Biomedical subjects

A B Lindstrom

Publications and source records attributed to A B Lindstrom.

14 recordsLinked to original sources

PubMed2000

Stability of hemoglobin and albumin adducts of benzene oxide and 1,4-benzoquinone after administration of benzene to F344 rats.

The stability of cysteinyl adducts of benzene oxide (BO) and mono-S-substituted cysteinyl adducts of 1,4-benzoquinone (1,4-BQ) was investigated in both hemoglobin (Hb) and albumin (Alb) following administration of a single oral dose of 400 mg [U-14C/13C6]benzene/kg body weight to F344 rats. Total radiobound adducts to Hb were stable, as were adducts formed by the reaction of [13C6]BO with cysteinyl residues on Hb. In both cases adduct stability was indicated by zero-order kinetics with decay rates consistent with the lifetime of rat erythrocytes. Hb adducts of 1,4-BQ were not detected, possibly due to the production of multi-S-substituted adducts within the erythrocyte. Regarding Alb binding, total radiobound adducts decayed more rapidly than expected (half-life of 0.4 days), suggesting that uncharacterized benzene metabolites were noncovalently bound or formed unstable adducts with Alb. Although adducts from reactions of BO and 1,4-BQ with Alb both decayed with rates consistent with those of Alb turnover in the rat, the half-life for 1,4-BQ-Alb (2.5 days) was shorter than that for BO-Alb (3.1 days), suggesting some instability of 1,4-BQ-Alb. Assuming similar rates of adduct instability in humans and rats, the 1,4-BQ-Alb adducts would be eliminated with a half-life of approximately 8 days, compared with BO-Alb, which would be expected to turnover with Alb (half-life of approximately 21 days).

Albumins↗

PubMed1999

Investigation of benzene oxide in bone marrow and other tissues of F344 rats following metabolism of benzene in vitro and in vivo.

This study examines the initial activation of benzene, exploring key aspects of its metabolism by measurement of benzene oxide (BO) and BO-protein adducts in vitro and in vivo. To assess the potential influence of various factors on the production of BO, microsomes were prepared from tissues that were either targets of benzene toxicity, i.e. the bone marrow and Zymbal glands, or not targets, i.e. liver and kidneys, of control and acetone-treated F344 rats. No BO or phenol was detected in microsomal preparations of bone marrow or Zymbal glands (less than 0.007 nmol BO/mg protein and 0.7 nmol phenol/mg protein). On the other hand, BO and phenol were readily detected in preparations of liver and kidney microsomes and acetone pretreatment resulted in a 2-fold (kidney) increase or 3.7-fold (liver) increase in production of these metabolites. Initial rates of BO production in the liver isolates were 30 (control) to 50 (acetone-treated) times higher than in the corresponding kidney tissues. The estimated half-life of BO in bone marrow homogenates was 6.0 min and the second-order reaction rate constant was estimated to be 1.35 x 10(-3) l (g bone marrow)(-1) (h)(-1). These kinetic constants were used with measurements of BO-bone marrow adducts in F344 rats, receiving a single gavage dosage of 50-400 mg benzene (kg body weight)(-1) (McDonald, T.M., et al. (1994), Cancer Res. 54, 4907-4914), to predict the bone marrow dose of BO. Among the rats receiving 400 mg (kg body weight) (-1), a BO dose of 1.13 x 10(3) nM BO-h was estimated for the bone marrow, or roughly 40% of the corresponding blood dose predicted from BO-albumin adducts. Together these data suggest that, although BO is not produced at detectable levels in the bone marrow or Zymbal glands of F344 rats, BO is rapidly distributed via the bloodstream to these tissues where it may play a role in toxicity.

Animals↗

PubMed1998

Formation of hemoglobin and albumin adducts of benzene oxide in mouse, rat, and human blood.

