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Phosphate flame retardants (PFRs) have been proposed as an alternative to brominated flame retardants and are increasingly used as flame retardants and plasticizers in various applications such as building materials, textiles, and electrical and electronic equipment.
However, with the introduction of organophosphate esters (OPEs) into the environment, the environmental problems caused by them have gradually attracted the attention of environmental scientists and become another hot spot in the research of new organic pollutants.
To aid in the study of these compounds, Alfa Chemistry provides a number of PFRs for use as reference standards.
OPEs enter the environment and are widely present in air, dust, water, soil, sediment and sludge. Numerous studies have focused on the occurrence of OPEs in indoor and aquatic environments, as humans have greater access to both substrates.
In addition, the broad physicochemical properties of OPEs lead to their diverse environmental behaviors, including phase distribution, migration, and degradation, which influence the pathways and levels of human exposure to these chemicals.
OPEs in the environment [1]
Given the structural similarities of OPEs to organophosphorus pesticides, uncertainty about their toxicity to biota and potential risks to environmental health has drawn increasing attention. Neurotoxicity, developmental and reproductive toxicity, and endocrine disrupting effects have been reported.
A review assessed the risks to surface water and sediments of 11 OPEs, including TCEP, TDCP, TCPP, TPhP, TCrP, TnBP, TiBP, TBEP, TEHP, EHDPP, and TEP. The results show that many compartments in the study area are exposed to ecological risks of some highly toxic OPEs, and the ecological risks of sediments appear to be more severe comparatively. [1]
Toxicological data of typical OPEs and calculated PNEC in surface water and sediment
Compound | Biota | Endpoint | Exposure time | Toxic effect | Effect concentration (mg/L) | RQmax (surface water) | RQmax (sediment) |
TCEP | Zebrafish | LC50 | 96 h | mortality | 202 | 0.006 | 0.03 |
TDCP | Zebrafish | LC50 | 96 h | mortality | 0.42 | 0.48 | 2.03 |
TCPP | Zebrafish | LC50 | 96 h | mortality | 13.5 | 1.9 | 5.94 |
TPhP | Zebrafish | LC50 | 96 h | mortality | 1.026 | 0.09 | 0.47 |
TCrP | Daphnia magna | EC50 | 48 h | mortality | 0.31 | 0.05 | 0.16 |
TnBP | Zebrafish | LC50 | 96 h | mortality | 7.82 | 0.05 | 0.04 |
TiBP | Daphnia magna | EC50 | 48 h | mortality | 11 | 0.11 | 0.06 |
TBEP | Zebrafish | LC50 | 96 h | mortality | 3.34 | 1.38 | 0.02 |
TEHP | Daphnia magna | EC50 | 48 h | mortality | 0.74 | 0.02 | < 0.001 |
EHDPP | Daphnia magna | EC50 | 48 h | mortality | 0.31 | 0.15 | 0.57 |
TEP | Zebrafish | LC50 | 96 h | mortality | 1250 | < 0.001 | 0.01 |
TPrP | Zebrafish | LC50 | 96 h | mortality | 252 | < 0.001 | 0.01 |
TDBP | Zebrafish | LOEC | 5 d | mortality | 1.42 | - | - |
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