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Solitary toxic adenoma and toxic multinodular goiter are very common forms of thyrotoxicosis around the world. Advances in molecular biology and genetics have led to new insights into the pathogenesis of these disorders. Current theories on autonomy in the thyroid are discussed in this article. The therapeutic roles of surgery, radioiodine ablation, and percutaneous ethanol administration also are reviewed.
Toxicity data collected in a laboratory setting are the primary source of potency information used for regulatory, modeling, or risk assessment purposes. However, the relative reproducibility of such toxicity data is rarely discussed. This study investigated the reproducibility of growth impairment data for the freshwater ciliate Tetrahymena pyriformis exposed to a structurally diverse group of chemicals of varying hydrophobicity within different modes of toxic action, either non-covalent narcosis or covalent electro(nucleo)philicity. The proportions of chemicals representing each mode of toxic action, or mechanism of action within each mode, were not chosen to emulate the occurrence of manufactured chemicals or chemicals within the TETRATOX database. Chemicals for which prior toxicity data existed were re-tested and reproducibility was evaluated. The toxic potency values of the selected chemicals were largely reproducible after re-testing of the toxic potency, as 98% of the chemicals had re-test toxicity values within one log unit of the original potency value. To further scrutinize the reproducibility of toxicity values, differences between values were investigated by mode of toxic action. A stringent criterion for reproducibility was enforced, which dictated that the re-tested toxicity value must be encompassed by the fiducial interval (FI) of the original toxicity value and vice versa for the chemical to be considered reproducible. Toxicity values of 28 of the 50 re-tested chemicals conformed to the criterion set for reproducible values. Of the nonreproducible chemicals, seven were narcotics: four nonpolar or neutral narcotics and three other narcotics (e.g. polar narcotics). However, four of these seven narcotics did have toxicity values encompassed by one FI, but not the other FI. The remaining chemicals that did not have reproducible potency measurements were electro(nucleo)philic in nature. Certain toxicophores were highly represented among these chemicals. These included quinone derivatives, electron releasing amino and hydroxyl moieties, and electron withdrawing nitro substituents, often in tandem with strong leaving groups (i.e. halogens), and unsaturated alcohols. Lack of reproducibility was common among the chemicals that elicited toxicity after either abiotic or biotic transformation. There was no clear trend between hydrophobicity and lack of reproducibility. While data are limited, these results suggest that toxic potency values of chemicals acting via the electro(nucleo)philic mode of toxic action could be more susceptible to non-reproducibility. Ramifications of such lack of reproducibility could manifest in predictive toxicology models and their use in regulatory and risk assessment endeavors.
The ecotoxicological and chemical response of five metals (Cd, Cr, Cu, Ni, and Zn) to selective fractionation techniques was assessed using the organism Daphnia magna. The metals Cu and Zn revealed similar toxicity patterns, showing an increased toxicity when lowering the pH, a marked reduction in toxicity after addition of ethylenediaminetetraacetic acid (EDTA). Similar toxicity reductions were obtained by passing the metal solutions over ion exchangers, activated charcoal, and filtration/solid-phase extraction units at neutral and basic pHs. The discrimination between Cu- and Zn-toxicity occurred in the oxidant reduction test, i.e., Zn toxicity was not affected by the addition of Na2S2O3, while Cu toxicity was strongly reduced. A second cluster was formed by Cd and Ni. The toxicity of both metals markedly decreased in the EDTA, ion exchangers, activated charcoal, filtration, and solid-phase extraction tests at high pHs. Discrimination between the toxicity of both metals was accomplished with the graduated pH test, in which a pH-independent toxicity response was found for Ni while the toxicity of Cd increased at lower pHs. Compared with the other metals, a very distinct toxicity pattern for Cr was observed. From the applied fractionation techniques, only the graduated pH and the anion resin tests resulted in a marked change in Cr toxicity. The produced toxicity patterns for each individual metal could therefore be used as fingerprints (i.e., toxicity identification fingerprints) in order to identify the toxicity caused by individual metals for D. magna.
