Jørn A. Holme

Differences in cytotoxicity versus pro-inflammatory potency of different PM fractions in human epithelial lung cells

Air pollution in Milan causes health concern due to the high concentrations of particulate matter (PM10 and PM2.5). The aim of this study was to investigate possible seasonal differences in PM10 and PM2.5 chemical composition and their biological effects on pro-inflammatory cytokine release and cytotoxicity. The PM was sampled during winter and summer seasons. The winter PMs had higher levels of PAHs than the summer samples which contained a greater amount of mineral dust elements. The PM toxicity was tested in the human pulmonary epithelial cell lines BEAS-2B and A549. The winter PMs were more cytotoxic than summer samples, whereas the summer PM10 exhibited a higher pro-inflammatory potential, as measured by ELISA. This inflammatory potential seemed partly due to biological components such as bacterial lipopolysaccharides (LPS), as evaluated by the use of Polymixin B. Interestingly, in the BEAS-2B cells the winter PM2.5 reduced proliferation due to a mitotic delay/arrest, while no such effects were observed in the A549 cells. These results underline that the in vitro responsiveness to PM may be cell line dependent and suggest that the PM different properties may trigger different endpoints such as inflammation, perturbation of cell cycle and cell death.

Cytotoxic effects of N-acetyl-p-benzoquinone imine, a common arylating intermediate of paracetamol and N-hydroxyparacetamol

The cytotoxic effects of N-acetyl-p-benzoquinone imine (NAPQI), a postulated ultimate reactive metabolite of paracetamol (pHAA), was studied in suspensions of isolated rat hepatocytes. Incubation of cells for 10-300 min with 0.1-0.5 mM NAPQI led to concentration dependent cell damage, as determined by increased trypan blue exclusion, lactate dehydrogenase release and glutathione (GSH) depletion. NAPQI and N-hydroxyparacetamol (N-OH-pHAA), a postulated proximate metabolite of pHAA, caused cytotoxic effects in the same concentration range. In contrast, no toxic effects of pHAA (less than or equal to 20 mM) could be demonstrated. With the short half-life of NAPQI, less than 0.5% of the NAPQI added is expected to be left in the incubation medium after a 2 min incubated period. Nevertheless, 10-120 min (depending on the concentration of NAPQI) elapsed before the cells responded with increased membrane permeability. Clearly, the initial damage caused by NAPQI must be followed by subsequent cellular steps before toxicity becomes apparent. The addition of N-acetylcysteine, GSH or ascorbate during the NAPQI exposure period fully protected the hepatocytes from NAPQI damage. Lesser effects were demonstrated when these agents were added after the 5 min NAPQI exposure period. The results presented in this study further support the hypothesis that NAPQI is the ultimate reactive formed from pHAA.

Recent Advances in Particulate Matter and Nanoparticle Toxicology: A Review of the In Vivo and In Vitro Studies

Epidemiological and clinical studies have linked exposure to particulate matter (PM) to adverse health effects, which may be registered as increased mortality and morbidity from various cardiopulmonary diseases. Despite the evidence relating PM to health effects, the physiological, cellular, and molecular mechanisms causing such effects are still not fully characterized. Two main approaches are used to elucidate the mechanisms of toxicity. One is the use of in vivo experimental models, where various effects of PM on respiratory, cardiovascular, and nervous systems can be evaluated. To more closely examine the molecular and cellular mechanisms behind the different physiological effects, the use of various in vitro models has proven to be valuable. In the present review, we discuss the current advances on the toxicology of particulate matter and nanoparticles based on these techniques.

