Research Nov-Dec 2013 | Volume 121 | Issue 11-12
Photochemically Altered Air Pollution Mixtures and Contractile Parameters in Isolated Murine Hearts before and after Ischemia
Rachel McIntosh-Kastrinsky,1 David Diaz-Sanchez,2 Kenneth G. Sexton,1 Corey M. Jania,3 Jose Zavala,1 Stephen L. Tilley,3 Ilona Jaspers,4 M. Ian Gilmour,2 Robert B. Devlin,2 Wayne E. Cascio,2,5 and Haiyan Tong2
Background: The cardiopulmonary effects of the individual criteria air pollutants have been well investigated, but little is known about the cardiopulmonary effects of inhaled multipollutant mixtures that more realistically represent environmental exposures.
Objectives: We assessed the cardiopulmonary effects of exposure to photochemically altered particle-free multipollutant mixtures.
Methods: We exposed mice to filtered air (FA), multipollutant mixtures, or ozone (O3) for 4 hr in a photochemical reaction chamber. Eight hours after exposure, we assessed cardiac responses using a Langendorff preparation in a protocol consisting of 20 min of global ischemia followed by 2 hr of reperfusion. Cardiac function was assessed by measuring the index of left-ventricular developed pressure (LVDP) and contractility (dP/dt) before ischemia. On reperfusion after ischemia, recovery of postischemic LVDP and size of infarct were examined. We used bronchoalveolar lavage (BAL) cell counts to assess lung inflammation.
Results: Exposure to the multipollutant mixtures decreased LVDP, baseline rate of left ventricular contraction (dP/dtmaximum), and baseline rate of left ventricular relaxation (dP/dtminimum) compared with exposure to FA. Exposure to O3 also decreased heart rate and dP/dtminimum. Time to ischemic contracture was prolonged in the multipollutant-mixture group relative to that in the FA group. Mice in the multipollutant-mixture group had better recovery of postischemic LVDP and smaller infarct size. Exposure to multipollutant mixtures and to O3 exposure increased numbers of macrophages in the BAL fluid.
Conclusions: Exposure to photochemically altered urban air pollution appears to affect cardiac mechanics in isolated perfused hearts. Inhalation of acute multipollutant mixtures decreases LVDP and cardiac contractility in isolated non-ischemic murine hearts, prolongs ischemic contracture, increases postischemic recovery of LVDP, and reduces infarct size.
Citation: McIntosh-Kastrinsky R, Diaz-Sanchez D, Sexton KG, Jania CM, Zavala J, Tilley SL, Jaspers I, Gilmour MI, Devlin RB, Cascio WE, Tong H. 2013. Photochemically altered air pollution mixtures and contractile parameters in isolated murine hearts before and after ischemia. Environ Health Perspect 121:1344–1348; http://dx.doi.org/10.1289/ehp.1306609
Address correspondence to H. Tong, Environmental Public Health Division, NHEERL/U.S. EPA, 109 T.W. Alexander Dr., Research Triangle Park, NC 27711 USA. Telephone: (919) 966-4993. E-mail: Tong.email@example.com
We thank B. O’Brien for excellent technical assistance in the execution of this study. We also thank Y. Ge for review of the manuscript.
The U.S. Environmental Protection Agency (EPA) Intramural Research Program supported this research. This work was also supported in part by the U.S. EPA Cooperative Agreement CR83346301 with the Center for Environmental Medicine, Asthma and Lung Biology at the University of North Carolina at Chapel Hill.
The research described in this article has been reviewed by the National Health and Environmental Effects Research Laboratory, U.S. EPA, and approved for publication. The contents of this article should not be construed to represent agency policy nor does mention of trade names or commercial products constitute endorsement or recommendation for use.
The authors declare they have no actual or potential competing financial interests.
