Natl Toxicol Program Tech Rep Ser. 1994 Dec;442:1-306.
p-Nitrobenzoic acid is produced in large volumes for organic synthesis and as an intermediate in the manufacture of pesticides, dyes, and industrial solvents. Groups of male and female F344/N rats and B6C3F1 mice were exposed to p-nitrobenzoic acid (>99% pure) in feed for 14 days, 13 weeks, or 2 years for toxicity and carcinogenicity studies. Genetic toxicology studies were conducted in in vitro assays with Salmonella typhimurium and cultured Chinese hamster ovary cells, and in studies of erythrocyte micronucleus formation in mice in the 13-week study. 14-DAY STUDY IN RATS: Groups of five male and five female rats were given 0, 2,500, 5,000, 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid in feed for 14 days. All rats survived until the end of the study. Male and female rats given 20,000 and 40,000 ppm lost weight. The final mean body weights of 10,000, 20,000, and 40,000 ppm males were 82%, 60%, or 52% that of the controls, and the final mean body weights of 10,000, 20,000, and 40,000 ppm females were 87%, 68%, and 65% that of the controls. There were no clinical findings that were characteristic of organ-specific toxicity. Absolute and relative spleen weights were significantly increased in rats exposed to 10,000, 20,000, and 40,000 ppm. There were decreases in erythrocyte count and hemoglobin and hematocrit values and increases in reticulocyte count, nucleated erythrocytes, and methemoglobin concentration that were most pronounced in the 20,000 and 40,000 ppm groups. Congestion of the spleen occurred in 10,000 ppm males and in 20,000 and 40,000 ppm females. Hypertrophy of the follicular epithelium of the thyroid gland was present in male and female rats exposed to 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid, while follicular hyperplasia was observed in the 40,000 ppm males and females. Atrophy of the testis was observed in 20,000 and 40,000 ppm males. Other lesions observed in 20,000 and 40,000 ppm rats included atrophy of the thymus in males and atrophy of the ovary, bone marrow, and thymus in females. 14-DAY STUDY IN MICE: Groups of five male and five female mice were given 0, 2,500, 5,000, 10,000, 20,000, or 40,000 ppm p-nitrobenzoic acid in feed for 14 days. Three males and two females given 40,000 ppm died during the study. All other animals survived until the end of the study. Male mice given 20,000 and 40,000 ppm and females given 20,000 ppm lost weight. Mean body weight gains of 20,000 and 40,000 ppm males and 10,000, 20,000, and 40,000 ppm females were significantly lower than those of the controls. There were no clinical findings related to organ-specific toxicity although lethargy and ataxia were observed in 40,000 ppm mice. Relative liver weights were significantly increased in 20,000 and 40,000 ppm males and females and in 10,000 ppm females. Absolute and relative thymus weights of 20,000 and 40,000 ppm males and of 10,000, 20,000, and 40,000 ppm females were reduced. No significant differences in hematology parameters occurred in exposed mice. Testicular degeneration was observed in three 20,000 ppm and two 40,000 ppm males. Bone marrow hemorrhage and atrophy occurred in 40,000 ppm females. 