微塑料对淡水鱼生长的影响研究

微塑料通常指尺寸小于5 mm的塑料碎片、薄膜或颗粒。为填补微塑料在淡水水域生态效应的空白,选择大小、生长情况相似的鲫鱼进行分组实验,分别暴露在不同浓度的微塑料水体中,相同条件下养殖60 d后,测量、计算其体长及体重的增长量。利用SPSS软件对实验结果进行统计分析,探讨各组鲫鱼生长的差异性。结果表明,微塑料浓度大于0.12 g/L时能极显著抑制淡水鱼体重的增长;微塑料的浓度大于0.18 g/L时能显著抑制淡水鱼体长的增长。     

光照周期对叙利亚地鼠生长发育和繁殖的影响

对离乳雄性叙利亚地鼠（Ｍｅｓｏｃｒｉｃｅｔｕｓａｕｒａｔｕｓ）和雌性叙利亚地鼠各３０只分别给以长光照（１６Ｌ：８Ｄ）、中光照（１２Ｌ：１２Ｄ）和短光照（８Ｌ：１６Ｄ）三种光周期处理,研究光周期对叙利亚地鼠生长发育和繁殖的影响。１３周龄时,短光照处理组雄性地鼠的体重显著（Ｐ＜０．０５）高于长光照和中光照组的体重;雌性地鼠９周龄时长光照组的体重显著（Ｐ＜０．０１）高于另外两个处理组的体重,较高的日食量可能是长光照组具有较大体重的原因之一,雄性地鼠的睾丸、副睾和肾上腺重量及雌性地鼠的卵巢、子宫和肾上腺重量表现了随着光照时间的延长而递增的趋势。长光照条件有利于雌性地鼠的正常发情和繁殖。每天１６ｈ的光照对繁殖地鼠是比较适宜的。     

4种饮用水对小鼠固有免疫及T细胞亚群的影响

为了探讨4种饮用水对小鼠固有免疫及T细胞亚群的影响,本研究将ICR小鼠按体重随机分为4组,分别为纯水组、过滤水组、自来水组和矿泉仿生水组,每组20只,雌雄各半,共4批。各组小鼠自由饮水摄食90 d,分别进行碳廓清实验和腹腔巨噬细胞吞噬鸡红细胞实验,应用LDH法检测NK细胞活性,同时测定胸腺和脾脏指数,应用血细胞分析仪检测外周血白细胞和中性粒细胞计数,采用流式细胞术检测T细胞亚群CD4+和CD8+百分比,并计算CD4+/CD8+比值。研究显示,各组小鼠的体重增长、胸腺指数、脾脏指数、吞噬指数α、外周血白细胞计数、中性粒细胞计数、小鼠脾细胞表面标志物CD4+百分比和CD8+百分比差异均无统计学意义(p0.05);过滤水组腹腔巨噬细胞吞噬指数、NK细胞活性高于纯水组和矿泉仿生水组(p0.05);自来水组NK细胞活性高于过滤水组、纯水组和矿化水组(p0.05);过滤水组吞噬率高于矿泉仿生水组(p0.05);自来水组、过滤水组、矿泉仿生水组的小鼠CD4+/CD8+比值均高于纯水组(p0.05);其余各组间无统计学差异。本研究表明,长期饮用过滤水对小鼠固有免疫有一定的促进作用,此外,过滤水和矿泉仿生水对小鼠T淋巴细胞亚群CD4+/CD8+比值有提高作用。     

超微戊己丸对小鼠胃内微生物的动态影响研究

目的探讨超微戊己丸对胃内微生物的影响及确定超微戊己丸的最佳超微剂量。方法将动物分为正常组、戊己丸传统组、超微全量、1／2量、1／4量、1／8量组,分别灌胃给药,每隔2d取各组小鼠胃内容物做微生物数量分析。结果戊己丸对胃内乳酸菌影响不大（P〉0．05）;戊己丸对胃内细菌有一定的抑制作用,其中超微全量、1／2量、1／4量组在5、7和9d细菌数显著低于正常组（P〈0．05）;戊己丸对大肠埃希菌具有抑制作用,超微全量、1／2量组、1／4量组大肠埃希菌数相对于正常组显著降低（P〈0．05）。结论超微戊己丸能够明显抑制胃内条件致病菌的生长,重新平衡胃内微生态,达到“驱邪”的目的。在无感染状态下,超微戊己丸1／4剂量对胃微生态系统能达到超微全量的调控效果。     

