N6-Formyllysine as a Biomarker of Formaldehyde Exposure: Formation and Loss of N6-Formyllysine in Nasal Epithelium in Long-Term, Low-Dose Inhalation Studies in Rats.

Exposure to both endogenous and exogenous formaldehyde has been established to be carcinogenic, likely by virtue of forming nucleic acid and proteins adducts such as N6-formyllysine. To better assess N6-formyllysine as a biomarker of formaldehyde exposure, we studied accumulation of N6-formyllysine adducts in tissues of rats exposed by inhalation to 2 ppm [13C2H2]-formaldehyde for 7, 14, 21, and 28 days (6 h/day) and investigated adduct loss over a 7-day postexposure period using liquid chromatography-coupled tandem mass spectrometry. Our results showed formation of exogenous adducts in nasal epithelium and to some extent in trachea but not in distant tissues of lung, bone marrow, or white blood cells, with a 2-fold increase over endogenous N6-formyllysine over a 3-week exposure period. Postexposure analyses indicated a biexponential decay of N6-formyllysine in proteins extracted from different cellular compartments, with half-lives of ∼25 and ∼182 h for the fast and slow phases, respectively, in cytoplasmic proteins. These results parallel the behavior of DNA adducts and DNA-protein cross-links, with protein adducts cleared faster than DNA-protein cross-links, and point to the potential utility of N6-formyllysine protein adducts as biomarkers of formaldehyde.

Formation, Accumulation, and Hydrolysis of Endogenous and Exogenous Formaldehyde-Induced DNA Damage.

Formaldehyde is not only a widely used chemical with well-known carcinogenicity but is also a normal metabolite of living cells. It thus poses unique challenges for understanding risks associated with exposure. N(2-)hydroxymethyl-dG (N(2)-HOMe-dG) is the main formaldehyde-induced DNA mono-adduct, which together with DNA-protein crosslinks (DPCs) and toxicity-induced cell proliferation, play important roles in a mutagenic mode of action for cancer. In this study, N(2)-HOMe-dG was shown to be an excellent biomarker for direct adduction of formaldehyde to DNA and the hydrolysis of DPCs. The use of inhaled [(13)CD2]-formaldehyde exposures of rats and primates coupled with ultrasensitive nano ultra performance liquid chromatography-tandem mass spectrometry permitted accurate determinations of endogenous and exogenous formaldehyde DNA damage. The results show that inhaled formaldehyde only reached rat and monkey noses, but not tissues distant to the site of initial contact. The amounts of exogenous adducts were remarkably lower than those of endogenous adducts in exposed nasal epithelium. Moreover, exogenous adducts accumulated in rat nasal epithelium over the 28-days exposure to reach steady-state concentrations, followed by elimination with a half-life (t1/2) of 7.1 days. Additionally, we examined artifact formation during DNA preparation to ensure the accuracy of nonlabeled N(2)-HOMe-dG measurements. These novel findings provide critical new data for understanding major issues identified by the National Research Council Review of the 2010 Environmental Protection Agency's Draft Integrated Risk Information System Formaldehyde Risk Assessment. They support a data-driven need for reflection on whether risks have been overestimated for inhaled formaldehyde, whereas underappreciating endogenous formaldehyde as the primary source of exposure that results in bone marrow toxicity and leukemia in susceptible humans and rodents deficient in DNA repair.

Carbon capture and sequestration: an exploratory inhalation toxicity assessment of amine-trapping solvents and their degradation products.

Carbon dioxide (CO2) absorption with aqueous amine solvents is a method of carbon capture and sequestration (CCS) from flue gases. One concern is the possible release of amine solvents and degradation products into the atmosphere, warranting evaluation of potential pulmonary effects from inhalation. The CCS amines monoethanolamine (MEA), methyldiethanolamine (MDEA), and piperazine (PIP) underwent oxidative and CO2-mediated degradation for 75 days. C57bl/6N mice were exposed for 7 days by inhalation of 25 ppm neat amine or equivalant concentration in the degraded mixture. The aqueous solutions were nebulized to create the inhalation atmospheres. Pulmonary response was measured by changes in inflammatory cells in bronchoalveolar lavage fluid and cytokine expression in lung tissue. Ames mutagenicity and CHO-K1 micronucleus assays were applied to assess genotoxicity. Chemical analysis of the test atmosphere and liquid revealed complex mixtures, including acids, aldehydes, and other compounds. Exposure to oxidatively degraded MEA increased (p < 0.05) total cells, neutrophils, and lymphocytes compared to control mice and caused inflammatory cytokine expression (statistical increase at p < 0.05). MEA and CO2-degraded MEA were the only atmospheres to show statistical (p < 0.05) increase in oxidative stress. CO2 degradation resulted in a different composition, less degradation, and lower observed toxicity (less magnitude and number of effects) with no genotoxicity. Overall, oxidative degradation of the amines studied resulted in enhanced toxicity (increased magnitude and number of effects) compared to the neat chemicals.