Received: 4 February 2013
Accepted: 17 October 2013
Advance Publication: 22 October 2013
Final Publication: 27 November 2013
Epidemiological studies have linked acute and chronic ambient air pollution exposure with cardiovascular diseases and shown that air pollution exposure increases the risk of mortality, ischemic heart disease, heart failure, and arrhythmias (Brook et al. 2010). The Clean Air Act (1970) and the Clean Air Act Amendments (1990) established National Air Quality Standards for individual “criteria pollutants.” Consequently, air pollution health effects research studies have largely focused on characterizing the effects of exposure to these pollutants on an individual basis. However, “real-world” air pollution is far more complex than exposure to an individual agent because real-world air pollution contains freshly emitted primary aerosol as well as photochemically aged secondary aerosols formed in the atmosphere during the oxidation of gas-phase precursors (Kanakidou et al. 2005). There is a growing realization that a multipollutant experimental approach is needed to understand the relevant modes of action of ambient air pollutant mixtures on human health (Dominici et al. 2010). However, there is currently a paucity of data on how complex mixtures impact key target organ systems associated with morbidity and mortality. To fill this critical knowledge gap, we tested whether inhaled exposure to particle-free complex mixtures representative of gaseous mixtures found in urban environments can modulate pulmonary inflammation and cardiac mechanics.
We used an environmental photochemical reaction chamber located at the University of North Carolina at Chapel Hill to generate model multipollutant-mixture atmospheres. The chamber uses sunlight to imitate the natural photochemistry of urban mixtures and produce a combination of compounds that is similar in composition to that found in urban multipollutant mixtures (Jeffries 1995; Sexton et al. 2004). Previous in vitro studies have utilized these chambers to expose individual cell cultures to examine the toxicity of air pollution mixtures and have shown that exposure to photochemically altered particle-free urban mixtures causes significant inflammatory responses (Sexton et al. 2004) and greater genetic alterations (Rager et al. 2011) compared with exposure to primary urban mixtures.
Experimental studies have demonstrated the ability of individual air pollutants to cause cardiopulmonary toxicity in animals. For example, acute exposure to particulate matter can increase pulmonary and systemic inflammation and lung injury, cause vascular dysfunction, alter heart rate variability, induce arrhythmia, and enhance cardiac ischemic injury (Brook et al. 2010). We (Cho et al. 2009; Tong et al. 2010) and others (Cozzi et al. 2006) have shown that particulate matter exposure can enhance cardiac ischemia/reperfusion injury in animals. However, extrapolation to multipollutant mixtures is far from simple. For instance, the redox cycling potential of a mixture, which is thought to be an important predictor of generation of inflammation, may be very different than that of its constituent parts. To address this issue, we tested the hypothesis that photochemically aged particle-free multipollutant mixtures can cause inflammation and impair cardiac function. Using a murine model, we evaluated the effects of multipollutant-mixture exposure on cardiovascular and pulmonary end points. We report here that exposure to multipollutant mixtures at concentrations that produce only minimal pulmonary effects significantly affect cardiac function—including decreased left ventricular developed pressure and contractility—but unexpectedly reduce cardiac ischemia/reperfusion injury.
Methods and Materials
Experimental animals. Mice were maintained at 22°C with a 12-hr light/dark cycle and free access to food (ProLab RMH 3000; PMI Nutrition, Saint Louis, MO) and water. We purchased 45 female C57BL/6 mice (5 months of age, mean weight 23.9 ± 0.39 g) from Jackson Laboratory (Bar Harbor, ME) and they were acclimated for 2 months before they were used. All experimental procedures were performed in compliance with protocols approved by the University of North Carolina at Chapel Hill Institutional Animal Care and Use Committee according to National Institutes of Health guidelines (National Research Council 2011). The animals were treated humanely and with regard for alleviation of suffering.
Generation of photochemical urban mixtures. The University of North Carolina at Chapel Hill’s outdoor environmental photochemical reaction chamber was used to generate exposure atmospheres. Synthetic Urban Mix (Scott Specialty Gases, Plumsteadville, PA), a volatile organic compound (VOC) mixture (Jeffries 1995), and NOx [nitric oxide (NO) and nitrogen dioxide (NO2)] were used as the starting materials for the test atmosphere. The synthetic particle-free urban mixture contains 55 different hydrocarbons at specific ratios that represent chemicals present in urban atmospheres (Sexton et al. 2004). On the morning of the exposure, the chamber was humidified naturally by pre-flushing with HEPA-filtered ambient air. At 0700 hours, the Synthetic Urban Mix volatile organics were drawn from a gas cylinder into the photochemical reaction chamber while a liquid mixture containing less-volatile organics was injected into the chamber. NOx was drawn from a gas cylinder (AirGas, National Welders, Morrisville, NC) into the chamber to establish a test atmosphere containing 2 ppm NOx.
