Abstract
Traffic-related PM2.5 can result in immune system damage and diseases; however, the possible mechanism of its effect remains unclear. Calcium (Ca2+) is a critical signaling molecule in a variety of cells. Indeed, Ca2+ is involved in numerous basic functions, including cell growth and death. In this study, Jurkat T cells were used to explore the possible mechanisms of PM2.5-elicited intracellular Ca2+signal responses. The results indicate that PM2.5 could raise the level of intracellular Ca2+ concentration ([Ca2+]i). The [Ca2+]i in Jurkat T cells significantly decreased after treatment with heparin as an inhibitor of inositol trisphosphate receptors (IP3 R), or procaine as an inhibitor of ryanodine receptors (RyR). The expression of calmodulin (CAM) protein decreased in a time-dependent manner after exposure to PM2.5, whereas the activity of Ca2+-Mg2+-ATPase seemed to show a slight drop trend after exposure to PM2.5. Our findings demonstrate that PM2.5 stimulation to Jurkat T cells would result in an increase in [Ca2+]i, which is modulated by IP3 R and RyR, as well as CAM.
Introduction
Fine particulate matter (PM2.5) refers to a mixture of solid and liquid atmospheric particles with an aerodynamic diameter less than or equal to 2.5 µm (Falcon-Rodriguez et al., 2016). As is well known, PM2.5 can deposit in the lower respiratory tract and reach pulmonary alveoli because of its ability to penetrate upper airways of the human respiratory tract (Araujo and Nel, 2009). PM2.5 is mainly emitted from anthropogenic activities such as fossil fuel burning, motor vehicles, and municipal construction. As China’s urbanization progresses, traffic sources PM2.5 gradually surpasses coal-fired sources as the main source of atmospheric PM2.5 in some metropolitan areas. It is well known that PM2.5 is composed of an inert carbonaceous core covered by multiple layers of chemicals such as sulfate, nitrate, organic chemicals (polycyclic aromatic hydrocarbons, PAHs), metals, and crustal elements (Cheng et al., 2015; Schwarze et al., 2006). Numerous studies have shown that PM2.5 are closely related to respiratory and cardiovascular diseases (Xie et al., 2015), as well as cancer (Hamra et al., 2014) and immune function injury (Atkinson et al., 2015; Cesaroni et al., 2013).
Calcium (Ca2+) is an important second messenger that regulates various biological functions such as proliferation, differentiation, apoptosis, and other transcriptional programs in lymphocytes (Orrenius et al., 2003). The dynamic intracellular Ca2 + concentration ([Ca2+]i) balance is the premise and basis for the normal structure and function of the cell. [Ca2+]i are changed by rapidly increasing the concentration of free Ca2+ by opening channels permeable to Ca2+ both in the surface of cell membranes and intracellular organelles containing high Ca2+ concentrations, namely the endoplasmic reticulum (ER) and sarcoplasmic reticulum (SR) (Reddish et al., 2017). Intracellular Ca2+ channels are located in ER and SR including inositol trisphosphate receptors (IP3 R) and ryanodine receptors (RyR), which can transport Ca2+ stored in the organelle to cytoplasm (Santulli and Marks, 2015). It was reported that traffic-related PM2.5 can alter the conformation of Orai1 and activate the stored-operated Ca2+ channels on the cell membrane, thus increasing extracellular Ca2+ influx (Tong et al., 2015). A previous study has shown that diesel exhaust particles can evoke a protracted Ca2+ influx by activation of Ca2+ permeable transient receptor potential vanilloid family member 4 (TRPV4) ion channels in human airway epithelia (Li et al., 2011). Additionally, exposure to environmental pollutant (TOCP, DBP, chlorpyrifos, and endosulfan) also can interfere with Ca2+ homeostasis in cerebral cortex by activation of RyR or IP3 R Ca2+ channels or inhibition of the SERCA pump (Dusza et al., 2018). It may suggest that external pollutants can also disrupt intracellular Ca2+ homeostasis by affecting intracellular Ca2+ channels.
