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Indoor particles affect vascular function in the aged

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Indoor Particles Affect Vascular Function in the Aged

Indoor Particles Affect Vascular Function in the Aged

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  • 1. Indoor Particles Affect Vascular Function in the AgedAn Air Filtration–based Intervention Study ¨Elvira Vaclavik Brauner1, Lykke Forchhammer1, Peter Møller1, Lars Barregard2, Lars Gunnarsen3, Alireza Afshari3, ˚Peter Wahlin4, Marianne Glasius4, Lars Ove Dragsted5, Samar Basu6, Ole Raaschou-Nielsen7, and Steffen Loft11 Institute of Public Health, Department of Environmental Health, Copenhagen, Denmark; 2Department of Occupational and EnvironmentalMedicine, Sahlgrenska University Hospital and Academy, Gothenburg, Sweden; 3Danish Building Research Institute, Hørsholm, Denmark;4 Department of Atmospheric Environment, National Environmental Research Institute, Roskilde, Denmark; 5The National Food Institute, DanishTechnical University, Lyngby, and Institute of Human Nutrition, Faculty of Life Sciences, Frederiksberg, Denmark; 6Clinical Nutrition andMetabolism, Department of Public Health and Caring Sciences, Uppsala, Sweden; and 7Institute of Cancer Epidemiology, Danish Cancer Society,Copenhagen, DenmarkRationale: Exposure to particulate matter is associated with risk ofcardiovascular events, possibly through endothelial dysfunction, AT A GLANCE COMMENTARYand indoor air may be most important.Objectives: We investigated effects of controlled exposure to indoor Scientific Knowledge on the Subjectair particles on microvascular function (MVF) as the primary end- Increased cardiovascular risk is associated with exposure topoint and biomarkers of inflammation and oxidative stress as air pollution.secondary endpoints in a healthy elderly population.Methods: A total of 21 nonsmoking couples participated in a random-ized, double-blind, crossover study with two consecutive 48-hour What This Study Adds to the Fieldexposures to either particle-filtered or nonfiltered air (2,533–4,058 Particles in indoor air affect endothelial function in elderlyand 7,718–12,988 particles/cm3, respectively) in their homes.Measurements and Main Results: MVF was assessed noninvasively by subjects. A significant improvement was shown after reduc-measuring digital peripheral artery tone after arm ischemia. Sec- tion of particles in the indoor air achieved by air filtrationondary endpoints included hemoglobin, red blood cells, platelet in their homes.count, coagulation factors, P-selectin, plasma amyloid A, C-reactiveprotein, fibrinogen, IL-6, tumor necrosis factor-a, protein oxida-tion measured as 2-aminoadipic semialdehyde in plasma, urinary8-iso-prostaglandin F2a, and blood pressure. Indoor air filtration sig- Short-term and chronic exposure to ambient levels of particu-nificantly improved MVF by 8.1% (95% confidence interval, 0.4– late matter (PM) is associated with increased morbidity and16.3%), and the particulate matter (diameter , 2.5 mm) mass of the mortality related to respiratory and cardiovascular disease (1, 2).indoor particles was more important than the total number concen- Biological mechanisms of action of PM are believed to in-tration (10–700 nm) for these effects. MVF was significantly asso- volve altered pulmonary inflammation, cardiac autonomicciated with personal exposure to iron, potassium, copper, zinc, function, endothelial dysfunction, systemic inflammation, ox-arsenic, and lead in the fine fraction. After Bonferroni correction, idative stress, and altered balance between blood clotting andnone of the secondary biomarkers changed significantly. fibrinolysis, with small particles being more potent per unitConclusions: Reduction of particle exposure by filtration of recircu- mass than larger particles due to their higher surface area andlated indoor air for only 48 hours improved MVF in healthy elderly reactivity (3–5). Traffic-related PM may be particularly rele-citizens, suggesting that this may be a feasible way of reducing the vant, as indicated by risk of cardiovascular events shortly afterrisk of cardiovascular disease. exposure in traffic (6). These particles may also penetrateKeywords: atherosclerosis; biomarkers; cardiovascular disease; indoor indoors, and previous studies have described increased mor-air pollution; inflammation tality associated with a residential address close to major roads with dense traffic as well as acute mortality associated with source allocation (7, 8). Abnormal endothelial function (EF) is a strong predictor of adverse cardiovascular outcomes (9, 10) and widely recognized in patients with atherosclerosis and its risk factors (11, 12). Inhalation of high concentrations of diesel exhaust particles has(Received in original form April 26, 2007; accepted in final form October 11, 2007) recently been shown to impair two important and complemen-Supported by contract no. 513943 from the Danish National Research Councils, tary aspects of vascular functions in healthy humans: theDenmark Velux Foundation, Denmark Environmental Cancer Risk, Nutrition and regulation of vascular tone and fibrinolysis (13).Individual Susceptibility, European Union 6th Framework Program, Priority 5: A number of personal monitoring studies have found that‘‘Food Quality and Safety.’’ biomarkers related to cardiovascular diseases show strongerCurrent affiliation for M.G.: Department of Chemistry, University of Aarhus, association with personal exposure than with ambient levelsAarhus, Denmark. (14, 15). This indicates that the exposure to particles generatedCorrespondence and request for reprints should be addressed to Steffen Loft, M.D., indoors could cause an additional increase in adverse effects.D.M.Sc., Institute of Public Health, Department of Environmental and Occupational However, studies of the health effects of indoor air on healthyHealth, Øster Farimagsgade 5A, DK-1014 Copenhagen K, Denmark. E-mail: s.loft@ humans are lacking. In addition, most of the mechanistic evi-pubhealth.ku.dk dence comes from experimental human or animal studies withThis article has an online supplement, which is accessible from this issue’s table ofcontents at www.atsjournals.org high levels of exposure, or from observational panel studies with associated difficulties in exposure assessment and controlAm J Respir Crit Care Med Vol 177. pp 419–425, 2008Originally Published in Press as DOI: 10.1164/rccm.200704-632OC on October 11, 2007 of confounders. Indoor penetration of ambient air particles isInternet address: www.atsjournals.org variable, and there are many indoor sources, such as cooking,
  • 2. 420 AMERICAN JOURNAL OF RESPIRATORY AND CRITICAL CARE MEDICINE VOL 177 2008candles, human activity, heating appliances, and environmental The test consisted of three stages: baseline, brachial arterial occlusion,tobacco smoke (15, 16). This underlines the importance of and a postocclusion recording of the induced reactive hyperemiaunderstanding details of indoor PM levels, and there is a specific response. Data was digitally stored as pulse wave tracings from bothneed to study this in the elderly, as they appear to have elevated hands and an MVF score describing the extent of hyperemia was com- puted using an automated algorithm in an operator independent manner.susceptibility (17) and have the largest attributable risk relatedto indoor PM, as they spend more time indoors (18). Secondary Endpoints The primary aim of this study was to use controlled exposure Hematological measurements, markers of inflammation, hemostasis, andto real-life indoor air particles to delineate the relationship be- oxidative stress. We measured hemoglobin, red blood cells, fibrinogen,tween intervention and microvascular function (MVF), as a mea- platelets, coagulation factors (II 1 VII 1 X), C-reactive protein (CRP),sure of EF in a healthy population of 42 elderly volunteers. We IL-6, tumor necrosis factor (TNF)-a, plasma amyloid A, 2-aminoapidicused two consecutive 48-hour periods in each private home, and semialdehyde, and urinary 8-iso-prostaglandin F2a (8-iso-PGF2a).an intervention was achieved by using high-efficiency particleair (HEPA) filters during one of these periods. Changes in Statistical Analysisperipheral artery tone due to enhanced flow after arm ischemia Due to three missing data points for the MVF score and one missingwas used to assess MVF as the a priori–defined primary end- blood sample, we used mixed-effect model repeated measures analysispoint. Secondary endpoints in terms of blood pressure, hema- to investigate the effect of intervention on the primary and secondarytological parameters, markers of inflammation, and hemostasis, outcome variables. Partner cluster and participant nested in partneras well as lipid and protein oxidation products, were included to cluster were included as random factor variables to account forelucidate potential mechanisms of action. interindividual variation and the effects of partners living at the same address. Exposure in terms of filtration status was included as a fixed categorical explanatory variable. Gender was included as a categoricalMETHODS variable, and age, body mass index, and indoor temperature as con- tinuous variables. We investigated dose–response relationships relatedFurther details of all methods are available in the extended METHODS in to the total NC, area and volume of particles, as well as mass concen-the online supplement. tration of PM2.5 and