Toxicological Evaluation of Chicken-Breast Meat with High-Dose Irradiation

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鸡组织中地克珠利和妥曲珠利残留HPLC检测方法的建立

鸡组织中地克珠利和妥曲珠利残留HPLC检测方法的建立

鸡组织中地克珠利和妥曲珠利残留HPLC检测方法的建立作者:施祖灏, 朱良强, 卢运站, 祁克宗, 彭开松, SHI Zu-hao, ZHU Liang-qiang, LU Yun-zhan, QI Ke-zong, PENG Kai-song作者单位:施祖灏,卢运站,祁克宗,彭开松,SHI Zu-hao,LU Yun-zhan,QI Ke-zong,PENG Kai-song(安徽农业大学动物科技学院,安徽,合肥,230036), 朱良强,ZHU Liang-qiang(安徽省兽医工作站,安徽,合肥,230022)刊名:中国兽医学报英文刊名:CHINESE JOURNAL OF VETERINARY SCIENCE年,卷(期):2009,29(1)被引用次数:5次1.陈杖榴兽医药理学 20022.EMEA Veterinary Medicines Evaluation Unit:Diclazuril(Extension to all ruminants and porcine species),Summary Report (1,2) 20043.EMEA Veterinary Medicines Evaluation Unit:Tohrazuril,Summary Report(1) 20044.JECFA Toxicological Evaluation of Certain Veterinary Drug Residues in Food:Diclazuril,WHO Food Additives Series 36 19965.JECFA Toxicological Evaluation of Certain Veterinary Drug Residues in Food:Diclazuril,WHO Food Additives Series 41 19986.动物性食品中兽药最高残留限量 20027.Fontaine A;Haustraete K Liquid chromatographic determination of diclazuril in permix and supplemented feed:interlaboratory study 1994(06)8.Kanda M;Ushiyama K;Igusa K Simple determination of residual antieoceidial drugs (dielazuril and nicarbazin) in chicken tissues by HPLC[外文期刊] 2003(02)9.王学红;梁剑平;华兰英妥曲珠利在鸡组织内的残留研究[期刊论文]-中兽医医药杂志 2005(01)1.文丽.方炳虎.刘颖地克珠利在鸡组织的残留检测[期刊论文]-广东畜牧兽医科技2007,32(4)2.祁克宗.施祖灏.彭开松.涂健.朱良强.陈玎玎.Qi Ke-Zong.Shi Zu-Hao.Peng Kai-Song.Tu Jian.Zhu Liang-Qiang.Chen Ding-Ding基质固相分散萃取-高效液相色谱法检测鸡组织中均三嗪类药物残留[期刊论文]-分析化学2007,35(11)3.施祖灏.葛庆联.陆俊贤.刘学贤.龚建森.朱良强.祁克宗.陈玎玎.彭开松.SHI Zuhao.GE Qinglian.LU Junxian. LIU Xuexian.GONG Jiansen.ZHU Liangqiang.QI Kezong.CHEN Dingding.PENG Kaisong同时检测2种均三嗪类抗球虫药物残留的样品前处理方法的比较[期刊论文]-色谱2009,27(3)4.董静.宫小明.张立.孙军.王洪涛.Dong Jing.Gong Xiao-ming.Zhang Li.Sun Jun.Wang Hong-tao QuEChERS-高效液相色谱法同时检测动物组织中的克球酚,地克珠利和磺胺类药物残留量[期刊论文]-中国卫生检验杂志2008,18(1)5.张涛.张丽芳.江善祥.薛飞群液相色谱-串联质谱法测定鸡蛋中地克珠利的残留量[期刊论文]-安徽农业科学2009,37(14)6.农业部畜牧兽医局动物源食品中乙氧酰胺苯甲酯残留检测方法——高效液相色谱法[期刊论文]-中国兽药杂志2002,36(10)7.张涛.张丽芳.薛飞群.Zhang Tao.Zhang Lifang.Xue Feiqun液相色谱-串联质谱法测定鸡肝脏和肌肉中地克珠利残留量[期刊论文]-中国农学通报2010,26(15)8.李永芳.陈湘宏.Li Yongfang.Chen Xianghong人血浆中病毒唑浓度的高效液相色谱测定法建立[期刊论文]-青海医学院学报2009,30(4)9.施祖灏.陆俊贤.葛庆联.龚建森.刘学贤.祁克宗.SHI Zu-hao.LU Jun-xian.GE Qing-lian.GONG Jian-sen.LIU Xue-xian.QI Ke-zong高效毛细管电泳法同时检测地克珠利和妥曲珠利的含量[期刊论文]-中国兽药杂志2008,42(9)10.刘九生母猪玉米赤霉烯酮中毒的诊断[期刊论文]-中国动物保健2004(5)1.杨丽萍.高淑霞.张秀玲.孙海涛.姜文学HPLC法检测家兔血浆中地克珠利含量[期刊论文]-中国兽药杂志2011(10)2.赵岳.沈建忠.程林丽.谷青.刘凯丽.王莹超高效液相色谱-串联质谱法测定鸡饲料中地克珠利的含量[期刊论文]-中国饲料 2012(3)3.罗浩师.张丽芳.薛飞群高效液相色谱-串联质谱法测定鸡脂肪中地克珠利残留量[期刊论文]-中国家禽 2012(20)4.江兆玲.薛飞群.张崇.肖遂.费陈忠.王霄旸.郑文丽.王春梅.王米超高效液相色谱法测定鸡组织中妥曲珠利及其代谢物的残留量[期刊论文]-中国家禽 2013(21)5.宫小明.孙军.董静.于金玲.王洪涛高效液相色谱-串联质谱法测定猪肉中的阿维菌素类、地克珠利、妥曲珠利及其代谢物残留[期刊论文]-色谱 2011(3)本文链接:/Periodical_zgsyxb200901019.aspx。

