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Gregory S Ladics

Publications and source records attributed to Gregory S Ladics.

12 recordsLinked to original sources

Use of SRBC antibody responses for immunotoxicity testing.

The production of antigen-specific antibodies represents a major defense mechanism of humoral immune responses and involves the cooperation and interaction of several immune cell types: antigen presenting cells, T helper cells, and B cells. Thus, there are several cells or cell products (e.g., interleukins) that may be altered following xenobiotic exposure, making assays that evaluate the production of antigen specific antibody a relatively comprehensive and sensitive assessment of immune function. Data suggest that the primary antibody response to SRBC may be one of the most sensitive endpoints available to assess chemical-induced alterations to the immune system. As a result, this endpoint has become the cornerstone of several recently established guidelines for assessing the potential immunotoxicity of xenobiotics. Five types of antibody may be produced in a humoral immune response (i.e., IgGs of various subtypes, IgM, IgD, IgA, or IgE). For immunotoxicity assessment, the focus has primarily been on assays that assess production of IgM antibodies. Although a number of assays have been developed to evaluate antibody production, the antibody forming cell (AFC) assay and enzyme-linked immunosorbent assay (ELISA) are the two most frequently employed to evaluate the potential immunotoxicity of a xenobiotic. In this manuscript, background information, as well as the pros and cons of each of these assays are discussed and detailed methods on conducting each assay are provided.

Animals↗

Immunotoxicogenomics: the potential of genomics technology in the immunotoxicity risk assessment process.

Evaluation of xenobiotic-induced changes in gene expression as a method to identify and classify potential toxicants is being pursued by industry and regulatory agencies worldwide. A workshop was held at the Research Triangle Park campus of the Environmental Protection Agency to discuss the current state-of-the-science of "immunotoxicogenomics" and to explore the potential role of genomics techniques for immunotoxicity testing. The genesis of the workshop was the current lack of widely accepted triggering criteria for Tier 1 immunotoxicity testing in the context of routine toxicity testing data, the realization that traditional screening methods would require an inordinate number of animals and are inadequate to handle the number of chemicals that may need to be screened (e.g., high production volume compounds) and the absence of an organized effort to address the state-of-the-science of toxicogenomics in the identification of immunotoxic compounds. The major focus of the meeting was on the theoretical and practical utility of genomics techniques to (1) replace or supplement current immunotoxicity screening procedures, (2) provide insight into potential modes or mechanisms of action, and (3) provide data suitable for immunotoxicity hazard identification or risk assessment. The latter goal is of considerable interest to a variety of stakeholders as a means to reduce animal use and to decrease the cost of conducting and interpreting standard toxicity tests. A number of data gaps were identified that included a lack of dose response and kinetic data for known immunotoxic compounds and a general lack of data correlating genomic alterations to functional changes observed in vivo. Participants concluded that a genomics approach to screen chemicals for immunotoxic potential or to generate data useful to risk assessors holds promise but that routine use of these methods is years in the future. However, recent progress in molecular immunology has made mode and mechanism of action studies much more practical. Furthermore, a variety of published immunotoxicity studies suggest that microarray analysis is already a practical means to explore pathway-level changes that lead to altered immune function. To help move the science of immunotoxicogenomics forward, a partnership of industry, academia, and government was suggested to address data gaps, validation, quality assurance, and protocol development.

Animals↗

Lack of cross-reactivity between the Bacillus thuringiensis derived protein Cry1F in maize grain and dust mite Der p7 protein with human sera positive for Der p7-IgE.

