E2 interference effects in the 12C(α,γ0)16O reaction

The E1-E2 interference sign between the E(c.m.)=2.68-MeV E2 resonance and an underlying E1 strength has been measured for the first time. An E1-E2 asymmetry parameter of a=0.07±0.05 was extracted from the thick-target γ-ray yields of the narrow resonance at angles of 45° and 135°. The positive sign of a corresponded to constructive interference at forward angles and, further, allowed the interference between the resonance and an E2 background to be identified as constructive below the resonance energy. The E2-E2 interference was then used to evaluate the global S(E2) data within the vicinity of the resonance 2.5≤E(c.m.)≤3.0  MeV. An analysis of the global S(E2) data that agreed with the interference scenario has determined the E2-E2 interference scheme of the 4.34-MeV resonance and background, resulting in a value of S(E2)(300)=62(-6)(+9)  keV b.

Complex learning and information processing by pigeons: a critical analysis

THREE MODELS OF CONDITIONAL DISCRIMINATION LEARNING BY PIGEONS ARE DESCRIBED: stimulus configuration learning, the multiple-rule model, and concept learning. A review of the literature reveals that true concept learning is not characteristic of the behavior of pigeons in matching-to-sample, oddity-from-sample, or symbolic matching studies. Instead, pigeons learn a set of sample-specific S(D) rules. Transfer of the discrimination to novel stimuli, at least along the hue dimension, is predicted by a "coding hypothesis", which holds that pigeons make a unique, but usually unobserved response, R(1), to each sample, and that the comparison stimulus chosen depends on which R(1) was emitted in the presence of the sample. Convincing evidence is found that pigeons do code sample hues, but there is little evidence that allows one to infer that the "coding event" must have behavioral properties. Parameters of the conditional discrimination paradigm are identified, and it is shown that by appropriate parametric manipulation, a variety of analogous tasks may be generated for both human and animal subjects. The tasks make possible the comparative study of complex learning, attention, memory, and information processing, with the added advantage that behavior processes may be compared systematically across tasks.

Toxicity and metabolism of subcytotoxic inorganic arsenic in human renal proximal tubule epithelial cells (HK-2)

Arsenic is an environmental toxicant and a human carcinogen. The kidney, a known target organ of arsenic toxicity, is critical for both in vivo arsenic biotransformation and elimination. This study investigates the potential of an immortalized human proximal tubular epithelial cell line, HK-2, to serve as a representative model for low level exposures of the human kidney to arsenic. Subcytotoxic concentrations of arsenite (< or = 10 micromol/L) and arsenate (< 100 micromol/L) were determined by leakage of LDH from cells exposed for 24 h. Threshold concentrations of arsenite (between 1 and 10 micromol/L) and arsenate (between 10 and 25 micromol/L) were found to affect MTT processing by mitochondria. Biotransformation of subcytotoxic arsenite or arsenate was determined using HPLC-ICP-MS to detect metabolites in cell culture media and cell lysates. Following 24 h, analysis of media revealed that arsenite was minimally oxidized to arsenate and arsenate was reduced to arsenite. Only arsenite was detected in cell lysates. Pentavalent methylated arsenicals were not detected in media or lysates following exposure to either inorganic arsenical. The activities of key arsenic biotransformation enzymes--MMAV reductase and AsIII methyltransferase--were evaluated to determine whether HK-2 cells could reduce and methylate arsenicals. When compared to the activities of these enzymes in other animal tissues, the specific activities of HK-2 cells were indicative of a robust capacity to metabolize arsenic. It appears this human renal cell line is capable of biotransforming inorganic arsenic compounds, primarily reducing arsenate to arsenite. In addition, even at low concentrations, the mitochondria are a primary target for toxicity.

Evolutionary expansion of CRIB-containing Cdc42 effector proteins

Cdc42, a small GTPase, regulates actin polymerization and other signaling pathways through interaction with many different downstream effector proteins. Most of these effector proteins contain a Cdc42-binding domain, called a CRIB domain. Here, we describe the evolutionary analysis of these CRIB-containing proteins in yeast, worms, flies and humans. The number of CRIB-containing effector proteins increases from yeast to humans, involving both an increase within families and the emergence of new families. These evolutionary changes correlate with the development of the more complex signaling pathways present in higher organisms.

Communicating with terminally ill cancer patients and their families

This qualitative study aimed to investigate whether 4th year undergraduate nursing students raise concerns about communication with terminally ill and dying cancer patients and their families. It focused on factors which could influence students' feelings of insecurity/security when communicating with this group of patients and their families, factors which could influence communication, and whether students felt adequately prepared for this kind of nursing. The research involved interviewing 12 student nurses in their 4th year of their undergraduate education at a Scottish university using content analysis for analyzing the data. Five themes and 13 sub-themes emerged from this analysis. The findings revealed that communicating with terminally ill and dying cancer patients in the acute setting is difficult for student nurses and issues about death and dying tended to be ignored. While it was found that university lectures about death and dying were helpful, lack of support and guidance within the clinical setting was a major concern.

The effects of sulfur, thiol, and thiol inhibitor compounds on arsine-induced toxicity in the human erythrocyte membrane

The mechanism of arsine (AsH(3)) toxicity is not completely understood. The first cytotoxic effect of AsH(3) is disruption of ion homeostasis, with a subsequent hemolytic action. The only accepted treatment for AsH(3) toxicity is exchange transfusion of the blood. In this study the effect of sulfur, sulfur compounds, thiol-containing compounds, and thiol inhibitors on AsH(3)-induced disruption of membrane transport and hemolysis in human erythrocytes was investigated in vitro. Elemental sulfur, sodium thiosulfate, 5, 5'-dithio-bis(2-nitrobenzoic acid), and meso-2,3-dimercaptosuccinic acid were successful in delaying hemolysis, but the most successful agent was the sulfhydryl inhibitor, N-ethylmaleimide (NEM). This indicated that sulfhydryl groups, possibly membrane sulfhydryls, are major factors in the hemolytic mechanism of AsH(3). Measuring intracellular ion concentrations tested the effect of NEM on AsH(3)-induced disruption of membrane transport. AsH(3) alone caused all ions tested to flow with their concentration gradients: Intracellular K+ and Mg++ decreased, whereas Na+, Cl-, and Ca++ increased. NEM was unable to prevent ion loss except for Ca++, whose increase was prevented for 1 h after AsH(3) treatment. The influx of Ca++ in AsH(3)-treated erythrocytes is an irreversible event leading to hemolysis. Reduction of oxygenated hemoglobin to carboxyhemoglobin completely inhibited AsH(3)-induced hemolysis. In addition, AsH(3) and NEM had no direct chemical interactions. We concluded that membrane sulfhydryl groups are likely targets of AsH(3) toxicity, with NEM being able to prevent AsH(3)-induced hemolysis.

