Jeffrey M. Charles

Chronic Dietary Toxicity/Oncogenicity Studies on 2,4-Dichlorophenoxyacetic Acid in Rodents

Forms of 2,4-dichlorophenoxyacetic acid (collectively known as 2,4-D) are herbicides used to control a wide variety of broadleaf and woody plants. Doses in the 2-year chronic/oncogenicity rat study were 0, 5, 75, and 150 mg/kg/day. The chronic toxicity paralleled subchronic findings, and a NOEL of 5 mg/kg/day was established. A slight increase in astrocytomas observed (in males only) at 45 mg/kg/day in a previously conducted chronic rat study was not confirmed in the present study at the high dose of 150 mg/kg/ day. Doses in the 2-year mouse oncogenicity studies were 0, 5, 150, and 300 mg/kg/day for females and 0, 5, 62.5, and 125 mg/ kg/day for males. No oncogenic effect was noted in the study. In summary, the findings of these studies indicate low chronic toxicity of 2,4-D and the lack of oncogenic response to 2,4-D following chronic dietary exposure of 2,4-D in the rat and mouse.

Evaluation of the genotoxicity of 2,4-dichlorophenoxyacetic acid and its derivatives in mammalian cell cultures.

2,4-dichlorophenoxyacetic acid and its derivatives (collectively known as 2,4-D) are herbicides used to control a wide variety of broadleaf and woody plants. The genetic toxicity of an ester (2,4-D 2-butoxyethylester) and two salts (2,4-D isopropylamine and 2,4-D triisopropanolamine) was investigated in cultured mammalian cells. The end points used were the induction of chromosomal aberrations in primary cultures of rat lymphocytes and forward mutations at the HGPRT locus of Chinese hamster ovary cells. There was no evidence of genotoxicity for the test materials in the experimental systems used. These results were consistent with the general lack of genotoxic potential for 2,4-D in a number of other test systems.

Ames assays and unscheduled DNA synthesis assays on 2,4-dichlorophenoxyacetic acid and its derivatives

2,4-dichlorophenoxyacetic acid and several of its derivatives (collectively known as 2,4-D) are herbicides used to control a wide variety of broadleaf and woody plants. The genetic toxicity in vitro of 2,4-D and seven of its salts and esters were examined by employing gene mutation in bacteria (Ames test) and induction of DNA damage and repair in rat hepatocytes. In addition, an in vivo unscheduled DNA synthesis (UDS) assay was performed on 2,4-D. There were no indications of genotoxic potential for 2,4-D acid, or any of its derivatives, in these assays. These results are consistent with the reported lack of carcinogenic potential for 2,4-D in both mice and rats.

In vivo micronucleus assays on 2,4-dichlorophenoxyacetic acid and its derivatives.

The potential for 2,4-D and seven of its salts and esters to induce cytogenetic abnormalities in mammalian cells in vivo was investigated in the mouse bone marrow micronucleus test. All the test materials were administered to male and female mice by oral gavage and the frequencies of micronucleated polychromatic erythrocytes (MN-PCE) in the bone marrow were determined at intervals of 24, 48 and 72 h following dosing. There were no significant increases in the incidence of MN-PCE in the treated mice at any of the bone marrow sampling times. These results are consistent with the reported lack of in vitro genetic toxicity for these materials in various in vitro genotoxicity assays as well as the absence of carcinogenic potential for 2,4-D in both mice and rats.

Comparative Subchronic and Chronic Dietary Toxicity Studies on 2,4-Dichlorophenoxyacetic Acid, Amine, and Ester in the Dog

Forms of 2,4-dichlorophenoxyacetic acid (2,4-D) are herbicides used in the control of a wide variety of broadleaf and woody plants. Subchronic toxicity studies in dogs were conducted on three forms of 2,4-D: the parent form, 2,4-D acid (ACID); 2,4-D dimethylamine salt (DMA); and 2,4-D 2-ethylhexyl ester (2-EHE). The three studies were designed to allow for comparison of the toxicity of the three forms. Doses in the subchronic studies, on an acid equivalent basis, were 0, 0.5 (ACID only), 1.0, 3.75, and 7.5 mg/kg/day. Treatment related findings in the three studies included reductions in body weight gain, and food consumption, and minor increases in blood urea nitrogen, creatinine, and alanine aminotransferase. The data from the three subchronic studies demonstrated the comparable toxicity of ACID, DMA, and 2-EHE and support a subchronic no observed adverse effect level (NOAEL) of 1.0 mg/kg/day for all three forms. Due to the similarity in toxicity of the three forms of 2,4-D, a 1-year chronic toxicity study was performed on the parent ACID to fully characterize the potential toxicity of 2,4-D in the dog. ACID was well tolerated at doses of 0, 1.0, 5.0, and 7.5 mg/kg/day. The clinical pathology alterations were similar to those seen in the subchronic studies and were not progressive. The histopathology alterations observed were not severe in nature and the no observed effect level in the chronic study was determined to be 1.0 mg/kg/day. There was no indication of any immunotoxic or oncogenic response in the studies. In conclusion, the findings of these studies indicate comparable toxicity among representative forms of 2,4-D and their generally low toxicity following subchronic and chronic dietary exposure in the dog.