原代地鼠肾细胞及狂犬病毒不同培养方式的研究

目的通过比较原代地鼠肾细胞在转瓶、微载体、细胞工厂的3种培养方式的培养效果,为原代地鼠肾细胞选择一种易扩大规模、培养高质量细胞的培养方式,进而提高狂犬病毒的产量。方法消化取得的细胞悬液分别在转瓶、微载体、细胞工厂中培养,通过显微镜观察细胞形态、计数等结果比对培养的差别。结果细胞工厂可以很好地培养原代地鼠肾细胞和狂犬病毒;而细胞在微载体上贴附性差,生长不好。结论实验结果表明细胞工厂可以取代转瓶,用于大规模培养原代地鼠肾细胞扩大狂犬病毒的产量。     

三株光合细菌的毒性试验研究

以昆明小白鼠为实验动物,对类球红细菌Z1、沼泽红假单胞菌Z2及光合细菌分离株C2采用急性毒性试验、骨髓细胞微核试验和精子畸形试验进行安全性评定。结果表明,急性毒性试验:实验组小白鼠的一般状况、器官含水量、器官系数及血常规检查,与对照组差异均无显著性(P>0.05);骨髓细胞微核试验和精子畸形试验实验组与阴性对照组(生理盐水)差异均无显著性(P>0.05),与阳性对照组(环磷酰胺40 mg/kg)比较,骨髓细胞微核试验差异有极显著性(P<0.01),精子畸形率试验差异有显著性(P<0.05)。以上结果说明,三株光合细菌均不具有毒性。     

封闭群五指山小型猪主要脏器重量与体重的相关性分析

目的测定封闭群五指山小型猪主要脏器重量和脏器系数,对脏器重量与体重的相关性进行分析,并计算出相应的直线回归方程和多元回归方程。方法实验选用6-10月龄普通级封闭群五指山小型猪30头（其中♂16头、♀14头）,分别测定体重和7个主要脏器重量,计算脏器系数,通过SAS软件进行脏器系数的性别间比较和各脏器重与体重间的相关与回归分析。结果性别间比较,小型猪仅有心脏的脏器系数差异有显著性（P〈0.05）。除公猪的胃脏和母猪的肺脏外,所测脏器重量与体重间均有明显的正相关线性关系;多因素分析显示公猪的肝脏和肾脏,母猪的心脏、肝脏和肾脏对各自体重有影响。结论封闭群五指山小型猪主要脏器系数性别间差异较小,其体重与某些脏器重量存在一定的线性关系。     

人参花食用安全性研究

目的:对人参花食用安全性进行毒理学评价.方法:采用大鼠经口急性毒性试验、遗传毒性试验(Ames试验、小鼠骨髓细胞微核试验、小鼠精子畸形试验)、大鼠30 d喂养试验.结果:雌、雄大鼠经口最大耐受剂量(MTD)均大于17.4 g/kg·bw.3项遗传毒性试验结果均为阴性.在大鼠30 d喂养试验中,6.0 g/kg·bw,3.0 g/kg·bw及1.5g/kg· bw 3个剂量组的实验动物均生长发育良好,体重、摄食量、饮水量、血液学、血液生化学、脏器系数及病理组织学相关指标均未见异常变化.结论:人参花属于实际无毒物,未见遗传毒性,长期服用是安全的.     

大鼠对乙酰柠檬酸三丁酯的安全耐受值测定

按体重将80只SD大鼠随机分为对照组,低、中、高剂量组,每组雌雄各10只。持续静脉给药观察4周后处死,观察体重、脏器系数、血液及生化指标以及病理切片。与对照组比较,各组大鼠体重无显著性差异(p0.05);高剂量组雄鼠脑、肺、胸腺脏器系数差异显著(p0.05),雌鼠肝、卵巢脏器系数有差异显著(p0.05);中高剂量组雌、雄鼠部分血液及生化指标差异显著(p0.05);病理切片观察,各组大鼠肝脏均出现脂变,中高剂量组大鼠附睾、大肠出现炎症,其他器官未见明显病理改变。中高剂量组ATBC溶液对大鼠有一定毒性,参考低剂量组给药浓度,大鼠对其安全剂量为500 mg/kg体重/d。     

