Surface area of particle administered versus mass in determining the pulmonary toxicity of ultrafine and fine carbon black: comparison to ultrafine titanium dioxide
© Sager and Castranova; licensee BioMed Central Ltd. 2009
Received: 30 September 2008
Accepted: 04 May 2009
Published: 04 May 2009
Nanoparticles are characterized by having a high surface area per mass. Particulate surface area has been reported to play an important role in determining the biological activity of nanoparticles. However, recent reports have questioned this relationship. This study was conducted to determine whether mass of particles or surface area of particles is the more appropriate dose metric for pulmonary toxicity studies. In this study, rats were exposed by intratracheal instillation to various doses of ultrafine and fine carbon black. At 1, 7, or 42 days post-exposure, inflammatory and cytotoxic potential of each particle type was compared on both a mass dosage (mg/rat) as well as an equal surface area dosage (cm2 of particles per cm2 of alveolar epithelium). In an additional study, the pulmonary responses to instillation of ultrafine carbon black were compared to equivalent particle surface area doses of ultrafine titanium dioxide.
Ultrafine carbon black particles caused a dose dependent but transient inflammatory and cytotoxic response. On a mass basis, these responses were significantly (65 fold) greater than those for fine sized carbon black. However, when doses were equalized based on surface area of particles given, the ultrafine carbon black particles were only slightly (non-significantly) more inflammogenic and cytotoxic compared to the fine sized carbon black. At one day post-exposure, inflammatory potencies of the ultrafine carbon black and ultrafine titanium dioxide particles were similar. However, while the pulmonary reaction to ultrafine carbon black resolved with time, the inflammatory effects of ultrafine titanium dioxide were more persistent over a 42 day post-exposure period.
These results indicate that for low toxicity low solubility materials, surface area of particles administered rather than mass burden of particles may be a more appropriate dose metric for pulmonary toxicity studies. In addition, ultrafine titanium dioxide appears to be more bioactive than ultrafine carbon black on an equivalent surface area of particles delivered basis.
Nanotechnology is considered to be one of the world's most promising new technologies, able to impact all phases of life, just as the industrial revolution did in the past two centuries. Utilizing the quantum properties of atoms and molecules, nanotechnology proposes the construction of novel molecular devices possessing extraordinary properties. However, both epidemiological and toxicological studies have contributed to a body of evidence suggesting that nano or ultrafine particles may induce or exaggerate a number of adverse biological effects. It has been suggested that nanoparticles may interfere with a number of molecular processes that should be considered before such particles are brought into wide commercial use .
Recent reports indicate that there can be considerable potential for exposure to nanoparticles in the workplace, especially during transfer, weighing, blending, and cleaning processes [2, 3]. There is also interest and debate as to whether low solubility, ultrafine particles should be regulated differently from fine size particles of the same composition .
When evaluating exposure-dose-effect relationships of inhaled particles, the definition and determination of dose is crucial. Conventionally and conveniently, doses usually are expressed in terms of particle mass. However, when the pulmonary inflammatory potential of ultrafine TiO2 was compared to fine size TiO2, particle surface area was found to be a better predictor of bioactivity than particle mass burden delivered . Studies, such as this with nanoparticles, have been used to support the hypotheses that particle surface area is important in determining pathology  and inflammation . However, recent reports by Warheit et al. [8, 9] have questioned this hypothesis.
In general, for a fixed mass of particles, surface area increases as particle size becomes smaller. Thus, a dose-dependence on particle surface area may explain the greater toxicity of nanoparticles compared with an equal mass of fine particles of the same material [10, 11]. The finding that particle surface area rather than mass appears to be a more appropriate metric of dose for predicting pulmonary inflammation may imply a need to reconsider exposure assessment practices for workplaces producing or using nanoparticles. Currently, occupational exposure limits for airborne dusts are defined in terms of mass per m3 of air . In support for the importance of exposure standards, Serita et al.  conducted an experiment that exposed rats to metallic ultrafine nickel at the Japanese regulated occupational exposure level (OEL). This OEL was based on data for fine nickel particles. However, the exposure to OEL concentrations in the form of ultrafine nickel caused severe lung injury after a single exposure . This finding supports the concept that surface area is the dose measure that predicts pulmonary response, rather than mass, and this has far reaching potential consequences for occupational standards that are based on mass .