Evaluation of the in vitro genetic toxicity of 4-(2,4-dichlorophenoxy)butyric acid

The herbicide 4-(2,4-dichlorophenoxy)butyric acid (2,4-DB) is principally used in the USA on peanuts, soybeans and alfalfa. In Europe, it is used on undersown spring barley and grassland (with clover). The genetic toxicity in vitro of the dimethylamine salt of 2,4-DB was examined by employing a range of end points including gene mutation in bacteria (Ames test) and mammalian cell cultures (CHO/HGPRT assay), cytogenetic abnormalities in mammalian cells (CHO/chromosomal aberration assay), and induction of DNA damage and repair in rat hepatocytes. There were no indications of genotoxic potential for 2,4-DB in the first three of these assays. One of the two criteria for a positive response in the UDS assay was exceeded but the increases did not exceed the second criteria for a positive response. The test material was therefore evaluated as weakly active in this assay. The weight of the evidence clearly indicates that 2, 4-DB is not genotoxic to mammals and are consistent with the reported lack of carcinogenic potential for 2,4-DB in both mice and rats.

Chronic inhalation exposures of Fischer 344 rats to 1,6-hexamethylene diisocyanate did not reveal a carcinogenic potential.

The polyisocyanates of 1,6-hexamethylene diisocyanate (HDI) find widespread commercial use as components of paints and in the formulation of light-stable polyurethane coating materials. This 2-year study assessed the oncogenicity of the diisocyanate monomer HDI in male and female Fischer-344 rats exposed 6 h/day, 5 days/week to mean analytical air concentrations of 0, 0.005, 0.025, and 0.164 ppm HDI. During the in-life phase, transient eye irritation was observed in 0.164 ppm males, and a slight body weight decrease (5%) in the 0.164 ppm females during the second year of exposure. There were no exposure-related effects on mortality. Compound-related, non-neoplastic histopathologic changes were limited to the respiratory tract and changes were characterized by epithelial tissue reaction to the acute irritant properties of HDI vapor. For tissues of the nasal cavity, the major histopathologic findings were degeneration of the olfactory epithelium characterized by destruction of the epithelial architecture often with narrowing or atrophy and occasional focal erosion or ulceration. In addition, there was variable degeneration of the respiratory epithelium with hyperkeratosis of the epithelium, epithelial and mucus secretory cell hyperplasia, squamous metaplasia, chronic-active inflammation, and errosive or ulcerative changes. These tissue effects along with a statistically significant decrease in body weight of female rats demonstrated attainment of a maximum tolerated dose. There was no evidence of progression of these changes in the nasal epithelium to neoplasia nor evidence of any compound-related neoplastic lesions for any of the other tissues examined. Therefore, it is concluded that HDI did not show a carcinogenic potential in this study.

Developmental Toxicity Studies in Rats and Rabbits and Two-Generation Reproduction Study in Rats on 4-(2,4-DichIorophenoxy)butyric Acid

4-(2,4-Dichlorophenoxy)butyric acid (2,4-DB) is principally used in the USA on peanuts, soybeans, and alfalfa. The developmental toxicity in rats (25/group) was studied at dose levels of 0, 31.25, 62.5, and 125 mg/kg/day. The maximum tolerated dose (MTD) was clearly exceeded at 125 mg/kg/day, as evidenced by a net weight loss in the dams during the dosing period, resulting in four dams totally resorbing their fetuses. The no-observed-effect level (NOEL) for maternal toxicity was 31.25 mg/kg/day based on a slight, but consistent, body weight effect at 62.5 mg/kg/day. The NOEL for embryo/fetal toxicity was 31.25 mg/kg/day based on increases in fetal skeletal variations at 62.5 mg/kg/day. The developmental toxicity in rabbits (16/group) was evaluated at dose levels of 0, 15, 30, or 60 mg/kg/day. The MTD was clearly exceeded at 60 mg/kg/day as evidenced by severe weight-gain depression during the dosing period in the does, resulting in two does aborting and two does being sacrificed in a moribund condition. The NOEL for maternal toxicity was 30 mg/kg/day based on the above noted effects at 60 mg/kg/day. The NOEL for embryo/fetal toxicity was 60 mg/kg/day due to the lack of any effects noted. The reproductive toxicity of 2,4-DB was investigated in a two-generation study with two litters bred per generation. Rats (28/sex/group for the F0 generation and 24/sex/group for the F1 generation) were fed dietary concentrations of 0, 60,300, and 1500 ppm during the first generation, but because it proved impossible to rear a filial generation at 1500 ppm, the second generation was continued at doses of 0, 60, and 300 ppm. Mating performance, fertility, and pregnancy rate were unimpaired. A NOEL for reproductive toxicity was 1500 ppm (111.8 mg/kg/day for males and 110.6 mg/kg/day for females); however, severe postnatal toxicity was produced at this level. The NOEL for postnatal toxicity was 300 ppm (22.5-32.6 mg/kg/day for males and 26.4-36.7 mg/kg/day for females depending on the generation). The NOELs for developmental and reproductive toxicity are in general agreement with those reported for 2,4-dichlorophenoxyacetic acid (2,4-D), the major metabolite of 2,4-DB.