Domoic acid was orally administered to 3 cynomolgus monkeys at doses of 0.5 mg/kg for 15 days and then at 0.75 mg/kg for another 15 days. After the 30-day dosing period, the treated monkeys were killed. Parameters monitored as markers for toxicity included body weight, food and water consumption, clinical observations, hematology, serum chemistry, light microscopy of all major organs (including brain and retina), and glial fibrillary acid protein immunohistochemistry. Domoic acid in serum and 24-hour urine samples was measured at several time points. All parameters measured remained unremarkable. Domoic acid concentrations measured in the 24-hour urine samples indicated that gastrointestinal absorption in the monkey was approximately 4-7 percent of the administered dose, which is at least twice that previously reported for the rat.
Toxic shock syndrome toxin 1 (TSST-1), plays a significant role in the pathogenesis of TSS. TSST-1 production is subject to physiologic and environmental constraints. Thus, DNA probes that detect the chromosomal gene encoding the toxin are of value diagnostically, epidemiologically, and for studies of gene expression. Several synthetic oligonucleotide probes complementary to two regions of the TSST-1 gene were used to ascertain the presence of this gene in the chromosomal DNA of 261 strains of S. aureus from various TSS-related and non-TSS-related sources. Isolates were from clinically confirmed menstrual and nonmenstrual cases of TSS and from healthy vaginal carriers of S. aureus. Other strains tested included clinical non-TSS isolates and food poisoning-associated staphylococcal isolates. Detection of the TSST-1 gene by the labeled gene probes correlated in all but two cases with production of TSST-1. Ten Centers for Disease Control (CDC) strains that were isolated from TSS patients and did not produce TSST-1 were also examined, as were several strains of Staphylococcus epidermidis isolated from patients with suspected TSS. Neither group of strains possessed the TSST-1 gene. Finally, a 7-kilobase DNA restriction fragment of S. aureus containing the entire TSST-1 gene was transformed into Escherichia coli strains HB101 and DH5 alpha via a plasmid vector.
Two new research approaches in combustion toxicology are: 1. the prediction of smoke toxicity from mathematical equations, which are empirically derived from, experiments on the toxicological interactions of complex fire gas mixtures and 2. the use of toxicant suppressants in materials or products to prevent the formation of toxic combustion products. The predictive approach consists of burning materials using a bench-scale method that simulates realistic fire conditions, measuring the concentrations of the primary fire gases--CO, CO2, low O2, HCN, HCl, HBr, and NO2--and predicting the toxicity of the smoke using either the 6- or 7-gas N-Gas Model. These models are based on the results of toxicological studies of these primary gases as individual gases and as complex mixtures. The predicted toxic potency is checked with a small number of animal (Fischer 344 male rats) tests to assure that an unanticipated toxic gas is not generated or an unexpected synergistic or antagonistic effect has not occurred. The results indicate if the smoke from a material or product is extremely toxic (based on mass consumed at the predicted toxic level) or unusually toxic (based on the gases deemed responsible). The predictions based on bench-scale laboratory tests have been validated with full-scale room burns of a limited number of materials of widely differing characteristics chosen to challenge the system. The advantages of this new approach are 1. the number of test animals is minimized by predicting the toxic potency from the chemical analysis of the smoke, 2. smoke may be produced under conditions that simulate the fire scenario of concern, 3. fewer tests are needed, thereby reducing the overall cost of the testing and 4, information is obtained on both the toxic potency of the smoke and the responsible gases. The N-Gas Models have been developed into the N-Gas Method (described in this paper) and these results have been used in computations of fire hazard. The 6-Gas Model is now part of the international standard ISO 13344 approved by 16 member countries of the International Standards Organization (ISO) and is also included in the U.S. national standard ASTM E1678 approved by the American Society for Testing and Materials (ASTM). In addition, the 6-Gas Model is used in the American National Standard--NFPA 269--approved by the National Fire Protection Association (Quincy, MA). The second new research approach, toxicant suppressants, examines the potential of chemical compounds, which when added to a material, to inhibit or reduce the concentration of a specific toxic gas normally generated during the material's thermal decomposition. The effectiveness of this approach was demonstrated at the National Institute of Standards and Technology (NIST) when HCN generation was reduced by 90% and the resultant toxicity of the combustion products was lowered by 50% when a flexible polyurethane foam (FPU) was treated with 0.1% (by weight) cuprous oxide (Cu2O). Copper and cupric oxide (CuO) also reduced the HCN generation but were not as efficient as Cu2O. Although melamine-treated FPU foams are being promoted as more fire safe than standard foams, a melamine-treated foam generated 10 times more HCN than a foam without melamine. The addition of Cu2O to this melamine foam also reduced the HCN generation by 90%.
