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Abstract
Tris(chloropropyl) phosphate (TCPP) is used as a flame retardant in textiles, furniture (flexible polyurethane foam), and other related products. In addition, it is manufactured for use in construction materials (rigid polyurethane foam), electronic products, paints, coatings, and adhesives. Several flame retardants have been removed from products in commerce because of toxicity concerns, and TCPP has been considered as a replacement flame retardant for use in these products. Because of concerns for increased use, and thus increased human exposure, the Consumer Product Safety Commission nominated TCPP for toxicological testing by the National Toxicology Program. Additional information on the evaluation of the potential toxicity of TCPP is available at the Program’s website (https://ntp.niehs.nih.gov/testing/status/agents/ts-m20263.html). The purpose of this report is to summarize and discuss TCPP effects on prenatal development. In these studies, time-mated female Sprague Dawley (Hsd:Sprague Dawley® SD®) rats received TCPP (95.7–97% pure) in 0.5% methylcellulose by gavage from implantation on gestation day (GD) 6 to the day before expected parturition (GD 20). Evidence of TCPP-related maternal and fetal toxicity was examined in the dose range-finding study followed by the standard prenatal developmental toxicity study.
Dose Range-finding Prenatal Developmental Toxicity Study:
Groups of 11 time-mated female rats were administered 0, 300, 650, or 1,000 mg TCPP/kg body weight per day (mg/kg/day) in 0.5% aqueous methylcellulose by gavage from GD 6 to GD 20. Vehicle control (0 mg/kg) animals received aqueous methylcellulose.
Maternal toxicity was observed in the 1,000 mg/kg group as evidenced by 7 of 11 dams being either found dead or euthanized moribund. Associated clinical observations in the 1,000 mg/kg group included convulsion, tremors, prone, gasping, hypoactivity, hunched posture, nasal discharge, stained fur, piloerection, salivation, and rooting (pre- and postdosing), which occurred throughout gestation. One female in the 650 mg/kg group was euthanized moribund on GD 16 with associated clinical observations including cold to touch, hypoactivity, paleness, ataxia, and labored breathing, which may have been related to TCPP exposure. All vehicle control and 300 mg/kg animals survived to study termination. No TCPP-related effects were found on maternal body weights, body weight gain, or feed consumption from GD 6 to GD 20. Additionally, there were no significant exposure-related effects on postimplantation loss, fetal body weights, or fetal sex ratio, although limited litters were available for assessment in the 1,000 mg/kg TCPP group because of maternal toxicity. Finally, there were no significant exposure-related external fetal findings (including examination of the palate).
Prenatal Developmental Toxicity Study:
Because of the maternal toxicity observed at 1,000 mg/kg in the dose ranging-finding study, groups of 25 time-mated female rats were administered 0 (n = 50), 162.5, 325, or 650 mg TCPP/kg/ body weight per day in 0.5% aqueous methylcellulose by gavage from GD 6 to GD 20. Vehicle control (0 m/kg) animals received aqueous methylcellulose. Animals were added to the vehicle control group to obtain historical control data for both maternal and fetal findings in this strain of rat. In this study, TCPP was well tolerated and no exposure-related effects occurred on mortality, maternal body weights, body weight gains, or feed consumption during gestation. Low incidences of clinical observations including nasal discharge, salivation, twitches, ataxia, piloerection, audible respiratory sounds, and hyperactivity were observed in the 650 mg/kg group. Adverse clinical observations were not observed in other groups exposed to TCPP. There were no notable placental or other maternal gross observations at necropsy except for dose-related increases in absolute (9%, 16%, and 26% at 162.5, 325, and 650 mg/kg, respectively) and relative liver weights.
No significant effects of TCPP were observed on postimplantation loss, mean fetal body weights, or fetal sex ratio. Likewise, no biologically relevant exposure-related malformations were found in external, visceral, and skeletal fetal exams of groups exposed to TCPP.
Conclusions:
Under the conditions of the prenatal study, no evidence of developmental toxicity† of TCPP was found in Hsd:Sprague Dawley® SD® rats administered 162.5, 325, or 650 mg/kg in the absence of overt maternal toxicity.
Trade names: Amgard TMCP, Antiblaze 80, Antiblaze TMCP, Fyrol PCF
†See Explanation of Levels of Evidence for Developmental Toxicity.