LLC-PK1 cells as a model for renal toxicity caused by arsine exposure

The mechanisms of arsine (AsH3) toxicity are not completely understood. Studies were undertaken to determine AsH3 and arsenite [As(III)] toxicity in a renal tubular epithelial cell line to model kidney dysfunction caused by AsH3 exposure. The hypothesis was that As(III) is the toxic metabolite responsible for the renal toxicity of AsH3. There was a concentration- and time-dependent toxic response after As(III) incubation. As(III) produced significant LDH leakage as early as 1 h and intracellular potassium loss at 5 h. AsH3 produced no changes in these parameters. AsH3 affected neither potassium nor LDH levels over 24 h and up to 1 mM AsH3 concentration. In this system, As(III) induced LDH leakage before K+ loss. Oxidative stress-like toxicity effects were also studied by determining levels of glutathione (GSH), glutathione disulfide (GSSG), and heat-shock protein 32 (Hsp32) levels. GSH levels were not markedly affected by any arsenical over a 6-h period or up to 100 microM concentration of the arsenical. However, 100 microM AsH3 significantly increased GSSG levels as early as 30 min and reached a maximum at 2.5 h. Incubation with 10 microM AsH3 was sufficient to significantly increase GSSG levels. As(III) had no marked effect on GSSG. Both arsenicals (50 microM) produced a slight increase (about threefold) in Hsp32 levels after 4-h incubation. These results showed that unchanged AsH3 produced oxidative stress-like toxic effects without producing cell death. However, similar As(III) concentrations induced the stress response and were toxic to the cells. These data indicated that AsH3 is not directly toxic to LLC-PK1 cells.

The evolving educational needs of nurses caring for the older adult: a literature review

Recent changes in long-term care policies in the United Kingdom have resulted in many more older patients/clients, previously nursed in long-term hospital facilities, now being cared for in the community. This change has had a significant impact on nurses, forcing many to make the transition from working in hospital to within the community. This transition calls for appropriate professional educational preparation to enable these nurses to undertake their new roles effectively. The literature search that forms the basis for this paper revealed relatively little material focusing specifically on the educational needs of such nurses in transition. However, literature that addresses the needs of nurses caring for the older individual in the acute setting, and in the community environment, was found and is explored.

Monomethylarsonous acid (MMA(III)) is more toxic than arsenite in Chang human hepatocytes

Methylation has been considered to be the primary detoxication pathway of inorganic arsenic. Inorganic arsenic is methylated by many, but not all animal species, to monomethylarsonic acid (MMA(V)), monomethylarsonous acid (MMA(III)), and dimethylarsinic acid (DMA(V)). The As(V) derivatives have been assumed to produce low toxicity, but the relative toxicity of MMA(III) remains unknown. In vitro toxicities of arsenate, arsenite, MMA(V), MMA(III), and DMA(V) were determined in Chang human hepatocytes. Leakage of lactate dehydrogenase (LDH) and intracellular potassium (K(+)) and mitochondrial metabolism of the tetrazolium salt XTT were used to assess cytotoxicity due to arsenic exposure. The mean LC50 based on LDH assays in phosphate media was 6 microM for MMA(III) and 68 microM for arsenite. Using the assay for K(+) leakage in phosphate media, the mean LC50 was 6.3 microM for MMA(III) and 19.8 microM for arsenite. The mean LC50 based on the XTT assay in phosphate media was 13.6 microM for MMA(III) and 164 microM for arsenite. The results of the three cytotoxicity assays (LDH, K(+), and XTT) reveal the following order of toxicity in Chang human hepatocytes: MMA(III) > arsenite > arsenate > MMA(V) = DMA(V). Data demonstrate that MMA(III), an intermediate in inorganic arsenic methylation, is highly toxic and again raises the question as to whether methylation of inorganic arsenic is a detoxication process.

Systemic indicators of inorganic arsenic toxicity in four animal species

The effect of arsenic compounds depends on the chemical form and is specific for certain organs. The lack of specific biological indicators for the effects of each arsenic species makes it difficult to differentiate their toxicity. Five prospective biological indicators of systemic toxicity were examined at time points ranging from 15 min to 24 h using male Sprague-Dawley rats, B6C3F1 mice, Golden-Syrian hamsters, and Hartley guinea pigs, following intraperitoneal dosing with 0.1 and 1 mg/kg sodium arsenite. Rats and mice were also dosed with 1 mg/kg sodium arsenate. Total blood arsenic levels were determined in all animal species to show that exposure occurred and as an index of the severity of the change is an indicator of toxicity. Total blood arsenic levels were increased in all animal species. This increase was dose, arsenic species, and animal dependent. Renal pyruvate dehydrogenase activity was significantly decreased at early time points in mice, hamsters, and guinea pigs, and at later time points in rats dosed with arsenite. Rats and mice dosed with arsenate also exhibited PDH decrease at early time points. Blood hematocrit and glucose were increased in the rat and guinea pig, respectively, after arsenite administration. Creatinine and urea nitrogen were found to be unresponsive to arsenic in most animal species. Data suggested that the mouse and secondly the hamster appear to be the most appropriate animal models for the study of acute arsenic toxicity.

Structural alterations in the rat kidney after acute arsine exposure

The mechanism of arsine (AsH3) toxicity is not completely understood. In this investigation, the toxicity of AsH3 and AsH3-produced hemolytic products was determined in primary culture of renal cortical epithelial cells and in the in situ isolated rat kidney. The objective of this study was to model kidney dysfunction caused by AsH3 exposure. The hypothesis was that unchanged AsH3 and AsH3-produced hemolysate that may contain arsenite (As(III)) as metabolite are both responsible for renal toxicity. Toxicity in isolated cells was determined by 2, 3-bis[2-methoxy-4-nitro-5-sulfophenyl]-2H-tetrazolium-5-carboxa nilide inner salt (XTT) bioreduction, intracellular potassium (K+), and lactate dehydrogenase (LDH) leakage. Data from XTT bioreduction showed that most toxicity occurred at 1 hour and was independent of the arsenic species. At 4 hours, the observed toxicity depended on the arsenic species and was generated by As(III). In the isolated cells, the As(III)-spiked hemolysate produced similar toxicities with regard to intracellular K and LDH. The AsH3-hemolysate only affected LDH at 1 hour. Unchanged AsH3 was very toxic to the isolated rat kidney. In this system, after 10 minutes exposure to AsH3, the effects of toxicity were observed mainly in the glomerular and peritubular endothelial cells. Tubular epithelial cells also presented early signs of toxicity. The AsH3-hemolysate was not toxic after a 1 -minute exposure. These data suggested that early cytotoxicity caused by unchanged AsH3 results in kidney dysfunction, produced by AsH3, and later by the formation of a hemolysate that may contain As(III). These data may be important in understanding the renal toxic effects after AsH3 intoxication.

Absorption and disposition of cobalt naphthenate in rats after a single oral dose

The absorption and disposition of inorganic cobalt salts after oral administration have not been completely characterized. The objective of this project was to investigate the absorption and disposition of cobalt naphthenate in Fischer 344 rats following a single oral dose. Cobalt naphthenate was given orally at 3 doses: 0.333, 3.33, or 33.3 mg Co(II)/kg. Tissues, urine, and feces were collected over a 36-h period from the low- and high-dose groups; blood was collected from all 3 dose groups. The majority of the dose in both the low- and high-dose groups was excreted in the feces (42% and 73.1%, respectively), indicating that cobalt was incompletely absorbed from the gastrointestinal tract following oral dosing. The percent of the dose excreted in the urine was similar for low and high doses (31.8% and 26.3%, respectively). Cobalt concentrations were found to be highest in the liver and kidneys. The blood versus time cobalt concentration curves for the low-dose, intermediate-dose, and high-dose groups were elevated 4- to 5-fold, 14- to 25-fold, and 25- to 60-fold over control blood levels, respectively. The peak plasma concentrations of 0.6 and 1.7 microg Co(II)/ml occurred at approximately 4.3 h for the intermediate-dose group, and 3.3 h for the high-dose group. The terminal elimination half-lives were 24.7 and 24 h for the intermediate- and high-dose groups, respectively. Thus, although the extent of cobalt absorption as indicated by the blood concentrations and areas under the blood-time curves was not proportional to dose, the calculated pharmacokinetic values for the time to peak blood concentration and the apparent elimination rate constants were independent of dose. The amount excreted in the urine was also proportional to the dose. These apparent anomalies were not related to protein binding in blood.

