Inhalation toxicity of Cyclosarin (GF) vapor in rats as a function of exposure concentration and duration: potency comparison to sarin (GB)

The inhalation toxicity of cyclohexyl methylphosphonofluoridate (GF) was examined in male and female Sprague-Dawley rats exposed by whole body in a dynamic 750-L chamber. The objectives of this study were to (1) generate GF vapor in a dynamic inhalation chamber system, starting in the lethal to near-lethal concentration range, (2) examine dose-response effects of inhaled GF vapor and analyze the relationship between concentration (C) and exposure duration (T) in determining probability of lethality, and (3) establish a lethal potency ratio between GF and the more volatile agent Sarin (GB). Using a syringe pump, GF vapor concentrations were generated for exposure times of 10, 60, and 240 min. Dose-response curves with associated slopes were determined for each exposure duration by the Bliss probit method. GF vapor exposures were associated with sublethal clinical signs such as tremors, convulsions, salivation, and miosis. Concentration-exposure time values for lethality in 50% of the exposed population (LCT(50)) were calculated for 24-h and 14-day postexposure periods for 10-, 60-, and 240-min exposures. In general, LCT(50) values were lower in female rats than males and increased with exposure duration; that is, CT was not constant over time. The GF LCT(50) values for female rats were 253 mg min/m(3) at 10 min, 334 mg min/m(3) at 60 min, and 533 mg min/m(3) at 240 min, while the values for males were 371, 396, and 585 mg min/m(3), respectively. The GB LCT(50) values for female rats were 235 mg min/m(3) at 10 min, 355 mg min/m(3) at 60 min, and 840 mg min/m(3) at 240 min, while the values for males were 316, 433, and 1296 mg min/m(3), respectively. At longer exposure durations, the LCT(50) for GF was less than that found for GB but at shorter exposure durations, the LCT(50) for GF was more than that found for GB. Empirical models, consisting of the toxic load model plus higher order terms, were developed and successfully fit to the data.     

Comparison of low-level sarin and cyclosarin vapor exposure on pupil size of the Gottingen minipig: effects of exposure concentration and duration

The current studies estimated effective (miosis) concentrations of the nerve agents' sarin (GB) and cyclosarin (GF) as a function of exposure duration in the Gottingen minipig and determined dependency of the median effective dosage (ECT50) over time. Male and female Gottingen minipigs were exposed to various concentrations of vapor GB or GF for 10, 60, or 180 min. Infrared images of the pig's pupil before, during, and after nerve agent exposure were captured digitally and pupil area was quantified. An animal was classified "positive" for miosis if there was a 50% reduction in pupil area (as compared to baseline) at any time during or after the GB or GF exposure. Maximum likelihood estimation was used on the resulting quantal data to calculate ECT50 (miosis) values, with approximate 95% confidence intervals, for each of the six gender-exposure duration groups. As a group, male minipigs were significantly more sensitive to the pupil constricting effects of GF than were female minipigs. In male minipigs, GF is approximately equipotent to GB for 60-min exposures and more potent for 10- and 180-min exposures. In the female minipig GF is slightly more potent than GB for 10-min exposures but then progressively becomes less potent over the 60- and 180-min durations of exposure. The values of the toxic load exponents were essentially independent of the model fits used: 1.32 +/- 0.18 for GB exposures and 1.60 +/- 0.22 for GF exposures. Since neither of these intervals overlaps 1, Haber's rule is not an appropriate time-dependence model for these data sets.     

Interaction of exposure concentration and duration in determining acute toxic effects of sarin vapor in rats.