Chemical constituents inside the chamber during the experiment were assessed by gas measurement methods as described previously (Rager et al. 2011). NO and NO2 levels were measured once per minute using a Teledyne model 9841 NOx analyzer (Teledyne Monitor Labs, Englewood, CO). Ozone (O3) was measured every minute with a Teledyne model 9811 monitor. Concentrations of these compounds were averaged during the exposure. Other secondary products such as the carbonyl-containing aldehydes and ketones were measured every 15 min by gas chromatography and mass spectrometry. Because the O3 level was elevated to 0.243 ppm in the chamber, the same concentration of O3 was used in the single-pollutant O3 exposure. O3 was generated from oxidized air using an O3 generator (model OL80A; Ozone Services, Yanco Industries, Burton, British Columbia, Canada).
Animal exposure. Because the photochemical reaction depends on the weather condition and because the multipollutant mixtures generated are not reproducible, mice were exposed in groups to photochemically aged particle-free multipollutant mixtures (n = 15), 0.245 ppm O3 (n = 14), or filtered air (FA; n = 16) for 4 hr (2000–2400 hours) during their dark cycle on 3 separate days in an outdoor photochemical reaction chamber. One group of mice per exposure (n = 7 in the multipollutant-mixture group; n = 6 in the O3 group; n = 8 in the FA group) was used for the isolated heart perfusion and the other mice (n = 8 per group) were used for assessing lung inflammation.
Cardiac function. As described previously (Tong et al. 2009), 8–11 hr after exposure, mice were anesthetized with an intraperitoneal (ip) injection of sodium pentobarbital (80 mg/kg body weight). After injecting the mice with intravenous heparin (100 units), the hearts were excised rapidly and placed in ice-cold Krebs–Henseleit buffer. The aortas were cannulated and perfused retrograde at a constant pressure of 100 cmH2O. The non-recirculating perfusate was Krebs–Henseleit buffer containing 120 mmol/L sodium chloride, 5.9 mmol/L potassium chloride, 1.2 mmol/L magnesium sulfate, 1.75 mmol/L calclium chloride, 25 mmol/L sodium bicarbonate, and 11 mmol/L glucose. The buffer was aerated with 95% oxygen and 5% carbon dioxide, and maintained at pH 7.4 and 37°C.
For assessment of contractile function, a latex balloon on the tip of a polyethylene catheter was inserted through the left atrium into the left ventricle. The catheter was connected to a pressure transducer (model 041500503; Argon Medical Devices, Athens, TX) at the same height as the heart. The pressure of the left ventricular balloon was inflated to 0–5 cmH2O. We used a PowerLab data acquisition system (AD Instruments, Milford, MA) to collect and process the heart rate, left ventricular developed pressure [LVDP, i.e., LV peak minus end-diastolic pressure (LVEDP)], and contractility (dP/dt) data. All hearts had been perfused for 25 min when the baseline measurements were taken. We then initiated 20 min of global no-flow ischemia followed by 2 hr of reperfusion. Onset of ischemic contracture was detected when the left ventricular pressure began to increase during ischemia. We measured recovery of LVDP, expressed as a percentage of the initial pre-ischemic LVDP, at 40 min of reperfusion after 20 min of ischemia.
Cardiac necrosis evaluation. As described previously by Tong et al. (2009, 2010), at the end of 2 hr of reperfusion, we perfused the hearts with 15 mL of a 1% solution of 2,3,5-triphenyltetrazolium chloride (TTC) dissolved in Krebs–Henseleit buffer, incubated them in 1% TTC at 37°C for 10 min, and then fixed them in formalin. We measured the area of necrosis by taking cross-sectional slices through the ventricles, which were then photographed using a digital camera mounted on a stereo-microscope. We quantified the resulting images by measuring the areas of stained (viable tissue) versus unstained tissue (infarct) using Adobe Photoshop (Adobe Systems, San Jose, CA). Infarct size was expressed as a percentage of the total ventricular section and averaged from four images.