However, there have been few studies on whether traffic-related PM2.5 can elevate [Ca2+]i by opening intracellular Ca2+ channels such as IP3 R and RyR on ER and SR. Therefore, this study was conducted to investigate whether IP3 R and RyRs are involved in traffic-related PM2.5-mediated Ca2+ increase in Jurkat T cells and the possible mechanisms of PM2.5-elicited [Ca2+]i overload.
Materials and methods
Reagents
RNAiso Plus, PrimeScript® RT Enzyme Mix I, and the SYBR® Premix Ex Taq™ II kit were purchased from TaKaRa Biotech Co. Ltd (Dalian, China). Phorbol 12,13-dibutyrate and ionomycin were purchased from Sigma-Aldrich (St. Louis, MO, USA). Rabbit monoclonal antibody to CAM and anti-rabbit secondary antibody, mouse-actin primary antibody and anti-mouse secondary antibody were purchased from Boster Ltd (Wuhan, China). Fluo 3-AM and dimethyl sulfoxide (DMSO) were purchased from Sigma Chemical Company (St. Louis, MO, USA).
Sampling and preparation of the particles
PM2.5 large volume air sampler (TH1000CII) at a flow rate of 1.05 m3/min was employed for sampling at the main traffic junction without large pollution sources nearby from September 1 to October 31, 2011 in Taiyuan, Shanxi, China. PM2.5 samples were collected on quartz filters (PALL, New York, USA). The collection of every filter lasted for 12 h (8:00 a.m. to 8:00 p.m.). The filter containing particles was then cut into 1 cm × 3 cm sections, submerged in deionized distilled water, and subjected to ultrasonic oscillation for three times, with 20 min per time. The solution was filtered with six layers of gauze for removing the impurities. The filtrates were frozen at −80°C for 24 h and then freeze-dried under vacuum to obtain the dried PM2.5 particles. Before use, the particles were diluted with sterilized 0.9% saline and mixed for 15 min with ultrasonic oscillation.
Cell culture
Jurkat T lymphoblastic leukemia cells (E6 -1, Shanghai Life Science Institute, China) were suspended in RPMI-1640 medium (Gibco) supplemented with 10% fetal bovine serum (FBS) (v/v), 1% penicillin, and streptomycin at 37°C in a 5% CO2 humidified incubator. All experiments were performed using cells in a logarithmic growth phase. Finally, some related indicators were measured.
MTT assay
The cytotoxicity of PM2.5 was evaluated using the MTT (3-[4, 5-dimethylthiazolyl-2]-2, 5-diphenyltetrazolium bromide) assay (Lombardi et al., 2017). Briefly, Jurkat T cells at the concentration of 1 × 106 cells/mL were cultured in 96-well plates at 37°C with PM2.5 at concentrations of 0, 5, 20, 80, 200, 320, and 800 µg/mL. After 24-h incubation, 20 µL of MTT solution (5 mg/mL) was added to each well and incubated for an additional 4 h at 37°C and 5% CO2. After the media was removed from each well, 200 µL of DMSO was added to dissolve the intracellular crystalline formazan product and incubated on a shaker at room temperature for 30 min until the crystals were completely dissolved. The absorbance was read at 550 nm by a spectrophotometer (Bio-Rad, Hercules, CA, USA). The results were calculated as a percentage of the absorbance of viable control cells. PM2.5 at the concentration of both 320 µg/mL and 800 µg/mL resulted in significantly decreased viability (p < 0.05). There was no statistically significant difference between cells treated with other PM2.5 concentrations and the control ones. Therefore, 50–200 µg/mL of PM2.5 were used for exposure experiments.
Ca2+-Mg2+-ATPase assay
A Ca2+-Mg2+-ATPase assay kit (A068, Nanjing Brioche, China) was used according to the manufacturer’s protocol for a 5-min centrifugal of 125 ×g on the collected cells and 400 µL saline was added in order to prepare a single cell suspension. Concrete steps were taken based on the kit instructions. The results were normalized to total protein concentration that was detected using the BCA assay.
