Title: Classification of Red Phosphorus
1Classification of Red Phosphorus
ECBI/09/00 Add 1
- Supplementary material for the application to
classify red phosphorus as R52 (R53) Clariant
GmbH, Sulzbach, Germany Dr. Adrian
BeardItalmatch Chemicals S.p.A., Genova,
Italy Dr. Silvestro Costanzi
2What is the purpose of this presentation?
- summarize the documents submitted to ECB
- discuss any critical points
- come to a decision at the ECB meeting on
25-Sep-2000 - on a revised classification of red phosphorus
- if no consensus can be found, then to decide
- whether further experiments and toxicity tests
are necessary - how any tests should be carried out
- (it is not the purpose to present new data)
3Why is Red Phosphorus (RP) a special case?
- RP is a polymeric form of phosphorus
- RP usually contains traces (around 50 ppm) of
white phosphorus (WP P4) - RP is currently classified as R 50 / R 53 by
analogy to white phosphorus - new experimental data show that RP has very
different environmental properties and should
therefore be classified as less hazardous (R 52) - as a polymer RP is not soluble in water
- structure of RP versus WP
4Properties (backup slide)
5Red Phosphorus Reactions in Water (1)
schematic overview of likely reactions
white phosphorus (P4, max. 200 mg/kg)
red phosphorus, amorphous polymer
1
2
3
4
OH
H3PO2X
H3PO3
H3PO4
H
X
no spontaneous dissolutionof yellow P
Reactions
6Red Phosphorus Reactions in Water (2)
- RP slowly reacts with water and dissolved oxygen
lt 3 of RP react within 4 months (at a loading
of 10 g/L) - main products are traces of phosphine and oxyacids
Red Phosphorus Hydroylsis Products - Yield
3.0
2.0
total Phosphorus in solution, based on input
1.0
0.0
0
20
40
60
80
100
120
Time d
7Aquatic Toxicology of Red Phosphorus
classification
results for red phosphorus after 24 h hydrolysis
LC50, EC50 mg/L
GermanWGK
fish gt 100 mg/Lalgae gt 100 mg/L
100
R 52, (R 53)
1
daphnia 36 mg/L
10
R 51, (R 53)
2
1
N, R 50, (R 53)
2
based on nominal loading rates, the sample
tested contained 50 mg WP / kg WGK
Wassergefährdungsklasse, water hazard class
8What determines the aquatic toxicity of Red
Phosphorus?
- experimental data indicate that it is not the
white phosphorus - on extraction of RP with water one does not find
WP in the water - after aqueous extraction of RP the content of WP
is unchanged - the hydrolysis products of red phosphorus form
the toxic agent - it is not clear which of the products yields the
toxic effects -not all products could be
identified - it would be nice to know the exact chemical
species and mechanism of toxic action, but for
classification the toxic effects only need to be
determined quantitatively
9Why was a nominal loading rate approach applied?
- in analogy to established concepts of water
accomodated fraction for sparingly soluble
substances and water-soluble fraction - the media were filtrated to avoid physical
effects of fine particles on the test organisms
? water-soluble fraction
10Why was a hydrolysis time of 24 hours chosen?
- the acute toxicity is to be tested
- OECD testing of difficult substances
- Half-life gt3 days gt test parent substance (not
the hydrolysis products) - EN ISO 5667-161998 Water quality - Sampling -
Part 16 Guidance on biotesting of samples
chapter 10.1.7 - mentions a 24 h hydrolysis time
- German guidance document on the classification of
substances that are hazardous to the aqueous
environment (LTwS-Nr. 10, ch. 3.6) - Half-life gt12 hours gt test parent substance
- 24 h are common time to prepare water-soluble
fractions of oil-based products (Girling, 1989) - longer term effects are covered by R53
11Which scenario was chosen for toxicity testing?
- a 24 hour hydrolysis represents appropriate
conditions for short term toxicity testing - longer hydrolysis times lead to more hydrolysis
products in solution and possibly higher
toxicity, but these longer term effects are
covered by R53 - other test conditions are also not worst case
(often due to experimental considerations), e.g. - decanting surface films,
- letting emulsions settle or
- filtration of particulates
- do not necessarily happen in the environment
12Why is a static toxicity test sufficient?
- the total concentration of phosphorus species was
measured at the beginning and end of the tests -
they were found to have remained fairly constant
(p. 22 Daphnia test) - when very slowly reacting soluble substances are
tested, static tests may be used also - therefore, we see no need for a semi-static test
13The influence of pH on the hydrolysis of RP
- only a pH-range which is representative and
realistic for the aquatic environment should be
considered pH 6 ... 8.5 - the rate of hydrolysis increases with increasing
pH values - pH values of toxicity test waters covered the
range of 7.5 ... 9
14The content of White in Red Phosphorus (Clariant)
- Clariant statisticsbased on 59 samples
- November 1996 - April 2000
- average value 38.6 mg/kg
Histogram WP in RP, Clariant
12
120
of samples
10
100
8
80
number of samples
6
60
4
40
2
20
0
0
10
20
30
40
50
60
70
80
90
100
110
120
130
White Phosphorus mg/kg
15The content of White in Red Phosphorus (Italmatch)
- Italmatch statistics based on 140 samples
- Nov.1996 - Jul. 2000
- average value 49.9 mg/kg
16Should the labelling of Red Phosphorus be tied to
maximum concentration of White Phosphorus?
- it is difficult to prepare RP with a defined,
high WP content (200 ppm) - in preparations, T-labelled compounds are
allowed up to 0.1 (1 000 ppm) without a
provision to label accordingly - 98 of RP samples have lt 0.01 WP
- there are strong indications that the aquatic
toxicity of RP is not due to released WP but
caused by hydrolysis products of RP
17Is the R 53 label (long term effects) justified?
- red phosphorus is an inorganic polymer
- it reacts very slowly in the aquatic environment
via disproportionating, hydrolysis and oxidation
without reaching an equilibrium for months - because there is no indication that the toxicity
of the reaction products declines quickly, R 53
seems justified