Cry1F protein, derived from Bacillus thuringiensis, is effective at controlling lepidopteran pests and a synthetic Cry1F transgene was transferred into maize. For the safety assessment of genetically modified food crops, the allergenic potential of the introduced novel trait(s) is evaluated. Because no single parameter is currently predictive of allergic potential, a 'weight of evidence' approach has been proposed. As part of this assessment, the amino acid (aa) sequence of the Cry1F protein was compared to a database of known allergens using recommended criteria. The Cry1F protein did not show significant similarity or a match of eight contiguous identical aa with any allergen. However, a single six contiguous aa match was identified between Cry1F and the Der p7 protein of the dust mite, Dermatophagoides pteronyssinus. To investigate whether Cry1F was cross-reactive with Der p7, sera from 10 dust mite allergic patients containing Der p 7-specific IgE antibody were used to compare IgE-specific binding. No evidence of cross-reactivity was observed between Cry1F and Der p7. This study provides in vitro IgE sera screening data, that when considered in the context of other bioinformatic data [Hileman R.E., Silvanovich, A., Goodman R.E., Rice E.A., Holleschak G., Astwood J.D., Hefle S.L., 2002. Bioinformatic methods for allergenicity assessment using a comprehensive allergen database. Int. Arch. Allergy Immunol. 128, 280-291; Stadler, M.B., Stadler, B.M., 2003. Allergenicity prediction by protein sequence. FASEB J. 17, 1141-1143.], adds further evidence arguing against the use of a six contiguous identical amino acid search to identify potential cross-reactive allergens. Cry1F is heat labile, rapidly hydrolyzed in an in vitro pepsin resistance assay, not glycosylated and not from an allergenic source. Taken together, these data indicate a lack of allergenic concern for Cry1F.

Allergens↗

Developmental toxicology evaluations--issues with including neurotoxicology and immunotoxicology assessments in reproductive toxicology studies.

Developmental and reproductive toxicology (DART) has routinely been a part of safety assessment. Attention is now focused on the effects of chemicals on the developing nervous and immune systems. This focus on developmental neurotoxicology (DNT) and developmental immunotoxicology (DIT) is based on the premise that children differ from adults in some aspects of their biology and, thus, may also differ in their responses to chemicals. This session's objective was to discuss issues common to DNT and DIT as they relate to DART protocols, including high dose selection and maternal toxicity, adequacy of pup exposure during lactation, use of a different dosing paradigm for DART versus DNT or DIT studies, and whether DIT and DNT endpoints can be incorporated into a single DART study for hazard identification purposes. Consensus was achieved on all topics except the adequacy for risk assessment purposes of the use of a limited number of endpoints for DIT and DNT, with the DNT endpoints being the primary focus of disagreement. Panelists indicated that a combination study design for hazard identification was feasible, though flexibility to meet the scientific needs of the project was emphasized. The adequacy of existing triggers for additional developmental studies was also questioned. Panelists iterated the importance of understanding pup exposure during the various life stages and the use of toxicokinetic data in designing these studies. The group agreed to consider the HESI ACSA Life Stages Task Force recommendations as a next step to address some of the issues and challenges raised during this session.

Abnormalities, Drug-Induced↗

Acute, subchronic, and mutagenicity studies with norbornene fluoroalcohol.

The object of this study was to evaluate the toxicity of norbornene fluoroalcohol (NBFOH), which is used as an intermediate in the production of fluorinated monomers and polymers. NBFOH was evaluated for acute oral, dermal, and inhalation toxicity, dermal sensitization using the Local Lymph Node Assay (LLNA), mutagenesis by the Ames assay, and subchronic toxicity in a 4-week inhalation rat study. NBFOH demonstrated slight acute toxicity in oral, dermal, and inhalation studies. Approximate lethal doses of 3400 and > 5000 mg/kg for the oral and dermal routes, respectively, and an approximate lethal concentration of 4300 mg/m(3) were determined. NBFOH demonstrated moderate skin irritation, was a severe eye irritant, produced dermal sensitization, but did not cause bacterial mutagenicity either in the presence or absence of S9 activation. Male and female rats were exposed nose only to airborne NBFOH at levels of 0, 410, 1400, and 1500 mg/m(3), 6 h/day, 5 days/week for 4 weeks with clinical and histopathology specimens collected 1 day after the final exposure. Due to the vapor pressure of NBFOH, the 1500 mg/m(3) atmosphere was 27% aerosol and 73% vapor; the 1400 mg/m(3) atmosphere was 5% aerosol and 95% vapor, and the 410 mg/m(3) level was only vapor. No test substance-related mortality or clinical signs of toxicity were observed over the course of the study, and male rats demonstrated significant weight loss and decreased food consumption at 1400 mg/m(3). Male rats from the 1500 mg/m(3) group demonstrated an 11% increase in prothrombin time that was significantly higher than the control value. Examination of fluoride in the urine did not demonstrate a concentration-response relationship, with minimal elevations observed in male rats at all exposure levels and sporadic increases in females. Both male and female rats exposed to 1400 mg/m(3) or greater had squamous metaplasia of the laryngeal mucosa and degeneration of the nasal olfactory and respiratory mucosa. Based on the above findings, NBFOH demonstrates the potential to produce allergic contact dermatitis, and subchronic inhalation studies indicate a no-observed-adverse-effect-level (NOAEL) of 410 mg/m(3).