[Ca2+]i assay
Total cell numbers were approximately 2 × 106 cells/mL by the trypan blue dye exclusion method. Cells suspended in PBS (pH: 7.2–7.4) were loaded with Fura 3-AM (5 µmol/L final concentration) using gentle agitation in a shaking dry oven at 37°C for 60 min. The cells were then washed twice with Phosphate Buffered Saline (PBS) and resuspended using binding buffer, which excluded the Ca2+ and Mg2+ to remove residual extracellular Fura-3/AM. Finally, the fluorescence intensity of each sample was measured on 526-nm emission wavelength and 488-nm excitation wavelength (Thermo Fisher Scientific, USA). First, 488 resting fluorescence intensity (F) in the cells was measured; then a final concentration of 0.3% Triton X-100 (20 µL of 30% Triton X-100) was added; 488 maximum fluorescence intensity (Fmax) was determined; a final concentration 3 mmol/L EGTA (240 µL stock solution) was added; 488 minimum fluorescence intensity (Fmin) was measured. Intracellular calcium ion concentration is calculated as follows: [Ca2+]i (nM) = Kd (F − Fmin)/(Fmax − F). Kd is Fura-3 and Ca2+ binding of the dissociation constant (a value of 450 nmol/L).
Quantitative real-time PCR analysis
Gene expression levels were measured using the real-time reverse transcription polymerase chain reaction assay. RNA was extracted using RNAiso Plus (Takara, China) according to the manufacturer’s recommendations. The cDNA was generated using 500 ng of total RNA from the Jurkat T cells with PrimeScript® RT Enzyme Mix I (TaKaRa) according to the manufacturer’s protocol. Real-time quantitative PCR (RT-qPCR) was performed with a Bio-Rad iQ5 Real-Time PCR system (Bio-Rad, USA) using a SYBR® Premix Ex Taq™ II kit (TaKaRa) in a reaction volume of 25 µL with 2 µL of template complementary DNA (cDNA). The Real-time PCR (RT-PCR) reaction mix was denatured at 95°C for 30 s and then subjected to 40 amplification cycles (30 s of denaturation at 95°C, 30 s of annealing at 60°C, and 20 s of extension at 72°C). The forward and reverse primers for CAM and glyceraldehyde-3-phosphate dehydrogenase (GAPDH) used in this study were designed with the OligoPerfectTM Designers software (Invitrogen, Carlsbad, CA); the sequences and product sizes are presented in Table 1. GAPDH was used as a housekeeping gene to normalize the data. The ΔCt was calculated by subtracting the ΔCt of GAPDH from the ΔCt of CAM for each sample. The ΔΔCt was calculated by subtracting the ΔCt of the control sample from the ΔCt of each treated sample. Fold change was determined using the equation, 2− ΔΔCt. All of the real-time PCR experiments were performed in triplicate and data were expressed as the mean of at least three independent experiments.
The sequences and product sizes of all genes.
CAM: calmodulin.
Western blotting
Cells (1 × 106 cells/mL) treated with PM2.5 were used for SDS-PAGE analysis. Cells were washed with PBS and then resuspended in 55 µL of Radio-Immunoprecipitation Assay (RIPA) buffer containing phosphatase inhibitors to extract total protein. Protein concentrations were determined using a BCA kit (Kangwei Biotech, Beijing, China). Cellular proteins (50 µg) were subjected to electrophoresis with 10% SDS-PAGE and blotted onto polyvinylidene fluoride (PVDF) membranes (Boster Brioche, WuHan, China). PVDF membranes were blocked with 5% skim milk in PBST (PBS with 0.05% Tween-20 ) and shaken for 2 h at room temperature. Next, the membranes were washed briefly three times in PBST and incubated with CAM and β-actin primary antibodies overnight at 4°C. Proteins were detected with enhanced chemiluminescence staining.
Statistical analysis
The experimental data were analyzed using SPSS 17.0. Statistical significance was evaluated using one-way analysis of variance to test the significance between multiple groups followed by a SNK test for multiple comparisons. Differences were considered significant at a probability level of p < 0.05.