13-WEEK STUDY IN RATS: Groups of 10 male and 10 female rats were given 0, 630, 1,250, 2,500, 5,000, or 10,000 ppm pnitrobenzoic acid in feed for 13 weeks resulting in approximate daily doses of 40, 70, 160, 310, or 660 mg/kg to males and 40, 80, 170, 340, or 680 mg/kg to females. All rats survived until the end of the study. Mean body weight gains and final mean body weights were significantly less than those of the controls in 2,500, 5,000, and 10,000 ppm males and in 5,000 and 10,000 ppm females. There were no clinical findings related to organ-specific toxicity. Differences in spleen weights and hematology parameters characteristic of regenerative anemia were observed in males and females, primarily in groups given 10,000 ppm. The absolute and relative spleen weights were significantly increased in 10,000 ppm males and females and the relative spleen weights were significantly increased in 5,000 ppm males hts were significantly increased in 5,000 ppm males and females. Methemoglobin, Heinz bodies, and reticulocyte counts were increased and erythrocyte counts, hemoglobin, and hematocrit values were decreased in 10,000 ppm males and females. Congestion, pigmentation, and accumulation of macrophages in the spleen and pigmentation in the kidney occurred in 2,500, 5,000, and 10,000 ppm males. Congestion and pigmentation of the spleen occurred in 10,000 ppm females. A yellowish brown pigment (hemosiderin) in the spleen and kidney was associated with hemolytic anemia. Mild cytoplasmic hyaline droplet accumulation was present in renal tubule epithelial cells in 10,000 ppm males while karyomegaly was present in male and female rats exposed to 2,500, 5,000, and 10,000 ppm p-nitrobenzoic acid. A chemical-related testicular lesion, consisting of atrophy of the seminiferous tubules, occurred in 10,000 ppm males. 13-WEEK STUDY IN MICE: Groups of 10 male and 10 female mice were given 0, 1,250, 5,000, 10,000, or 20,000 ppm pnitrobenzoic acid in feed for 13 weeks resulting in approximate daily doses of 170, 330, 670, 1,900, or 4,000 mg/kg body weight to males and 240, 460, 970, 2,500, or 4,900 mg/kg to females. All mice survived until the end of the study, except one 1,250 ppm female that was killed accidentally. Final mean body weights and mean body weight gains of all exposed males and of 5,000, 10,000, and 20,000 ppm females were significantly lower than those of the controls. No clinical findings or differences in organ weights or histopathology related to organ-specific toxicity were observed in exposed mice. 2-YEAR STUDY IN RATS: Groups of 60 male and 60 female rats were given 0, 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid in feed for 2 years. Ten males and 10 females from each exposure group were evaluated at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of 1,250 and 2,500 ppm males were similar to that of the controls. Two-year survival of 5,000 ppm males was marginally greater than that of the controls and was attributed in part to a decrease in the severity of nephropathy and a decrease in the incidence of mononuclear cell leukemia. Survival of exposed females was similar to that of the