Chemical |
Hydrofluoric acid |
CAS-number : |
7664-39-3 |
|
Synonyms : |
anhydrous hydrofluoricacid |
anhydrous hydrogen fluoride |
fluoric acid |
fluorivetyhappo. |
hydrofluoric acid |
hydrofluoride |
Hydrogen fluoride |
|
Sumformula of the chemical : |
HF |
EINECS-number : |
2316348 |
|
Purity, % : |
30 |
30 - 80 % HF aqueous |
80 |
|
99 |
99 % anhydrous |
|
Uses : |
Metal trades; glass; polish; chemical industry.
HF is used in
metal industry; in manufacturing of fluorine containing plastic
and polymers (teflon) and freons.
Anhydrous HF and hydrofluoric acid is used for the production
of organoflour compounds and inorganic fluorides, as well as
catalyst of alkylation reactions in the petrochemical industry.
It is also used for etching of glass and pickling of stainless
steel (EU RA Report 2001).
|
|
State and appearance : |
Colourless.
|
|
Molecular weight : |
20.01 |
|
Spesicif gravity (water=1) : |
0.991 |
|
|
Vapor density (air=1) : |
0.71 |
|
|
Vapor pressure, mmHg : |
358 |
0 °C |
|
Melting point, °C : |
-83.1 |
|
-92.3 |
|
|
Boiling point, °C : |
112.2 |
azeotrope with water |
19.5 |
|
|
pKa : |
3.17 |
|
3.19 |
|
|
Other bindings : |
Soil can bind fluorides tightly if pH is > 6.5; high calcium
content will also immobilize fluorides (Sax 1986).
In fresh water at pH above 5, the free ion is main fluoride
species.
At lower pH the proportion of fluoride ion decreases,
while HF2- (hydrogen difluoride ion) and non-dissociated HF
increase.
In the presence of phosphate insoluble fluorapatite
is formed, a large part of which is transferred to the bottom
sediments (EU RA Report 2001).
In seawater fluoride belongs to the macrocomponents; the total
fluoride content is divided in 51% F-, 47% MgF+, 2% CaF+ and
traces of HF and HF2- (EU RA Report 2001).
|
|
Other physicochemical properties : |
Solubility: misciple.
|
|
Other information of degradation : |
Natural alkalinity slowly dissipates acidity (Sax 1986).
|
|
Other information of bioaccumulation : |
In aquatic organisms fluoride accumulates primarily in the
exoskeleton of crustacea and in the bones of fish.
No F
accumulation was reported in edible tissues.
In fish BCF-values
of 53-58 (d.w.) and <2 (w.w) were found.
In crustacea
BCF-values based on whole body fluoride content are found to be
<1 (based on dry weight).
The highest reported BCF-values for
mollusca and aquatic macrophyta were 3.2 and 7.5 (w.w.),
respectively (EU RA Report 2001).
Earthworma collected from F-polluted sites reflected F
contamination very well.
At highest polluted sites the F
content in worms reached values of up to 135 mg/kg (without
gut), whereas worms from umpolluted sites showed contents of
6-14 mg/kg.
The F content in the whole worm from unpolluted
sites was found to be much higher and reached values up to 150
mg/kg.
This was due to the fluoride content of soil contained
in the gut (EU RA Report 001).
The most important F exposure route of F for plants in uptake
from the atmosphere.
Grass species have in comparison to other
plant species a relatively high uptake rate.
The equilibrim
between the concentration in the atmosphere and in the grass is
generally reached within 24 hours.
In a period without rainfall
the half-life of fluoride in grass is circa 4 days in the
summer and circa 12 days in the winter (EURA Report 2001).
|
|
LC50 values to mammals in inhalation exposure, ppm : |
1310 |
ihl-rat, Sax 1986 |
1278 |
1hr, ihl-rat |
500 |
1hr, ihl-mus |
1780 |
1hr, ihl-mky |
4342 |
15min, ihl-gpg |
|
-- |
342 |
1hr, ihl-mus, Sweet 1987 |
|
LDLo values to mammals in oral exposure, mg/kg : |
80 |
orl-gpg, Sax 1986 |
|
LDLo values to mammals in non-oral exposure , mg/kg : |
100 |
scu-gpg, Sax 1986 |
25 |
ipr-rat |
|
LCLo values to mammals in inhalation exposure, mg/kg : |
1000 |
ihl-gpg, Sax 1986 |
260 |
ihl-gpg |
|
LCLo values to mammals in inhalation exposure, ppm : |
50 |
30 min, ihl-hmn, Sax 1986 |
342 |
1hr, ihl-mus |
1774 |
1hr, ihl-mky |
4327 |
15min, ihl-gpg |
|
TCLo values to mammals in inhalation exposure, mg/kg : |
0.47 |
4hr, ihl-rat, 1-22d preg. |
4.98 |
4hr, ihl-rat, 1-22d preg. |
|
teratogenic effect, Sax 1986 |
|
-- |
100 |
1min, ihl-man, sense organs and |
|
special senses |
|
lungs, thorax or |
|
TCLo values to mammals in inhalation exposure, ppm : |
110 |
1 min, ihl-man, Sax 1986 |
|
Health effects : |
Direct contact: highly irritable; severe and painful injury on
contact.
