Tris(2-butoxyethyl) phosphate (TBEP) is a major organophosphorus flame retardant and has been widely increasing as a substitute for brominated flame retardants. TBEP may have adverse effects on human health; however, its impact on immune and allergic responses remains largely uncharacterized. In this study, the effects of low-dose TBEP comparable with the level of actual human exposure to that of human tolerable daily intake on allergic asthmatic mice were explored. Five-week-old C3H/HeJSlc male mice consumed a diet containing approximately 0.02, 0.2 or 2 μg/kg/day TBEP and were intratracheally administrated ovalbumin (OVA) (1 μg/mouse every 2 weeks from 5 to 11 weeks of age). Exposure to 2 μg/kg/day TBEP with OVA tended to enhance allergic pulmonary inflammation and significantly elevated mRNA levels of interleukin-5, eotaxin-1 and estrogen receptor alpha (ERα) compared with OVA alone. In mediastinal lymph nodes (MLNs), TBEP (0.2 or 2 μg/kg/day) with OVA significantly increased in total cell number and promoted conventional dendritic cell activation than OVA alone; MLN cell proliferation by OVA restimulation was also enhanced in these groups. In the bone marrow (BM), TBEP (0.02 or 0.2 μg/kg/day) with OVA resulted in a net decrease in total cell number and fraction of CCR2 + Gr-1 + cells; the fraction of Gr-1 + cells increased. In conclusion, oral exposure to low-dose TBEP levels equivalent to tolerable daily intake may exacerbate allergic pulmonary inflammation by promoting a skewed T-helper 2 cell response, upregulation of ERα and dysregulation of both MLN and BM microenvironments. K E Y W O R D S allergic asthma, estrogen receptor, low-dose effects, organophosphorus flame retardants, Th2 response, tris(2-butoxyethyl) phosphate 1 | INTRODUCTION Flame retardants (FRs) are used globally to meet flammability standards for building materials, textiles and appliances. Because of their toxicity, persistence in the environment and bioaccumulation, brominated FRs, including polybrominated diphenyl ethers, have been banned or voluntarily phased out in many countries. There is growing demand for less toxic alternatives (van der Veen & de Boer, 2012). In particular, the use of organophosphorus FRs (OPFRs) as FRs and plasticizers in consumer products, including plastics, textiles, paints and furniture, is gaining popularity (Marklund, Andersson, & Haglund, 2005). In Japan, approximately 100 000 tons of FR materials are used per year, of which about 27% were OPFRs (Ministry of the Environment in Japan, 2017). In the United States, the Agency for Toxic Substances and Disease Registry reports that OPFRs account for 11.5% of the total consumption of FRs (Agency for Toxic