Occupational Solvent Exposure and Brain Function: An fMRI Study
Cheuk Ying Tang1,2, David M. Carpenter1, Emily L. Eaves1, Johnny Ng1, Nimalya Ganeshalingam1, Clifford Weisel3, Hua Qian3, Gudrun Lange4,5, Nancy L. Fiedler3
1 Department of Radiology, and, 2 Department of Psychiatry, Mount Sinai School of Medicine, New York, New York, USA, 3 Department of Environmental and Occupational Medicine, 4 Department of Psychiatry, and, 5 Department of Radiology, UMDNJ-New Jersey Medical School, Newark, New Jersey, USA
Environ Health Perspect 119:908-913 (2011). http://dx.doi.org/10.1289/ehp.1002529 [online 04 February 2011]
Background: Deficits in cognitive function have been demonstrated among workers chronically exposed to solvents, but the neural basis for these deficits has not been shown.
Objectives: We used functional magnetic resonance imaging (fMRI) to compare pathophysiological changes in brain function between solvent-exposed and control workers.
Methods: Painters, drywall tapers, and carpenters were recruited from the International Union of Painters and Allied Trades, District Council 9 in New York City and District Council 21 in Philadelphia, Pennsylvania, and from the Carpenters Union in New Jersey. Twenty-seven solvent-exposed and 27 control subjects of similar age, education, and occupational status completed the N-Back working memory test during fMRI. After controlling for confounders (age; lifetime marijuana, cocaine, and alcohol use; blood lead; symptoms of depression; verbal intelligence), voxelwise group analysis and regional activation levels were compared and then correlated with an index of lifetime solvent exposure.
Results: Solvent-exposed workers’ performance on the N-Back was significantly worse than that of controls. Activation of the anterior cingulate, prefrontal, and parietal cortices—areas serving working memory function and attention—was also significantly lower for solvent-exposed workers relative to controls. After controlling for confounders, we observed a negative correlation between lifetime solvent exposure and activation in these same regions among the solvent-exposed workers.
Conclusions: This study is one of the few to document neural structures affected by exposure to solvents. Our findings provide a biological mechanism for the neurobehavioral deficits in working memory and attention that have previously been reported by other groups studying the effects of chronic exposure to solvents. These imaging markers, which are consistent with the neurobehavioral measures in our subject population, are consistent with altered brain pathology caused by prolonged exposure to solvent mixtures during construction work.
Key words: brain function, fMRI, solvent exposure
Address correspondence to C.Y. Tang, Department of Radiology and Psychiatry, Mount Sinai School of Medicine, One Gustave L. Levy Place, Box 1234, New York, NY 10029 USA. Telephone: (212) 241-7255. Fax: 212-534-2683. E-mail: Cheuk.Tang@mssm.edu
This research was funded by grant R01 OH008198 from the National Institute for Occupational Safety and Health and Center for Environmental Exposures and Disease grant P30ES005022 from the National Institute of Environmental Health Sciences.
The authors declare they have no actual or potential competing financial interests.
Received 07 June 2010; accepted 04 February 2011; online 04 February 2011.
Workers chronically exposed to solvent mixtures frequently exhibit significantly compromised attention, processing speed, and working memory relative to demographically similar unexposed controls (Baker 1994; Benignus et al. 2005; Mikkelsen 1997). Although anatomical studies using magnetic resonance imaging (MRI) and computed tomography (CT) have detected structural changes, these have typically been seen only in subjects with severe solvent exposures, such as workers diagnosed with chronic toxic encephalopathy (Ellingsen et al. 1993; Thuomas et al. 1996) or organic solvent abusers (Filley et al. 1990; Rosenberg et al. 1988; Unger et al. 1994; Yamanouchi et al. 1995). Moreover, many of these studies suffered from poor characterization of exposure, confounding, inability to determine dose response, and biased subject selection (Ridgway et al. 2003). Other studies involving workers with varying levels and durations of exposure have also reported no cognitive correlations (Gericke et al. 2001; Seeber et al. 2009).
In the absence of a clear neurobiological basis for compromised cognitive performance, several investigators have questioned the validity of solvent-induced cognitive impairment (Gericke et al. 2001). However, cognitive changes observed in solvent-exposed subjects may be due to neurochemical alterations that can be detected with functional imaging. For example, in a study by Haut et al. (2000), positron emission tomography (PET) scans revealed that subjects diagnosed with chronic solvent encephalopathy (n = 6) did not use typical areas of anterior activation [dorsolateral prefrontal cortex (DLPFC)] and showed less anterior activity than did controls (n = 6) without solvent exposure but with comparable behavioral performance on the experimental task. That study, however, included a small number of subjects (n = 6) diagnosed with cognitive dysfunction based on a previous comprehensive neuropsychological evaluation and therefore may not reflect the larger group of workers chronically exposed to solvents.
Thus, the purpose of the present study was to evaluate neural activation patterns with functional MRI (fMRI) during performance of working memory tasks among construction workers with and without chronic exposure to solvents and without a diagnosed cognitive impairment.
