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Biomedical subjects

J G Vos

Publications and source records attributed to J G Vos.

At least 55 records · Page 3Linked to original sources

Differential effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin, bis(tri-n-butyltin) oxide and cyclosporine on thymus histophysiology.

Recent advances in the histophysiology of the normal thymus have revealed its complex architecture, showing distinct microenvironments at the light and electron microscopic level. The epithelium comprising the major component of the thymic stroma is not only involved in the positive selection of thymocytes, but also in their negative selection. Dendritic cells, however, are more efficient than epithelial cells in mediating negative selection. Thymocytes are dependent on the epithelium for normal development. Conversely, epithelial cells need the presence of thymocytes to maintain their integrity. The thymus rapidly responds to immunotoxic injury. Both the thymocytes and the nonlymphoid compartment of the organ can be targets of exposure. Disturbance of positive and negative thymocyte selection may have a major impact on the immunological function of the thymus. Suppression of peripheral T-cell-dependent immunity as a consequence of thymus toxicity is primarily seen after perinatal exposure when the thymus is most active. Autoimmunity may be another manifestation of chemically mediated thymus toxicity. Although the regenerative capacity of thymus structure is remarkable, it remains to be clarified whether this also applies to thymus function. In-depth mechanistic studies on chemical-induced dysfunction of the thymus have been conducted with the environmental contaminants 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and bis(tri-n-butyltin)oxide (TBTO) as well as the pharmaceutical immunosuppressant cyclosporine (CsA). Each of these compounds exerts a differential effect on the morphology of the thymus, depending on the cellular targets for toxicity. TCDD and TBTO exposure results in cortical lymphodepletion, albeit by different mechanisms. An important feature of TCDD-mediated thymus toxicity is the disruption of epithelial cells in the cortex. TBTO primarily induces cortical thymocyte cell death. In contrast CsA administration results in major alterations in the medulla, the cortex remaining largely intact. Medullary epithelial cells and dendritic cells are particularly sensitive to CsA. The differential effects of these three immunotoxicants suggest unique susceptibilities of the various cell types and regions that make up the thymus.

Animals↗

Immunohistochemical method for detecting lesions in the prostate gland of bulls treated with diethylstilbestrol-dipropionate.

Hyperplastic and metaplastic lesions in the prostate gland of bulls are used as morphological evidence for the illegal administration of oestrogens or compounds with oestrogenic activity, like stilbenes. Exogenous and endogenous androgens can suppress the effects of these drugs, resulting in suspect or negative results. The detection of epithelial changes immunohistochemically with cytokeratin antibodies appeared to facilitate the diagnosis of hyperplasia and metaplasia in the prostate. A specific and sensitive method for detecting such lesions in formalin-fixed, paraffin-embedded prostate samples has been developed with the commercially available cytokeratin monoclonal antibody 34 beta E12, and applied to bulls treated with diethylstilbestrol-dipropionate. The highly reproducible staining pattern of 34 beta E12 can be used for the detection of hyperplasia and metaplasia in the prostate glands of animals treated illegally with oestrogens.

Animals↗

Alterations of dendritic cells in the rat thymus without epithelial cell loss during cyclosporine treatment and recovery.

After cyclosporine treatment, dendritic cells disappear from the rat thymic medulla. The present study was undertaken to examine the ultrastructural alterations in the dendritic cell population during 14-day cyclosporine treatment and subsequent 6-week recovery. Four dendritic cell subtypes were defined ultrastructurally by a newly developed classification system. In addition, the potential effect of cyclosporine on six medullary epithelial cell subtypes was studied. During cyclosporine treatment, a prominent reduction of dendritic cells was seen at the ultrastructural level, whereas the total number of medullary epithelial cells remained largely unchanged. These findings were confirmed by immunohistochemistry. The number of mature dendritic cells declined later than the number of immature ones. A decrease in the antigen-processing capacity of remaining dendritic cells was suggested by the disappearance of Birbeck granules and the reduced number of tubulovesicular complexes. These findings support a disturbance of clonal deletion during cyclosporine treatment. The dendritic cell alterations appeared reversible 4 weeks after the restoration of the original architecture. During recovery, dendritic cells displaying lysosomal elements outnumbered those found in the normal uninvoluted thymus. This phenomenon probably reflects an enhanced turnover of cell organelles. No treatment-related effect on epithelial cell subtypes was seen.