Results
Cytosolic Ca2+ measurements
To investigate the [Ca2+]i changes in Jurkat T cells induced by PM2.5, the active Jurkat T cells were stimulated by different concentrations of PM2.5 for 3 h, the [Ca2+]i levels in 100 µg/mL of PM2.5 exposure group increased, whereas the [Ca2+]i levels in 200 µg/mL of PM2.5 group decreased. There was no significant difference for [Ca2+]i levels among different groups of the resting cells (Figure 1(a)). Thus we chose 100 µg/mL of PM2.5 to determine the role of PM2.5 in intracellular Ca2+ regulation. We pretreated resting and active Jurkat T cells with 100 µg/mL of PM2.5 for 1 h, 3 h, 6 h, 12 h, and there was no significant difference for [Ca2+]i levels between saline control groups of the resting and active cells in difference hours, but both the resting and active group the [Ca2+]i levels in 100 µg/mL PM2.5 group at the peak of 3 h, the [Ca2+]i levels gradually decreased in a time-dependent manner (p < 0.05). Moreover, regardless of the resting and active groups, the [Ca2+]i levels at different times of 100 µg/mL PM2.5 groups except for the 12 h of active group were significantly increased compared with their own control groups (p < 0.05) (Figure 1(b) and (c)). This result shows that PM2.5 induces an increase of [Ca2+]i in Jurkat T cells at 3 h. We noted that compared to the resting groups, the active groups show a more pronounced stimulation induced by PM2.5, which indicates that under the inflammation stimulation PM2.5 can cause stronger effect of [Ca2+]i elevation on lymphocyte.

Effects of PM2.5 on [Ca2+]i in Jurkat T cells. (a) [Ca2+]i was measured after the resting and active cells exposed to 50 µg/mL, 100 µg/mL, and 200 µg/mL PM2.5 for 3 h. (b and c) [Ca2+]i was measured after the resting and active cells exposed to 100 µg/mL PM2.5 for 1, 3, 6, 12 h. All data (mean ± SD) shown in this figure were the average of triplicates determinants. *Indicates statistically significant differences from their respective saline control group. #Indicates statistically significant differences from the respective 3 h 100 µg/mL PM2.5 group (p < 0.05 by SNK test). PDB: phorbol 12,13-dibutyrate; [Ca2+]i: intracelluar Ca2 + concentration; Ca2 +: calcium.
Intracellular Ca2+-Mg2+-ATPase activity
To investigate whether PM2.5 can influence the activity of intracellular Ca2+-Mg2+-ATPase, resting and active Jurkat T cells were stimulated by different concentrations of PM2.5. Although Ca2+-Mg2+-ATPase in 100 µg/mL of PM2.5 group obviously decreased, there was no significant statistical difference with the normal saline groups (Figure 2). This result suggestss that the PM2.5 may decrease the expression of the Ca2+-Mg2+-ATPase activity that leads to the increase of the cell membrane permeability to Ca2+, which may induce the increase of [Ca2+]i in Jurkat T cells.

The activity of Ca2+-Mg2+-ATPase in Jurkat T cells after treated with 50 µg/mL, 100 µg/mL, and 200 µg/mL PM2.5 for 3 h. Results are shown as the alternation in the activity of Ca2+-Mg2+-ATPase for triplicate samples. Data are presented as mean ± SD. Ca2 +: calcium.