In vitro tissue specificity for arsine and arsenite toxicity in the rat

The mechanism of arsine (AsH3) toxicity is not completely understood. In this investigation, we determined AsH3 and arsenite (AsIII) toxicity in Sprague Dawley rat blood, liver, and kidney. In all systems, there were dose- and time-dependent responses. Red blood cells were very susceptible to AsH3 toxicity. This was demonstrated by an immediate intracellular potassium loss and by hemolysis and lactate dehydrogenase (LDH) leakage that occurred by one h. AsIII concentrations up to 1 mM were not toxic to red blood cells using these indicators. Both AsH3 and AsIII produced toxicity in primary hepatocytes. Both produced significant LDH leakage and decreases in intracellular K+ by 5 h, but AsIII was more toxic than AsH3. At 24 h, both arsenic species showed similar toxicity. In renal cortical epithelial cells, AsH3 produced no effects on LDH and K+ over a 5-h period but produced significant LDH leakage by 24 h. In these cells, AsIII produced significant toxicity as early as in 3 h. These results showed that unchanged AsH3 produced toxicity in tissues, in addition to blood, and that toxicity of arsenicals is arsenic species- and tissue-dependent.

Glutathione, albumin, cysteine, and cys-gly effects on toxicity and accumulation of mercuric chloride in LLC-PK1 cells

Speciation plays a profound if not dominant role in both transport and toxicity of Hg(II). Hg(II) has a high affinity for sulfhydryl groups. The formation constant for Hg2+ and the anionic form of a sulfhydryl group R-S- is > or =10(10) higher than that for the carboxyl or amino groups. The kidneys are the target organ for Hg(II) toxicity and the primary site of Hg(II) accumulation. Sulfhydryl groups have been implicated in both transport and nephrotoxicity; however, the role endogenous thiol compounds play in these parameters is not clear. The roles that albumin, glutathione, and the glutathione-derived complexes cysteinylglycine and L-cysteine play in toxicity and accumulation of HgCl2 were studied in LLC-PK1 cells incubated with different Hg(II):thiol ratios. In cysteine-containing medium, almost all 1:2 Hg(II):thiol complexes protected against Hg(II) toxicity up to 120 microM Hg, increased membrane-bound Hg(II), and decreased intracellular Hg(II) accumulation. In cysteine-free medium, all 1:1 Hg(II):thiol complexes were as toxic as uncomplexed Hg(II), and almost all 1:2 Hg(II):thiol complexes protected at > or =20 microM Hg, except albumin, which protected at < or =20 microM Hg. In cysteine-free but cystine-containing medium, two 1:1 Hg(II):thiol complexes were toxic at > or =80 microM Hg and two provided complete protection. All 1:2 complexes provided protection at 80-160 microM Hg. This investigation used defined media to demonstrate that mercury cytotoxicity in LLC-PK1 cells was dependent on Hg(II) concentration, the ligand, and the presence of a cysteine source for the cells. These effects were only partially explained by intracellular Hg(II) levels.

Disposition, toxicity, and intestinal absorption of cobaltous chloride in male Fischer 344 rats

The absorption and disposition of inorganic cobalt salts after oral administration have not been well characterized. The objectives of this study were to compare in vivo results with cobalt transport through the in vitro everted small intestine and to relate the disposition results to a biochemical indicator of cobalt toxicity. Cobalt chloride was given to male Fischer 344 rats orally at 33.3 mg Co(II)/kg or intravenously at 4.16 mg Co(II)/kg. By 36 h, 74.5% of the oral dose was eliminated in the feces. The liver, kidney, and heart accumulated cobalt to the greatest extent. Following the single oral dose, the blood cobalt concentration-time curve was triphasic, peaked at 3.2 h, and had an absorptive half-life of 0.9 h, an elimination phase half-life of 3.9 h, and a terminal elimination half-life of 22.9 h. Following intravenous administration, 10.1% of the dose was excreted in the feces, indicating that cobalt can be secreted in the bile. Following a single intravenous injection, the concentration-time curve displayed three segments. The first segment, which occurred during the first 4 h, had a rapid half-life of 1.3 h. The second phase, from 4 to 12 h, demonstrated a slower clearance rate with a half-life of 4.3 h. The final and slowest phase, from 12 to 36 h, had a half-life of 19 h. Intestinal jejunal ring experiments indicated that cobalt transport has both active and passive components; however, cobalt transport through the in vitro rat everted duodenum indicated that cobalt transport had almost exclusively passive components with facilitated diffusion. The finding that uptake was saturable may explain the small extent of absorption following oral dosing. Heme oxygenase studies following subcutaneous and intravenous administration resulted in an increase in activity (twofold) over controls, while oral administration did not. We concluded that the extent of cobalt absorption across the gastrointestinal tract is incomplete, and that the concentration administered and the route of exposure may determine its systemic toxicity.

The community gerontological nurse: themes from a needs analysis

With the move of care into the community, the role of nurses caring for older people is changing. However, nurses may not be adequately prepared to cope with this changing role, especially if their training and experience have been primarily hospital based. This study involves an educational needs analysis of registered nurses working in the care of older people in nursing homes and clients' own homes. It is based on focus groups with registered nurses and individual interviews with other professionals, as well as group discussions with older people. The aim of this project is to provide research-based input into the design of a new community care of older people module, to be offered at Napier University, Edinburgh from February 1998. The results presented here consist of three themes or patterns that have emerged from the interview data. The specialist/generalist theme concerns issues of role definition and gerontological specialism. The social/medical theme addresses the shift towards a social model of care when nurses move into the community settings. Finally, the physical health/mental health theme represents the need for greater integration of skills and knowledge from both mental health and general health nursing in the field of community care for older people. The results indicate the need for significant attitude changes and provide a major challenge to educationalists.

The implications of head injury for family relationships

Many of those sustaining head injury recover to the point that they no longer require hospital care. However, the family frequently has to cope with an individual with varying degrees of disability involving physical, psychological, cognitive and social dysfunctioning. This review of the literature briefly considers the possible effects that head injury may have for the injured person before going on to discuss the consequences that such an injury may have for the family of that individual. The family's need for information and education is highlighted and it is suggested that the nurse has an important role to play in this context.

Arsenate toxicity in human erythrocytes: characterization of morphologic changes and determination of the mechanism of damage

Chronic arsenic exposure is associated with alterations in peripheral circulation and vascular disease. Toxicity to the vasculature is documented, but the effect of arsenic on the erythrocyte has not been evaluated. To determine if arsenic was toxic to human erythrocytes and whether this could contribute to vascular disease, human erythrocytes were incubated in vitro with sodium arsenate, As(V), or sodium arsenite, As(III), and assessed for damage. After 5 h of incubation with 10 mM As(V) or As(III), significant cell death (hemolysis) only occurred in the As(V) treated cells. Morphologic changes were assessed by scanning electron microscopy and light microscopy. As(V) induced a classic discocyte-echinocyte transformation extending to the formation of sphero-echinocytes; these changes were concentration dependent. As(III) treatment also resulted in echinocyte formation but less extensive than in As(V) treated cells, and no sphero-echinocytes were formed. The observed damage was consistent with reported changes induced by ATP depletion, and measurement of ATP in these samples confirmed this as a mechanism of damage. As(V) treatment at concentrations as low as 0.01 mM for 5 h significantly depleted ATP, and As(III) was relatively ineffective in causing ATP depletion. Based on these three parameters, the erythrocyte was estimated to be as much as 1000 times more susceptible to As(V) than As(III). ATP is required for the cell to maintain membrane integrity and deform efficiently in circulation. The changes described here could contribute to vascular occlusion, ischemia, and tissue death associated with arsenic circulatory disorders.