PURPOSE: Several investigations have revealed that the alpha/beta ratio for prostate cancer is atypically low, and that hypofractionation or high-dose-rate (HDR) brachytherapy regimens using appropriate radiation doses may be expected to yield tumor control and late sequelae rates that are better or at least as favorable as those achieved with conventional radiation therapy. In this setting, we attempted treating localized prostate cancer patients with HDR brachytherapy combined with hypofractionated external beam radiation therapy (EBRT). The purpose of this study was to evaluate the feasibility of using this approach, with special emphasis on the relationship between the severity of acute genitourinary (GU) toxicity and the urethral dose calculated from the dose-volume histogram (DVH) of HDR brachytherapy. METHODS AND MATERIALS: Between September 2000 and December 2003, 70 patients with localized prostate cancer were treated by iridium-192 HDR brachytherapy combined with hypofractionated EBRT at the Gunma University Hospital. Hypofractionated EBRT was administered in fraction doses of 3 Gy, three times per week; a total dose of 51 Gy was delivered to the prostate gland and the seminal vesicles using the four-field technique. No elective pelvic irradiation was performed. After the completion of EBRT, all the patients additionally received transrectal ultrasonography (TRUS)-guided HDR brachytherapy. The fraction size and the number of fractions in HDR brachytherapy were prospectively changed, whereas the total radiation dose for EBRT was fixed at 51 Gy. The fractionation in HDR brachytherapy was as follows: 5 Gy x 5, 7 Gy x 3, 9 Gy x 2, administered twice per day, although the biologic effective dose (BED) for HDR brachytherapy combined with EBRT, assuming that the alpha/beta ratio is 3, was almost equal to 138 in each fractionation group. The planning target volume was defined as the prostate gland with 5-mm margin all around, and the planning was conducted based on computed tomography images. The number of patients in each fractionation group was as follows: 13 in the 5-Gy group; 19 in the 7-Gy group, and 38 in the 9-Gy group. The tumor stage was T1 in 10 patients, T2 in 36 patients, and T3 in 24 patients. The Gleason score was 2-6 in 11 patients, 7 in 34 patients, and 8-10 in 25 patients. Androgen ablation was performed in all the patients. The median follow-up duration was 14 months (range 3-42 months). The toxicities were graded based on the Radiation Therapy Oncology Group/European Organization for Research and Treatment of Cancer toxicity criteria. RESULTS: The main symptoms of acute GU toxicity were dysuria and increase in urinary frequency or nocturia. The grade distribution of acute GU toxicity in the patients was as follows: Grade 0-1, 39 patients (56%), and Grade 2-4, 31 patients (44%). One patient who developed acute urinary obstruction was classified as having Grade 4 toxicity. Comparison of the distribution of the grade of acute GU toxicity among the different fractionation groups revealed no statistically significant differences among the groups. The urethral dose in HDR brachytherapy was evaluated using the following DVH parameters: V30 (percentage of the urethral volume receiving 30% of the prescribed radiation dose), V80, V90, V100, V110, V120, V130, and V150. The V30-110 values in the patients with Grade 2-4 acute GU toxicity were significantly higher than those in patients with Grade 0-1 toxicity. On the other hand, there were no significant differences in the V120-150 values between patients with Grade 0-1 and Grade 2-4 toxicity. Regarding the influence of the number of needles implanted for the radiation therapy, patients with 11 needles or less showed a significantly higher incidence of Grade 2-4 acute GU toxicity compared with those with 12 needles or more (p < 0.05). CONCLUSIONS: It was concluded that HDR brachytherapy combined with hypofractionated EBRT is feasible for localized prostate cancer when considered from the viewpoint of acute toxicity. Increase in the fraction dose or reduction in the number of fractions in HDR brachytherapy did not affect the severity of acute GU toxicity, and the volume of urethra receiving an equal or lower radiation dose than the prescribed dose was more closely associated with the grade severity of acute GU toxicity than that receiving a higher than the prescribed dose.