Ca2+ signal regulation of IP3 R and RyR channels
We examined the role of the IP3 R and RyR channels in the PM2.5-induced Ca2+ signal response. Firstly, Jurkat T cells were pretreated with various concentrations of heparin (40, 80, 100, 120 µg/mL) and PM2.5 (100 µg/mL) for 3 h. In resting Jurkat T cells, heparin at the concentrations of 100 µg/mL and 120 µg/mL significantly inhibited PM2.5-stimulated Ca2+ elevation and caused a decrease of [Ca2+]i, which has a significant difference compared with the PM2.5 group. When it comes to activated Jurkat T cells, the [Ca2+]i in Jurkat T cells induced by both concentrations of heparin were significantly lesser than that in the PM2.5 control group (p < 0.01). Therefore, we chose 120 µg/mL heparin as the inhibitor dose to further determine the role of IP3 R in Ca2+ signal regulation. Figure 3(a) shows that no remarkable change on [Ca2+]i level was observed between saline and heparin + saline group, which means heparin has no effect on the original state of [Ca2+]i. Regardless of resting and activated Jurkat T cells, the [Ca2+]i level in the 100 µg/mL PM2.5 group was significantly greater than that in the saline group (p < 0.01). [Ca2+]i level in the heparin + PM2.5 group was lower than that of the PM2.5 group. This finding suggests that IP3 R regulates the Ca2+ response of Jurkat T cells to PM2.5. What’s more, to test whether RyR are involved in PM2.5-elicited Ca2+ elevation, we used procaine, an antagonist of RyR, to observe the effect of PM2.5 on RyR channels. Resting and active Jurkat T cells were incubated with saline and various concentrations of procaine (1, 2, 4, 6, 10 mmol/L) with PM2.5 (100 µg/mL) for 3 h. [Ca2+]i decreased with increasing dose of procaine, both in the resting groups and active groups, so we chose the moderate dose of 6 mmol/L to verify the role of RyR in Ca2+ signal regulation. As suggested in Figure 3(b), there was no significant difference between saline and procaine groups both in resting and active Jurkat T cells. Compared to the saline group, PM2.5 was significantly potent in increasing the level of [Ca2+]i; however, the [Ca2+]i level in the procaine + PM2.5 groups was less than that of the PM2.5 group in either resting or active Jurkat T cells, and inhibition of RyR can effectively reduce the increase of [Ca2+]i induced by PM2.5. Thus, blocking these two channels in resting and active Jurkat T cells can obviously decrease the [Ca2+]i level, and the higher the dose of those two channels inhibitors was, the less the level of [Ca2+]i was. It shows a negative correlation between the concentration of inhibitors and [Ca2+]i. Therefore, we can confirm that both IP3 R and RyR channels play an important role in [Ca2+]i regulation. Under the stimulation of PM2.5, the Jurkat cells start the calcium-ON mechanism, which promotes the Ca2+ transport from the organelle to the cytoplasm through the IP3 R and RyR channels.

Effects of heparin and procaine on [Ca2+]i in Jurkat T cells. (a) [Ca2+]i was measured after the resting and active cells exposed to 0 µg/mL or 100 µg/mL of PM2.5 with or without 120 µg/mL heparin for 3 h. (b) [Ca2+]i was measured after the resting and active cells exposed to 0 µg/mL or 100 µg/mL of PM2.5 with or without 6 µg/mL procaine for 3 h. Data are presented as mean ± SD. *Indicates statistically significant differences from their respective saline control group. #Indicates statistically significant differences from their respective 100 µg/mL PM2.5 group (p < 0.05). Ca2 +: calcium.
The mRNA and protein expression of CAM in Jurkat T cells
The mRNA and protein expression of CAM in Jurkat T cells were detected with RT-PCR and Western blotting. Figure 4(a) shows that regardless of the resting or active Jurkat T cells, the mRNA expression of CAM was the least in the 100 µg/mL of PM2.5 groups and there shown a significantly difference compared with the saline group (p < 0.05). Figure 4(b) and (c) shows that under the same exposure condition, protein expression of CAM gradually decreased with elevated PM2.5 concentrations, which presented a dose-dependent relationship. Compared with the resting cells group, the effect of the active cells groups is more pronounced. Therefore, we speculate that PM2.5 may reduce the expression of CAM at the gene level and interfere with translocation, and then affect the balance of [Ca2+]i homeostasis. Therefore, Ca2+ may lose the chance of binding to CAM, thus resulting in an increase of [Ca2+]i and eventually leading to Ca2+ overload.