海水酸化及升温对刺参生长及能量收支的影响

以东亚浅海生态系统中的关键种——刺参(Apostichopus japonicus)为实验对象,研究了CO₂驱动的海水酸化及升温对其生长及能量收支的影响。实验设置对照组(大连近海水温, pCO₂ 400μatm)、升温组(大连近海水温+3℃, pCO₂ 400μatm)、酸化组(大连近海水温, pCO₂ 1100μatm)和酸化升温组(大连近海水温+3℃,pCO₂ 1100μatm)。结果表明:与对照组相比,温度升高3℃对刺参的生长无显著影响;酸化组刺参的特定生长率最低,较对照组降低0.19%/d,个体体重的变异系数最大;酸化升温组刺参的终末体重和特定生长率与对照组相较无显著差异,但其摄食率和排粪率均显著高于对照组。升温组和酸化组的刺参能量的分配模式与对照组相比未发生明显改变,但酸化升温组刺参的能量分配模式发生显著变化,其粪便能所占摄食能的比例显著升高。研究表明,海水酸化抑制了刺参的生长但未改变其能量的分配,生长的降低主要取决于摄食减少;而海水酸化与温度升高的共同作用可能会通过...     

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.     

Effects of long term low dose acrylamide exposure on rat bone marrow polychromatic erythrocytes

Abstract

I investigated whether long term low dose exposure to acrylamide increased micronucleus frequency in rat bone marrow polychromatic erythrocytes (PCEs). Twenty-five male and 25 female Wistar rats were used. Animals of each sex were segregated into two treatment groups and one control group. Each treatment group consisted of ten animals and each control group consisted of five animals. Acrylamide, 2 or 5 mg/kg/day, was administered to the treatment groups in their drinking water for 90 days. Twenty-four hours after the last treatment, bone marrow samples were obtained and analyzed for the frequency of micronucleated polychromatic erythrocytes (MNPCEs). The cytotoxic effect of acrylamide on bone marrow also was tested by assessing the polychromatic erythrocyte/normochromatic erythrocyte (PCE/NCE) ratio. Both doses of acrylamide significantly increased the frequency of MNPCEs in both male and female rats. Acrylamide also decreased the PCE/NCE ratio in both sexes compared to the control group. My study showed that chronic low dose exposure to acrylamide increased the formation of micronuclei in PCEs of male and female rat bone marrow.     

1-Methyl-2-pyrrolidinone (NMP) does not induce structural and numerical chromosomal aberrations in vivo

1-Methyl-2-pyrrolidinone induces aneuploidy in yeast, but only under special treatment conditions. Other genotoxic effects have not been found in vitro, and in vivo no data are available in the literature. Therefore, NMP was investigated in the mouse micronucleus test and the Chinese hamster bone marrow test for structural and numerical chromosomal aberrations. These tests can detect both types of alterations as demonstrated by appropriate positive control substances (cyclophosphamide, vincristine sulfate and benomyl). NMP at single oral doses up to 3800 mg/kg body weight (∼ 80% of the LD₅₀) did not lead to an increase either in micronucleated erythrocytes or in structural or numerical chromosomal aberrations when bone marrow was sampled 16, 24 and 48 h after treatment in the micronucleus test or after 24 and 48 h for karyotype analysis.     

Genotoxicity of drinking water from three Korean cities

Organic content of drinking tap water from Seoul, Taejon, and Suwon was extracted with an XAD-2 resin column and organic solvents. Four doses of the extract equivalent to 4, 2, 1, and 0.5 l water were tested for mutagenicity in Salmonella typhimurium strains TA98 and TA100 in the presence and absence of S9 mix. The organic extracts of the water from all three cities were mutagenic in TA 98 without S9 mix and in TA 100 with and without S9 mix. The highest number of revertants per plate was found in the absence of S9 mix. Three doses of the extract (equivalent to 22, 11, and 3.7 l water) were also tested in the bone marrow micronucleus test using BDF1 mice. At the highest dose, a significant increase of the micronucleus frequency was observed. The time required to be on the effect, however, varied with the source of the water. Our results indicate that the drinking tap waters from the three cities were genotoxic clearly in the bacterial test and also in the in vivo assay with mice. As we found no genotoxicity of the source water as seen in a previous study, it is likely that the chlorination process leads to the genotoxicity of the tap water.     

