Faculty Bibliography

Soluble and insoluble chromium (Cr) agents are concomitantly released with ozone (O-3) during welding. Although pulmonary implications from exposure to each agent individually have been investigated, the effects from simultaneous exposure, as occurs under actual working conditions, are unclear. To investigate the retention/distribution of inhaled Cr, male F-344 rats were exposed nose-only to atmospheres containing soluble potassium chromate (K2CrO4) or O-3, either alone or in combination, at 360 mu g Cr/m(3) and 0.3 ppm O-3. In a second phase of the study, insoluble barium chromate (BaCrO4) was used in place of K2CrO4. Rats were exposed for 5 h/day, 5 days/wk for 2 or 4 wk. One day after the final exposure, rats were euthanized and their lungs either removed intact or lavaged for quantitation of tissue-, lavaged cell-, and acellular lavage fluid-associated Cr. In general, rats inhaling insoluble Cr had greater total lung Cr burdens than did rats exposed to soluble Cr. Simultaneous inhalation of O-3 and K2CrO4 led to reduced lung Cr levels compared to those in rats receiving K2CrO4 only; with BaCrO4 coexposure to O-3 resulted in increased lung BaCrO, levels compared to BaCrO3 alone. Particle solubility also affected Cr levels in lavageable cells, with those from rats inhaling BaCrO, alone or BaCrO4 + O-3 consistently having greater burdens than their K2CrO4 counterparts; the presence of O-3 itself had no effect upon cell Cr levels when either compound was used. Solubility-dependent differences were also apparent in acellular lavage fluid, with Cr levels initially being greater in fluids from rats inhaling K2CrO4 alone; as exposures continued, these burdens became greater in the rats inhaling BaCrO4 alone. Although inhalation of either Cr/O-3 mixture yielded significant differences in fluid Cr levels, the presence of 4 did lead to reductions in levels compared to those in rats inhaling either Cr agent alone. In postlavage lung tissue, there were time-dependent increases in Cr levels in rats from all exposure groups; however, the most dramatic increase occurred with rats exposed to BaCrO4 + O-3. Lastly, while significant solubility-dependent differences in the relative distribution of Cr among the three pulmonary compartments were discerned, a specific effect attributable to O-3 itself was not evident. The results of this study indicate that Cr retention and distribution within the lungs, as well as any effect from coexposure to O-3, are modulated by the solubility of the inhaled Cr particles

Hosts exposed to vanadium (V) display a subsequent decrease in their resistance to infectious microorganisms. Our earlier studies with rats inhaling occupationally relevant levels of V (as, ammonium metavanadate, NH4VO3) indicated that several nascent/inducible functions of pulmonary macrophages (PAM) were reduced. In the present study, V-exposed rats were examined to determine whether some of the same effects might also occur in situ. Rats were exposed nose-only to air or 2 mg V/m3 (as NH4VO3) for 8 h/d for 4 d, followed, 24 h later, by intratracheal (it) instillation of polyinosinic:polycytidilic acid (polyl:C) or saline. Analysis of lavaged lung cells/fluids after polyl:C instillation indicated that total lavageable cell/neutrophil numbers and protein levels, while significantly elevated in both exposure groups (as well as in saline-treated V-exposed rats), were always greater in V-exposed hosts. Exposure to V also affected the inducible production of interleukin 6 (IL-6) and interferon gamma (IFN gamma), but apparently not that of tumor necrosis factor-alpha (TNF alpha) or IL-1. Although polyl:C induced significant increases in lavage fluid IL-6 and IFN gamma levels in both exposure groups, levels were greater in V-exposed rats. If calculated with respect to total lavaged protein, however, V-exposed rats produced significantly less cytokine. Following polyl:C instillation, there were no marked exposure-related differences in basal or stimulated superoxide anion production by pooled lavaged cells or PAM specifically. With V-exposed rats, pooled cells recovered 24 h after saline instillation displayed reduced production (in both cases) compared to the air control cells; PAM-specific production was affected only after stimulation. In both exposure groups, polyl:C caused decreased superoxide production in recovered cells. Though less apparent with pooled cells, there was a time post polyl:C instillation-dependent decrease in stimulated PAM-specific superoxide production; this effect was greater in PAM from V-exposed rats than in PAM from air controls. Phagocytic activity of PAM from rats in both exposure groups was significantly increased by polyl:C instillation, although total activity in cells obtained from V-exposed rats was always significantly lower compared to air control cells. Our results indicate that short-term, repeated inhalation of occupationally relevant levels of V by rats modulates pulmonary immunocompetence. Modified cytokine production and PAM functionality in response to biological response modifiers (such as lipopolysaccharide, IFN gamma, or polyl:C) may be, at least in part, responsible for the increases in bronchopulmonary disease in humans occupationally exposed to V