Bronchoalveolar lavage. Lung inflammation has been shown to be one of the pathways that mediate the cardiac effects (Brook et al. 2010); therefore, we examined whether exposure to multipollutant mixtures or to O3 resulted in lung inflammation. Twelve hours after exposure, mice were anesthetized with an ip injection of pentobarbital sodium (50 mg/kg). The lungs were lavaged five times with 1 mL 1× Hanks’ Balanced Salt Soultion (HBSS; Gibco, Life Technologies, Carlsbad, CA) and cellular components of the bronchoalveolar lavage (BAL) fluid were separated by centrifugation at 1,500 rpm for 10 min at 4oC. The cell pellet was resuspended in 500 μL HBSS and total cells were counted using a hemocytometer. Cytospin preparations were made and stained with Hema 3 (Fisher Scientific, Waltham, MA) to evaluate the BAL cellular composition.
Statistical analysis. Data are expressed as mean ± SE. Nonparametric analyses were performed because the data were not normally distributed. We performed comparisons among the multipollutant-mixture, O3, and FA control groups by Kruskal–Wallis U-test followed by Dunn’s multiple comparison test. We used the Mann–Whitney U-test to compare the multipollutant-mixture or O3 groups with the FA control group. The statistical significance level was set at p < 0.05.
Composition of particle-free photochemically generated multipollutant mixtures. Photochemical reactions of the original hydrocarbons and NOx mixtures generated > 300 carbonyl secondary products. Among those products, the levels of detected VOC compounds estimated in the chamber are listed in Table 1. As reported by Rager et al. (2011), the average chamber levels of NO and NO2 decreased throughout the day, and levels of secondary chemical products such as O3, formaldehyde, and acetaldehyde increased. The photochemical chamber contained 0.243 ppm of O3 and secondary carbonyls. The formaldehyde level in the photochemical chamber was 5× higher than that in the O3 and FA control chambers, and the acetaldehyde level was elevated in the photochemical chamber but not detectable in the O3 and FA control chambers. No particulate matter or secondary organic aerosol was formed within the chamber.
Cardiac effects. When compared with the FA control, the baseline heart rate prior to ischemia decreased with O3 exposure, whereas heart rate was unchanged in the hearts of mice exposed to the particle-free multipollutant mixtures (Figure 1A). We observed no differences in baseline coronary artery flow rate at constant pressure between the multipollutant-mixture or O3 groups compared with the FA control group (Table 2). However, hearts from the multipollutant-mixture group had lower baseline LVDP (69.2 ± 16.0 cmH2O) compared with the FA group (146.4 ± 14.8 cmH2O; p < 0.05) although there was no significant difference between the FA- and O3-groups (134.2 ± 5.4 cmH2O) (Figure 1B). Exposure to multipollutant mixtures or O3 decreased baseline left ventricular contractility. The baseline rate of contraction (dP/dtmaximum; maximum first derivative of the change in left ventricular pressure/time) was lower in the multipollutant-mixture group (2,764 ± 558 cmH2O/sec) compared with the FA group (5,405 ± 400 cmH2O/sec; p < 0.05) (Figure 2A). Yet, the change in dP/dtmaximum did not differ between the O3 (4,070 ± 704 cmH2O/sec) and FA group. The baseline rate of relaxation (dP/dtminimum; minimum first derivative of the change in left ventricular pressure/time) was decreased by exposure to the multipollutant mixtures (–1,822 ± 335 cmH2O/sec; p < 0.01) and O3 exposure (–2,477 ± 407 cmH2O/sec; p < 0.05) when compared with the FA control (–3,675 ± 242 cmH2O/sec) (Figure 2B).