Materials and Methods
Subjects. One hundred and thirty-three solvent-exposed subjects (industrial painters) and 78 controls (drywall tapers, glazers, carpenters) were recruited for the study, which included a screening medical evaluation; a structured psychiatric interview (Composite International Diagnostic Interview for Diagnostic and Statistical Manual of Mental Disorders, Fourth Edition [DSM-IV (CIDI)] (American Psychiatric Association 1994); cognitive and sensory testing; assessment of lifetime use of alcohol, marijuana, and cocaine; and lifetime history of solvent exposure. A subgroup of these subjects volunteered to participate in the fMRI study (46 solvent exposed; 39 controls). There were no females among the participants. Solvent-exposed workers had at least 10 years of employment in their respective trades. Control subjects who reported solvent exposure were excluded (n = 4). After screening for psychiatric conditions, current medication use, MRI compatibility, incidental findings, ability to perform the N-Back task, and excessive motion during the scans, 19 solvent-exposed workers and 12 controls were eliminated from further analysis. For the depression assessment, we used the Beck Depression Inventory-II (BDI-II) questionnaire, a widely used depression scale with excellent reliability (Beck et al. 1996). Reading test scores [North American Adult Reading Test (NAART) (Blair and Spreen 1989)] were used as an indicator of verbal intelligence. After the study procedures were fully explained, all participants provided informed consent. Study protocols, including informed consent procedures, were approved by the institutional review boards of UMDNJ-Robert Wood Johnson Medical School and Mount Sinai Medical School.
Exposure assessment. We calculated a cumulative lifetime exposure index for each subject who reported ever working with solvent-based paints. The work duration and time spent performing specific job tasks (spray, roller, brush, rag/sponge, and cleaning equipment) was determined based on the completion of a computerized questionnaire administered by a trained technician. Subjects reported painting activities in 5-year intervals, estimating the percentage of time spent in each activity and the protective equipment worn during those activities for their working lifetime. Subjects reported in the questionnaire that they uniformly wore clothing that covered their skin during bridge and other industrial painting tasks, so no estimate of dermal exposure from solvents was included in the final exposure calculation.
To assess representative air concentrations of solvents during current painting activities, field samples were collected in a series of week-long sampling programs during different seasons at New Jersey Department of Transportation and New York City Bridge Maintenance work sites (Qian et al. 2010). Historic estimates of exposure to solvents were estimated from changes in paint composition determined by U.S. Environmental Protection Agency (EPA) regulations to reduce ozone, research literature reports from the past 25 years (e.g., PubMed, TOXLINE), regulatory documents (e.g., Health Hazard Evaluation, U.S. EPA, Material Safety Data Sheets), and commercial sources (e.g., National Paints and Coatings Association, Journal of Protective Coatings and Linings). We followed this approach because only limited data exist documenting historical air concentrations of organic solvents during construction painting.
Exposure to solvents during painting activities, however, is reduced with the use of protective equipment. For example, since 1998 painters have been required by the Occupational Safety and Health Administration (OSHA) to wear respirators when spraying in a confined space (OSHA 1998) but not for brushing or rolling operations. Therefore, lifetime exposure to solvents was modified based on the type of respirator used and the amount of time a respirator was worn during different painting activities. We searched the American National Standards Institute, National Institute for Occupational Safety and Health (NIOSH), OSHA, PubMed (National Center for Biotechnology Information 2010), TOXLINE (National Library of Medicine 2010), and respirator manufacturers’ databases for current and historical assigned protection factors of different respirators.
The solvent exposure index was calculated from the time spent applying paint with each application method (T), air concentrations of organic solvents for that application method during the appropriate time period (C), and a protection factor for the protective equipment (P) used during the appropriate time period according to Equation 1:
where i, j, k, and m are indices for the five 5-year intervals worked (1981–2005), months worked in each 5-year interval, weeks per month, and application method, respectively (questionnaire data); Cijkm is the air concentration of organic solvent (parts per million; personal air sampling badges, field air samples, historical paint composition, and air concentration data); Tijkm is the painting time (hours per week; questionnaire data); and Pijkm is the protection factor of respirator type (questionnaire data and historical protection factors).
The calculated solvent exposures were summed over all the exposure events of the subject’s career to generate the cumulative lifetime solvent exposure index in parts per million-hours. We performed a Monte Carlo simulation using 240 iterations to provide an empirical distribution of the exposure simulation for each painter, rather than calculating the exposure index as a single mean concentration for each painting method and protection factor for all painters during each time period. The median value from the distribution was assigned as the exposure index for each subject. For the Monte Carlo simulation, the time spent painting and the protective equipment used were entered as constants for each 5-year time period based on questionnaire responses (Wang et al. in press). Air concentrations varied using the actual data collected during current painting activities (Qian et al. 2010), adjusted with data from the literature documenting historic air concentrations.
