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Biomedical subjects

J G Vos

Publications and source records attributed to J G Vos.

At least 19 recordsLinked to original sources

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

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

Abnormal thymus development and impaired function of the immune system in rats after prenatal exposure to aciclovir.

Aciclovir (synonym: acyclovir) causes abnormal thymus development in rats. After treatment on day 10 of gestation a weight reduction of the organ is obvious in 21-day-old fetuses which persists postnatally. Adult male rats exposed in utero to one or three injections of 100 mg aciclovir/kg body wt given to the dam on day 10 of pregnancy showed a reduction of the thymus weight to 333 +/- 158 mg and 276 +/- 61 mg (control: 428 +/- 92 mg; n = 10). Corresponding alterations were detectable in female offspring. Liver weight was also decreased and spleen weight (in relation to body wt) was significantly increased in the offspring after the three exposures. In a host resistance model with Trichinella spiralis the function of the immune system of rats prenatally exposed to aciclovir was examined. Six weeks postnatally 10-12 randomly selected male rat offspring of one control and two treatment groups (1 or 3 injections of 100 mg aciclovir/kg body wt on day 10 of gestation) were infected orally with 500 Trichinella spiralis muscle larvae. Before and several times after the infection blood was taken from a tail vein or obtained by decapitation for examination of the antibody titers (IgM, IgG, IgA, IgE) to antigens of T. spiralis. Six weeks after the infection the weight of relevant organs was determined and tongue preparations were used for T. spiralis muscle larvae counting. Aciclovir exposed animals showed a different immune response than control rats. IgM titers in both treatment groups were higher than in controls two weeks after the infection but not different by the end of the experiment.(ABSTRACT TRUNCATED AT 250 WORDS)

Acyclovir

Alterations in the cortical thymic epithelium of rats after in vivo exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD): an (immuno)histological study.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) induces thymic atrophy in rats. The present study was initiated to provide (immuno)histological data on the mechanism of action. Juvenile male Wistar rats were orally intubated once with 50 or 150 micrograms/kg TCDD. They were euthanized 4 or 10 days thereafter, or were allowed to stay alive until Day 20 or 26. Growth retardation occurred rapidly in all TCDD-treated animals. Lethality was demonstrated within 20-21 days after administration. At Days 4 and 10 after intubation, thymic atrophy was shown by reduction of thymic weight and cortex/medulla ratio. Staining patterns for T-cell markers in the atrophic thymuses coincided with the reduction of cortical areas. There was no evidence indicating that the effects were indirectly caused by stress. TCDD-induced thymic atrophy persisted until Day 26 after administration. Immunohistochemical analysis revealed prominent changes in the cortical thymic epithelium at the 150-micrograms/kg dose level. First, in the cortex epithelial cell aggregates were observed both at Day 4 and at Day 10 after administration. Apparently, the architecture of the epithelium had changed in these animals. Second, at 10 days after administration epithelial cells were found with the simultaneous expression of markers that in the normal uninvoluted thymus only occur either in the subcapsular/medullary area or in the cortex. This phenotype points to an unusual stage of differentiation. We conclude that TCDD exposure affects the cortical epithelium of the rat thymus at a high dose level. Apparently, it disturbs the epithelial network and interfers with the differentiation of epithelial cells.

Animals

Chemicals trophic for the thymus: risk for immunodeficiency and autoimmunity.