Therefore, if in fact the inflammatory potential of a particle is driven by surface area rather than mass, then a given airborne mass concentration of a material in the form of fine particles could be much less inflammogenic than the same airborne mass concentration of same material in the form of ultrafine particles. Therefore, determining if high surface area of nanoparticles is a driver for inflammatory potential is of great importance for development of protective occupational health measures.
The present study aims to address the issue of whether, for low toxicity low solubility materials, mass or surface area of particles administered is a more appropriate dose metric when assessing pulmonary toxicity of nanoparticles. To address this question, in vivo intratracheal exposures of rats to ultrafine carbon black (UFCB) and fine carbon black (FCB) were conducted. Animals were exposed to carbon black particles based on mass, and dose was normalized to surface area of particles administered. Resulting pulmonary damage and inflammation were compared on a mass dose and surface area of carbon black particles administered to determine which dose metric was more appropriate in evaluating nanoparticle toxicity. In additional experiments, the pulmonary activity of ultrafine carbon black (UFCB) was compared to ultrafine titanium dioxide (UFTiO2) on an equivalent surface area of particles delivered basis.
UFCB and FCB suspended in acellular bronchoalveolar lavage fluid (BALF) were administered to Fischer 344 rats via intratracheal instillation to assess pulmonary toxicity. The dose of particles administered was given on a mass basis (mg/rat) and was also normalized to surface area of particles administered per alveolar epithelial surface area (cm2/cm2) using a value for alveolar epithelial surface area in the rat reported by Stone et al. . The surface areas of the respective particles (269.0 m2/g for UFCB and 8.1 m2/g for FCB, respectively) were determined by the BET gas absorption technique . This comparison of mass and surface area doses was conducted to assess whether surface area of particles administered is the more appropriate dose metric that should be considered when assessing nanoparticle pulmonary toxicity parameters. Pulmonary toxicity parameters measured included PMN number, LDH activity, albumin levels, inflammatory mediators (TNF-α, MIP-2, and IL-1β), as well as zymosan-stimulated chemiluminescence and NO dependent chemiluminescence.
Comparison of pulmonary toxicity of UFCB and FCB
Effect of Exposure to UFCB vs. FCB (High Dose) on pulmonary responses.
1.5 ± 0.2
1.1 ± 0.1
1.0 ± 0.1
22.1 ± 0.8*
8.1 ± 0.3*
4.2 ± 0.7*
15.5 ± 0.4*
5.7 ± 0.2*
3.3 ± 0.2*
49.3 ± 1.4
43.8 ± 0.8
45.1 ± 1.7
179.1 ± 6*
116.3 ± 4*
84.6 ± 2*
135.3 ± 6*
88.6 ± 2*
71.9 ± 1*
0.21 ± 0.1
0.12 ± 0.01
0.18 ± 0.02
0.48 ± 0.02*
0.31 ± 0.025*
0.32 ± 0.01*
0.40 ± 0.01*
0.25 ± 0.01*
0.26 ± 0.01*
24.8 ± 0.5
28.2 ± 0.6
32.2 ± 0.6
45.3 ± 2*
50.4 ± 1*
60.1 ± 1*
30.9 ± 0.8
34.3 ± 1
38.6 ± 0.9
437.7 ± 14
497.2 ± 22
476.5 ± 22
544.1 ± 34*
727.8 ± 29*
615.2 ± 21*
384.9 ± 22
485.8 ± 22
532.9 ± 22
58.1 ± 4
69.7 ± 5
70.5 ± 7
184.9 ± 10*
213.6 ± 8*
262.8 ± 9*
78.6 ± 6
83.7 ± 9
115.7 ± 12
Zym. Stim. Chemi.
