Toll-like receptor 4 in glial inflammatory responses to air pollution in vitro and in vivo
© The Author(s). 2017
Received: 21 December 2016
Accepted: 29 March 2017
Published: 14 April 2017
Exposure to traffic-related air pollution (TRAP) is associated with accelerated cognitive aging and higher dementia risk in human populations. Rodent brains respond to TRAP with activation of astrocytes and microglia, increased inflammatory cytokines, and neurite atrophy. A role for Toll-like receptor 4 (TLR4) was suggested in mouse TLR4-knockouts, which had attenuated lung macrophage responses to air pollution.
To further analyze these mechanisms, we examined mixed glial cultures (astrocytes and microglia) for RNA responses to nanoscale particulate matter (nPM; diameter <0.2 μm), a well-characterized nanoscale particulate matter subfraction of TRAP collected from a local freeway (Morgan et al. Environ Health Perspect 2011; 119,1003–1009, 2011). The nPM was compared with responses to the endotoxin lipopolysaccharide (LPS), a classic TLR4 ligand, using Affymetrix whole genome microarray in rats. Expression patterns were analyzed by significance analysis of microarrays (SAM) for fold change and by weighted gene co-expression network analysis (WGCNA) to identify modules of shared responses between nPM and LPS. Finally, we examined TLR4 activation in hippocampal tissue from mice chronically exposed to nPM.
SAM and WGCNA analyses showed strong activation of TLR4 and NF-κB by both nPM and LPS. TLR4 siRNA attenuated TNFα and other inflammatory responses to nPM in vitro, via the MyD88-dependent pathway. In vivo, mice chronically exposed to nPM showed increased TLR4, MyD88, TNFα, and TNFR2 RNA, and decreased NF-κB and TRAF6 RNA TLR4 and NF-κB responses in the hippocampus.
These results show TLR4 activation is integral in brain inflammatory responses to air pollution, and warrant further study of TLR4 in accelerated cognitive aging by air pollution.
KeywordsAir pollution Nanoparticulate matter Microglia Astrocytes TLR4 NF-kB TNFα Cell culture Hippocampus
Traffic-related air pollution (TRAP) is associated in human populations with accelerated cognitive aging [1–4] and increased risk of dementia [5–8]. Exposure to high levels of fine particulate matter (PM2.5) in older adults is associated with greater cognitive decline, equivalent to 2 years of normal cognitive aging [9, 10], and developmental exposure to TRAP is associated with delayed and impaired cognitive development [11, 12].
TRAP-associated changes of normal aging include decreased white and grey matter [13, 14], while post mortem samples from a highly polluted Mexican City showed white matter hyperintensities and neuroinflammation [15, 16]. Rodent models given controlled exposure to TRAP particulate material (PM), showed corresponding loss of dendritic spines  and microglial activation [18, 19]. Brain inflammatory responses include increased IL-1α and TNFα [17, 18, 20], together with NF-κB  and detoxifying enzymes associated with Nrf2 . In our model, mice were chronically exposed to nPM, a nano-scaled subfraction of TRAP [18, 23].
Airborne PM is defined by three size classes: coarse, PM10; <10 μm diameter; fine, PM2.5; <2.5 μm; and ultrafine, PM0.2; <0.2 μm. The PM0.2, though not EPA regulated, have more toxicity and greater redox activity than larger size fractions . In rodents, in vivo exposure to PM0.2 shows their penetration into the brain via the nose [25, 26]. The present studies use a nano-sized water-soluble subfraction of PM0.2 (nPM) with strong redox and inflammatory activity in vitro and in vivo that induced microglial activation TNFα and other cytokines associated with oxidative stress [24, 27].
To further study glial roles, we used an in vitro model of mixed glia (astrocytes and microglia), in which nPM induced TNFα induction with well-defined dose response . In media from nPM-treated glia, primary neurons had shorter neurites and fewer growth cones; these nPM effects were mediated by the TNFα receptor TNFR1 . We hypothesized further that these mechanisms involve a priori genes of interest NF-κB and TLR4 (Toll-like receptor 4), through MyD88-dependent pathways, shown for lung macrophage responses to TRAP [28, 29]. TLR4 has over 30 known ligands . Its role in inflammatory pathways may include neuroprotective functions, e.g., by increasing amyloid β-peptide uptake by microglia . While a TLR4 response to air pollution has been hypothesized, its exact involvement remains unclear, as TLR4 mutant individuals still showed immune cell response to PM .
These questions were agnostically approached by Affymetrix microarray in mixed glia cultures for responses to nPM and to lipopolysaccharide (LPS). The endotoxin LPS is relevant to TRAP induced inflammatory responses. While nPM does not contain endotoxin , the larger sized PM have endotoxin activity , whereas the TLR4 pathway is necessary for LPS responses. Our findings were compared with LPS responses of BV-2 microglial cells [34, 35] and primary cultured microglia .
Two bioinformatics approaches were used: fold changes in RNA expression were identified by significance analysis of microarrays (SAM) and shared modules of RNA responses between LPS and nPM were identified by weighted gene co-expression network analysis (WGCNA), which has advantages over differential expression analysis. WCGNA enables the reduction of high-dimensional data into fewer variables for analysis of shared responses between treatments. While both SAM and WGCNA identify larger responses, WGCNA also identifies subtler interactions within a network. WGCNA provides further insight into the relationships between genes, extending beyond known pathways .
Following SAM and WGCNA, we analyzed transcription factor target (TFT) enrichment and upstream regulators. Finally, bioinformatics findings were verified in vitro by siRNA experiments with mixed glia and in vivo with hippocampal RNA from mice exposed to nPM.
Animals and ethics statement
Pregnant Sprague Dawley rats, from Envigo (Livermore, CA, USA) and C57BL/6J female mice, from the NIA Aged Rodent Colony (Charles River Labs) were maintained under standard conditions according to NIH guidelines. Protocols were approved by the University of Southern California Institutional Animal Care and Use Committee.
