Search PubMed⌕ Search

Biomedical subjects

A L Brooks

Publications and source records attributed to A L Brooks.

At least 37 records · Page 2Linked to original sources

Effects of beryllium metal particles on the viability and function of cultured rat alveolar macrophages.

The physicochemical properties of particles influence their in vivo toxicity following deposition in the respiratory tract. To evaluate the relative contributions of mass and surface area to particle-induced toxicity, rat pulmonary alveolar macrophages (PAM) were exposed to four types of particles in vitro. We used three beryllium metal samples: relatively large (Be-II) and relatively small (Be-V) sized fractions of beryllium metal obtained from an aerosol cyclone, and a beryllium metal aerosol generated by laser vaporization of bulk beryllium metal in an argon atmosphere (Be-L). We also used glass beads (GB) as a negative control particle. End points examined included cell viability, determined by trypan blue dye exclusion, and changes in phagocytic ability, measured by counting the number of sheep red blood cells internalized by the PAM. Phagocytic ability was inhibited by exposure to beryllium particles at concentrations that did not cause appreciable cell death. Results describing effects based on the mass concentration of particles in culture medium were transformed by the amount of specific surface area of the particles to permit the expression of toxicity relative to the amount of particle surface per unit volume of culture medium. On a mass basis, the order of particle-related cytotoxicity was Be-L greater than Be-V greater than Be-II greater than GB, and for inhibition of phagocytosis, the order was Be-L approximately Be-V greater than Be-II greater than GB. When analyzed on a specific surface area basis, the cytotoxicity of the different materials became more similar in a fashion that was largely predicted by the amount of surface of the particles administered. However, because differences in specific surface area among the beryllium particle samples did not entirely predict cytotoxicity, we concluded that factors in addition to specific surface area influenced the expression of toxic effects in cultures of PAM exposed to beryllium metal.

Animals↗

Chromosome damage in rat pulmonary alveolar macrophages following ozone inhalation.

To determine whether ozone is clastogenic at environmentally relevant exposure levels, rats were exposed for 6 h to 0.0, 0.12, 0.27, or 0.80 ppm ozone. The alveolar macrophages were isolated from animals sacrificed 28 h after the end of the exposure. The mitotic index and frequency of chromosome aberrations were determined. No change in the mitotic index was detected following 0.12 ppm ozone exposure. A significant decrease in mitotic index was observed after exposure to 0.27 ppm ozone; a significant (4-fold) increase in the frequency of dividing macrophages was detected following exposure to 0.8 ppm ozone. Only chromatid-type aberrations were observed. There was a significant increase in the frequency of cells with chromatid gaps and in the frequency of cells with chromatid deletions. Animals exposed to 0.27 ppm ozone had the highest proportion of cells with chromatid deletions (0.172) relative to background level (0.028). No exchanges or chromosome-type aberrations were detected in any of the animals. These data suggest that ozone, at relatively low levels, is clastogenic in macrophages from exposed rats.

Administration, Inhalation↗

The combined effects of alpha-particles and X-rays on cell killing and micronuclei induction in lung epithelial cells.

Understanding how cellular damage produced by high-linear energy transfer (LET) radiation interacts with that produced by low-LET is important both in radiation therapy and in evaluating risk. To study such interactions, rat lung epithelial cells (LEC) were grown on Mylar films and exposed to both X-rays and alpha-particles, separately or simultaneously. Cell killing, and the numbers of binucleated cells and micronuclei, were measured as indicators of damage. X-rays and alpha-particles given separately caused dose-related increases in cell cycle time, with alpha-particles producing greater mitotic delay than X-rays. Damage from alpha-particles and X-rays given simultaneously did not interact to alter further the cell cycle. Cell survival data following exposure to X-rays and alpha-particles, combined or individually, were fitted by linear-quadratic models. Survival curves following exposure to alpha-particles only, or to 1.0 Gy alpha-particles plus graded X-ray doses, were adequately described using only the linear (alpha) term of a linear-quadratic model with alpha coefficients of 0.9 +/- 0.04 and 1.03 +/- 0.18 Gy-1, respectively. Survival following exposure to X-rays only or to 0.06 Gy alpha-particles combined with X-rays was best fitted using both alpha and beta terms of the linear-quadratic model (0.12 +/- 0.03)D + (0.007 +/- 0.002)D2 and (0.57 +/- 0.08)D + (0.3 +/- 0.02)D2, respectively. The numbers of micronuclei produced by exposure to alpha-particles or X-rays alone increased linearly with dose, with slopes of 0.48 +/- 0.07 and 0.19 +/- 0.05 micronuclei/binucleated cell per Gy for alpha and X-rays, respectively. Simultaneous exposure to graded levels of X-rays and a constant alpha dose of either 1.0 or 0.06 Gy increased micronuclei frequency, with a slope of 0.74 +/- 0.05 or 0.58 +/- 0.04 micronuclei/binucleated cell per Gy, respectively. These slopes are similar to that produced by alpha-particles alone. These studies demonstrated that both cell killing and the induction of micronuclei were increased by combined exposures compared with that predicted for separate exposures.