PURPOSE: We have been treating localized prostate cancer with high-dose-rate (HDR) brachytherapy combined with hypofractionated external beam radiation therapy (EBRT) at our institution. We recently reported the existence of a correlation between the severity of acute genitourinary (GU) toxicity and the urethral radiation dose in HDR brachytherapy by using different fractionation schema. The purpose of this study was to evaluate the role of the urethral dose in the development of acute GU toxicity more closely than in previous studies. For this purpose, we conducted an analysis of patients who had undergone HDR brachytherapy with a fixed fractionation schema combined with hypofractionated EBRT. METHODS AND MATERIALS: Among the patients with localized prostate cancer who were treated by 192-iridium HDR brachytherapy combined with hypofractionated EBRT at Gunma University Hospital between August 2000 and November 2004, we analyzed 67 patients who were treated by HDR brachytherapy with the fractionation schema of 9 Gy x two times combined with hypofractionated EBRT. Hypofractionated EBRT was administered at a fraction dose of 3 Gy three times weekly, and a total dose of 51 Gy was delivered to the prostate gland and seminal vesicles using the four-field technique. No elective pelvic irradiation was performed. After the completion of EBRT, all the patients additionally received transrectal ultrasonography-guided HDR brachytherapy. The planning target volume was defined as the prostate gland with a 5-mm margin all around, and the planning was conducted based on computed tomography images. The tumor stage was T1c in 13 patients, T2 in 31 patients, and T3 in 23 patients. The Gleason score was 2-6 in 12 patients, 7 in 34 patients, and 8-10 in 21 patients. Androgen ablation was performed in all the patients. The median follow-up duration was 11 months (range 3-24 months). The toxicities were graded based on the Radiation Therapy Oncology Group and the European Organization for Research and Treatment of Cancer toxicity criteria. RESULTS: The main symptoms of acute GU toxicity were dysuria and increase in the urinary frequency or nocturia. The grade distribution of acute GU toxicity in the patients was as follows: Grade 0-1, 42 patients (63%); Grade 2-3, 25 patients (37%). The urethral dose in HDR brachytherapy was determined using the following dose-volume histogram (DVH) parameters: V30 (percentage of the urethral volume receiving 30% of the prescribed radiation dose), V80, V90, V100, V110, V120, V130, and V150. In addition, the D5 (dose covering 5% of the urethral volume), D10, D20, and D50 of the urethra were also estimated. The V30-V150 values in the patients with Grade 2-3 acute GU toxicity were significantly higher than those in patients with Grade 0-1 toxicity. The D10 and D20, but not D5 and D50, values were also significantly higher in the patients with Grade 2-3 acute GU toxicity than in those with Grade 0-1 toxicity. Regarding the influence of the number of needles implanted, there was no correlation between the number of needles implanted and the severity of acute GU toxicity or the V30-V150 values and D5-D50 values. CONCLUSIONS: It was concluded that HDR brachytherapy combined with hypofractionated EBRT is feasible for localized prostate cancer, when considered from the viewpoint of acute toxicity. However, because the urethral dose was closely associated with the grade of severity of the acute GU toxicity, the urethral dose in HDR brachytherapy must be kept low to reduce the severity of acute GU toxicity.