Formaldehyde-associated changes in microRNAs: tissue and temporal specificity in the rat nose, white blood cells, and bone marrow.

MicroRNAs (miRNAs) are critical regulators of gene expression, yet much remains unknown regarding their changes resulting from environmental exposures as they influence cellular signaling across various tissues. We set out to investigate miRNA responses to formaldehyde, a critical air pollutant and known carcinogen that disrupts miRNA expression profiles. Rats were exposed by inhalation to either 0 or 2 ppm formaldehyde for 7, 28, or 28 days followed by a 7-day recovery. Genome-wide miRNA expression profiles were assessed within the nasal respiratory epithelium, circulating white blood cells (WBC), and bone marrow (BM). miRNAs showed altered expression in the nose and WBC but not in the BM. Notably in the nose, miR-10b and members of the let-7 family, known nasopharyngeal carcinoma players, showed decreased expression. To integrate miRNA responses with transcriptional changes, genome-wide messenger RNA profiles were assessed in the nose and WBC. Although formaldehyde-induced changes in miRNA and transcript expression were largely tissue specific, pathway analyses revealed an enrichment of immune system/inflammation signaling in the nose and WBC. Specific to the nose was enrichment for apoptosis/proliferation signaling, involving let-7a, let-7c, and let-7f. Across all tissues and time points assessed, miRNAs were predicted to regulate between 7% and 35% of the transcriptional responses and were suggested to play a role in signaling processes including immune/inflammation-related pathways. These data inform our current hypothesis that formaldehyde-induced inflammatory signals originating in the nose may drive WBC effects.

Dosimetry of N6-formyllysine adducts following [¹³C²H2]-formaldehyde exposures in rats.

With formaldehyde as the major source of endogenous N6-formyllysine protein adducts, we quantified endogenous and exogenous N6-formyllysine in the nasal epithelium of rats exposed by inhalation to 0.7, 2, 5.8, and 9.1 ppm [¹³C²H2]-formaldehyde using liquid chromatography-coupled tandem mass spectrometry. Exogenous N6-formyllysine was detected in the nasal epithelium, with concentration-dependent formation in total as well as fractionated (cytoplasmic, membrane, nuclear) proteins, but was not detected in the lung, liver, or bone marrow. Endogenous adducts dominated at all exposure conditions, with a 6 h 9.1 ppm formaldehyde exposure resulting in one-third of the total load of N6-formyllysine being derived from exogenous sources. The results parallel previous studies of formaldehyde-induced DNA adducts.

Formaldehyde and epigenetic alterations: microRNA changes in the nasal epithelium of nonhuman primates.

BACKGROUND: Formaldehyde is an air pollutant present in both indoor and outdoor atmospheres. Because of its ubiquitous nature, it is imperative to understand the mechanisms underlying formaldehyde-induced toxicity and carcinogenicity. MicroRNAs (miRNAs) can influence disease caused by environmental exposures, yet miRNAs are understudied in relation to formaldehyde. Our previous investigation demonstrated that formaldehyde exposure in human lung cells caused disruptions in miRNA expression profiles in vitro. OBJECTIVES: Using an in vivo model, we set out to test the hypothesis that formaldehyde inhalation exposure significantly alters miRNA expression profiles within the nasal epithelium of nonhuman primates. METHODS: Cynomolgus macaques were exposed by inhalation to approximately 0, 2, or 6 ppm formaldehyde for 6 hr/day for 2 consecutive days. Small RNAs were extracted from nasal samples and assessed for genome-wide miRNA expression levels. Transcriptional targets of formaldehyde-altered miRNAs were computationally predicted, analyzed at the systems level, and assessed using real-time reverse transcriptase polymerase chain reaction (RT-PCR). RESULTS: Expression analysis revealed that 3 and 13 miRNAs were dysregulated in response to 2 and 6 ppm formaldehyde, respectively. Transcriptional targets of the miRNA with the greatest increase (miR-125b) and decrease (miR-142-3p) in expression were predicted and analyzed at the systems level. Enrichment was identified for miR-125b targeting genes involved in apoptosis signaling. The apoptosis-related targets were functionally tested using RT-PCR, where all targets showed decreased expression in formaldehyde-exposed samples. CONCLUSIONS: Formaldehyde exposure significantly disrupts miRNA expression profiles within the nasal epithelium, and these alterations likely influence apoptosis signaling.