Compared with the FA group (13.2 ± 1.4 min), time to ischemic contracture was not affected in the O3 group (14.0 ± 1.8 min), but was prolonged in the multipollutant-mixture group during the 20 min of ischemia (17.3 ± 0.5 min; p < 0.05). There was also an increase in postischemic recovery of LVDP at 40 min after reperfusion in the multipollutant-mixture group compared with the FA control group (70.7 ± 23.7% for multipollutant mixtures vs. 21.0 ± 7.1% for FA; p = 0.05) (Figure 3A). Infarct size was smaller in the multipollutant-mixture group (39.6 ± 6.6%) compared with the FA control (57.3 ± 4.6% for FA; p < 0.05) (Figure 3B). By 40 min of reperfusion, heart rate, LVDP, contractility, and coronary flow rate were not different among the multipollutant-mixture, O3, and FA groups (Table 2).
Airway inflammation. Compared with the FA controls, the BAL from mice exposed to the multipollutant mixtures or O3 showed an increase in the number of macrophages (Figure 4). However, we found no influx of neutrophils or other cell types after any exposure.
Although our understanding of the health effects of single pollutants has advanced considerably over the last several decades, knowledge of the effects of multipollutant mixtures is limited. In the present study we used a photochemical reaction chamber to generate particle-free urban-like multipollutant mixtures for the purpose of evaluating the pulmonary and cardiac responses in mice to inhalation of an atmosphere containing complex multipollutant mixtures or O3 at the same concentration as present in the multipollutant mixtures. Thus, any difference in measured responses between these two exposures can be ascribed to effects of the multipollutant mixtures. Short-term inhalation of photochemically altered particle-free multipollutant mixtures and O3 alone depressed cardiac contractility (dP/dt) in the isolated perfused heart. However, exposure to the particle-free multipollutant mixtures delayed the onset of ischemic contracture and preserved contractile function during reperfusion in isolated mouse hearts. In addition, although we found no significant difference in the mechanical responses between the multipollutant mixtures and O3 alone, the magnitude of the effect of O3 alone was always less than the effect of the multipollutant mixtures. Thus, it appears that one or more of the multipollutant-mixture’s component(s) contribute to an additional effect beyond that of O3 alone.
Experimental studies by Gordon (2007) implicated particulate mass and the physicochemical properties of air pollutants as determinants of the health effects of air pollution inhalation. In particular, organic components of air pollution are thought to play an important role in affecting biological responses (Castranova et al. 2001). In the present study, mice were exposed to particle-free photochemically altered products of hydrocarbons and NOx, indicating that the cardiac effects measured following exposure resulted from gaseous components of multipollutant mixtures. We have previously exposed cultured lung cells to similar multipollutant mixtures in the photochemical reaction chamber and showed that gaseous products elicited biological and biochemical responses in the absence of particles (Sexton et al. 2004). Furthermore, animal studies have shown that spontaneously hypertensive and mildly cardiomyopathic rats exposed to filtered diesel exhaust exhibited either a similar degree or a greater magnitude of electrophysiological changes compared with exposure to whole diesel exhaust (Carll et al. 2012; Lamb et al. 2012), implying that gaseous components of air pollution might be driving the cardiovascular effects.
As shown previously (Sexton et al. 2004), levels of secondary chemical products such as O3, formaldehyde, acetaldehyde, and many volatile and semivolatile organic hydrocarbons increase as the photochemical reaction progresses. Therefore, the animals in our study were exposed to higher levels of secondary products, which may elicit biological effects on the cardiovascular system. Secondary products formed during the photochemical reactions can induce more robust inflammatory responses (Sexton et al. 2004) and greater genomic changes (Rager et al. 2011) in cultured lung cells. Secondary products, such as O3 generated during the photochemical reactions, may have contributed to the biological effects, including the O3-induced heart rate and baseline rate of left ventricular relaxation changes that we report here. Epidemiological studies have linked short-term O3 exposure with cardiovascular and respiratory mortality in 95 large U.S. communities (Bell et al. 2004). O3 exposure has also been associated with increased hospital admissions for heart failure (Yang 2008). Most recently, a controlled human-exposure study (Devlin et al. 2012) demonstrated that short-term O3 exposure increased pulmonary and systemic inflammation, altered autonomic control of heart rhythm, and induced changes in blood proteins involved in fibrinolysis. In addition, an animal study (Chuang et al. 2009) demonstrated that 5 days (8 hr/day) of 0.5 ppm O3 exposure in mice altered heart rates and mean blood pressure, inhibited endothelial-dependent vasorelaxation, and induced mitochondrial damage and atherogenesis.
