFPs via the gradual neutralization of ROS (reactions (8)–(9)) [34].
| Q + e− + H+ → QH• | (1) |
| QH• + e− + H+ → QH2 | (2) |
| QH2 + O2 → QH• + O2•− + H+ |
| or QH2 + O2 → Q•− + O2•− + 2H+ | (3) |
| Q•− + O2 ⇋ Q + O2•− | (4) |
| O2•− + 2H+ → H2O2 + O2 | (5) |
| H2O2 + Men+ → Men+1 + OH− + HO• | (6) |
| Men+1 + e− → Men+ | (7) |
| HO• + e− → OH− | (8) |
| O2•− + 4H+ + 3e− → 2H2O | (9) |
The soluble metal fraction of PM is widely considered to be the main contributor to PM-induced ROS generation, with metal dissolution from PM, in turn, enhancing ROS generation [18,27,39]. Strong positive correlations were determined between the soluble metal fraction and the OP of PM [40,41]. In the present study, a correlation analysis was performed to estimate the relationship between the OPDTT of the composite UFPs and their soluble metal concentration. As the NAC and ALB concentrations increased from 0 to 7000 μM, there was no significant correlation between the OPDTT and the soluble metal concentration. Interestingly, as the OPDTT increased in response to an increasing ALB concentration, the correlations for some composite UFPs became significantly positive, indicating that within this ALB concentration range, the soluble metal concentration was an important contributor to the OPDTT and that metal release was enhanced by ROS generation. However, at relatively high concentrations of NAC and ALB, the soluble metal concentration remained constant and correlated weakly with the OPDTT. This result can be partially attributed to the inhibition of ROS generation by the high concentrations of the reductive pulmonary inhalants.
To a certain degree, our findings demonstrate the importance of the reductive pulmonary inhalant concentration in affecting the oxidative stress induced by UFPs in lung fluid. At lower doses, reductive pulmonary inhalants may not exert antioxidant effects; instead, they could potentially exacerbate the oxidative stress instigated by UFPs, unless administered at higher concentrations. A previous model-based analysis by Lakey et al. [42] also indicated that PM-induced oxidative stress in the lung was potentially increased by lower concentrations of antioxidants in lung fluid (e.g., 40 μM ascorbate, 207 μM uric acid, 109 μM glutathione, and 0.7 μM α-tocopherol). Nutritional studies have likewise shown that antioxidant concentration is an essential determinant of the anti- or pro-oxidant effects of these agents [20,21]. Consequently, it is imperative to consider both the concentration and type of reductive pulmonary inhalants and their combined impact when designing respiratory disease therapies to mitigate UFP-induced oxidative stress. Failing to do so may inadvertently lead to detrimental effects stemming from the treatment.
5. Conclusion
In this study, an increase in the OPDTT of composite UFPs was observed at lower concentrations of reductive pulmonary inhalant and a decrease at higher concentrations. Moreover, at lower concentration ranges, a significant positive correlation emerged between the OPDTT of the composite UFPs and their soluble metal concentration. This correlation implied a potential contribution of the soluble metal fraction to the OPDTT and a possible promotion of further metal release via ROS generation. To a certain extent, our findings can help clarify the concentration-dependent effects of reductive pulmonary inhalants on UFP-induced oxidative stress. They also highlight the importance of proper dosing of reductive pulmonary inhalants, either alone or as a combination therapy, to avoid inadvertent harmful effects and decrease the risk of UFPs deposited in the lung.
Moreover, recognizing the variability in UFP exposure levels to humans in the actual environment, our future investigations will incorporate diverse ratios of UFPs to lung fluid. This approach aims to simulate the actual UFP exposure level to humans in different situations, thereby yielding more comprehensive insights into the concentration-dependent effects of reductive pulmonary inhalants on UFP-induced oxidative stress.
CRediT authorship contribution statement
Ya-Qi Yu: Investigation, Methodology, Data Curation, Formal Analysis, Visualization, Funding Acquisition, Writing - Original Draft. Tong Zhu: Conceptualization, Resources, Project Administration, Supervision, Funding Acquisition, Writing - Review & Editing.
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
This study was supported by the National Natural Science Foundation of China (grant numbers 91844000 and 41421064), and the China Postdoctoral Science Foundation (grant number 2022M720232).
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