Sarin (GB) vapor exposure is associated with both systemic and local toxic effects occurring primarily via the inhalation and ocular routes. The objective of these studies was to develop models for predicting dose-response effects of GB vapor concentrations as a function of exposure duration. Thus, the probability of GB vapor-induced lethality was estimated in rats exposed to various combinations of exposure concentration and duration. Groups of male and female Sprague-Dawley rats were exposed to one of a series of GB vapor concentrations for a single duration (5-360 min) in a whole-body dynamic chamber. The onset of clinical signs and changes in blood cholinesterase activity were measured with each exposure. Separate effective concentrations for lethality in 50% of the exposed population (LC50) and corresponding dose-response slopes were determined for each exposure duration by the Bliss probit method. Contrary to that predicted by Haber's rule, the interaction of LC50 x time (LCT50) values increased with exposure duration (i.e., the CT for 50% lethality in the exposed population and corresponding dose-response slope was not constant over time). A plot of log (LCT50) versus log (exposure time) showed significant curvature. Predictive models derived from multifactor probit analysis of results describing the relationship between exposure conditions and probability of lethality in the rat are discussed. Overall, female rats were more sensitive to GB vapor toxicity than male rats over the range of exposure concentration and duration studied. Miosis was the initial clinical sign noted after the start of GB vapor exposure. Although blood cholinesterase activity was significantly inhibited by GB vapor exposure, poor correlation between cholinesterase inhibition and exposure conditions or cholinesterase inhibition and severity of clinical signs was noted.     

Comparison of sarin and cyclosarin toxicity by subcutaneous,intravenous and inhalation exposure in Gottingen minipigs

Abstract

Sexually mature male and female Gottingen minipigs were exposed to various concentrations of GB and GF vapor via whole-body inhalation exposures or to liquid GB or GF via intravenous or subcutaneous injections. Vapor inhalation exposures were for 10, 60 or 180?min. Maximum likelihood estimation was used to calculate the median effect levels for severe effects (ECT₅₀ and ED₅₀) and lethality (LCT₅₀ and LD₅₀). Ordinal regression was used to model the concentration?×?time profile of the agent toxicity. Contrary to that predicted by Haber’s rule, LCT₅₀ values increased as the duration of the exposures increased for both nerve agents. The toxic load exponents (n) were calculated to be 1.38 and 1.28 for GB and GF vapor exposures, respectively. LCT₅₀ values for 10-, 60- and 180-min exposures to vapor GB in male minipigs were 73, 106 and 182?mg?min/m³, respectively. LCT₅₀ values for 10-, 60?- and 180-min exposures to vapor GB in female minipigs were 87, 127 and 174?mg?min/m³, respectively. LCT₅₀ values for 10-, 60- and 180-min exposures to vapor GF in male minipigs were 218, 287 and 403?mg?min/m³, respectively. LCT₅₀ values for 10-, 60- and 180-min exposures in female minipigs were 183, 282 and 365?mg?min/m³, respectively. For GB vapor exposures, there was a tenuous gender difference which did not exist for vapor GF exposures. Surprisingly, GF was 2–3 times less potent than GB via the inhalation route of exposure regardless of exposure duration. Additionally GF was found to be less potent than GB by intravenous and subcutaneous routes.     

Comparison of Low-Level Sarin and Cyclosarin Vapor Exposure on Pupil Size of the Gottingen Minipig: Effects of Exposure Concentration and Duration

The current studies estimated effective (miosis) concentrations of the nerve agents' sarin (GB) and cyclosarin (GF) as a function of exposure duration in the Gottingen minipig and determined dependency of the median effective dosage (ECT50) over time. Male and female Gottingen minipigs were exposed to various concentrations of vapor GB or GF for 10, 60, or 180 min. Infrared images of the pig's pupil before, during, and after nerve agent exposure were captured digitally and pupil area was quantified. An animal was classified “positive” for miosis if there was a 50% reduction in pupil area (as compared to baseline) at any time during or after the GB or GF exposure. Maximum likelihood estimation was used on the resulting quantal data to calculate ECT50 (miosis) values, with approximate 95% confidence intervals, for each of the six gender–exposure duration groups. As a group, male minipigs were significantly more sensitive to the pupil constricting effects of GF than were female minipigs. In male minipigs, GF is approximately equipotent to GB for 60-min exposures and more potent for 10- and 180-min exposures. In the female minipig GF is slightly more potent than GB for 10-min exposures but then progressively becomes less potent over the 60- and 180-min durations of exposure. The values of the toxic load exponents were essentially independent of the model fits used: 1.32 ± 0.18 for GB exposures and 1.60 ± 0.22 for GF exposures. Since neither of these intervals overlaps 1, Haber's rule is not an appropriate time-dependence model for these data sets.     

