Chemically induced sperm granuloma in rat.
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Toxicological effect of 3-chloro-1,2-propanediol on rats were studied to provide scientific basis for assessing the effect of Chloropropanols on human health. 170 SD rats were divided randomly into 8 groups and the dose of 0, 0.25, 0.5, 1.0, 2.0, 4.0, 8.0, 16.0 mg/kg 3-chloro-1,2-propanediol were given to rats for 90 days by gavages per day, respectively. The weight and food efficiency, hematology and clinical chemistry, NAG, GGT and total protein in urine, sperm number, sperm survive rate and sperm aberration rate, the LDH and LDH-X activity in testis, rate of organ/weight and histopathological analysis were measured. The results showed that different dose of 3-chloro-1,2-propanediol did not has adverse effect on body weight, food efficiency, Hb, red cell, white cell, serum AST, ALT, creatine, ALP, LDH, total protein and albumin, urine GGT and total protein, LDH activity in testis. At the dose of 4.0, 8.0 and 16.0 mg/kg group, the activity of NAG in urine and the rate of kidney/weight was significantly increased compared with negative control groups; the pathological changes in kidney were observed in the same groups, and the sperm number was also significantly decreased. At the dose of 8.0 and 16.0 mg/kg group, sperm survive rate and the X-LDH activity were significantly decreased and pathological changes were also observed in testis and caudal epididymis. It was concluded that the activity of NAG in urine and sperm number is the sensitive biological effective marker. Because urine is a kind of convenient available biological material, NAG activity in urine is a good biological effective marker for assessing effect of Chloropropanols on health. If the NAG activity can be used as sensitive marker for assessment on human health need to be tested further in human study.
OBJECTIVE: To explore the absorption, distribution and excretion of 3-Chloro-1,2-propandiol (3-MCPD) in healthy male SD rats after oral administration. METHODS: 3-MCPD was administrated with a single oral dosage of 75 mg/kg BW to each rat. Samples of blood, tissues (including liver, kidney, brain and testicle) and excreta were then collected, and analyzed by the GC-MS method to determine 3-MCPD concentrations. The reported value is the mean value of three rats. RESULTS: At 2 h after the administration, 3-MCPD concentrations in blood, testicle and kidney were (67.46 +/- 7.72), (78.37 +/- 5.15) and (56.21 +/- 3.64) microg/g, respectively. At 24 h, however, the corresponding values changed to (1.07 +/- 0.97) microg/g, (49.43 +/- 28.18) microg/g and (11.41 +/- 2.55) microg/g. During the 24-hour period, 9.74 +/- 3.05% of the given parent compound was excreted in urine, whereas 0.56 +/- 0.22% and 0.28 +/- 0.03% were excreted in feces and bile, respectively, which implies that kidney is a major organ for excretion 3-MCPD. CONCLUSIONS: 3-MCPD was quickly absorbed through the alimentary tract and quickly distributed into a number of tissues, and then accumulated in the target organs, especially in the testicle. The excretion of the parent compound was largely through the kidney. It was inferred that 3-MCPD was mainly metabolized in the liver.
OBJECTIVE: The AOAC 2000.01 method was validated in order to establish Chinese national standard for determination of 3-monochloropropane-1,2-diol (3-MCPD) in foods. METHODS: Using gas chromatography with mass spectrometric detection and incorporating the using of a deuterated internal standard of 3-MCPD, the recovery test were carried out by fortified 3-MCPD standard in soy sauces, flour and salami. RESULTS: Linearity, precision and recovery were complied with the method AOAC2000.01 that was adopted First Action by AOAC International. The limit of detection was 0.005 mg/kg. CONCLUSION: AOAC2000.01 was adopted as the Chinese national standard GB/T 5009.191.
Six proficiency tests have now been completed in an ongoing program of the UK Food Analysis Performance Assessment Scheme (FAPAS) for the analysis of acrylamide in a range of food matrixes. Homogeneous test material samples were requested by laboratories throughout the world, with 29 to 45 submitting results for each test. Results were analyzed by appropriate statistical procedures, and z-scores were awarded for reported values. In the absence of both legislation and collaborative trial data, the target standard deviation was derived from the Horwitz equation, although it is acknowledged that there is a need to establish a "fit for purpose" target standard deviation specifically for acrylamide analysis. Participants were encouraged to use the analytical method routinely used in their own laboratory and to provide details of their procedure. Close examination of the data submitted indicates that performance is generally acceptable in terms of accuracy. There is no significant difference between results submitted by gas chromatography and liquid chromatography (GC and LC) methods, and no method dependency on the use of internal standards or sample size. However, choice of extraction solvent may be important, with indications that plain water is an acceptable extraction method. There is evidence from the most recent test that direct (underivatized) GC methodology may present problems, but more data are required and this aspect will be monitored in the continuing proficiency testing program.
A method for the determination of the residual epichlorohydrin and sym-dichloroisopropyl alcohol in cationic etherified reagent by gas chromatography has been established. Methyl benzoate, which has high extraction efficiency for the two components, was used as extractant. With an HP-5 capillary column, the two components were baseline separated and they eluted before the extractant. The linear ranges achieved were 5 - 590 mg/kg for epichlorohydrin and 21 - 480 mg/kg for sym-dichloroisopropyl alcohol. The limits of detection were 1.2 mg/kg for epichlorohydrin and 2.2 mg/kg for sym-dichloroisopropyl alcohol. Recoveries for epichlorohydrin were 95.93% - 103.42% with relative standard deviations of 2.4% - 10.6% and those for sym-dichloroisopropyl alcohol were 98.54% - 107.40% with relative standard deviations of 6.6% -11.1%. The method is simple, fast, and convenient.
