
(d)
Simple asphyxiant. Some gases and vapours present at high concentrations act as asphyxiants by reducing the oxygen content of air. Many of these are odourless and
colourless. Many also pose a fire or explosion risk, often at values below which asphyxiation can occur. (Although capable of asphyxiation, they are not considered to
be substances hazardous to health under COSHH.)
(e)
Suspected human carcinogens –
see
TLV Appendix A, Category A2 (below).
(f)
The value is for total dust containing no asbestos and <1% crystalline silica.
(g)
Confirmed human carcinogen –
see
TLV Appendix, A, Category A1 (below).
(h)
Fibres longer than 5
µ
m and with an aspect ratio ≥3:1 as determined by the membrane filter method at 400–450X magnification (4 mm objective) phase contrast
illumination.
(i)
Welding fumes cannot be classified simply. The composition and quantity of both are dependent on the alloy being welded and the process and electrodes used.
Reliable analysis of fumes cannot be made without considering the nature of the welding process and system being examined; reactive metals and alloys such as
aluminium and titanium are arc-welded in a protective inert atmosphere such as argon. These arcs create relatively little fume, but they do create an intense radiation
which can produce ozone. Similar processes are used to arc-weld steels, also creating a relatively low level of fumes. Ferrous alloys also are arc-welded in oxidizing
environments that generate considerable fume and can produce carbon monoxide instead of ozone. Such fumes generally are composed of discrete particles of
amorphous slags containing iron, manganese, silicon, and other metallic constituents depending on the alloy system involved. Chromium and nickel compounds are
found in fumes when stainless steels are arc-welded. Some coated and flux-cored electrodes are formulated with fluorides and the fumes associated with them can
contain significantly more fluorides than oxides. Because of the above factors, arc-welding fumes frequently must be tested for individual constituents that are likely to
be present to determine whether specific TLVs are exceeded. Conclusions based on total fume concentration are generally adequate if no toxic elements are present in
welding rod, metal, or metal coating and conditions are not conducive to the formation of toxic gases.
Most welding, even with primitive ventilation, does not produce exposures inside the welding helmet above 5 mg/m
3
. That which does, should be controlled.
(j)
UK control limits for asbestos:
Chrysotile 0.3 fibres/ml of air averaged over any continuous 4 hr period
0.9 fibres/ml of air averaged over any continuous 10 min period
Any other form of asbestos, 0.2 fibres/ml of air averaged over any continuous 4 hr period
alone or in mixtures 0.6 fibres/ml of air averaged over any continuous 10 min period
Action levels for cumulative exposures within a 12 week period:
(
a)
for chrysotile, 72 fibre hours/ml of air
(
b
) for any other form of asbestos, alone or in mixtures, 48 fibre hours/ml of air
(
c
) for both types of exposure at different times within the period, a proportionate number of fibre hours/ml
The lack of limits should not be taken to imply an absence of hazard. In the absence of a specific OEL for a particular dust, exposure should be adequately controlled
and where there is no indication of the need for a lower value, personal exposure should be kept below both 10 mg/m
3
8 hr TWA total inhalable dust and 4 mg/m
3
8 hr TWA respirable dust.
(k)
UK limits for lead are 8 hr TWA concentrations as follows:
Lead other than lead alkyls – 0.15 mg/m
3
of air
Lead alkyls – 0.1 mg/m
3
of air
These are ceiling values that must not be exceeded when calculating 8 hr TWA. They should be read in conjunction with biological limits for lead.
(l)
As measured by the vertical elutriator cotton-dust samples.
(m)
Polytetrafluoroethylene decomposition products: thermal decomposition of the fluorocarbon chain in air leads to the formation of oxidized products containing
carbon, fluorine and oxygen. Because these products decompose in part by hydrolysis in alkaline solution, they can be quantitatively determined in air as fluoride to
provide an index of exposure. No TLV is recommended pending determination of the toxicity of the products, but air concentration should be minimal. (Trade names:
Algoflon, Fluon, Teflon, Tetran.)
(n)
In the UK vinyl chloride is also subject to an overriding annual maximum exposure limit of 3 ppm.
(o)
As sampled by a method that does not collect vapour.
TLV Appendix A: Carcinogens (excerpts)
The Chemical Substances Threshold Limit Values Committee classifies certain substances found in the occupational environment as either confirmed or suspected human