GB toxicity reassessed using newer techniques for estimation of human toxicity from animal inhalation toxicity data: new method for estimating acute human toxicity (GB)

Estimated human inhalation toxicity values for Sarin (GB) were calculated using a new two independent (concentration, exposure time), one dependent (toxic response), non-linear dose response (toxicity) model combined with re-evaluated allometric equations relating to animal and human respiration. Historical animal studies of GB toxicity containing both exposure and fractional animal response data were used to test the new process. The final data set contained 6621 animals, 762 groups, 37 studies and 7 species. The toxicity of GB for each species was empirically related to exposure concentration (C; mg m(-3)) and exposure time (T; min) through the surface function Y = b0 + b1 Log10C + b2 Log10T or Y = b0 + b2 Log10C(n)T where Y is the Normit, b0, b1 and b2 are constants and n is the 'toxic load exponent' (Normit is PROBIT - 5). Between exposure times of 0.17 and 30 min, the average value for n in seven species was 1.35 +/- 0.15. The near parallel toxic load equations for each species and the linear relationship between minute volume/body weight ratio and the inhalation toxicity (LCt50) for GB were used to create a pseudo-human data set and then an exposure time/toxicity surface for the human. The calculated n for the human was 1.40. The pseudo-human data had much more variability at low exposure times. Raising the lower exposure limit to 1 min, did not change the LCt50 but did result in lower variability. Raising the lower value to 2 min was counterproductive. Based on the toxic load model for 1-30 min exposures, the human GB toxicities (LCt01, LCt05, LCt50 and LCt95) for 70 kg humans breathing 15 l min(-1) were estimated to be 11, 16, 36 and 83; 18, 25, 57 and 132 and 24, 34, 79 and 182 mg x min m(-3) for 2, 10 and 30 min exposures, respectively. These values are recommended for general use for the total human population. The empirical relationships employed in the calculations may not be valid for exposure times >30 min.     

Toxicological interactions between carbon monoxide and carbon dioxide

Fischer 344 male rats were subjected to 30-min individual or combined exposures of carbon monoxide (CO) and carbon dioxide (CO2). All deaths from CO occurred during the exposures, and the LC50 values were 4600 and 5000 ppm, depending on experimental conditions. Animals exposed to CO2 concentrations ranging from 1.3 to 14.7% for 30 min were neither incapacitated nor fatally injured. The addition of nonlethal concentrations of CO2 (1.7 to 17.3%) to sublethal concentrations of CO (2500 to 4000 ppm) caused deaths of the exposed rats both during and following (up to 24 h) the 30-min exposures. The most toxic combination of these two gases (2500 ppm CO plus 5% CO2) increased the rate of carboxyhemoglobin (COHb) formation 1.5 times that found in rats exposed to 2500 ppm of CO alone. The COHb equilibrium levels were the same. Exposure to both CO and CO2 produced a greater degree of acidosis and a longer recovery time than that observed with either single gas. The results fit a mathematical model indicating a synergistic interaction. Combustion of 11 materials at their LC50 values indicated that CO was probably the primary toxicant in one case and that the combined CO plus CO2 was the cause of the deaths in three other cases. Additional fire gases need to be studied to explain deaths from the other materials.     

