|
|
||||||||
VASCULAR BIOLOGY
Department of Epidemiology, Research Institute, National Cardiovascular Center, Suita, Osaka, Japan
Submitted 27 September 2005 ; accepted in final form 4 January 2006
| ABSTRACT |
|---|
|
|
|---|
nanomaterials; ubiquitin proteasome; autophagy; atherosclerosis
Several pathways have been proposed for potential exposure of humans to nanomaterials (19). Whereas inhalation may be the major route of exposure, ingestion and dermal exposure are also possible during the manufacture, use, and disposal of engineered nanomaterials. Furthermore, intravenous, subcutaneous, or intramuscular administration is needed for therapeutic and diagnostic applications of nanotechnological devices. After inhaled nanoparticles are deposited in the respiratory tract, their small size promotes uptake into cells and transcytosis into the vasculature and lymphatics. Because nanoparticles are barely recognized by phagocytosing cells such as lung macrophages compared with microsized particles (2), uptake seems likely to occur via epithelial or endothelial cells (ECs).
According to epidemiological studies conducted in the United States and Europe (4, 10), modest increases in the mass of particulate matter are associated with increased duration of hospitalization and mortality as a result of cardiovascular disorders. Traffic-derived nanosized particles are most likely responsible for these cardiovascular actions, because the larger surface area per mass potentially leads to enhanced biological toxicity (2, 19). Because nanoparticulate air pollution is known to translocate into the vasculature (17, 18), direct effects of nanoparticles on the cardiovascular system could be one possible mechanism explaining these epidemiological findings. In this context, vascular endothelium could represent a primary target for nanomaterials after translocation into the circulation. We thus hypothesized that nanomaterials may directly interact with ECs to induce endothelial injury or cell death, promote thrombosis, and destabilize atheromatous plaques. In the present study, we focused particularly on the direct effects of fullerenes, one of the major nanomaterials, on endothelial injury and toxicity, using cultured vascular ECs to explore the possibilities of cellular toxicity leading to cardiovascular disease.
| MATERIALS AND METHODS |
|---|
|
|
|---|
Cell culture. Human umbilical vein ECs (HUVECs) were purchased from Cascade Biologics (Portland, OR) and cultured in Medium 200 supplemented with low-serum growth supplement (LSGS; Cascade Biologics) as described previously (30). Cells were used at passages 36 for experiments.
Electron microscopy. Samples were fixed in 0.1 M sodium cacodylate-buffered (pH 7.4) 2.0% glutaraldehyde solution at 4°C overnight and postfixed in 0.1 M sodium cacodylate-buffered (pH 7.4) 1% OsO4 solution at 4°C for 2 h. After dehydration in an ethanol gradient (50100% for 10 min each), samples were embedded in EPON812 at 60°C for 2 days. Ultrathin sections (80 nm) were stained using uranyl acetate and lead citrate. Sections were examined using an electron microscope (model JEM2000EX; JEOL, Tokyo, Japan) at 100 kV.
LDH cytotoxicity assay.
Cytotoxicity assay was performed using a CytoTox 96 nonradioactive cytotoxicity assay kit (Promega, Madison, WI) in accordance with the instructions of the manufacturer. Briefly, after treating HUVECs at
90% confluence in six-well plates with C60(OH)24 (1100 µg/ml) for 24 h, culture medium was collected. Lactate dehydrogenase (LDH), a stable cytosolic enzyme released during cell lysis, was measured at 490-nm absorbance using a standard 96-well plate reader. Cytotoxicity was expressed relative to basal LDH release in untreated control cells.
Proliferation assay.
Proliferation assay was performed using a Cell Counting-8 kit (Dojindo Laboratories, Kumamoto, Japan) according to the instructions of the manufacturer. Briefly, after treating HUVECs at
30% confluence in 12-well plates with C60(OH)24 (1100 µg/ml) for 24 h, water-soluble tetrazolium salt (WST-8) was added for 3 h and culture medium was collected. Conversion of WST-8 into formazan by living cells (active mitochondria) was measured using a standard 96-well plate reader at 450-nm absorbance. Total numbers of living cells were compared with untreated control samples.