PM10–2.5 up to blood sampling. These were analyzed in single-exposure models and in a multiple-component,Study Population and Design backward stepwise selection procedure. Similarly, the mass concentra-A total of 21 couples, aged 60–75 (median, 67) years and mean body tion of each element analyzed in the PM2.5 and PM10–2.5 fractions weremass index of 25 (SD, 3.24), were recruited, and one female was later analyzed with and without adjustment for mass concentration of theexcluded. All participants were healthy nonsmokers, and each was his/ fraction. The significance threshold was P less than 0.05 in all analyses.her own control, excluding confounding by factors that are stablewithin an individual over time but vary between participants. The project design was a double-blind crossover intervention with RESULTSrandomized order of 48-hour exposure to recirculated particle-filteredand nonfiltered indoor air in the volunteer’s homes located in Exposure CharacterizationCopenhagen in proximity (,350 m) to major roads (.10,000 vehicles/ ¨24 h). Two filter units (Airshower; Airsonett AB, Angelholm, Sweden), Table 1 summarizes indoor levels of PM characteristics andrunning continuously with airflow of 540 m3/hour, sound level less than NO2 during the two different exposure scenarios. The HEPA35 dB, and filter exhaust height of 2.15 m, were placed in the bedroom filter placed in homes effectively removed ultrafine, fine, andand living room of each apartment during the study period (either with coarse particles, whereas levels of NO2 were unaltered. Filtra-or without a HEPA filter, according to scenario; see Figure E2 in the tion mean efficacy within each apartment was uniform: 59.8%online supplement). When the HEPA filter was removed, filtration (bedroom) and 61.2% (living area), and this was not signifi-efficiency of the unit was less than 10%, with unchanged noise, airflow, cantly correlated with NCurban background, maximum traffic den-and appearance. The air pollution monitoring equipment was always sity within a 100-m radius, room volume, or carpeting coveragepositioned at the furthest point diagonally away from the filter. (see Table E1). Figure 1 depicts NC10–700 nm, Area10–700 nm, and The size distribution and number concentration (NC) of particles(10–700 nm) in each residence were continuously monitored. Particle Volume10–700 nm of particles with and without filtration of thesamples were collected using Dichotomous Stacked Filter Units (Uni- air in one of the included homes. Occasional peaks could beversity of Hertfortshire, Hatfield, UK) (19), as fine (diameter , 2.5 mm related to candle burning and cooking. The average change in[PM2.5]) and coarse (10–2.5 mm diameter [PM10–2.5]) fractions. Particlemass was determined gravimetrically, and elemental composition wasdetermined using a proton-induced X-ray emission method (20). TABLE 1. GEOMETRIC MEAN AND 95% CONFIDENCE INTERVAL Blood and spot-urine was sampled on the morning after each OF INDOOR CONCENTRATIONS OF PARTICULATE MATTER48-hour scenario, and, to avoid problems due to diurnal variation, NUMBER CONCENTRATION10–700 nm, AREA10–700 nm,each scenario started at the same time of morning. For the duration of VOLUME10–700 nm, PARTICULATE MATTER MASS, INDOOR NO2,the study, we asked participants to stay indoors (equivalent to 92–94% RELATIVE HUMIDITY, AND TEMPERATUREof time) and keep windows closed. The study was approved by the local ethics committee and in Nonfiltered Air Particle-filtered Airaccordance with the Declaration of Helsinki. All participants gave Geometric Mean Geometric Meanwritten, informed consent before inclusion. Variable (95% CI) (95% CI)Primary Endpoint NC10–700 nm, no./cm3 10,016 (7,718–12,998) 3,206 (2,533–4,058) Area10–700 nm, mm2/cm3 173 (144–209) 47 (38–58)Vascular function. MVF was measured immediately before blood Volume10–700 nm, mm3/cm3 5.7 (4.7–6.8) 1.6 (1.3–2.0)sampling and noninvasively using reactive hyperemia–peripheral arte- PM10–2.5, mg/m3 9.4 (8.1–1.0) 4.6 (3.5–6.0)rial tonometry (RH-PAT), as previously described in detail (21–23). PM2.5, mg/m3 12.6 (11.2–14.1) 4.7 (3.9–5.7)This technique uses finger-mountable pneumatic sensors (Endo-PAT NO2, ppb 20 (18–21) 20 (18–22)2000; Itamar Medical Ltd., Cesaria, Israel) specifically designed to Relative humidity, % 34.0 (30.9–37.4) 34.0 (31.1–37.1)continuously record the digital arterial pulse wave amplitude. A blood Temperature, 8C 21.6 (21.2–22.0) 21.5 (21.1–21.9)pressure cuff was placed above the elbow of the right arm for hyper-emia testing, while the left arm served as a control. The plethysmo- Definition of abbreviations: CI 5 confidence interval; NC 5 number concen-graphic finger probes were placed on the index fingers of both hands. tration; PM 5 particulate matter.