Effects of PM2.5 on CAM expression in Jurkat T cells. (a) CAM mRNA expression was measured after the resting and active cells were exposed to 50 µg/mL, 100 µg/mL, and 200 µg/mL PM2.5 for 3 h. (b and c) The expression of CAM protein in Jurkat T cells after 50 µg/mL, 100 µg/mL, and 200 µg/mL PM2.5 exposure for 3 h. Data are presented as mean ± SD. *Indicates statistically significant differences from their respective saline control group (p < 0.05). CAM: calmodulin; PDB: phorbol 12,13-dibutyrate.
Discussion
In order to establish a model of active T lymphocytes for further investigating the effects of PM2.5 on T lymphocytes under inflammatory stimuli activated state, we chose the phorbol 12,13-dibutyrate (PDB) and ionomycin (Ion) in our experiments with the purpose of simulating the activation of T lymphocytes. PDB belongs to protein kinase C (PKC) activators, is a nonphysiological diacylglycerol (DAG), and can pass through the cell membrane freely, thus simulating the DAG function and directly activating protein kinase signaling pathways (Sun et al., 2000). Ion is a calcium ionophore and can enable extracellular Ca2+ influx and intracellular Ca2 + release from intracellular Ca2+ stores, leading to an increase of the [Ca2+]i (Morgan and Jacob, 1994). Studies have shown that only the Ca2+ ionophore, such as A23187 and ionomycin, cannot activate T lymphocytes (Truneh et al., 1985), whereas the PDB and Ion synergies can induce gene activation and proliferate responses; they will induce resting T cells to secrete IL-2 and IFN-γ to modulate their immune functions and proliferation status (Wang et al., 2015). The current study suggests that PM2.5 tended to induce higher [Ca2+]i in T lymphocyte and exacerbate the Ca2+ homeostasis imbalance in the case of inflammatory condition. Our data show that, after 1 to 3 h exposure to PM2.5, the [Ca2+]i increased, which is consistent with the previous study (Lin et al., 2006), but as time went on, the [Ca2+]i decreased at 6–12 h. Indeed, the investigator suggests that most of the Ca2+ released into the cytosol will be re-uptaken by the Ca2+ pump back into the ER and SR to maintain the Ca2+ concentration in it. Moreover, Ca2+-Mg2+-ATPase and Na+/Ca2+ pumps on the cell membrane further transport intracellular Ca2+ out of cells and reduce [Ca2+]i levels (Berridge et al., 2000).
It is reported that Ca2+-Mg2+-ATPase is a special protein that embeds in the cell membrane lipid bilayer (Takakuwa and Kanazawa, 1982). Its activity has a very close relationship with cellular energy metabolism and the physiological processes of signal transduction. Under normal circumstances, the [Ca2+]i is approximately 100 nmol/L, but the extracellular Ca2+ concentration is 10,000 times that of [Ca2+]i (Galione and Churchill, 2002). The main substance that maintains the low intracellular Ca2+ level is the Ca2+-Mg2+-ATPase. The primary role of Ca2+-Mg2+-ATPase is to pump Ca2+ out of the cell to maintain the Ca2+ homeostasis environment inside and outside the cell. We observed that exposure to 100 µg/mL of PM2.5 caused Ca2+-Mg2+-ATPase activity to appear declining trend, which may explain the results that the [Ca2+]i was the highest in the 100 µg/mL PM2.5 group. A relevant study described that the Ca2+-Mg2+-ATPase activity decreased with the elevated Pb+, Na+, and Ca2+ concentrations in the cells (Sun et al., 2007). Recent study shows that exposure to Al causes the decrease of Ca2+-Mg2+-ATPase activity, which leaving Ca2+-Mg2+-ATPase unable to keep up with the Ca2+ transport needs and further aggravating Ca2+ overload (Cao et al., 2018). Previous report also indicates that Ca2+ overload disrupts the structure and function of mitochondria, impedes cellular energy metabolism, and reduces ATP production (Zhu et al., 1995). Therefore, decreasing Ca2+-Mg2+-ATPase activity of cell membrane results in a decline of Ca2+ active outflow, and thus causes an increase of [Ca2+]i, which leads to a vicious circle that may give rise to cytotoxicity or apoptosis.