Western blot analysis.
Western blot analysis was performed as described previously (29). Proteins were obtained by homogenizing HUVECs with Triton X-based lysis buffer (1% Triton X-100, 20 mM Tris, pH 7.4, 150 mM NaCl, 1 mM EDTA, 1 mM EGTA, 2.5 mM sodium pyrophosphate, 1 mM
-glycerol phosphate, 1 mM Na3VO4, 1 µg/ml leupeptin, and 0.1% protease inhibitor mixture; Nacalai Tesque, Kyoto, Japan). Protein concentration was determined using the bicinchoninic acid method (Pierce, Rockford, IL). Equal amounts of proteins (15 µg) were separated by SDS-PAGE (7.5% and 14%) and transferred onto nitrocellulose membrane (Pall, Ann Arbor, MI). After being blocked with 3% BSA, membranes were incubated with primary antibody (1:1,000 dilution) at 4°C overnight and membrane-bound antibodies were visualized using horseradish peroxidase-conjugated secondary antibodies (1:10,000 dilution, 1 h) and the ECL system (Amersham Biosciences, Little Chalfont, UK). Experiments were performed three or more times, and equal loading of protein was ensured by measuring total actin expression.
Activity assay for 20S proteasome. Activity of the 20S proteasome was determined using the 20S proteasome assay kit (Calbiochem, San Diego, CA) according to the instructions of the manufacturer. Cells were lysed in Triton X-based lysis buffer as described above. The assay mixture contained 178 µl of reaction buffer (25 mM HEPES and 0.5 mM EDTA, pH 7.6), 10 µl of substrate [10 µM Suc-Leu-Val-Tyr-7-amino-4-methylcoumarin (AMC)], 2 µl of SDS (0.03%), and 10 µl of cell lysate (10 µg of protein). After incubation for 30 min at 37°C, the fluorescence of liberated AMC was measured using excitation and emission wavelengths at 340 and 450 nm, respectively.
Microarray analysis.
Total RNA was isolated from HUVECs treated with or without C60(OH)24 (100 µg/ml, 24 h) using an RNeasy Kit (Qiagen, Valencia, CA) according to the instructions of the manufacturer. Only samples with A260/A280 between 1.7 and 2.2 (measured in 10 mM Tris·HCl, pH 7.6) were considered suitable for use. Hybridization samples were prepared according to the GeneChip Expression Analysis Technical Manual (701021, Rev. 5, section 2, "Eukaryotic Sample and Array Processing," chapt. 1, "Eukaryotic Target Preparation"; http://www.affymetrix.com/support/technical/manuals.affx). Total RNA (2 µg) was amplified for each sample. Next, cRNA (30 µg) was fragmented in 40 µl of 1x fragmentation buffer. Hybridization cocktails were made as described in the GeneChip Expression Analysis Technical Manual (701021, Rev. 5, section 2, chapt. 2, "Eukaryotic Target Hybridization") and hybridized to human genome U133 plus2.0 chips at 60 rpm and 45°C for 16 h using the Hybridization Oven 640 110 V (no. 800138; Affymetrix, Santa Clara, CA). Human genome U133 plus2.0 chips (Affymetrix) comprise 54,000 probe sets and provide comprehensive coverage of the transcribed human genome on a single array to analyze expression levels of >47,000 transcripts and variants, including 38,500 well-characterized human genes plus
6,500 new genes. GeneChips were stained with streptavidin-phycoerythrin using a Fluidics Station 450 (00-0079; Affymetrix). After being washed extensively, GeneChips were scanned using a GeneChip Scanner 3000 (00-0074; Affymetrix). Data were analyzed using GeneChip Operating Software version 1.1 (no. 690036; Affymetrix) according to GeneChip Expression Analysis Data Analysis Fundamentals (chapt. 4, "First-Order Data Analysis and Data Quality Assessment"; and chapt. 5, "Statistical Algorithms Reference"; http://www.affymetrix.com/support/technical/manuals.affx). To allow comparison, all chips were scaled to a target intensity of 500 on the basis of all probe sets on each chip. Comparison of GeneChip array data was obtained using custom analysis services (Kurabo Industries, Osaka, Japan). Kurabo Industries is the authorized service provider for Affymetrix Japan (Tokyo, Japan). Genes that were significantly upregulated (top 100 genes; see Supplemental Table 1; http://ajpcell.physiology.org/cgi/content/full/00481.2005/DC1) or downregulated (top 100 genes; Supplemental Table 2) in two independent experiments are summarized. Microarray data were deposited in the National Center for Biotechnology Information's Gene Expression Omnibus (GenBank accession no. GSE3364).