Imaging. All imaging was performed on a 1.5-T Sonata MRI scanner (Siemens, Erlangen, Germany). We performed fMRI using a blood-oxygenation level–dependent (BOLD) technique, an MRI method to measure regional blood flow (Ogawa et al. 1990). Gradient echo planar imaging sequence was acquired using the following protocol: 32 axial slices, 3 mm skip 1 mm, repetition time (TR) = 2.5 sec, echo time (TE) = 30 msec, flip angle = 90°, field of view (FOV) = 21 cm, matrix size = 64 × 64. For incidental pathology screening, we also acquired T2-weighted anatomical scans of the whole brain using a turbo spin-echo pulse sequence (34 axial slices, TR = 5,380 msec, TE = 99 msec, flip angle = 170°, FOV = 210 mm, matrix = 512 × 336, voxel size = 0.41 × 0.41 × 4 mm). All scans were read by a radiologist for incidental findings. For coregistration and normalization purposes, a high-resolution T1-weighted structural image with good gray/white matter contrast was acquired using a three-dimensional magnetization-prepared rapid-gradient echo sequence with the following protocol: matrix size = 256 × 256 × 208, FOV = 21 cm, TR = 2,500 msec, TE = 4.38 msec, inversion time (TI) = 1,100 msec, and an 8° flip-angle fast low-angle-shot (FLASH) acquisition, giving a total imaging time of about 10 min.
Working memory task. We applied an N-Back task during the fMRI acquisition for activation of the working memory circuitry. The N-Back task (Kirchner 1958; Owen et al. 2005) is a continuous performance task that is commonly used in functional imaging for the study of cognition where memory load can be adjusted using the parameter N. In our implementation of the fMRI-compatible N-Back task, the subject is presented with a sequence of letters (using a visual display mounted in the MRI scanner bore) and asked to press a button when presented with target letters defined according to one of N prespecified conditions (in this case, four conditions referred to as 0-, 1-, 2-, or 3-back). For the 0-back condition, the subject had to identify the target letter “T” each time it was presented. For the 1-back condition, the subject was asked to identify each letter that matched the letter preceding it, so that target letters for the sequence “BDDOFFHBYYFKKL,” for example, would have been the second D, F, Y, and K in the sequence (shown in italics for illustration only). For a 2-back pattern the subject was asked to identify letters that matched a letter two positions back in the sequence (e.g., the second K, F, U, and S in the sequence “DKJKFGFUBUCSKS”), and for a 3-back pattern the subject was asked to identify letters that matched a letter three positions back. Subjects received instructions and performed testing trials for each condition before they entered the MRI suite. Each of the four conditions was repeated three times in a counterbalanced pseudo-random order, with each 28-sec N-Back run preceded by an 8-sec period of fixation and a 4-sec instruction period to inform the subject of the task level (0-, 1-, 2-, or 3-back; total scan time, 8 min 8 sec). Responses were recorded using a Brainlogics fiber optics subject response glove (PST Inc., Pittsburgh, PA). Task performance was scored using the ePrime program (PST Inc.) as correct hits (subject identified the correct target), false hits (subject pressed the button when a nontarget letter was displayed), and misses (subject did not press the button when a target letter was displayed). In addition, the 0-back condition was used to determine average reaction times by recording the time difference between the presentation of the 0-back target and the time of button press.
Analysis. For analysis and visualization of the fMRI, we used both software developed in-house under Matlab (version 7.8; Mathworks Inc., Natick, MA) and public domain software. BOLD data were processed using SPM5 software (Wellcome Department of Cognitive Neurology, Institute of Neurology, University College London, London, UK). fMRI analysis followed standard procedures using SPM5. Briefly, functional data was slice-time corrected by interpolation to the middle slice before motion correction. The functional images were coregistered to each subject’s anatomical scans. Coregistered anatomical images were then segmented to produce the parameters used for normalization into a standard anatomical brain reference template developed by the Montreal Neurological Institute (Collins et al. 1994; Evans et al. 1992). Using this reference atlas, voxel locations in the brain can be referenced using absolute x-, y-, and z-coordinates. The number of voxels in an activated region is indicated as cluster size. The brain region that such voxel/coordinates fall into is indicated by a Brodmann area number, as is normally done in fMRI reports (Brodmann 1909). We have also indicated the actual names of these regions [e.g., anterior cingulate cortex (ACC), DLPFC, insular cortex IC, and parietal portex (PC)]. Images were spatially smoothed using a 6-mm isotropic Gaussian smoothing kernel. Individual contrast images were produced in the context of the general linear model using a boxcar function (0-back vs. 1-, 2-, 3-back) convolved with a canonical hemodynamic response function. Next, to produce a group activation map, we performed a one-sample t-test using each subject’s contrast images to determine areas of increased activity during the active (1-, 2-, 3-back) state compared with baseline (0-back). Significant clusters were identified (p < 0.001, uncorrected). Additional voxelwise t-tests for group differences in activation were computed (Toga and Mazziota 2002). A voxelwise analysis of covariance (ANCOVA) was computed to compare the activation levels of each group while accounting for differences in overall task performance using d-prime as a nuisance variable. For the solvent-exposed group, we also computed voxel-by-voxel correlation maps between percent activation (defined as the amount of BOLD signal level while performing the N-Back task relative to the BOLD signal while at rest) and solvent exposure levels. To analyze regional blood flow differences, we extracted percent activation values from the regions as defined in the significant activation clusters in the group maps. Regions of interest (ROIs) with 3-mm radii were obtained from the local maxima of these clusters. Percent activation values for these ROIs were extracted from individual subjects’ scans and transferred to Statistica (version 9; Statsoft Inc., Tulsa, OK) for further statistical analysis. Partial correlation analysis was performed while controlling for the following confounding variables: current blood lead level; verbal IQ (NAART); lifetime alcohol, marijuana, and cocaine use; age; and depression score. NAART and lifetime alcohol use, lead exposure, marijuana use, and cocaine use for each subject were classified by percentile rank according to the distribution among all study participants.