The thymus is considered as the privileged site of T-lymphocyte generation. The organ is extremely vulnerable to the toxic action of chemicals. The classical example is the "acute stress-induced involution" mediated by glucocorticoid steroid hormones from the adrenal cortex. Nowadays a number of substances have been identified that act in a differential way on the thymus. Examples presented are some organotin compounds acting on immature lymphoblasts in the outer cortex, glucocorticosteroids acting on small thymocytes in the cortex, 2,3,7,8-tetrachlorodibenzo-p-dioxin acting on epithelial cells in the cortex, and cyclosporin acting on dendritic cells and epithelium in the medulla. The mechanisms of toxicity include receptor binding (Ah, aryl hydrocarbon receptor; dioxin); the Ca(2+)-dependent activation of an endogenous endonuclease resulting in DNA fragmentation ("programmed cell death" or apoptosis; dioxin and glucocorticosteroids); and interference with cell proliferation (some organotin compounds). The consequences of toxicity can be a decrease in thymic output of newly-generated T-lymphocytes (i.e. generation of a new T-cell repertoire), or induction of autoimmune symptoms by the creation of unwanted repertoire. This latter phenomenon may be applicable to cyclosporin that under specified conditions can induce so-called syngeneic graft-vs-host disease. This survey presents a brief description of the function of the thymus and the various thymic cell populations involved. Thereafter the susceptibility to toxic insults and the mechanisms of toxicity are reviewed. Finally, the consequences of toxic action for the host defence system, and hence the health status, are considered.

Adrenal Cortex Hormones

Effects of the colour additive caramel colour III on the immune system: a study with human volunteers.

Administration of the colour additive Caramel Colour III to rats has been associated with decreased numbers of lymphocytes and several other changes in the immune system, as well as in immune function parameters, specifically in animals fed a diet with a relatively low vitamin B6 content. The effects are caused by the imidazole derivative 2-acetyl-4(5)-tetrahydroxybutylimidazole (THI). Caramel Colour III is commonly used in food products such as bakery products, soya-bean sauces, brown sauces, gravies, soup aromas, brown (dehydrated) soups, brown malt caramel blend for various applications, vinegars and beers, and effects in humans on dietary intake cannot be excluded. Elderly male volunteers with a marginal deficit in vitamin B6 were considered a relevant and potentially sensitive group to study possible effects of Caramel Colour III on blood lymphocyte numbers (total and within subsets) or on proliferative responses of lymphocytes to mitogenic stimulation. In addition, several other haematological parameters, as well as serum immunoglobulin levels and immunoglobulin production in vitro by pokeweed mitogen-stimulated mononuclear blood cells were studied. The results of this double-blind intervention study demonstrated that in a selected test group of apparently healthy elderly male volunteers with a biochemically marginally deficient vitamin B6 status, Caramel Colour III containing 23 (commercial sample) or 143 (research sample) ppm THI and administered at the level of the current acceptable daily intake of 200 mg/kg body weight/day for 7 days did not affect any of the factors investigated.

Administration, Oral

Reversibility of thymic atrophy induced by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and bis(tri-n-butyltin)oxide (TBTO).

We studied the reversibility of thymic atrophy induced by intubation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 10 days after a single dose of 50 micrograms/kg, or bis(tri-n-butyltin)oxide (TBTO), 4 days after a single dose of 75 mg/kg. This was done by an experimental design in which the atrophic thymus was placed in an in vivo situation in which the toxic chemical was no longer present, e.g. by transplantation of atrophic thymic lobes in untreated normal rats with connection to the vasculature of the recipient. At 20 days after the transplantation, the atrophic thymus showed the morphology and architecture of a normal uninvoluted thymus: lymphocyte counts and phenotypic expression of markers on lymphocytes, epithelium, and macrophages in the transplanted lobe did not differ from those in untreated donor rats or those in the normal uninvoluted thymus. Considering the mechanism of action of the toxic chemical, TBTO has been claimed to affect preferentially (passenger) lymphocytes in the thymus: the recovery after transplantation therefore is explained on the mere influx of newly-recruited precursor cells from the bone marrow. For TCDD a toxic action on the stationary epithelial component of the thymus has been claimed. We conclude that this epithelial damage is reversible within the 3-week period of the present experiment, with respect to both the morphology and immunologic phenotype of epithelium and other cell populations, as well as the recruitment of lymphocytes.

Animals

An enzyme-linked immunosorbent assay of anti-sheep red blood cell antibodies of the classes M, G, and A in the rat.

