Precision Constraints for Three-Flavor Neutrino Oscillations from the Full MINOS+ and MINOS Dataset.

We report the final measurement of the neutrino oscillation parameters Δm_{32}^{2} and sin^{2}θ_{23} using all data from the MINOS and MINOS+ experiments. These data were collected using a total exposure of 23.76×10^{20} protons on target producing ν_{µ} and ν[over ¯]_{µ} beams and 60.75 kt yr exposure to atmospheric neutrinos. The measurement of the disappearance of ν_{µ} and the appearance of ν_{e} events between the Near and Far detectors yields |Δm_{32}^{2}|=2.40_{-0.09}^{+0.08}(2.45_{-0.08}^{+0.07})×10^{-3} eV^{2} and sin^{2}θ_{23}=0.43_{-0.04}^{+0.20}(0.42_{-0.03}^{+0.07}) at 68% C.L. for normal (inverted) hierarchy.

Carcinogenic effects of acrylamide in Sencar and A/J mice.

Acrylamide structurally resembles vinyl carbamate, a proposed proximate carcinogenic form of ethyl carbamate. To test the hypothesis that acrylamide should possess carcinogenic properties, it was tested in the Salmonella-microsome assay for point mutation, as a skin tumor initiator in the Sencar mouse, and for its ability to induce lung adenomas in the A/J mouse. Acrylamide was found to be without activity as a mutagen in Salmonella strains TA 1535, TA 1537, TA 98, and TA 100 both in the presence and absence of rat liver microsomes using both the plate and liquid suspension assays. However, acrylamide was found to approximate ethyl carbamate in potency as a tumor initiator in the skin of the female Sencar mice. As with ethyl carbamate, acrylamide was more potent by systemic routes of administration relative to topical application. Acrylamide was also found to induce lung adenomas in male and female A/J mice using both the p.o. and i.p. routes of administration. Acrylamide was approximately one-seventh as potent as ethyl carbamate in the induction of lung adenomas. These data confirm the hypothesis that acrylamide possesses carcinogenic properties similar to ethyl carbamate.

Structure, synthesis, and post-transcriptional modification of ribosomal ribonucleic acid in Bdellovibrio bacteriovorus.

The structure, synthesis, and post-transcriptional modifications of 23-S and 16-S ribosomal RNAs (rRNAs) have been studied in the facultatively parasitic bacterium, Bdellovibrio bacteriovorus. The mature 23-S and 16-S type of rRNAs in Bdellovibrio are larger than the analogous molecules in Escherichia coli by at least 1.0 - 10(5) and 0.5 - 10(5) daltons, respectively, and have a conformation different from E. coli rRNAs as judged by relative electrophoretic mobilities in polyacrylamide gels with and without denaturing conditions. Studies on the kinetics of synthesis and maturation of ribosomal RNA in Bdellovibrio show that precursor forms analogous to p23-S and p16-S in E. coli are synthesized. In addition, some earlier precursor rRNAs in Bdellovibrio are seen that appear analogous to the 25S and 17.5-S pre-rRNAs that have only been observed in the RNAase III deficient mutant of E. coli strain AB301-105 (Nikolaev, Birenbaum, M. and Schlessinger, D. (1975) Biocheim, Biophys. Acta 395, 478-489). These early precursor stages have not been observed in other procaryotic species, including E. coli that have normal levels of RNAase III. The results from the Bdellovibrio system provide that the 25-s and 17.5-S pre-rRNAs are normal stages of rRNA modification and are part of a multiple step maturation process, and therefore are not aberrations associated with the RNase III deficient mutation.

Use of biological assay systems to assess the relative carcinogenic hazards of disinfection by-products.

Other workers have clearly shown that most, if not all, drinking water in the U.S. contains chemicals that possess mutagenic and/or carcinogenic activity by using bacterial and in vitro methods. In the present work, increased numbers of tumors were observed with samples of organic material isolated from 5 U.S. cities administered as tumor initiators in mouse skin initiation/promotion studies. Only in one case was the result significantly different from control. In studies designed to test whether disinfection practice contributes significantly to the tumor initiating activity found in drinking water mixed results have been obtained. In one experiment, water disinfected by chlorination, ozonation or combined chlorine resulted in a significantly greater number of papillomas when compared to nondisinfected water. In two subsequent experiments, where water was obtained from the Ohio River at different times of the year, no evidence of increased initiating activity was observed with any disinfectant. Analysis of water obtained at the comparable times of the year for total organic halogen, and trihalomethane formation revealed a substantial variation in the formation of these products. Considering the problems such variability poses for estimating risks associated with disinfection by-products, a model system which makes use of commercially obtained humic acid as a substrate for chlorination was investigated using the Ames test. Humic and fulvic acids obtained from two surface waters as well as the commercially obtained humic acid were without activity in TA 1535, TA 1537, TA 1538, TA 98 or TA 100 strains of S. typhimurium. Following treatment with a 0.8 molar ratio of chlorine (based on carbon) significant mutagenic activity was observed with all humic and fulvic acid samples. Comparisons of the specific mutagenic activity of the chlorinated products suggests that the commercial material might provide a useful model for studying health hazards associated with disinfection reactions by-products.