Sequence of toxic events in arsine-induced hemolysis in vitro: implications for the mechanism of toxicity in human erythrocytes

Arsine, the hydride of arsenic (AsH3), is the most acutely toxic form of arsenic, causing rapid and severe hemolysis upon exposure. The mechanism of action is not known, and there are few detailed investigations of the toxicity in a controlled system. To examine arsine hemolysis and understand the importance of various toxic responses, human erythrocytes were incubated with arsine in vitro, and markers of toxicity were determined as a function of time. The earliest indicators of damage were changes in sodium and potassium levels. Within 5 min incubation with 1 mm arsine, the cells lost volume control, manifested by leakage of potassium, influx of sodium, and increases in hematocrit. Arsine did not, however, significantly alter ATP levels nor inhibit ATPases. These changes were followed by profound disturbances in membrane ultrastructure (examined by light and electron microscopy). By 10 min, significant numbers of damaged cells formed, and their numbers increased over time. These events preceded hemolysis, which was not significant until 30 min. It has been proposed that arsine interacts with hemoglobin to form toxic hemoglobin oxidation products, and this was also investigated as a potential cause of hemolysis. Essentially on contact with arsine, methemoglobin was formed but only reached 2-3% of the total cellular hemoglobin and remained unchanged for up to 90 min. There was no evidence that further oxidation products (hemin and Heinz bodies) were formed in this system. Based on these observations, hemolysis appears to be dependent on membrane disruption by a mechanism other than hemoglobin oxidation.

Reactive oxygen species do not cause arsine-induced hemoglobin damage

Previous work suggested that arsine- (AsH3-) induced hemoglobin (HbO2) damage may lead to hemolysis (Hatlelid et al., 1996). The purpose of the work presented here was to determine whether reactive oxygen species are formed by AsH3 in solution, in hemoglobin solutions, or in intact red blood cells, and, if so, to determine whether these species are responsible for the observed hemoglobin damage. Hydrogen peroxide (H2O2) was detected in aqueous solutions containing AsH3 and HbO2 or AsH3 alone but not in intact red blood cells or lysates. Additionally, high-activity catalase (19,200 U/ml) or glutathione peroxidase (68 U/ml) added to solutions of HbO2 and AsH3 had only a minor protective effect against AsH3-induced damage. Further, the differences between the visible spectra of AsH3-treated HbO2 and H2O2-treated HbO2 indicate that two different degradative processes occur. The presence of superoxide anion (O2-) was measured by O2(-)-dependent reduction of nitro blue tetrazolium (NBT). The results were negative for O2-. Exogenous superoxide dismutase (100 micrograms/ml) did not affect AsH3-induced HbO2 spectral changes, nor did the hydroxyl radical scavengers, mannitol, and DMSO (20 mM each). The general antioxidants ascorbate (< or = 10 mM) and glutathione (< or = 1 mM) also had no effect. These results indicate that the superoxide anion and the hydroxyl radical (OH) are not involved in the mechanism of AsH3-induced HbO2 damage. The results also indicate that although AsH3 contributes to H2O2 production in vitro, cellular defenses are adequate to detoxify the amount formed. An alternative mechanism by which an arsenic species is the hemolytic agent is proposed.

Environmental health and hazardous waste issues related to the U.S.-Mexico border

Environmental health and environmental quality issues along the U.S.-Mexico border have been of concern for several years. The enactment of the North American Free Trade Agreement and the presence of the maquiladoras (foreign-owned industries using imported raw materials) have intensified those concerns recently. Efforts to assess these issues are complicated by the fact that many of the issues affecting the border region are within federal jurisdiction, but the problems are regional and local in nature. Thus, state and local governments become involved with public concerns about real and potential problems. One major problem is that environmental health data from this region are lacking, particularly from Mexico. Some new agencies such as the Border Environment Cooperation Commission, the United States-Mexico Border Health Commission, and the North American Commission on Environmental Cooperation have joined several existing agencies at the federal and state level to address environmental quality and health. Several studies have been initiated to determine air and water quality, but little is being done in the areas of hazardous waste and health assessment. Several problems are anticipated in the generation of such data, such as its format and accessibility. Data gaps and research needs are discussed.

Inorganic mercury chloride-induced apoptosis in the cultured porcine renal cell line LLC-PK1

HgCl2 is known to be a renal toxin, but its mechanisms of toxicity are not well understood. The cell line LLC-PK1 was used as a model for renal proximal tubule cells, and the effects of different concentrations of HgCl2 were studied. Apoptosis in response to 35 microM HgCl2 was confirmed by observation of morphological features characteristic of apoptotic cells as well as cleavage of chromosomal DNA into fragments of multiples of 200 base pairs. Ten percent of LLC-PK1 cells in a monolayer underwent apoptosis. These cells detached from the culture flask before apoptosis. Measurement of transepithelial resistance (TER) was used as a functional assay of junctional complex integrity in a novel approach to characterize preapoptotic events in this cell line. Monolayers of LLC-PK1 cells that contained apoptotic cells showed a transient decrease in TER followed by a recovery of TER to the initial levels. The decrease in TER was accompanied by a loss of hemicysts within the monolayer. These data indicate a temporary loss of junctional complexes within the monolayer during apoptosis. One hundred micromolar HgCl2 caused all cells to become necrotic within 3 hr. HgCl2 (10 microM) caused some changes in cell morphology, but no cell death.

Reactions of arsine with hemoglobin

The mechanism of arsine (AsH3) induced hemolysis was studied in vitro using isolated red blood cells (RBCs) from the rat or dog. AsH3-induced hemolysis of dog red blood cells was completely blocked by carbon monoxide (CO) preincubation and was reduced by pure oxygen (O2) compared to incubations in air. Since CO and O2 bind to heme and also reduce hemolysis, these results suggested a reaction between AsH3 and hemoglobin in the heme-ligand binding pocket or with the heme iron. Further, sodium nitrite induction of methemoglobin (metHb) to 85% and 34% of total Hb in otherwise intact RBCs resulted in 56% and 16% decreases in hemolysis, respectively, after incubation for 4 h. This provided additional evidence for the involvement of hemoglobin in the AsH3-induced hemolysis mechanism. Reactions between AsH3 and hemoglobin were studied in solutions of purified dog hemoglobin. Spectrophotometric studies of the reaction of AsH3 with various purified hemoglobin species revealed that AsH3 reacted with HbO2 to produce metHb and, eventually, degraded Hb characterized by gross precipitation of the protein. AsH3 did not alter the spectrum of deoxyHb and did not cause degradation of metHb in oxygen, but bound to and reduced metHb in the absence of oxygen. These data indicate that a reaction of AsH3 with oxygenated hemoglobin HbO2, may lead to hemolysis, but there are reactions between AsH3 and metHb that may not be directly involved in the hemolytic process.