The potential for chemicals to adversely affect human immunologic health has traditionally been evaluated in rodents, under laboratory conditions. These laboratory studies have generated valuable hazard identification and immunotoxicologic mechanism data; however, genetically diverse populations exposed in the wild may better reflect both human exposure conditions and may provide insight into potential immunotoxic effects in humans. In addition, comparative studies of species occupying reference and impacted sites provide important information on the effects of environmental pollution on the immunologic health of wildlife populations. In this symposium overview, Peter Hodson describes physiological changes in fish collected above or below the outflows of paper mills discharging effluent from the bleaching process (BKME). Effects attributable to BKME were identified, as were physiological changes attributable to other environmental factors. In this context, he discussed the problems of identifying true cause and effect relationships in field studies. Mohamed Faisal described changes in immune function of fish collected from areas with high levels of polyaromatic hydrocarbon contamination. His studies identified a contaminant-related decreases in the ability of anterior kidney leukocytes to bind to and kill tumor cell line targets, as well as changes in lymphocyte proliferation in response to mitogens. Altered proliferative responses of fish from the contaminated site were partially reversed by maintaining fish in water from the reference site. Peter Ross described studies in which harbor seals were fed herring obtained from relatively clean (Atlantic Ocean) and contaminated (Baltic Sea) waters. Decreased natural killer cell activity and lymphoproliferative responses to T and B cell mitogens, as well as depressed antibody and delayed hypersensitivity responses to injected antigens, were identified in seals fed contaminated herring. In laboratory studies, it was determined that rats fed freeze-dried Baltic Sea herring had higher virus titers after challenge with rat cytomegalovirus (RCMV) than rats fed Atlantic Ocean herring; perinatal exposure of rats to oil extracted from Baltic herring also reduced the response to challenge with RCMV. Keith Grassman reported an association between exposure to polyhalogenated aryl hydrocarbons and decreased T cell immunity in the offspring of fish-eating birds (herring gulls and Capsian terns) at highly contaminated sites in the Great Lakes. The greatest suppression of skin test responses to phytohemagglutinin injection (an indicator of T cell immunity) was consistently found at sites with the highest contaminant concentrations. Judith Zelikoff addressed the applicability of immunotoxicity studies developed in laboratory-reared fish for detecting altered immune function in wild populations. She presented data from studies done in her laboratory with environmentally relevant concentrations of metals as examples. Although the necessity of proceeding with caution when extrapolating across species was emphasized, she concluded that published data, and results presented by the other Symposium participants, demonstrate that assays similar to those developed for use in laboratory rodents may be useful for detecting immune system defects in wildlife species directly exposed to toxicants present in the environment.

Determination of the ability of a medical device to interact with the immune system currently involves assessment of the immunogenic potential and biocompatibility of the device or an extract of the device. However, implants are often in the body for extended periods of time and/or are placed by a surgical procedure that in and of itself will generate an acute inflammatory response. This symposium discussed studies that have been performed to evaluate the immunogenicity of various devices consisting of several different compositions (i.e., silicone, metals, and latex) in contact with different anatomical sites, the ability of a device to modulate an inflammatory response generated by a surgical procedure or trauma, and the response of the body to a material left in place for extended periods of time. This symposium brought together scientists from many different disciplines to begin to identify and fill in the gaps in this area.