  • 3. Brauner, Møller, Forchhammer, et al.: Indoor Particles Affect Vascular Function ¨ 421 Figure 1. Number con- centration (NC10–700 nm; black line), Area10–700 nm; (red line), and Vol- ume10–700 nm; (blue line) of particles during 48 hours without and 48 hours with filtration of the indoor air in one of the included homes. Peaks in NC10–700 nm (asterisks) occurred dur- ing candle burning and cooking, as indicated.NC10–700 nm over the entire study period within the included Primary endpoint. Three pulse wave tracings of RH-PATapartments is presented in the online supplement (Figure E1); were not recorded due to instrument failure. The MVF scorepeaks were not related to rush hour traffic, but rather to indoor was significantly improved by 8.1% (95% confidence intervalactivities. The concentrations of the elements in the indoor fine [CI], 0.4–16.3%; P 5 0.03) during air filtration, as assessed infraction of particles (PM2.5) per indoor air unit of nonfiltered the mixed-effects model with inclusion of filtration as a categor-and particle-filtered indoor air are presented in the online ical variable (Table 2). The MVF score was significantly andsupplement (Table E2). There was a relatively high concentra- inversely associated with mass concentration of PM2.5 andtion of sulfur, consistent with substantial penetration from out- NC10–700 nm during both scenarios in the single-exposure mod-door air originating from long-range transport, and this fraction els, whereas PM10–2.5, Area10–70 nm, and Volume10–700 nm werewas also relatively rich in metals. All concentrations were sub- not significant predictors (Table 3). After applying a backwardstantially reduced by HEPA filtration. With the exception of stepwise selection approach and the stepwise exclusion of ex-chromium, antimony, arsenic, and chlorine, the concentrations posure variables: PM10–2.5 mass, Volume10–700 nm, NC10–700 nm,of all the elements within the PM2.5 fraction of indoor air were and Area10–70 0nm, only PM2.5 mass was a significant predictor ofsignificantly correlated with Area10–700 nm and Volume10–700 nm of MVF score in the reduced model. Of the elements in PM2.5particles (Table E3). fraction, we found that iron, copper, potassium, zinc, lead, and arsenic were all significantly and inversely associated with MVFBiomarkers and Function Tests score. When these single-element associations were adjusted forMVF score, hematological parameters, oxidative products, and the mass concentration of the PM2.5 fraction, we found that onlymarkers of inflammation and hemostasis are presented in Table potassium was