Interactions of rat red blood cell sulfhydryls with arsenate and arsenite

Arsenic-thiol interactions were investigated by determining changes in rat blood sulfhydryls after exposure to arsenate, As(V), or arsenite, As(III). Incubation with As(V) resulted in time- and dose-dependent depletion of nonprotein sulfhydryls (NPSH), specifically glutathione (GSH). At the highest As(V) concentration (10 mM), significant loss of glutathione was only observed after 3 h of incubation, but by 5 h 0.5 mM As(V) and higher was sufficient to deplete GSH. As(V) was reduced to As(III) at all dose levels, indicating a redox interaction with GSH, but oxidized glutathione (GSSG) was not formed in sufficient quantities to account for losses in GSH. This may be due to formation of another oxidized species such as a protein-mixed-disulfide (ProSSG). Further evidence that glutathione reduces arsenate was obtained by pretreating cells with the sulfhydryl derivatizing agent N-ethylmaleimide (NEM). Removal of thiols with NEM severely inhibited the formation of As(III) in these incubations, indicating that the main pathway for arsenate reduction in red cells is sulfhydryl dependent. As(III) demonstrated a completely different profile of sulfhydryl interaction. Sulfhydryls (NPSH and GSH) were depleted but the losses were primarily accounted for by oxidation to GSSG. As(III) was also a more potent sulfhydryl depleting agent, requiring only 0.1 mM As(III) to significantly reduce GSH after 5 h of incubation. Significant levels of GSSG formed at all doses of As(III). Evidence is presented to suggest that As(III) also formed mixed complexes with protein and glutathione. Samples that were acid precipitated displayed loss of cytosolic glutathione, which could be reversed if NEM was added prior to protein precipitation. Arsenic was detected in high quantities in the protein precipitates, and this was also found to be reversible by NEM treatment. The fact that both GSH depletion and protein binding were reversible by NEM treatment points to formation of a mixed complex of protein, GSH, and As(III), possibly ProS-As-(SG)x. Arsenic affinity chromatography and polyacrylamide gel electrophoresis were used to characterize arsenic binding proteins in red-cell cytosol. The main arsenic binding protein appeared to be hemoglobin.

An in vitro model for arsine toxicity using isolated red blood cells

A novel test system using isolated red blood cells (RBCs) and arsine (AsH3) in aqueous solution was developed to allow quantitation of AsH3 exposure and to study the toxicity of AsH3 in vitro. In this system AsH3 gas was generated and dissolved in aqueous solution, the concentration was measured, and the standardized solution was mixed with rat or dog red blood cells (RBCs). AsH3 was found to be stable in solution at neutral pH for several hours, but was lost quickly from solution as the acidity was increased to pH 2. Approximately 74% of the initial 0.56 mM AsH3, measured as total arsenic, was found to be taken up by, or strongly associated with, dog RBCs within 5 min of incubation and 82% of the initial 0.49 mM AsH3 was found in rat RBCs after 10 min incubation. Following hypotonic lysis of rat RBCs, 55% of the cell-associated arsenic was found in the membrane fraction with the balance found in the cytosolic fraction. The in vitro technique was used to examine factors influencing AsH3 toxicity using hemolysis as the end point. Hemolysis levels in dog and rat RBC incubations were found to increase with time after exhibiting a lag phase of about 30 min. At the AsH3 concentrations used, maximum levels of hemolysis were observed by 2 hr; maximum hemolysis at room temperature for dog RBCs was 20% and for rat RBCs was 22%. Increasing the temperature from room temperature to 37 degrees C resulted in increased hemolysis in dog RBCs (36%) and rat RBCs (90%).(ABSTRACT TRUNCATED AT 250 WORDS)

Oxidation-reduction reactions of metal ions

Several metal or metalloid ions exist in multiple oxidation states and can undergo electron transfer reactions that are important in biological and environmental systems. There are endogenous metal ions such as iron, copper, and cobalt that participate in oxidation-reduction reactions with species of oxygen like molecular dioxygen, superoxide, and hydrogen peroxide. These reactions may be modulated by endogenous reducing agents such as glutathione, ascorbate, and tocopherol. The reactions can be described in terms of thermodynamics through the use of standard electrode potentials. A favorable reaction will depend on the concentrations of the reactants and may depend on the pH and/or on the presence of organic ligands that form complexes with the metal or metalloid. Arsenate (As(V)) can react with glutathione in buffered aqueous solutions to produce arsenite (As(III)) and oxidized glutathione. This reaction may be important in the methylation reactions of arsenic. Arsenic species can decrease the red blood cell levels of reduced glutathione, but the products of oxidation and the mechanism of oxidation are more complex than those found in water alone. Chromium (VI) is thought to interact with DNA after first reacting with a reducing agent such as glutathione to form lower oxidation states of chromium. These examples illustrate the importance of oxidation-reduction reactions for toxic metals and metalloids.

Glutathione effects on toxicity and uptake of mercuric chloride and sodium arsenite in rabbit renal cortical slices

The mechanism of renal uptake of nephrotoxic heavy metals such as HgCl2 and NaAsO2 is not clear. The metals are known to react with endogenous sulfhydryls such as glutathione (GSH), so metal-GSH conjugates may be delivered to the kidney. To study this possibility, renal cortical slices from male New Zealand white rabbits were incubated with 10(-4) M HgCl2 or 10(-3) M NaAsO2 +/- stoichiometric amounts (1-3x) of GSH; or synthetic metal-GSH conjugates [10(-4) M Hg(SG)2 or 10(-3) M As(SG)3]. Incubations were performed at 37 degrees C in DME-F12 buffer (95/5 O2/CO2) for 8 hr. Hg(SG)2 reduced slice K+/DNA content, as an indicator of viability, significantly less than HgCl2. As(SG)3 exhibited a 2-hr delay in K+/DNA content reduction compared to NaAsO2. This delay in toxicity was not correlated to changes in uptake. Arsenic and mercury accumulation, determined by proton-induced X-ray emission, were also identical between the metal salts and the metal-GSH conjugates. Exogenous GSH decreased HgCl2 cytotoxicity and was correlated to a decrease in Hg accumulation in the slice. Exogenous GSH had limited if any protective effects against cytotoxicity by NaAsO2 and a decrease in As accumulation was not observed. Complex metal-GSH interactions appear to exist and impact on the uptake and toxicity of these metals.

Effect of arsenic exposure on alveolar macrophage function. II. Effect of slightly soluble forms of As(III) and As(V)

The pulmonary toxicity of a substance depends on a number of chemical and physical characteristics, including the solubility of the compounds. In the lung, insoluble forms of metals may be more tumorigenic than soluble forms despite the fact that this effect has not been quantitated and the mechanism of action has not been elucidated. The toxic effects of slightly soluble forms of As(III) and As(V) were evaluated by determining alteration in function of pulmonary alveolar macrophages (PAM) following in vivo and in vitro exposure. Male Sprague-Dawley rats were used throughout. Twenty-four hours following intratracheal instillation of 1 mg/kg (as arsenic) of either arsenic trisulfide (As(III)) or calcium arsenate (As(V)), PAM were lavaged and analyzed for alterations in superoxide (O2-), and tumor necrosis factor (TNF-alpha) production. There were no differences in bronchoalveolar lavage fluid TNF-alpha. PAM lavaged from As(V)-exposed animals showed significant increases in O2- production and in basal release of TNF-alpha. PAM lavaged from animals receiving As(III) did not show significant alterations. To test the direct effects of arsenic, PAM were lavaged from control animals and exposed to concentrations of 0.1 to 300 micrograms/ml arsenic in vitro for up to 24 hr. Doses used were not cytotoxic to PAM, since LDH release was not significantly increased. Significant dose-dependent inhibition of O2- production was only evident after 24 hr exposure to arsenicals. Both As(III) and As(V) produced inhibition at concentrations of 10 micrograms/ml. Suppression of LPS-induced release of TNF-alpha also occurred at similar concentrations for both arsenicals (4-5 micrograms/ml). Neither arsenical inhibited prostaglandin E2 production. Measurement of soluble arsenic concentrations indicated dissolution of the compounds could not account for all of the effects seen. Arsenic-induced alteration in PAM function may compromise host defense.