In order to investigate the immune system as a possible target for toxicity by chemicals, functional assays of the immune system are required. Sheep red blood cells (SRBC) are widely used as an antigen to study the immune competence of animals. Since routine toxicology includes data mainly provided with rat toxicity studies, there is a need for easy, specific, and reproducible assays of antibody responses to sheep erythrocytes in the rat. This report describes an enzyme-linked immunosorbent assay (ELISA) of anti-SRBC antibodies of the classes M, G and A in the serum of rats. Antigen preparations, prepared from ghosts of sheep erythrocytes by extraction with KCl, were used to coat the bottom of wells in 96 well microtiter plates. Serum samples from rats, that were immunized with sheep erythrocytes, were titrated on these plates, using specific polyclonal antibodies to rat immunoglobulins M and G, to which peroxidase was conjugated. Immunoglobulin A was assayed, using monoclonal anti-rat IgA antibodies, and polyclonal rat anti-mouse IgG that was conjugated with peroxidase. The results indicate that the ELISA of serum titers of IgM, G and A to sheep erythrocytes is an easy and reliable method, that can be used to detect the effects of chemicals on the immune system of the rat.

Animals

Characterization of cloned chicken anemia virus DNA that contains all elements for the infectious replication cycle.

Circular double-stranded replication intermediates were identified in low-molecular-weight DNA of cells of the avian leukemia virus-induced lymphoblastoid cell line 1104-X-5 infected with chicken anemia virus (CAV). To characterize the genome of CAV, we cloned linearized CAV DNA into the vector pIC20H. Transfection of the circularized cloned insert into chicken cell lines caused a cytopathogenic effect, which was arrested when a chicken serum with neutralizing antibodies directed against CAV was added. Chickens inoculated at 1 day of age with CAV collected from cell lines transfected with cloned CAV DNA developed clinical signs of CAV. The 2,319-bp cloned CAV DNA contained all the genetic information needed for the complete replication cycle of CAV. The CAV DNA sequence has three partially overlapping major reading frames coding for putative peptides of 51.6, 24.0, and 13.6 kDa. The CAV genome probably contains only one promoter region and only one poly(A) addition signal. Southern blot analysis using oligomers derived from the CAV DNA sequence showed that infected cells contained double- and single-stranded CAV DNAs, whereas purified virus contained only the minus strand. It is the first time that the genome of one of the three known single-stranded circular DNA viruses has been completely analyzed.

Amino Acid Sequence

Effects of ozone, hexachlorobenzene, and bis(tri-n-butyltin)oxide on natural killer activity in the rat lung.

The respiratory tract is a major route of exposure to noxious agents as well as pathogens such as viruses. Natural killer (NK) activity is an important first line of defense to virally infected cells as well as certain neoplasms; therefore, testing the effects of exposure to toxic compounds on this activity is important in understanding the immunotoxic potential of the compound. Lymphoid cell suspensions, obtained after enzymatic dispersion of rat lungs and purification over nylon wool columns, showed in vitro natural killer activity toward YAC lymphoma cells. Validation of the test with well-known NK activity stimulators such as Bacillus Calmette-Guérin (BCG), interleukin-2 (IL-2), interferon (IFN), and inhibitors like anti-asialo-GM1 (ganglio-n-tetrasylceramide) antibody confirmed the reliability of the test as an assay for detecting NK activity in rat lungs. Using this assay, we studied the effects of exposure to ozone (O3), hexachlorobenzene (HCB), and bis(tri-n-butyltin)oxide (TBTO) on NK activity in rat lung. Inhalation exposure to O3 for 7 days at 0.4 and 0.8 mg/m3 resulted in stimulation, and exposure at 1.6 mg O3/m3 resulted in suppression of NK activity. Oral exposure to HCB in concentrations of 150 and 450 mg/kg food for 6 weeks suppressed NK activity in rat lungs in a dose-related manner. This was also true for 6 weeks of oral exposure of rats to 20 and 80 mg TBTO/kg food, but to a lesser extent. In summary, we have developed and validated a method to measure the effects of (toxic) substances on NK activity in rat lung.

Animals