鸡血球肽螯合铁的结构表征及其稳定性研究

鸡血球肽螯合铁的结构表征及其稳定性研究

石景,邹烨,马晶晶,等. 鸡血球肽螯合铁的结构表征及其稳定性研究[J]. 食品工业科技,2023,44(19):427−432. doi:10.13386/j.issn1002-0306.2022120119SHI Jing, ZOU Ye, MA Jingjing, et al. Structural Characterization and Stability Study of Iron-Chelating Peptides from Chicken Blood[J]. Science and Technology of Food Industry, 2023, 44(19): 427−432. (in Chinese with English abstract). doi:10.13386/j.issn1002-0306.2022120119· 营养与保健 ·鸡血球肽螯合铁的结构表征及其稳定性研究石 景1,2,3,邹 烨2,3,4,马晶晶2,3,4,杨 彪1,2,3,4,王道营2,3,4,徐为民1,2,3,4, *,杨 静2,3,4,*(1.南京农业大学食品科技学院,江苏南京 210095;2.省部共建国家重点实验室培育基地江苏省食品质量安全重点实验室,江苏南京 210014;3.江苏省农业科学院农产品加工研究所,江苏南京 210014;4.农业农村部农产品冷链物流技术重点实验室,江苏南京 210014)摘 要:为了评估鸡血用于膳食铁补充剂的潜力,本文以鸡血和氯化亚铁为原料制备了鸡血球肽螯合铁,采用扫描电镜及差示扫描量热对其结构进行表征,分析了其在不同温度(30~80 ℃)及pH (2~9)下的稳定性,并对其体外稳定性进行了探讨。

结果表明鸡血球肽和铁结合生成一种新的肽铁螯合物。

该螯合物具有良好的热稳定性(铁保留率73.76%以上)并耐酸碱。

经体外模拟消化发现,鸡血球肽螯合铁的消化稳定性(铁保留率为86.01%)优于硫酸亚铁和葡萄糖酸亚铁。

药理学毒理学试验食品评价

药理学毒理学试验食品评价
风险就是度量一个不利事件发生的可能性、发 生的几率、不利结果、结果的严重性
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风险分析框架
风险评估
基于Байду номын сангаас学
风险管理
基于政策
风险交流
关于风险的信息和意见的互动交流
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风险分析(Risk Analysis)
有三部分组成 风险评估(Risk Assessment):核心和基础 风险管理(Risk Management) 风险信息交流(Risk Communication)
➢ 最小致死量(minimal lethal dose,MLD,LD01, LDmin):
指外源化学物使受试动物群体中仅引起个别发生死亡的剂量
➢ 半数致死量(median lethal dose,LD50):又称致死中量,
指外源化学物能引起一群动物50%死亡的剂量或浓度
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效应(effect):指一定剂量外源化学物与机体接触后所 引起的生物学改变
在细胞分裂的后期仍留在子细胞的胞质内,成为一个或几个规则的 次核
常用啮齿类动物骨髓多染红细胞(PCE)微核试验。PCE是红细胞 成熟的一个阶段,此时有的红细胞的主核已排出,微核容易辩 认
观察的遗传学终点:染色体完整性改变和染色体分离改变
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微核照片
结果:
1、微核率:计数1000个嗜多染红细胞,观察含有微核的嗜多染红细胞数
NOEL≥300倍:进行安全性评价
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第三阶段 代谢试验
目的:
➢ 了解受试物在体内的吸收、分布和排泄的速度及蓄积性
➢ 了解有无毒性代谢产物形成
➢ 寻找可能的靶器官
➢ 为选择慢性毒性试验的动物种系提供依据
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第四阶段 慢性毒性试验(包括致癌试验)

碧云天生物技术 Beyotime Biotechnology 碧云天 BCA蛋白浓度测定试剂盒(增强

碧云天生物技术 Beyotime Biotechnology 碧云天 BCA蛋白浓度测定试剂盒(增强

碧云天生物技术/Beyotime Biotechnology 订货热线:400-168-3301或800-8283301 订货e-mail :****************** 技术咨询:***************** 网址:碧云天网站 微信公众号BCA 蛋白浓度测定试剂盒(增强型)产品编号 产品名称包装 P0010SBCA 蛋白浓度测定试剂盒(增强型)200次产品简介:BCA 蛋白浓度测定试剂盒(增强型) (Enhanced BCA Protein Assay Kit)是根据目前世界上最常用的两种蛋白浓度检测方法之一BCA 法研制而成,实现了蛋白浓度测定的简单、高稳定性、高灵敏度和高兼容性。

和碧云天生产的普通BCA 蛋白浓度测定试剂盒相比,灵敏度更高,检测浓度下限达到10µg/ml ,最小检测蛋白量达到0.2µg ,待测样品体积为1-20µl 。

和碧云天生产的普通BCA 蛋白浓度测定试剂盒相比,显色速度更快,相同的样品孵育较短时间即可进行吸光度测定。

在20-1000µg/ml 浓度范围内有较好的线性关系。

本产品从0.025到0.5mg/ml 的标准曲线参考图1。

图1. 本试剂盒蛋白标准曲线的效果图。

左图为加入BCA 工作液后37ºC 分别孵育30、60和120分钟后的吸光度实测效果图,右图为37ºC 孵育60分钟时的实际显色效果图。

图中数据仅供参考,实际的检测效果可能会略有不同。

BCA 法测定蛋白浓度不受绝大部分样品中的化学物质的影响,可以兼容样品中高达5%的SDS ,5%的Triton X-100,5%的Tween20、60、80。

但本试剂盒受螯合剂和略高浓度的还原剂的影响,需确保EDTA 低于10mM ,无EGTA ,二硫苏糖醇(DTT)低于1mM ,β-巯基乙醇(β-Mercaptoethanol)低于0.01%。

不适用BCA 法时建议试用碧云天生产的Bradford 蛋白浓度测定试剂盒(P0006)。

家禽肌肉组织中硝基咪唑类药物残留高效液相色谱检测法研究

家禽肌肉组织中硝基咪唑类药物残留高效液相色谱检测法研究

家禽肌肉组织中硝基咪唑类药物残留高效液相色谱检测法研究沈建忠1,项新华2,张 跃1,赵 珊2(1中国农业大学动物医学院,北京 100094;2北京市疾病预防控制中心,北京 100013)摘要:建立了检测家禽肌肉组织中甲硝唑、洛硝哒唑、二甲硝咪唑残留的高效液相色谱法。