Statistical analysis. Data are means ± SE. Statistical evaluations were performed using an unpaired Student's t-test. Values of P < 0.05 were considered statistically significant.
| RESULTS |
|---|
|
|
|---|
|
|
30% confluence were treated with C60(OH)24 (1100 µg/ml) for 24 h and then the total number of living cells was measured using WST-8. HUVEC growth was inhibited by C60(OH)24 in a dose-dependent manner (Fig. 3A). Quantitative analysis (Fig. 3B) revealed that only the maximal concentration of 100 µg/ml C60(OH)24 significantly inhibited cell growth (64.2 ± 4.7%, n = 6; P < 0.01 vs. controls).
|
|
|
|
|
|
| DISCUSSION |
|---|
|
|
|---|
Some novel mechanistic insights of this study are that fullerene causes EC injury or cell death by increasing the accumulation of polyubiquitinated proteins in the cytosol and facilitating excessive autophagic cell death. EC injury and death are closely related to the initiation of atherosclerosis (14, 23). Furthermore, through nitric oxide production, ECs offer important protective functions against ischemic heart disease, including myocardial infarction, by inhibiting platelet aggregation (16) and lowering blood pressure (27). We thus propose that exposure to nanomaterials is a potential risk for cardiovascular disease, including atherosclerosis and ischemic heart disease. However, because quantitatively significant EC toxicity from water-soluble fullerene was observed only at high dosage, further validations (particularly in vivo) are needed.
We recently found that carbon black (CB), a chemically inert carbon nanoparticle present in diesel exhaust particles (13), shows endothelial cytotoxicity by mechanisms different from those of fullerene (31). Specifically, microarray analysis revealed that CB stimulated the induction of several proinflammatory mediators, including E-selectin, ICAM-I, IL-8, heme oxygenase-1, and prostaglandin endoperoxide synthase 2. However, such effects were not observed in fullerene-stimulated ECs. Furthermore, CB did not cause accumulation of polyubiquitinated proteins in ECs. Although the underlying mechanisms remain unclear, our findings indicate that the results reported herein could be specific to fullerene. Another report (21) examined the effects of several nanomaterials, including metals (TiO2, SiO2, Co, Ni, polyvinyl chloride), on endothelial toxicity. The report showed that only Co2+ particles possessed cytotoxic effects on ECs, supporting the concept that cytotoxicity varies among different nanoparticles.
Several pathways lead to cell death (6). Two major types of programmed cell death have been distinguished: the caspase-mediated process of apoptosis and the caspase-independent process involving autophagy.
In the present study, we found that exposure to fullerene did not induce cleavage of caspase-3 or PARP, which are the hallmarks of apoptosis (5, 20). Furthermore, no clear chromatin condensation was apparent in the nuclei (Fig. 6B). The present results thus indicate that the induction of apoptosis does not seem to be responsible for fullerene-induced cell death and/or injury.
Conversely, fullerene markedly increased the accumulation of polyubiquitinated proteins (Fig. 5A). Normally, under physiological conditions, cells degrade ubiquitinated proteins using 20S proteasomes. Fullerene does not seem to modify proteasome activity directly (Fig. 5B). Ultrastructural analysis revealed the excess formation of phagosome-like vesicles in the cytosol (Fig. 6B). Vesicles have been determined to be autophagosomes on the basis of Western blot analysis using specific marker LC3 II (9, 32) (Fig. 7). Similarly, the formation of phagosomes was observed after treating alveolar macrophages with single-wall and multiwall carbon nanotubes (8). Autophagy (type II programmed death) is known to be an alternative pathway to exclude unnecessary proteins and cellular organelles. We thus propose that accumulation of ubiquitinated proteins and abnormal activation of an autophagic death pathway could be responsible at least for cell death or injury caused by water-soluble fullerene.