Behavioral. We used t-tests to compare N-Back accuracy and reaction time between solvent-exposed subjects and controls.
Among the painters, we excluded 19 subjects from the analysis because of current psychiatric disorder (n = 3), current use of medication (n = 3), no solvent exposure (n = 5), and incomplete data (n = 8). Among the controls, we excluded 12 because of exposure to solvents (n = 4), current psychiatric disorder (n = 1), medication use (n = 2), anatomical finding (n = 1), and incomplete data (n = 4). Solvent-exposed subjects were similar to controls in age; education; number of years worked; lifetime alcohol, marijuana, and cocaine use; and BDI scores (Table 1). Although from similar occupational groups, the solvent-exposed subjects had significantly lower reading test scores (NAART) and significantly higher blood lead concentrations than did controls. Controls were more likely to be Caucasian than were solvent-exposed workers.
The performance scores of the N-Back task (Table 2) showed that solvent-exposed subjects scored significantly fewer correct hits (p = 0.005) and more false hits (p = 0.016) than controls, consistent with previous neurobehavioral studies (Bockelmann et al. 2002; Colvin et al. 1993; Kishi et al. 1993; Morrow et al. 1992; Ryan et al. 1988). For the 0-back condition (press button when target appears) used to estimate reaction time, solvent-exposed subjects were slower than controls (p = 0.034).
The statistical parametric mapping (SPM) group maps show areas of activation consistent with other fMRI studies using working memory paradigms in normal controls. We detected significant activated clusters in the ACC, DLPFC, PC, and insular cortex (IC) (Figure 1, Table 3). Because of the imbalance in race (no African Americans in the control group), we performed the between-group comparisons on Caucasians only. After correcting for verbal IQ and lead exposure, SPM maps showed that, relative to controls, solvent-exposed subjects had reduced activation in areas in the ACC and bilateral DLPFC (Figure 2A). Accounting for task performance differences, the ANCOVA showed that the solvent-exposed subjects had significantly reduced activation in the left DLPFC and increased activation in the left parietal regions compared with controls (Figure 2B). Among solvent-exposed subjects, lifetime solvent exposure was significantly and negatively correlated with activation detected in the ACC, DLPFC, and PC after control for confounders (Figure 3, Table 4). Percent activation values extracted from the ROIs also showed significant correlations with lifetime solvent exposure (Table 4).
SPM group activation map comparing N‑Back performance with rest for all subjects [painters (n = 27) and controls (n = 27)]. Significant activated clusters (p < 0.001) in the anterior cingulate gyrus (ACG), prefrontal cortex (PFC), IC, and PC are shown using a rainbow color spectrum superimposed on anatomical magnetic resonance images. Significantly activated voxels are colored from purple (p = 0.001) to red (variable depending on location, but at least p < 0.001).
SPM maps corrected for verbal IQ and lead exposure (A) or corrected for verbal IQ, lead exposure, and task performance (B) of significant group differences (p < 0.001) in activation of the working memory network. Green indicates regions where painters had lower activation and blue indicates regions where painters had higher activation, compared with controls.
SPM maps of significant correlations (p < 0.001) between activation and lifetime solvent exposure in painters. Green indicates decreased activation with increased exposure levels (observed in anterior cingulate gyrus, prefrontal cortex, PC, and IC); blue indicates increased activation with increased exposure levels (no significant voxels present); and red indicates general group activation patterns with the N‑Back task.
This is one of the few human fMRI studies to evaluate activation patterns among individuals with chronic occupational exposure to solvent mixtures and control of potential confounders. As hypothesized, our study showed a negative correlation between solvent exposure and activation in the ACC, DLPFC, and PC among the solvent-exposed group, suggesting defects in the brain circuitry underlying performance of attention and working memory tasks. Moreover, solvent-exposed subjects exhibited significantly lower activation of the ACC and DLPFC and significantly worse performance on the N-Back task than did controls. Our findings of lower activity in the ACC and DLPFC of solvent-exposed workers compared with controls is consistent with studies that used nuclear tracer techniques such as single-photon-emission computed tomography (SPECT) or PET and found reduced blood flow in these areas (Callender et al. 1993; Fincher et al. 1997; Haut et al. 2000).