样品经乙酸乙酯振荡提取,浓缩,盐酸溶解残渣,己烷萃取除去脂肪。

氢氧化钠调节溶液到pH 4.8~5.2,过C 18小柱,甲醇洗脱,S pheris orb C 18柱分离,320nm 处检测。

流动相为醋酸缓冲液2乙腈(85∶15,v/v )。

甲硝唑、洛硝哒唑和二甲硝咪唑检测限分别为0.5、1.0和1.0ng ・g -1。

肉鸡肌肉组织中添加6.0ng ・g -1水平回收率分别为:甲硝唑89.8%,洛硝哒唑81.7%,二甲硝咪唑86.6%。

此方法具有定性合理,检测限低,分析快速,准确等特点。

关键词:家禽;硝基咪唑类药物;肌肉组织;残留;高效液相色谱Determination of Nitroimidazole s in Poultry Muscle T issue s by H igh 2performance Liquid ChromatographySHE N Jian 2zhong 1,XI ANG X in 2hua 2,ZH ANG Y ue 1,ZH AO Shan 2(1College o f Veterinary Medicine ,China Agricultural Univer sity ,Beijing 100094;2Beijing Center for Disease Prevention and Control ,Beijing 100013)Abstract :A method was developed for determination of metronidazole (MTZ ),ronidazole (RNZ ),and dimetrida 2zole (DMZ )in poultry muscle by high 2performance liquid chromatography.A fter an initial extraction with ethyl acetate and evaporation in sequence ,the sam ple was res olved in hydrochloric acid.Hexane was used in the liquid 2liquid extrac 2tion to rem ove fat.A C 18s olid 2phase extraction was performed after neutralization with 5.0m ol ・L -1NaOH or 1.0m ol ・L -1HCl to pH 4.8-5.2and the cartridge was rinsed with methanol.Detecting wavelength was set at 320nm and m o 2bile phase was acetate bu ffer s olution and acetonitrile (85∶15,v/v ).The limits of detection were 0.5,1.0and 1.0ng・g -1for MTZ ,RNZ and DMZ ,respectively.Recoveries of MTZ ,RNZ and DMZ in muscle fortified at 6.0ng ・g -1were 89.8%,81.7%and 86.6%,respectively.K ey words :P oultry ;Nitroimidazoles ;Muscle ;Residue ;High 2performance liquid chromatography收稿日期:2001211219基金项目:国家自然科学基金重点资助项目(30130140)作者简介:沈建忠(19632),男,浙江桐乡人,教授,博士,主要从事兽医药理学与毒理学研究。

水产品中孔雀石绿的风险评估(二)

水产品中孔雀石绿的风险评估(二)

水产品中孔雀石绿的风险评估(二)王群;宋怿;马兵【摘要】以食品添加剂联席专家委员会第70次会议对孔雀石绿的风险评估报告为主要依据,分析了水产品中孔雀石绿的膳食暴露评估和风险特征,为方便快捷地了解国际组织对孔雀石绿的风险评估提供参考.【期刊名称】《中国渔业质量与标准》【年(卷),期】2012(002)001【总页数】5页(P22-26)【关键词】孔雀石绿;水产品;风险评估【作者】王群;宋怿;马兵【作者单位】中国水产科学研究院,北京100141;中国水产科学研究院,北京100141;中国水产科学研究院,北京100141【正文语种】中文【中图分类】S-1《水产品中孔雀石绿的风险评估(一)》[1]主要介绍了孔雀石绿(Malachite green,MG)的毒性,给出了孔雀石绿和无色孔雀石绿毒性(Leucomalachite Green,LMG)的综合评价,本文主要介绍水产品中孔雀石绿的膳食暴露评估和风险特征,为正确地了解孔雀石绿对人体健康风险提供依据。

1 膳食暴露评估暴露评估是风险评估的第3个阶段,目的是确定风险人群接触待评物质的来源、类型、程度和持续时间等,为风险评估提供可靠的暴露数据或估测值[2]。

如果危害物可以通过食物传递给人就需要进行膳食暴露评估,在进行化学危害物的膳食暴露评估时,利用食物消费数据与食物中化学物含量数据,可以得到膳食暴露量的估计值。

食品添加剂联席专家委员会(JECFA)采用2组不同的数据对MG进行了膳食暴露的初步评估[3]:第一组评估数据采用了抽样监测数据结果,这些MG的阳性数据可能是由环境污染或非法使用造成的。

第二组评估数据采用一项比较详尽的MG在养殖鱼体内药物代谢和残留研究结果,该研究模拟MG的真实使用情况,所采用的实验鱼规格为“适合人类食用”。

评估方法一:JECFA研究了一些关于MG和LMG的监测报告,从这些报告中选择3 277份样本,其中222份样本显示为阳性,残留范围在0.2~600 μg/kg(图1),这些数据来自于英国1995-2006年对鱼肉中MG和LMG的监测数据,如果在样本中发现这2种物质,JECFA评估时就考虑MG和LMG的总和。

低剂量氯化镉对大鼠睾丸组织酶活性的影响

低剂量氯化镉对大鼠睾丸组织酶活性的影响

低剂量氯化镉对大鼠睾丸组织酶活性的影响1韦凌娅1,吕中明2,顾呈华2,王民生2*1 东南大学公共卫生学院,南京(210009)2 江苏省疾病预防控制中心,南京(210009)E-mail: weilingya@摘要:目的:研究低剂量氯化镉染毒对睾丸组织酶活性的影响。

方法:40只健康雄性SD 大鼠分成4组,剂量分别为0 (生理盐水)、0.1、0.2、0.4mg/kg bw,腹腔注射染毒,1次/天,每周染毒5天,共染毒8周,实验结束颈椎脱臼处死,取单侧睾丸,测定睾丸匀浆上清液中酶的活力。

结果:LDH-x、β-Glu、ACP和AKP活力均降低(P<0.05)。

MDA含量与NOS活力增加、SOD和GSH-Px活力显著降低。

结论:镉可以导致睾丸组织酶活力下降,降低抗氧化能力,对睾丸组织产生损伤作用。

关键词:氯化镉,睾丸组织酶,氧化损伤中图分类号:R114镉对雄性生殖系统的影响被认为是影响人类生育的重要因素,已受到普遍关注。

有报道显示,亚慢性镉染毒可使睾丸体积变小,重量减轻,肉眼观察出现睾丸病理改变,镜检发现曲细精管呈不同程度的萎缩、变性,管内生精细胞数少或缺如,无精子形成或极少,管腔内可见坏死的细胞碎片[1-2],说明镉可以严重干扰破坏大鼠睾丸曲细精管上皮的生精过程,对大鼠的生殖功能产生影响。

睾丸是许多具有生殖毒性的化学物质的靶器官。

精子发生是一个多时相的复杂过程,要经历精原细胞增殖、精母细胞成熟分裂和精子形成等多个阶段,这一过程与睾丸中多种酶的活性存在相关关系。

研究表明,在形态学尚无明显改变时,往往其生化过程已经发生改变,表现为睾丸组织中一些酶的活性出现了变化,如乳酸脱氢酶同功酶(LDH-x)、酸性磷酸酶(ACP)、碱性磷酸酶(AKP)及β-葡萄糖醛酸苷酶等。