EC injury and/or death appears to represent a primary mechanism for the initiation of atherosclerosis (14, 23). Injury and/or denudation of ECs trigger the attachment of leukocytes to the subendothelial region and promote transendothelial migration of cells, allowing the initiation of atherosclerosis. EC injury also leads to the loss of beneficial functions, including antithrombogenic and blood pressure-lowering functions via nitric oxide, which leads to the progression of ischemic heart disease, including myocardial infarction. In addition to cell death and injury, fullerene also inhibited EC growth. Impairment of EC growth may be related to impairment of angiogenesis. Because angiogenesis is crucial to the maintenance of vascular integrity by forming collateral vessels in response to tissue ischemia (11), fullerene inhibition of EC growth may be related to the progression of ischemic heart disease. Collectively, the present findings support the concept that exposure to fullerene could be a risk for atherosclerosis and ischemic heart disease.
The present study used 1100 µg/ml fullerene concentrations for in vitro experiments. The pathophysiological concentrations of fullerene are barely known. In addition to engineered nanomaterials, traffic-derived nanoparticles are known to represent a risk for cardiovascular disorders, including atherosclerosis and ischemic heart disease (2, 4). The maximal concentration of particulate matter <2.5 µm in Chongqing, one of the biggest cities in China, was
700 µg/m3 (daily average) (26), indicating that an individual could inhale
10,000 µg of particulate matter during the course of 24 h there. This value is equivalent to
1 µg/ml when the extracellular fluid volume is 12 L in a 60-kg person. The fullerene dosage used in this study was up to 100-fold higher than this level.
The kinetics of water-soluble fullerene in vivo have not yet been completely determined. Normally, inhaled microparticles are cleaned off by alveolar macrophages via phagocytosis. However, this is not applicable to nanoparticles (2, 19), which appear to translocate to extrapulmonary sites via blood and lymph and thus reach other tissues (19). Using radiolabeled water-soluble fullerene administered intravenously to rats, Yamago et al. (28) demonstrated that most fullerenes moved rapidly to the liver (within 1 h) and then were distributed to various other tissues, including spleen, lung, kidney, heart, and brain. Extraction seems slow, and >90% was retained in the body 1 wk later, raising concern about chronic toxic effects. Although we could not clearly observe EC cytotoxicity after acute treatment with low-dose fullerene (10 µg/ml, 24 h), treatment for 8 days seems to enhance toxicity (Fig. 8). The effects of chronic exposure to low-dose fullerene in vivo need to be examined, particularly with regard to the cardiovascular system.
In summary, in the present study, we examined the direct effects of water-soluble fullerene on vascular endothelial cells to explore the potential toxicity of fullerene in humans, especially regarding the cardiovascular systems. We found that fullerene causes cytotoxic injury or cell death in vascular ECs, indicating that exposure to fullerene could represent a risk for atherosclerosis and ischemic heart disease. Because cytotoxicity by water-soluble fullerene occurs only at high doses, further validation experiments using blood vessels and animal models are warranted.
| GRANTS |
|---|
|
|
|---|
| ACKNOWLEDGMENTS |
|---|
| FOOTNOTES |
|---|
The costs of publication of this article were defrayed in part by the payment of page charges. The article must therefore be hereby marked "advertisement" in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.
| REFERENCES |
|---|
|
|
|---|
2. Borm PJA and Kreyling W. Toxicological hazards of inhaled nanoparticles: potential implications for drug delivery. J Nanosci Nanotechnol 4: 521531, 2004.[CrossRef][ISI][Medline]
3. Bosi S, Feruglio L, Da Ros T, Spalluto G, Gregoretti B, Terdoslavich M, Decorti G, Passamonti S, Moro S, and Prato M. Hemolytic effects of water-soluble fullerene derivatives. J Med Chem 47: 67116715, 2004.[CrossRef][ISI][Medline]
4. Brook RD, Franklin B, Cascio W, Hong Y, Howard G, Lipsett M, Luepker R, Mittleman M, Samet J, Smith SC Jr, and Tager I. Air pollution and cardiovascular disease: a statement for healthcare professionals from the Expert Panel on Population and Prevention Science of the American Heart Association. Circulation 109: 26552671, 2004.