Alpha Particles↗

In vitro genotoxicity of dyes present in colored smoke munitions.

Genetic toxicology studies were conducted on organic dyes and mixtures used in colored smoke munitions. The dyes studied included Solvent Red 1; two different batches (Lot 1 and Lot 2) of Disperse Red 11; terephthalic acid; and a mixture of 25 parts Solvent Red 1, 5 parts Disperse Red 11, and 16 parts terephthalic acid. The dyes were evaluated for their ability to produce mutations in Salmonella bacterial strains and in Chinese hamster ovary (CHO) cells. The dyes were also tested in CHO cells to determine cytotoxicity and the induction of sister chromatid exchanges and chromosome aberration. None of the dyes were genotoxic in the standard Ames assay using bacterial strain TA1535 or TA100 with or without the addition of S-9 or in TA98 and TA1538 without S-9. With S-9, Disperse Red 11 (Lot 2) showed significant mutagenic activity in TA98 and TA1538 which increased as a function of S-9 concentration. However, the maximum level of mutagenic activity detected was low (3.8 revertants/micrograms). The azo dye Solvent Red 1 was also negative in a pre-incubation assay designed to reduce azo compounds to free amines. Solvent Red 1 was cytotoxic to mammalian cells, caused a significant increase in SCE, but was not mutagenic or clastogenic. Disperse Red 11 (Lot 1 and Lot 2) were not cytotoxic or clastogenic but produced an increase in cell cycle time and SCE frequency. Only Disperse Red 11 (Lot 2) increased mutations in the CHO/hypoxanthine-guanine phosphoribosyltransferase (HGPRT) assay. The mutagenic activity of the dye mixture was not significant, suggesting no synergistic interaction between the dyes. These studies demonstrated that none of the dyes was clastogenic and that a contaminant in Disperse Red 11 (Lot 2) may be responsible for the weak mutagenic activity in both mammalian and bacterial cell systems.

Animals↗

Cytogenetic effects of cigarette smoke on pulmonary alveolar macrophages of the rat.

To determine accurately the potential genetic damage induced by toxic inhaled agents, the cells that receive a high concentration of such agents should be analyzed. Pulmonary alveolar macrophages (PAMs) represent such cells. We compared the cytogenetic effects of cigarette smoke on PAMs of rats exposed repeatedly by different methods. This study was part of a larger investigation of the health effects resulting from different methods of exposing rats to cigarette smoke. Fischer 344/N male rats (4/group) were randomly selected from five different exposure groups: 1) nose-only sham-exposed (air) control, 2) whole-body sham-exposed control, 3) nose-only intermittent, 4) nose-only continuous, and 5) whole-body continuous. The rats were exposed 6 hr/day, 5 days/week for 22-24 days. All smoke-exposed rats received the same daily concentration x time product (600 mg.hr.m-3 for the first week, 1200 mg.hr.m-3 thereafter) of cigarette smoke. Rats were injected intraperitoneally with colchicine at the end of exposure. PAMs were obtained by lung lavage and chromosomal damage was measured. Highly significant smoke-induced differences in both structural and numerical aberrations were observed in continuously exposed rats vs. sham controls, regardless route of exposure. The structural aberrations observed were chromatid-type deletions. Both hypoploid and hyperploid cells were detected. Our data suggest that cigarette smoke is clastogenic and may disrupt spindle-fiber formation. These activities may play a role in the induction of human carcinogenesis caused by cigarette smoke exposure.