睾丸中还含有丰富的抗氧化物质,如SOD、还原型谷胱甘肽(GSH)、维生素C和维生素E等,这些物质在精子生成过程中也起着重要的作用,同时可保护生殖细胞免于氧化损伤。

高效液相色谱法测定鸡肉中磺胺类药物残留的不确定度评定_赵健亚

高效液相色谱法测定鸡肉中磺胺类药物残留的不确定度评定_赵健亚

高效液相色谱法测定鸡肉中磺胺类药物残留的不确定度评定赵健亚1,陈 丹2,谢怀根2,肖 静1,*(1.南通大学公共卫生学院,江苏 南通 226019;2.南通市动物疫病预防控制中心,江苏 南通 226006) 摘 要:依据JJF 1059—1999《测量不确定度评定与表示》和CNAS —GL06《化学分析中不确定度的评估指南》规定的测量不确定度的基本方法,建立数学模型,分析高效液相色谱法测定鸡肉中磺胺类药物残留的不确定度来源,并对各分量进行量化,给出5种磺胺类药物残留测定结果的扩展不确定度,评定结果表明:影响检测结果不确定度的主要因素为标准曲线拟合、样品前处理过程和测量重复性等。

关键词:不确定度;磺胺;高效液相色谱法;鸡肉Uncertainty Evaluation for Determination of Sulfonamide Residues in Chicken by High Performance Liquid ChromatographyZHAO Jian-ya 1,CHEN Dan 2,XIE Huai-gen 2,XIAO Jing 1,*(1. School of Public Health, Nantong University, Nantong 226019, China ;2. Nantong Center for Animal Disease Control and Prevention, Nantong 226006, China)Abstract :A mathematical model was established according to the basic method for uncertainty evaluation from JJF 1059—1999 and CNAS-GL06. The sources of uncertainty for determining sulfonamide residues in chicken by high performance liquid chromatography (HPLC) were analyzed and each component of uncertainty was quantified. The expanded uncertainty for fi ve sulfonamides residues results was calculated. The major uncertainty sources were standard curve fi tting, sample pretreatment and measurement repeatability.Key words :uncertainty ;sulfonamides ;high performance liquid chromatography (HPLC);chicken 中图分类号:TS207.3 文献标志码:A 文章编号:1002-6630(2013)10-0144-04doi:10.7506/spkx1002-6630-201310031收稿日期:2012-02-24基金项目:国家自然科学基金青年科学基金项目(31000539);南通市应用研究计划项目(K2010066)作者简介:赵健亚(1980—),女,讲师,硕士,主要从事食品安全质量控制研究。