Collection of nanoscale particulate material (nPM)
The nPM utilized in these studies are a nanoscale subfraction of TRAP (<200 nm diameter) collected from urban air in Los Angeles near the CA-110 Freeway using a high-volume impactor sampler . These aerosols represent a mix of fresh ambient PM mostly from vehicular traffic [39, 40]. nPM was collected continuously for 5 weeks on Teflon filters, followed by resuspension in deionized water by vortexing and sonication . The nPM comprised approximately 20% by mass of ambient PM2.5 in that location . Water-soluble metals and organic compounds were efficiently transferred from the filter into aqueous suspension for exposures . Relative to the total filter-trapped ultrafines (PM0.2), the nPM subfraction eluted into aqueous phase was depleted in black carbon and water-insoluble organic compounds . Stock nPM solution had trace endotoxin levels (2.5 EU/mL by Limulus amoebocyte assay) compared to that eluted from filter collected ambient air (2.0 EU/mL). Treatment levels were 0.05–0.08 EU/mL, equivalent to sterile water (FDA 2015). These low EU levels are consistent with the negligible endotoxin activity in ultrafine PM (below Limulus assay threshold) . Frozen stocks at 20 °C retain chemical stability for >30 days, including long-lived free radicals [18, 24]. The nPM was re-aerosolized to an airborne concentration of 300 μg/ml. Mice (3 month old) were exposed to nPM or filtered air for 150 h during 10 weeks (5 h/day, 3 days/week).
One month after exposure, mice were anesthetized by isoflurane and saline perfused. One hemisphere was cryosectioned for histochemistry and the other, microdissected by brain region.
Primary mixed glia (microglia and astrocytes) were cultured from neonatal postnatal day 3 rat cerebral cortex (mixed sex, Sprague Dawley; Envigo, Livermore, CA). Mixed glial cultures were used because some astrocyte responses to LPS are microglial dependent [42, 43]. Mixed glial cultures were 3:1 astrocytes to microglia . Cerebral cortex was mechanically dissociated, strained by a 70-μm Millipore filter, and plated onto 75-cm2 cell culture flasks in Dulbecco’s modified Eagle’s medium/F12 (Cellgro, Mediatech, Herndon, VA) supplemented with 10% fetal bovine serum, 1% penicillin, and 1% L-glutamine. Cultures were incubated at 37 °C with 95:5% mixture of air:CO2. Media was refreshed twice in week 1 and once during week 2. Cells were trypsinized, plated on six-well plates, and treated with nPM (10 μg/mL, 24 h) or LPS (100 ng/mL, 48 h for microarray, 24 h for TLR4 knockdown). The 10 μg/mL dose of nPM is based on published work demonstrating conditioned media from mixed glia treated with 10 μg/mL nPM reduced inhibited neurite outgrowth and reduced the number of neurites .
Total cell RNA was isolated by TRIzol; cDNA was reverse transcribed (Promega) and analyzed on Affymetrix Rat Whole Genome 230.2 array. For individual gene verification, q-PCR was done with Taq Master Mix (Biopioneer), with primers designed with Primer3 and verified by NCBI Primer-BLAST (Basic Local Alignment Search Tool). Data was quantified as ΔΔCT and normalized to GAPDH.
For nPM microarray, RNA-cDNA was prepared from N = 4 treated and N = 4 controls. For LPS cultures, we compared five treated versus four control cultures. Microarray was verified by q-PCR, with N = 14 per group.
Raw Affymetrix data were normalized by the Robust Multi-array Averaging R algorithm [44–46]. The output is then transformed to log2. LPS and nPM microarrays were independently normalized to controls within each individual experiment. These datasets are available as raw data files, given in Additional file 1.
Significance analysis of microarrays (SAM)
Normalized microarray data were analyzed for fold change by SAM, to assess differential expression associated with nPM and/or LPS exposure relative to controls. The input into SAM was an individual log2 fold change score for each microarray probe, with significance calculated using permutation tests (100 permutations) and presented as q-values to account for false discovery rate, with an FDR threshold at 1% (q < 0.01).
Weighted gene co-expression network analysis (WGCNA)
Gene expression networks were identified using the WGCNA package in R . Adjacency matrices for nPM and LPS were generated by first calculating biweight midcorrelations of gene expression for each gene pair. To construct weighted gene networks, these measures of co-expression (correlation coefficients) are raised to a power of β—the soft-thresholding power. This value is chosen by analyzing scale-free topology. More information on selecting a β value can be found in work by Zhang and Horvath . For this analysis we used a soft-thresholding power of 6. Adjacency for each gene pair was then defined using topological overlap matrices (TOMs). TOM incorporates higher-order connections by taking into account the number of “neighbors”, or connections, that a pair of genes share . Individual TOMs were estimated for both nPM and LPS. A consensus topological overlap (across nPM and LPS) was calculated using the component-wise (parallel) minimum of the individual TOMs. TOMs were then converted to dissimilarity matrices by subtracting from 1. Modules were then defined by employing hierarchical clustering with TOMs as input with the following WGCNA parameters: unsigned network, minimum module size of 30, and medium sensitivity (deepSplit = 2). Hierarchical clustering assigns each gene to a specific module (denoted by different colors), which represent networks of highly interconnected genes.
Following module assignment, eigengenes were estimated for each module. The eigengene is a single quantitative value for a module, which represents its overall gene score, based on levels of messenger RNA (mRNA) for all genes assigned to that module. The use of eigengenes enables dimension reduction—instead of comparing gene expression between exposure and controls for thousands of genes, comparisons of higher-order measures of gene expression between exposure and controls can be carried out for less than 100 modules. We then screened for hub genes (genes that are highly connected within a given module). Although the hierarchical clustering assigns each gene to one module, module membership can be defined by calculating eigengene-based connectivity (kME) for each gene-by-module pair as the correlation between expression levels of a gene and the eigengene (quantitative score) for a module. kME was calculated in each set (nPM and LPS), then consensus kME scores were generated as meta-analytic scores by Stouffer’s method. Based on kME, hubs for each module were defined as the genes with the highest connectivity (kME ≥0.80).
Pathway enrichment analysis by Kyoto Encyclopedia of Genes and Genomes (KEGG) (www.genome.jp/kegg/) and Gene Ontology (GO; Gene Ontology Consortium, geneontology.org) used two gene sets as inputs—those with differential expression for both the nPM and LPS treatment (SAM results), and those identified as hub genes in modules enriched by both nPM and LPS (WGCNA results). Whereas GO was utilized in SAM to determine only the most enriched responses, GO is utilized here to describe the composition of the module and therefore uses relaxed stringency. Increased and decreased transcripts were considered independently . Pathway figures were generated using Cytoscape with the ClueGo plugin , with enriched processes depicted as nodes, and networks, which are groups of connected nodes.