5. Budihardjo I, Oliver H, Lutter M, Luo X, and Wang X. Biochemical pathways of caspase activation during apoptosis. Annu Rev Cell Dev Biol 15: 269290, 1999.[CrossRef][ISI][Medline]
6. Clarke PG. Developmental cell death: morphological diversity and multiple mechanisms. Anat Embryol (Berl) 181: 195213, 1990.[Medline]
7. Colvin VL. The potential environmental impact of engineered nanomaterials. Nat Biotechnol 21: 11661170, 2003.[CrossRef][ISI][Medline]
8. Jia G, Wang H, Yan L, Wang X, Pei R, Yan T, Zhao Y, and Guo X. Cytotoxicity of carbon nanomaterials: single-wall nanotube, multi-wall nanotube, and fullerene. Environ Sci Technol 39: 13781383, 2005.[Medline]
9. Kabeya Y, Mizushima N, Ueno T, Yamamoto A, Kirisako T, Noda T, Kominami E, Ohsumi Y, and Yoshimori T. LC3, a mammalian homologue of yeast Apg8p, is localized in autophagosome membranes after processing. EMBO J 19: 57205728, 2000.[CrossRef][ISI][Medline]
10. Katsouyanni K, Touloumi G, Samoli E, Gryparis A, Le Tertre A, Monopolis Y, Rossi G, Zmirou D, Ballester F, Boumghar A, Anderson HR, Wojtyniak B, Paldy A, Braunstein R, Pekkanen J, Schindler C, and Schwartz J. Confounding and effect modification in the short-term effects of ambient particles on total mortality: results from 29 European cities within the APHEA2 project. Epidemiology 12: 521531, 2001.[CrossRef][ISI][Medline]
11. Kondo T, Kobayashi K, and Murohara T. Nitric oxide signaling during myocardial angiogenesis. Mol Cell Biochem 264: 2534, 2004.[CrossRef][ISI][Medline]
12. Kreuter J. Nanoparticulate systems for brain delivery of drugs. Adv Drug Deliv Rev 47: 6581, 2001.[CrossRef][ISI][Medline]
13. Lam CW, James JT, McCluskey R, and Hunter RL. Pulmonary toxicity of single-wall carbon nanotubes in mice 7 and 90 days after intratracheal instillation. Toxicol Sci 77: 126134, 2004.
14. Libby P. Inflammation in atherosclerosis. Nature 420: 868874, 2002.[CrossRef][Medline]
15. Martinet W, De Bie M, Schrijvers DM, De Meyer GR, Herman AG, and Kockx MM. 7-Ketocholesterol induces protein ubiquitination, myelin figure formation, and light chain 3 processing in vascular smooth muscle cells. Arterioscler Thromb Vasc Biol 24: 22962301, 2004.
16. Moncada S, Palmer RM, and Higgs EA. Nitric oxide: physiology pathophysiology, and pharmacology. Pharmacol Rev 43: 109142, 1991.[ISI][Medline]
17. Nemmar A, Hoet PH, Vanquickenborne B, Dinsdale D, Thomeer M, Hoylaerts MF, Vanbilloen H, Mortelmans L, and Nemery B. Passage of inhaled particles into the blood circulation in humans. Circulation 105: 411414, 2002.