3.14 ± .08
3.06 ± .09
3.22 ± .30
7.28 ± .13*
5.35 ± .12*
3.85 ± .55
4.48 ± .10*
4.06 ± .04*
2.96 ± 41
NO Dep. Chemi.
0.68 ± .05
0.52 ± .06
0.49 ± .07
4.2 ± .06*
3.6 ± .05*
2.4 ± .40*
4.0 ± .04*
1.7 ± .05*
1.3 ± .04
Potency difference between UFCB and FCB when analyzed on a mass vs. surface area.
Zym. Stim. Chemi.
NO Dep. Chemi.
In regards to the other pulmonary toxicity parameters assessed for UFCB and FCB exposure, the same trend was noted. LDH activity in BALF was measured to assess cellular cytotoxicity, and BALF albumin levels were analyzed to assess air/blood barrier injury. Exposure to either UFCB or FCB caused a dose dependent cytotoxicity which declined with time post-exposure (data similar to figure 1 not shown). However, at the high dose, LDH activity remained significantly elevated over control at all post-exposure time points (Table 1). Effects on albumin levels showed the same trend as LDH activity, with exposure to the high dose of both UFCB and FCB causing a significant increase in albumin levels over control at all post-exposure time points (Table 1). On a mass dose basis, a significantly greater mass dose of FCB (65 fold higher) was required at all post-exposure time points, to obtain the same responses as seen with UFCB exposure in regards to LDH activity and albumin levels (Table 2). However, when dose was normalized to surface area of particles administered, the UFCB exposure produced LDH activity and albumin levels that were at most only 2-fold greater than the FCB exposure at all post-exposure time points analyzed (Table 2). When dose-response curves assessing LDH activity and albumin levels based on surface area of particles administered between UFCB and FCB exposure were assessed using a linear regression curve analysis with a 95% confidence interval (data similar to figure 2 not shown), there was no significant difference between the two curves at any post-exposure time points.
IL-1β, TNF-α, and MIP-2 mediator levels in the BAL were also measured for UFCB and FCB exposure at all post-exposure time points. The highest dose of UFCB caused a significant increase in these mediator levels over control values at all post-exposure time points. However, FCB exposure did not increase mediator levels significantly over control at any post-exposure time point (Table 1). For all three mediators, a significantly greater mass dose of FCB (130 fold higher) was required to obtain the comparable mediator levels as elicited by UFCB exposure (Table 2). However, when dose was normalized to surface area of particles administered, TNF-α and MIP-2 levels produced by UFCB exposure were at most only 1.5 or 1.7 fold greater than FCB levels. IL-1β cytokine levels for UFCB exposure were at most only 2.6 fold greater than FCB IL-1β cytokine levels (Table 2). Dose response curves assessing TNF-α, IL-1β, and MIP-2 mediator levels based on surface area of particles administered between UFTiO2 and FTiO2 exposure were assessed using a linear regression curve analysis with a 95% confidence interval (data similar to figure 2 not shown). This analysis showed there was no significant difference for any of the mediators between the two curves at any post-exposure time point.
Alveolar macrophage zymosan-stimulated and NO dependent chemiluminescence were measured to assess reactive oxygen species production after UFCB and FCB exposures. UFCB and FCB both caused dose-dependent and transient increases in zymosan-stimulated chemiluminescence, which returned to control levels by 42 days post-exposure (Table 1). A significantly greater mass dose of FCB (130 fold higher) was required to produce comparable zymosan-stimulated chemiluminescence levels as elicited by UFCB exposure at all post-exposure times (Table 2). However, when dose was normalized to surface area of particles administered, UFCB zymosan-stimulated chemiluminescence levels were only 1.2 to 1.8-fold higher than FCB zymosan-stimulated chemiluminescence levels (Table 2). On a mass dose basis, in regards to NO-dependent chemiluminescence levels, UFCB was 68 times more potent than FCB at 1 day post-exposure and was 130 fold more potent at 7 and 42 days post-exposure. However, when dose was normalized to surface area of particles administered, UFCB NO-dependent chemiluminescence levels were only 1.5-fold greater than FCB at 1 day post-exposure and 3 fold greater at 42 days post-exposure (Table 2). When the surface area zymosan-stimulated or NO-dependent chemiluminescence dose-response curves were analyzed using a linear regression curve with a 95% confidence interval (data similar to figure 2 not shown), there was no significant difference between the UFCB and FCB dose-response curves at any post-exposure time point.