controls. Mean body weights of 5,000 ppm males were 2% to 8% lower than those of the controls through week 80. Final mean body weights of exposed males were similar to that of the controls. Mean body weights of 5,000 ppm females were 2% to 9% lower than those of the controls during the first year of the study and were 10% to 16% lower during the second year of the study. Final mean body weights of exposed females were 97% (1,250 ppm), 92% (2;500 ppm), and 84% (5,000 ppm) that of the controls. Feed consumption by exposed males and females was similar to that by the controls. Dietary levels of 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid delivered approximately 50, 100, or 210 mg/kg body weight per day to males and 60, 125, or 250 mg/kg per day to females. There were no clinical findings attributable to organ-specific toxicity. Pathology Findings: There were increases in the incidences of clitoral gland adenoma and of clitoral gland adenoma or carcinoma (combined) (4/50, 14/49, 15/49, 15/50) in exposed females. The incidences of clitoral gland adenoma or carcinoma (combined) in the exposed groups (29% to 31%) exceeded the historical control mean incidence (11%) and range (2% to 21%) in female F344/N rats in recent 2-year NTP feed studies. The increased incidences of clitoral gland neoplasms were considered to be some evidence of carcinogenic activity in female rats exposed to p-nitrobenzoic acid. The incidences of hyperplasia of the clitoral gland in exposed females were marginally lower than that of the controls (10/50, 6/49, 6/ 49, 7/50). There was a chemical-related decrease in the severity of nephropathy in male rats. Male rat kidneys were examined using both single and step-section analyses, and the incidences of renal tubule neoplasms were not statistically greater than those of the controls. Mild hyaline droplet accumulation was observed in renal tubule epithelial cells in 10,000 ppm males in the 13-week study, but this effect was not severe enough to lead to a chemical-related neoplastic response in the 2-year study as has been observed with other chemicals. At the 15-month interim evaluation, hematologic parameters characteristic of a mild regenerative anemia and significant differences in spleen weights were noted in 5,000 ppm females. These differences included decreases in erythrocyte count, hemoglobin, and hematocrit, increases in spleen weights, and hemosiderin accumulation in splenic macrophages. At 2 years, significant decreases in the incidences of mononuclear cell leukemia were observed in 5,000 ppm males and 2,500 and 5,000 ppm females (males: 29/50, 35/50, 26/50, 2/50; females: 17/50, 11/50, 3/50, 0/50). While the mechanism for this decrease is unknown, decreases in the incidence of mononuclear cell leukemia have also been observed in 2year studies with other amine/nitro compounds. 