Mutagenic by-products from chlorination of humic acid.

Chlorination of humic and fulvic acid results in the formation of direct-acting mutagenicity, detectable in the Salmonella/microsome assay (Ames test). This mutagenicity is being characterized as part of an overall effort aimed at evaluating potential health risks associated with the presence of mutagenic chemicals in drinking water. A number of chlorinated organic compounds, including several known mutagens, have been identified and quantified in diethyl ether extracts of chlorinated humic acid solutions. However, the total mutagenicity of these compounds accounts for only about 7% of the original mutagenicity. Synergistic or antagonistic interactions among the identified components have been ruled out as possible explanations for the failure to account for a higher percentage of the activity. Recent progress has been made to separate the activity into neutral and strong acid fractions. Further isolation of the strong acids by high-pressure liquid chromatography (HPLC) has resulted in the purification of the mutagenicity into a major peak of activity with a specific mutagenicity of about 20,000 TA100 revertants per milligram. Several trichlorohydroxyfuranone isomers have been tentatively identified in this fraction. The contribution of these types of compounds to the mutagenicity of chlorinated humic acid is under investigation.

Results of toxicological testing of Jefferson Parish pilot plant samples.

Five toxicological tests were performed using concentrated drinking water samples collected at a pilot-scale drinking water treatment plant that had streams treated with different disinfectants (no disinfectant, ozone, chlorine dioxide, monochloramine, or chlorine) before treatment with granular activated carbon (GAC). The toxicological tests used in this study were the Ames Salmonella assay, a subchronic in vivo toxicity assay in mice, the SENCAR mouse skin initiation-promotion assay, a rat liver foci assay, and the lung adenoma assay in strain A mice. These tests were conducted to determine the general toxicity and the mutagenic/carcinogenic potential associated with the use of disinfection and/or GAC in the treatment of drinking water. The stability of the mutagenic activity of the samples tested was determined by repeated analysis using the Ames Salmonella assay. Results indicated that the samples remained mutagenic for the duration of the tests. All the drinking water concentrates (4000 X) prepared by the XAD resin adsorption procedure failed to provide statistically significant indication of carcinogenic activity in the SENCAR mouse, rat liver foci, and the lung adenoma assays. However, concentrates of the chlorine, chlorine dioxide, and monochloramine treated waters gave consistent mutagenic responses in the Ames Salmonella assay. GAC was effective for 6 months in removing both the mutagenicity of chlorine-treated water and the potential of water to become mutagenic when treated with chlorine. In the in vivo, subchronic 30-day toxicity test in mice, some statistically significant differences in organ weights and body weights of animals exposed to different concentrates of some of the samples were observed. However, a consistent pattern of these differences indicating overt toxicity was not detected.

Feasibility of micronucleus methods for monitoring genetic damage in two feral species of small mammals.

Peromyscus leucopus (white-footed mouse) and Cryptotis parva (least shrew) possess desirable attributes for biomonitoring contamination of terrestrial ecosystems, but few studies have examined the potential use of these species for monitoring exposure to genotoxic contaminants. The susceptibility of laboratory-reared C. parva, P. leucopus, and Mus musculus (house mouse, strain CD-1) to micronucleus (MN) induction by known clastogens was evaluated. Animals were exposed for 24 hr to methyl methanesulfonate (MMS; 12.5, 25, and 50 mg/kg), 4-nitroquinoline 1-oxide (4-NQO; 7.5, 15, and 30 mg/kg), or mercuric chloride (HgCl2; 6, 12, and 24 mg/kg). Both MMS and 4-NQO induced dose-related increases in micronucleated polychromatic erythrocytes (MNPCE) in all three species, whereas HgCl2 induced a weak response only in P. leucopus. P. leucopus and C. parva were more sensitive than M. musculus to MMS. Similar micronucleus responses to 4-NQO were seen in each of the species. The feasibility of using blood for MN assessment was evaluated by comparing MN frequencies in bone marrow (BM) PCE, and blood PCE and normochromatic erythrocytes (NCE) in untreated animals, and following daily treatment for 1, 2, 3, and 10 days with 0.4 mg/kg triethylenemelamine (TEM). The results indicated that micronucleated erythrocytes were removed from the circulating blood in P. leucopus, but not in C. parva. Measurement of BM and blood MN levels appears feasible for monitoring exposure to genotoxic agents in C. parva and P. leucopus, and for distinguishing between acute and chronic exposure in C. parva.