The IP3 R and RyR channels, which regulate intracellular Ca2+ signal release and many physiological functions, usually localize in intracellular Ca2+ stores such as ER, SR, mitochondria of the cells (Santulli et al., 2018). The distributions of these two receptors systems vary with tissues (Gambardella et al., 2018). Our finding shows that 120 µg/mL heparin can significantly inhibit elevated [Ca2+]i stimulated by the PM2.5 both in resting and activated Jurkat T cells, indicating that IP3 R channels are involved in the regulation of Ca2+ levels stimulated by PM2.5 in Jurkat T cells. In accord with our present findings, a recent study found that augmenters of liver regeneration inhibited IP3R-mediated Ca2+ release and thus maintained the cytosolic Ca2+ at a physiological level, protecting the cells from the apoptosis caused by ER stress (Xiao et al., 2018). Additionally, several studies have also shown that cytosolic-free Ca2+ concentrations can be increased by IP3-sensitive Ca2+ pools (Dusza et al., 2018; Santulli et al., 2017). Interestingly, our findings revealed that when resting and active Jurkat T cells were incubated with 6 µg/mL of procaine + saline, the [Ca2+]i level almost had no change. It indicates that the procaine blocker has no effect on Jurkat T cells normal [Ca2+]i. However, the [Ca2+]i elevating effect induced by PM2.5 was prevented by pretreatment with procaine, and it may indicate that RyR may have been involved in Ca2+ signal responses elicited by PM2.5. As reported earlier, the BaP metabolite, 7,8-benzo(a)pyrene quinone, can induce human B cell lines, human blood mononuclear cells, and mouse spleen lymphocytes to increase intracellular Ca2+ levels by the RyR-dependent pathway (Gao et al., 2005). According to the component analysis of PM2.5 in this study affiliated in online supplemental material, there were 13 common PAHs detected in PM2.5, and the mass of PAHs accounts for about 0.55% of particulates. Thus we consider that traffic-related PM2.5 can induce disorders of [Ca2+]i homeostasis, and IP3 R and RyR channels play important roles in Ca2+ signal responses.
Calmodulin (CAM), a widely existing Ca2+ receptor and versatile regulatory protein in all eukaryotes, is the core of metabolic modulation of the second messenger Ca2+ (Gillespie and Hodge, 2013). The CAM and Ca2+ were combined to form Ca2+-CAM complexes, which ensures the accurate combination of CAM and target enzyme/protein so as to regulate their activities (Sanabria et al., 2008). As shown in our results, traffic-related PM2.5 induced a decline of Jurkat T cells CAM expression, so that the Ca2+ signal cannot be fully passed on downstream protein molecules, which may cause toxic effects on cellular immune functions eventually. The ability of CAM regulation Ca2+ attenuated when the expression of CAM reduced. Meanwhile, increased [Ca2+]i could produce cytotoxic effects (Seales et al., 2006). It was reported that cadmium could increase free Ca2+ concentration in spleen lymphocytes of LACA mouse and reduce the expression of CAM (Xiao et al., 2008). Therefore, PM2.5 may decrease the expression of CAM and reduce its ability to regulate Ca2+ and further disrupt the Ca2+ homeostasis.