Tissue distribution and elimination of indium in male Fischer 344 rats following oral and intratracheal administration of indium phosphide

The use of indium phosphide (InP) in the semiconductor industry has raised concerns about potential occupational exposure. The tissue distribution and elimination of indium were investigated in adult male Fischer 344 rats following either a single or 14 consecutive daily oral doses, or following an intratracheal instillation of InP (10 mg/kg). The concentrations of indium ions in blood, urine, feces, and tissues were quantified either using direct acid digestion followed by electrothermal atomic absorption spectrophotometry (ET-AAS) or using an extraction method with methyltricapryl ammonium ions to remove indium from the matrix followed by ET-AAS. Indium was poorly absorbed from the gastrointestinal tract in both single and multiple oral dose studies. Upon its absorption, indium was relatively evenly distributed among the major organs such as liver, kidney, lung, spleen, and testes. By 96 h after oral dose treatment, less than 0.11% of the dose of indium was recovered from tissues in the single- or multiple-dose experiment. At 96 h, retention of indium in the body was about 0.36% of the dose (except for lung) following intratracheal instillation of InP. Following oral dose administration, the majority of indium was recovered from the gastrointestinal tract and its contents. The high recovery of indium (73% of the dose) in the feces after intratracheal instillation presumably reflects mucociliary clearance and/or biliary excretion of indium. Urinary indium accounted only for 0.08-0.23% of the dose during a 240-h collection period in both single- and multiple-dose studies. It seems that fecal excretion serves as the major route for indium elimination, and this results from poor absorption. Because of the poor absorption of indium following multiple oral doses or intratracheal instillation of InP, it seems unlikely that indium will accumulate in the body following InP exposure.

Effect of arsenic exposure on alveolar macrophage function. I. Effect of soluble as(III) and as(V)

Despite potential differences in the mechanism and potency of toxicity between the two common oxidation states of arsenic (As(III) and As(V)), assessments of the risk from inhaled arsenic generally ignore the oxidation state of inorganic arsenicals. Differences between potency and toxicity of As(III) and As(V) were evaluated by determining alteration in function of pulmonary alveolar macrophages (PAM) following in vivo and in vitro exposure to soluble arsenic. Male Sprague-Dawley rats were used throughout. One day following intratracheal instillation of 1 mg/ml (as arsenic) of either sodium arsenite (As(III)) or sodium arsenate (As(V)), PAM were lavaged and analyzed for alterations in superoxide (O2-), prostaglandin E2 (PGE2), and tumor necrosis factor (TNF-alpha) production. There were no differences in bronchoalveolar lavage fluid PGE2 or TNF-alpha. PAM lavaged from As(V)-exposed animals showed significant increases in O2- production. In vivo exposure to either oxidative form of arsenic decreased basal and lipopolysaccharide (LPS)-induced release of TNF-alpha production by PAM, but did not suppress LPS-induced production of PGE2. To test the direct effects of arsenic on PAM function, PAM were lavaged from control animals and exposed, in vitro, to either arsenical for up to 24 hr to concentrations of 0.1 to 300 micrograms/ml arsenic. Doses used were not cytotoxic to PAM, since LDH release was not significantly increased, even at the highest dose. Significant dose-dependent inhibition of O2- production was only evident after 24 hr exposure to arsenicals. As(III) was more potent than As(V), inhibiting O2- at concentrations as low as 0.1 micrograms/ml compared to 1.0 micrograms/ml of As(V). Suppression of LPS-induced release of TNF-alpha also occurred at lower concentrations of As(III), 50% inhibition at 0.15 micrograms/ml, compared to As(V), 50% inhibition at 1.8 micrograms/ml. While As(III) exposure had no affect on PGE2 production, As(V) caused inhibition of LPS-induced PGE2 production at concentrations above 1.0 micrograms/ml. Differences between As(III) and As(V) indicate that different mechanisms and/or potencies exist between the two arsenic species. Arsenic-induced alteration in PAM function may compromise host defense against infections and alter immune surveillance.

Substrate specificity of rat liver aldehyde dehydrogenase with chloroacetaldehydes

Chlorinated acetaldehydes have been the focus of research due to their role as reactive intermediates and their possible occurrence in chlorinated drinking water. This study investigated the in vitro substrate specificity of cytosolic and mitochondrial rat liver aldehyde dehydrogenase toward these compounds. Monochloroacetaldehyde was found to be extensively metabolized by these enzymes, to an even greater extent than the standard substrate propionaldehyde. Dichloroacetaldehyde was metabolized to a much lesser extent, and chloral hydrate is not metabolized by this enzyme family. The Km (mM) and Vmax (Vmax for propionaldehyde set to 100) values with the low Km cytosolic enzyme were monochloroacetaldehyde 0.046 and 582, and dichloroacetaldehyde 0.13 and 54.9, and those with the high Km cytosolic enzyme were dichloroacetaldehyde 0.35 and 23.4. The values with the low Km mitochondrial enzyme were monochloroacetaldehyde 0.057 and 462 and dichloroacetaldehyde 0.038 and 12.9, and those with the high Km mitochondrial enzyme were monocloroacetaldehyde 0.024 and 55.5 and dichloroacetaldehyde 0.29 and 3.44. These data suggest that aldehyde dehydrogenase plays a significant role in the metabolism of monochloroacetaldehyde and, to some extent, dichloroacetaldehyde. Some evidence also suggested that alcohol dehydrogenase plays a significant role in the metabolism of dichloroacetaldehyde and chloral hydrate.

Effects of acute and subchronic exposure of topically applied fullerene extracts on the mouse skin

The recent discovery that fullerenes (C60) can be produced in macroscopic quantities has sparked much interest in the chemistry of this unusual molecule. Concerns have also arisen about the potential carcinogenic effects of this molecule. We have addressed the potential acute and subchronic toxic effects of fullerenes applied in benzene on the mouse skin. The acute toxic effects measured in this study included epidermal DNA synthesis and the induction of ornithine decarboxylase activity in the epidermis. At the topical dose of fullerenes used in these studies (i.e., 200 micrograms), we found no effect on either DNA synthesis or ornithine decarboxylase activity over a 72 hour time course after treatment. The subchronic effects of the fullerenes as a mouse skin tumor promoter was assessed by repeatedly applying the chemical to the skin after initiation with the polycyclic aromatic hydrocarbon, 7,12-dimethylbenzanthracene (DMBA). Repeated administration of the fullerenes for up to 24 weeks post-initiation did not result in either benign or malignant skin tumor formation, whereas promotion with the phorbol ester, 12-O-tetradecanoyl-phorbol- 13-acetate (TPA) resulted in the formation of benign skin tumors. Our data indicate that fullerenes applied in benzene at a likely industrial exposure level do not cause acute toxic effects on the mouse skin epidermis.