An efficient and novel method for the identification of toxic compounds in industrial wastewater was developed. In the first step, the samples collected were tested for toxicity using the recently developed ToxAlert 10 system based upon luminescence inhibition of freeze-dried Vibrio fischeri. In the second step, sequential solid-phase extraction (SSPE) and liquid chromatography/mass spectrometry (LC/MS) for compound identification were employed to isolate and identify compounds in the waters. Average recoveries ranging from 72 to 95% were obtained using the SSPE methodology for ubiquitous analytes such as poly(ethylene glycol)s, nonylphenol and alcohol polyethoxylates, phenols, linear alkylbenzenesulfonates, and benzene- and naphthalenesulfonates. In the third step, all the extracts obtained after SSPE followed by LC/MS identification were tested again with the ToxAlert system. The procedure was applied to influent and effluent samples of a sewage treatment plant (STP) and to a raw tannery effluent that constitutes the main type of influent in the receiving waters of the STP. This method has shown that, despite the complexity of the untreated tannery wastewaters with an average total organic carbon (TOC) value of 1960 mg of C/L, the biological treatment of the STP eliminates compounds that inhibit luminiscence of V. fischeri. In the final step, the chemical toxicity of the tentatively identified chemicals was tested to identify the toxicants in the waters. Comparison of the toxicities of the sample, the extracts, and individual components has shown that diverse classes of pollutants were responsible for toxicity, as all fractions of toxic samples gave significant bioluminescence inhibition values. Toxicity of the two intermediate-polarity SSPE fractions was attributed to alcohol ethoxylates, nonylphenol ethoxylates, bis(2-ethylhexyl)phthalate, and linear alkylbenzenesulfonates. In the most nonpolar and most polar fractions, identification of the compounds responsible for toxicity was unclear. By the toxicity-based fractionation, followed by LC/MS methodology, it was feasible to identify between 1.4 and 7.5% of the TOC, thus expanding the number of toxicants identified in these complex wastewaters as compared to those identified by conventional gas chromatography/mass spectrometric (GC/MS) methods. When artificial water samples were reconstituted using similar concentrations of the chemicals detected in the wastewaters, nonsynergetic toxicity effects were observed for all analytes with the exception of 2,6-naphthalenedisulfonate (2,6-NPS), which promoted the bioluminescence inhibition. The toxicity-directed identification was successful for the STP's samples and showed 1400 times higher toxicity for the raw tannery wastewaters as compared to the mixed industrial and domestic wastewaters by applying the Weibull model.
BACKGROUND: The toxicity of a given cancer therapy is an important end point in clinical trials examining the potential costs and benefits of that therapy. Treatment-related toxicity is conventionally measured with one of several toxicity criteria grading scales, even though the reliability and validity of these scales have not been established. PURPOSE: We determined the reliability of the National Cancer Institute of Canada Clinical Trials Group (NCIC-CTG) expanded toxicity scale and the World Health Organization (WHO) standard toxicity scale by use of a clinical simulation of actual patients. METHODS: Seven experienced data managers each interviewed 12 simulated patients and scored their respective acute toxic effects. Inter-rater agreement (agreement between multiple raters of the same case) was calculated using the kappa (kappa) statistic across all seven randomly assigned raters for each of 18 toxicity categories (13 NCIC-CTG and five WHO categories). Intra-rater agreement (agreement within the same rater on one case rated on separate occasions) was calculated using kappa over repeated cases (where raters were blinded to the repeated nature of the subjects). Proportions of agreement (estimate of the probability of two randomly selected raters assigning the same toxicity grade to a given case) were also calculated for inter-rater agreement. Since minor lack of agreement might have adversely affected these statistics of agreement, both kappa and proportion of agreement analyses were repeated for the following condensed grading categories: none (0) versus low-grade (1 or 2) versus high-grade (3 or 4) toxicity present. RESULTS: Modest levels of inter-rater reliability were demonstrated in this study with kappa values that ranged from 0.50 to 1.00 in laboratory-based categories and from -0.04 to 0.82 for clinically based categories. Proportions of agreement for clinical categories ranged from 0.52 to 0.98. Condensing the toxicity grades improved statistics of agreement, but substantial lack of agreement remained (kappa range, -0.04-0.82; proportions of agreement range, 0.67-0.98). CONCLUSIONS: Experienced data managers, when interviewing patients, draw varying conclusions regarding toxic effects experienced by such patients. Neither the NCIC-CTG expanded toxicity scale nor the WHO standard toxicity scale demonstrated a clear superiority in reliability, although the breadth of toxic effects recorded differed.