The behavioral performances between solvent-exposed workers and controls were significantly different, and one might argue that the resulting activation differences are the result of performance. We ran a voxel-by-voxel ANCOVA to take into account the behavioral performance differences between the groups. This result showed that the left DLPFC had reduced activation in the solvent-exposed subjects but regions in their left PC showed increased activity relative to the controls. Evidence of compensatory increases in the function of regions in the PC was also reported in a PET study by Haut et. al. (2000). Although in that study a much smaller number of subjects were imaged (six exposed to organic solvents vs. six controls) using a different working memory task, and the authors also reported reduced activation in the left DLPFC. One explanation for this left-sided significance is that our working memory task involved letters and thus was likely to be verbally mediated (Petrides et al. 1993; Smith et al. 1996).
It has been widely accepted that working memory is supported by a tightly integrated network of the frontal and parietal regions (Chafee and Goldman-Rakic 2000; Jung and Haier 2007; Posner and Petersen 1990). A dysfunctional prefrontal cortex may cause aberrant activation patterns in the posterior aspects of the brain. Our finding of increased activity in the parietal lobe in solvent-exposed subjects compared with controls supports this notion. Some fMRI studies have shown a population sample having hyperactivity in the target brain region as an indicator of dysfunction. This hyperactivity is assumed to be an indicator of local compensatory function: The less “efficient” brain region has to work harder (showing increased blood flow) to perform the same task, as has been shown in studies of normal cognition and intelligence (Haier 1993; Neubauer and Fink 2009). Other fMRI studies have detected a different pattern of activation in the population sample, which is taken as an indicator of brain plasticity where other brain regions have taken over the function of the target brain region, which is allegedly defective. This has been reported in alcohol studies (Pfefferbaum et al. 2001) and in solvent exposure studies (Haut et al. 2000). The observed hypoactivity is similar to studies that found reduced activation in areas affected by traumatic brain injury (Chen et al. 2004; McAllister et al. 2006) or Alzheimer’s disease (Johnson et al. 2006). In the present study we found this reduced activity in the DLPFC to be more specific in the left DLPFC after we accounted for the task performance. The reduced activation in the affected brain areas is consistent with altered neuronal pathology, which might be caused by an altered blood supply mechanism or neuronal death due to solvent exposure rather than due to performance.
As part of the present study, we also acquired proton density and T2-weighted images for the purpose of screening for incidental pathologies. We excluded from the analysis patients with white matter abnormalities, as determined by hyperintensities in the T2-weighted images. This suggests that the loci that differed between the solvent-exposed subjects and the controls involved gray matter regions, although we cannot rule out the possibility that white matter played a role as well. A study using other imaging techniques such as diffusion tensor imaging (Basser et al. 2000) might elucidate the role of white matter. Our correlation results also show an inverse relationship between activation and lifetime solvent exposure among the solvent-exposed subjects, supporting a direct relationship between exposure and blood flow in brain regions that subserve working memory as opposed to indirect compensatory or other cognitive effects.
The prefrontal cortex together with the parietal and anterior cingulate forms the neural substrate for working memory and attention (Posner and Petersen 1990; Smith and Jonides 1999; Smith et al. 1998). The prefrontal cortex is the last brain region to develop in the human brain and may be the most vulnerable to physical or chemical insults. The prefrontal cortex is the most vulnerable in neurodegenerative disorders, and atrophy of the prefrontal cortex is also one of the morphological changes in aging (Decarli et al. 1994; Fuster 2008; Raz et al. 1997).
A few studies have looked into solvent effects on neurotransmitters such as dopamine, acetylcholine, and γ-aminobutyric acid (GABA), with limited consistent results. Brain dopamine concentrations with solvent exposure have been studied in rodent models, and both increases (Rea et al. 1984) and decreases (Kondo et al. 1995) have been reported, albeit using different methodologies. The dopamine relationship is certainly relevant considering that it is an important neurotransmitter involved in DLPFC signaling (Williams and Goldman-Rakic 1995). Increases in striatal acetylcholine with exposure levels have also been reported (Honma 1983; Stengard 1995; Tsuga and Honma 2000). Changes in GABA binding detected in rat frontal cortex depended on the chronic or subchronic exposure levels (Beckstead et al. 2000; Bjornaes and Naalsund 1988). GABA might be a reasonable target considering the addictive effects in the recreational use of certain solvents. Many additional studies on the effects of solvents on other neurotransmitter actions such as GABAa, glycine, N-methyl-D-aspartic acid, nicotine, and 5-hydroxytryptamine-3 have been performed (Bowen et al. 2006).
Anatomical studies of solvent exposure in humans have shown diffuse atrophy in the cerebellar regions, brainstem, frontal cortex, and PC (Keski-Santti et al. 2009; Rosenberg et al. 2002; Thuomas et al. 1996). Most of these anatomical findings were nonspecific, and some included the frontal and parietal regions where we found evidence of functional deficits. The results of our functional imaging study in the frontal and parietal regions are also consistent with the diminished cognitive function observed among solvent-exposed subjects.