Animals↗

The induction of chromosome damage in CHO cells by beryllium and radiation given alone and in combination.

Studies were conducted to determine the effects of BeSO4 or X rays, alone and in combination, on cell cycle kinetics, cell killing, and the production of chromosome aberrations in Chinese hamster ovary (CHO) cells. The concentration of BeSO4 required to kill 50% of CHO cells exposed to BeSO4 for 20 h was determined to be 1.1 mM with 95% confidence intervals of 0.72 to 1.8 mM. During the last 2 h of the 20-h beryllium treatment (0.2 and 1.0 mM), cells were exposed to 0.0, 1.0, or 2.0 Gy of X rays. Exposure to either BeSO4 or X rays produced a change in cell cycle kinetics which resulted in an accumulation of cells in the G2/M stage of the cell cycle. However, combined exposure to both agents resulted in a block similar to that observed following exposure to X rays only. The background level of chromosome damage was 0.05 +/- 0.015 aberrations/cell in the CHO cells. Seven hours after the end of exposure to 0.2 and 1.0 mM beryllium, 0.03 +/- 0.003 and 0.09 +/- 0.02 aberrations/cell, respectively, were observed. The data for chromosome aberrations following X-ray exposure were fitted to a linear model with a coefficient of 0.14 +/- 0.01 aberrations/cell/Gy. When beryllium was combined with the X-ray exposure the interactive response was predicted by a multiplicative model and was significantly higher (P less than 0.05) than predicted by an additive model. The influence of time after radiation exposure on the interaction between beryllium and X rays was also determined. No interaction between beryllium and X-ray exposure in the induction of chromosome-type aberrations (P greater than 0.05) was detected. The frequency of chromatid-type exchanges and total aberrations was significantly higher (P less than 0.05) in the radiation plus beryllium-exposed cells when compared to cells exposed to X rays only, at both 9 and 12 h after X-ray exposure. These data suggest that the multiplicative interaction may be limited to cells in the S and G2 stages of the cell cycle.

Animals↗

The cytogenetic and hepatotoxic effects of dioxin on mouse liver cells.

The cytogenetic and hepatotoxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on mouse liver cells were investigated. Male C57BL/6J strain mice, which have TCDD receptors, were given single intraperitoneal injections of 25, 37.5, 75 and 150 micrograms of TCDD/kg body weight or corn oil carrier alone. Two-thirds hepatectomies were carried out at 1 or 7 days after injection and chromosomal aberrations and mitotic indexes of the regenerating hepatocytes were scored 54 hr after hepatectomy. Liver sections from additional intact mice were studied for TCDD-hepatotoxicity at 1, 7 and 30 days after injection. The three high doses of TCDD caused hepatotoxicity with necrosis of liver cells and focal architectural collapse by 30 days after injection. No evidence was obtained of an increase in the frequency of chromosomal structural aberrations at doses that allowed sufficient mitotic activity for cytogenetic evaluation. We conclude that TCDD is not a clastogen for mouse hepatocytes, although high doses cause marked hepatocellular necrosis.

Animals↗

Current status of cytogenetic procedures to detect and quantify previous exposures to radiation.