Therapeutic effects of hypothermia on Lewisite toxicity

The cytotoxicity of the arsenical vesicant Lewisite was assessed in first passage cultures of proliferating neonatal human skin keratinocytes. Both munitions grade and distilled Lewisite were extremely toxic with LC(50) values in the low ng/ml range, with no significant differences between them. This similarity in toxicity was also mirrored with respect to their toxic effects on hairless guinea pig skin. Two-, 4- and 6-min vapour exposures of these agents resulted in similar and severe skin injury that was obvious by 3-5h post-exposure and almost maximal at 24h. The toxicity of Lewisite in culture was temperature dependent, with a >10-fold reduction in 24h LC(50) values as the incubation temperature was reduced from 37 to 25 degrees C. However, this cooling induced protection was not persistent. In contrast, cooling of Lewisite exposed hairless guinea pig skin at approximately 10 degrees C for as little as 30 min post-exposure resulted in dramatic and permanent protection, with 4h of cooling almost completely eliminating Lewisite induced skin injury. Further, significant protection was also evident even when cooling was delayed for as long as 2h post-Lewisite exposure. In an effort to investigate whether cooling might also increase the window in which chelation therapy against this vesicant agent would be useful, we examined the protective effects of the heavy metal chelator dimercaptosuccinic acid (DMSA). Topical application to Lewisite exposed skin was extremely protective, even when delayed for 2h after Lewisite. Cooling of Lewisite exposed skin for 2h, followed by DMSA topical application resulted in decreased skin injury compared to either treatment in isolation. It appears that the simple and non-invasive application of cooling measures may provide not only significant therapeutic relief to Lewisite exposed skin, but that it may also increase the therapeutic window in which medical countermeasures against this vesicant agent are useful.     

Use of the biotic ligand model to predict pulse-exposure toxicity of copper to fathead minnows (Pimephales promelas)

Concentrations of cationic metals (e.g., Ag, Cd, Cu, Ni, Pb, Zn) and other water quality parameters (e.g., pH, alkalinity, hardness, dissolved organic carbon (DOC) concentration) often cycle daily in surface waters, and the toxicity of the metals to aquatic organisms is altered by variations in those water quality parameters. Consequently, a method is needed to predict the LC50s (median lethal concentrations) of dissolved metals in temporally varying water quality. In this study, we combined the biotic ligand model (BLM), which predicts toxicity of cationic metals across a wide range of water quality conditions, with a one-compartment uptake-depuration (OCUD) model, which predicts toxicity of a chemical at any exposure time in either continuous or time-variable exposures, to test whether we could accurately predict pulse-exposure toxicity of Cu to fathead minnow (FHM; Pimephales promelas) larvae. First, we conducted continuous-exposure toxicity tests to calculate 1- to 96-h Cu LC50s for the FHM larvae. Then we re-parameterized the default Cu BLM for FHM until the corresponding predicted Cu LA50s (medial lethal accumulations at the biotic ligand) collapsed together into a narrow band and also fit the generalized pattern of an OCUD model [i.e., a steeply sloping plot of ln(LA50) versus ln(time) at short exposure times, followed by a gradual approach to an incipient lethal level at longer exposure times]. Next, in 72-h tests, we exposed FHM larvae to 2- or 8-h square-wave pulses of elevated Cu concentration followed by recovery in uncontaminated water for the remaining 22 or 16 h in each of three consecutive 24-h pulse-and-recovery cycles, at pH 6 or 7 in water containing either 0.5 or 2 mEq/L hardness and 0 or 20 mg DOC/L. Using the combined BLM-OCUD model developed from continuous-exposure data, we then predicted the Cu LA50s in the pulse-exposure tests and compared those LA50s to the observed pulse-exposure Cu LA50s. Although predicted pulse-exposure LA50s were within approximately 4x of the observed pulse-exposure LA50s, delayed deaths during the recovery phases of the exposures precluded more accurate predictions of pulse-exposure Cu LA50s and, as a consequence, of pulse-exposure dissolved Cu LC50s. We conclude that one global OCUD equation linked to a re-parameterized Cu BLM for FHM can be used to predict the acute toxicity of continuous and pulse exposures of Cu to FHM larvae across a range of water quality conditions; but to improve the accuracy of those predictions, a mechanism must be developed to account for delayed deaths.     