Comparison of ultrafine carbon black and ultrafine titanium dioxide potency over 42 days
The proposed adverse health effects associated with the inhalation of airborne ultrafine or nanoparticles from particulate matter air pollution or from exposure to engineered nanoparticles are topics of ongoing scientific and public concern [16, 17]. For analyzing the possible toxicity of nanoparticles, it is necessary to utilize a dose metric that will accurately assess the particles' potential to cause a change in toxicity parameters. Previous toxicity studies have emphasized mass of particles administered as the primary dose metric. However, data from the present study indicate that, for low toxicity low solubility materials, surface area of particles administered appears an appropriate dose metric in studies assessing pulmonary toxicity of nanoparticles.
Data from the present study indicate that when carbon black particles are administered on a mass dose basis, UFCB particles have a significantly greater potential to cause pulmonary inflammation and damage than FCB particles of the same composition. However, when doses of the ultrafine and fine carbon black are normalized to surface area of particles administered, the difference in responses of the two particle sizes becomes non-significant. Our laboratory has reported similar results when comparing pulmonary response to ultrafine and fine titanium dioxide . This, therefore, indicates that, for low toxicity low solubility materials, surface area of particles rather than mass maybe an appropriate dose metric when analyzing nanoparticle toxicity.
A study conducted by Donaldson et al. , compared the toxicity of ultrafine and fine particles. UFCB (14 nm) and FCB (260 nm) were instilled into rat lungs based on an equal mass dose. BAL was performed at 6 hours post-exposure and inflammation was assessed by measuring PMN number. Donaldson et al.  showed that on a mass basis UFCB caused substantially more inflammation than FCB. In a recent study by Duffin et al. , the inflammatory potential of UFCB and UFTiO2 was greater than the fine size analogs on an equivalent mass basis. However, the potency of the ultrafine and fine particles was found to be similar when the intratracheally instilled dose to rats was normalized to equivalent particle surface area delivered. Recently, a study by Stoeger et al.  utilized six different types of ultrafine carbon particles. The BET-specific surface areas ranged about 35 to 800 m2/g, and the mean particle sizes ranged from 10 to 45 nm. This study found that, while the inflammatory potential of these six different particles was dependent on particle type, potency was most strongly related to the BET surface area . These findings support the results of the current study. The results indicate that particle surface area is a critical driver of the cytotoxic and inflammatory potential of nanoparticles. In contrast, Warheit et al. [8, 9] reported that intratracheal instillation of fine or ultrafine TiO2 resulted in similar levels of acute inflammation and cytotoxicity. They argued that these results were at variance with the "conventional wisdom" that nano-sized particles, due to their larger surface area, are more toxic than fine-sized particles of the same composition. These results conflict with a study from our lab comparing the pulmonary response over a 42 day post-exposure period to intratracheal instillation of ultrafine vs fine TiO2 . Results of this study are very similar to the current study with CB, indicating that ultrafine TiO2 was more potent that fine TiO2 on a mass dose basis, but potencies were similar when exposure was expressed on an equivalent surface area of particles delivered basis. The failure of Warheit and colleagues to observe this relationship is most likely due to severe agglomeration of UFTiO2 in their studies, as noted by their dynamic light scattering data indicating that both fine and ultrafine TiO2 suspended in PBS exhibited a mean diameter in excess of 2 μm. In contrast, with the current study and that by Sager et al.  with TiO2, particles were suspended in BALF, which greatly improved dispersion and, thus, effective particle surface area delivered . Indeed, Shvedova et al.  reported that improved dispersion of ultrafine carbon black (UFCB) particles in BAL fluid increased the inflammatory and damage potency compared to UFCB suspended in PBS; i.e., intratracheal instillation of a 30 fold greater mass of poorly dispersed UFCB suspended in PBS was required to attain the same level of pulmonary damage (LDH activity) and inflammation (PMN level) as well dispersed UFCB suspended in BAL fluid in a rat model.