Little is known about the formation and disposition of benzene oxide (BO), the initial metabolite arising from oxidation of benzene by cytochrome P450. In this study, reactions of BO with hemoglobin (Hb) and albumin (Alb) were investigated in blood from B6C3F1 mice, F344 rats, and humans in vitro. The estimated half-lives of BO in blood were 6.6 min (mice), 7.9 min (rats), and 7.2 min (humans). The following second-order rate constants were estimated for reactions between BO and cysteinyl residues of Hb and Alb [in units of L (g of Hb- or Alb-h)-1]: mouse Hb = 1.16 x 10(-)4, rat Hb = 15.4 x 10(-)4, human Hb = 0.177 x 10(-)4, mouse Alb = 2.68 x 10(-)4, rat Alb = 4.96 x 10(-)4, and human Alb = 5.19 x 10(-)4. These rate constants were used with BO-adduct measurements to assess the systemic doses of BO arising from benzene in vivo in published animal and human studies. Among rats receiving a single gavage dose of 400 mg of benzene/kg of body weight, the BO dose of 2.62 x 10(3) nM BO-h, predicted from Alb adducts, was quite similar to the reported AUC0-infinity = 1.09 x 10(3) nM BO-h of BO in blood. Interestingly, assays of Hb adducts in the same rats predicted a much higher dose of 14.7 x 10(3) nM BO-h, suggesting possible in situ generation of adducts within the erythrocyte. Doses of BO predicted from Alb adducts were similar in workers exposed to benzene [13.3 nM BO-h (mg of benzene/kg of body weight)-1] and in rats following a single gavage dose of benzene [8. 42 nM BO-h (mg of benzene/kg of body weight)-1]. Additional experiments indicated that crude isolates of Hb and Alb had significantly higher levels of BO adducts than dialyzed proteins, suggesting that conjugates of low-molecular-weight species were abundant in these isolates.

Animals↗

PubMed1998

Sample timing and mathematical considerations for modeling breath elimination of volatile organic compounds.

Real-world exposure measurements are a necessary ingredient for subsequent detailed study of the risks from an environmental pollutant. For volatile organic compounds, researchers are applying exhaled breath analysis and the time dependence of concentrations as a noninvasive indicator of exposure, dose, and blood levels. To optimize the acquisition of such data, samples must be collected in a time frame suited to the needs of the mathematical model, within physical limitations of the equipment and subjects, and within logistical constraints. Additionally, one must consider the impact of measurement error on the eventual extraction of biologically and physiologically relevant parameters. Given a particular mathematical model for the elimination kinetics (in this case a very simple pharmacokinetic model based upon a multiterm exponential decay function that has been shown to fit real-world data extremely well), we investigated the effects on synthetic data caused by sample timing, random measurement error, and number of terms included in the model. This information generated a series of conditions for collecting samples and performing analyses dependent upon the eventual informational needs, and it provided an estimate of error associated with various choices and compromises. Though the work was geared specifically toward breath sampling, it is equally applicable to direct blood measurements in optimizing sampling strategy and improving the exposure assessment process.

Air Pollutants↗

PubMed1998

Trichloroethene levels in human blood and exhaled breath from controlled inhalation exposure.

The organic constituents of exhaled human breath are representative of bloodborne concentrations through gas exchange in the blood/breath interface in the lungs. The presence of specific compounds can be an indicator of recent exposure or represent a biological response of the subject. For volatile organic compounds, sampling and analysis of breath is preferred to direct measurement from blood samples because breath collection is noninvasive, potentially infectious waste is avoided, the sample supply is essentially limitless, and the measurement of gas-phase analytes is much simpler in a gas matrix rather than in a complex biological tissue such as blood. However, to assess the distribution of a contaminant in the body requires a reasonable estimate of the blood level. We have investigated the use of noninvasive breath measurements as a surrogate for blood measurements for (high) occupational levels of trichloroethene in a controlled exposure experiment. Subjects were placed in an exposure chamber for 24 hr; they were exposed to 100 parts per million by volume trichloroethene for the initial 4 hr and to purified air for the remaining 20 hr. Matched breath and blood samples were collected periodically during the experiment. We modeled the resulting concentration data with respect to their time course and assessed the blood/breath relationship during the exposure (uptake) period and during the postexposure (elimination) period. Estimates for peak blood levels, compartmental distribution, and time constants were calculated from breath data and compared to direct blood measurements to assess the validity of the breath measurement methodology. Blood/breath partition coefficients were studied during both uptake and elimination. At equilibrium conditions at the end of the exposure, we could predict actual blood levels using breath elimination curve calculations and a literature value partition coefficient with a mean ratio of calculated:measured of 0.98 and standard error (SE) = 0.12 across all subjects. blood/breath comparisons at equilibrium resulted in calculated in vivo partition coefficients with a mean of 10.8 and SE = 0.60 across all subjects and experiments and 9.69 with SE = 0.93 for elimination-only experiments. We found that about 78% of trichloroethene entering the body during inhalation exposure is metabolized, stored, or excreted through routes other than exhalation.