Acute inhalation toxicity of high concentrations of silane in male ICR mice

In order to examine the toxicity of silane, male ICR mice were exposed to silane for 30 min (n=8), 1 or 4 h (n=12) at concentrations of 2500, 5000, 7500 (30-min experiment only) or 10000 ppm. In the 1- and 4-h experiments, 12 mice were divided into two sub-groups: four for 2-day observation and eight for 2-week observation. The mortality was six deaths out of eight mice exposed to 10000 ppm for 4 h. No deaths occurred in any of the other experiments. In the mice sacrificed 2 days after the exposure, acute renal tubular necrosis was observed at 10000 ppm (1-h exposure) or at 2500 ppm or more (4-h exposure). Reduction in body weight, increase in relative kidney weight and blood urea nitrogen (BUN) level, and splenic atrophy and inflammatory changes of the nasal mucosa were also seen in the 10000 ppm-4 h exposure group. In the mice sacrificed 2 weeks after the exposure, tubulo-interstitial nephritis (TIN) developed at 7500 ppm or more (30-min exposure) or at 5000 ppm or more (1- and 4-h exposure). BUN increased in a dose-dependent manner, and BUN in TIN positive mice was significantly higher than that in TIN negative mice (1- and 4-h exposure). No histopathological changes were observed in the glomeruli. These results indicate that the LC₅₀ of silane in mice is between 5000 and 10000 ppm for 4-h exposure and is greater than 10000 ppm for 1-h or 30-min exposure. The target site of silane toxicity is the renal tubule, and the no-observed-effect levels of silane for acute inhalation exposure in mice are 1000 ppm for 4-h exposure (from the previous report of our research group), 2500 ppm for 1-h exposure and 5000 ppm for 30-min exposure.     

Temporal changes in respiratory dynamics in mice exposed to phosgene

One hallmark of phosgene inhalation toxicity is the latent formation of life-threatening, noncardiogenic pulmonary edema. The purpose of this study was to investigate the effect of phosgene inhalation on respiratory dynamics over 12 h. CD-1 male mice, 25-30 g, were exposed to 32 mg/m(3) (8 ppm) phosgene for 20 min (640 mg min/m(3)) followed by a 5-min air washout. A similar group of mice was exposed to room air for 25 min. After exposure, conscious mice were placed unrestrained in a whole-body plethysmograph to determine breathing frequency (f), inspiration (Ti) and expiration (Te) times, tidal volume (TV), minute ventilation (MV), end inspiratory pause (EIP), end expiratory (EEP) pause, peak inspiratory flows (PIF), peak expiratory flows (PEF), and a measure of bronchoconstriction (Penh). All parameters were evaluated every 15 min for 12 h. Bronchoalveolar lavage fluid (BALF) protein concentration and lung wet/dry weight ratios (W/D) were also determined at 1, 4, 8, and 12 h. A treatment x time repeated-measures two-way analysis of variance (ANOVA) revealed significant differences between air and phosgene for EEP, EIP, PEF, PIF, TV, and MV, p < or =.05, across 12 h. Phosgene-exposed mice had a significantly longer mean Ti, p < or =.05, compared with air-exposed mice over time. Mice exposed to phosgene showed marked increases (approximately double) in Penh across all time points, beginning at 5 h, when compared with air-exposed mice, p < or =.05. BALF protein, an indicator of air/blood barrier integrity, and W/D were significantly higher, 10- to 12-fold, in phosgene-exposed than in air-exposed mice 4-12 h after exposure, p 相似文献   

TEMPORAL CHANGES IN RESPIRATORY DYNAMICS IN MICE EXPOSED TO PHOSGENE

One hallmark of phosgene inhalation toxicity is the latent formation of life-threatening, noncardiogenic pulmonary edema. The purpose of this study was to investigate the effect of phosgene inhalation on respiratory dynamics over 12 h. CD-1 male mice, 25-30 g, were exposed to 32 mg/m 3 (8 ppm) phosgene for 20 min (640 mg min/m 3) followed by a 5-min air washout. A similar group of mice was exposed to room air for 25 min. After exposure, conscious mice were placed unrestrained in a whole-body plethysmograph to determine breathing frequency (f), inspiration (Ti) and expiration (Te) times, tidal volume (TV), minute ventilation (MV), end inspiratory pause (EIP), end expiratory (EEP) pause, peak inspiratory flows (PIF), peak expiratory flows (PEF), and a measure of bronchoconstriction (Penh). All parameters were evaluated every 15 min for 12 h. Bronchoalveolar lavage fluid (BALF) protein concentration and lung wet/dry weight ratios (W/D) were also determined at 1, 4, 8, and 12 h. A treatment × time repeated-measures two-way analysis of variance (ANOVA) revealed significant differences between air and phosgene for EEP, EIP, PEF, PIF, TV, and MV, p ≤ .05, across 12 h. Phosgene-exposed mice had a significantly longer mean Ti, p ≤ .05, compared with air-exposed mice over time. Mice exposed to phosgene showed marked increases (approximately double) in Penh across all time points, beginning at 5 h, when compared with air-exposed mice, p ≤ .05. BALF protein, an indicator of air/blood barrier integrity, and W/D were significantly higher, 10- to 12-fold, in phosgene-exposed than in air-exposed mice 4-12 h after exposure, p ≤ .001 and p ≤ .05, respectively. These results indicate that exposure to phosgene causes early bronchoconstriction, a temporal obstructivelike injury pattern, and disruption of mechanical rhythm largely regulated by the progressive production of pulmonary edema on airway flow. Potential therapeutic intervention may include compounds that produce bronchodilation and mechanical ventilation support if warranted.     