The levels of the secondary products, formaldehyde and acetaldehyde, increased during the photochemical process in this study. Formaldehyde and acetaldehyde occur naturally in the environment and are produced in forest fires, automobile exhaust, and tobacco smoke. The ambient formaldehyde concentration was in the range of 0.4–7.5 ppb with a mean value of 2.2 ppb in New York City in the summertime in 2009 (Lin et al. 2012) and the ambient concentration of acetaldehyde averaged 5 μg/m3 (National Toxicology Program 2011). In the present study, exposure to formaldehyde may have contributed to the observed cardiac-depressive activity of the inhaled particle-free multipollutant mixtures. Similarly, acetaldehyde, another component of the multipollutant mixtures, could also affect cardiac function. Acetaldehyde has been shown to disrupt calcium ion (Ca2+) handling in the myocardium and to disturb cardiac excitation-contraction coupling (Oba et al. 2008), leading to reduced cardiac contractility. Therefore, the cardiac-depressive effects of inhalation of the multipollutant mixtures used in this study may have resulted from acetaldehyde-induced myocardial toxicity. Above all, the respiratory responses to volatile and semivolatile organic components of multipollutant mixtures, such as O3, have been investigated in the past; yet the cardiovascular effects of those components are not well known. More research is needed to evaluate the cardiovascular effects of exposure to these ubiquitous air contaminants.
The mechanistic basis for the cardiac-mechanical effects of exposure to multipollutant mixtures and O3 was not explored in this study. However, there are several pathways by which the air pollution mixtures could affect the cardiovascular system (Brook et al. 2010). Oxidative stress from multipollutant-mixture components such as O3 could cause systemic oxidative stress, resulting in myocardial contractile dysfunction. In addition, activation of pulmonary receptors could initiate a neurocardiogenic effect, producing an intracardiac response affecting cardiac cellular function. It is also possible that some components of multipollutant mixtures might translocate into the circulation, with attendant direct oxidative effects on the heart and vasculature. We detected only macrophage accumulation in BAL in this study, suggesting that airway inflammation may not mediate the cardiac effects of inhalation to multipollutant mixtures or to O3.
The decreased LVDP and cardiac contractility, delayed ischemic contracture, and preserved contractility during reperfusion consequent to exposure to inhaled multipollutant mixtures could indicate altered intracellular Ca2+ regulation in the myocardium. The pro-redox components of multipollutant mixtures could modulate the cardiac myocytes’ Ca2+ handling by reducing the intracellular Ca2+, or cause a change in the sensitivity of the contractile proteins to Ca2+, resulting in decreased cardiac contractility. On the other hand, the reduced intracellular Ca2+ overload during ischemia is associated with the preservation of mitochondrial function and adenosine triphosphate stores (Kowalchuk and Nesto 1989), as suggested by the multipollutant mixtures’ induced delay of ischemic contracture and better recovery of postischemic LVDP and smaller infarct size during reperfusion. Future studies are needed to better understand the role of intracellular Ca2+ regulation in mediating cardiovascular physiological effects from air pollution exposure.
In this study we used a perfused isolated heart model to evaluate the ventricular function. However, isolated heart models lack innervation and blood supply and, therefore, lack influence by autonomic and hormonal control: This could alter findings in intact hearts.
Inhalation of particle-free photochemically altered multipollutant mixtures affects cardiac function in isolated mouse hearts. Specifically, inhalation of multipollutant mixtures depressed cardiac contractility in isolated non-ischemic hearts, and delayed ischemic contracture and preserved cardiac contractility in reperfused hearts, while eliciting mild pulmonary inflammation evidenced only by macrophage accumulation. Future studies are needed to identify the active components of photochemical reaction products responsible for the effects on myocardial mechanical performance as well as the mechanisms that underlie the cardiac effects.