Animals↗

Host resistance to rat cytomegalovirus (RCMV) and immune function in adult PVG rats fed herring from the contaminated Baltic Sea.

The immunotoxic potential of many classes of environmental contaminants has been well established in laboratory studies, with much attention being focussed on aryl hydrocarbon (Ah)-receptor binding polychlorinated biphenyl (PCB), polychlorinated dibenzo-p-dioxin (PCDD), and polychlorinated dibenzofuran (PCDF) congeners. In a semi-field study, we previously showed that harbour seals (Phoca vitulina) fed herring from the contaminated Baltic Sea had lower natural killer cell activity, T-lymphocyte functionality and delayed-type hypersensitivity responses than seals fed herring from the relatively uncontaminated Atlantic Ocean. While ethical and practical constraints preclude in-depth studies in seals, specific reagents and a wider array of immune function tests allow such studies in laboratory rats. We therefore carried out a feeding study in rats aimed at extending our observations of contaminant-induced immunosuppression in harbour seals. The same two herring batches used in the seal study were freeze-dried, supplemented and fed to female adult PVG rats for a period of 4 1/2 months. Daily contaminant intakes of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxic equivalents (TEQ) were estimated to be 0.3 ng/kg body weight and 1.6 ng/kg in the Atlantic and Baltic groups, respectively. At the end of the feeding experiment, no contaminant-related changes in spleen CD4+/CD8+ cellularity, natural killer cell activity, or mitogen-induced proliferative responses of thymus or spleen cells could be detected. However, total thymocyte numbers and thymus CD4+/CD8+ ratios were reduced in the Baltic group. A novel model was established to assess the specific T-cell response to rat cytomegalovirus (RCMV). When applied to the feeding study, no differences between the Atlantic and Baltic groups in the RCMV-induced proliferative T-lymphocyte responses could be detected, but virus titres in salivary glands of infected rats of the Baltic Sea group were higher. These elevated RCMV titres and changes in thymus cellularity suggest that the dietary exposure to low levels of contaminants may have been immunotoxic at a level which our immune function test could not otherwise detect. While the herring diet per se appeared to have an effect on several immune function parameters, lower plasma thyroid hormone levels in the Baltic Sea group of rats confirmed that exposure to the environmental mixture of contaminants led to adverse PHAH-related health effects.

Animal Feed↗

Impaired immunity in harbour seals (Phoca vitulina) exposed to bioaccumulated environmental contaminants: review of a long-term feeding study.

Mass mortalities among seals and dolphins inhabiting contaminated marine regions have led to speculation about a possible involvement of immunosuppression associated with environmental pollution. To evaluate whether contaminants at ambient environmental levels can affect immune function of seals, we carried out an immunotoxicological study under semifield conditions. Two groups of 11 harbour seals (Phoca vitulina) originating from a relatively uncontaminated area were fed herring from either the highly polluted Baltic Sea or the relatively uncontaminated Atlantic Ocean. Changes in immune function were monitored over a 2 1/2-year period. The seals that were fed contaminated Baltic herring developed significantly higher body burdens of potentially immunotoxic organochlorines and displayed impaired immune responses as demonstrated by suppression of natural killer cell activity and specific T-cell responses. During a 2-week fasting experiment performed at the end of the feeding study, mobilization of organochlorines from the blubber did not lead to a strong increase of contaminant levels in the blood, and no enhancement of the existing immunosuppression was observed. These results demonstrate that chronic exposure to environmental contaminants accumulated through the food chain affects immune function in harbour seals, whereas short-term fasting periods, which are normal for seals, do not seem to pose an additional risk. The seals of this study were not exposed perinatally to high levels of environmental chemicals, and body burdens of organochlorines measured near the end of the study were lower than those generally observed in free-ranging seals inhabiting many contaminated regions. Therefore, it may be expected that environmental contaminants adversely affect immune function of free-ranging seals inhabiting contaminated regions at least as seriously as observed in these studies.

