Suda M, Tsuruta H, Honma T
National Institute of Industrial Health (Ministry of Labour), Kawasaki, Japan.
Ind Health. 1999 Jan;37(1):22-7. doi: 10.2486/indhealth.37.22.
The correlations of lethal doses of various industrial chemicals for rats and mice with occupational exposure limit values were investigated. 50% lethal dose (LD50) values obtained by oral (p.o.) and intraperitoneal (i.p.) injection and 50% lethal concentration (LC50) values obtained by inhalation exposure were collected from Registry of Toxic Effects of Chemical Substances (RTECS). Threshold Limit Value (Time-Weighted Average) (TLVs-TWA) and Threshold Limit Value (Short Term Exposure Limit) (TLVs-STEL) recommended by American Conference of Governmental Industrial Hygienists (ACGIH) were used as exposure limits. TLVs-TWA or TLVs-STEL and LD50 or LC50 values obtained for the rats were plotted on logarithmic scales on the ordinate and abscissa, respectively. High correlations were obtained between these parameters. The order of correlations was: TLVs-STEL vs. LC50s > TLVs-TWA vs. LC50s > TLVs-TWA vs. LD50s i.p. > TLVs vs. LD50s p.o. The same calculations for the relationship between TLVs and lethal doses in mice were also performed. The order of the three types of correlations was same as that of the rats; however, correlation coefficients for TLVs-STEL vs. LC50s and for TLVs-TWA vs. LC50s obtained in mice were smaller than those in rats. TLVs-TWA are, therefore, well correlated with LC50 values rather than LD50 values, particularly with those in rats. High correlations between TLVs-STEL vs. LC50s were also obtained, as had been expected before calculation. The equation: TLV-TWA = 10b x (LC50)a can be obtained from these plottings, where the values a and b are taken from each linear regression line. TLV-TWA for each chemical can be calculated by using LC50 and the equation. The upper and lower 95% confidence limits for calculated TLV-TWA were TLV-TWA (calculated from LC50) x 22.9 and TLV-TWA (calculated)/22.9, respectively, where LC50 for rats expressed in ppm x hr was used.
研究了各种工业化学品对大鼠和小鼠的致死剂量与职业接触限值之间的相关性。通过口服(p.o.)和腹腔注射(i.p.)获得的50%致死剂量(LD50)值以及通过吸入暴露获得的50%致死浓度(LC50)值取自化学物质毒性效应登记数据库(RTECS)。美国政府工业卫生学家会议(ACGIH)推荐的阈限值(时间加权平均)(TLVs-TWA)和阈限值(短期暴露限值)(TLVs-STEL)用作接触限值。将大鼠的TLVs-TWA或TLVs-STEL以及LD50或LC50值分别以对数尺度绘制在纵坐标和横坐标上。这些参数之间获得了高度相关性。相关性顺序为:TLVs-STEL与LC50s的相关性>TLVs-TWA与LC50s的相关性>TLVs-TWA与腹腔注射LD50s的相关性>TLVs与口服LD50s的相关性。还对小鼠中TLVs与致死剂量之间的关系进行了相同的计算。三种类型相关性的顺序与大鼠相同;然而,小鼠中TLVs-STEL与LC50s以及TLVs-TWA与LC50s的相关系数小于大鼠中的相关系数。因此,TLVs-TWA与LC50值的相关性良好,而非与LD50值,特别是与大鼠中的LC50值。如计算前预期的那样,TLVs-STEL与LC50s之间也获得了高度相关性。从这些绘图中可以得到方程:TLV-TWA = 10b×(LC50)a。其中a和b的值取自每条线性回归线。每种化学品的TLV-TWA可通过使用LC50和该方程来计算。计算得到的TLV-TWA的95%置信上限和下限分别为TLV-TWA(根据LC50计算)×22.9和TLV-TWA(计算值)/22.9,其中使用的是大鼠以ppm·hr表示的LC50。