Reactions of arsenic(III) and arsenic(V) species with glutathione

Arsenic is metabolized by living systems using oxidation-reduction and methylation reactions, and reduced glutathione (GSH) has been shown to be important in that metabolism. In this study, the solution reactions between GSH and arsenate, arsenite, and their methylated metabolites, monomethylarsonic acid (MMA) and dimethylarsinic acid (DMA), were characterized using 1H and 13C NMR under a nitrogen atmosphere. Binding to GSH through the thiol group was primarily followed by shifts in the carbon atom bonded to the sulfhydryl group of the cysteinyl residue, i.e., the CH2 carbon atom and the protons bonded to it. The methylated metabolites also showed shifts in the methyl groups attached to the arsenic atom after reaction with GSH. Sodium arsenite, As(III), bound to GSH to form an As(SG)3 complex in solution as indicated by NMR spectra. The identity of the complex was confirmed by FAB-MS after isolation of the compound. Mixtures of sodium arsenate, As(V), and GSH showed that arsenate oxidized GSH in D2O solutions at pH 7 to form oxidized glutathione (GSSG). When the molar ratio of As:GSH exceeded 1:2, evidence for the formation of As(SG)3 was observed. MMA and DMA are both As(V) species, and mixtures with GSH showed oxidation to GSSG initially followed by formation of CH3.As(SG)2 and (CH3)2.As.SG, respectively. The effects of GSH on arsenic metabolism may result from direct reactions between the two compounds.

Determination and metabolism of dithiol chelating agents. XII. Metabolism and pharmacokinetics of sodium 2,3-dimercaptopropane-1-sulfonate in humans

The sodium salt of 2,3-dimercaptopropane-1-sulfonic acid (DMPS) is used p.o. for the treatment of chronic lead and Hg intoxication in humans. The metabolism and pharmacokinetics of DMPS were determined after p.o. administration of 300 mg of DMPS to each of 10 normal young men. The absorbed DMPS was metabolized rapidly and extensively to a disulfide form(s). By 24 hr after DMPS administration, the area under the blood concentration-time curve of unaltered DMPS was 3.9 compared to 143 for altered DMPS. Altered DMPS is the difference between total DMPS and unaltered DMPS. Unaltered DMPS is the unbound, parent compound;, total DMPS consists of unaltered DMPS plus oxidized [disulfide] DMPS which is determined after reduction with dithiothreitol. In blood the altered form was confined to plasma. By 15 hr, only 3.7% of the administered DMPS was excreted in the urine as unaltered DMPS and 38.7% as altered DMPS. The unaltered and altered DMPS represented 9 and 91%, respectively, of the total amount of DMPS in the urine. Altered DMPS was converted to unaltered DMPS by treatment with dithiothreitol, which indicates that the altered DMPS is a disulfide(s). There was a high correlation between the urinary excretion of Hg and the urinary excretion of unaltered DMPS (r = 0.920 +/- 0.022 S.E.).

Comparisons among children's responses to the Hand Test by grade, race, sex, and social class

Four hundred sixty-four children in grades K-8 of an urban school were tested in order to develop norms, check for the presence of developmental trends, and compare the performance of different demographic groups on the Hand Test. Comparisons across grade, race, sex, and socioeconomic class indicated that separate norms for grades, but single norms for race, sex, and socioeconomic levels are appropriate for elementary school children. Discrepancies in the developmental trends raised concern about the validity of indices of psychopathology especially as they apply to children in grades K-8.

Interscorer reliability for the Hand Test administered to children

The utility of the Hand Test as a quick, reliable measure of 100 children's personalities was assessed. The interscorer reliability of the Hand Test was estimated by both intraclass correlations and the Kappa coefficient for 100 children. Following training, satisfactory intraclass correlations were obtained for the Quantitative scores (20 of 22 above .70) and Qualitative scores (12 of 27 above .70) Kappa coefficients were generally lower. Scorers' memory overload and low response frequency are discussed as possible bases for the low reliabilities of Qualitative scores. Although the Hand Test reliability for Quantitative scores is consistent with those of other projective tests, consideration should be given to the modification of the directions of administration for young children and clarification of scoring rules.

Comparison of the disposition and in vitro metabolism of 4-vinylcyclohexene in the female mouse and rat

4-Vinylcyclohexene (VCH) is a chemical to which humans are exposed in the rubber industry. A chronic carcinogenicity bioassay conducted by the National Toxicology Program showed that oral administration of VCH induced tumors in the ovaries of mice but not in those of rats. The hypothesis tested was that the species and organ specificity of VCH toxicity was due to differences in the disposition of VCH between the female rat and mouse. Therefore, the disposition of a single oral dose of 400 mg/kg [14C]VCH was studied in female B6C3F1 mice and Fischer 344 rats. Mice eliminated greater than 95% of the dose in 24 hr, whereas rats required 48 hr to eliminate greater than 95% of the dose. The major routes of excretion of [14C]VCH-derived radioactivity were in the urine (50-60%) and expired air (30-40%). No evidence was obtained to indicate that the ovaries of either species retained VCH as a parent compound or as radioactive equivalents. A dramatic difference was observed between the rat and mouse in the appearance of a monoepoxide of VCH in blood from 0.5 to 6 hr after VCH administration (800 mg/kg, ip). VCH-1,2-epoxide was present in the blood of mice with the highest concentration at 2 hr (41 nmol/ml). The blood concentration of VCH-1,2-epoxide in rats was less than 2.5 nmol/ml at all times examined. VCH-7,8-epoxide was not present in the blood of either species at the level of detection. These findings were supported by in vitro studies of VCH epoxidation by liver microsomes. The rate of epoxidation of VCH (1 mM) to VCH-1,2-epoxide was 6.5-fold greater in mouse liver microsomes than that in rat liver microsomes. The species difference in the rate of epoxide formation by the liver may be an important factor in the species difference in susceptibility to VCH-induced ovarian tumors.

Determination and metabolism of dithiol chelating agents: X. In humans, meso-2,3-dimercaptosuccinic acid is bound to plasma proteins via mixed disulfide formation

meso-2,3-Dimercaptosuccinic acid (DMSA) is orally effective for the treatment of chronic lead intoxication in humans. Earlier studies have shown that the majority of DMSA, given p.o. to normal humans, is excreted in the urine as mixed disulfides with L-cysteine. We have developed an assay for the determination of DMSA that has made possible the determination of the form of DMSA in blood and plasma. After p.o. administration of 10 mg DMSA/kg to four normal young men, no unaltered DMSA (unaltered DMSA is the unbound, parent compound; total DMSA consists of unaltered DMSA plus oxidized (disulfide) DMSA and is determined after reduction with dithiothreitol) was found in the blood over an 8-hr period. Only after treatment of blood or plasma with the disulfide-reducing agent, dithiothreitol, was DMSA detected. This indicates that DMSA is in disulfide linkage with plasma proteins and/or non-protein sulfhydryl compounds. Most of the DMSA in the plasma (92-95%) was found to be bound to plasma proteins, mainly albumin. The remaining DMSA may be bound to small molecular weight (less than 10,000 MW) nonprotein sulfhydryl compounds such as cysteine. Plasma protein appears to serve as a depot and reservoir of DMSA, which can exchange for cysteine. The urinary excretion of unaltered DMSA and DMSA mixed disulfides with L-cysteine suggests that this exchange takes place at the kidney.(ABSTRACT TRUNCATED AT 250 WORDS)

Dissolution of crystalline gallium arsenide in aqueous solutions containing complexing agents

Crystalline gallium arsenide (GaAs) was found to dissolve in an aqueous solution containing the inorganic anions, chloride, sulfate, bicarbonate, monohydrogen phosphate, and dihydrogen phosphate, and the organic anions, acetate and citrate. The aqueous solution was made up to resemble lung fluid (Gamble solution) and was maintained at a pH of 7.4. The concentrations of arsenic (As) and gallium (Ga) in solution and the As-GA ratio on the surface of the GaAs increased continuously as the time of contact with the aqueous solution increased. X-ray photoelectron spectroscopic studies of the GaAs surface, at various time intervals, showed that As migrated to the surface and was oxidized to a species resembling As2O3 and, finally, was dissolved. The zinc present in the crystalline GaAs also migrated to the surface.