As noted above, suspension of UFCB and UFTiO2 in BAL fluid greatly improved dispersion of these nanoparticles. Evidence cited above indicates that improved dispersion increases the bioactivity of tested nanoparticles. An issue is whether a poorly dispersed or a well dispersed nanoparticle suspension more closely represents aerosol sizes generated in the workplace. Data from our laboratory indicate that suspension of UFTiO2 in BAL fluid results in a mean particle diameter of 204 nm, which is close to the count mode aerodynamic diameter for UFTiO2 (138 nm) generated from a dry bulk sample by an acoustical generator [23, 24]. Furthermore, structure sizes of multi-walled carbon nanotubes (MWCNT) determined by electron microscopic analysis of MWCNT suspended in a dispersion medium which mimics BAL fluid closely resemble structures generated from a dry bulk sample by an acoustical generator [23, 25]. In addition, structure morphology of a MWCNT aerosol produced by this acoustical generator closely resembles that reported in a workplace during production and use of MWCNT . Therefore, it appears that use of well dispersed nanoparticle suspensions for evaluation of bioactivity is relevant for risk assessment of workplace exposures.
In this study, BAL fluid, i.e., diluted alveolar lining fluid was used to effectively disperse UFCB and UFTiO2. Porter et al.  reported the use of dipalmitoyl-sn-glycero-3-phosphocholine (DPPC) and serum albumin in phosphate-buffered saline at concentrations found in BAL fluid was also an effective dispersant for UFCB, UFTiO2, and MWCNT. In contrast, DPPC alone was found to be an ineffective dispersant [21, 26]. Recently, Hessemann  reported that serum albumin in phosphate-buffered saline was an effective dispersion medium for UFTiO2. However, concentrations of albumin required when used alone rather than in combination with DPPC are likely high enough to substantially coat the nanoparticles, which may alter surface activity. In contrast, the combination of DPPC and albumin at the low levels found in the BAL fluid did not alter the bioactivity of crystalline silica in a rat or mouse model [21, 23].
The post-exposure time point comparison of equivalent particle surface area doses of UFCB and UFTiO2 indicates that at 1 day post-exposure UFCB and UFTiO2 produce similar inflammation, cytotoxicity, and air/blood barrier damage. However, as post-exposure time period increases, the inflammation and lung injury caused by UFTiO2 was sustained, while that for UFCB tended to resolve. This indicates that UFTiO2 causes more persistent pulmonary toxicity than UFCB exposure. Such persistent pulmonary responses to UFTiO2 lead NIOSH to recommend an exposure standard for UFTiO2 which was significantly lower than that for fine TiO2 .
These results support the hypothesis that, for low toxicity low solubility materials, surface area of particles administered, not mass of particles, maybe a more appropriate dose metric to assess to pulmonary inflammation nanoparticles. In addition, the data suggest that on an equivalent surface area of particles delivered basis ultrafine titanium dioxide appears more bioactive than ultrafine carbon black.
Animals for in vivo exposures
The rats used for the in vivo experiments were male Fischer CDF (F344/DuCrl) rats weighing 200–300 g (~10 weeks old at arrival) obtained from Charles Rivers (Raleigh, NC). The animals were housed in an AAALAC-accredited; specific pathogen-free, environmentally controlled facility. The animals were monitored to be free of endogenous viral pathogens, parasites, mycoplasms, Helicobacter and CAR Bacillus. Animals were housed in ventilated cages which were provided HEPA-filtered air, with Alpha-Dri virgin cellulose chips and hardwood Beta-chips used as bedding. The rats were maintained on a ProLaB 3500 diet and tap water, both of which were provided ad libitum.