Cardiopulmonary response to inhalation of secondary organic aerosol derived from gas-phase oxidation of toluene.

The biological response to inhalation of secondary organic aerosol (SOA) was determined in rodents exposed to SOA derived from the oxidation of toluene, a precursor emitted from anthropogenic sources. SOA atmospheres were produced to yield 300 µg·m(-3) of particulate matter (PM) plus accompanying gases. Whole-body exposures were conducted in mice to assess both pulmonary and cardiovascular effects. ApoE(-/-) mice were exposed for 7 days and measurements of TBARS and gene expression of heme-oxygenase-1 (HO-1), endothelin-1 (ET-1), and matrix metalloproteinase-9 (MMP-9) were made in aorta. Pulmonary inflammatory responses in both species were measured by bronchoalveolar lavage fluid (BALF) cell counts. No pulmonary inflammation was observed. A mild response was observed in mouse aorta for the upregulation of ET-1 and HO-1, with a trend for increased MMP-9 and TBARS, and. Overall, toluene-derived SOA revealed limited biological response compared with previous studies using this exposure protocol with other environmental pollutants.

Dermal and ocular exposure systems for the development of models of sulfur mustard-induced injury.

Sulfur mustard (SM) is a chemical threat agent for which the effects have no current treatment. Due to the ease of synthesis and dispersal of this material, the need to develop therapeutics is evident. The present article details the techniques used to develop SM laboratory exposure systems for the development of animal models of ocular and dermal injury. These models are critical to enable evaluation of SM injury and therapeutics against that injury. Iterative trials were conducted to optimize dermal and ocular injury models in guinea pigs and rabbits respectively. The goal was a homogeneous and diffuse ocular and dermal injury that compares to the human injury. Dermal exposures were conducted by either a flow-past or static vapor cup system. Ocular exposures were conducted by a static exposure system. Ocular and dermal exposures were conducted with vaporized SM. Vapor concentrations increased with time in the dermal and ocular exposure systems but were stable with varying amounts of applied SM. A dermal deposition estimation study was also conducted. Deposited volumes increased with exposure time.

Inhalation exposure systems for the development of rodent models of sulfur mustard-induced pulmonary injury.

Sulfur mustard (SM) is a chemical threat agent for which its effects have no current treatment. Due to the ease of synthesis and dispersal of this material, the need to develop therapeutics is evident. The present manuscript details the techniques used to develop SM laboratory exposure systems for the development of animal models of pulmonary injury. These models are critical for evaluating SM injury and developing therapeutics against that injury. Iterative trials were conducted to optimize a lung injury model. The resulting pathology was used as a guide, with a goal of effecting homogeneous and diffuse lung injury comparable to that of human injury. Inhalation exposures were conducted by either nose-only inhalation or intubated inhalation. The exposures were conducted to either directly vaporized SM or SM that was nebulized from an ethanol solution. Inhalation of SM by nose-only inhalation resulted in severe nasal epithelial degeneration and minimal lung injury. The reactivity of SM did not permit it to transit past the upper airways to promote lower airway injury. Intratracheal inhalation of SM vapors at a concentration of 5400 mg x min/m(3) resulted in homogeneous lung injury with no nasal degeneration.

Generation and characterization of gasoline engine exhaust inhalation exposure atmospheres.