Genes significant by SAM from each dataset, and shared hub genes from modules enriched by both treatments were analyzed for enriched transcription factor targets (TFTs) using WEB-based Gene Set Analysis Toolkit (WEB-GESTALT); cutoff at p < 0.01. Because TFT analysis makes corrections for false positives, TFT analysis has more power in connected networks (WGCNA modules) versus broad gene lists (SAM results) and can therefore detect greater TFT enrichment in a subset versus complete gene lists.
TLR4 siRNA cultures
Glia were transfected with lipofectamine (10 μL/well media) and TLR4 siRNA (Thermo Fisher Scientific, siRNA ID 198667), or negative control siRNA (Thermo Fisher Scientific, AM4611), combined with Opti-MEM media and added to culture media. For control cultures, only Opti-MEM media was added to culture media. After 48 h, cells were treated with either nPM (10 μg/mL, 24 h) or LPS (100 ng/mL, 24 h), and harvested for RNA (TRIzol) and protein (RIPA buffer).
Scrambled RNA induced JNK1/2 (no change by nPM, 1.6× by scrambled RNA) and STAT1 (4.7× by nPM, 7.4× by scrambled RNA), with no effect on other genes queried. nPM effects were unchanged by scrambled RNA.
Protein concentration was analyzed by the V-PLEX Proinflammatory Panel 2 immunoassay (K15059D-1, Mesoscale Diagnostics, Rockville, MD).
Ordinary one-way analysis of variance test was used, with Tukey’s posttest to correct for multiple comparisons. All analysis used Graphpad Prism 6.
Hierarchical clustering and heatmap generation were performed in MatLab (Version R2014b) to identify the relation of gene expression changes among different groups of this study. Genes were clustered by Pearson correlation coefficients.
Guided by results from microarray analysis, we investigated TLR4 involvement in nPM response by TLR4 knockdown in vitro, and investigated TLR4 activation in the hippocampus following chronic in vivo exposure.
Significance analysis of microarrays (SAM)
Among the RNA responders to LPS and nPM, 530 were shared: 268 increased in both; 223 decreased in both (Fig. 2a–c; q < 0.1). A subset of 39 RNAs had divergent directions of response to nPM and LPS, with 80% increased by nPM. Divergent responses were analyzed by GO (“SAM biological processes analysis by Gene Ontology (GO)”).
Verification by q-PCR
Eight TNFα-associated RNA level changes detected by microarray were confirmed by q-PCR: five increased (Jak2, STAT1, TNFα, TNFRSF9, and TRAFD1) and three non-changers (Fos, TRAF3ip, and TRAF6) (Additional file 2: Figure S1).
SAM biological processes analysis by Gene Ontology (GO)
The top enriched biological processes (20% minimum enrichment) by nPM or LPS were determined from GO.
KEGG pathway analysis corroborated the main GO findings: increased RNAs for enrichment in NF-κB, TLR signaling, and cytokine response; decreased RNAs, for enrichment in DNA replication (not shown).
LPS responses: Increased RNAs yielded 18 enriched nodes, including “response to tumor necrosis factor”, “I-kappaB kinase/NF-kappaB signaling”, “response to oxidative stress”, “reactive oxygen species metabolic process”, “chronic inflammatory response”, “response to interferon gamma”, “nitric oxide biosynthetic process”, and “response to cytokine” (Additional file 2: Figure S1). Unlike nPM GO, LPS had enriched processes for “antigen processing and presentation of peptide antigen” and “reactive nitrogen species metabolic processes”, among others. Decreased RNAs were enriched for “regulation of protein serine/threonine kinase activity” and “response to wounding” (not shown).
Data from prior microarray analysis of LPS-treated BV-2 microglial cells [34, 35] and primary cultured microglia  were also analyzed for GO processes. These datasets showed LPS responses of NF-κB, IFN-y, oxidative stress, and cytokine pathways, corresponding to our results.
Divergence between nPM and LPS: For the 39 RNAs with divergent responses by SAM, identified above (“Significance analysis of microarrays (SAM)” section), one third (15/39) were in the “response to chemical stimulus”.
Weighted gene co-expression network analysis (WGCNA)
In the blue module (increased RNAs), nPM responders had twofold more hub genes (1196/2042) than LPS responders (558/2042). For the shared responses of nPM and LPS, hub genes were 25% (497/2042). The turquoise module (decreased RNAs) with 530 shared hub genes had 2.7-fold more hub genes for nPM (1842/2612) than for LPS (681/2612). The hub genes of the blue and turquoise modules were highly correlated by kME and by fold change (biweight mid-correlation +0.44 for nPM, blue; −0.24 for nPM, turquoise).
WGCNA process analysis by Gene Ontology (GO)
The shared hub genes for both nPM and LPS treatment in the blue module (increased RNAs) enriched similar biological processes as the SAM analysis for nPM treatment (Fig. 3a): “I-kappaB kinase/NF-kappaB signaling”, “TLR signaling pathway”, “JAK-STAT cascade”, “cytokine secretion”, and “response to LPS”, among other processes (Fig. 5a). The shared nodes include genes composing the intracellular TLR4 signaling pathway, components of NF-κB, and downstream inflammatory cytokines like TNFα, IL-1α, and IL-1β. All a priori genes of interest (“Background”) were in the blue (increased) module.
The shared hub genes in both nPM and LPS treatment, of turquoise module (decreased RNAs), were enriched for “DNA replication” (also in Fig. 3b), “regulation of dendritic spine development”, “chromatin assembly or disassembly”, “positive regulation of purine nucleotide biosynthetic process”, and “cellular biogenic amine metabolic process” (Fig. 5b).
Transcription factor DNA binding target (TFT)
Transcription factor target (TFT) analysis
The shared responses showed the largest enrichment of TFTs, with six TFTs for IRFs and five for NF-κB from the RNAs shared by SAM. Analysis by SAM had four and two TFTs for IRF and NF-κB, respectively.
Both IRFs and NF-κB are controlled by intracellular processes following TLR4 activation, suggesting that TLR4 is a mediator of glial responses to nPM and LPS.