Reaction of gallium arsenide with concentrated acids: formation of arsine

Crystalline particles of gallium arsenide (GaAs) (approximately 2 microns in diameter) react with concentrated hydrochloric acid (HCl) (11.6 to 9 M) to form highly toxic arsine (AsH3) gas. None of the other strong acids that were investigated reacted with gallium arsenide to form AsH3. A spectrophotometric method, based on the reaction of AsH3 with silver diethyldithiocarbamate in a chloroform solution containing morpholine, was used to detect AsH3 gas dissolved in aqueous solutions and to determine the AsH3 gas that was liberated by the reaction of GaAs with HCl. Active sites on the gallium arsenide surface initiate the reaction that forms AsH3 gas. Absorption of oxygen or ions from solution on these active sites inhibits the formation of AsH3.

Dermal absorption of phthalate diesters in rats

This study examined the extent of dermal absorption of a series of phthalate diesters in the rat. Those tested were dimethyl, diethyl, dibutyl, diisobutyl, dihexyl, di(2-ethylhexyl), diisodecyl, and benzyl butyl phthalate. Hair from a skin area (1.3 cm in diameter) on the back of male F344 rats was clipped, the [14C]phthalate diester was applied in a dose of 157 mumol/kg, and the area of application was covered with a perforated cap. The rat was restrained and housed for 7 days in a metabolic cage that allowed separate collection of urine and feces. Urine and feces were collected every 24 hr, and the amount of 14C excreted was taken as an index of the percutaneous absorption. At 24 hr, diethyl phthalate showed the greatest excretion (26%). As the length of the alkyl side chain increased, the amount of 14C excreted in the first 24 hr decreased significantly. The cumulative percentage dose excreted in 7 days was greatest for diethyl, dibutyl, and diisobutyl phthalate, about 50-60% of the applied 14C; and intermediate (20-40%) for dimethyl, benzyl butyl, and dihexyl phthalate. Urine was the major route of excretion of all phthalate diesters except for diisodecyl phthalate. This compound was poorly absorbed and showed almost no urinary excretion. After 7 days, the percentage dose for each phthalate that remained in the body was minimal and showed no specific tissue distribution. Most of the unexcreted dose remained in the area of application. These data show that the structure of the phthalate diester determines the degree of dermal absorption. Absorption maximized with diethyl phthalate and then decreased significantly as the alkyl side chain length increased.

Pharmacokinetics of 14C-etretinate in healthy volunteers and two patients with biliary T-tube drainage

The pharmacokinetic profile of 14C-etretinate, a retinoid that is effective in the treatment of psoriasis, was studied in six healthy male volunteers and two biliary T-tube patients. Following a 100 mg oral dose of 14C-etretinate (20 microcurie), etretinate and its major blood metabolites (etretin, isoetretin) were measured by HPLC and total carbon-14 was measured in blood, bile, urine, and feces by liquid scintillation counting. Etretinate was extensively metabolized in healthy volunteers and in T-tube patients. During the absorption phase, 75 per cent of the total radioactivity in the blood could be accounted for as etretinate, etretin, and isoetretin whereas these compounds accounted for only approximately 12 per cent of the blood radioactivity in T-tube patients over the same time period. The blood concentrations of etretinate, etretin, and isoetretin appeared to be substantially reduced in T-tube patients compared to those in healthy volunteers. A higher proportion of the total drug was excreted in the feces and bile of the T-tube patients (84 per cent) than in the feces of healthy volunteers (62 per cent). The major factor responsible for the observed decrease in etretinate blood concentrations following biliary cannulation appears to be the reduced absorption of etretinate due to the elimination of solubilizing bile salts in the duodenum. Carbon-14 related material was detected in urine and feces for as long as 3 weeks in healthy subjects supporting the previous observation that a long terminal elimination half-life exists for etretinate, even following a single dose of the compound.

Metabolism and excretion of gallium arsenide and arsenic oxides by hamsters following intratracheal instillation

The increasing use of gallium arsenide (GaAs) in the electronics industry has produced the need for pharmacokinetic and toxicologic data on GaAs. The disposition in male Syrian golden hamsters (n = 4) following intratracheal instillation of GaAs (mean volume diameter 5.8 micron), arsenic (III) oxide (arsenite), and arsenic (V) oxide (arsenate) at a dose of 5 mg/kg body weight was examined. Blood, kidney, liver, and lung samples were collected at 1, 2, and 4 days after administration. Excreta were collected daily. Urinary metabolite profiles were determined after separation on a mixed anion-cation-exchange column. Total As content was analyzed by direct hydride flame atomic absorption spectrophotometry after digestion. Arsenic blood levels after GaAs, arsenite, and arsenate administration were 0.185 +/- 0.041, 0.596 +/- 0.117, and 0.310 +/- 0.045 ppm, respectively, after Day 1. Arsenic blood levels after GaAs administration increased to 0.279 +/- 0.021 ppm on Day 2 indicating continued absorption while levels decreased for the arsenite and arsenate groups. At Day 1 the liver contained 0.565 +/- 0.036, 2.62 +/- 0.26, and 0.579 +/- 0.144% of the arsenic dose of GaAs, arsenite, and arsenate, respectively. The arsenite and arsenate were rapidly excreted in the urine with almost half the dose appearing after 4 days; in contrast, only about 5% of the GaAs was found at the corresponding time. Total recoveries, as arsenic equivalents, for the three compounds were between 75 and 80%. Ratios of the two major urinary metabolites (dimethylarsinic acid/total inorganic As species) were 1.41, 1.71, and 0.983 for GaAs, arsenite, and arsenate, respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

Pulmonary clearance and toxicity of respirable gallium arsenide particulates intratracheally instilled into rats

Gallium arsenide (GaAs) is an intermetallic compound that is recognized as a potential toxicological risk to workers occupationally exposed to its dust. Previous results have shown that rats intratracheally instilled with a fraction of GaAs particulates, characterized with a mean count diameter of 8.30 microns and a mean volume diameter of 12.67 microns, developed signs of systemic arsenic intoxication, pulmonary inflammation, and pneumocyte hyperplasia. The results of the present study confirm these findings and also show that a significantly smaller fraction of GaAs is a relatively more severe pneumotoxicant. Decreasing the particle mean count and mean volume diameter to 1.63 micron and 5.82 microns, respectively, increased the in vivo dissolution rate of GaAs, increased the severity of pulmonary lesions previously associated with GaAs exposure, and resulted in unique pathological sequelae in affected lung tissue. Pulmonary fibrosis, as indicated by analysis of lung 4-hydroxyproline content, was not considered statistically significant although histological examination of lung tissue revealed a mild fibrotic response. These results provide additional evidence that pulmonary exposure to respirable GaAs particulates is a potential health hazard in the semiconductor industry.