In the current study, our results suggest that PM2.5 can trigger [Ca2+]i increase adjusted by intracellular stores, and CAM and Ca2+-Mg2+-ATPase may have involved in Ca2+ signal regulation. Moreover, PM2.5 appeared to have more approaches to alter the [Ca2+]i in T cells. Relative study has shown that PM can elicit the high [Ca2+]i through the channels on cytomembrane such as Orail1 in Jurkat T cells and TRPV4 in human respiratory epithelial cells (Li et al., 2011; Tong et al., 2015). Ca2+ is an important second messenger, it can promote critical signal transduction and functional events, such as oxidative stress (OS), apoptosis, inflammatory reaction, immune function, and other signal molecules. It was noted that soluble metals (e.g. Fe, Vi, Ni, and Zn) and PAHs absorbed in PM can contribute to the reactive oxygen species (ROS) generation (Al Hanai et al., 2019). For instance, alveolar macrophages could produce large amounts of ROS when exposed to PM2.5. OS can damage biofilm Ca2+ channels in cytomembranes, ER/SR and Ca2+ pumps, then increasing Ca2+ influx and bring about lipid peroxidation of biofilms, which can impair cell membrane functions and change its permeability (Schmidt et al., 2004). Furthermore, OS can interfere with the cytokine secretion and eventually leads to immune system dysfunction (Clemens and Lowell, 2019). With higher [Ca2+]i levels than the physiological state in cells, Ca2+ can trigger further generation of ROS (Tiwari et al., 2017) and activate Nrf2, NF-κB, and MAPK pathways (Al Hanai et al., 2019) to regulate inflammatory responses. Simultaneously, the increased [Ca2+]i can activate caspase-3, trigger Fas ligand, and inhibit the gap junctional intercellular communication (Ji et al., 2018) to induce apoptosis. Further, oxygen stress also can trigger mitochondria-mediated apoptosis (Tiwari et al., 2017). Additionally, the increased [Ca2+]i can activate MMP-1 in vitro (Li et al., 2011) and CAN-NFAT signaling pathway in Jurkat T cells, upregulate the expression of TNF and IL-2, and regulate cellular immune function (Tong et al., 2015). Collectively, high levels of [Ca2+]i elicited by PM2.5 can be immunotoxic to lymphocytes and affect the function and survival status of lymphocytes.
Because of the complexity of PM2.5, in this study we only considered PM2.5 as a whole with a preliminary discussion on its effect on Ca2+ signaling responses in T lymphocytes. Currently, more and more studies have begun to study the mechanisms of toxicity of PM2.5 components from a microscopic perspective (Chen et al., 2018; Li et al., 2019; Zou et al., 2016). Thus further studies are needed to determine which components are involved in IP3 R and RyR channels opening. Additionally, we measured the Ca2+-Mg2+-ATPase activity using a visible light spectrophotometer. Although we have repeated trails, and limited to experimental conditions, the data are highly variable. Therefore, a stable measuring method is requires to assure the stability of data. Similarly, intracellular Ca2+ changes are very rapid, and we have only selected four time periods for research, which limits our study of the opening mechanisms of Ca2+ channels, whereas real-time Ca2+ response monitoring by flow cytometry can provide more Ca2+ regulation information. Hence, we suggest further advanced methods to investigate the Ca2+ signal regulation of specific component of PM2.5.
In summary, our results revealed that traffic-related PM2.5 can induce a disorder of Ca2+ homeostasis of Jurkat T cells. The intracellular IP3 R and RyR channels are involved in Ca2+ efflux from ER/SR, which results in increased [Ca2+]i, accompanied by reduced CAM expression, as well as possible decreased Ca2+-Mg2+-ATPase activity.
Supplemental material
Supplemental Material, Appendix_(5) - IP3R and RyR channels are involved in traffic-related PM2.5-induced disorders of calcium homeostasis
Supplemental Material, Appendix_(5) for IP3R and RyR channels are involved in traffic-related PM2.5-induced disorders of calcium homeostasis by Huichao Zhao, Guoqiang Tong, Jiejing Liu, Jing Wang, Hongmei Zhang, Jianying Bai, Lifang Hou and Zhihong Zhang in Toxicology and Industrial Health
Footnotes
Acknowledgement
The authors thank Ms Gao Shaofen and Ms Gao Yan of Department of Foreign Languages at Shanxi Medical University for the language polishing to this manuscript.
Authors’ Contribution
Huichao Zhao, Guoqiang Tong and Jiejing Liu contributed equally to this work.
Declaration of Conflicting Interests
The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The author(s) disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This work was supported by the National Natural Scientific Foundation of China (no. 81072261).
Supplemental material
Supplemental material for this article is available online.
References
Supplementary Material
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