significantly and independently associated with2 according to exposure scenario. MVF score (Table E2). There was no effect of exposure on the TABLE 2. GEOMETRIC MEAN AND 95% CONFIDENCE INTERVAL OF MICROVASCULAR FUNCTION AND BIOMARKERS ACCORDING TO FILTRATION SCENARIO AND RELATIONSHIP BETWEEN BIOMARKERS AND INTERVENTION FILTRATION IN THE HOMES OF 41 ELDERLY SUBJECTS Effect Marker Nonfiltered Air Particle-filtered Air P Value % Change (95% CI)a Microvascular function score* 1.78 (1.68 to 1.89) 1.95 (1.80 to 2.11) 0.040 8.1 (0.4 to 16.3) Hemoglobin, mmol/L 9.0 (8.8 to 9.2) 9.1 (8.8 to 9.3) 0.029 0.9 (0.1 to 1.8) Red blood cell count 3 1012/L 4.8 (4.6 to 4.9) 4.8 (4.8 to 4.9) 0.115 0.7 (20.2 to 1.5) Plasma fibrinogen, mmol/L 9.8 (9.5 to 10.1) 9.8 (9.7 to 10.0) 0.639 0.7 (22.3 to 3.7) Platelet count 3 109/L 227 (209 to 246) 230 (212 to 249) 0.372 1.3 (21.5 to 4.1) Coagulation factors (II 1 VII 1 X) 1.00 (0.96 to 1.04) 1.02 (0.97 to 1.07) 0.061 1.9 (20.1 to 3.9) Plasma C-reactive protein, mg/L 1.5 (1.3 to 1.9) 1.6 (1.4 to 1.9) 0.755 2.0 (210.4 to 16.1) Plasma IL-6, ng/L 1.2 (1.0 to 1.6) 1.2 (0.9 to 1.5) 0.130 26.6 (214.5 to 2.1) TNF-a, ng/L 1.1 (1.0 to 1.4) 1.2 (1.0 to 1.4) 0.848 0.5 (24.4 to 5.6) Plasma amyloid A, mg/L 3.8 (3.0 to 4.9) 3.7 (2.9 to 4.8) 0.486 23.1 (211.7 to 6.2) Plasma-selectin, mg/L 72.7 (65.8 to 80.2) 76.8 (67.3 to 87.7) 0.412 5.6 (27.6 to 20.7) 8-iso-PGF2a, nmol/mmol† 0.5 (0.4 to 0.5) 0.4 (0.4 to 0.5) 0.173 26.3 (214.8 to 3.0) PLAAS, pmol/mg protein 31.7 (26.1 to 38.6) 32.3 (26.7 to 39.1) 0.986 20.2 (219.4 to 24.5) Systolic blood pressure, mm Hg 81 (78 to 84) 81 (78 to 84) 0.443 20.2 (23.8 to 3.5) Diastolic blood pressure, mm Hg 136 (131 to 141) 133 (129 to 139) 0.893 21.4 (24.7 to 2.2) Definition of abbreviations: 8-iso-PGF2a 5 8-iso-prostaglandin F2a; CI 5 confidence interval; PLAAS 5 2-aminoapidic semi- aldehyde in plasma proteins; PM 5 particulate matter; TNF 5 tumor necrosis factor. Mixed model regression with partner cluster and subject nested in partner cluster used as random factors. All model estimates adjusted for age, gender, body mass index, and indoor temperature. Exposure to particle-filtered indoor air: categorical (yes/no) included as a predictor and the natural logarithm of the effect marker in question included as a continuous outcome variable. The predictive value of the estimates (%-change) expressed relative to exposure to particle-filtered indoor air. * The microvascular function score described in detail in the extended methods section of the online supplement. † 8-Iso-prostaglandin F2a: creatinine corrected concentration.
