Accumulating evidence suggests that outdoor air pollution may have a significant impact on central nervous system (CNS) health and disease. To address this issue, the National Institute of Environmental Health Sciences/National Institute of Health convened a panel of research scientists that was assigned the task of identifying research gaps and priority goals essential for advancing this growing field and addressing an emerging human health concern. Here, we review recent findings that have established the effects of inhaled air pollutants in the brain, explore the potential mechanisms driving these phenomena, and discuss the recommended research priorities/approaches that were identified by the panel.

cells; C-6 cells; SchizophreniaSchizophrenia is a chronic psychiatric illness with two major types of symptoms-positive or psychotic symptoms, such as hallucinations and delusions, and negative or deficit symptoms, such as amotivation, apathy, and asociality. Approximately 1% of the population suffers from schizophrenia (Kaplan and Sadock 1988). The serendipitous discovery of chlorpromazine four decades ago not only provided the first efficacious therapeutic intervention, but also opened horizons into research about the etiology and therapy of this disease. It was soon hypothesized that chlorpromazine and similar drugs worked by being pharmacological antagonists of the neurotransmitter dopamine (Seeman et al. 1976;Creese et al. 1976), a hypothesis that ultimately provided the foundation for the commonly accepted division of dopamine receptors into two classes (Garau et al. 1978), now often called D 1 and D 2 (Kebabian and Calne 1979).During the past decade, molecular cloning studies have resulted in the identification of several genes coding for dopamine receptors. There now are at least two From the Departments of Pharmacology (CP, RBM) and Psychiatry (CPL, RBM), and Medicinal Chemistry (RBM), Curricula in Toxicology (CPL, RBM), and Neurobiology (MML, RBM), UNC Neuroscience Center (CPL, CP, MML, RBM), University of North Carolina School of Medicine, Chapel Hill, North Carolina; and Molecular Neuropharmacology Section (CM, DJ, JAS, AMG, DRS), National Institutes of Neurological Disorders and Stroke, Bethesda, Maryland.Address correspondence to: Dr. Cindy Lawler, CB #7250; UNC Neuroscience Center, University of North Carolina School of Medicine, Chapel Hill, NC 27599-7250. Received April 17, 1998; revised August 27, 1998; accepted September 21, 1998. (Zhou et al. 1990;Monsma et al. 1990;Sunahara et al. 1990;Dearry et al. 1990) and D 1B (Tiberi et al. 1991) or D 5 (Sunahara et al. 1991], both of these linked functionally to stimulation of cAMP synthesis, and preferentially recognizing 1-phenyl-tetrahydrobenzazepines (e.g., SCH23390). The D 2 -like receptors come from at least three genes and include multiple splice variants. The D 2 -like receptors [D 2S (Bunzow et al. 1988), D 2L (Giros et al. 1989;Monsma et al. 1989), D 3 (Sokoloff et al. 1990, and D 4 ] sometimes are linked to inhibition of cAMP synthesis and have a different pharmacological specificity from the D 1 -like receptors (i.e., having much higher affinity for spiperone or sulpiride).The traditional view of antipsychotic drug efficacy posits a primary role for pharmacological antagonism of D 2 -like receptors. Despite the demonstrable effectiveness of dopamine D 2 receptor antagonists, however, a substantial number (up to 20%) of patients are considered unresponsive to these typical antipsychotics (Kane et al. 1988). Furthermore, the typical antipsychotics have significant and serious side effects that make them less than optimal therapeutic agents (see Peacock and Gerlach 1996). For example, they cause acute drug-induced parkinsonian symptoms (...