Comparison of non-crystalline silica nanoparticles in IL-1β release from macrophages

BackgroundRespirable crystalline silica (silicon dioxide; SiO2, quartz) particles are known to induce chronic inflammation and lung disease upon long-term inhalation, whereas non-crystalline (amorphous) SiO2 particles in the submicrometre range are regarded as less harmful. Several reports have demonstrated that crystalline, but also non-crystalline silica particles induce IL-1β release from macrophages via the NALP3-inflammasome complex (caspase-1, ASC and NALP3) in the presence of lipopolysaccharide (LPS) from bacteria. Our aim was to study the potential of different non-crystalline SiO2 particles from the nano- to submicro-sized range to activate IL-1β responses in LPS-primed RAW264.7 macrophages and primary rat lung macrophages. The role of the NALP3-inflammasome and up-stream mechanisms was further explored in RAW264.7 cells.ResultsIn the present study, we have shown that 6 h exposure to non-crystalline SiO2 particles in nano- (SiNPs, 5–20 nm, 50 nm) and submicro-sizes induced strong IL-1β responses in LPS-primed mouse macrophages (RAW264.7) and primary rat lung macrophages. The primary lung macrophages were more sensitive to Si-exposure than the RAW-macrophages, and responded more strongly. In the lung macrophages, crystalline silica (MinUsil 5) induced IL-1β release more potently than the non-crystalline Si50 and Si500, when adjusted to surface area. This difference was much less pronounced versus fumed SiNPs. The caspase-1 inhibitor zYVAD and RNA silencing of the NALP3 receptor reduced the particle-induced IL-1β release in the RAW264.7 macrophages. Furthermore, inhibitors of phagocytosis, endosomal acidification, and cathepsin B activity reduced the IL-1β responses to the different particles to a similar extent.ConclusionsIn conclusion, non-crystalline silica particles in the nano- and submicro-size ranges seemed to induce IL-1β release from LPS-primed RAW264.7 macrophages via similar mechanisms as crystalline silica, involving particle uptake, phagosomal leakage and activation of the NALP3 inflammasome. Notably, rat primary lung macrophages were more sensitive with respect to silica-induced IL-1β release. The differential response patterns obtained suggest that silica-induced IL-1β responses not only depend on the particle surface area, but on factors and/or mechanisms such as particle reactivity or particle uptake. These findings may suggest that bacterial infection via LPS may augment acute inflammatory effects of non-crystalline as well as crystalline silica particles.

Differential effects of nitro-PAHs and amino-PAHs on cytokine and chemokine responses in human bronchial epithelial BEAS-2B cells

Nitro-polycyclic aromatic hydrocarbons (nitro-PAHs) are found in diesel exhaust and air pollution particles. Along with other PAHs, many nitro-PAHs possess mutagenic and carcinogenic properties, but their effects on pro-inflammatory processes and cell death are less known. In the present study we examined the effects of 1-nitropyrene (1-NP), 3-nitrofluoranthene (3-NF) and 3-nitrobenzanthrone (3-NBA) and their corresponding amino forms, 1-AP, 3-AF and 3-ABA, in human bronchial epithelial BEAS-2B cells. The effects of the different nitro- and amino-PAHs were compared to the well-characterized PAH benzo[a]pyrene (B[a]P). Expression of 17 cytokine and chemokine genes, measured by real-time PCR, showed that 1-NP and 3-NF induced a completely different cytokine/chemokine gene expression pattern to that of their amino analogues. 1-NP/3-NF-induced responses were dominated by maximum effects on CXCL8 (IL-8) and TNF-alpha expression, while 1-AP-/3-AF-induced responses were dominated by CCL5 (RANTES) and CXCL10 (IP-10) expression. 3-NBA and 3-ABA induced only marginal cytokine/chemokine responses. However, 3-NBA exposure induced considerable DNA damage resulting in accumulation of cells in S-phase and a marked increase in apoptosis. B[a]P was the only compound to induce expression of aryl hydrocarbon receptor (AhR)-regulated genes, such as CYP1A1 and CYP1B1, but did not induce cytokine/chemokine responses in BEAS-2B cells. Importantly, nitro-PAHs and amino-PAHs induced both qualitatively and quantitatively different effects on cytokine/chemokine expression, DNA damage, cell cycle alterations and cytotoxicity. The cytokine/chemokine responses appeared to be triggered, at least partly, through mechanisms separate from the other examined endpoints. These results confirm and extend previous studies indicating that certain nitro-PAHs have a considerable pro-inflammatory potential.