Administration, Inhalation↗

PubMed1997

Measurement of benzene oxide in the blood of rats following administration of benzene.

Although it is generally assumed that metabolism of benzene proceeds through an initial step involving oxidation to benzene oxide (BO) by CYP450 in the liver, the production of BO has never been unambiguously confirmed in animals dosed with benzene. Furthermore, prevailing hypotheses of the mechanism by which benzene causes cancer have ignored the possibility that BO might play a direct role, despite the fact that BO is electrophilic, binds covalently to cell macromolecules and is presumably genotoxic. A likely reason for this lack of attention to the role of BO in the carcinogenesis of benzene is the presumption that this epoxide is too reactive to escape the hepatocyte after it is formed. We employed gas chromatography-mass spectrometry to measure BO in the blood of F344 rats, both in vitro and up to 24 h following oral administration of benzene. Surprisingly, BO was relatively stable in rat blood at 37 degrees C (estimated half-life = 7.9 min) and, after administering a single dosage of 400 mg benzene/kg body wt, a blood concentration of 90 nM BO (8.5 ng/ml) was measured for approximately 9 h. Using a published PBPK model we estimate that approximately 4.3% of the metabolized dose of benzene was released as BO from the liver into blood. This confirms that BO is, indeed, formed from metabolism of benzene and is sufficiently stable to be distributed throughout the body at levels which are likely to be greater than those of the other electrophilic benzene metabolites.

Animals↗

PubMed1997

Alveolar breath sampling and analysis to assess trihalomethane exposures during competitive swimming training.

Alveolar breath sampling was used to assess trihalomethane (THM) exposures encountered by collegiate swimmers during a typical 2-hr training period in an indoor natatorium. The breath samples were collected at regular intervals before, during, and for 3 hr after a moderately intense training workout. Integrated and grab whole-air samples were collected during the training period to help determine inhalation exposures, and pool water samples were collected to help assess dermal exposures. Resulting breath samples collected during the workout demonstrated a rapid uptake of two THMs (chloroform and bromodichloromethane), with chloroform concentrations exceeding the natatorium air levels within 8 min after the exposure began. Chloroform levels continued to rise steeply until they were more than two times the indoor levels, providing evidence that the dermal route of exposure was relatively rapid and ultimately more important than the inhalation route in this training scenario. Chloroform elimination after the exposure period was fitted to a three compartment model that allowed estimation of compartmental half-lives, resulting minimum bloodborne dose, and an approximation of the duration of elevated body burdens. We estimated the dermal exposure route to account for 80% of the blood chloroform concentration and the transdermal diffusion efficiency from the water to the blood to in excess of 2%. Bromodichloromethane elimination was fitted to a two compartment model which provided evidence of a small, but measurable, body burden of this THM resulting from vigorous swim training. These results suggest that trihalomethane exposures for competitive swimmers under prolonged, high-effort training are common and possibly higher than was previously thought and that the dermal exposure route is dominant. The exposures and potential risks associated with this common recreational activity should be more thoroughly investigated.

Adult↗

PubMed1997

Exhaled human breath measurement method for assessing exposure to halogenated volatile organic compounds.

The organic constituents of exhaled human breath are representative of blood-borne concentrations through gas exchange in the blood/breath interface in the lungs. The presence of specific compounds can be an indicator of recent exposure or represent a biological response of the subject. For volatile organic compounds (VOCs), sampling and analysis of breath is preferred to direct measurement from blood samples because breath collection is noninvasive, potentially infectious waste is avoided, and the measurement of gas-phase analytes is much simpler in a gas matrix rather than in a complex biological tissue such as blood. To exploit these advantages, we have developed the "single breath canister" (SBC) technique, a simple direct collection method for individual alveolar breath samples, and adapted conventional gas chromatography-mass spectrometry analytical methods for trace-concentration VOC analysis. The focus of this paper is to describe briefly the techniques for making VOC measurements in breath, to present some specific applications for which these methods are relevant, and to demonstrate how to estimate exposure to example VOCs on the basis of breath elimination. We present data from three different exposure scenarios: (a) vinyl chloride and cis-1,2-dichloroethene from showering with contaminated water from a private well, (b) chloroform and bromodichloromethane from high-intensity swimming in chlorinated pool water, and (c) trichloroethene from a controlled exposure chamber experiment. In all cases, for all subjects, the experiment is the same: preexposure breath measurement, exposure to halogenated VOC, and a postexposure time-dependent series of breath measurements. Data are presented only to demonstrate the use of the method and how to interpret the analytical results.