TLR4 siRNA experimental manipulations
The siRNA knockdown of TLR4 was confirmed for protein and mRNA. TLR4-siRNA treatment lowered RNA similarly in controls (65%) and nPM (80%) (Fig. 6a). siRNA for TLR4 lowered protein levels by 60% in all groups (Fig. 6b). Scrambled siRNA treatments for TLR4 did not differ from controls (Fig. 6a).
The 30-fold increase of TNFα protein by nPM was blocked by siRNA (−80%) (Fig. 7a). TNFα mRNA was also increased eightfold by nPM, and blocked by siRNA (−80%) (see below). IL-1β protein increased by nPM (5.5×) (Fig. 7b). siRNA treatment induced IL-1β (2.3×), with a modest further induction by nPM (1.3×) (Fig. 7b). IL-6 protein increased 80× by nPM, with reduced induction by nPM in siRNA cultures (3.4×) (Fig. 7c). nPM treatment increased KC 142×, with reduced induction by nPM in siRNA cultures (5.8×) (Fig. 7d).
NF-κB was increased by nPM (2×), with induction blocked by TLR4 siRNA (Fig. 8c). Mentioned above (“Inflammatory proteins”), TNFα was increased 8× by nPM, and blocked by TLR4 siRNA (−80%) (Fig. 8d). TNFR1 mRNA did not respond to nPM or LPS (not shown).
In the JAK/STAT pathway, JAK2 was activated by nPM and LPS (6.1× and 3.7×, respectively), with siRNA blockade (Fig. 8e). STAT1 mRNA was increased by nPM (4.8×) and by LPS (9.1×), and also siRNA blocked (Fig. 8f).
TRIF (Toll/IL-1 receptor domain-containing adaptor protein-inducing IFN-β), of the MyD88-independent endocytosis pathway, was decreased by LPS (0.72×, p < .05) and did not respond to nPM (not shown). IFN-β did not respond to nPM or LPS (not shown). This further confirms the absence of endotoxin activity in our nPM, because the “endocytosis pathway” is a known endotoxin-specific TLR4 response.
Treatment clustering (x-axis): the non-transfected cultures, the control group shows the least similarity to the nPM and LPS groups. The clustering of three TLR4 siRNA groups suggests similar responses. Importantly, on the heat map, the TLR4 siRNA-treated cultures are in the adjacent column to the control group, indicating the siRNA treatment returned RNA to control levels. Gene clustering (y-axis): NF-κB, TLR4, and JAK2, cluster with TLR4.
In vivo nPM exposure
This is the first comprehensive expression analysis of rodent in vitro glial responses to TRAP particulate matter, which shows broad activation of immune and stress pathways in response to nPM, with 2000 transcripts responding. Guided by the expression analysis, we then demonstrated TLR4 knockdown attenuated a subset of inflammatory response to nPM. Finally, we showed that TLR4 and associated TLR4 pathway RNAs were altered in the hippocampus following in vivo nPM exposure.
This is also the first direct comparison of LPS and air pollution PM for gene expression responses. WGCNA in conjunction with SAM was used to show the extensive overlap of inflammatory responses between nPM and LPS. About 25% of the RNAs responding to nPM were shared with LPS responses. The overlap was enriched for inflammatory responses like TLR4, NF-κB, TNFα, and multiple interleukins. Shared responses to nPM and LPS were also enriched in transcription factor targets (TFTs) for NF-κB and IRFs. These findings are consistent with the exacerbation of lung LPS inflammatory responses when combined with PM exposure [53, 54].
Importantly, the shared LPS and nPM responses were not due to endotoxin presence in these nPM samples. The negligible endotoxin activity of the nPM is consistent with findings that the endotoxin contained within PM is mostly bound in large diameter particles (coarse PM) , which are excluded from collection of nPM. Physiologically, the coarse PM are mainly trapped in upper airways.
The nPM and LPS treatments differed 10-fold in the scale of responding RNA modules by WGCNA: nPM treatment enriched 85% (38/45) modules, while LPS enriched only 9% (4/45). This 10-fold greater genomic response to nPM than LPS may be attributed to the greater chemical heterogeneity of the nPM, which includes transition metals, nitrate, sulfate, and water-soluble organic compounds .
Glial activation by air pollution exposure is characterized by cell-specific markers like GFAP (astrocytes) and Iba1 (microglia) [18, 23, 55], and by inflammatory cytokines like TNFα and IL-1α [17, 18, 20, 21]. Our results with mixed glia corroborate the cytokine increases, and extend the responses to new signaling pathways including TLR4, NF-κB, and JAK/STAT, as shown by WCGNA (blue module). The enrichment of transcription factors for NF-κB and IRFs by nPM treatment suggests the important role of TLR4 activation in glial responses to nPM.
The TLR4-dependent glial responses to nPM were shown by TLR4 knockdown in vitro, which attenuated the nPM induction of TNFα and other cytokines. This is best visualized by the heatmap (Fig. 10). Non-transfected control and nPM or LPS-treated cultures were on opposite extremes of the heat map, indicating the least similarity of any conditions. Conversely, TLR4 siRNA cultures treated with nPM or LPS were adjacent to control cultures, indicating highest similarity of any treatment groups. Though both nPM and LPS responses are TLR4 dependent, they function through divergent intracellular TLR4 signaling pathways. LPS activates TLR4 through both the TLR4 receptor endocytosis response to endotoxin, and the MyD88-dependent NF-κB inflammatory pathway. The nPM activated the NF-κB inflammatory response through MyD88-dependent signaling, but not the endocytosis pathway. NF-κB activation leads to increased TNFα, IL-1β, and IL-6 (seen in "Inflammatory Proteins") . In vivo exposure of mice to nPM induced hippocampal RNA changes for TLR4 components of MyD88-dependent NF-κB activation, and the TNFα pathway.
The activation of TLR4 with TNFα induction by nPM has implications for the neurodegenerative and cognitive impact of air pollution exposure (see “Background”). We hypothesize that TLR4 activation in glia is a mediator of neurite atrophy induced in young mice by air pollution PM, assessed as the area of silver-stained neuronal processes . In co-cultures of mixed glia and neonatal neurons, nPM impairs neurite outgrowth, mainly via the TNFα secreted by nPM exposed mixed glia . TLR4-knockout mice showed protection from airway inflammation , giving a rationale for considering neuroprotection by drugs that block TLR4. However, blocking TLR4 in humans, as a therapeutic approach must be considered cautiously, because attenuated TLR4 function, seen in human TLR4 SNP variants, increases the susceptibility to infection .