AIMS: To explore the scope for regulating to reduce the toxicity of manufactured cigarettes sold in New Zealand (NZ), based on published toxicant emissions by brand. METHODS: Internet searches of published cigarette smoke emissions of 13 toxicants chosen on risk assessment principles, for 20 British Columbian, 15 Australian brands, and one NZ brand, Holiday Extra-mild (HEM), tested by Health Canada intensive smoke machine method at Labstat Inc, Kitchener, Ontario, as a ratio of toxicant to nicotine yield. We estimated relative overall smoke toxicity per disease group and per brand, after adjusting for the published cigarette-attributed mortality fractions for cancer, cardiovascular, and respiratory disease. RESULTS: After allowing for nicotine yield, filter ventilation, and compensatory over-smoking, there were significant differences between brands, with the NZ brand estimated to be the most toxic. Low-yield cigarettes (<0.9 mg nicotine ISO) were estimated to be on average 19% more potent overall than medium-yield cigarettes (p<0.01). Of toxicants identified and measurable in smoke; 1,3-butadiene accounted for 45% of cancer potency; hydrogen cyanide for 89% of cardiovascular; and acrolein for 97% of respiratory potency--these three toxicants accounting for 65% of identified brand potency. Individual toxicant emissions varied across brands by a factor of 1.5 for carbon monoxide, to 32 for lead. Compared with HEM, one Canadian brand, 'Export A full flavor', carried a 37% lower cancer risk. This lower risk was largely due to differences in nicotine yield, lowering the toxicant/nicotine ratio. CONCLUSIONS: Cigarettes, unregulated, are unduly dangerous. Though many smoke toxicants cannot yet be quantified, risk assessment based on current data suggests that regulation could partly reduce identifiable cancer risk, and possibly eliminate the excess cardiovascular and respiratory toxicity of HEM, when compared with regular Canadian brands. The first goal should be to reduce emissions of the leading three toxicants, in addition to more effective charcoal filters. Tobacco smoke, unlike unburnt or non-smoking tobacco, contains toxic gases and trillions of reactive oxygen species molecules per puff, and will remain inherently harmful. Regulation could usefully part-reduce smoke toxicity exposure for continuing smokers, while not relenting on efforts to assist smokers and society to be quit of smoking.
In this study, the effect of hardness on the combined outcome of metal mixtures was investigated using Daphnia magna. The toxic unit (TU) was calculated using modified LC(50) values based on the hardness (i.e., LC(50-soft) and LC(50-hard)). From a bioassay test, the degree of sensitivity to hardness on the toxicity changes was in the order: Cd<Cu<Zn<Pb, with 25, 66, 77 and 88% decreases in the LC(50) values, respectively, when the hard test solution was replaced with a soft test solution. In mixture toxicity tests, the difference in the test solution hardness was found to clearly cause different toxicities, as determined by the TU calculated by the LC(50-hard), using the toxicity of a standard culture medium as the reference. That is, approximately four to five times higher toxicity was observed in soft (i.e., 44+/-4 mg/L as CaCO(3)) rather than hard water (i.e., 150+/-10mg/L as CaCO(3)) test solutions. In the tests where the modified reference toxicity values (i.e., LC(50-soft) and LC(50-hard) for soft and hard test solution, respectively) obtained from the individual metal toxicity tests with different hardness were used to calculate the TU, the results showed very similar D. magna toxicities to those of the TU from the mixture of soft and hard test solutions, regardless of the hardness. According to the toxicity results of the mixture, the aquatic toxic effects of the acid mine drainage (AMD) collected from mine areas that contained metal mixtures were investigated using Daphnia magna and the modified LC(50) value of the TU hardness function calculated for varying solution hardness. The results of the biological WET test closely matched our overall prediction, with significant correlation, having a p-value of 0.513 in one way ANOVA test (n=19). Therefore, this study revealed that the predicted toxicity of the metal mixture agreed well with the biological toxicity test when the modified LC(50) value was employed as the basis of hardness in the TU calculation.