Summary of Exposure-related Findings in Rats in the Prenatal Developmental Toxicity Gavage Study of Tris(chloropropyl) Phosphate
0 mg/kga | 162.5 mg/kg | 325 mg/kg | 650 mg/kg | |
---|---|---|---|---|
Maternal Parameters | ||||
Animals on Study | 50 | 25 | 25 | 25 |
Number Pregnant | 44 | 21 | 21 | 20 |
Number Died or Euthanized Moribund | 0 | 0 | 0 | 0 |
Clinical Observations | None | None | None | Ataxia, audible respiratory sounds, hyperactivity, nasal discharge, piloerection, salivation, and twitches |
Body Weight and Feed Consumptionb | ||||
Necropsy Body Weight | 382.3 ± 3.1 | 386.3 ± 4.2 | 384.3 ± 5.1 | 379.4 ± 8.2 |
Body Weight Change GD 6 to 21 | 139.6 ± 2.5 | 143.6 ± 3.0 | 139.9 ± 3.8 | 137.6 ± 6.3 |
Feed Consumption GD 6 to 21 | 22.8 ± 0.23 | 22.5 ± 0.33 | 22.9 ± 0.33 | 22.2 ± 0.42 |
Necropsy Observations | ||||
Organ Weights | None | 9% ↑ in absolute liver weight | 16% ↑ in absolute liver weight | 26% ↑ in absolute liver weight |
Developmental/Fetal Parameters | ||||
Number of Litters Examined | 44 | 21 | 21 | 20 |
Number of Live Fetuses Evaluated | 599 | 300 | 270 | 259 |
Number of Live Fetuses per Litterc | 13.61 ± 0.30 | 14.29 ± 0.37 | 12.86 ± 0.62 | 12.95 ± 0.91 |
Number of Early Resorptionsd | 22 | 11 | 11 | 15 |
Number of Late Resorptionsd | 2 | 0 | 0 | 0 |
Number of Dead Fetusesd | 1 | 0 | 2 | 0 |
Number of Whole Litter Resorptions | 0 | 0 | 0 | 0 |
Percent Postimplantation Lossc | 3.81 ± 1.13 | 3.42 ± 0.99 | 4.33 ± 1.19 | 7.17 ± 4.50 |
Fetal Body Weight per Litterb | 5.29 ± 0.04 | 5.22 ± 0.06 | 5.42 ± 0.08 | 5.22 ± 0.07 |
Male Fetal Weight per Litter | 5.42 ± 0.05 | 5.35 ± 0.06 | 5.47 ± 0.06 | 5.34 ± 0.06 |
Female Fetal Weight per Litter | 5.17 ± 0.04 | 5.08 ± 0.06 | 5.30 ± 0.09 | 5.09 ± 0.07 |
Gravid Uterine Weightb | 98.89 ± 1.93 | 101.98 ± 2.23 | 95.76 ± 4.06 | 91.78 ± 5.91 |
External Findings | None | None | None | None |
Visceral Findings | None | None | None | None |
Skeletal Findings | None | None | None | None |
Level of Evidence of Developmental Toxicity: No evidence |
GD = gestation day.
- a
This study had two vehicle control groups. Data from both vehicle control groups were combined and are presented here.
- b
Results given in grams. Data are displayed as mean ± standard error.
- c
Data are displayed as mean ± standard error.
- d
No statistical analyses were performed on number of early resorptions, number of late resorptions, or number of dead fetuses.
Contents
- Foreword
- Collaborators
- Contributors
- Explanation of Levels of Evidence for Developmental Toxicity
- Peer Review
- Publication Details
- Acknowledgments
- Introduction
- Materials and Methods
- Results
- Discussion
- Conclusions
- References
- Appendix A. Chemical Characterization and Dose Formulation Studies
- Appendix B. Ingredients, Nutrient Composition, and Contaminant Levels in NIH-07 Rat and Mouse Ration
- Appendix C. Sentinel Animal Program
- Appendix D. Summary of Peer Review Panel Comments
- Appendix E. Supplemental Files
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- NTP Developmental and Reproductive Toxicity Technical Report on the Prenatal Dev...NTP Developmental and Reproductive Toxicity Technical Report on the Prenatal Development Studies of Tris(chloropropyl) Phosphate (CASRN 13674-84-5) in Sprague Dawley (Hsd:Sprague Dawley® SD®) Rats (Gavage Studies)
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