The direct translocation of nPM into the brain, via the nose, is consistent with the rapid translocation of radiolabeled carbon and manganese ultrafine PM into the brain from the olfactory neurons in the olfactory epithelium [25, 26]. Moreover, we recently showed rapid microglial activation in the olfactory epithelium following nPM exposure, with subsequent cortical neuroinflammation .
Other neurodegenerative conditions also involve TLR4 in glial and neuronal responses . In cerebral ischemia/reperfusion models for stroke injury, HSP70 binds to TLR4, activating MyD88-IRAK-TRAF6 and NF-κB pathways, with downstream induction of TNFα and other cytokines [60, 61], as observed for nPM-LPS responses (Fig. 8). The synergies of cerebral ischemic damage with air pollution, observed clinically and in a rodent model , may now be understood as mediated by the nPM-LPS TLR4 modules described here and the TLR4 role in cerebral ischemia .
The role of TLR4 may extend to pro-amyloidogenic air pollution associations [8, 62–64]. In transgenic mouse AD models, neurodegenerative changes were modulated with varying TLR4 expression [65, 66]. Although no TLR variant has been validated as a risk factor for AD, TLR4-mediated monocyte responses showed individual variations with more than 1000 QTLs . Notably, most of these QTLs involve genes associated with lysosome pathways, consistent with the endosomal associations of nPM-LPS in glial responses. These QTLs may be examined in future studies for SNPs that modify neurotoxic impact of air pollution. We anticipate a broad sharing of inflammatory gene variants that converge on TLR pathways in the neurodegenerative impact of air pollution that accelerates cognitive aging and increases dementia risk.
This in vitro evidence showed TLR4-dependent and independent glial responses to nPM. Knockdown of TLR4 reduced nPM induction of numerous inflammatory cytokines, and attenuated activation of NF-κB and JAK/STAT pathways. Chronic nPM exposure caused TLR4 activation in the hippocampus and increased TNFα, which we hypothesize is a mediator of neurite atrophy in the hippocampus. These results further resolve the mechanisms by which nPM elicits neuroinflammation, and suggest TLR4’s involvement in cognitive impairments from air pollution exposure.
Activator protein 1
BT3B and CNC homology 1
BTB domain and CNC homolog 1
Glyceraldehyde 3-phosphate dehydrogenase
Insulin promoter factor 1
Interleukin 1 receptor-associated kinase 1
Interferon regulatory factor
Janus kinase 2
c-Jun N-terminal kinase
Chemokine (C-X-C motif) ligand 1
Kyoto Encyclopedia of Genes and Genomes
Myeloid differentiation primary response 88
Nuclear factor of activated T cells
Nuclear factor kappa-light-chain-enhancer of activated B cells
Nanoscale particulate matter
Quantitative trait loci
Significance analysis of microarrays
Serum response factor
Signal transducers and activator 1
Transforming growth factor beta-activated kinase 1
Transcription factor target
Toll-like receptor 4
TNFα receptor 1
TNF receptor super family 9
Tumor necrosis factor alpha
Topological overlap matrix
TNF receptor-associated factor 3 interacting protein
TNF receptor-associated factor 6
TNF receptor-associated factor domain 1
Traffic-related air pollution
Toll/IL-1 receptor domain-containing adaptor protein-inducing interferon beta
Weighted gene co-expression network analysis
We thank Jasmine Zhou for statistical advice on the bioinformatics analysis.
This work was supported by the grants to CEF from the National Institute of Aging R21 AG-040753, R21 AG-050201) and the Cure Alzheimer’s Fund and T32AG0037 supporting NCW. These funding bodies had no role in interpreting the data or writing the article.
Availability of data and materials
Datasets of this study are available as raw data files in the Additional file 1 and will be made available on the Gene Expression Omnibus (GEO) database.
NCW carried out the experiments and data analysis and draft the manuscript. MEL performed microarray data analysis. AH performed data analysis and draft figures. FS and AS contributed to the collection, extraction, and chemical characterization of the nPM samples. CS contributed the nPM samples and designed the nPM collection. TEM participated in the design of studies and manuscript writing. CEF conceived the study, guided the experimental design, and edited the drafts. All authors read and approved the final manuscript.
The authors declare that they have no competing interests.
Consent for publication
This study did not include human participants or human subject-derived data. Animal protocols were approved by the University of Southern California Institutional Animal Care and Use Committee.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Open AccessThis article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.
- Power MC, Weisskopf MG, Alexeeff SE, Coull BA, Spiro 3rd A, Schwartz J. Traffic-related air pollution and cognitive function in a cohort of older men. Environ Health Perspect. 2011;119:682–7.View ArticlePubMedGoogle Scholar
- Ranft U, Schikowski T, Sugiri D, Krutmann J, Kramer U. Long-term exposure to traffic-related particulate matter impairs cognitive function in the elderly. Environ Res. 2009;109:1004–11.View ArticlePubMedGoogle Scholar
- Wellenius GA, Boyle LD, Coull BA, Milberg WP, Gryparis A, Schwartz J, Mittleman MA, Lipsitz LA. Residential proximity to nearest major roadway and cognitive function in community-dwelling seniors: results from the MOBILIZE Boston Study. J Am Geriatr Soc. 2012;60:2075–80.PubMedPubMed CentralGoogle Scholar
- Zeng Y, Gu D, Purser J, Hoenig H, Christakis N. Associations of environmental factors with elderly health and mortality in China. Am J Public Health. 2010;100:298–305.View ArticlePubMedPubMed CentralGoogle Scholar
- Wu Y-C, Lin Y-C, Yu H-L, Chen J-H, Chen T-F, Sun Y, Wen L-L, Yip P-K, Chu Y-M, Chen Y-C. Association between air pollutants and dementia risk in the elderly. Alzheimers Dement (Amst). 2015;1:220–8.PubMed CentralGoogle Scholar
- Oudin A, Forsberg B, Adolfsson AN, Lind N, Modig L, Nordin M, Nordin S, Adolfsson R, Nilsson LG. Traffic-related air pollution and dementia incidence in northern Sweden: a longitudinal study. Environ Health Perspect. 2016;124:306–12.PubMedGoogle Scholar
- Jung CR, Lin YT, Hwang BF. Ozone, particulate matter, and newly diagnosed Alzheimer’s disease: a population-based cohort study in Taiwan. J Alzheimers Dis. 2015;44:573–84.PubMedGoogle Scholar
- Cacciottolo M, Wang X, Driscoll I, Woodward N, Saffari A, Reyes J, Serre ML, Vizuete W, Sioutas C, Morgan TE, et al. Particulate air pollutants, APOE alleles, and their contributions to cognitive impairment in older women and to amyloidogenesis in experimental models. Transl Psychiatry. 2016. In Press.