Determination of acute mortality in adults and sublethal embryo responses of Palaemonetes pugio to endosulfan and methoprene exposure

Adult grass shrimp (Palaemonetes pugio) were exposed to endosulfan or methoprene for 96 h and LC(50) values were calculated. Male and female P. pugio cohorts were also exposed to endosulfan for 96 h in an attempt to determine potential differences in sensitivity between the sexes. Results from the methoprene exposure indicated that this pesticide was not acutely toxic to adult grass shrimp at 1 mg l(-1). Due to the lack of sensitivity, sex specific tests with methoprene were not performed. The calculated LC(50) for a population of grass shrimp, including both males and females exposed to endosulfan, was 0.62 microg l(-1). The LC(50) determinations for the sex specific tests were 0.92 microg l(-1) for males and 1.99 microg l(-1) for females. Following these acute exposures, reproductively active grass shrimp were chronically exposed to 200 ng l(-1) endosulfan or 1 mg l(-1) methoprene and were allowed to produce embryos. The resulting embryos were assessed for potential sublethal toxicity. There were no observed differences in the percent successfully hatching or larval mortality 3-days post hatch among the treatments. However, endosulfan treated embryos had a significantly increased hatching time (9.76 days compared to 8.72 days in controls). Methoprene treated embryos also took longer to hatch (9.55 days), but this delay was not significantly different from controls. These findings suggest that endosulfan may preferentially affect male grass shrimp and exposed female grass shrimp may produce embryos with delayed hatching times.     

Dose-rate effects of ethylene oxide exposure on developmental toxicity.

In risk assessment, evaluating a health effect at a duration of exposure that is untested involves assuming that equivalent multiples of concentration (C) and duration (T) of exposure have the same effect. The limitations of this approach (attributed to F. Haber, Zur Geschichte des Gaskrieges [On the history of gas warfare], in Funf Vortrage aus den Jahren 1920-1923 [Five lectures from the years 1920-1923], 1924, Springer, Berlin, pp. 76-92), have been noted in several studies. The study presented in this paper was designed to specifically look at dose-rate (C x T) effects, and it forms an ideal case study to implement statistical models and to examine the statistical issues in risk assessment. Pregnant female C57BL/6J mice were exposed, on gestational day 7, to ethylene oxide (EtO) via inhalation for 1.5, 3, or 6 h at exposures that result in C x T multiples of 2100 or 2700 ppm-h. EtO was selected because of its short half-life, documented developmental toxicity, and relevance to exposures that occur in occupational settings. Concurrent experiments were run with animals exposed to air for similar periods. Statistical analysis using models developed to assess dose-rate effects revealed significant effects with respect to fetal death and resorptions, malformations, crown-to-rump length, and fetal weight. Animals exposed to short, high exposures of EtO on day 7 of gestation were found to have more adverse effects than animals exposed to the same C x T multiple but at longer, lower exposures. The implication for risk assessment is that applying Haber's Law could potentially lead to an underestimation of risk at a shorter duration of exposure and an overestimation of risk at a longer duration of exposure. Further research, toxicological and statistical, are required to understand the mechanism of the dose-rate effects, and how to incorporate the mechanistic information into the risk assessment decision process.     