18. Nemmar A, Hoylaerts MF, Hoet PH, and Nemery B. Possible mechanisms of the cardiovascular effects of inhaled particles: systemic translocation and prothrombotic effects. Toxicol Lett 149: 243253, 2004.[CrossRef][ISI][Medline]
19. Oberdorster G, Oberdorster E, and Oberdorster J. Nanotoxicology: an emerging discipline evolving from studies of ultrafine particles. Environ Health Perspect 113: 823839, 2005.[ISI][Medline]
20. Patel T, Gores GJ, and Kaufmann SH. The role of proteases during apoptosis. FASEB J 10: 587597, 1996.[Abstract]
21. Peters K, Unger RE, Kirkpatrick CJ, Gatti AM, and Monari E. Effects of nano-scaled particles on endothelial cell function in vitro: studies on viability, proliferation and inflammation. J Mater Sci Mater Med 15: 321325, 2004.[CrossRef][ISI][Medline]
22. Rancan F, Rosan S, Boehm F, Cantrell A, Brellreich M, Schoenberger H, Hirsch A, and Moussa F. Cytotoxicity and photocytotoxicity of a dendritic C60 mono-adduct and a malonic acid C60 tris-adduct on Jurkat cells. J Photochem Photobiol B 67: 157162, 2002.[CrossRef][Medline]
23. Ross R. Atherosclerosis: an inflammatory disease. N Engl J Med 340: 115126, 1999.
24. Sayes CM, Gobin AM, Ausman KD, Mendez J, West JL, and Colvin VL. Nano-C60 cytotoxicity is due to lipid peroxidation. Biomaterials 26: 75877595, 2005.[CrossRef][ISI][Medline]
25. Seaton A and Donaldson K. Nanoscience, nanotoxicology, and the need to think small. Lancet 365: 923924, 2005.[CrossRef][ISI][Medline]
26. Venners SA, Wang B, Xu Z, Schlatter Y, Wang L, and Xu X. Particulate matter, sulfur dioxide, and daily mortality in Chongqing, China. Environ Health Perspect 111: 562567, 2003.[ISI][Medline]
27. Wilkinson IB, Franklin SS, and Cockcroft JR. Nitric oxide and the regulation of large artery stiffness: from physiology to pharmacology. Hypertension 44: 112116, 2004.
28. Yamago S, Tokuyama H, Nakamura E, Kikuchi K, Kananishi S, Sueki K, Nakahara H, Enomoto S, and Ambe F. In vivo biological behavior of a water-miscible fullerene: [14C] labeling, absorption, distribution, excretion and acute toxicity. Chem Biol 2: 385389, 1995.[CrossRef][ISI][Medline]
29. Yamawaki H, Lehoux S, and Berk BC. Chronic physiological shear stress inhibits tumor necrosis factor-induced proinflammatory responses in rabbit aorta perfused ex vivo. Circulation 108: 16191625, 2003.
30. Yamawaki H, Pan S, Lee RT, and Berk BC. Fluid shear stress inhibits vascular inflammation by decreasing thioredoxin-interacting protein in endothelial cells. J Clin Invest 115: 733738, 2005.[CrossRef][ISI][Medline]
31. Yamawaki H and Iwai N. Mechanisms underlying nano-sized air pollution-mediated progression of atherosclerosis: carbon black causes cytotoxic injury/inflammation and inhibits cell growth in vascular endothelial cells. Circ J 70: 129140, 2006.[CrossRef][ISI][Medline]
32. Yoshimori T. Autophagy: a regulated bulk degradation process inside cells. Biochem Biophys Res Commun 313: 453458, 2004.[CrossRef][ISI][Medline]
This article has been cited by other articles:
![]() |
S. T. Stern, B. S. Zolnik, C. B. McLeland, J. Clogston, J. Zheng, and S. E. McNeil Induction of Autophagy in Porcine Kidney Cells by Quantum Dots: A Common Cellular Response to Nanomaterials? Toxicol. Sci., November 1, 2008; 106(1): 140 - 152. [Abstract] [Full Text] [PDF] |
||||
![]() |
S. T. Stern and S. E. McNeil Nanotechnology Safety Concerns Revisited Toxicol. Sci., January 1, 2008; 101(1): 4 - 21. [Abstract] [Full Text] [PDF] |
||||
| ||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
| HOME | HELP | FEEDBACK | SUBSCRIPTIONS | ARCHIVE | SEARCH | TABLE OF CONTENTS |
| Visit Other APS Journals Online |