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Journal of Integrative Agriculture© 2012, CAAS. All rights reserved. Published by Elsevier Ltd.T oxicological Evaluation of Chicken-Breast Meat with High-Dose IrradiationZHU Jia-ting 1, FENG Min 1, Y AN Jian-min 1, LIU Chun-quan 2, HA Y i-ming 3, GAO Mei-xu 3, Y ANG Ping 1, W ANG Zhi-dong 3, W ANG De-ning 1, LI Shu-rong 3 and GU Gui-qiang 11Institute of Atomic Energy in Application for Agriculture, Jiangsu Academy of Agricultural Sciences, Nanjing 210014, P.R.China 2 Institute of Farm Product Processing, Jiangsu Academy of Agricultural Sciences, Nanjing 210014, P.R.China3 Institute of Agro-Products Processing Science&Technology, Chinese Academy of Agricultural Sciences, Beijing 100193, P.R.ChinaAbstractIn this paper, toxicity and safety of high-dose irradiated chicken-breast meat were evaluated. For assays of acute toxicity,genetic toxicity, and sub-chronic toxicity, ames test, mice bone marrow erythrocyte micronucleus, and mice sperm abnormality were performed. The results showed that, in the acute oral toxicity tests, median lethal dose (more than 10 000 mg kg -1) in male and female ICR mice showed no toxicological signs. For subacute 30-d oral toxicology of irradiated chicken-breast meat with dose of 10, 15 and 25 kGy in both male and female SD rats, no noticeable toxicological effects were observed. It is concluded that chicken-breast meat with high-dose irradiation has no acute toxicity and no genotoxicity, nor harmful effects on the animal body at the tested dosage range. Therefore, high-dose irradiated chicken-breast meat is safe for pet consumption.Key words: toxicological assessment, chicken-breast meat, irradiated, high doseINTRODUCTIONGamma irradiation has been commonly employed for decontamination and sterilization of pet foods to pro-long the storage period (Lin et al . 2002, 2009; Parke et al . 2005; Liu et al . 2006; Zhu et al . 2009). There is ample published evidence showing the enormous po-tential of this method for extending shelf life of chicken meat by eliminating certain spoilage and pathogenic organisms. Many countries in the world are engaged in the commercialization of irradiation food according to the Bulletin of the Meeting of Combined Expert Com-mittee of FAO (the Food and Agriculture Organization of the United Nation)/IAEA (the International Atomic Energy Agency)/WHO (the World Health Organization)(Diehl 2002; Child et al . 2009; Tamikazu et al . 2009).At present, irradiated foods including 6 food categories and 18 food varieties have been permitted by the Minis-try of Health of the P.R.China to enter Chinese markets (Wang and Chao 2003).In recent years, with rapid development of domestic and international pet industry, huge economic benefits are brought out by pet food enterprises. China is the world’s food irradiation superpower, with a total of about 2×105 t irradiated food in 2009 (Gao et al. 2010).However, the safety of irradiated food was still drawn great attention by many consumers, a variety of stud-ies to assure the safety of irradiation technique for pet food have been carried out, but not comprehensive enough. Especially, the effects of high-dose irradiation on main nutrients, physical and chemical indicators,toxicological evaluation of pet food were still rarely re-ported (Lin et al . 2002, 2009).Received 10 November, 2011 Accepted 26 March, 2012Correspondence ZHU Jia-ting, Tel/Fax: +86-25-84391942, E-mail: zjtlw@Toxicological Evaluation of Chicken-Breast Meat with High-Dose Irradiation2089For some special demands of pet food, low-dose irradiation (below 10 kGy) is impossible to achieve com-pletely sterilization. Many researchers recognized and reported that gamma irradiation in low doses, below 10 kGy could kill most organisms without deterioration of food quality (Thayer et al. 1995; Lacroix and Quattara 2000; Mahrour et al. 2003; Javanmard et al. 2006; Waje and Kwon 2007). However, few studies on the high-dose irradiation effects on food toxicity have been re-ported (Wang et al. 1987); the safety of irradiation ster-ilization for high doses hitherto needs to be confirmed. According to the Irradiated Food Safety Management Measures (1996, China), to develop new varieties of irradiated food (over 10 kGy) should provide sensory traits, nutritional, toxicological, microorganisms, and other indicators. In this paper, a complete toxicologi-cal assessment of irradiated chicken-breast meat with high doses, including test of genotoxicity, acute oral toxicity, and a 30-d sub-chronic toxicity was conducted in order to evaluate the safety of 60Co-irradiated chicken-breast meat as a pet food.RESULTSAcute toxicity testAfter oral administration of irradiated chicken-breast meat, none of the mice had any significant symptom of poisoning or death in all dosage groups (data not shown). The LD50of irradiated chicken-breast meat in both male and female mice was more than 10000 mg kg-1 body weight (BW). No toxicological effects were observed in 14-d period, in terms of body weight, food consumption, organ weight, and gross pathological alterations. Therefore, the acute toxicity of irradiated chicken-breast meat belongs to low toxicity grade or practically non-toxic (Ministry of Health of the P.R. China 2003).Ames testNo evidence of cytotoxicity (reduced rate of spontane-ously occurring clones and visible thinning of the bac-terial lawn) was observed at all testing dosage levels of irradiated chicken-breast meat. The mean number of revertants per plate of irradiated chicken-breast meat treatment groups at all dose levels for four strains of TA97, TA98, TA100, and TA102with or without S-9, were negative. None of the treated groups has two folds or more revertant counts than the concurrent control and no dose-relationship was observed. The mean number of revertant clones of the negative control was within the historical range of the laboratory. The positive con-trol mutagens induced the increases in revertant clones, confirming the validity of the assay. The results of Ames test indicate that irradiated chicken-breast meat has no genetic toxicity (Tables 1-3); similar results were obtained from the duplicate test (data not shown). Therefore, the Ames test result for irradiated chicken-breast was negative.Micronucleus test on bone marrow cellThe micronucleus of the irradiated chicken-breast meat treatment groups at all dose levels as well as the nega-tive control group were significantly lower than thoseTable 1 The influence of irradiated chicken-breast meat (sample B) used in Salmonella typhimurium reversionDose (μg/dish)TA97TA98TA100TA102-S9+S9-S9+S9-S9+S9-S9+S910123±8132±1136±444±6173±12184±14270±18291±13 40123±9133±1037±646±4173±10181±14270±15288±18 200125±9134±1135±547±5174±8185±13272±16293±18 1000123±7132±1036±546±7171±8183±13274±19289±16 5000124±8133±1036±545±5172±13185±14273±14291±16 Concurrent125±9135±935±547±7175±10182±12270±12290±19 Solvent122±8132±938±546±6173±14182±11269±15292±18 Positive853±53**Positive control: TA97-S9500.0 used atabrine