Animal Feed↗

Impaired immunity in harbour seals [Phoca vitulina] fed environmentally contaminated herring.

In recent years, mass mortalities among seals and dolphins have been attributed to infections with different morbilliviruses. In all cases, these marine top predators were exposed to high levels of persistent lipophilic environmental contaminants accumulated through the food chain. This observation led to the hypothesis that a contaminant-related suppression of the immune system might have contributed to the severity of the virus outbreaks. We conducted a semi-field feeding experiment, in which we fed two groups of harbour seals (Phoca vitulina) fish with different levels of contaminants. During a period of 2 1/2 years, blood samples were taken at regular intervals, and the functioning of different compartments of the immune system was monitored and compared. We found impaired natural killer (NK) and specific T cell responses in the seals fed contaminated fish. This is the first demonstration of immunosuppression in mammals following chronic exposure to environmental contaminants at ambient environmental levels.

Animals↗

Immune effects of hexachlorobenzene in the rat: role of metabolism in a 13-week feeding study.

The role of metabolism and porphyria in the immunomodulating effects of hexachlorobenzene (HCB) was investigated. To this end, female Wistar rats received a diet with two different doses of HCB and pentachlorobenzene (PCB), either in combination or not with the cytochrome P450IIIA1 inhibitor, triacetyloleandomycin (TAO). Urinary metabolites and urinary and liver porphyrins were measured at regular intervals and data have been published elsewhere. Skin lesions were scored weekly and after 13 weeks of exposure lymphoid organs were weighed, spleens were examined by morphometry, and serum.(auto)antibody levels were determined by ELISA. The probability of causal relationships between the different parameters was determined by analysis of correlation. HCB caused a dose-dependent increase of the incidence, but not the severity, of skin lesions, and dose-dependently increased weights of popliteal lymph nodes and spleen and serum levels of IgM, IgA, and autoantigen-specific IgM. IgG and IgG autoantibody levels were not changed. The splenomegaly could be attributed to an expansion of all splenic compartments. PCB caused no skin lesions and had only minor, predominantly immunosuppressive effects. TAO virtually lacked immunomodulating activity of its own, hardly affected the induction of skin lesions by HCB, did not change the immune effects of HCB, and suppressed IgG levels when combined with PCB. Comparison of the immunological data with those found in the same rats as to induction of porphyria and biotransformation of HCB and PCB, indicates that the HCB-induced porphyria, being markedly reduced by coadministration of TAO, is not involved in the immunomodulating effects of HCB. The same conclusion could be drawn for the oxidative HCB metabolites, since TAO inhibited their formation, while the same metabolites were formed upon administration of PCB that lacked the immunostimulatory effects of HCB. Therefore, HCB itself, its nonoxidative metabolites, or their precursors are likely candidates for inducing the immune effects. Further, an immune component in the HCB-induced skin lesions, usually associated with dermal porphyrin accumulation, is suggested by the observations that TAO profoundly reduced induction of porphyria, but not of skin lesions and immune effects, by HCB.

Adjuvants, Immunologic↗

Toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to the human thymus after implantation in SCID mice.

There are conflicting data with regard to the sensitivity of the human immune system to the toxic action of the highly toxic environmental pollutant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). SCID mice engrafted with human fetal thymus and liver tissue fragments (SCID-hu mice), which sustain normal human T cell differentiation in the thymus graft, were used to directly assess the sensitivity of the human thymus for TCDD. Wistar rats and SCID-hu mice were exposed to 1, 5 or 25 micrograms TCDD/kg body weight. Histopathologic effects were evaluated for rat thymus and transplanted human thymus on Day 4 after exposure. The relative size of the cortex showed a dose-dependent decrease in both the normal rat thymus and grafted human thymus (significant at 25 micrograms/kg). SCID-ra mice (SCID mice with a fetal rat thymus and liver graft) were used as an intermediate model between the normal rat and SCID-hu mice, and were exposed to the same dose levels of TCDD. However, 90% of the SCID-ra mice developed a cutaneous graft-versus-host reaction, associated with lymphodepletion of the rat thymus grafts, and hence a limited number of SCID-ra mice were available for evaluation of TCDD effects. The data obtained in SCID-ra mice were in line with those in normal rat and grafted human thymus. In gas chromatography/mass spectrometry analysis, TCDD tissue concentrations in the normal rat thymus and grafted human thymus were similar. We conclude that the human thymus serves as a target for TCDD, and that the human thymus and the Wistar rat thymus display a comparable sensitivity to the toxic action of TCDD.