Mutagenic and clastogenic properties of 3-chloro-4-(dichloromethyl)-5-hydroxy-2 (5H)-furanone: a potent bacterial mutagen in drinking water.

3-Chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (MX) was found to be a direct-acting mutagen in the Ames test for strains TA1535, TA1538, TA92, TA97, TA98, TA100 and TA102. The highest mutagenic response (approximately 13,000 revertants/nmol) was seen in strain TA100. The TA100 response was six- to tenfold higher than in TA98, TA97, and TA102, and 100- to 500-fold higher than in TA1535, TA92, and TA1538. The addition of a 9,000 x g supernatant fraction (S-9) from livers of polychlorinated biphenyl-treated rats, along with cofactors for NADPH generation, resulted in a 90% reduction in the TA100 mutagenicity. MX induced chromosomal aberrations in Chinese hamster ovary cells after 6-8 hr exposure without S-9 at a dose as low as 4 micrograms/ml, and after 2 hr exposure with S-9 at a dose of 75 micrograms/ml. The oral dose of MX lethal to 50% (LD50) in Swiss-Webster mice was determined to be 128 mg/kg. MX did not induce micronuclei in mouse bone marrow when administered by oral gavage at doses up to 70% of the LD50.

Human papillomavirus type 18 in conjunctival intraepithelial neoplasia.

Human papillomaviruses are oncogenic viruses that have been found in a variety of epithelial neoplasias. We sought to confirm their presence in conjunctival intraepithelial neoplasia. Five tumors were studied with a polymerase chain-reaction assay designed to detect the E6 region of human papillomavirus types 16 and 18. Human papillomavirus type-16 DNA was found in four of the five tumors, including two tumors that contained both type-16 and type-18 DNA. Viral DNA was not present in the fifth tumor.

Urine mutagenicity and biochemical effects of the drinking water mutagen, 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX), following repeated oral administration to mice and rats.

Mutagenicity analysis of urine from rats treated by oral gavage with MX at a dose of 64 mg/kg for 14 days revealed that only 0.3% of the administered compound was excreted in a genotoxically active form. At lower doses, mutagenicity was not detectable. No evidence of micronucleus induction in peripheral blood erythrocytes was observed in mice treated similarly. These findings indicate that MX is extensively detoxified in vivo and is unlikely to cause genetic damage in systemic tissues except at relatively high doses where detoxification pathways become saturated. In a separate experiment, significant depressions were observed in D-glucaric acid and thioether excretion and in levels of several liver enzymes involved in xenobiotic metabolism. The mechanism for these metabolic alterations and their relevance to the in vivo metabolism of the compound require further investigation.

Genotoxic activity of organic chemicals in drinking water.

The information summarized in this review provides substantial evidence for the widespread presence of genotoxins in drinking water. In many, if not most cases, the genotoxic activity can be directly attributed to the chlorination stage of drinking water treatment. The genotoxic activity appears to originate primarily from reactions of chlorine with humic substances in the source waters. Genotoxic activity in drinking water concentrates has been most frequently demonstrated using bacterial mutagenicity tests but results with mammalian cell assay systems are generally consistent with the findings from the bacterial assays. There is currently no evidence for genotoxic damage following in vivo exposures to animals. In some locations genotoxic contaminants of probable industrial and/or agricultural origin occur in the source waters and contribute substantially to the genotoxic activity of finished drinking waters. The method used for sample concentration can have an important bearing on study results. In particular, organic acids account for most of the mutagenicity of chlorinated drinking water, and their recovery from water requires a sample acidification step prior to extraction or XAD resin adsorption. Considerable work has been done to determine the identity of the compounds responsible for the mutagenicity of organic concentrates of drinking water. Recently, one class of acidic compounds, the chlorinated hydroxyfuranones, has been shown to be responsible for a major part of the mutagenic activity. Strategies for drinking water treatment that have been evaluated with respect to reduction of genotoxins in drinking water include granular activated carbon (GAC) filtration, chemical destruction, and the use of alternative means of treatment (i.e., ozone, chlorine dioxide, and monochloramine). GAC treatment has been found to be effective for removal of mutagens from drinking water even after the GAC is beyond its normal use for organic carbon removal. All disinfectant chemicals appear to have the capacity of forming mutagenic chemicals during water treatment. However, the levels of mutagenicity formed with the alternative disinfectants have been generally less than those seen with chlorine and, especially in the case of ozone, highly dependent on the source water.(ABSTRACT TRUNCATED AT 400 WORDS)

Formation of mutagens following chlorination of humic acid. A model for mutagen formation during drinking water treatment.