Oral chromium(VI) does not affect the frequency of micronuclei in hematopoietic cells of adult mice and of transplacentally exposed fetuses

Chromium(VI) compounds are genotoxic in a variety of cellular systems. Their potential carcinogenicity is affected by toxicokinetic patterns restricting bioavailability to certain targets, and by metabolic pathways affecting interaction of chromate-derived reactive species with DNA. Epidemiological data indicate that chromium(VI) can be carcinogenic to the human respiratory tract following inhalation at doses that are only achieved in certain occupational settings. However, concern has been raised that adverse effects may also result from oral intake. In order to further explore this issue, we performed studies in BDF1 and Swiss mice of both genders and various age. Sodium dichromate dihydrate and potassium dichromate were administered either with the drinking water, up to a concentration of 500 mg chromium(VI)/l for up to 210 consecutive days, or in a single intragastric dose of 17.7 mg/kg body weight. Under these conditions, no increase of the micronucleus frequency was observed in either bone marrow or peripheral blood erythrocytes. Conversely, the same compounds induced a clastogenic damage following intraperitoneal injection, which by-passes detoxification mechanisms. In addition, due to the hypothesis that susceptibility may be increased during the period of embryogenesis, we treated pregnant mice, up to a concentration of 10 mg chromium(VI)/l drinking water. There was no effect on the numbers of fetuses/dam and on body weight of fetuses. Again, no toxic or genotoxic effect was observed either in bone marrow of pregnant mice or in liver and peripheral blood of their fetuses. Thus, even at doses that largely exceed drinking water standards (up to 10,000 times) or by massive intragastric administration, chromium(VI) is not genotoxic to hematopoietic cells of either adult mice or transplacentally exposed fetuses. These conclusions are consistent with the poor toxicity and lack of carcinogenicity of oral chromium(VI), and are mechanistically explained by the high efficiency of chromium(VI) detoxification processes in the gastrointestinal tract.     

Rapid method for improving slide quality in the bone marrow micronucleus assay; an adapted cellulose column procedure

Micronuclei are routinely scored in anucleate erythrocytes in bone marrow smears stained with acridine orange. Intense fluorescence from the many nucleated cells in the preparations can interfere with micronucleus detection and cause fatigue in the reader. A method for removing nucleated cells by filtering bone marrow through cellulose packed in syringes was developed by Romagna some ten years ago, but has not been used routinely because of the excessive time needed to prepare columns. We have modified the method very simply by filling chromatography columns by pipet with a cellulose suspension. We show here that column filtration of bone marrow does not affect the numbers of micronucleated polychromatic erythrocytes (MN-PCEs) scored from mice treated with the chromosome breaking agents mitomycin C and cyclophosphamide, or the aneuploidy-inducing spindle poisons, colchicine and vinblastine. The extra preparation time is only about half an hour for a full scale micronucleus assay, and results in better slides and faster scoring.     

Oral chromium(VI) does not affect the frequency of micronuclei in hematopoietic cells of adult mice and of transplacentally exposed fetuses

Chromium(VI) compounds are genotoxic in a variety of cellular systems. Their potential carcinogenicity is affected by toxicokinetic patterns restricting bioavailability to certain targets, and by metabolic pathways affecting interaction of chromate-derived reactive species with DNA. Epidemiological data indicate that chromium(VI) can be carcinogenic to the human respiratory tract following inhalation at doses that are only achieved in certain occupational settings. However, concern has been raised that adverse effects may also result from oral intake. In order to further explore this issue, we performed studies in BDF1 and Swiss mice of both genders and various age. Sodium dichromate dihydrate and potassium dichromate were administered either with the drinking water, up to a concentration of 500 mg chromium(VI)/l for up to 210 consecutive days, or in a single intragastric dose of 17.7 mg/kg body weight. Under these conditions, no increase of the micronucleus frequency was observed in either bone marrow or peripheral blood erythrocytes. Conversely, the same compounds induced a clastogenic damage following intraperitoneal injection, which by-passes detoxification mechanisms. In addition, due to the hypothesis that susceptibility may be increased during the period of embryogenesis, we treated pregnant mice, up to a concentration of 10mg chromium(VI)/l drinking water. There was no effect on the numbers of fetuses/dam and on body weight of fetuses. Again, no toxic or genotoxic effect was observed either in bone marrow of pregnant mice or in liver and peripheral blood of their fetuses. Thus, even at doses that largely exceed drinking water standards (up to 10,000 times) or by massive intragastric administration, chromium(VI) is not genotoxic to hematopoietic cells of either adult mice or transplacentally exposed fetuses. These conclusions are consistent with the poor toxicity and lack of carcinogenicity of oral chromium(VI), and are mechanistically explained by the high efficiency of chromium(VI) detoxification processes in the gastrointestinal tract.     

Studies on the in vivo and in vitro mutagenicity and the lipid peroxidation of chlorinated surface (drinking) water in rats and metabolically competent human cells.