The estimation of the magnitude of a dose of ionizing radiation to which an individual has been exposed (or of the plausibility of an alleged exposure) from chromosomal aberration frequencies determined in peripheral blood lymphocyte cultures is a well-established methodology, having first been employed over 25 years ago. The cytogenetics working group has reviewed the accumulated data and the possible applicability of the technique to the determination of radiation doses to which American veterans might have been exposed as participants in nuclear weapons tests in the continental U.S.A. or the Pacific Atolls during the late 1940s and 1950s or as members of the Occupation Forces entering Hiroshima or Nagasaki shortly after the nuclear detonations there. The working group believes that with prompt peripheral blood sampling, external doses to individuals of the order of about 10 rad (or less if the exposure was to high-LET radiation) can accurately be detected and measured. It also believes that exposures of populations to doses of the order of maximum permissible occupational exposures can also be detected (but only in populations; not in an individual). Large exposures of populations can also be detected even several decades after their exposure, but only in the case of populations, and of large doses (of the order of 100 to several hundred rad). The working group does not believe that cytogenetic measurements can detect internal doses from fallout radionuclides in individuals unless these are very large. The working group has approached the problem of detection of small doses (less than or equal to 10 or so rad) sampled decades after the exposure of individuals by using a Bayesian statistical approach. Only a preliminary evaluation of this approach was possible, but it is clear that it could provide a formal statement of the likelihood that any given observation of a particular number of chromosomal aberrations in a sample of any particular number of lymphocytes actually indicates an exposure to any given dose of radiation. It is also clear that aberration frequencies (and consequently doses) would have to be quite high before much confidence could be given to either exposure or dose estimation by this method, given the approximately 3 decades of elapsed time between the exposures and any future blood sampling.(ABSTRACT TRUNCATED AT 400 WORDS)

Abnormalities, Radiation-Induced↗

The structure-function relationships of nitrofluorenes and nitrofluorenones in the Salmonella mutagenicity and CHO sister-chromatid exchange assays.

Nitrofluorenes and nitrofluorenones are bacterial mutagens and are detected in a variety of environmental pollution sources. We tested a series of nitrosubstituted fluorenes and fluorenones for their genotoxicity using both Salmonella bacteria and Chinese hamster ovary (CHO) cells to determine if structure-function relationships observed in bacteria for mutation induction are similar to those for mutations and SCE induction in mammalian (CHO) cells. The compounds studied were 2-nitrofluorene (2-NF), 2,7-dinitrofluorene (2,7-DNF), 3-nitrofluorenone (3-NFone), 2-nitrofluorenone (2-NFone), 2,7-dinitrofluorenone (2,7-DNFone), 2,4,7-trinitrofluorenone (2,4,7-TNFone), and 2,4,5,7-tetranitrofluorenone (2,4,5,7-TNFone). In bacteria, the presence of carbonyl group to convert mono-nitrofluorenes to nitrofluorenones and the addition of a second nitro group to either mono-nitrofluorene or fluorenone to form the dinitro compounds increased mutagenic activity in the Ames test. Location of the nitro group relative to the carbonyl group was important in enhancing mutagenic activity as 2-nitrofluorenone was more mutagenic than 3-nitrofluorenone. In CHO cells, the di-, tri- and tetra-nitrofluorenones were cytotoxic and delayed the progression of CHO cells through the cell cycle. The degree of the cytotoxicity could be decreased by the addition of S9. None of the compounds produced mutations when tested in the CHO/HGPRT mutation assay with the addition of S9. Nonetheless, the current study did show that these compounds, both with and without the activation by S9, can interact with the DNA and produce SCE in CHO cells. The addition of a carbonyl group had no influence on SCE frequency since both 2-nitrofluorene and 2-nitrofluorenone induced a similar frequency of SCE either with or without S9. Additional nitro groups, forming di-, tri- or tetra-nitrofluorenones, increased the frequency of SCE induced, especially when tested with S9 which limits cytotoxicity. The addition of a single nitro group to 2-nitrofluorenone did not change the SCE frequency but did cause a large increase in the frequency of mutations in bacteria. In contrast, 2,4,7-TNFone and 2,4,5,7-TNFone were less mutagenic than the 2,7-DNFone in bacteria but were more effective in production of SCE in CHO cells. This study illustrates that structure-function relationships are dependent on both the compounds tested and the type of genetic change induced.

Animals↗

Upper cervical instability in rheumatoid arthritis.

Upper cervical instability remains a significant problem for the patient with rheumatoid arthritis. Seventeen patients treated by upper cervical fusions for instability, were followed to determine the efficacy of our current treatment protocol. Improvement in neurologic status was observed in ten of 11 patients presenting with neurologic symptoms. In all patients with preoperative pain, improvement occurred at least one grade. However, complete amelioration of pain was noted in only five patients. A pseudarthrosis rate of 25% reflects the difficulty in achieving a solid arthrodesis in the patient with rheumatoid disease. Modification of the wedge compression technique may help ensure arthrodesis in rheumatoid patients.