Skin, eyes; gangrene of affected areas may follow.
General sensation: Severe irritation to eyes resulting in
visual defects.
Skin contact results in pungent irritating
odour.
Severe burns.
Recognition odour 0.03 mg/m3.
Dose effect
relations: 3 ppm = good warning properties; MAC 8 hr, 10 ppm,
MAC 0.5 - 1 hr, 30 ppm sour taste smarting eyes; 60 ppm, burn
pain may be delayed up to 1 hr; apparent irritation of nose and
eyes; 120 ppm irritation of skin, respiratory system; vapors
can cause ulcers of respiratory tract; 50 - 250 ppm dangerous
with short exposure; 1500 ppm fatal to animals in tract. 5 min
concentration of 50 - 250 ppm can be dangerous even for brief
exposures (Sax 1986).
|
|
Mutagenicity : |
dnd, dmg, ihl, 1300 ppb, 6 w;
sln, dmg, ihl, 2900 ppb (Sax 1986).
cyt, rat, ihl, 1 mg/m3, 6 hr (Sweet 1987).
Exposure to hydrogen fluoride induces increased frequence of
lethal and sterile mutations both in plants and in banana flies
(Borg 1976).
|
|
Effects on amphibia : |
LDLo, 112 mg/kg, scu, frog (Sax 1986).
|
|
Effects on plants : |
Fluorides can be damaging to plants when present in acid soils
(Sax 1986).
|
|
EC50 values to algae, mg/l : |
43 |
96 hr, Scenedesmus sp. |
122 |
96 hr, Selenastrum capricornutum |
|
EU RA Report 2001 |
|
LC50 values to crustaceans, mg/l : |
300 |
> 300 NaF, 48hr, shrimp, Sax 1986 |
|
EC50 values to crustaceans, mg/l : |
26 |
26-48 mg/l, 96 hr, Benthic macroinvert. |
48 |
12-19 mg CaCO3/l |
97 |
48 hr, Daphnia magna, 250 mg CaCO3/l |
153 |
48 hr, Daphnia magna, 173 mg CaCO3/l |
352 |
48 hr, Daphnia magna, 250 mg CaCO3/l |
270 |
48 hr, Daphnia sp., 204 mg CaCO3/l |
|
EU RA Report 2001 |
|
NOEC values to crustaceans, mg/l : |
3.7 |
21 d, Daphnia magna, 250 mg CaCO3/l |
14.1 |
21 d, Daphnia magna, 250 mg CaCO3/l |
|
EU RA Report 2001 |
|
LC50 values to fishes, mg/l : |
299 |
48 hr, Leuciscus idus melanotus, 25 mg CaCO3/l |
51 |
96 hr, Oncorhynchus mykiss, 17 mg CaCO3/l |
108 |
96 hr, Oncorhynchus mykiss, 22 mg CACO3/l |
165 |
96 hr, Salmo trutta, 21 mg/ CaCO3/l |
340 |
96 hr, Gasterosteusaculeatus, 78 mg CaCO3/l |
|
EU RA Report 2001 |
|
Other information of water organisms : |
60 mg/l, fish, lethal;
40 mg/l, fish, harmful (Sax 1986).
0.9 - 4.5 mg/l NaF, lobster, not toxic;
100 mg/l NaF, mullet, ambasis, safgha, terapon, prawn, jaruba,
no effect, 96hr;
7.2 mg/l NaF, 108 hr, brown mussels, toxic effect;
52 mg/l NaF, 72 d, mullet, crab, physical deterioration;
52 mg/l NaF, 72 d, shrimp, affects reproduction (Sax 1986).
|
|
Other information : |
Strong irritant.
Highly toxic via ingestion or inhalation.
Moderately toxic with chronic exposure.
Emits toxic vapors when
heated to decomposition (Sax 1986).
Air pollution high (Sax 1986).
|
References |
2285 | Anon. 1989.
Miljöfarliga ämnen - exempellista och vetenskaplig
dokumentation. 303 p.
Stockholm.
Rapport från
kemikalieinspektionen (KEMI) 10. |
2692 | Borg, H. 1976.
Ekologiska effekter av fluorider - en
litteraturöversikt.
SNV PM 707. |
3351 | EU RA Report 2001.Existing Substances: hydrogen fluoride.
European Union Risk Assessment Report (Vol 8).
Institute for
Health and Consumer Protection.
European Chemicals Bureau.
European Communities.
|
2147 | Sax, I. 1986.
Hazardous chemicals information annual No. 1.
Van
Nostrand Reinhold Information Services, New York. 766 s. |
2101 | Sweet, D. 1987.
Registry of toxic effects of chemical
substances 1985 - 1986 edition.
U.S.
Department of health and
human services. |
2689 | WHO 1984.
Fluorine and fluorides.
Environ.
Health Criteria 36,
WHO, Geneva. |