  • 4. 422 AMERICAN JOURNAL OF RESPIRATORY AND CRITICAL CARE MEDICINE VOL 177 2008TABLE 3. THE RELATIONSHIP BETWEEN THE MICROVASCULAR bradykinin) and endothelium-independent (sodium nitroprus-FUNCTION SCORE AND CONTINUOUS PARAMETERS OF side) vasodilators (13). Moreover, this group showed thatEXPOSURE MEASURED WITH AND WITHOUT FILTRATION endothelium-dependent vasodilatation occurring in the pres-OF THE INDOOR HOME AIR ence of mild systemic inflammation was persistent 24 hours after Single-Exposure Component Model the same exposure in 15 volunteers (31). We found an effect on MVF at a 10-times lower exposure level in an elderly popula-Exposure Variable % Change (95% CI) P Value tion, which may be more susceptible. Indeed, EF measured inNC10–700 nm 23.2 (26.2 to 20.0) 0.048 connection with previous exposure studies was only negativelyArea10–700 nm 23.1 (26.2 to 0.1) 0.060 associated with ambient levels of PM2.5 and sulfate and/or blackVolume10–700 23.2 (26.3 to 0.1) 0.060 nm carbon among diabetics, who are particularly susceptible, andPM2.5 25.5 (29.2 to 21.6) 0.007*PM10–2.5 22.5 (26.2 to 1.4) 0.200 diabetes enhances vulnerability to particulate air pollution– associated impairment in vascular reactivity and EF (32). More- Definition of abbreviations: CI 5 confidence interval; NC 5 number concen- over, EF measured as acetylcholine-induced vasodilatation intration; PM 5 particulate matter. aorta segments 1 hour after systemic administration of diesel Mixed model regression with partner cluster and subject nested in partner exhaust particles was only reduced in hyperlipidemic apolipo-cluster used as random factor variables. All model estimates are adjusted for age,gender, and body mass index. The natural logarithm of the exposure variable in protein E knockout mice, whereas there was a tendency towardquestion and the microvascular function score were included as a continuous enhanced vasodilatation in wild-type mice, and no effect onpredictor and outcome variables, respectively. The relative predictive value endothelium-independent vasodilatation in any type of mouse(%-change) of estimates is expressed per doubling in exposure variable numbers. (33). Thus, EF appears to be negatively affected by exposure to * In a stepwise backward selection process with all variables of exposure particulate air pollution in susceptible individuals, and thisincluded, only PM2.5 was a significant predictor of the microvascular function could provide part of a mechanistic link to acute cardiovascularscore. Exclusion order: PM10–2.5 (P 5 0.345); volume (P 5 0.475); number (P 50.564); and area (P 5 0.737). events as well as progression of atherosclerosis. Digital MVF was defined as our primary endpoint because this functional measure reflects coronary EF and can be con- sidered a more specific predictor of cardiovascular risk than thebaseline peripheral arterial tone amplitude in either the ische- secondary biomarkers that were included to elucidate potentialmic or control arm. mechanisms. The method has been validated in clinical settings Secondary endpoints. Filtration of the indoor air was signif- (23, 34, 35), but ours is the first group to use it in relation to theicantly associated with an increase in hemoglobin concentration effects of air pollution. The portable, user-independent, auto-in the blood (Table 2). None of the other biomarkers was sig- mated, and noninvasive equipment allowed us to study the mostnificantly associated with exposure as categorical or continuous relevant exposure in terms of indoor air within the homes ofvariables. However, an association between NC10–700 nm and elderly volunteers. In another experimental study using this8-iso-PGF2a was borderline significant (P 5 0.055), and a dou- technique, we included 29 young, healthy volunteers and foundbling in NC10–700nm corresponded to a 4.31 (95% CI, 20.09 to that the MVF score geometric mean was higher (2.14; 95% CI,8.91) % increase. After Bonferroni correction, none of the 2.08–2.19), reflecting the general consensus that aging increasessecondary endpoints changed significantly in accordance with susceptibility. In a study of patients referred for coronary angio-exposure as either a continuous or categorical variable. None of graphy, those showing endothelial dysfunction had an averagethese secondary endpoints correlated with MVF score (P > MVF score of 1.27, whereas patients without coronary endothe-0.099). lial dysfunction had an average MVF score of 1.78 (34), which is NO2 was not a significant predictor when included in the comparable to our healthy, elderly volunteers. Endothelium-above models of primary and secondary endpoints (P > 0.20). independent vasodilatation assessed by the peripheral arteryThe intake of medication with antiinflammatory properties had tone response to nitroglycerin was similar in the two groups inno significant effects on the predictive value of exposure on that study (34). These data support the application of RH-PATthese endpoints and was not significantly associated with any of as a convenient, noninvasive measure of EF.the markers studied here (P > 