- Ailshire J, Crimmins EM. Fine particulate matter air pollution and cognitive function among older US adults. 2014.Google Scholar
- Ailshire JA, Clarke P. Fine particulate matter air pollution and cognitive function among U.S. older adults.
- Perera FP, Tang DL, Wang S, Vishnevetsky J, Zhang BZ, Diaz D, Camann D, Rauh V. Prenatal polycyclic aromatic hydrocarbon (PAH) exposure and child behavior at age 6-7 years. Environ Health Perspect. 2012;120:921–6.View ArticlePubMedPubMed CentralGoogle Scholar
- Peterson BS, Rauh VA, Bansal R, Hao X, Toth Z, Nati G, Walsh K, Miller RL, Arias F, Semanek D, Perera F. Effects of prenatal exposure to air pollutants (polycyclic aromatic hydrocarbons) on the development of brain white matter, cognition, and behavior in later childhood. JAMA Psychiatry. 2015;72:531–40.View ArticlePubMedPubMed CentralGoogle Scholar
- Chen JC, Wang X, Wellenius GA, Serre ML, Driscoll I, Casanova R, McArdle JJ, Manson JE, Chui HC, Espeland MA. Ambient air pollution and neurotoxicity on brain structure: evidence from women’s health initiative memory study. Ann Neurol. 2015;78:466–76.View ArticlePubMedPubMed CentralGoogle Scholar
- Casanova R, Wang X, Reyes J, Akita Y, Serre ML, Vizuete W, Chui HC, Driscoll I, Resnick SM, Espeland MA, et al. A voxel-based morphometry study reveals local brain structural alterations associated with ambient fine particles in older women. Front Hum Neurosci. 2016;10:495.View ArticlePubMedPubMed CentralGoogle Scholar
- Calderon-Garciduenas L, Engle R, Mora-Tiscareno A, Styner M, Gomez-Garza G, Zhu H, Jewells V, Torres-Jardon R, Romero L, Monroy-Acosta ME, et al. Exposure to severe urban air pollution influences cognitive outcomes, brain volume and systemic inflammation in clinically healthy children. Brain Cogn. 2011;77:345–55.View ArticlePubMedGoogle Scholar
- Calderon-Garciduenas L, Solt AC, Henriquez-Roldan C, Torres-Jardon R, Nuse B, Herritt L, Villarreal-Calderon R, Osnaya N, Stone I, Garcia R, et al. Long-term air pollution exposure is associated with neuroinflammation, an altered innate immune response, disruption of the blood-brain barrier, ultrafine particulate deposition, and accumulation of amyloid beta-42 and alpha-synuclein in children and young adults. Toxicol Pathol. 2008;36:289–310.View ArticlePubMedGoogle Scholar
- Fonken LK, Xu X, Weil ZM, Chen G, Sun Q, Rajagopalan S, Nelson RJ. Air pollution impairs cognition, provokes depressive-like behaviors and alters hippocampal cytokine expression and morphology. Mol Psychiatry. 2011;16:987–95. 973.View ArticlePubMedPubMed CentralGoogle Scholar
- Morgan TE, Davis DA, Iwata N, Tanner JA, Snyder D, Ning Z, Kam W, Hsu YT, Winkler JW, Chen JC, et al. Glutamatergic neurons in rodent models respond to nanoscale particulate urban air pollutants in vivo and in vitro. Environ Health Perspect. 2011;119:1003–9.View ArticlePubMedPubMed CentralGoogle Scholar
- Mumaw CL, Levesque S, McGraw C, Robertson S, Lucas S, Stafflinger JE, Campen MJ, Hall P, Norenberg JP, Anderson T, et al. Microglial priming through the lung-brain axis: the role of air pollution-induced circulating factors. Faseb Journal. 2016;30:1880–91.View ArticlePubMedGoogle Scholar
- Levesque S, Taetzsch T, Lull ME, Kodavanti U, Stadler K, Wagner A, Johnson JA, Duke L, Kodavanti P, Surace MJ, Block ML. Diesel exhaust activates and primes microglia: air pollution, neuroinflammation, and regulation of dopaminergic neurotoxicity. Environ Health Perspect. 2011;119:1149–55.View ArticlePubMedPubMed CentralGoogle Scholar
- Campbell A, Oldham M, Becaria A, Bondy SC, Meacher D, Sioutas C, Misra C, Mendez LB, Kleinman A. Particulate matter in polluted air may increase biomarkers of inflammation in mouse brain. Neurotoxicology. 2005;26:133–40.View ArticlePubMedGoogle Scholar
- Zhang H, Liu H, Davies KJ, Sioutas C, Finch CE, Morgan TE, Forman HJ. Nrf2-regulated phase II enzymes are induced by chronic ambient nanoparticle exposure in young mice with age-related impairments. Free Radic Biol Med. 2012;52:2038–46.View ArticlePubMedPubMed CentralGoogle Scholar
- Cheng H, Saffari A, Sioutas C, Forman HJ, Morgan TE, Finch CE. Nano-Scale Particulate Matter from Urban Traffic Rapidly Induces Oxidative Stress and Inflammation in Olfactory Epithelium with Concomitant Effects on Brain. Environ Health Perspect. 2016.