Genotoxic effects of the drinking water mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX) in mammalian cells in vitro and in rats in vivo

The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]- furanone) (MX), which is formed during chlorination of drinking water and accounts for about one third of the Ames mutagenicity of tap water, has been studied with respect to its genotoxicity in vitro and in vivo. Treatment with 30-300 microM MX (1 h) induced DNA damage in a concentration-dependent manner in suspensions of rat hepatocytes, as measured by an automated alkaline elution system. The effect was similar in hepatocytes from PCB-induced and uninduced rats. DNA damage was induced in V79 Chinese hamster cells and in isolated rat testicular cells, at the same concentration level as in hepatocytes. Pretreating testicular cells with diethylmaleate, which depletes 85% of cellular glutathione, had no significant effect on the DNA damage induced by MX. The treatment conditions used in the alkaline elution experiments were not cytotoxic to any of the cell types used, as determined by trypan blue exclusion. V79 cells exposed to 2-5 microM MX (2 h) showed an increased frequency of sister-chromatid exchanges (SCE) whereas no significant effect on HGPRT mutation induction was observed. Higher concentrations (greater than 10 microM, 2 h) apparently blocked cell division. The data indicate that MX can react directly with DNA or that MX is metabolized to an ultimate mutagen via some enzyme which is common in mammalian cells. The in vivo experiments showed no evidence of genotoxicity after intraperitoneal (18 mg/kg, 1 h) or oral (18, 63 or 125 mg/kg, 1 h) administration of MX, as measured by alkaline elution, in any of the following organs: the pyloric part of the stomach, the duodenum, colon ascendens, liver, kidney, lung, bone marrow, urinary bladder and the testes. In conclusion, MX is a direct-acting genotoxicant in vitro but no in vivo genotoxicity was detected.

Genotoxicity studies with paracetamol.

Paracetamol and its major ultimate reactive metabolite, N-acetyl-p-benzoquinone imine (NAPQI) were studied for their genotoxic potential. Neither paracetamol nor NAPQI were found to cause mutations in Salmonella typhimurium, whereas NAPQI was severely cytotoxic to the bacteria. Radiolabelled paracetamol was found to bind covalently to DNA added to mouse-liver microsomal incubations at a rate of 2.6 pmoles/mg DNA/min. Paracetamol also bound covalently to hepatic DNA at a level of 15 pmoles/mg DNA after a hepatotoxic dose of paracetamol to mice. NAPQI caused extensive DNA single-strand breaks as evidenced by alkaline elution of DNA from treated Reuber hepatoma cells. This effect occurred at concentrations which later resulted in cytotoxicity. Paracetamol was shown to induce increased DNA-repair synthesis in isolated mouse-liver cells in monolayer culture, at concentrations where also cytotoxicity was evident. Increased DNA-repair synthesis occurred at lower paracetamol concentrations in cells isolated from mice pretreated with phenobarbital. Taken together, these data show that paracetamol can cause DNA interaction leading to damage at levels which are cytotoxic.

Brominated phenols: characterization of estrogen-like activity in the human breast cancer cell-line MCF-7.

A large number of halogenated phenols are detected in the blood of humans, fish and wild-animals. We have characterized the estrogen-like activity of phenol, 4-bromophenol (4-BP), 2,4-dibromophenol (2,4-DBP), 2,4,6-tribromophenol (2,4,6-TBP) and 4-tert-butylphenol (tert-BP) using the estrogen-dependent human breast cancer cell line MCF-7. 4-BP, 2,4-DBP and 4-tert-BP all bind to the estrogen receptor (ER) with approximately 10,000-fold less affinity than 17 beta-estradiol (17 beta-E). 2,4,6-TBP was only able to displace 43% of radiolabelled estrogen when tested at concentrations up to 1 microM, whereas phenol had no affinity for the ER. 4-tert-BP stimulated cell growth and induced estrogen-regulated proteins such as the progesterone receptor (PgR) and pS2. The brominated phenols, however, although binding to the ER, did not stimulate cell growth or increase the levels of the PgR or pS2, or reduce the level of 17 beta-E induced pS2. On the contrary, 4-BP, 2,4-DBP and partly 4-tert-BP reduced 17 beta-E-stimulated cell growth apparently by an ER independent mechanism.