Exposure atmospheres for a rodent inhalation toxicology study were generated from the exhaust of a 4.3-L gasoline engine coupled to a dynamometer and operated on an adapted California Unified Driving Cycle. Exposure levels were maintained at three different dilution rates. One chamber at the lowest dilution had particles removed by filtration. Each exposure atmosphere was characterized for particle mass, particle number, particle size distribution, and detailed chemical speciation. The majority of the mass in the exposure atmospheres was gaseous carbon monoxide, nitrogen oxides, and volatile organics, with small amounts of particle-bound carbon/ions and metals. The atmospheres varied according to the cycle, with the largest spikes in volatile organic and inorganic species shown during the "cold start" portion of the cycle. Ammonia present from the exhaust and rodents interacted with the gasoline exhaust to form secondary inorganic particles, and an increase in exhaust resulted in higher proportions of secondary inorganics as a portion of the total particle mass. Particle size had a median of 10-20 nm by number and approximately 150 nm by mass. Volatile organics matched the composition of the fuel, with large proportions of aliphatic and aromatic hydrocarbons coupled to low amounts of oxygenated organics. A new measurement technique revealed organics reacting with nitrogen oxides have likely resulted in measurement bias in previous studies of combustion emissions. Identified and measured particle organic species accounted for about 10% of total organic particle mass and were mostly aliphatic acids and polycyclic aromatic hydrocarbons.

Influence of impactor operating flow rate on particle size distribution of four jet nebulizers.

When a nebulizer is evaluated by the Andersen Cascade Impactor (ACI), the flow rate is generally maintained at 28.3 L/min, as recommended by the manufacturer. However, the nebulizer flow rate that a patient inhales is only around 18 L/min. Because the drive flow of a nebulizer is approximately 6-8 L/min, the nebulized drug is mixed with outside air when delivered. Evaluating impactor performance at the 28.3 L/min flow rate is less than ideal because an additional 10 L/min of outside air is mixed with the drug, thereby affecting the drug size distribution and dose before inhalation and deposition in the human lung. In this study we operated the ACI at an 18.0 L/min flow rate to test whether the effect of the changing ambient humidity was being exaggerated by the 28.3 L/min flow rate. The study was carried out at three different relative humidity levels and two different impactor flow rates with four commercially available nebulizers. The mass median aerodynamic diameter (MMAD) and the geometric standard deviation (GSD) of the droplets were found to increase when the impactor was operated at a flow rate of 18 L/min compared to that of 28.3 L/min. The higher MMAD and GSD could cause the patient to inhale less of the drug than expected if the nebulizer was evaluated by the ACI at the operating flow rate of 28.3 L/min.

Identification of urinary metabolites of orally administered N,N-dimethyl-p-toluidine in male F344 rats.

The metabolism of orally administered N,N-dimethyl-p-toluidine (DMPT) in male F344 rats was investigated. The rat urinary metabolite profile was determined by analytical reverse-phase high performance liquid chromatography (HPLC). Four radiolabeled peaks were observed, isolated, and purified by solid-phase extraction (SPE) and preparative HPLC methods. The 4 peaks were identified as p-(N-acetylhydroxyamino)hippuric acid (M1), DMPT N-oxide (M2), N-methyl-p-toluidine (M3), and parent DMPT. Metabolites M1 and M2 were identified by spectrometric and spectroscopic methods, including mass fragmentation pattern identification from both liquid chromatography/mass spectrometry and gas chromatography/mass spectrometry, and from chemical analysis of nuclear magnetic resonance spectra. Structural confirmation of metabolite M2 was accomplished by comparison with a synthetic standard. Peaks M3 and the peak suspected to be DMPT were identified by comparison of their HPLC retention times and mass fragmentation patterns with authentic standards of N-methyl-p-toluidine and DMPT, respectively. DMPT metabolism is similar to that reported for N,N-dimethylaniline.

Disposition and clearance of tungsten after single-dose oral and intravenous exposure in rodents.

Tungsten (W) has been nominated for study to the National Toxicology Program (NTP) because of reported associations between concentrations of W in drinking water and childhood leukemia. The disposition of W (administered as sodium tungstate dihydrate in water) in plasma, liver, kidneys, uterus, femur, and intestine of rodents (Sprague-Dawley rats and C57BL/6N mice) was characterized after exposures by oral gavage (1, 10, or 100 mg/kg) or intravenous (1 mg/kg) administration. Each tissue (or plasma) was collected and analyzed by inductively coupled plasma mass spectrometry at 1, 2, 4, or 24 h after dose administration. W was observed in plasma and all tissues after both gavage and i.v. administration. In rats, concentrations in plasma and most tissues peaked at 4 h. In mice, concentrations in plasma and most tissues peaked at 1 h. Although the amount of W in each matrix decreased significantly by 24 h, there was W remaining in several tissues, especially at the higher doses.

Disposition of orally and intravenously administered methyltetrahydrofuran in rats and mice.