Animals↗

Short term fasting does not aggravate immunosuppression in harbour seals (Phoca vitulina) with high body burdens of organochlorines.

Two groups of 11 harbour seals (Phoca vitulina) with different body burdens of organochlorines were subjected to an experimental 15-day fasting period, during which they lost an average 16.5% of their body weights. Blood levels of the most persistent organochlorines showed an approximate twofold increase, while levels of aryl hydrocarbon receptor-binding organochlorines remained largely unaffected. Few differences in immunological parameters were observed between the two dietary groups. Numbers of circulating lymphocytes dropped to about 65% of the initial values and NK cell activity showed a slight increase in both groups. Mitogen- and antigen-induced lymphoproliferative responses of the Baltic group of seals remained within normal ranges. These results suggest that relatively short-term fasting periods do not present an additional immunotoxicological risk to seals with high body burdens of organochlorines.

Adipose Tissue↗

Markers for immunotoxic effects in rodents and man.

There is growing interest and concern in society about the capacity of chemicals to impair immune responses and trigger autoimmune disease. Methods to investigate chemical-induced immunosuppression have been developed and validated in the mouse and rat. Animal models that are suitable to investigate the ability of chemicals to induce autoimmune disease are virtually lacking. From the plethora of tests to assess immunity in man, panels of biomarkers to study immunotoxicity in humans have been proposed. Such studies in humans are considerably more complex than in animals as non-invasive tests are limited, responses in the population are heterogeneous, and exposure levels are often low. Human risk assessment is therefore mostly based on animal studies. As examples of compounds affecting biomarkers in animals and man, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and hexachlorobenzene are discussed.

Animals↗

Early detection of immunotoxicity: from animal studies to human biomonitoring.

This paper introduces approaches to tests for potential immunotoxicity in rodents and man and the application for evaluation of risk. Chemicals can affect the immune system. Direct effects of chemicals can result in malfunctioning of the system that can lead to decreased resistance to infections or tumors. Auto-immunity, a situation in which immune reactions to self components occur, can also be due to chemicals. Finally, chemicals can induce immune responses causing more harm to the tissue in which they take place than the chemical itself would have done. This situation is called allergy or hypersensitivity. Assessment of potential immunotoxicity can be performed in experimental animals. An array of in vivo assays of the immune system, in addition to ex vivo/in vitro assays are available to study the functional consequences of such immunotoxic effects. In particular host resistance models are valuable in this respect, since they offer endpoints that are relevant for estimation of risk to man. There is a number of examples of immunotoxic compounds. Data on direct immunotoxicity of chemicals are mainly derived from animal research, whereas detailed information in man is available only to a limited extent. The majority of such data comes from immunotherapeutic drugs, intentionally designed to influence the immune system. Environmental pollutants that are reported to have immunotoxic effects include among others dioxin and polychlorinated biphenyls oxidant gases. It is difficult at present to conclude from immunotoxic effects as they have been observed in man what their consequences are in terms of resistance to infections. Assessment of immunotoxic processes in man is difficult, as often detailed information is lacking and the immune system can only be studied to a limited extent. Although tests are available to study immune responses in man, it is often not easy to link the outcome of such assays to exposure to immunotoxicants. Few biomarkers for the immune system exist that provide specific information on the toxic activity in man and extent of exposure, or (susceptibility for) disease associated with chemical exposure.

Animals↗

Impaired cellular immune response in harbour seals (Phoca vitulina) feeding on environmentally contaminated herring.