Aqueous chlorination of humic acids results in the formation of compounds with direct-acting mutagenic activity in the Ames/Salmonella plate assay for tester strains TA98, TA100, TA1535, TA1537 and TA1538. The addition of a rat-liver microsomal fraction (S9) plus cofactors causes a substantial decrease of activity, the extent of which is tester strain dependent. The non-chlorinated humic acids are not mutagenic either in the presence or absence of S9. Formation of mutagenic activity and of total organic halogen (TOX) is linearly related to humic concentration in the range of 0.2-1.6 mg/ml total organic carbon (TOC), and to chlorine concentration in the range of 0.1-1.0 chlorine equivalents per mole of carbon. The mutagenic activity is due predominantly to non-volatile compounds. Mutagenic activity is also detectable, after sample concentration by lyophilization, upon chlorination at a humic acid level of 0.02 mg/ml TOC. The specific mutagenic activities (per mg TOX), and also the degree of chlorine incorporation into humic acid, at 0.02 mg/ml TOC are similar to those present after chlorination at 1 mg/ml TOC. Production of mutagens is greatly dependent on the chlorination pH, with a pattern of decreasing mutagenic activity with increasing pH. This order of activity can be at least partially explained by the alkali liability of the compounds. Chlorination of commercial humic acids is proposed as a model for examination of mutagen formation during water chlorination.

Reduction of genotoxicity of a creosote-contaminated soil after fungal treatment determined by the Tradescantia-micronucleus test.

The fungal degradation of polyaromatic hydrocarbons (PAH) in a contaminated soil from a hazardous waste site was evaluated in a pilot-scale study. As some PAH are known to be mutagens, the Tradescantia-micronucleus test (TRAD-MCN) was selected to evaluate the genotoxicity of the soil before and after fungal treatment. The genotoxicity test was conducted with Tradescantia clone 4430. Cuttings were exposed for 30 h to different dilutions of soil extracts from the PAH-contaminated soil before and after fungal treatment. Soil extracts before fungal treatment exhibited a relatively strong genotoxic effect in the meiotic pollen mother cells even at a 1% concentration, and the highest concentration without significant effect was 0.25%. After fungal treatment, the depletion of selected PAH was associated with a reduction of the soil genotoxicity. The 2% concentration of the extract from the fungal-treated soil showed genotoxic effects comparable to the 1% soil extract without fungal treatment. These results indicate that the Trad-MCN test has a potential utility for evaluating the efficiency of bioremediation of genotoxic soil contaminants.

Activity of 1,1,1- and 1,1,3-trichloroacetones in a chromosomal aberration assay in CHO cells and the micronucleus and spermhead abnormality assays in mice.

1,1,1- and 1,1,3-trichloroacetones (TCA) result from the disinfection of municipal water supplies with chlorine, and are direct-acting mutagens in the Ames/Salmonella assay. The objective of this study was to further investigate the genotoxicity of these compounds in mammalian cells using an in vitro chromosomal aberration assay in Chinese hamster ovary (CHO) cells and the micronucleus and spermhead abnormality assays in mice. Both compounds induced significant increases in structural chromosomal aberrations in CHO cells in the presence and in the absence of rat S9 metabolic activation (MA). 1,1,3-TCA was more cytotoxic to CHO cells but 1,1,1-TCA resulted in a higher proportion of cells with aberrations. The clastogenic activities of both compounds were reduced in assays conducted with MA. Neither compound resulted in the induction of a significant increase in micronucleated polychromatic erythrocytes from bone marrow of Swiss-Webster mice when administered by oral gavage; nor were effects seen on the incidence of sperm with head-shape abnormalities, testis weight, or epididymal sperm concentration in B6C3F1 mice 21 or 35 days after treatment. These data indicate that the drinking water contaminants 1,1,1- and 1,1,3-TCA are clastogenic in vitro, but are not clastogenic to bone marrow cells in vivo, and do not adversely affect several indicators of testicular function in mice.

Studies on the potent bacterial mutagen, 3-chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone: aqueous stability, XAD recovery and analytical determination in drinking water and in chlorinated humic acid solutions.