To examine the biological plausibility of the adverse health effects of ambient paniculate matter (PM), we have studied the pulmonary and cardiovascular effects of ambient PM in an animal model of pulmonary hypertension. A centrifugal aerosol concentrator was used to concentrate ambient paniculate matter up to 10-fold. Normal and monocrotaline-treated rats were exposed nose-only for 3 hrs to filtered air or concentrated ambient PM ranging from 160 to 900 ?g/m3. At 3 hrs post-exposure, the percentage of neutrophils in peripheral blood was significantly elevated in PM-exposed animals while the percentage of lymphocytes was decreased. This demargination of neutrophils occurred in both normal and monocrotaline-treated animals. The hematological changes returned to control levels by 24 hrs after exposure. Evidence that these changes were a result of exposure to the particulate and not the gaseous components of urban air was demonstrated by a lack of hematological changes in animals exposed to HEPA-filtered air from the centrifugal concentrator. Heart rate and core temperature were monitored in unrestrained normal and monocrotaline-treated rats for 1 hr prior to, during, and 24 hrs after, single or multiple exposures to PM. No consistent changes in heart rate or core temperature were observed after exposure to concentrated ambient PM. Pulmonary injury, as evidenced by increased protein levels in lavage fluid, occurred in monocrotaline-treated but not in normal animals exposed to greater than 360 ?g/m3 PM. The observed pattern of hematological changes suggests an activation of the sympathetic stress response which appeared to manifest pulmonary injury only in animals with compromised health

Monitoring fishery resources affected by contaminant discharges can include two distinct components: (1) monitoring contaminant exposure (e.g., residues in fish tissues), and (2) monitoring biological effects. Although exposure monitoring may be appropriate for evaluating the efficacy of ecological restoration programs, effects monitoring is an equally important and often overlooked aspect of monitoring programs. Advantages of monitoring effects indices include (1) biotic integration of diverse exposure pathways and temporal variability; (2) ability to integrate responses across multiple stressors; and (3) cost effectiveness relative to extensive chemical analyses. The objective of our work was to develop and review biomarker selection criteria including: (1) sensitivity (response time, permanence of response, degree of responsiveness); (2) specificity (specific to contaminant exposure); (3) applicability (cost-effectiveness, scientific acceptance); and (4) reproducibility (biological, methodological). Emphasis is placed on selection criteria for biomarkers associated with organochlorine, petroleum hydrocarbon, or metal exposure and effects.

Lung cell populations may be directly exposed to environmental airbone toxicants such as ozone (O3). Since pulmonary macrophages (M phi) play a pivotal role in host pulmonary immunocompetence, their function in this regard may be compromised by pollutant exposure thereby giving rise to an increased incidence of pulmonary disease. The current in vitro study was designed to provide some insight into possible mechanisms by which O3 induces decreased host pulmonary resistance against microbial pathogens. Specifically, this study investigated the impact of an acute O3 exposure upon the ability of a cultured mouse M phi cell line (WEHI-3) to interact with, and respond to, the major M phi-activating cytokine, interferon-gamma (IFN gamma). The results of this study indicate that WEHI-3 exposure to 1 ppm O3 for 4 h reduced both the binding of, and responsivity to, IFN gamma. Among the functional parameters affected by this inability to properly bind/respond to IFN gamma were: reactive oxygen intermediate production, phagocytic activity, and cellular calcium ion elevation; IFN gamma-enhanced expression of surface histocompatibility antigens was unaffected by O3 exposure. The reduced activity of any one of these critical M phi functions could provide a basis for previously-documented increases in microbial pathogen survival in the lungs, and overall compromise of host health following O3 exposure