Alternatives for Brominated Flame Retardants - Miljøstyrelsen

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BCF(18d, conc. 0.009-0.01 mg/l)=84 - 193 [3]
BCF(38d, conc. 0.090 mg/l)=61-144 (T) [11]
3KR[LQXVSKR[LQXV (fw)
Bioaccumulation (4 months, food conc.=100 ug/g)=0.06 [3]
3LPHSKDOHVSURPHODV(fw)
BCF(105d, mesocosmos, conc. 60 ug/l)=68-160 [3]
BCF(1h-1d)=1,743 (F) [11]
BCF(1h-1d)=561 (F) [11]
BCF(1h-1d)=218 (F) [11]
6DOPRJDLUGQHUL(fw):
♦BCF(90d)=271 [3]
BCF(112d, conc.=60 ug/l)=43 [3]
2QFRUK\QFKXVP\NLLV (fw):
BCF(1h-1d)=1,368 (F) [11]
BCF(1h-1d)=573 (F) [11]
BCF(1h-1d)=931 (F) [11]
BCF(6h)=2,590 (F) [11]
BCF(6h)=18,900 (F) [11]
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♦Triphenyl phosphate biodegrades under aerobic conditions (halflife
of 4 days or less) in water. However, biodegradation in benthic
sediments is unclear. If released to soil, biodegradation will be the
predominant fate process and aqueous hydrolysis may be important
in alkaline soils. Biodegradation is expected to be the dominant fate
process of triphenyl phosphate in soil; screening tests exhibited
aerobic half-lives of about 4 days or less in natural waters [2].
Half-life in killifish=5h [3].
Half-life in goldfish>100h [3]
♦Percent degraded (20d)=93.8 % (OECD 303A) [3]
Percent degraded (48 h)=40 %, sludge inoc. [3]
Percent degraded (40 days)=53 %, unknown inoc. [3]
♦Percent degraded (24 h)=96 %, sludge inoc. [3]
Percent degraded (2-4 days)=50 %, unknown inoc. [3]
♦Percent degraded (96h)=100 %, sludge inoc. [3]
Percent degraded (49-84d)=93-96 %, adap. sludge inoc. [3]
BOD 7 =61.9% BODth, adap. sludge inoc. [3]
BOD 28 =81.8% BODth, adap. sludge inoc. [3]
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No relevant data
No relevant data
0RELOLW\ ♦K oc =3,100 [3]
K d (silty clay)=21.52 [3]
K d (loamy sand)=77.72 [3]