A COMPARATIVE STUDY OF CHEMICALLY INDUCED DNA DAMAGE IN ISOLATED HUMAN AND RAT TESTICULAR CELLS

Testicular cells prepared from human organ transplant donors or from Wistar rats were used to compare 15 known reproductive toxicants with respect to their ability to induce DNA damage, measured as single-strand DNA breaks and alkali labile sites (ssDNA breaks) with alkaline filter elution. The compounds tested included various categories of chemicals (i.e., pesticides, industrial chemicals, cytostatics, and mycotoxins) most of which are directly acting genotoxicants (i.e., reacting with DNA either spontaneously or via metabolic activation). In addition, a few indirect genotoxic and nongenotoxic reproductive toxicants were included. Six of the chemicals induced no significant levels of ssDNA breaks in human and rat testicular cells; methoxychlor (10 to 100 microM, human and rat), benomyl (10 to 100 microM, human and rat), thiotepa (10 to 1000 microM, human and rat), cisplatin (30 to 1000 microM, human; 100 to 1000 microM, rat), Cd2+ (30 to 1000 microM, human; 100 to 1000 microM, rat), and acrylonitrile (30 to 1000 microM, human; 30 to 300 microM, rat). Four chemicals induced significant levels of ssDNA breaks in testicular cells from both species: styrene oxide (> or = 100 microM, rat and human), 1,2-dibromoethane (EDB) (> or = 100 microM, rat; 1000 microM human), thiram (> or = 30 microM, rat; > or = 100 microM, human), and chlordecone (300 microM, rat; > or = 300 microM, human). Finally, five chemicals induced ssDNA breaks in one of the two species. Four chemicals induced significant ssDNA breaks in rat testicular cells only: 1,2-dibromo-3-chloropropane (DBCP) (> or = 10 microM), 1,3-dinitrobenzene (1,3-DNB) (> or = 300 microM), Cr6+ (1000 microM), and aflatoxin B1 (> or = 100 microM), the last two of these produced only a minor positive response. One chemical, acrylamide, induced a marginal increase in ssDNA breaks in human at 1000 microM, but not in rat testicular cells. Although based on a limited number of donors, the data indicate a close correlation between the induction of DNA damage in human and rat testicular cells in vitro. For some chemicals, however, there appears to be differences in the susceptibility to chemically induced ssDNA breaks of isolated testicular cells from the two species. The data indicate that the parallel use of human and rat testicular cells provides a valuable tool in the assessment of human testicular toxicity.

An automated alkaline elution system: DNA damage induced by 1,2-dibromo-3-chloropropane in vivo and in vitro

An automated alkaline elution system for the detection of DNA damage has been developed. After manual application of samples, which is completed within 5 min, the subsequent supply of liquids, changes in flow rates, and temperature are controlled automatically. The system operates 16 filters and may easily be expanded. The sensitivity of the fluorometric DNA determinations with the Hoechst 33258 dye is increased by using an elution buffer (20 mM Na2EDTA, pH 12.50) with low background fluorescence. DNA is determined using an automated setup similar to the one recently presented by Sterzel et al. (1985, Anal. Biochem. 147, 462-467). The most significant modification is the use of a neutralization buffer which allows variations in the pH of eluted fractions. This change increases the sensitivity of the DNA measurements. The automated alkaline elution system was evaluated using the nematocide 1,2-dibromo-3-chloropropane (DBCP) in a study of its genotoxic effects in the testes and the kidneys. Significant DNA damage was induced in testicular cells by 2.5 microM DBCP (1 h) in vitro and 85 mumol/kg DBCP ip (3 h) in vivo. The damage appeared after short treatment times (10 min in vivo). Variations in the observed DBCP response in vivo were largely due to interanimal variations. The automated alkaline elution system proved to be a sensitive assay also for the detection of DNA damage in kidney nuclei prepared from rats exposed to DBCP. Provided that kidney nuclei from untreated rats, mice, or hamster were kept ice-cold until lysing, 85-100% of their DNA was retained after 16 h of elution, indicating highly intact DNA. Under the same conditions, guinea pig DNA was rapidly degraded unless the nuclei were prepared in a buffer with a higher concentration of Na2EDTA (20 mM).