at μg/dish; TA98-S9used daunorubicin at 6.0 μg/dish; TA100-S9, TA102-S9used methyl methanesulfonate at 1.0 μL/dish;TA97+S9, TA98+S9, TA100+S9used 2-AF at 10.0 μg/dish; TA102+S9used 1.8-dihydroxyanthraquinone at 50.0 μg/dish. **, P<0.01 compared to the negative control. The resultwas mean±SD of 3 plates. Solvent control: ddH2O. The same as below.1611±114**1803±133**875±87**1740±105**1809±105**2066±134**1885±91**2090ZHU Jia-ting et al.in positive control group treated with cyclophospha-mide (CP) (P<0.01), confirming the validity of the trial. There were no significant differences of micronucleus between the negative control group and the irradiated chicken-breast meat treatment groups (P>0.05). The polychromatic erythrocytes (PCE)/normochromatic erythrocytes (NCE) ratio of each group was within nor-mal range. The result indicating that irradiated chicken-breast meat is not mutagenic in vivo at the tested dos-age 5000 mg kg-1 BW (Table 4).Mice sperm abnormality trialThe sperm abnormality of the irradiated chicken-breast meat treatment groups at three different dose levels were 2.46, 2.52 and 2.64%, respectively, which had no sig-nificant differences compared with the negative con-trol group (P>0.05). The sperm abnormality ratios in all treatment groups as well as the negative control group (2.64% sperm abnormalities) was significantly lower than those in positive control group (7.44% sperm abnormalities) treated with CP at 40 mg kg-1 (P<0.01) (Table 5). The sperm abnormality test was a method of evaluating genetic injury to male reproductive cells of mammals (including humans) in vivo test. It was indicated that no genotoxicity was found on mice sperm for irradiated chicken-breast (samples B, C and D).Subacute 30-d oral toxicology study in ratsNo decease, abnormal behaviors- or treatment-related toxic signs were observed for the mice throughout the experimental period. Table 6 shows the body weight, body weight gain and food consumption data from the 30-d study.Male and female rats’ body weight as well as body weight gain in the experiment period had no significant differences (P>0.05) except the body weight of a male rat group at d-30 (P<0.05). Further analysis on the d-30 male rat body weight using Dunnett t-test that com-pares each dose level group with the control group shows no significant difference with or without irradi-ated treatment (P>0.05).Food consumption and food utilization of the male rats had no significant differences compared with the female rats at all other dose levels at other testing weeks (P>0.05). No significant differences in total food con-sumption and total food utilization between the treat-ment and control groups.All hematological parameters had no statistically sig-nificant differences between the irradiated treatment and control groups in the end periods of the 30-d study (Table 7). All clinical chemistry measurements find-ings between the treatment and control groups in the end periods of the 30-d study were presented in TableTable 2 The influence of irradiated chicken-breast meat (sample C) used in S. typhimurium reversionDose (μg/dish)TA97aTA98TA100TA102-S9+S9-S9+S9-S9+S9-S9+S910120±7132±1235±648±4175±9184±13270±18288±15 40123±10134±736±447±7172±12181±14269±12284±14 200124±8133±937±345±4174±9185±14272±12287±16 1000122±9132±834±548±5176±9185±12272±16288±19 5000123±11134±1236±446±5173±14186±10269±12282±19 Concurrent122±9130±934±645±6175±10180±12271±13285±17 Solvent120±9133±1036±546±4176±11184±13273±16284±17 Positive853±53** 1611±114**1803±133**875±87**1740±105**1809±105**2066±134**1885±91**Table 3 The influence of irradiated chicken-breast meat (sample D) used in S. typhimurium reversionDose (μg/dish)TA97aTA98TA100TA102-S9+S9-S9+S9-S9+S9-S9+S910122±7133±935±443±6173±12180±14258±18286±15 40125±10136±737±644±7176±12185±10259±12291±18 200120±8132±1236±446±4170±8189±15258±12294±14 1000124±10137±1134±247±4174±6184±10263±16288±17 5000123±7135±1234±544±6175±10182±11260±10295±17 Concurrent125±12133±1138±545±5172±10184±15264±19287±13 Solvent122±9136±834±445±6174±11182±16262±14290±11 Positive853±53** 1611±114**1803±133**875±87**1740±105**1809±105**2066±134**1885±91**Toxicological Evaluation of Chicken-Breast Meat with High-Dose Irradiation 20918. Through the simple factor analysis of variance, the total protein (TP) levels of sample D group of male rats were significantly higher than those in the control group (P <0.05), the albumin (ALB) levels of sample B and D groups of male rats were significantly higher than those in the control group (P <0.05), the aspartate transami-nase (AST) levels of sample D group of male rats were significantly lower than those in the control group (P <0.05), and other hematological parameters had no statistically significant differences (P >0.05) between the irradiated treatment and control groups in the end periods of the 30-d study.No statistically significant differences in absolute organ weight and organ-to-body weight ratios (Table 9) were observed.In the tests of gross anatomy, the size, color, and shape of heart, lung, liver, spleen, kidney, stomach,intestine, and testis of all the tested rats were normal,as evaluated by eye observation. The pathological ex-amination was conducted by high dose group vs . the control group only. No pathological changes of liver,kidney, spleen, stomach/duodenum, testis, and ovary tissues were observed for the high-dose group vs . the control group (Table 10). In summary, no toxic side effect was observed in the 30-d study.DISCUSSIONFood irradiation is recognized by the world health com-munity as a good method for preserving food and en-suring its wholesomeness. In the last 50 years, re-search activities have concluded that when used under good manufacturing practices, irradiation will: (i) in-crease food safety and reduce foodborne illness; (ii)lengthen the shelf-life of many perishable products; and (iii) reduce the risks of post-processing contamination of intact, packaged products (Smith and Pillai 2004;Quested et al . 