BackgroundExposure to ambient air pollution is widespread and may be detrimental to human brain development and a potential risk factor for Autism Spectrum Disorder (ASD). We conducted a systematic review of the human evidence on the relationship between ASD and exposure to all airborne pollutants, including particulate matter air pollutants and others (e.g. pesticides and metals).ObjectiveTo answer the question: “is developmental exposure to air pollution associated with ASD?”MethodsWe conducted a comprehensive search of the literature, identified relevant studies using inclusion/exclusion criteria pre-specified in our protocol (registered in PROSPERO, CRD # 42015017890), evaluated the potential risk of bias for each included study and identified an appropriate subset of studies to combine in a meta-analysis. We then rated the overall quality and strength of the evidence collectively across all air pollutants.ResultsOf 1,158 total references identified, 23 human studies met our inclusion criteria (17 case-control, 4 ecological, 2 cohort). Risk of bias was generally low across studies for most domains; study limitations were related to potential confounding and accuracy of exposure assessment methods. We rated the quality of the body of evidence across all air pollutants as “moderate.” From our meta-analysis, we found statistically significant summary odds ratios (ORs) of 1.07 (95% CI: 1.06, 1.08) per 10-μg/m3 increase in PM10 exposure (n = 6 studies) and 2.32 (95% CI: 2.15, 2.51) per 10-μg/m3 increase in PM2.5 exposure (n = 3 studies). For pollutants not included in a meta-analysis, we collectively evaluated evidence from each study in rating the strength and quality of overall evidence considering factors such as inconsistency, imprecision, and evidence of dose-response. All included studies generally showed increased risk of ASD with increasing exposure to air pollution, although not consistently across all chemical components.ConclusionAfter considering strengths and limitations of the body of research, we concluded that there is “limited evidence of toxicity” for the association between early life exposure to air pollution as a whole and diagnosis of ASD. The strongest evidence was between prenatal exposure to particulate matter and ASD. However, the small number of studies in the meta-analysis and unexplained statistical heterogeneity across the individual study estimates means that the effect could be larger or smaller (including not significant) than these studies estimate. Our research supports the need for health protective public policy to reduce exposures to harmful airborne contaminants among pregnant women and children and suggests opportunities for optimizing future research.

Dihydrexidine (DHX), the first high-affinity D 1 dopamine receptor full agonist, is only 10-fold selective for D 1 versus D 2 receptors, having D 2 affinity similar to the prototypical agonist quinpirole. The D 2 functional properties of DHX and its more D 2 selective analog N-n-propyl-dihydrexidine (PrDHX) were explored in rat brain and pituitary. DHX and PrDHX had binding characteristics to D 2 receptors in rat striatum typical of D 2 agonists, binding to both high-and low-affinity sites and being sensitive to guanine-nucleotides. Consistent with these binding data, both DHX and PrDHX inhibited forskolin-stimulated cAMP synthesis in striatum with a potency and intrinsic activity equivalent to that of quinpirole. Unexpectedly, however, DHX and PrDHX had little functional effect at D 2 receptors expressed on dopaminergic neurons that mediate inhibition of cell firing, dopamine release, or dopamine synthesis. Quantitative receptor competition autoradiography demonstrated that DHX bound to D 2 receptors in striatum (predominantly postsynaptic receptor sites) with equal affinity as D 2 sites in the substantia nigra (autoreceptor sites). The data from these experiments, coupled with what is known about the location of specific dopamine receptor isoforms, lead to the hypothesis that DHX, after binding to D 2L and D 2S receptors, causes agonist-typical functional changes only at some of these receptors. This phenomenon (herein termed "functional selectivity") suggests that drugs may be targeted not only at specific receptor isoforms but also at separate functions mediated by a single isoform, yielding novel approaches to drug discovery. (D 2S ), D 3 , and D 4 . D 1 -like receptors preferentially recognize 1-phenyl-tetrahydrobenzazepines (e.g., SCH23390) over benzamides (e.g., sulpiride), whereas the D 2 -like receptors have the opposite pharmacological specificity. D 1 -and D 2 -like receptors have been defined traditionally by their opposing effects on the enzyme adenylate cyclase, with D 1 receptors positively coupled to this enzyme, whereas D 2 receptors are either negatively coupled or uncoupled to this effector. More recently, the actions of dopamine D 1 -and D 2 -like receptors on signaling systems other than adenylate cyclase have been confirmed in a variety of systems, including coupling to G protein inwardly rectifying potassium channels, phosphatidylinositol hydrolysis, and voltage-activated calcium channels (Jaber et al., 1996).

Recent data indicate that approximately 12% of children in the United States are affected by neurodevelopmental disorders, including attention deficit hyperactivity disorder, learning disorders, intellectual disabilities, and autism spectrum disorders. Accumulating evidence indicates a multifactorial etiology for these disorders, with social, physical, genetic susceptibility, nutritional factors, and chemical toxicants acting together to influence risk. Exposure to endocrine-disrupting chemicals during the early stages of life can disrupt normal patterns of development and thus alter brain function and disease susceptibility later in life. This article highlights research efforts and pinpoints approaches that could shed light on the possible associations between environmental chemicals that act on the endocrine system and compromised neurodevelopmental outcomes.