Animals↗

Subchronic toxicity of a fluoroalkylethanol mixture in rats.

The objective of this study was to evaluate the subchronic toxicity of a commercial fluoroalkylethanol mixture, which is an intermediate in the production of fluoroorganic compounds that are used as protectants and surfactants. The test substance was administered daily by gavage to Sprague-Dawley rats as a suspension in aqueous methylcellulose. The dosages were 0, 25, 100, or 250 mg kg(-1) day(-1). A 1- and 3-month recovery period was included to evaluate the reversibility of toxic effects. No test substance-related mortality or neurotoxicity occurred. Body weights and/or nutritional parameters were significantly reduced at 100 and 250 mg kg(-1) day(-1), and these effects were reversible. Broken and absent teeth were observed in rats dosed with 250 mg kg(-1) day(-1), and microscopic tooth lesions (ameloblast degeneration/disorganization) occurred at 100 and 250 mg kg(-1) day(-1) and persisted with decreased severity throughout recovery. Decreased red cell mass parameters occurred at 90 days in the 250 mg kg(-1) day(-1) group, but red cell counts were normal thereafter during recovery. A persistent elevation of liver weights was seen in groups given > or =100 mg kg(-l) day(-1). The increased weights correlated with microscopic hepatocellular hypertrophy only in males and females administered 250 mg kg(-1) day(-1). Hepatic beta-oxidation was increased in a dose-dependent manner and persisted through 1 month of recovery at 250 mg kg(-1) day(-1). Increased kidney weights were observed at 25 (females only), 100, and 250 mg kg(-1) day(-1). These elevated weights persisted in the high dose after recovery and correlated with microscopic tubular hypertrophy (males only). Thyroid follicular hypertrophy was present at 100 and 250 mg kg(-1) day(-1) but was not present after recovery. Total fluorine in whole blood increased with continuous dosing and achieved steady state in approximately 42 days. Both plasma and urine fluoride levels were elevated in a dose-dependent manner. Under the conditions of the study, the no-observed adverse effect level for this mixture was 25 mg kg(-1) day(-1) for subchronic toxicity.

Administration, Oral↗

Evaluation of the reproductive and developmental toxicity of a fluoroalkylethanol mixture.

The objective of these studies was to evaluate the reproductive and developmental toxicity of a commercial fluoroalkylethanol mixture, which is an intermediate in the production of fluorotelomers. The test substance was administered daily by gavage to Sprague-Dawley rats as a suspension in 0.5% aqueous methylcellulose. In a one-generation reproductive toxicity study, rats (20 per sex per group) were given dosages of 0, 25, 100, or 250 mg kg(-1) day(-1) for a period of 74 days prior to cohabitation, and during mating, gestation, and lactation. Body weights, feed consumption, clinical signs, gross pathology, sperm parameters, estrous cyclicity, and reproductive performance were evaluated for the P1 generation. The F1 offspring were.evaluated during the lactation period for growth and survival and given a gross pathology examination at weaning. A subset of the offspring were retained; body weights, feed consumption, clinical signs, and age at onset of vaginal opening and preputial separation were evaluated, and gross pathology was performed on postnatal day 60. In the developmental toxicity study, groups of time-mated Sprague-Dawley female rats were given the test substance as a suspension in 0.5% aqueous methylcellulose at daily dosages of 0, 50, 200, or 500 mg kg(-1) day(-1) by gavage on gestation days 6-20. During the in-life portion of the study, growth parameters and clinical observations were made. On gestation day 21, dams were euthanized, and the thoracic and abdominal viscera were examined. The uterine contents were removed and examined, and fetuses were evaluated for any alterations. In the reproduction study, litter size at birth, number of live pups per litter on day 0 and 4 of lactation, and pup weights during lactation were reduced in groups administered > or =100 mg kg(-1) day(-1). No other reproductive parameters were affected. There were no adverse reproductive effects observed at 25 mg kg(-1) day(-1). In the developmental toxicity study, reduced maternal body weight parameters, increased perineal fur staining, and increased fetal skeletal alterations were observed at 500 mg kg(-1) day(-1). There was no maternal or developmental toxicity at 50 or 200 mg kg(-1) day(-1). Under the conditions of the studies, the no-observed adverse effect levels for this mixture were 25 mg kg(-1) day(-1) for subchronic toxicity and reproductive parameters and 200 mg kg(-1) day(-1) for developmental toxicity end points. No functional reproductive or developmental effects were observed at dose levels that did not adversely affect adult animals.