3-Chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone (MX) was detected by gas chromatography/mass spectrometry in drinking water samples from 3 locations in the U.S.A., and also in a chlorinated humic acid solution. MX appears to account for a significant proportion of the mutagenicity of these samples, as measured in the Ames test using strain TA100 without metabolic activation. Studies on recovery of MX from spiked water samples by XAD-2/8 resin adsorption/acetone elution indicated that sample acidification prior to resin adsorption was essential to the effective recovery of MX. The stability of MX in aqueous solution was pH and temperature dependent. At 23 degrees C the order of stability, based on persistence of mutagenic activity was found to be: pH 2 greater than pH 4 greater than pH 8 greater than pH 6. The half-life at pH 8 and 23 degrees C was 4.6 days. One of the degradation products has been tentatively identified as 2-chloro-3-(dichloromethyl)-4-oxo-2-butenoic acid, an open form of MX which appears to be in the "E" configuration. Overall, these results suggest that MX is formed during water chlorination as a result of reaction of chlorine with humic substances, and that a substantial fraction of the MX formed is likely to persist throughout the distribution system.

Identification of mutagenic compounds formed during chlorination of humic acid.

Humic acid chlorination products are being studied in an effort to identify the chemicals responsible for the mutagenicity formed during water chlorination. In the present report, 19 chlorinated organic compounds have been identified and quantified in ether extracts of chlorinated humic acid solutions. 10 of these compounds, including a number of chlorinated propanones and chlorinated propenals, are direct-acting mutagens in the Salmonella/microsome mutagenicity assay. The position of the chlorine substituent has been found to be an important factor in the mutagenic activity of these two classes of compounds. The total mutagenicity of the compounds identified thus far, when tested either individually or as a composite, accounts for only 7-8% of the total TA100 mutagenicity, and less than 2% of the TA98 mutagenicity formed during humic acid chlorination. The addition of bromide to the humic acid chlorination reaction results in up to a 2-fold increase in the level of mutagenicity formed.

Mutagenicity of coal tar paints used in drinking water distribution systems.

The aim of this study was to evaluate the mutagenicity of coal tar paints used for coating drinking water tanks and pipes, as a preliminary screening for potential genotoxic hazards associated with leaching of mutagens into drinking water during water storage and distribution. To this end, the Salmonella/microsome assay was performed on different fractions of two paints. The fractions were obtained using different fractionation procedures (a sequential solvent extraction and an acid-base fractionation) for removing the presence of inhibitory components. Both fractionation procedures confirmed an extraordinarily high mutagenicity in both paints, with metabolic activation, much higher than the mutagenicity of the unfractionated paints. The acid-base fractionation was more time-consuming but gave higher mutagenicity recoveries and provided information as to the general nature of the genotoxic constituents, which were concentrated in the neutral fractions. On the other hand, the sequential solvent extraction by sonication was a shorter and simpler method and permitted to reveal the presence of direct-acting mutagens. It is concluded that the application of the Salmonella/microsome assay coupled with both fractionation methods may give complementary and confirmatory data on the genotoxic properties of these coal based paints, as a screening of the potential mutagenic/carcinogenic hazards derived from these materials used in drinking water distribution systems.

Venous velocity increase with a pneumatic foot compression garment.

Intermittent compression garments have been widely accepted for prophylaxis of deep venous thrombosis. They have broad applicability in both elective and emergent situations. Development of a new type of garment that acts to compress the plantar plexus of the foot provides a potential method of prophylaxis for patients with contraindications to the traditional calf- or thigh-high garments. Evaluation of the ability of the foot compression garment demonstrates a statistically significant increase in peak femoral venous velocity (40.6 cm/sec) as compared with the resting state (25.9 cm/sec). This increase in femoral venous velocity is comparable to that seen with single-cell compression socks. The authors conclude that the recently introduced foot garment produces increases in peak femoral venous velocity similar to those produced by existing garments and that use of the foot compression garment may provide deep venous thrombosis prophylaxis in patients who previously have not been candidates for a compression garment.

Advances in research on carcinogenic and genotoxic by-products of chlorine disinfection: chlorinated hydroxyfuranones and chlorinated acetic acids.

The introduction of chlorination of public drinking water in the early 1900's was a major factor in the fight against waterborne disease. In the 1970's it was discovered that chlorine reacted with naturally occurring organic constituents, particularly in surface water, to yield small quantities of chlorinated by-products such as chloroform for which regulations were subsequently developed. Since then there has been shown to be a substantial number of other by-products some in concentrations of a few nanograms/l and others similar concentrations to the THM. Of particular note are the potent bacterial mutagen MX and the chlorinated acetic acids. Current research into the significance of these for man is described and the key issues for risk assessment are identified.