2010; Farkas and Mohácsi-Farkas 2011).The most important element in food irradiation is the dose used on the product. The exposure must be ad-equate to produce desired results, yet low enough tomaintain the quality of foods. In most countries, in-cluding the USA, guidelines exist and define the mini-mum and maximum exposures for various commodities.Most of the claims of adverse effects of irradiation do not apply to the typical doses approved for pasteuriza-tion and they generally only apply in theory to the much higher doses required for sterilization. High doses of irradiation sterilize food kill all microorganisms except for viruses. However, radiation-sterilized meat and poul-try products produced by current methods have beenTable 4 Effect of irradiated chicken-breast meat on bone marrow micronucleus and PCE/NCE ratioGroups Dose SexMicronucleusPCE/NCE(mg kg -1BW)Number of PCEs countedNumber of micronucleiMicronuclei frequency (‰)PCE countedPCE/NCE Sample B 50001 000×58 1.40±0.89200×50.94±0.051 000×57 1.20±1.10200×50.93±0.05Sample C 50001 000×59 1.60±1.14200×50.95±0.051 000×56 1.00±1.00200×50.94±0.05Sample D 50001 000×57 1.40±0.89200×50.92±0.041 000×59 1.60±1.14200×50.94±0.04Negative control01 000×58 1.80±0.84200×50.95±0.041 000×57 1.40±0.89200×50.92±0.04Positive control CP401 000×517536.20±4.21**200×50.73±0.051 000×518735.80±3.96**200×50.72±0.04Cyclophosphamide (CP) was treated to mice as the positive control at a dose of 40 mg kg -1. The same as in Table 5.Table 5 Effect of irradiated chicken-breast meat on sperm counts and sperm morphology in micegroupsDoseTotal spermsAbnormal typeTotal abnormalAbnormal (mg kg -1 BW)counted Ghost-likeAmorphous Kinks tail Two heads Two tails sperms Negative control 01 000×516121087322132 2.64Sample B 5 0001 000×51911781212123 2.46Sample C 5 0001 000×51510884234126 2.52Sample D 5 0001 000×52013882423132 2.64CP401 000×54934232151814193727.44**Large roundheag ratios (%)Banana shape2092ZHU Jia-ting et al .Table 6 Body weight and food consumption of rats in 30-d studyGroups Body weight (g)Body weight gain (g)Week 1Week 2Week 3Week 4 Control 43.8±9.438.0±7.528.7±5.522.6±7.0133.1±19.1 Sample B 42.2±7.939.2±5.126.2±6.224.2±7.4131.8±13.8 Sample C 42.2±8.337.6±4.825.5±4.023.8±7.5129.1±17.2 Sample D 44.5±5.536.0±5.628.2±2.824.27±8.2132.9±16.1 Control 56.2±5.364.7±8.0236.3±21.5 Sample B 62.7±3.2*65.0±6.458.2±7.154.2±4.1240.1±14.2 Sample C 59.9±4.869.0±7.757.8±7.5238.1±20.6 Sample D 59.9±3.970.3±6.159.7±4.850.5±7.6240.3±11.6Groups Weekly feed intake (g)Total feed intake (g)Week 1Week 2Week 3Week 4 Control 108.0±16.5144.8±17.3131.4±14.4166.8±20.8550.9±37.1 Sample B 107.3±13.2128.2±12.4160.7±14.2545.2±36.3 Sample C 110.5±14.9144.2±14.1129.4±12.1155.1±22.9539.1±43.5 Sample D 109.6±14.1144.7±11.5131.8±10.2161.9±15.9547.9±41.7 Control 128.3±10.0190.9±10.1197.5±22.0226.0±13.7742.6±35.9 Sample B 135.4±11.6*208.0±16.2197.4±23.5765.7±49.2 Sample C 129.4±14.2196.2±16.4186.7±22.2215.9±15.4728.2±47.4 Sample D 131.7±14.4189.3±12.7195.1±14.2218.8±14.9734.9±35.7Groups Food utilization (%)Total food utilization (%)Week 1Week 2Week 3Week 4 Control 40.5±6.026.3±4.721.8±3.113.7±4.224.2±3.0 Sample B 39.6±7.926.3±2.420.2±3.114.9±3.824.1±1.4 Sample C 38.9±9.826.2±2.919.6±2.015.1±3.323.9±2.2 Sample D 40.8±4.424.8±2.921.4±0.914.8±4.624.2±2.1 Control 44.0±5.234.0±4.132.1±3.822.6±4.931.8±2.0 Sample B 46.5±3.531.2±1.929.6±2.924.1±1.831.4±1.3 Sample C 46.8±5.935.2±2.731.1±3.923.6±5.632.7±2.3 Sample D45.9±4.637.2±3.330.7±2.523.1±3.132.7±1.4*, P <0.05.63.9±13.051.4±12.351.4±13.5224.9±6.5148.9±9.8Table 7 Termination (d-30) hematological results of 30-d feeding testItemUnit Irradiated chicken-breast meat of female rats Irradiated chicken-breast meat of male rats Control B C D Control B C D Hemoglobin concentration g L -1Erythrocyte count 1012 L -18.17±0.277.99±0.197.94±0.168.01±0.348.19±0.378.39±0.308.36±0.268.34±0.23Leukocyte count 109 L -1 6.52±1.53 6.46±1.10 6.65±1.82 6.24±1.147.38±1.237.17±1.237.03±1.657.33±1.58Platelet count 109 L -1Neutrophils %20.6±5.218.0±4.520.4±5.419.3±4.318.3±3.918.2±4.620.2±4.319.5±3.7Basophils %0.50±0.530.50±0.710.70±0.670.60±0.520.70±0.670.50±0.710.50±0.530.50±0.53Eosinophils %0.60±0.840.60±0.700.50±0.530.70±0.670.60±0.700.70±0.670.60±0.700.50±0.71Lymphocytes %74.4±4.676.6±4.974.1±4.775.3±4.377.0±3.776.1±4.574.4±4.575.2±2.8Moncocytes%133±6132±5135±4129±6131±8135±5134±6137±4715±33711±38717±38738±32722±38730±36747±46722±433.9±1.74.3±0.84.3±1.64.1±1.43.4±1.64.5±1.64.3±1.64.3±1.5Table 8 Serum biochemistry findings in SD rats after 30 d of Ac administrationItem Unit Irradiated chicken-breast meat of female ratsIrradiated chicken-breast meat of male ratsControl B C D ControlB C D ALT U L -138.8±5.734.2±4.635.5±5.935.2±4.345.2±7.942.2±10.443.6±8.644.8±8.6AST U L -1TP g L -168.7±2.871.4±3.571.3±3.173.2±2.0*71.5±3.169.3±3.969.7±3.473.2±2.4ALB g L -142.9±2.045.3±1.5*44.7±2.245.3±1.8*43.8±0.842.8±0.843.3±1.044.5±1.3CHL mmol L -1 2.10±0.19 2.15±0.26 2.09±0.24 2.11±0.31 2.04±0.27 1.98±0.25 1.99±0.25 1.97±0.23TG mmol L -10.83±0.24 1.02±0.170.91±0.260.83±0.23 1.21±0.37 1.18±0.34 1.13±0.36 1.22±0.29BUN mmol L -18.50±0.838.30±0.809.05±0.779.18±0.779.15±1.068.40±0.978.95±1.379.06±1.13UA μmol L -179.5±12.179.3±12.183.7±13.580.0±12.7CR μmol L -148.0±3.549.8±3.755.4±3.1*56.0±2.6*52.3±3.050.1±3.953.2±5.253.1±2.7GLUmmol L -15.43±0.865.38±0.405.60±0.705.38±0.715.48±0.865.43±0.685.43±0.765.73±0.58*, P <0.05 vs. the same sex control group.135.8±15.1121.8±27.8101.8±29.2116.8±19.8*121.2±13.3119.5±27.5104.7±28.5121.4±15.6117.8±10.9114.3±13.4117.2±16.5108.8±12.9Toxicological Evaluation of Chicken-Breast Meat with High-Dose Irradiation2093rated by experts as superior to their canned counter-parts in texture, appearance, and, in some instances, vitamin retention and taste (Steele and Engel 1992). The ground breaking research into irradiation of food at high doses was carried out in the USA. In September 1997, a study group appointed by WHO concluded that foods treated with doses greater than 10 kGy can be consid-ered safe and nutritionally adequate when produced under established Good Manufacturing Practice. This conclusion was based on their evaluation of all avail-able data regarding the wholesomeness of food irradi-ated at high dose (Anonymous 1997).It is more than fifty years since irradiation sterilization was used for food and currently more than thirty coun-tries have adopted this technique. In China, seven kinds of food have been approved for irradiation by the Minis-try of Health of the P.R.China. This showed clearly the technique of irradiation used for food sterilization has been accepted by market and laws. However, so far, there have no reports about whether the technique with high doses is safe to chicken breast. It is our hope to supply some toxicity and genotoxicity data for the appli-cation of high-dose irradiated chicken-breast meat.In our study we observe no acute toxic effects of the high-dose irradiated chicken-breast taken via the oral route and we conclude that the LD50is higher than 10000 mg kg-1. For sub-chronic toxicity of irradiated chicken-breast meat with dose of 10, 15 and 25 kGy in both male and female ICR mice, no noticeable toxico-logical effects were observed. And the administration of irradiated chicken-breast meat with high dose for 30 d at dietary levels was well tolerated and did not affect health, behavior and neurological parameters of SD rats. It is concluded that high-dose irradiated chicken-breast meat has no acute toxicity and no genotoxicity, nor harmful effects on the human body at the tested dos-age range, which is some concordant with the litera-ture review. Just as commented in 1983 and 1989, food irradiated with the dosage of 10-30 kGy is safe (Yang et al. 1994). The point of view was brought up by the Joint FAO/IAEA/WHO Expert Committee and it has been proved world wide by a lot of experiments (Thayer et al. 1987; Lester et al. 1996).CONCLUSIONThe lack of acute toxicity, no mutagenic effects andTable 9 Mean (±SD) organ weights (g) and organ weight to final body weight ratios (%) in the ratsOrgan