Brook RD, Rajagopalan S, Pope CA III, Brook JR, Bhatnagar A, Diez-Roux AV, et al. 2010. Particulate matter air pollution and cardiovascular disease: an update to the scientific statement from the American Heart Association. Circulation 121(21):2331–2378.
Carll AP, Hazari MS, Perez CM, Krantz QT, King CJ, Winsett DW, et al. 2012. Whole and particle-free diesel exhausts differentially affect cardiac electrophysiology, blood pressure, and autonomic balance in heart failure–prone rats. Toxicol Sci 128(2):490–499.
Castranova V, Ma JY, Yang HM, Antonini JM, Butterworth L, Barger MW, et al. 2001. Effect of exposure to diesel exhaust particles on the susceptibility of the lung to infection. Environ Health Perspect 109(suppl 4):609–612.
Cho SH, Tong H, McGee JK, Baldauf RW, Krantz QT, Gilmour MI. 2009. Comparative toxicity of size-fractionated airborne particulate matter collected at different distances from an urban highway. Environ Health Perspect 117:1682–1689; doi: 10.1289/ehp.0900730.
Chuang GC, Yang Z, Westbrook DG, Pompilius M, Ballinger CA, White CR, et al. 2009. Pulmonary ozone exposure induces vascular dysfunction, mitochondrial damage, and atherogenesis. Am J Physiol Lung Cell Mol Physiol 297(2):L209–L216.
Cozzi E, Hazarika S, Stallings HW III, Cascio WE, Devlin RB, Lust RM, et al. 2006. Ultrafine particulate matter exposure augments ischemia-reperfusion injury in mice. Am J Physiol Heart Circ Physiol 291(2):H894–H903.
Lamb CM, Hazari MS, Haykal-Coates N, Carll AP, Krantz QT, King C, et al. 2012. Divergent electrocardiographic responses to whole and particle-free diesel exhaust inhalation in spontaneously hypertensive rats. Toxicol Sci 125(2):558–568.
Lin Y, Schwab JJ, Demerjian KL, Bae MS, Chen WN, Sun Y, et al. 2012. Summertime formaldehyde observations in New York City: ambient levels, sources and its contribution to HOx radicals. J Geophys Res 117:D08305; doi: 10.1029/2011JD016504.
National Toxicology Program. 2011. Acetaldehyde: CAS No. 75-07-0. In: Report on Carcinogens. 12th ed. Washington, DC:National Toxicology Program, 21–24. Available: http://ntp.niehs.nih.gov/ntp/roc/twelfth/roc12.pdf [accessed 5 November 2013].
Oba T, Maeno Y, Nagao M, Sakuma N, Murayama T. 2008. Cellular redox state protects acetaldehyde-induced alteration in cardiomyocyte function by modifying Ca2+ release from sarcoplasmic reticulum. Am J Physiol Heart Circ Physiol 294(1):H121–H133.
Rager JE, Lichtveld K, Ebersviller S, Smeester L, Jaspers I, Sexton KG, et al. 2011. A toxicogenomic comparison of primary and photochemically altered air pollutant mixtures. Environ Health Perspect 119:1583–1589; doi: 10.1289/ehp.1003323.
Tong H, McGee JK, Saxena RK, Kodavanti UP, Devlin RB, Gilmour MI. 2009. Influence of acid functionalization on the cardiopulmonary toxicity of carbon nanotubes and carbon black particles in mice. Toxicol Appl Pharmacol 239(3):224–232.
EHP is pleased to announce that it is now operating under a continuous publication workflow! As indicated in a previous announcement, continuous publication allows EHP to post new content online throughout the month, as each paper becomes ready for an issue. This gets content out to our readers much more quickly than the old issue-based model, and unlike our previous Advance Publication model, these are final, edited articles. (more…)
EHP is pleased to announce that Prenatal Exposure to Glycol Ethers and Neurocognitive Abilities in 6-Year-Old Children: The PELAGIE Cohort Study, published in EHP on 14 October 2016, has been selected by the Children’s Environmental Health Network (CEHN) as its May 2017 Article of the Month. CEHN Article of the Month summaries discuss the potential policy implications of current children’s environmental health research. The CEHN summary can be viewed here.