The disposition of [14C]methyltetrahydrofuran (14C-MTHF) in rats and mice was determined by following changes in the radioactivity in tissue and excreta with time after dosing. MTHF administered orally (1, 10, or 100 mg/kg) or intravenously (1 mg/kg) to either rats or mice was rapidly metabolized and excreted with <8% (mice) or 8-22% (rats) of the dose remaining in the body after 24 h (1 and 10 mg/kg doses) or 72 h (100 mg/kg dose). Based on recovery of radioactivity in excreta (other than feces) and tissues (other than the gastrointestinal [GI] tract), absorption of orally administered MTHF was essentially complete (93-100%). There were no overt signs of toxicity observed at any dose studied. The major route of excretion in mice was in urine followed by exhaled CO2. In rats the major route of excretion was exhaled CO2 followed by urinary excretion. The excretion of exhaled volatile organic compounds (VOC) was dose-dependent in both species; at lower doses exhaled VOC represented 1-5% of dose, but at the highest dose (100 mg/kg) this proportion rose to 14% (mice) and 27% (rats). Analysis of the VOCs exhaled at the high dose indicated that the increase was due to exhalation of the parent compound, 14C-MTHF. Analysis of urine showed three highly polar peaks in the mouse urine and two polar peaks in the rat urine. Because the 14C label in MTHF was in the methyl group, the polar metabolites were considered likely due to the one-carbon unit getting into the metabolic pool and labeling intermediate dietary metabolites.

Measurement of plasma or urinary metabolites and Hprt mutant frequencies following inhalation exposure of mice and rats to 3-butene-1,2-diol.

Studies were performed to determine if the detoxification pathway of 1,3-butadiene (BD) through 3-butene-1,2-diol (BD-diol) is a major contributor to mutagenicity in BD-exposed mice and rats. First, female and male mice and rats (4-5 weeks old) were exposed by nose-only for 6h to 0, 62.5, 200, 625, or 1250 ppm BD or to 0, 6, 18, 24, or 36 ppm BD-diol primarily to establish BD and BD-diol exposure concentrations that yielded similar plasma levels of BD-diol, and then animals were exposed in inhalation chambers for 4 weeks to BD-diol to determine the mutagenic potency estimates for the same exposure levels and to compare these estimates to those reported for BD-exposed female mice and rats where comparable blood levels of BD-diol were achieved. Measurements of plasma levels of BD-diol (via GC/MS methodology) showed that (i) BD-diol accumulated in a sub-linear fashion during single 6-h exposures to >200 ppm BD; (ii) BD-diol accumulated in a linear fashion during single or repeated exposures to 6-18 ppm BD and then in a sub-linear fashion with increasing levels of BD-diol exposure; and (iii) exposures of mice and rats to 18 ppm BD-diol were equivalent to those produced by 200 ppm BD exposures (with exposures to 36 ppm BD-diol yielding plasma levels approximately 25% of those produced by 625 ppm BD exposures). Measurements of Hprt mutant frequencies (via the T cell cloning assay) showed that repeated exposures to 18 and 36 ppm BD-diol were significantly mutagenic in mice and rats. The resulting data indicated that BD-diol derived metabolites (especially, 1,2-dihydroxy-3,4-epoxybutane) have a narrow range of mutagenic effects confined to high-level BD (>or=200 ppm) exposures, and are responsible for nearly all of the mutagenic response in the rat and for a substantial portion of the mutagenic response in the mouse following high-level BD exposures.

Medical nebulizer performance: effects of cascade impactor temperature.

BACKGROUND: During operation of a jet nebulizer, the temperature of the nebulizer outlet could decrease by more than 10 degrees C, depending on the nebulizer type and operating conditions, such as driving flow rate and fill volume. The droplet size distribution generated from the nebulizer can be measured by a cascade impactor. However, when the cascade impactor is operated at ambient room temperature, the droplets could evaporate because of the temperature difference between the nebulizer outlet and the body of the impactor. METHODS: An 8-stage cascade impactor was used to measure the particle size distribution from 4 different types of jet nebulizer (LC Plus, Side-Stream, VixOne, and Micromist) in 2 temperature conditions: ambient (22 degrees C) and low (10 degrees C). Two different formulations, albuterol (aqueous solution) and budesonide (suspension), were used. RESULTS: There was a significantly larger (p < 0.05) mass median aerodynamic diameter and smaller respirable fraction for each nebulizer with the impactor at low temperature than with the impactor at ambient temperature. The mass median aerodynamic diameter of the nebulizers with the impactor operating at low temperature appeared 15-130% larger than with the impactor operating at ambient temperature, for both formulations. The respirable fraction also changed from 10% when the impactor was operated at low temperature to 65% when the impactor was operated at ambient temperature. CONCLUSION: The results provide important information for the use of a cascade impactor to measure the particle-size distribution of nebulizer aerosols.