In a 2.5-year immunotoxicological study, two groups of captive harbour seals (Phoca vitulina) were fed herring from the heavily polluted Baltic Sea or from the relatively uncontaminated Atlantic Ocean. Blood samples were collected at regular intervals, and functional immunological parameters were monitored. T cell mitogen and mixed lymphocyte-induced proliferative responses of peripheral blood mononuclear cells (PBMC) obtained from seals fed Baltic herring were significantly reduced over the course of experiment. Upon immunization with rabies virus antigen (RV) and tetanus toxoid (TT), specific proliferative responses of PBMC from the seals fed Baltic herring were also significantly reduced. Impairment of T cell-mediated immune responses became especially apparent during the second year on the respective diets, and correlated significantly to 2,3,7,8-tetrachloro-dibenzo-p-dioxin toxic equivalent levels in blubber biopsies taken from the seals after 2 years on the respective diets. Humoral immune responses, including lipopolysaccharide (LPS)-induced lymphoproliferative responses, in vitro immunoglobulin production by PBMC, as well as RV-, TT-and poliovirus-specific serum antibody responses following immunization, remained largely unaffected. We conclude that suppression of the cellular immune response in the seals fed Baltic herring was induced by the chronic exposure to immunotoxic environmental contaminants accumulated through the food chain. Since cellular immune responses are known to be of crucial importance in the clearance of morbillivirus infections, these results suggest that environmental pollution-related immunosuppression may have contributed to the severity and extent of recent morbillivirus-related mass mortalities among marine mammals.

Animals↗

Contaminant-related suppression of delayed-type hypersensitivity and antibody responses in harbor seals fed herring from the Baltic Sea.

Recent mass mortalities among several marine mammal populations have led to speculation about increased susceptibility to viral infections as a result of contaminant-induced immunosuppression. In a 2.5-year study, we fed herring from either the relatively uncontaminated Atlantic Ocean or the contaminated Baltic Sea to two groups of captive harbor seals and monitored immune function in the seals. Seals fed the contaminated fish were less able to mount a specific immunological response to ovalbumin, as measured by in vivo delayed-type hypersensitivity (DTH) reactions and antibody responses. The skin reaction to this protein antigen was characterized by the appearance of mononuclear cells which peaked at 24 hr after intradermal administration, characteristic of DTH reactions in other animals studied. These DTH responses correlated well with in vitro tests of T-lymphocyte function, implicating this cell type in the reaction. Aryl-hydrocarbon (Ah) receptor-dependent toxic equivalent (TEQ) profiles in blubber biopsies taken from the seals implicated polychlorinated biphenyls rather than dioxins or furans in the observed immunosuppression. Marine mammal populations currently inhabiting polluted coastal environments in Europe and North America may therefore have an increased susceptibility to infections, and pollution may have played a role in recent virus-induced mass mortalities.

Animals↗

Histopathology of the immune system as a tool to assess immunotoxicity.

Immunotoxicology studies the undesired effects of interactions between xenobiotics and the immune system, mainly in toxicity experiments in rodents. The histopathology of the lymphoid organs is a cornerstone in such studies. In this review we describe practical aspects of sampling lymphoid organs and subsequent tissue processing and application of conventional and advanced histologic techniques. Thereafter, some aspects of proper reading and interpretation of histopathology is discussed, in relation to modifying factors such as age, sex, strain of animals, housing conditions, and nutritional status. These factors can substantially confound the outcome and interpretation of experiments, due to the highly dynamic characteristics of the immune system. Immunotoxicity tests are normally performed in a tiered approach. We describe the screening tier in the rat species that has been developed in the National Institute of Public Health and Environmental Protection, Bilthoven, The Netherlands, and illustrate the value of histopathology by an example of immunotoxicity testing of pesticides. Subsequently, the tiered approach in the mouse species followed by the National Toxicology Program in the USA, is described. In the evaluation of chemicals with suspected immunotoxic potential using this approach, histopathology proved to be less sensitive in 'flagging' immunotoxicity. This may be related to the lower doses that are applied in this toxicity design, because at higher doses histopathology is a sensitive indicator of toxicity. A global description of pathologic alterations after toxic insult is given, followed by representative examples taken from immunosuppressive drugs--the cytostatic agent 5-fluorouracil, and drugs interfering with cytokine expression, namely, Cyclosporin A, FK-506, and Rapamycin.