Administration, Oral↗

A proposed testing framework for developmental immunotoxicology (DIT).

A group of thirty immunotoxicology experts from the U.S. and E.U. representing government, industry, and academia met in May 2003, in Washington, D.C., to reach consensus regarding the most appropriate methods to assess developmental immunotoxicology (DIT) for hazard identification, including under what conditions such testing might be required. The following points represent the major conclusions from this roundtable discussion: (1) the rat is the preferred model; (2) any DIT protocol should be based on immune assays already validated; (3) DIT methods should be incorporated into standard developmental and reproductive toxicity protocols to the extent possible rather than a "stand-alone" protocol; (4) the approach to address DIT potential should be similar for chemicals and drugs, but the experimental design should be flexible and should reflect the specific questions to be answered; (5) it is possible to utilize a study design that assesses all critical windows in one protocol, with the results leading to further study of specific effects, as warranted; (6) animals should be exposed throughout the treatment protocol; (7) the triggers for DIT may include structure-activity-relationships, results from other toxicity studies, the intended use of a drug/chemical and/or its anticipated exposure of neonates and/or juveniles.

Animals↗

Workshop overview: approaches to the assessment of the allergenic potential of food from genetically modified crops.

There is a need to assess the safety of foods deriving from genetically modified (GM) crops, including the allergenic potential of novel gene products. Presently, there is no single in vitro or in vivo model that has been validated for the identification or characterization of potential food allergens. Instead, the evaluation focuses on risk factors such as source of the gene (i.e., allergenic vs. nonallergenic sources), physicochemical and genetic comparisons to known allergens, and exposure assessments. The purpose of this workshop was to gather together researchers working on various strategies for assessing protein allergenicity: (1) to describe the current state of knowledge and progress that has been made in the development and evaluation of appropriate testing strategies and (2) to identify critical issues that must now be addressed. This overview begins with a consideration of the current issues involved in assessing the allergenicity of GM foods. The second section presents information on in vitro models of digestibility, bioinformatics, and risk assessment in the context of clinical prevention and management of food allergy. Data on rodent models are presented in the next two sections. Finally, nonrodent models for assessing protein allergenicity are discussed. Collectively, these studies indicate that significant progress has been made in developing testing strategies. However, further efforts are needed to evaluate and validate the sensitivity, specificity, and reproducibility of many of these assays for determining the allergenicity potential of GM foods.

Animals↗

Evaluation of a 15-day screening assay using intact male rats for identifying steroid biosynthesis inhibitors and thyroid modulators.

An in vivo screening assay using intact adult male rats has been evaluated for its ability to detect four endocrine-active compounds (EACs) via oral (gavage) administration. The test compounds included the aromatase inhibitor fadrozole (FAD), the testosterone biosynthesis inhibitor ketoconazole (KETO), and the thyroid modulators phenobarbital (PB) and propylthiouracil (PTU). Three of the test compounds (KETO, PB, and PTU) have been previously evaluated in the 15-day intact male assay with compound administration via intraperitoneal injection (ip). For the current studies, male rats were dosed for 15 days via oral gavage and euthanized on the morning of test day 15. The endpoints evaluated included final body and organ weights (liver, thyroid gland, testes, epididymides, prostate, seminal vesicles with fluid, accessory sex gland unit [ASG]), serum hormone concentrations (testosterone [T], estradiol [E2], dihydrotestosterone [DHT], luteinizing hormone [LH,] follicle stimulating hormone [FSH], prolactin [PRL], T(3), T(4), thyroid stimulating hormone [TSH]), and histopathology of the testis, epididymis, and thyroid gland; positive results for each endpoint are described below. In addition, an evaluation of immune system endpoints (humoral immune function, spleen and thymus weights, and spleen cell number) was conducted on a subset of animals dosed with either KETO or PB. FAD and KETO decreased the weights for the androgen-dependent tissues and caused similar patterns of hormonal alterations (decreased serum T and DHT; increased serum FSH and/or LH). In addition, KETO caused spermatid retention. For FAD and KETO, effects on thyroid parameters were not indicative of thyroid toxicity. PB and PTU caused thyroid effects consistent with thyroid modulators (increased thyroid weight, decreased serum T(3) and T(4), increased serum TSH, thyroid follicular cell hypertrophy/hyperplasia, and colloid depletion). In addition, PB increased relative liver weight and altered reproductive hormone concentrations (decreased serum DHT, PRL, LH; increased serum E2). Orally administered KETO and PB did not alter the primary humoral immune response to sheep red blood cells (SRBC), although spleen weights were increased at the highest doses for both compounds. In the current study, all four test substances were identified as endocrine-active. The effects that were observed in the current study via oral (gavage) compound administration were similar to the responses that were observed by the ip route in previous studies for KETO, PB, and PTU. Overall, the sensitivity (i.e., the dose required to elicit similar magnitude responses) between the ip and oral routes of administration were similar for the three EACs that were examined by both routes of administration. This article, in addition to the > 20 compounds that have already been examined using the 15-day intact male assay, supports this assay as a viable screening assay for detecting EACs, and also illustrates that the ability to identify EACs using the intact male assay will be equivalent regardless of the route of compound administration.