Concentration and particle size of airborne toxic algae (brevetoxin) derived from ocean red tide events.

Red tides in the Gulf of Mexico are formed by blooms of the dinoflagellate Karenia brevis, which produces brevetoxins (PbTx). Brevetoxins can be transferred from water to air in the wind-powered whitecapped waves during red tide episodes. Inhalation exposure to marine aerosol containing PbTx causes respiratory problems. A liquid chromatograph/ tandem mass spectrometric method was developed for the detection and quantitation of several PbTxs in ambient samples collected during red tide events. This method was complemented by a previously developed antibody assay that analyzes the entire class of PbTx compounds. The method showed good linearity, accuracy, and reproducibility, allowing quantitation of PbTx compounds in the 10 pg/m3 range. Air concentrations of PbTxs and brevenal for individual samples ranged from 0.01 to 80 ng/m3. The particle size showed a single mode with a mass median diameter between 6 and 10 microm, which was consistent for all of the PbTx species that were measured. Our results imply that individual PbTxs were from the same marine aerosol or from marine aerosol that was produced from the same process. The particle size indicated the likelihood of high deposition efficiency in the respiratory tract with the majority of aerosol deposited in the upper airways and small but not insignificant deposition in the lower airways.

Analysis of butadiene urinary metabolites by liquid chromatography-triple quadrupole mass spectrometry.

1,3-Butadiene (BD) is a monomer produced in petrochemical production facilities and from several combustion sources. The United States Environmental Protection Agency has defined BD as a probable human carcinogen. Methods for assessing exposure and internal dose are therefore of critical interest, and one technique is the measurement of urinary metabolites. Here we describe methods for measuring two urinary metabolites, N-acetyl-S-(3,4-dihydroxybutyl)-L-cysteine (referred to as MI) and an isomeric mixture of the regio- and stereoisomers (R)/(S)-N-acetyl-S-(1-(hydroxymethyl)-2-propen-yl)-L-cysteine and (R)/(S)-N-acetyl-S-(2-hydroxy-3-butenyl)-L-cysteine (referred to as MII). The method is based on isolation of the metabolites by solid-phase extraction and measurement using liquid chromatography and triple quadrupole mass spectrometry (LC-MS(3)). The LC-MS(3) allowed good selectivity with minimal sample preparation. Assay accuracy was within 10% or better, with substantial improvement in accuracy accompanying the commercial availability of deuterated internal standards for both compounds. Assay precision and linearity passed rigorous validation criteria, and precision-based limits of quantitation values were 12 and 1 ng/mL for MI and MII, respectively. Data are shown from analysis of human urine from occupationally exposed individuals and rat urine from BD exposures conducted to investigate rodent metabolic profiles. Both of these data sets clearly show that this assay can discern previously described relationships between BD exposure and the production of MI/MII.

Chronic self-administration of nicotine in rats impairs T cell responsiveness.

Chronic exposure of rodents to nicotine via subcutaneously or intracerebroventricularly implanted miniosmotic pumps affects T cell function. However, this method of continuous nicotine administration does not replicate the self-motivated administration of nicotine in human smokers. To determine whether nicotine impairs the immune system under conditions pertinent to human smokers, we investigated the T cell responsiveness of male Lewis rats self-administering (SA) nicotine (0.03 mg/kg of body weight per injection) 40 to 50 times/day for 5 weeks, using a model of virtually unlimited access to nicotine. Compared with sham control animals, the concanavalin A-induced proliferation of spleen cells from SA rats was significantly decreased. Moreover, the ability of spleen cells to mobilize intracellular Ca(2+) after ligation of the T cell antigen receptor (TCR) with an anti-alphabeta TCR antibody was significantly less in SA than in control rats. In addition, inositol 1,4,5-trisphosphate (IP(3))-sensitive intracellular Ca(2+) stores were markedly depleted in spleen cells from SA animals. These results suggest that chronic nicotine self-administration suppresses T cell responsiveness, and this suppression may result from an impaired TCR-mediated signaling that stems from the depletion of IP(3)-sensitive intracellular Ca(2+) stores.