Breath Tests↗

PubMed1996

Alveolar breath sampling and analysis to assess exposures to methyl tertiary butyl ether (MTBE) during motor vehicle refueling.

Methyl tertiary butyl ether (MTBE) is added to gasoline (15% by volume) in many areas of the U.S. to help control carbon monoxide emissions from motor vehicles. In this study we present a sampling and analytical methodology that can be used to assess consumers' exposures to MTBE that may result from routine vehicle refueling operations. The method is based on the collection of alveolar breath samples using evacuated one-liter stainless steel canisters and analysis using a gas chromatograph-mass spectrometer equipped with a patented "valveless" cryogenic preconcentrator. To demonstrate the utility of this approach, a series of breath samples was collected from two individuals (the person pumping the fuel and a nearby observer) immediately before and for 64 min after a vehicle was refueled with premium grade gasoline. Results demonstrate low levels of MTBE in both subjects' breaths before refueling, and levels that increased by a factor of 35 to 100 after the exposure. Breath elimination models fitted to the post exposure measurements indicate that the half-life of MTBE in the first physiological compartment was between 1.3 and 2.9 min. Analysis of the resulting models suggests that breath elimination of MTBE during the 64 min monitoring period was approximately 115 micrograms for the refueling subject while it was only 30 micrograms for the nearby observer. This analysis also shows that the post exposure breath elimination of other gasoline constituents was consistent with previously published observations. These results demonstrate that this new methodology can be used effectively in studies designed to assess exposures to MTBE. The method can be used to objectively demonstrate recent exposures, the relative magnitude of an exposure, and the approximate duration of the resulting bloodborne dose. Once a blood/breath partition coefficient for MTBE has been firmly established, the bloodborne concentration of the absorbed material can be determined using these techniques as well.

Air Pollutants↗

PubMed1996

A methodological approach for exposure assessment studies in residences using volatile organic compound-contaminated water.

This paper presents a methodological approach for assessing total exposures to volatile organic compounds (VOCs) in residences using contaminated water supplies. This approach is founded on assessment of ingestion, inhalation, and dermal exposures; both long-term (i.e., 12 to 24 hr) low-level exposures and short-term (i.e., approximately 10 min) high-level exposures are considered. The methodology is based on the collection of water samples to establish the identity of the contaminants, maximum source terms, and possible dermal and ingestion exposures; integrated whole-air samples are collected to assess long- and short-term inhalation exposures; whole-air grab samples are used to confirm peak and typical inhalation exposures; and alveolar breath samples are used to confirm exposures and to estimate contaminant concentrations in the blood of the test subjects. While we do not suggest that this methodology should supersede any current investigative approach, this material is primarily offered as a consolidated reference to the many people or organizations who might contemplate a study of this type. Application of this investigative protocol should provide detailed exposure assessment information, while it supplies critical real world data for risk assessment specialists, toxicologists, and modeling experts. Data from a recent field study assessing exposures to trichloroethylene are presented to illustrate the utility and some of the limitations of this strategy.

Administration, Inhalation↗

PubMed1995

Measurement of volatile organic compounds in exhaled breath as collected in evacuated electropolished canisters.

A set of three complementary analytical methods were developed specifically for exhaled breath as collected in evacuated stainless steel canisters using gas chromatographic-mass spectrometric detection. The first is a screening method to quantify the carbon dioxide component (generally at 4-5% concentration), the second method measures the very volatile high-level endogenous compounds [e.g. acetone and isoprene at 500-1000 parts per billion by volume (ppbv), methanol, ethanol, dimethylsulfide at 2-10 ppbv], and the third method is designed to measure trace-level environmental contaminants and other endogenous volatile organic compounds (VOCs) (sub-ppbv) in breath. The canister-based sample format allows all three methods to be applied to each individual sample for complete constituent characterization. Application of these methods is shown to be useful in the following ways: analysis of CO2 levels indicates the approximate quantity of alveolar breath collected (as opposed to whole breath) in a sample; levels of major endogenous compounds are shown to be influenced by physical activities and subsequent recovery periods; and environmental exposures to xenobiotic VOCs can be characterized by assessment of post-exposure breath elimination curves. The instrumentation and methodology are described and example chromatograms and quantitative data plots demonstrating the utility of the methods are presented.