- Li N, Sioutas C, Cho A, Schmitz D, Misra C, Sempf J, Wang M, Oberley T, Froines J, Nel A. Ultrafine particulate pollutants induce oxidative stress and mitochondrial damage. Environ Health Perspect. 2003;111:455–60.View ArticlePubMedPubMed CentralGoogle Scholar
- Elder A, Gelein R, Silva V, Feikert T, Opanashuk L, Carter J, Potter R, Maynard A, Ito Y, Finkelstein J, Oberdorster G. Translocation of inhaled ultrafine manganese oxide particles to the central nervous system. Environ Health Perspect. 2006;114:1172–8.View ArticlePubMedPubMed CentralGoogle Scholar
- Oberdorster G, Sharp Z, Atudorei V, Elder A, Gelein R, Kreyling W, Cox C. Translocation of inhaled ultrafine particles to the brain. Inhal Toxicol. 2004;16:437–45.View ArticlePubMedGoogle Scholar
- Cheng H, Davis DA, Hasheminassab S, Sioutas C, Morgan TE, Finch CE. Urban traffic-derived nanoparticulate matter reduces neurite outgrowth via TNFalpha in vitro. J Neuroinflammation. 2016;13:19.View ArticlePubMedPubMed CentralGoogle Scholar
- Shoenfelt J, Mitkus RJ, Zeisler R, Spatz RO, Powell J, Fenton MJ, Squibb KA, Medvedev AE. Involvement of TLR2 and TLR4 in inflammatory immune responses induced by fine and coarse ambient air particulate matter. J Leukoc Biol. 2009;86:303–12.View ArticlePubMedPubMed CentralGoogle Scholar
- Becker S, Fenton MJ, Soukup JM. Involvement of microbial components and toll-like receptors 2 and 4 in cytokine responses to air pollution particles. Am J Respir Cell Mol Biol. 2002;27:611–8.View ArticlePubMedGoogle Scholar
- Molteni M, Gemma S, Rossetti C. The role of toll-like receptor 4 in infectious and noninfectious inflammation. Mediators Inflamm. 2016;2016:6978936.View ArticlePubMedPubMed CentralGoogle Scholar
- Tahara K, Kim HD, Jin JJ, Maxwell JA, Li L, Fukuchi K. Role of toll-like receptor signalling in Abeta uptake and clearance. Brain. 2006;129:3006–19.View ArticlePubMedPubMed CentralGoogle Scholar
- den Hartigh LJ, Lame MW, Ham W, Kleeman MJ, Tablin F, Wilson DW. Endotoxin and polycyclic aromatic hydrocarbons in ambient fine particulate matter from Fresno, California initiate human monocyte inflammatory responses mediated by reactive oxygen species. Toxicol In Vitro. 2010;24:1993–2002.View ArticleGoogle Scholar
- Mueller-Anneling L, Avol E, Peters JM, Thorne PS. Ambient endotoxin concentrations in PM10 from Southern California. Environ Health Perspect. 2004;112:583–8.View ArticlePubMedPubMed CentralGoogle Scholar
- Juknat A, Pietr M, Kozela E, Rimmerman N, Levy R, Gao F, Coppola G, Geschwind D, Vogel Z. Microarray and pathway analysis reveal distinct mechanisms underlying cannabinoid-mediated modulation of LPS-induced activation of BV-2 microglial cells. PLoS One. 2013;8:e61462.View ArticlePubMedPubMed CentralGoogle Scholar
- Hwang SH, Choi YG, Jeong MY, Hong YM, Lee JH, Lim S. Microarray analysis of gene expression profile by treatment of Cinnamomi Ramulus in lipopolysaccharide-stimulated BV-2 cells. Gene. 2009;443:83–90.View ArticlePubMedGoogle Scholar
- Holtman IR, Raj DD, Miller JA, Schaafsma W, Yin Z, Brouwer N, Wes PD, Moller T, Orre M, Kamphuis W, et al. Induction of a common microglia gene expression signature by aging and neurodegenerative conditions: a co-expression meta-analysis. Acta Neuropathol Commun. 2015;3:31.View ArticlePubMedPubMed CentralGoogle Scholar
- DiLeo MV, Strahan GD, den Bakker M, Hoekenga OA. Weighted correlation network analysis (WGCNA) applied to the tomato fruit metabolome. PLoS One. 2011;6:e26683.View ArticlePubMedPubMed CentralGoogle Scholar
- Misra C, Kim S, Shen S, Sioutas C. A high flow rate, very low pressure drop impactor for inertial separation of ultrafine from accumulation mode particles. J Aerosol Sci. 2002;33:735–52.View ArticleGoogle Scholar
- Ning Z, Geller MD, Moore KF, Sheesley R, Schauer JJ, Sioutas C. Daily variation in chemical characteristics of urban ultrafine aerosols and inference of their sources. Environ Sci Technol. 2007;41:6000–6.View ArticlePubMedGoogle Scholar
- Liu QH, Babadjouni R, Radwanski R, Cheng H, Patel A, Hodis DM, He SH, Baumbacher P, Russin JJ, Morgan TE, et al. Stroke damage is exacerbated by nano-size particulate matter in a mouse model. Plos One. 2016;11:e0153376.View ArticlePubMedPubMed CentralGoogle Scholar
- Sardar SB, Fine PM, Mayo PR, Sioutas C. Size-fractionated measurements of ambient ultrafine particle chemical composition in Los Angeles using the NanoMOUDI. Environ Sci Technol. 2005;39:932–44.View ArticlePubMedGoogle Scholar
- Holm TH, Draeby D, Owens T. Microglia are required for astroglial Toll-like receptor 4 response and for optimal TLR2 and TLR3 response. Glia. 2012;60:630–8.View ArticlePubMedGoogle Scholar
- Pascual O, Ben Achour S, Rostaing P, Triller A, Bessis A. Microglia activation triggers astrocyte-mediated modulation of excitatory neurotransmission. Proc Natl Acad Sci U S A. 2012;109:E197–205.View ArticlePubMedGoogle Scholar
- Irizarry RA, Bolstad BM, Collin F, Cope LM, Hobbs B, Speed TP. Summaries of Affymetrix GeneChip probe level data. Nucleic Acids Res. 2003;31:e15.View ArticlePubMedPubMed CentralGoogle Scholar
- Bolstad BM, Irizarry RA, Astrand M, Speed TP. A comparison of normalization methods for high density oligonucleotide array data based on variance and bias. Bioinformatics. 2003;19:185–93.View ArticlePubMedGoogle Scholar
- Irizarry RA, Hobbs B, Collin F, Beazer-Barclay YD, Antonellis KJ, Scherf U, Speed TP. Exploration, normalization, and summaries of high density oligonucleotide array probe level data. Biostatistics. 2003;4:249–64.View ArticlePubMedGoogle Scholar
- Langfelder P, Horvath S: WGCNA: an R package for weighted correlation network analysis. BMC Bioinformatics. 2008;9:559.View ArticlePubMedPubMed CentralGoogle Scholar
- Zhang B, Horvath S. A general framework for weighted gene co-expression network analysis. Stat Appl Genet Mol Biol. 2005;4:17.Google Scholar
- Yip AM. The Generalized Topological OVerlap Matrix for Detecting Modules in Gene Networks. BIOCOMP. 2006.