0.79). Finally, the order of ran- An assessment of endothelium-independent vasodilation usingdomization had no affect on the parameters studied. PAT to measure the hyperemic response to sublingual nitrogly- cerine would have clarified the mechanism by which particulate filtration improved MVF in our study. This was not performed,DISCUSSION as the administration of nitroglycerine in the home environmentEF constitutes an independent predictor of cardiovascular posed unacceptable risks of adverse effects to the elderly studyevents (24, 25), and the clinical implications of endothelial participants. Previous studies have suggested a role for oxida-dysfunction and the association between endothelial cell dys- tive stress and reduced nitric oxide bioavailability in mediatingfunction and cardiac events are well established (26, 27). There adverse vascular effects of PM (13, 31). As the digital hyperemichave been a number of studies showing associations between response is largely dependent on nitric oxide (35), we believeimproved EF after interventions of increased exercise (28), that the improvement in MVF after particle filtration in oursmoking cessation (29), and weight reduction (30). In this study, study represents a generalized improvement in EF.we investigated the effects of intervention using HEPA filtra- Limitations to the use of MVF score for EF assessment in-tion of indoor air particles for 48 hours. Our main finding was clude the limited data on associations with outcomes and othera significant improvement in MVF demonstrated by an in- risk factors such as smoking, hypertension, and hypercholester-creased flow-mediated vasoresponse after reduction of indoor olemia.air particles, most likely indicating a general improvement in We attempted to address the mechanisms of the associationEF. between MVF and particle exposure by means of biomarkers as A recent experimental study including 30 young healthy secondary endpoints. There was a borderline significant (P 5 0.055)volunteers was the first to demonstrate that inhalation of diesel association between particle NC10–700 nm and excretion of freeemission in high doses (300 mg/m3) could impair vasomotor re- 8-iso-PGF2a, a major F2-isoprostane, although this was far fromsponses to both endothelium-dependent (acetylcholine and significant after Bonferroni correction. The F2-isoprostanes are
  • 5. Brauner, Møller, Forchhammer, et al.: Indoor Particles Affect Vascular Function ¨ 423formed from arachidonic acid through nonenzymatic, free substantially to indoor NC, whereas vehicle emissions probablyradical–catalyzed reaction, and are reliable markers of lipid contributed less. Of the elements in the PM2.5 fraction, weperoxidation in a variety of conditions, including acute and found significant associations between individual increases inchronic inflammatory conditions (36). Excretion of free 8-iso- iron, copper, potassium, zinc, lead, and arsenic concentrationsPGF2a was elevated in cigarette smokers (37) and in subjects and reduced MVF score, whereas other elements, including theafter high-dose exposure to woodsmoke (38), and has been transition metals, vanadium, titanium, chromium, and nickel,shown to be associated with coronary artery disease (39). We had no effects. Iron and copper are typical elements associatedhave previously found correlations between lipid and protein with brake dust from vehicles, and their presence indoors mayoxidation products in plasma and personal exposure to black be due to penetration (20). Transition metals, including iron andcarbon in PM2.5 in individuals living in Copenhagen (40). copper, catalyze the formation of reactive oxygen species viaHowever, in the present study, we found no effect of particle Haber-Weiss reactions (50), which may explain the effects ob-exposure on protein oxidation assessed by plasma protein 2- served for iron and copper. However, the associations betweenaminoapidic semialdehyde, although this lack of effect may have the metals and the MVF score were not independent of thebeen due to the use of heparinized plasma, which is not ideal for PM2.5 mass, and we found no clear associations between thethe measurement. MVF score and markers of oxidative stress, as discussed pre- The biomarkers related to inflammation responses and viously here. Only potassium showed an independent associationcoagulation (IL-6, TNF-a), the acute-phase reactants (fibrino- with the MVF score. Potassium is a typical element associatedgen, CRP, and serum amyloid A), as well as coagulation factors with particles generated from the burning of biomass and smok-II, VII, and X showed no sign of effect. Previously, experimen- ing (51, 52), and indoor penetration of ambient particles fromtal exposure to concentrated ambient air particles at mean biomass burning, including long-range transport, and/or pene-concentrations of 120 mg/m3 caused increased fibrinogen levels tration of environmental tobacco smoke from neighboring apart-among 15 volunteers (41). In another study including 13 healthy ments, may have contributed to the effect on MVF. A relativelysubjects exposed to woodsmoke