Acetone↗

PubMed1995

Collection of a single alveolar exhaled breath for volatile organic compounds analysis.

Measurement of specific organic compounds in exhaled breath has been used as an indicator of recent exposure to pollutants or as an indicator of the health of an individual. A typical application involves the collection of multiple breaths onto a sorbent cartridge or into an evacuated canister with the use of a relatively complex sampling apparatus. A new method has been developed wherein a single exhaled breath is directly transferred from the mouth into an evacuated 1 l or 1.8 l stainless steel SUMMA canister. The single breath canister (SBC) method avoids the necessity for a complex sampling system requiring maintenance and cleaning and allows easy collection of samples. Additionally, it is possible to collect a rapid sequence of samples from a subject to establish the elimination curve subsequent to an exposure to specific volatile organic compounds with a theoretical resolution of adjacent breaths. The SBC method was compared to an accepted canister based sampling system to assure comparability and then used to demonstrate its utility by measuring the absorption and elimination of chloroform during and after exposure to chlorinated shower water.

Breath Tests↗

PubMedDate not supplied

Gasoline-contaminated ground water as a source of residential benzene exposure: a case study.

In a private residence using gasoline-contaminated ground water (approximately 300 micrograms/l benzene), a series of experiments were performed to assess the potential benzene exposures that may occur in the shower stall, bathroom, master bedroom, and living room as a result of a single 20-min, shower. Integrated fixed site SUMMA TM-polished canister and Tenax GC air samples were collected in the target microenvironments over 20, 60, and 240 min. periods. These results were compared with the long-term personal Tenax GC samples (6 h) and grab samples collected with glass, gas-tight syringes at 0, 10, 18, 20, 25, 25.5, and 30 min. Maximum benzene concentrations occurred in the shower stall (758-1670 micrograms/m3) and bathroom (366-498 micrograms/m3) during and immediately after the shower. Inhalation exposures in the shower stall during the 20-min. shower were 2.1-4.9 times higher than corresponding 20-min, bathroom exposures. The total benzene dose resulting from the shower was estimated to be approximately 281 micrograms, with 40% via inhalation and 60% via the dermal pathway. This total is 2 to 3.5 times higher than the mean inhalation dose received during a concurrent 6 h occupation of the house. These results indicate that domestic use of gasoline-contaminated water can produce relatively high benzene exposures that vary significantly according to an individual's proximity to the water use zone. The information in this document has been funded wholly or in part by the U.S. Environmental Protection Agency. It has been subjected to Agency review and approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. The entire experiment was reviewed and approved by the Research Triangle Institute Human Subjects Review Committee.

Air Pollution↗

PubMedDate not supplied

Development and testing of a whole-air sampler for measurement of personal exposure to volatile organic compounds.

A small and relatively lightweight (3.35 kg) whole-air (canister) sampler that can be worn to monitor personal exposures to volatile organic compounds was developed and evaluated. The prototype personal whole-air sampler (PWAS) consists of a 1-l canister, a mass flow controller, two 1.3 amp hour batteries, a DC/DC converter, and an electronics module with a digital display for the sampling set point, actual flow rate, and battery voltage. The sampler (25.5 x 22.5 x 7.5 cm) fits into a laptop computer carrying case and is able to collect a 900 ml sample at a linear flow rate over 12-16 hours. Laboratory tests demonstrated that the sample flow rate was not affected by temperature or the activity of the person wearing the sampler. Recoveries of methylene chloride, chloroform, 1,1,1-trichloroethane, benzene, n-octane, o-xylene, n-decane, and p-dichlorobenzene averaged 89% or better for three final prototype samplers. Recoveries were slightly lower for vinyl chloride (74%) and n-dodecane (82%). The precision for the three prototypes was excellent during laboratory tests with the coefficient of variation (CV) < 10% for all the test compounds. Although the unit was designed for use as a personal whole-air sampling system, it can also be used as an extremely compact microenvironmental whole-air sampler.

Environmental Exposure↗