Bronchoalveolar fluid collection for particle suspension media
Rats were euthanized with an i.p. injection of sodium pentobarbital (> 100 mg/kg body weight) and exsangainated by cutting the descending aorta. A tracheal cannula was inserted and bronchoalveolar lavage was conducted . A 6 ml aliquot of cold Ca+2 and Mg+2-free phosphate-buffered saline (PBS) was used for the lavage wash. The cold PBS was flushed into and out of the lungs two times before the bronchoalveolar lavage (BAL) was collected. The BAL from five rats was combined and centrifuged at 600 × g for 10 minutes using a Sorvall RC 3B Plus centrifuge (Sorvall Thermo Electron Corporation, Asheville NC). The supernatant was decanted into a new tube while the pellet was discarded. This BAL fluid was then used as the vehicle for particle suspensions. The BAL fluid was collected fresh the same day that the particulate suspensions were made.
Ultrafine carbon black (UCB – Printex 90, primary particle size = 14 nm), fine carbon black (FCB-Arosperse 15 V, primary partial size = 260 nm) and ultrafine titanium dioxide (UFTiO2-Aeroxide TiO2 P-25, primary partial size = 21 nm; an 80/20 mixture of anatase/rutile) were obtained as a gift from the Degussa Corporation (Parsippany, NJ).
Suspension of UFCB, FCB, and UFTiO2
UFCB, FCB, and UFTiO2 were suspended in rat BAL fluid as described previously . Briefly, each particle sample was sieved using a Retsch AS 200 Sieve (Retsch GmbH, Haan, Germany) through 1.18 mm, 250 μm, and 45 μm mesh screens, and particle samples were weighed to desired amounts. Each respective particle sample was then suspended in the fresh rat BAL fluid to obtain the desired concentration (mg/ml). Once the particles were added to the suspension media, the suspensions were pulse sonicated with 5 individual pulses at a duty cycle setting of 10% and an output setting of 1 with a Branson 450 Sonifier probe sonicator (Branson Ultrasonics Corporation, Danbury, CT). This method has been reported previously to result in well dispersed suspensions as determined by light and electron microscopy . In a previous study, our laboratory evaluated the diameter of UFCB and UFTiO2 structures after suspension in BAL fluid using the dynamic light scattering (DLS) technique. Mean diameter of well dispersed UFCB was 131 ± 4 nm, while UFTiO2 was 204 ± 18 nm . Microscopically, FCB dispersed in BAL fluid exhibited structures less than 1 μm in diameter on average .
In vivo exposures
To receive their respective dose of particles, each rat was anesthetized with an intraperitoneal (i.p.) injection of methohexital sodium (30–40 mg/kg body weight; Monarch Pharmaceuticals, Bristol, TN). Each animal was then instilled via intratracheal instillation (IT) using a 20-gauage 4-inch ball tipped animal feeding needle. Each animal was instilled with 0.3 ml of their respective dose of UFCB, FCB or UFTiO2.
Bronchoalveolar lavage and cell differentials
At 24-hours, 7 days, and 42 days post-IT, the animals were euthanized with an i.p. injection of sodium pentobarbital (> 100 mg/kg body weight) and exsanguinated by cutting the descending aorta. A tracheal cannula was inserted and bronchoalveolar lavage (BAL) was conducted . A 6 ml aliquot of cold Ca+2 and Mg+2 free PBS was used for the first lavage wash. The cold PBS was flushed into and out of the lungs two times before the BAL fluid was collected. After the first lavage wash was collected, the BAL continued with 8 ml aliquots of cold Ca+2 and Mg+2-free PBS until an additional 80 ml of BAL was collected. The BAL from all rats was then centrifuged at 600 × g for 10 minutes using a Sorvall RC 3B Plus centrifuge (Sorvall Thermo Electron Corporation, Asheville NC). After centrifugation, the supernatant from the first lavage wash was decanted into a clean conical vial and stored on ice to be used for cytotoxicity analysis. The remaining lavage wash supernatants were discarded, and the cells remaining were washed with cold Ca+2 and Mg+2-free PBS and spun again at 600 × g for 10 minutes. After this, the supernatant was discarded, and the cells were resuspended in 1 ml of HEPES-buffered medium.