particles at 280 mg/m3, serum high level of indoor sulfur in the PM2.5 fraction, which cor-amyloid A as well as factor VIII in plasma and the factor VIII/ related with the urban background levels (Table E3), suggestsvon Willebrand factor ratio were significantly increased, substantial penetration of long-range transported particles. Thesewhereas IL-6, TNF-a, CRP, and fibrinogen showed no increase findings are in keeping with a recent source apportionment(38). High exposure to diesel emission at 300 mg/m3 caused study in Copenhagen, which showed associations between dailydiminished fibrinolytic capacity in other studies, whereas the cardiovascular-related admissions and daily urban backgroundplasma concentration of IL-6, TNF-a, von Willebrand factor concentrations of secondary sulfate-rich particles and biomassactivity, prothrombin fragments, CRP, and fibrinogen were un- particles in PM10 (53). Unfortunately, we could not addressaltered, despite reduced EF (13, 42). A recent study showed contributions from elemental carbon or organic compoundssome association between ambient PM levels and global co- directly in the present study.agulation function, whereas fibrinogen was unaffected (43). In NO2 was not a significant predictor of any of the endpoints,other panel studies, CRP levels have been found to be asso- and this result was expected, as the filtration of recirculatedciated with ambient or personal PM exposure (44–46). Accord- indoor air had no effects on NO2 levels. Furthermore, the intakeingly, acute-phase reactants, such as CRP, fibrinogen, and of minor medications had no effect on our results, which wasamyloid A in plasma, may respond at relatively high levels of also expected, as these medications were constant within theseparticle exposure, whereas cytokine levels in plasma do not individuals throughout the study, and each individual was his/seem to be sensitive for the detection of inflammatory responses her own control.in this respect. Moreover, there are no obvious associations The effects we show in this study were measured after a 48-between biomarkers of inflammation or oxidative stress and hour intervention. It is possible that the effects occurred muchMVF. In accordance with this observation, we found no sign of earlier, and it may also be speculated that further improvementcorrelations in the present study. The recent finding of associ- may occur after prolonged intervention by 6 months to 1 year,ation between expression of adhesion molecules on leukocytes and that this could result in further reduction in cardiovascularor in plasma and ambient levels of PM in observational panel risk in this healthy, elderly age group.studies suggest these as promising biomarkers for experimentalexposure studies, (46–48), although we found no effect on P-selectin in the present study. We found that PM exposure wassignificantly associated with a decrease in hemoglobin, without ConclusionsBonferroni correction, which is in agreement with earlier results The results of this study indicate that reduction of particles in(49); however, in another previous study, we observed a positive recirculated indoor air by filtration significantly improves MVFassociation with exposure to black smoke among young women in a healthy, nonsmoking, elderly population. The improvement(40). Our results may suggest that some component of PM could not be ascribed to significant reductions in inflammationcauses sequestration of red blood cells in the circulation, but the or oxidative stress by means of biomarkers. Indoor air sourceseffect on hemoglobin may also be due to chance, considering differ from outdoor air and indoor PM2.5 mass, rather than totalthe large number of secondary endpoints. numbers or surface area of particles had the most important Indoor air contains a mixture of PM from both indoor and association with MVF. Indoor air filtration represents a feasibleoutdoor sources with various chemical species and trace ele- means of reducing cardiovascular risk and suggests long-termments. We analyzed size distribution and elemental composi- and large-scale studies with cardiovascular events as endpoints.tion of particles within the PM2.5 and PM10–2.5 fractions in bothscenarios and found that PM2.5 mass was the only remaining Conflict of Interest Statement: None of the authors has a financial relationship with a commercial entity that has an interest in the subject of this manuscript.independent predictor of the MVF score in the reduced multi-exposure model, indicating that the indoor fine particle mass, Acknowledgment: The authors thank Janne Kjærsgaard for expert assistance withrather than numbers or surface area of particles, are important blood sampling, Betty Bugel Mogensen for NO2 measurements, Britta Krath for ¨ analysis of 2-aminoapidic semialdehyde, and technicians at National Environ-for the effect on EF. However, this may be due to the fact that mental Research Institute and Danish Building Research Institute for technicalindoor sources, such as cooking and candle burning, contributed assistance.
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