Activities of Daily Living↗

A primary pulmonary sarcoma in a rhesus monkey after inhalation of plutonium dioxide.

A pulmonary fibrosarcoma of bronchial origin was discovered in a Rhesus monkey that died of pulmonary fibrosis 9 years after inhalation of plutonium-239 dioxide and with a radiation dose to lung of 1400 rad (14 Gy). It grew around the major bronchus of the right cardiac lung lobe and extended into the bronchial lumen and into surrounding pulmonary parenchyma. It also readily invaded muscular pulmonary arteries, resulting in infarction and scarring in the right cardiac lobe. Despite this aggressive growth, the tumor did not metastasize. The primary cause of death was severe pulmonary fibrosis involving the alveolar septa and and perivascular and peribronchial interstitium. Bullous or pericitrical emphysema was prominent. The initial lung burden of plutonium in this monkey was 270 nCi (10 kBq) which is equivalent to approximately 500 times the maximum permissible lung burden for man on a radioactivity per unit body weight basis. The time-dose relationship for survival is consistent with that of dogs and baboons that inhaled plutonium dioxide and died with lung tumors.

Administration, Inhalation↗

Isolation, identification and bacterial mutagenicity of 2-nitro-9-fluorenone from diesel-exhaust particle extracts.

Organic extracts of diesel-exhaust particles show direct mutagenic activity in the Salmonella typhimurium bacterial mutagenicity assay. Nitro-aromatic compounds are believed to be responsible for part of the mutagenicity. A previously unidentified polyfunctional nitro-aromatic compound, 2-nitro-9-fluorenone (2N-Fone) was isolated from diesel-exhaust particles using a two-step fractionation scheme consisting of Sephadex LH20 chromatography and silica-gel thin-layer chromatography. Positive identification was by gas chromatography/mass spectroscopy and coelution with an authentic standard. Direct and indirect mutagenicities of 2N-Fone in several bacterial strains were also determined. The results indicated that 2N-Fone produces 60-70 rev/nmole of direct mutagenic activity, and is about 1/5 to 1/10 as mutagenic as 1-nitropyrene.

Chromatography↗

Uptake and clearance of plutonium-238 from liver cells transplanted into fat pads of F344 rats.

This research is directed toward understanding the role of liver cells and the liver environment in plutonium biokinetics. Animals injected with liver cells and control animals received a single intraperitoneal injection of 37 kBq (1 microCi) 238Pu citrate and were serially sacrificed 1, 5, 10, 15, 30, 60 or 70 days later. Uptake, retention and distribution of Pu in intact liver and in liver cells growing in fat pads were determined. From these measurements, it was observed that the cells of the intact liver took up about twice as much 238Pu as liver cells transplanted into the fat pads of the same animal. The retention half-life was 8.3 days for the total activity in the liver, 20 days using tracks/cell measurements in the liver and 16 days for the tracks/cell measurements in the liver cells translocated to fat pads. When the data on tracks/cell were standardized relative to the amount of Pu present at 5 days after the injection, there was no significant difference between the retention of Pu in liver cells from intact animals and liver cells transplanted into the fat pads. About 20 per cent of the 5-day Pu liver burden in both liver cells and liver cells transplanted into fat pads was retained at 70 days. The smaller retention and clearance for liver cells in different environments indicate that uptake and clearance of Pu from the body is dependent, to a major extent, upon hepatocyte function.

Animals↗

Fractionation of diesel particle extracts by sephadex LH-20 and thin-layer chromatography.