Androgens↗

Evaluation of a 15-day screening assay using intact male rats for identifying antiandrogens.

An in vivo screening assay using intact adult male rats has been evaluated for its ability to detect six antiandrogenic compounds via oral administration. The test compounds included cyproterone acetate (CPA), flutamide (FLUT), p,p'-DDE (DDE), di-n-butyl phthalate (DBP), linuron (LIN), and vinclozolin (VCZ). Two of the test compounds (DDE and FLUT) have been previously evaluated in the 15-day intact male assay with compound administration via intraperitoneal injection (ip). For the current studies, male rats were dosed for 15 days via oral gavage and euthanized on the morning of test day 15. The endpoints evaluated included final body and organ weights (liver, thyroid gland, testes, epididymides, prostate, seminal vesicles with fluid, accessory sex gland unit [ASG]), serum hormone concentrations (testosterone [T], estradiol [E2], dihydrotestosterone [DHT], luteinizing hormone [LH], follicle stimulating hormone [FSH], prolactin [PRL], T(3), T(4), and thyroid stimulating hormone[TSH]), and histopathology of the testis, epididymis, and thyroid gland; positive results for each endpoint are described below. In addition, an evaluation of immune system endpoints (humoral immune function, spleen and thymus weights, and spleen cell number) was conducted on a subset of animals dosed with either DDE or FLUT. All six endocrine-active compounds (EACs) increased relative liver weight. FLUT and VCZ caused the typical pattern for an androgen receptor (AR) antagonist, although not all endpoints were statistically significant for VCZ: decreased ASG weights, hormonal alterations (increased T, DHT, LH, and FSH), and induced Leydig cell hypertrophy and/or hyperplasia. CPA caused effects consistent with its mixed AR antagonist/progesterone receptor agonist activity: it decreased ASG weights, caused hormonal alterations (increased T and E2; decreased FSH), and caused spermatid retention. DBP, a compound with antiandrogen-like activity via a nonreceptor mediated mechanism, caused hormonal alterations (decreased T, DHT, and E2; increased LH, FSH, and PRL) and induced general testicular degeneration. LIN, a weak AR antagonist, decreased ASG weights, caused hormonal alterations (decreased T, DHT, and LH; increased E2), and caused spermatid retention. Unlike the other AR antagonists evaluated, DDE, a weak AR antagonist, did not alter reproductive parameters. All six antiandrogens caused some effects on thyroid parameters, although only CPA, DDE, and VCZ caused results consistent with a potential thyroid-modulator. FLUT and DDE did not alter the primary humoral immune response to SRBC, spleen or thymus weights, or spleen cell number. In the current study, 5 of the six test substances were identified as endocrine-active substances consistent with their known/proposed mechanism(s) of action. The effects that were observed in the current study via oral (gavage) compound administration were similar to the responses that were observed by the ip route in previous studies for DDE and FLUT. This report, in addition to the > 20 compounds that have already been examined using the 15-day intact male assay, supports this assay as a viable screening assay for detecting EACs, and also illustrates that the ability to identify EACs using the intact male assay will be equivalent regardless of the route of compound administration.

Androgen Antagonists↗