Acute and subacute inhalation toxicity studies of a new broad spectrum insect repellent, N,N-diethylphenylacetamide

N,N-Diethylphenylacetamide (DEPA) is an inexpensive, long-acting and broad spectrum insect repellent. The acute LC50 for a 4-h exposure of DEPA aerosol was found to be 1.451 mg l-1 (1.290-1.633) in male and 1.375 mg l-1 (1.307-1.447) in female rats. DEPA did not cause delayed deaths. Acute exposure to 0.9 LC50 revealed that liver might be a target organ for DEPA toxicity. On subacute exposures to 0.2, 0.6 and 0.8 LC50 for 6 h per day, 5 days a week for 2 weeks, there was no significant change in the 0.2 LC50 group, as evaluated by the body weight gain and organ body weight ratio. The minimal changes observed in the 0.6 LC50 group were of reversible type as the animals recovered on cessation of exposure. A massive concentration of 0.8 LC50 produced lethal effects. The study shows that DEPA has a low mammalian toxicity by inhalation as was found earlier with cutaneous application of the insect repellent.     

A comparison of the acute toxicity of chemicals to fish, rats and mice

The acute toxicity of chemicals to rainbow trout, as shown by intraperitoneal injections (IP LD50), oral dosing (oral LD50) and aqueous exposure (LC50) was compared with published values for IP LD50S and oral LD50S of mice and rats. The method of comparison was by simple linear regression analyses of log-transformed data, modified to recognize that X (fish toxicity) was neither fixed nor measured without error. Within-species comparisons demonstrated very strong linear correlations (r = 0.866-0.998) between IP and oral LD50S. Variability was least for the fish data since it was all generated in one laboratory. Comparisons between species of IP and oral LD50S gave correlation coefficients ranging from 0.59 to 0.95 with the majority over 0.80. Correlations were best (r = 0.83-0.94) between fish LD50S and rat and mice IP LD50S. Correlations were poorest between fish and mammalian oral LD50S (r = 0.59-0.66) because the sample sizes and the ranges of values were very small. In all cases, the slopes were close to, or equalled, 1.0. Comparisons of fish LC50S to fish or mammalian LD50S were not as successful. Correlation coefficients ranged from 0.19 to 0.83. Presumably the cause was the aqueous exposure. Interactions of the chemicals with water (e.g. dissociation) and with lipid membranes (partitioning) should cause considerable variations in uptake efficiency. However, adjustments of LC50S for dissociation constants and partition coefficients did not improve these correlations, probably because there were few chemicals for which all data were available. These comparisons demonstrate a potential for a wider use of surrogate species in toxicity testing and for adapting existing data from mammalian toxicology to aquatic hazard assessments.     

Toxicity of fenvalerate to developing steelhead trout following continuous or intermittent exposure

Environmental toxicant exposure commonly vary in terms of duration and concentration. However, laboratory toxicity tests usually entail continuous exposures to constant concentrations. We compared survival, growth, and toxicant accumulation in early life-stage steelhead trout intermittently or continuously exposed to fenvalerate (FV) for 70 d after fertilization. Acute lethality was assessed in ancillary 96-h LC50 determinations with juvenile fish. Intermittent exposures were daily 4.5-h introductions of toxicant, and continuous exposures were to constant concentrations. All tests were conducted in a flow-through dilution apparatus, and mean concentrations for the entire exposure period were calculated for comparisons between regimens. The respective 96-h LC50 values for intermittently and continuously exposed were 88 and 172 ng/l. In the subchronic study, marked lethality (32%) and reduced terminal weight (50%) were found following exposures to cyclic FV concentrations that yielded an average of 80 ng/l (peak of 461). Continuous exposure to 80 ng FV/l did not affect these parameters. At mean FV concentrations above 20 ng/l, bioaccumulation was greater following intermittent than continuous exposure. Interaction of partitioning and elimination processes may partially explain differences in FV accumulation and subsequent toxicity.     