The solvent-exposed subjects in our study have worked with solvent mixtures for an average of 22 years. Unfortunately, we do not have actual historical measurements of solvent exposure for our subjects and therefore cannot determine a specific dose–response analysis for the imaging results in this study. Nevertheless, the highly significant relationship between our lifetime solvent exposure metric and activation patterns validates the neural basis for alterations in cognitive function so often observed among these workers. Future studies are needed to better understand the exposure concentrations over a working lifetime associated with neurological effects among workers.
The current OSHA permissible exposure limit (PEL) for toluene is 200 ppm, the same value as for general industry. The (NIOSH) PEL is 100 ppm, whereas the threshold limit value for toluene as recommended by American Conference of Governmental Industrial Hygienists (ACGIH) is 50 ppm (Agency for Toxic Substances and Disease Registry 2001). Unfortunately, without actual historical exposure measurements for our subjects, we cannot be certain of the exact solvent concentrations to which they were exposed. Although many manufacturing sites follow current and historical ACGIH recommendations, worksites for construction painters are often less well controlled, and industrial hygiene measurements are not routinely collected (Qian et al. 2010). Therefore, excursions from recommended solvent exposure limits may have occurred. In addition, it is not unreasonable to believe that our sample of solvent-exposed subjects was exposed to higher concentrations historically than those recommended currently by ACGIH based on their average (i.e., 22 years) and minimum (10 years) lengths of time spent working with solvent-based paints. Under these estimated exposure conditions, our results show changes in the biological substrates that are consistent with the neurobehavioral observations documented in an extensive literature of workers who continue to be exposed to solvent mixtures during their working lifetime.
- Agency for Toxic Substances and Disease Registry 2001. Toluene Toxicity: Standards and Regulations. Available: http://www.atsdr.cdc.gov/csem/toluene/standards_regulations.html [accessed 26 May 2011]
- American Psychiatric Association 1994. Diagnostic and Statistical Manual of Mental Disorders (DSM-IV). 4th ed. Washington, DC:American Psychiatric Association.
- Baker EL. 1994. A review of recent research on health effects of human occupational exposure to organic solvents. A critical review. J Occup Med 36(10):1079–1092.
- Basser PJ, Pajevic S, Pierpaoli C, Duda J, Aldroubi A. 2000. In vivo fiber tractography using DT-MRI data. Magn Reson Med 44(4):625–632.
- Beck AT, Steer RA, Brown GK. 1996. BDI-II, Beck Depression Inventory: Manual. San Antonio, TX:Psychological Corporation.
- Beckstead MJ, Weiner JL, Eger EI, Gong DH, Mihic SJ. 2000. Glycine and γ-aminobutyric acidA receptor function is enhanced by inhaled drugs of abuse. Mol Pharmacol 57(6):1199–1205.
- Benignus VA, Geller AM, Boyes WK, Bushnell PJ. 2005. Human neurobehavioral effects of long-term exposure to styrene: a meta-analysis. Environ Health Perspect 113:532–538.
- Bjornaes S, Naalsund LU. 1988. Biochemical changes in different brain areas after toluene inhalation. Toxicology 49(2–3):367–374.
- Blair JR, Spreen O. 1989. Predicting premorbid IQ: a revision of the National Adult Reading Test. Clin Neuropsychol 3(2):129–136.
- Bockelmann I, Darius S, McGauran N, Robra BP, Peter B, Pfister EA. 2002. The psychological effects of exposure to mixed organic solvents on car painters. Disabil Rehabil 24(9):455–461.
- Bowen SE, Batis JC, Paez-Martinez N, Cruz SL. 2006. The last decade of solvent research in animal models of abuse: mechanistic and behavioral studies. Neurotoxicol Teratol 28(6):636–647.
- Brodmann K. 1909. Vergleichende Lokalisationslehre der Grosshirnrinde in ihren Prinzipien dargestellt auf Grund des Zellenbaues. Leipzig:Barth.
- Callender TJ, Morrow L, Subramanian K, Duhon D, Ristovv M. 1993. Three-dimensional brain metabolic imaging in patients with toxic encephalopathy. Environ Res 60(2):295–319.
- Chafee MV, Goldman-Rakic PS. 2000. Inactivation of parietal and prefrontal cortex reveals interdependence of neural activity during memory-guided saccades. J Neurophysiol 83(3):1550–1566.
- Chen JK, Johnston KM, Frey S, Petrides M, Worsley K, Ptito A. 2004. Functional abnormalities in symptomatic concussed athletes: an MRI study. Neuroimage 22(1):68–82.
- Collins DL, Neelin P, Peters TM, Evans AC. 1994. Automatic 3D intersubject registration of MR volumetric data in standardized Talairach space. J Comput Assist Tomogr 18(2):192–205.
- Colvin M, Myers J, Nell V, Rees D, Cronje R.. 1993. A cross-sectional survey of neurobehavioral effects of chronic solvent exposure on workers in a paint manufacturing plant. Environ Res 63(1):122–132.