The Microtox Acute Toxicity Test has been successfully used to measure the toxicity of metals and other pollutants at high concentrations (ppm) in selected environmental samples. However, metals and other toxicants are often found in much lower concentrations (ppb) in many municipal wastewaters and receiving waters. In order to assess the toxicity of these pollutants in these samples, a more sensitive toxicity assay is needed. The Microtox chronic toxicity test has been developed to measure the sublethal effect of toxicants over multiple generations of the test species, Vibrio fisheri. In this study, the toxicity of the 13 priority pollutant metals [i.e. As, Se, Cd, Cr (III and VI), Cu, Pb, Sb, Ag, Tl, Zn, Be, Hg and Ni] to V. fisheri was evaluated using the Microtox chronic toxicity test. In this test, the inhibitory concentration (IC), lowest observable effect concentration (LOEC), and no observable effect concentration (NOEC) were obtained after 22-h of incubation at 27+/-1 degrees C, by comparing the light output of the control to that of the test sample. Among the 13 priority pollutant metals, beryllium (Be) was found to be the most toxic in the test (LOEC=0.742-1.49 microg/l) while thallium (Tl) was the least toxic (LOEC=3840-15300 microg/l). The LOECs for copper (as Cu) and lead (Pb) in reagent (ASTM Type I) water were 6.78-13.6 microg/l and 626-1251 microg/l, respectively. The toxicity of copper sulfate (as Cu) in reagent water was shown and significantly reduced with the addition of natural organic matter (fulvic acid) or EDTA to the sample. The LOEC values for the 13 priority pollutant metals in this test were comparable to or lower than those reported for commonly used aquatic toxicity tests, such as the Ceriodaphnia dubia assay.
The toxicity of 39 laundry detergent components including surfactants, enzymes, builders, fabric brighteners, fillers, and coloring agents to the cladoceran Ceriodaphnia cf. dubia was determined. The difference between the most and the least toxic components was approximately 17,000-fold and 1,000,000-fold for the mg/L and mmol/L EC50 data, respectively. Two of the components had high toxicity (EC50 values < 1 mg/L), 11 moderate toxicity (EC50 values between 1 and 10 mg/L), and the remaining 26 components had low toxicity (EC50 values > 10 mg/L). Analysis revealed that mixtures of the components interacted antagonistically, additively, and synergistically. On a molarity basis the most toxic group of compounds was the surfactants followed by the brighteners. The most toxic individual components included sodium carboxymethyl cellulose, sodium silicate solution, four brighteners, sodium perborate tetrahydrate, and the surfactants. Many of the most toxic components, however, contributed very little to the toxicity of the detergents due to being present in the detergents at low concentrations. The main contributors to the toxicity of detergents were the sodium silicate solution and the surfactants-with the remainder of the components contributing very little to detergent toxicity. The potential for acute aquatic toxic effects due to the release of secondary or tertiary sewage effluents containing the breakdown products of laundry detergents may frequently be low. However, untreated or primary treated effluents containing detergents may pose a problem. Chronic and/or other sublethal effects that were not examined in this study may also pose a problem.
The underlying etiology of the toxic oil syndrome may be related to any of several toxic contaminants. The hypothesis is made that two or more toxic compounds may act synergistically to cause vascular damage in the toxic oil syndrome. To support this hypothesis, previous studies are reviewed concerning the remarkable synergistic toxic action of allylamine and beta-aminopropionitrile on the media of blood vessels. Although these toxins are not directly related to the toxic oil syndrome, this previous experimental work emphasizes the possibility that unexplored synergistic actions may be important. Furthermore, the hypothesis that contaminating fatty acid anilides in toxic oil undergo alterations during cooking is supported by high pressure liquid chromatographic analysis. The theoretic metabolism of fatty acid anilides is discussed. Recent data concerning the toxic actions of the anilides of oleic and linoleic acid are given. These data suggest that these anilides induce immunologic alterations that may be similar to those seen in the toxic oil syndrome. In addition, the heated anilides appear to have increased toxicity, supporting the concept that the use of toxic oil in cooking may increase its toxicity.