A method was developed to concentrate fractions high in bacterial mutagenicity from diesel exhaust particle (DEP) extracts. The two-step fractionation of organic extracts of DEP employed Sephadex LH-20 followed by thin-layer chromatography (TLC). In both steps, nitro-substituted polycyclic aromatic hydrocarbons (nitro-PAHs) were found to co-elute with the fractions of highest specific bacterial mutagenic activity. Although recoveries of mass and mutagenicity from the LH-20 fractionation were high, very low (20-30%) recovery of mutagenicity was found after TLC. Recovery studies using 14C-labeled 1-nitropyrene showed that 78% of the compound was recovered unaltered through the combined fractionation. The most bioactive TLC subfraction was chromatographed using gas chromatography with thermionic specific detection. A sizeable peak was found to co-elute with a nitropyrene standard, but no peak was found co-eluting with nitrofluoranthene. Triple quadrapole mass spectrometry was used to measure the concentrations of nitropyrene in each of the fractions. Nitropyrene was enriched 160-fold in the most bioactive TLC subfraction over the starting material, for a final concentration of over 3200 micrograms g-1. Masses corresponding to several two- and three-ring methylated nitro-PAHs were found in the same fraction, including nitro-(methylbiphenyls/methylacenapthenes) and nitro-(methylanthracenes/methylphenanthrenes).

Animals↗

Early cytokinetic and morphological response of rat lungs to inhaled benzo(a)pyrene, gallium oxide, and SO2.

The purpose of this study was to determine if the early cytokinetic and morphological responses of the lung to inhaled particles and an irritant gas are altered by the presence of a carcinogen. Fischer-344 rats were exposed by nose-only inhalation to a combination of benzo(a)pyrene (B(a)P) (7 mg/m3) adsorbed onto gallium oxide particles (22 mg/m3) and SO2 (5 ppm) or to gallium oxide particles and SO2 alone for 2 h per day for 9 days. Serial sacrifices were performed up to 28 days after the beginning of the exposure. Cell proliferation in the lungs was studied in 1-micron-thick glycol methacrylate autoradiographs of tritiated thymidine-labeled tissues. Cytokinetic and morphological changes in the two groups were similar. However, there were several changes associated only with B(a)P treatment such as increased proliferation in most cell types at 8 or 11 days and foci of large proliferating cuboidal cells in the alveolar region. Cell proliferation in airway and alveolar regions of lungs in both groups increased during exposure and decreased subsequently. Small foci of hyperplastic alveolar cells and hypertrophic terminal bronchiolar cells were present in both groups although they occurred more frequently in the group that received B(a)P. These cytokinetic and morphological changes were interpreted as a repair response of the lungs to a toxic insult. Whether the differences between the two treatments were related to the carcinogenic nature of B(a)P or to the toxic nature of B(a)P will be determined in a long-term study.

Animals↗

Body composition of beef heifers at puberty.

Three trials were conducted to study age, weight, percent body fat and protein content of 131 crossbred and purebred beef heifers at puberty, to investigate relationships among various pubertal measurements and to determine if body fat and protein values could be used in combination with age, weight and shoulder height to predict the onset of puberty. Trials 1 and 2 compared heifers on treatments of high (H), medium (M) and low (L) levels of energy. The rations were formulated at 120, 100 and 80 percent of the National Research Council (NRC) recommendation for energy. The protein level was 100 percent of the NRC recommendation for all three treatments. Each animal was examined every two weeks per rectum for the presence of follicles and corpora lutea. The presence of a mature corpus luteum indicated the attainment of puberty. Trial 3 heifers were fed the same level of nutrition but ovulation data were based on weekly rectal palpations and on the presence of greater than 2.0 ng/ml blood plasma progesterone. Percentage of fat and protein were quantified in all trials using a whole body counter. In Trial 1 there was a significant difference (P<0.01) among energy levels for mean weight and percent fat values at puberty, but no differences in age at puberty. Even though heifers in Trial 2 were also fed different energy levels, there were no differences among treatments for the variables measured. The onset of puberty in Trial 2 appeared to be delayed due to cooler than normal weather during that experimental period. Heifers in Trial 2 tended to be older and reached puberty approximately one month later in the year than heifers in Trials 1 and 3, despite similarities in weight gain among the trials. In all trials, high R(2) values for multiple stepwise regression analyses indicated that body composition estimates were useful in predicting weight at puberty in beef heifers. The results of this study do not support a critical body weight or body composition hypothesis in the beef heifer. It was concluded that these data indicate environmental factors may have more effect than nutrition on the onset of puberty.

Journal Article↗