- Decarli C, Murphy DGM, Gillette JA, Haxby JV, Teichberg D, Schapiro MB, et al. 1994. Lack of age-related differences in temporal lobe volume of very healthy adults. Am J Neuroradiol 15(4):689–696.
- Ellingsen DG, Bekken M, Kolsaker L, Langard S. 1993. Patients with suspected solvent-induced encephalopathy examined with cerebral computed tomography. J Occup Med 35(2):155–160.
- Evans AC, Marrett S, Neelin P, Collins L, Worsley K, Dai W, et al. 1992. Anatomical mapping of functional activation in stereotactic coordinate space. Neuroimage 1(1):43–53.
- Filley CM, Heaton RK, Rosenberg NL. 1990. White matter dementia in chronic toluene abuse. Neurology 40(3 pt 1):532–534.
- Fincher CE, Chang TS, Harrell EH, Kettelhut MC, Rea WJ, Johnson A, et al. 1997. Comparison of single photon emission computed tomography findings in cases of healthy adults and solvent-exposed adults. Am J Ind Med 31(1):4–14.
- Fuster JM. 2008. The Prefrontal Cortex. 4th ed. Boston:Academic Press.
- Gericke C, Hanke B, Beckmann G, Baltes MM, Kuhl KP, Neubert D, et al. 2001. Multicenter field trial on possible health effects of toluene—III. Evaluation of effects after long-term exposure. Toxicology 168(2):185–209.
- Haier RJ, ed. 1993. Cerebral Glucose Metabolism and Intelligence. Norwood, NJ:Ablex.
- Haut MW, Leach S, Kuwabara H, Whyte S, Callahan T, Ducatman A, et al. 2000. Verbal working memory and solvent exposure: a positron emission tomography study. Neuropsychology 14(4):551–558.
- Honma T.. 1983. Changes in acetylcholine metabolism in rat brain after a short-term exposure to toluene and normal hexane. Toxicol Lett 16(1–2):17–22.
- Johnson SC, Schmitz TW, Moritz CH, Meyerand ME, Rowley HA, Alexander AL, et al. 2006. Activation of brain regions vulnerable to Alzheimer’s disease: the effect of mild cognitive impairment. Neurobiol Aging 27(11):1604–1612.
- Jung RE, Haier RJ. 2007. The Parieto-Frontal Integration Theory (P-FIT) of intelligence: converging neuroimaging evidence. Behav Brain Sci 30(2):135–154.
- Keski-Santti P, Mantyla R, Lamminen A, Hyvarinen HK, Sainio M. 2009. Magnetic resonance imaging in occupational chronic solvent encephalopathy. Int Arch Occup Environ Health 82(5):595–602.
- Kirchner WK. 1958. Age differences in short-term retention of rapidly changing information. J Exp Psychol 55(4):352–358.
- Kishi R, Harabuchi I, Katakura Y, Ikeda T, Miyake H.. 1993. Neurobehavioral effects of chronic occupational exposure to organic solvents among Japanese industrial painters. Environ Res 62(2):303–313.
- Kondo H, Huang J, Ichihara G, Kamijima M, Saito I, Shibata E, et al. 1995. Toluene induces behavioral activation without affecting striatal dopamine metabolism in the rat—behavioral and microdialysis studies. Pharmacol Biochem Behav 51(1):97–101.
- McAllister TW, Flashman LA, McDonald BC, Saykin AJ. 2006. Mechanisms of working memory dysfunction after mild and moderate TBI: evidence from functional MRI and neurogenetics. J Neurotrauma 23(10):1450–1467.
- Mikkelsen S.. 1997. Epidemiological update on solvent neurotoxicity. Environ Res 73(1–2):101–112.
- Morrow LA, Robin N, Hodgson MJ, Kamis H. 1992. Assessment of attention and memory efficiency in persons with solvent neurotoxicity. Neuropsychologia 30(10):911–922.
- National Center for Biotechnology Information 2010. PubMed. Available: http://www.ncbi.nlm.nih.gov/pubmed [accessed 27 December 2010]
- National Library of Medicine 2010. Toxicology Literature Online (TOXLINE). Available: http://toxnet.nlm.nih.gov/cgi-bin/sis/htmlgen?TOXLINE [accessed 27 December 2010]
- Neubauer AC, Fink A. 2009. Intelligence and neural efficiency. Neurosci Biobehav Rev 33(7):1004–1023.
- Ogawa S, Lee TM, Kay AR, Tank DW. 1990. Brain magnetic resonance imaging with contrast dependent on blood oxygenation. Proc Natl Acad Sci USA 87(24):9868–9872.
- OSHA (Occupational Safety and Health Administration) 1998. Respiratory protection; final rule, 29 CFR Parts 1910 and 1926. Fed Reg 63:1152–1300.
- Owen AM, McMillan KM, Laird AR, Bullmore E. 2005. N-Back working memory paradigm: a meta-analysis of normative functional neuroimaging. Hum Brain Map 25(1):46–59.