Assessment of the potential developmental toxicity of arsenic in humans must be based entirely on the extensive animal literature; no appropriate human data are available. Hazard identification of developmental toxicity of arsenic in animal studies is complicated by the co-occurrence of maternal and developmental toxicity when the pregnant dam is exposed to the toxicant. Current regulatory guidance requires that, when maternal and developmental toxicity occur at the same or similar doses, detailed consideration needs to be given to whether developmental toxicity is secondary to maternal toxicity or whether it represents a distinct hazard. In this review, these principles were applied to the relatively large database of animal studies available for hazard identification of inorganic arsenic as a developmental toxicant. It is concluded that maternal and developmental toxicity occur in the same dose range for this potent cytotoxicant, although differential no observed adverse effect levels can be identified depending on the endpoints used. Various evidence from the basic science literature indicates that developmental toxicity is not secondary to maternal toxicity. Current regulatory guidance falls short of defining effective approaches to resolving the difficulties posed by co-occurrence of maternal and developmental toxicity.
The study on the toxicity of heavy metals Hg2+, Cd+, Cu2+ and Pb2+ to Arabidopsis se d germination and seedling growth showed that the test heavy metals had a stronger toxicity on seedling growth than on seed germination. The toxicity on seedlings was in order of Cu2+ > Hg2+ > Cd2+ /Pb2+, while on seeds was Hg2+ > Cd2+ > Pb2+/Cu2+. Seed germination rate was decreased with increasing stress duration, and different heavy metals showed different toxicity at different stress duration. For example, Hg2+ displayed a stronger toxicity at 12 - 24 h stress, while Cd2+ was at 0 - 12 h stress. It seemed that seed coat played an important role in seed tolerance to heavy metals. The interaction between non-toxic ions and heavy metal ions on seed germination showed that Ca2+, Mg2+, K+ and Na+ at 5 mmol x L(-1) could enhance the toxicity of Hg2+, but did not affect Cd2+ toxicity. For seedling growth, Ca2+, Mg2+, K+ and Na+ might enhance the toxicity of Hg2+, Ca2+ might alleviate the toxicity of Cd2+ but enhance the toxicity of Cu2+ , and K+ might alleviate Pb2+ toxicity. The mechanism of heavy metals injury was discussed in the paper.
Semipermeable membrane devices (SPMDs) were deployed for 4 weeks in two rivers in Lithuania. The SPMD dialysates were tested in the Microtox assay and, surprisingly, the sample from the relatively clean Ula River exhibited three times more toxicity than the sample from the Vilnia River receiving discharge from several industrial enterprises and municipal waste-water. The whole dialysates were subjected to bioassay-directed fractionation on silica gel columns. Toxicity testing of each fraction revealed that most of the toxicity was contained in fraction 10, which was eluted with 100% acetone. GC/FID, GC/ECD, and GC/FTIR/MS analysis of the fractions indicated that the major component of this fraction was oleic acid. The oleic acid was most likely the hydrolysis product of methyl oleate, the major impurity of the SPMD triolein. It can be inferred that oleic acid was responsible for the toxicity of this fraction in Microtox, as a threefold difference in the toxicity between the two samples was also marked by a threefold difference in their oleic acid content. Toxicity of unsaturated fatty acids in various tests, including Microtox, has been demonstrated elsewhere. Vilnia fraction 2, which was eluted with 100% hexane, exhibited the most toxicity of the remainder of silica gel fractions. The spectral analysis demonstrated that other toxic fractions contained a number of halogenated compounds and PAHs. In general, SPMDs have proved to be a useful way to screen for hydrophobic toxicants in water. However, sample clean-up procedures to remove oleic acid may be required prior to toxicity testing for the estimation of the true toxic potential of the accumulated pollutants.