Aging↗

Time course of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)-induced thymic atrophy in the Wistar rat.

Exposure to sublethal doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in Wistar rats results in thymic atrophy and reduced thymic cellularity. In a first experiment, rats were once orally intubated with 0, 1, 5, 25, 50, and 150 micrograms TCDD/kg body wt and sacrificed at Day 10. The dose that produced one-half of the maximal thymic involution was estimated at about 10-20 micrograms/kg. The time course (Days 0-21) of thymic atrophy induced by a single oral intubation of 25 micrograms TCDD/kg body wt revealed four phases. In phase 1 (initiation phase, Days 0-2) a decrease in proliferative activity was seen in cortical thymocytes, whereas no changes occurred in thymic cellularity. Phase 2 (lymphodepletion phase, Days 2-8) was characterized by an initial strong depletion of immature CD4+CD8+ double-positive (DP) cells (Day 4), followed by a more gradual decrease in the number of mature thymocytes (Day 6). On Day 8 the lymphodepletion was maximal. In phase 3 (stationary phase, Days 8-13) no changes occurred in thymic cellularity. Although the first signs of recovery were already seen on Day 6, indicated by a recovery in proliferative activity in the thymus cortex, an increase in thymic cellularity was observed first after Day 13 (phase 4, recovery phase, Day 13 onward). Reversibility of thymic atrophy is therefore observed within the estimated half-life of TCDD in the rat thymus (> 16 days). We conclude that TCDD exerts a rapidly reversible effect on an intrathymic cortical target cell population.

Administration, Oral↗

The intrathymic target cell for the thymotoxic action of 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Sublethal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) produces thymic atrophy and thymic lymphodepletion in all species investigated. Lymphodepletion is first seen in the cortex of the thymus, but also occurs in the medulla at later time points. This article surveys in vivo and in vitro studies on TCDD-induced thymus toxicity. It is concluded that the first intrathymic target cell for the action of TCDD is the cortical epithelial cell.

Animals↗

Effects of small doses of dioxins on the immune system of marmosets and rats.

There is no doubt that TCDD is capable of inducing effects on a variety of components and functions of the immune system in a variety of species. In fact, such changes seem to belong to the most sensitive variables affected by TCDD. Some of the biological effects, induced at rather high doses of TCDD exhibiting general toxicity (> 3 micrograms TCDD/kg body wt), may be considered unspecific or the result of the pronounced thymus involution. However, other effects (such as that on lymphocyte subtype patterns in marmosets or a reduced resistance of mice to influenza viruses) have been reported to occur at dose levels far from those leading to thymic involution or general toxicity. It should be remembered that the pathognomonic relevance for man of subtle modifications in the pattern of lymphocyte surface receptors is largely unknown. Until now, such deviations are considered rather as biological phenomena than indications or causes of specific diseases. Nevertheless, such changes represent clear-cut biological effects induced by TCDD. Since effects of TCDD on components and defined functions of the immune system have been revealed in several species, it would be surprising if humans were largely resistant to such effects, but reliable data in humans with high exposures to defined dioxins verified by an appropriate quantification of the exposure are scarce as of now. Data published so far have not revealed pronounced alterations of such variables. However, no studies of well-defined human populations with quantified body burdens have been performed with modern methods (such as flow cytometry) analyzing a wide variety of surface receptors. Performance of such studies is essential for a better and reliable risk assessment, and the technology is available. Some of the effects observed (such as the changes in the pattern of lymphocyte subpopulations) must certainly be considered as biological effects induced by TCDD, and the situation is similar to the induction of hepatic monooxygenases, which are also observable in this dose range. However, the relevance of such changes with respect to adverse health effects in humans is presently difficult to judge in the absence of clear-cut functional deficits demonstrated so far either in vivo or in vitro.

Animals↗