- Petrides M, Alivisatos B, Meyer E, Evans AC. 1993. Functional activation of the human frontal-cortex during the performance of verbal working memory tasks. Proc Natl Acad Sci USA 90(3):878–882.
- Pfefferbaum A, Desmond JE, Galloway C, Menon V, Glover GH, Sullivan EV. 2001. Reorganization of frontal systems used by alcoholics for spatial working memory: an fMRI study. Neuroimage 14(1):7–20.
- Posner MI, Petersen SE. 1990. The attention system of the human brain. Annu Rev Neurosci 13:25–42.
- Qian H, Fiedler N, Moore DF, Weisel CP. 2010. Occupational exposure to organic solvents during bridge painting. Ann Occup Hygiene 54(4):417–426.
- Raz N, Gunning FM, Head D, Dupuis JH, McQuain J, Briggs SD, et al. 1997. Selective aging of the human cerebral cortex observed in vivo: differential vulnerability of the prefrontal gray matter. Cereb Cortex 7(3):268–282.
- Rea TM, Nash JF, Zabik JE, Born GS, Kessler WV. 1984. Effects of toluene inhalation on brain biogenic amines in the rat. Toxicology 31(2):143–150.
- Ridgway P, Nixon TE, Leach JP. 2003. Occupational exposure to organic solvents and long-term nervous system damage detectable by brain imaging, neurophysiology or histopathology. Food Chem Toxicol 41(2):153–187.
- Rosenberg NL, Grigsby J, Dreisbach J, Busenbark D, Grigsby P. 2002. Neuropsychologic impairment and MRI abnormalities associated with chronic solvent abuse. J Toxicol Clin Toxicol 40(1):21–34.
- Rosenberg NL, Spitz MC, Filley CM, Davis KA, Schaumburg HH. 1988. Central nervous system effects of chronic toluene abuse—clinical, brainstem evoked response and magnetic resonance imaging studies. Neurotoxicol Teratol 10(5):489–495.
- Ryan CM, Morrow LA, Hodgson M. 1988. Cacosmia and neurobehavioral dysfunction associated with occupational exposure to mixtures of organic solvents. Am J Psychiatry 145(11):1442–1445.
- Seeber A, Bruckner T, Triebig G.. 2009. Occupational styrene exposure and neurobehavioural functions: a cohort study with repeated measurements. Int Arch Occup Environ Health 82(8):969–984.
- Smith EE, Jonides J. 1999. Storage and executive processes in the frontal lobes. Science 283(5408):1657–1661.
- Smith EE, Jonides J, Koeppe RA. 1996. Dissociating verbal and spatial working memory using PET. Cereb Cortex 6(1):11–20.
- Smith EE, Jonides J, Marshuetz C, Koeppe RA. 1998. Components of verbal working memory: evidence from neuroimaging. Proc Natl Acad Sci USA 95(3):876–882.
- Stengard K.. 1995. Tail pinch increases acetylcholine release in rat striatum even after toluene exposure. Pharmacol Biochem Behav 52(2):261–264.
- Thuomas KA, Moller C, Odkvist LM, Flodin U, Dige N. 1996. MR imaging in solvent-induced chronic toxic encephalopathy. Acta Radiol 37(2):177–179.
- Toga AW, Mazziota JC. 2002. Analysis. In: Brain Mapping: The Methods. 2nd ed. San Diego:Elsevier. pp. 605–687.
- Tsuga H, Honma T.. 2000. Effects of short-term toluene exposure on ligand binding to muscarinic acetylcholine receptors in the rat frontal cortex and hippocampus. Neurotoxicol Teratol 22(4):603–606.
- Unger E, Alexander A, Fritz T, Rosenberg N, Dreisbach J.. 1994. Toluene abuse: physical basis for hypointensity of the basal ganglia on T2-weighted MR images. Radiology 193(2):473–476.
- Wang SW, Qian H, Weisel C, Nwankwo C, Fiedler N. . Development of solvent exposure index for construction painters. J Occup Environ Hyg..
- Williams GV, Goldman-Rakic PS. 1995. Modulation of memory fields by dopamine D1 receptors in prefrontal cortex. Nature 376(6541):572–575.
- Yamanouchi N, Okada S, Kodama K, Hirai S, Sekine H, Murakami A, et al. 1995. White matter changes caused by chronic solvent abuse. AJNR Am J Neuroradiol 16(8):1643–1649.
As we begin a new year, we are highlighting EHP articles that attracted the most viewers in 2016: (more…)
Since 1993 the News section of EHP has provided readers with objective, accurate information on timely environmental health topics. After years as one of the most popular features of EHP, and as our main tool for reaching a broader audience, we felt it was time the News had its own home on our website. We are now pleased to present our brand-new page devoted exclusively to EHP News! (more…)
EHP is proud to announce that “Acute Impact of Hourly Ambient Air Pollution on Preterm Birth,” published in EHP on 29 April 2016, has been selected by the Children’s Environmental Health Network (CEHN) as its November 2016 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.