An interlaboratory study was performed to evaluate the effectiveness of a headspace gas chromatography (GC) method for the determination of 1,3-dichloro-propan-2-ol (1,3-DCP) in soy sauce and related products at levels above 5 ng/g. The test portion is mixed with an internal standard (d5-1,3-DCP) and ammonium sulfate in a sealed headspace vial. After achieving equilibrium, the headspace is sampled either by gas-tight syringe or solid-phase microextraction (SPME) and analyzed by GC with mass spectrometric detection. 1,3-DCP is detected in the selected-ion mode (monitoring m/z 79 and 81 for 1,3-DCP and m/z 82 for the deuterated internal standard) and quantified by measurement against standards. Test materials comprising soy, dark soy, mushroom soy, and teriyaki sauces, both spiked and naturally contaminated, were sent to 9 laboratories in Europe, Japan, and the United States; of these, 5 used SPME and 4 used syringe headspace analysis. Test portions were spiked at 5.0, 10.0, 20.0, 100.0, and 500.0 ng/g. The average recovery for spiked blank samples was 108% (ranging from 96-130%). Based on results for spiked samples (blind pairs at 5, 10, 20, 100, and 500 ng/g) as well as a naturally contaminated sample (split-level pair at 27 and 29 ng/g), the relative standard deviation for repeatability (RSDr) ranged from 2.9-23.2%. The relative standard deviation for reproducibility (RSDR) ranged from 20.9-35.3%, and HorRat values of between 1.0 and 1.6 were obtained.
Glycerol chlorohydrines, such as 3-chloro-1,2-propanediol and 1,3-dichloro-2-propanol, are present in commercial protein hydrolysates used for human nutrition. These compounds are genotoxic and 1,3-dichloro-2-propanol induced tumors in rats. Now it is reported that both compounds are active at inducing malignant transformation of mouse fibroblasts. Therefore, the carcinogenic risk to humans by exposure to these compounds contained in food is of concern. The investigation of the in vivo carcinogenic potential of 3-chloro-1,2-propanediol is urgently required to further evaluate the carcinogenic risk to exposed consumers.
Chemicals can interfere with hormonal control of the male reproductive tract and/or directly alter male reproductive tract function. A review is presented of those chemicals developed and tested as male contraceptive agents which have a direct effect on the male reproductive tract with minimal disturbance of the hormonal milieu. Such chemicals can have one or more sites of action: 1) the testis, disturbing spermatogenesis; 2) the epididymis, altering sperm maturation; 3) the vas deferens, affecting sperm transport; and 4) the accessory sex glands, entering the ejaculate and changing the functional activity of the spermatozoa. Examples of each mode of action are presented.
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A biochemical and histochemical study was carried out on the effects of low doses of alpha chlorohydrin on the lipid metabolism of the rat testis and epididymis. Administration of alpha chlorohydrin in low doses (6.5 mg/kg for 9 days) to Wistar strain rats caused an elevation of lipid levels in the testis and epididymis. Actually, an increase in the neutral fat occurred with a corresponding decrease in the phospholipids after treatment with alpha chlorohydrin. We suggest that the rat's total lipid, total cholesterol, cholesterol esters, and triglycerides were increased at the cost of phospholipids. The altered levels of lipid fractions were due to the increased activity of glycerol phosphate dehydrogenase and to the decreased activities of nonspecific esterase and lipase after treatment with the drug. These alterations of lipid metabolism, which were regulated through their enzyme systems, strongly reflect the damage to the metabolism of the testis and epididymis after treatment with low doses of alpha chlorohydrin, although there was no histological damage at this dose level.
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During their development, spermatozoa are continually bathed in fluid provided by epithelial secretions of the seminiferous tubule and the epididymal duct. This fluid or microenvironment is probably very important for spermatozoal maturation and survival. Micropuncture and microanalytic studies have revealed the occurrence of several biochemical changes of this specialized microenvironment along the epididymal duct; these changes seem to be linked to sperm maturation. The interactions between maturing spermatozoa and their microenvironment must be understood before interference in sperm maturation through intervention of the formation of the microenvironment is possible. Several compounds have been shown to interfere in spermatozoal maturation in the epididymis although their use as male contraceptives requires further investigation.
Fourteen chemicals of varied uses were tested for carcinogenicity by oral administration in male and female Charles River CD rats. Under the conditions of the tests, propane sultone, propylene imine, and ethylenethiourea, in addition to the positive control N-2-fluorenylacetamide, were carcinogenic. Avadex, bis(2-chloroethyl) ether, the potassium salt of bis(2-hydroxyethyl) dithiocarbamic acid, ethylene carbonate, and semicarbazide hydrochloride were not carcinogenic under the test conditions. Dithiooxamide, glycerol alpha-monochlorohydrin, and thiosemicarbazide gave somewhat ambiguous results, though administered at high enough dose levels to be toxic. An inadequate number of animals survived treatments with sodium azide, sodium bisulfide, and vinylene carbonate, or the animals may not have received sufficiently high doses of the test chemicals to provide maximum test sensitivity. However, there were no indications that these three chemicals were carcinogenic under the test conditions.