Using these BAL cell samples, counting of polymorphonuclear neutrophils (PMN) and alveolar macrophages (AM) was conducted to assess inflammation. The number of AM and PMN was determined according to their unique cell diameters, using an electronic cell counter equipped with a cell sizing attachment (Beckman Coulter Multisizer 3 Counter, Hialeah, FL).
BAL fluid lactate dehydrogenase activity and albumin concentration
The degree of cytotoxicity induced by the instilled particles was determined by lactate dehydrogenase (LDH) activity in the BAL fluid. LDH activity was measured using Roche COBAS MIRA Plus chemical analyzer (Roche Diagnostic Systems Inc., Branchburg, NJ) as described previously by our laboratory . Albumin concentrations were assessed to examine if instilled particle exposures had compromised the integrity of the alveolar air/blood barrier. The air/blood barrier damage was determined by the concentration of albumin in the BAL fluid. Albumin concentrations were also measured using a Cobas Fara II Analyzer (Roche Diagonostic Systems, Montclair, NJ) as previously described by our laboratory .
Mediator measurements in bronchoalveolar lavage fluid
The presences of inflammatory mediators present in the BAL fluid were analyzed by enzyme-linked immunosorbent assay (ELISA). The levels of mediators present were measured using commercially available ELISA kits (BioSource International Inc., Camarillo, CA). Three mediators were quantified: tumor necrosis factor-α (TNF-α), interleukin (IL)-β, and macrophage-inflammatory protein-2 (MIP-2).
Zymosan-stimulated and NO-dependent alveolar macrophage chemiluminescence
Reactive oxygen species production was determined by measuring AM chemiluminescence. According to Van Dyke et al. , only AM will generate reactive oxygen species in response to unopsonized zymosan in the chemiluminescence assay procedure. The AM chemiluminescence assay was conducted in the same manner as previously described by our laboratory . Briefly, resting AM chemiluminescence was determined by incubating 1.0 × 106 AM/ml at 37°C for 20 minutes, followed by the addition of 5-amino-2,3-dihydro-1,4, phthalazinedione (luminol) to a final concentration of 0.08 μg/ml. This was then followed by the measurement of chemiluminescence for 15 minutes at 37°C.
Zymosan-stimulated chemiluminescence (CL) was determined by adding unopsonized zymosan (2 mg/ml) to the AM samples immediately prior to measurement of chemiluminescence. Zymosan-stimulated CL was calculated as (CL with zymosan – resting CL). NO-dependent chemiluminescence was determined by adding the unopsonized zymosan as well as N-nitro-L-arginine methyl ester HCL (L-NAME) to the AM samples immediately prior to measurement of chemiluminescence. NO-dependent CL was calculated as (zymosan-stimulated CL without L-NAME – zymosan-stimulated CL with L-NAME). Zymosan-stimulated and NO-dependent chemiluminescence were both measured using a Berthold automated luminometer (Berthold Autolumat LB 953, EG&G, Gaithersburg, MD) at 390–620 nm for 15 minutes.
Statistical differences between control groups and treatment groups for the in vivo experiments examining the toxicity of carbon black and titanium dioxide were determined using an analysis of variance (ANOVA) with significance set at p ≤ 0.05. Individual means were compared using the Student-Newman-Keuls Method multiple comparison procedure with an overall significance level of p ≤ 0.05. In addition, linear regression curve analysis with a 95% confidence interval was conducted on the surface area data of each pulmonary parameter measured.
Association for Assessment and Accreditation of Laboratory Animal Care
Analysis of variance
Bronchoalveolar lavage fluid
- Ca+2 :
Fine carbon black
- Mg+2 :
Macrophage inflammatory protein
Occupational exposure level
Phosphate buffered saline
Tumor necrosis factor
Ultrafine carbon black
- UFTiO2 :
Ultrafine titanium dioxide.
The findings and conclusions in this report are those of the authors and do not necessarily represent the views of the National Institute for Occupational Safety and Health.
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