Effects of whole-body VX vapor exposure on lethality in rats

Male and female rats were whole-body exposed to VX vapor in a 1000-L single-pass exposure chamber. Estimated exposure dosages producing lethal (LCT50) effects in 50% of exposed male and female rats were established for 10, 60, and 240 min exposure durations. A potency comparison with GB and GF shows that VX becomes increasingly more potent than these G agents with increasing exposure duration. VX is approximately 4-30 times more potent than GB and 5-15 times more potent than GF. Gender differences in the estimated median dosages were not significant at the 10, 60, and 240 min exposure durations. An empirical toxic load model was developed and the toxic load exponent for lethality (n) in the equation Cn x T = k was determined to be n = 0.92. The VX-G regeneration assay was successfully used as a biomarker for the presence of VX in the blood plasma and RBC fractions of the blood 24 h postexposure.     

Toxicity evaluation of metal plating wastewater employing the Microtox assay: a comparison with cladocerans and fish

The relative sensitivity of the Microtox assay is closely related to the type of toxicant, and hence its utility in biomonitoring effluents is better evaluated on a case-by-case basis. The Microtox assay, employing the marine bacterium Vibrio fischeri, was evaluated for its applicability in monitoring metal plating wastewater for toxicity. The results of the Microtox assay after 5, 15, and 30 min of exposure, were compared with data obtained from conventional whole effluent toxicity testing (WET) methods that employed Daphnia magna, Ceriodaphnia dubia, and the fathead minnow (Pimephales promelas). The Microtox assay produced notably comparable EC50 values to the LC50 values of the acute fathead minnow toxicity test (< 0.5 order of difference). The Spearman's rank correlation analyses showed that the bacterial assay, regardless of exposure duration, correlated better with the acute fish than the daphnid results (p < 0.05). These observations were consistent to other studies conducted with inorganic contaminants. The relative sensitivity of the 30-min Microtox assay was within the range of the two frequently used acute daphnid/fish toxicity tests. In conclusion, the Microtox assay correlated well with the acute fathead minnow data and is well suited for toxicity monitoring for these types of industrial wastes.     

UPPER AIRWAY AND PULMONARY EFFECTS OF OXIDATION PRODUCTS OF (+)- α -PINENE,d -LIMONENE,AND ISOPRENE IN BALB/ c MICE

The oxidation products (OPs) of ozone and the unsaturated hydrocarbons d -limonene, (+)-α -pinene, and isoprene have previously been shown to cause upper airway irritation in mice during 30-min acute exposures. This study evaluated the effects of OPs and the hydrocarbons themselves on the upper airways, the conducting airways, and the lungs over a longer exposure period. The time course of development of effects and the reversibility of effects were investigated; in addition, we assessed possible exacerbation of sensory responses of the airways to the unreacted hydrocarbons. Respiratory parameters in male BALB/ c mice were monitored via head-out plethysmography. Exposures to OPs or hydrocarbons were for 60 min, followed by a 30-min challenge period with air or hydrocarbon, and a 15-min recovery period with air only. Experiments were also performed where limonene/ozone exposures were separated 6 h from the challenge period. Ozone concentration in the reaction mixture was 3.4 ppm, and concentrations of hydrocarbons were 47 ppm (α -pinene), 51 ppm (d -limonene), and 465 ppm (isoprene). Due to reaction, the ozone concentration at the point of exposure was less than 0.35 ppm; exposure to 0.30 ppm ozone for 60 min did not produce effects different from air-exposed control animals. As previously established, upper airway irritation was a prominent effect of OP exposure. In addition, over the longer exposure period we observed the development of airflow limitation that persisted for at least 45 min postexposure. All effects from limonene/ozone exposures were reversible within 6 h. Exposures to OPs did not cause enhanced upper airway irritation during challenge with the hydrocarbons, indicating that a 1-h exposure to OPs did not increase the sensitivity of the upper respiratory system. However, airflow limitation was exacerbated in animals exposed to d -limonene alone immediately following exposure to limonene OPs. These findings suggest that terpene/ozone reaction products may have moderate-lasting adverse effects on both the upper airways and pulmonary regions. This may be important in the context of the etiology or exacerbation of lower airway symptoms in office workers, or of occupational asthma in workers involved in industrial cleaning operations.