- Hong G, Zhang W, Li H, Shen X, Guo Z. Separate enrichment analysis of pathways for up- and downregulated genes. J R Soc Interface. 2014;11:20130950.View ArticlePubMedPubMed CentralGoogle Scholar
- Bindea G, Mlecnik B, Hackl H, Charoentong P, Tosolini M, Kirilovsky A, Fridman WH, Pages F, Trajanoski Z, Galon J. ClueGO: a Cytoscape plug-in to decipher functionally grouped gene ontology and pathway annotation networks. Bioinformatics. 2009;25:1091–3.View ArticlePubMedPubMed CentralGoogle Scholar
- Lehnardt S, Lachance C, Patrizi S, Lefebvre S, Follett PL, Jensen FE, Rosenberg PA, Volpe JJ, Vartanian T. The toll-like receptor TLR4 is necessary for lipopolysaccharide-induced oligodendrocyte injury in the CNS. J Neurosci. 2002;22:2478–86.PubMedGoogle Scholar
- Xiong Q, Ru Q, Chen L, Yue K, Tian X, Ma B, Liu L, Wu R, Xu C, Pi M, Li C. Combined effects of fine particulate matter and lipopolysaccharide on apoptotic responses in NR8383 macrophages. J Toxicol Environ Health A. 2015;78:443–52.View ArticlePubMedGoogle Scholar
- Inoue K, Takano H, Sakurai M, Oda T, Tamura H, Yanagisawa R, Shimada A, Yoshikawa T. Pulmonary exposure to diesel exhaust particles enhances coagulatory disturbance with endothelial damage and systemic inflammation related to lung inflammation. Exp Biol Med (Maywood). 2006;231:1626–32.Google Scholar
- Kleinman MT, Araujo JA, Nel A, Sioutas C, Campbell A, Cong PQ, Lia H, Bondy SC. Inhaled ultrafine particulate matter affects CNS inflammatory processes and may act via MAP kinase signaling pathways. Toxicol Lett. 2008;178:127–30.View ArticlePubMedPubMed CentralGoogle Scholar
- Tak PP, Firestein GS. NF-kappaB: a key role in inflammatory diseases. J Clin Invest. 2001;107:7–11.View ArticlePubMedPubMed CentralGoogle Scholar
- Gabehart K, Correll KA, Loader JE, White CW, Dakhama A. The lung response to ozone is determined by age and is partially dependent on toll-Like receptor 4. Respir Res. 2015;16:117.
- Ferwerda B, McCall MB, Verheijen K, Kullberg BJ, van der Ven AJ, Van der Meer JW, Netea MG. Functional consequences of toll-like receptor 4 polymorphisms. Mol Med. 2008;14:346–52.View ArticlePubMedPubMed CentralGoogle Scholar
- Wang Y, Ge P, Zhu Y. TLR2 and TLR4 in the brain injury caused by cerebral ischemia and reperfusion. Mediators Inflamm. 2013;2013:124614.PubMedPubMed CentralGoogle Scholar
- Wang YJ, Chen G, Yu XD, Li YC, Zhang L, He ZZ, Zhang NN, Yang XP, Zhao YS, Li N, Qiu H. Salvianolic acid B ameliorates cerebral ischemia/reperfusion injury through inhibiting TLR4/MyD88 signaling pathway. Inflammation. 2016;39:1503–13.View ArticlePubMedGoogle Scholar
- Brea D, Blanco M, Ramos-Cabrer P, Moldes O, Arias S, Perez-Mato M, Leira R, Sobrino T, Castillo J. Toll-like receptors 2 and 4 in ischemic stroke: outcome and therapeutic values. J Cereb Blood Flow Metab. 2011;31:1424–31.View ArticlePubMedPubMed CentralGoogle Scholar
- Kim SH, Knight EM, Saunders EL, Cuevas AK, Popovech M, Chen LC, Gandy S. Rapid doubling of Alzheimer’s amyloid-beta40 and 42 levels in brains of mice exposed to a nickel nanoparticle model of air pollution. F1000Res. 2012;1:70.PubMedPubMed CentralGoogle Scholar
- Block ML, Calderon-Garciduenas L. Air pollution: mechanisms of neuroinflammation and CNS disease. Trends Neurosci. 2009;32:506–16.View ArticlePubMedPubMed CentralGoogle Scholar
- Walter S, Letiembre M, Liu Y, Heine H, Penke B, Hao W, Bode B, Manietta N, Walter J, Schulz-Schuffer W, Fassbender K. Role of the toll-like receptor 4 in neuroinflammation in Alzheimer’s disease. Cell Physiol Biochem. 2007;20:947–56.View ArticlePubMedGoogle Scholar
- Jin JJ, Kim HD, Maxwell JA, Li L, Fukuchi K. Toll-like receptor 4-dependent upregulation of cytokines in a transgenic mouse model of Alzheimer’s disease. J Neuroinflammation. 2008;5:23.View ArticlePubMedPubMed CentralGoogle Scholar
- Qin Y, Liu Y, Hao W, Decker Y, Tomic I, Menger MD, Liu C, Fassbender K. Stimulation of TLR4 attenuates Alzheimer’s disease-related symptoms and pathology in tau-transgenic mice. J Immunol. 2016;197(8):3281-3292.
- Kim S, Becker J, Bechheim M, Kaiser V, Noursadeghi M, Fricker N, Beier E, Klaschik S, Boor P, Hess T, et al. Characterizing the genetic basis of innate immune response in TLR4-activated human monocytes. Nat Commun. 2014;5:5236.View ArticlePubMedGoogle Scholar