In the present study, DNA damaging and mutagenic effects of chlorinated drinking water (CDW) extracts obtained from polluted raw water resources were examined in metabolically competent human Hep G2 hepatoma cells using the in vitro micronucleus assay and the single cell gel electrophoresis (SCGE, comet assay). Additionally, the in vivo induction of micronuclei (MN) was studied in polychromatic erythrocytes (PCEs) derived from bone marrow of CDW-treated Wistar rats. Furthermore, we examined the influence of CDW on the lipid peroxidation (LpO) in blood, liver, kidney and testicle of rats. The results demonstrated significant increases of micronucleated PCEs in the bone marrow of rats fed with relatively low CDW doses (33.3ml/kg body weight per day). Similar effects, i.e. increases of MN frequencies, were found in Hep G2 hepatoma cells after CDW treatment (41 MN/1000 binucleated cells (BNCs) for 167ml CDW) in comparison to the vehicle control (24 MN/1000 BNC). Additionally, DNA damages caused by CDW were observed in the comet assay. As a product of LpO, the levels of malondialdehyde (MDA) were significantly enhanced almost in all animals and organs tested after CDW treatment. In livers and serum of rats dose-dependent increases of MDA were observed. The data indicated that extracts from CDW obtained from polluted raw water were able to cause oxidative damages and to induce various biological effects in mammalian cells in vivo and in vitro, i.e. clastogenicity and/or aneugenicity, DNA strand breaks and/or alkali-labile damages. The consistency of the results among the various biological systems and endpoints led to the conclusion that the consumption of chlorinated drinking water obtained from polluted raw water may enhance the body burden with mutagenic and/or carcinogenic substances and therefore, means a potential genetic hazard for human health.     

Studies on the in vivo and in vitro mutagenicity and the lipid peroxidation of chlorinated surface (drinking) water in rats and metabolically competent human cells

In the present study, DNA damaging and mutagenic effects of chlorinated drinking water (CDW) extracts obtained from polluted raw water resources were examined in metabolically competent human Hep G2 hepatoma cells using the in vitro micronucleus assay and the single cell gel electrophoresis (SCGE, comet assay). Additionally, the in vivo induction of micronuclei (MN) was studied in polychromatic erythrocytes (PCEs) derived from bone marrow of CDW-treated Wistar rats. Furthermore, we examined the influence of CDW on the lipid peroxidation (LpO) in blood, liver, kidney and testicle of rats. The results demonstrated significant increases of micronucleated PCEs in the bone marrow of rats fed with relatively low CDW doses (33.3 ml/kg body weight per day). Similar effects, i.e. increases of MN frequencies, were found in Hep G2 hepatoma cells after CDW treatment (41 MN/1000 binucleated cells (BNCs) for 167 ml CDW) in comparison to the vehicle control (24 MN/1000 BNC). Additionally, DNA damages caused by CDW were observed in the comet assay. As a product of LpO, the levels of malondialdehyde (MDA) were significantly enhanced almost in all animals and organs tested after CDW treatment. In livers and serum of rats dose-dependent increases of MDA were observed. The data indicated that extracts from CDW obtained from polluted raw water were able to cause oxidative damages and to induce various biological effects in mammalian cells in vivo and in vitro, i.e. clastogenicity and/or aneugenicity, DNA strand breaks and/or alkali-labile damages. The consistency of the results among the various biological systems and endpoints led to the conclusion that the consumption of chlorinated drinking water obtained from polluted raw water may enhance the body burden with mutagenic and/or carcinogenic substances and therefore, means a potential genetic hazard for human health.     

Effect of food and water deprivation on the parameters of the mouse bone marrow micronucleus test

This study reports the influence of acute starvation on spontaneous and cyclophosphamide (CP) induced micronucleus (MN) frequencies in the bone marrow polychromatic erythrocytes (PCE) of CD-1 mice. Groups of mice (5/sex) were deprived of either food alone or food and water for 0, 24, 48 and 72 h prior to sacrifice. Although there was no evidence of a significant increase in MN-PCE frequencies among the starved groups, a significant depressant effect of starvation on erythropoietic activity was observed. Peak levels of CP-induced (40 mg/kg b.w.) MN-PCE's appeared later in male mice deprived of food and water after treatment compared to mice given food and water ad libitum. The results indicate that starvation is detrimental to bone marrow erythropoiesis and that starvation may alter the response of mice to clastogens.