2-YEAR STUDY IN MICE: Groups of 60 male and 60 female mice were given 0, 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid in feed for 2 years. Ten males and 10 females from each exposure group were evaluated at 15 months. Survival, Body Weights, Feed Consumption, and Clinical Findings: Two-year survival rates of exposed mice were similar to those of the controls. Mean body weights of 5,000 ppm males were 6% to 12% lower than those of the controls after week 17, and mean body weights of 5,000 ppm females were 12% to 24% lower than those of the controls after week 16. The final mean body weight of 5,000 ppm females was 19% less than that of the controls; final mean body weights of males were similar to that of the controls. Feed consumption by exposed mice was similar to that by the controls. Dietary levels of 1,250, 2,500, or 5,000 ppm p-nitrobenzoic acid delivered approximately 150, 300, or 675 mg/kg per day to males and 170, 365, or 905 mg/kg per day to females. There were no clinical findings of organ-specific toxicity. No chemical-related effects on hematology parameters were noted at the 15-month interim evaluation. Pathology Findings: There were no increases or decreases in neoplasms in male or female mice that were considered to be related to chemical administration. GENETIC TOXICOLOGY: p-Nitrobenzoic acid was mutagenic in Salmonella typhimurium strain TA100 with and without S9. No mutagenic activity was noted in strains TA98, TA1535, or TA1537, with or without S9. p-Nitrobenzoic acid induced sister chromatid exchanges and chromosomal aberrations in cultured Chinese hamster ovary cells in the absence of S9; with S9, results of both tests were negative. In vivo, no increase in micronuclei was observed in peripheral blood erythrocytes of male or female mice administered p-nitrobenzoic acid in dosed feed for 13 weeks. CONCLUSIONS: Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of p-nitrobenzoic acid in male F344/N rats exposed to 1,250, 2,500, or 5,000 ppm. There was some evidence of carcinogenic activity of p-nitrobenzoic acid in female F344/N rats based on increases in the incidences of clitoral gland adenoma and of clitoral gland adenoma or carcinoma (combined). There was no evidence of carcinogenic activity of p-nitrobenzoic acid in male or female B6C3F1 mice exposed to 1,250, 2,500, or 5,000 ppm. There were chemical-related decreases in the incidences of mononuclear cell leukemia in exposed male and female rats. p-Nitrobenzoic acid caused mild hematologic toxicity in female rats. Synonyms: 4-Nitrobenzoic acid; nitrodracylic acid; p-nitrobenzenecarboxylic acid; p-carboxynitrobenzene
对硝基苯甲酸大量生产用于有机合成,并作为制造农药、染料和工业溶剂的中间体。将雄性和雌性F344/N大鼠以及B6C3F1小鼠分组,使其在饲料中接触对硝基苯甲酸(纯度>99%)14天、13周或2年,以进行毒性和致癌性研究。采用鼠伤寒沙门氏菌和培养的中国仓鼠卵巢细胞进行体外试验,并在13周研究中对小鼠红细胞微核形成进行研究,开展遗传毒理学研究。
大鼠14天研究:将每组五只雄性和五只雌性大鼠在饲料中给予0、2500、5000、10000、20000或40000 ppm的对硝基苯甲酸,持续14天。所有大鼠均存活至研究结束。给予20000和40000 ppm的雄性和雌性大鼠体重减轻。10000、20000和40000 ppm雄性大鼠的最终平均体重分别为对照组的82%、60%或52%,10000、20000和40000 ppm雌性大鼠的最终平均体重分别为对照组的87%、68%和65%。没有出现具有器官特异性毒性特征的临床症状。接触10000、20000和40000 ppm的大鼠脾脏绝对重量和相对重量显著增加。红细胞计数、血红蛋白和血细胞比容值降低,网织红细胞计数、有核红细胞和高铁血红蛋白浓度增加,在20000和40000 ppm组中最为明显。10000 ppm雄性大鼠以及20000和40000 ppm雌性大鼠出现脾脏充血。接触10000、20000或40000 ppm对硝基苯甲酸的雄性和雌性大鼠甲状腺滤泡上皮细胞肥大,而在40000 ppm雄性和雌性大鼠中观察到滤泡增生。在20000和40000 ppm雄性大鼠中观察到睾丸萎缩。在20000和40000 ppm大鼠中观察到的其他病变包括雄性大鼠胸腺萎缩以及雌性大鼠卵巢、骨髓和胸腺萎缩。