MeasureIrradiated chicken-breast meat of female rats Irradiated chicken-breast meat of male ratsControl Sample B Sample C Sample D Control Sample B Sample C Sample DLiver Weight (g)10.276±1.42810.086±0.7159.861±1.13410.119±1.19215.686±1.64916.049±1.00614.962±2.28415.214±1.777 Ratio (%) 4.469±0.399 4.410±0.232 4.381±0.396 4.424±0.351 4.623±0.376 4.688±0.253 4.402±0.458 4.446±0.386 Kidney Weight(g) 2.055±0.204 2.075±0.237 1.880±0.188 1.946±0.177 2.998±0.233 2.976±0.270 2.916±0.333 2.810±0.210 Ratio (%)0.901±0.1130.905±0.0720.836±0.0670.852±0.0480.884±0.0370.870±0.0820.859±0.0500.823±0.054 Spleen Weight (g)0.602±0.0890.602±0.0780.582±0.0840.624±0.0920.864±0.1140.887±0.0930.860±0.1830.826±0.173 Ratio (%)0.263±0.0390.264±0.0350.259±0.0360.273±0.0330.255±0.0270.259±0.0280.255±0.0570.242±0.050 Testicular Weight (g) 2.923±0.203 2.948±0.209 2.837±0.115 2.823±0.089 Ratio (%)0.862±0.0420.862±0.0640.842±0.0690.828±0.050Table 10 liver, kidneys, stomach, duodenum, spleen, testicular, and ovaries pathological examination of 30-d feeding studyVisceral organs Pathological changes Negative control Sample B Sample CSample DLiver Swelling of liver cellular1/100/100/100/100/100/101/100/10 Hepatic steatosis0/101/101/101/100/100/100/100/10Sinusoidal expansion and congestion0/100/100/100/100/100/100/100/10Mesenchymal inflammatory cell infiltration and hyperplasia of fibrous tissue0/100/100/100/100/100/100/100/10 Kidney Glomerular cellularity increase0/100/100/100/100/100/100/100/10 Renal tubular epithelial cell degeneration, necrosis0/100/100/100/100/100/100/100/10Pathological casts0/100/100/100/100/100/100/100/10Interstitial congestion, inflammatory cell infiltrating0/100/100/100/100/100/100/100/10 Stomach/duodenum Mucosa slough, degeneration0/100/100/100/100/100/100/100/10 Submucosa, tunica serosa hyperemia, inflammatory cell infiltrating0/100/100/100/100/100/100/100/10 Spleen Splenic sinuses dilatation, splenic nodules atrophy0/100/100/100/100/100/100/100/10 Testicular Seminiferous tubules and spermatogenic cells dysplasia0/100/100/100/10 Ovaries Follicular, corpus luteum abnormalities0/100/100/100/102094ZHU Jia-ting et al. lack of harmful effects found in the hematology, clini-cal chemistry and histopatology in this safety assess-ment indicate that high-dose (10-25 kGy, the dose rec-ommended for quarantine and hygienic purposes) irra-diated chicken-breast meat may have a large safetymargin.MATERIALS AND METHODSMaterialsDried chicken-breast meat was purchased from JinanUniwell Pet Food Co., Ltd., China. The sample wascrushed into powder, then packaged as 100 g samples inPVC (poly-vinyl chloride) containers used for gammairradiation. Gamma irradiation was performed at the Insti-tute of Atomic Energy in Application for Agriculture,Jiangsu Academy of Agriculture Science (JAAS), China.The power of irradiation equipment of gamma rays of 60Cois 29.6 PBq, the radiation doses on the chicken-breastmeat were 10, 15 and 25 kGy, respectively. In reference tothe food safety toxicology evaluation procedures andmethods (Ministry of Health of the P.R.China 2003), thesafety toxicology for irradiated-chicken breast wasevaluated, irradiated chicken-breast meat powder (sampleB, C and D) was mixed with bidistilled water to a certaindose for assays of acute toxicity, genetic toxicity, andsub-chronic toxicity, ames test, mice bone marrow eryth-rocyte micronucleus, and mice sperm abnormality. Irradi-ated chicken-breast meat powder (sample B, C and D)was added to a basal feed at concentrations of 100 g kg-1d-1, respectively and the rats were administrated for 30-dfeeding study.Instruments and chemical agentsHematology analyzer (Sysmex XE-2100, Kobe, Japan),Auamatic biochemical analyzer (Beckman LX 20, USA),and pathologic microtome sector (A0820, AO ScientificInstruments, Buffalo, NY, USA) are the main instrumentsused. The strains of TA97, TA98, TA100, and TA102weresupplied by Shanghai Institutes of Preventive Medicine,the mixture of liver microsomal enzymes (S9) were culturedby a toxicological department of Jiangsu Center for Dis-ease Control and Prevention, China; cyclophosphamide (CP) was bought from Jiangsu Hengrui Medicine Co., Ltd., China.Animals and housingMale and female ICR mice and SD rats were purchased from Zhejiang Laboratory Animal Center in Zhejiang, China (laboratory animal reproduction license # SCXK [SH] 2008-0033). The studies were conducted in compliance with Good Laboratory Practices at Jiangsu Disease Control and Preven-tion (JDC) (laboratory animal use permit # SYXK [JS] 2008-0003. All animals were housed as groups of five animals per cage in standard plastic cages. Temperature inside the experi-mental room was controlled at 22-24°C, humidity was con-trolled at 52-58%, and light control was maintained as a 12-h cycle of dark-light throughout the test period. All animals were examined for their general physical conditions upon adop-tion and acclimatized for 1 wk before any test.Ames testMutagenicity was determined by the Ames salmonella plate test. A strain of bacterium Salmonella typhimurium is an auxotrophic mutant and requires histidine for its growth. The strains of TA97, TA98, TA100, and TA102were qualified for use in the test. The tests were performed twice by the plate incorporation test on 5 groups of different doses of irradiated-chicken breast in the test were 5000, 1000, 200, 40, and 8 μg/dish, respectively. The known carcinogens, such as daunorubicin, dexon, sodium azide, and 2-aminofluorene, were used as positive controls. Dimethyl sulfoxide was used as the solvent for the 2-aminofluorene, distilled water for other groups. The test substance will be considered to be mutagenic if the revertant clones are two or more folds the number of spontaneous revertant clones on negative sol-vent control plates. A dose response relationship was ob-served in at least 2 concentrations. The test was repeated under the same conditions to confirm the results.Mice bone marrow erythrocyte micronucleus assayFifty of 7-8 wk-old ICR mice of 25-30 g, 25 male and 25 female, were divided into five groups randomly. Cyclo-phosphamide (40 mg kg-1) was used as positive control; ddH2O was used as negative control. The irradiated-chicken breast dose levels of testing groups (sample B, C and D) were all of 5000 mg kg-1. The testing samples were freshly prepared by mixing irradiated-chicken breast with ddH2O to a total volume of 20 mL. Testing materials were ig administered once at 0.20 mL 10 g-1 at 24 h intervals. Execu-tion via cervical vertebra dislocation was conducted 6 h after the last dose administration. Sternum bone was re-moved and the bone marrow cells were pulled out and mixed with fetal bovine serum immediately following the sacrifice. One drop of the mixture was smeared onto a clean slide and air-dried. The slides were briefly flamed, then fixed with immersion in 95% methanol for 10 min, and stained in ordinary staining jars with Giemsa working solu-tion for 15 min. Stained slides were washed gently with dd。

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