小鼠14天研究:将每组五只雄性和五只雌性小鼠在饲料中给予0、2500、5000、10000、20000或40000 ppm的对硝基苯甲酸,持续14天。给予40000 ppm的三只雄性和两只雌性小鼠在研究期间死亡。所有其他动物均存活至研究结束。给予20000和40000 ppm的雄性小鼠以及给予20000 ppm的雌性小鼠体重减轻。20000和40000 ppm雄性小鼠以及10000、20000和40000 ppm雌性小鼠的平均体重增加显著低于对照组。没有出现与器官特异性毒性相关的临床症状,尽管在40000 ppm小鼠中观察到嗜睡和共济失调。20000和40000 ppm雄性和雌性小鼠以及10000 ppm雌性小鼠的相对肝脏重量显著增加。20000和4,000 ppm雄性小鼠以及10000、20000和40000 ppm雌性小鼠的胸腺绝对重量和相对重量降低。接触的小鼠血液学参数没有显著差异。在三只20000 ppm和两只40000 ppm雄性小鼠中观察到睾丸退化。40000 ppm雌性小鼠出现骨髓出血和萎缩。
大鼠13周研究:将每组十只雄性和十只雌性大鼠在饲料中给予0、630、1250、2500、5000或10000 ppm的对硝基苯甲酸,持续13周,雄性大鼠的日剂量约为40、70、160、310或660 mg/kg,雌性大鼠的日剂量约为40、80、170、340或680 mg/kg。所有大鼠均存活至研究结束。2500、5000和10000 ppm雄性大鼠以及5000和10000 ppm雌性大鼠的平均体重增加和最终平均体重显著低于对照组。没有出现与器官特异性毒性相关的临床症状。在雄性和雌性大鼠中观察到脾脏重量和再生性贫血特征性血液学参数的差异,主要在给予10000 ppm的组中。10000 ppm雄性和雌性大鼠的脾脏绝对重量和相对重量显著增加,5000 ppm雄性大鼠的相对脾脏重量显著增加。5000 ppm雄性和雌性大鼠的高铁血红蛋白、海因茨小体和网织红细胞计数增加,红细胞计数、血红蛋白和血细胞比容值降低。2500、5000和10000 ppm雄性大鼠出现脾脏充血与色素沉着、巨噬细胞积聚以及肾脏色素沉着。10000 ppm雌性大鼠出现脾脏充血和色素沉着。脾脏和肾脏中的黄褐色色素(含铁血黄素)与溶血性贫血有关。10000 ppm雄性大鼠肾小管上皮细胞出现轻度细胞质透明滴积聚,而接触2500、5000和10000 ppm对硝基苯甲酸的雄性和雌性大鼠出现核肿大。10000 ppm雄性大鼠出现一种与化学物质相关的睾丸病变,即曲细精管萎缩。
小鼠'13周研究:将每组十只雄性和十只雌性小鼠在饲料中给予0、1250、5000、10000或20000 ppm的对硝基苯甲酸,持续13周,雄性大鼠的日剂量约为170、330、670、1900或4000 mg/kg体重,雌性大鼠的日剂量约为240、460、970、2500或4900 mg/kg。所有小鼠均存活至研究结束,除一只1250 ppm雌性小鼠意外死亡。所有接触的雄性小鼠以及5000、10000和20000 ppm雌性小鼠的最终平均体重和平均体重增加显著低于对照组。在接触的小鼠中未观察到与器官特异性毒性相关的临床症状、器官重量差异或组织病理学差异。
大鼠2年研究:将每组60只雄性和60只雌性大鼠在饲料中给予0、1250、2500或5000 ppm的对硝基苯甲酸,持续2年。在15个月时对每个暴露组的十只雄性和十只雌性大鼠进行评估。
存活、体重、饲料消耗和临床症状:1250和2500 ppm雄性大鼠的两年存活率与对照组相似。5000 ppm雄性大鼠的两年存活率略高于对照组部分原因是肾病严重程度降低和单核细胞白血病发病率降低。暴露雌性大鼠的存活率与对照组相似。到第80周,5000 ppm雄性大鼠的平均体重比对照组低2%至8%。暴露雄性大鼠的最终平均体重与对照组相似。在研究的第一年,5000 ppm雌性大鼠的平均体重比对照组低2%至9%,在研究的第二年低10%至16%。暴露雌性大鼠的最终平均体重分别为对照组的97%(1250 ppm)、92%(2500 ppm)和84%(5000 ppm)。暴露雄性和雌性大鼠的饲料消耗与对照组相似。1250、2500或5000 ppm对硝基苯甲酸的饮食水平分别为雄性大鼠每天约50、100或210 mg/kg体重,雌性大鼠每天约60、125或250 mg/kg。没有出现可归因于器官特异性毒性的临床症状。病理结果:暴露雌性大鼠的阴蒂腺腺瘤和阴蒂腺腺瘤或癌(合并)发病率增加(4/50、14/49、15/49、15/50)。暴露组阴蒂腺腺瘤或癌(合并)的发病率(29%至31%)超过了最近两年NTP饲料研究中雌性F344/N大鼠的历史对照平均发病率(11%)和范围(2%至21%)。阴蒂腺肿瘤发病率增加被认为是雌性大鼠接触对硝基苯甲酸后致癌活性的一些证据。暴露雌性大鼠阴蒂腺增生的发病率略低于对照组(10/50、6/49、6/49、7/50)。雄性大鼠的肾病严重程度出现与化学物质相关的降低。对雄性大鼠肾脏进行单切片和连续切片分析,肾小管肿瘤的发病率在统计学上不高于对照组。在13周研究中,10000 ppm雄性大鼠的肾小管上皮细胞观察到轻度透明滴积聚,但这种影响不够严重,在2年研究中未导致与化学物质相关的肿瘤反应,而其他化学物质已观察到这种反应。在15个月的中期评估中,5000 ppm雌性大鼠出现轻度再生性贫血特征性血液学参数以及脾脏重量的显著差异。这些差异包括红细胞计数、血红蛋白和血细胞比容降低,脾脏重量增加,以及脾巨噬细胞中含铁血黄素积聚。在2年时,5000 ppm雄性大鼠以及2500和5000 ppm雌性大鼠的单核细胞白血病发病率显著降低(雄性:29/50、35/50、26/50、2/50;雌性:17/50、11/50、3/50、0/50)。虽然这种降低的机制尚不清楚,但在其他胺/硝基化合物的2年研究中也观察到单核细胞白血病发病率降低。
小鼠2年研究:将每组60只雄性和60只雌性小鼠在饲料中给予0、1250、2500或5000 ppm的对硝基苯甲酸,持续2年。在15个月时对每个暴露组的十只雄性和十只雌性小鼠进行评估。
存活、体重、饲料消耗和临床症状:暴露小鼠的两年存活率与对照组相似。17周后,5000 ppm雄性小鼠的平均体重比对照组低6%至12%,16周后,5000 ppm雌性小鼠的平均体重比对照组低12%至24%。5000 ppm雌性小鼠的最终平均体重比对照组低19%;雄性小鼠的最终平均体重与对照组相似。暴露小鼠的饲料消耗与对照组相似。1250、2500或5000 ppm对硝基苯甲酸的饮食水平分别为雄性大鼠每天约150、300或675 mg/kg,雌性大鼠每天约170、365或905 mg/kg。没有出现器官特异性毒性的临床症状。在15个月的中期评估中,未观察到与化学物质相关的血液学参数影响。
雄性或雌性小鼠的肿瘤发病率没有增加或减少被认为与化学物质给药有关。
对硝基苯甲酸在有或没有S9的情况下对鼠伤寒沙门氏菌TA100菌株具有致突变性。在有或没有S9的情况下,TA98、TA1~35或TA1537菌株未观察到致突变活性。在没有S9的情况下,对硝基苯甲酸在培养的中国仓鼠卵巢细胞中诱导姐妹染色单体交换和染色体畸变;在有S9的情况下,两项试验结果均为阴性。在体内,给予对硝基苯甲酸的雄性或雌性小鼠在含药饲料中喂养13周后,外周血红细胞中未观察到微核增加。
在这些2年饲料研究的条件下,没有证据表明接触1250、2500或5000 ppm对硝基苯甲酸的雄性F344/N大鼠具有致癌活性。基于阴蒂腺腺瘤和阴蒂腺腺瘤或癌(合并)发病率增加,有一些证据表明对硝基苯甲酸对雌性F344/N大鼠具有致癌活性。没有证据表明接触1250、2500或5000 ppm对硝基苯甲酸的雄性或雌性B6C3F1小鼠具有致癌活性。暴露的雄性和雌性大鼠单核细胞白血病发病率出现与化学物质相关的降低。对硝基苯甲酸对雌性大鼠造成轻度血液学毒性。
4-硝基苯甲酸;硝基水杨酸;对硝基苯羧酸;对羧基硝基苯