World Environment and Energy (2009)

 
   

Halogenated solvents

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Although this essay is devoted to solvents, much of the information may be extrapolated to other organic halogenated substances, such as refrigerants, fire control compounds, aerosol propellants, anaesthetics etc.

There are a number of types and classes of halogenated solvents. Practically all of them have some environmental and health and safety issues. However, there are massive quantities of misinformation, even disinformation, about them. It is hoped that this essay will help place the church back into the centre of the village. It is not the intention to discuss individual solvents in great detail, nor to indicate their applications. They are most often used for cleaning mechanical parts and garments and as carrier solvents for coatings and adhesives. In order to simplify the page structure, I'll classify the solvents initially by their environmental effects and secondly by their health and safety effects.

Ozone depletion

Many solvents are ozone depleting, in varying degrees, measured by their Ozone Depleting Potential (ODP) which is an index related to the effect that the simplest chlorofluorocarbon (CFC) gas, CFC-11, which is given as an ODP of 1. The most popular CFC solvent, CFC-113 has an ODP of 0.8. This was popular for much precision and electronics cleaning before it became a controlled substance under the Montreal Protocol, along with all the other CFC solvents.

Another class of controlled substance is the hydrochlorofluorocarbon (HCFC) type. Generally these have ODPs between about 0.03 and 0.1. The Montreal Protocol gives them a longer phase-out time, but some countries have already eliminated or substantially reduced their use. The two main HCFC solvents are HCFC-141b, with a high ODP of 0.1 and the isomers of HCFC-225, with a relatively low ODP.

Chlorocarbon solvents are generally considered as non-ozone-depleting with the exception of 1,1,1-trichloroethane, which has an ODP of 0.1 and tetrachloromethane, more usually known as carbon tetrachloride (CTC), with a massive ODP of 1.3. The other non-ozone-depleting ones, exempt from control under the Montreal Protocol, are trichloroethylene (TCE), popular for metal degreasing, perchloroethylene (PCE), frequently used for dry cleaning garments and methylene chloride or dichloromethane (DCM), often used for adhesives or in paint strippers. These are all toxic (see below) but are widely used.

Only one bromocarbon solvent has been considered useful in recent years. This is 1-bromopropane, also known as n-propyl bromide (nPB). This substance has become very controversial because, although it decomposes in the atmosphere fairly rapidly, it has a relatively high ODP and is apparently toxic (see below). It has very similar physical characteristics to TCE and, because it was initially believed to be less toxic than TCE, gained a certain popularity. The big stumbling block is the fact that it has never been introduced into the Montreal Protocol as a controlled substance. The reason for this may seem obscure but it is because the Protocol's Scientific Assessment Panel has not been able to reliably assess it's ozone depletion potential because of its short atmospheric residency time. Unfortunately, the standard models for such an assessment do not work because the ODP is related to the meteorological conditions, and subsequently to the latitude of emissions. As far as can be ascertained, the ODP is very low at higher latitudes, rising to about 0.1 in the tropics. Nevertheless, this range of ODP is within the range of controlled substances and it would seem anomalous that nPB has not been included as a controlled substance into the Protocol. It is possible that the lack of a decision by the Parties to the Protocol may be at least partially political.

Bromochloromethane is a solvent that had a brief moment of glory in the mid-1990s but its high ODP attracted the attention of the Parties to the Montreal Protocol and it was quickly introduced as a controlled substance.

Perfluorocarbons (PFCs), hydrofluorocarbons (HFCs) and hydrofluoroethers (HFEs) are not ozone-depleting. They are therefore not subject to any control by the Montreal Protocol.

Climate change

Nearly all halogenated solvents have a Global Warming Potential (GWP) greater than that of carbon dioxide. In particular, CFCs -- controlled by the Montreal Protocol -- have high values but PFCs, HFCs and HFEs are particularly bad.

PFCs are rarely used by themselves as a solvent but they have atmospheric residency times of the order of thousands of years and GWPs often exceeding 10,000 times that of carbon dioxide; they are amongst the worst substances for instigating climate change. On the other hand, there are a number of HFCs which are used as solvents and these have GWPs usually between 300 and 1500. As a general rule, HFE solvents have slightly lower GWPs than the HFC solvents.

PFCs and HFCs are controlled substances under the Kyoto Protocol.

Health and Safety

Other than for pure PFCs and HFCs, most halogenated solvents are quite toxic to very toxic, even suspected carcinogens in some cases. As a rough guide, brominated solvents are more toxic than chlorinated solvents which are more toxic than fluorinated solvents. However, many commercial solvents are not pure substances but are blends, often with other toxic solvents such as methanol. Even HFC and HFE blends may contain chlorinated solvents which are much more toxic than the major product.

The acute toxicity of a single dose of most solvent vapours is not high under normal conditions. Nevertheless, heavy doses of some halogenated solvents have been known to cause cardiac arrest. It should be remembered that these substances are quite closely related to surgical anaesthetics. Other than that, many deaths have been caused by suffocation while cleaning equipment where the heavy vapours have not been evacuated, displacing air. When cleaning equipment which has contained any halogenated solvent, extreme precautions should be imposed to ensure the safety of the personnel. In particular, large closed tanks should be cleaned only with surveillance by a second person outside, capable of pulling up an unconscious person by a safety rope.

Chlorinated solvents, such as TCE, PCE and DCM, are all toxic to some degree to the liver. Operating personnel should never be exposed to solvent vapours exceeding the Operator Exposure Level imposed by the national authorities of the country concerned. Unfortunately, a considerable amount of disinformation has been propagated about the carcinogenicity of these solvents. Because they are known to cause cancerous tumours in laboratory animals, scaremongering has been rife, extrapolating these results to humans. It has been shown that this is scientifically invalid because the manner in which the solvents are metabolised is entirely different between rodents and humans. Very important epidemiological tests, involving cohorts of thousands of persons exposed to the solvents over many years, have never proved that these substances are carcinogenic. The solvents have been used industrially for over 100 years, often under uncontrolled conditions with bad exposure levels. It can be stated fairly categorically that if the operator exposure levels are respected, the risk of contracting any cancer is negligible. The two ozone-depleting chlorocarbon solvents have very different toxicity ratings. Carbon tetrachloride is very toxic and has been banned from use as a solvent since the 1950s in most western countries. On the other hand, it is still used in some developing countries, despite the danger of doing so. On the other hand, 1,1,1-trichloroethane has a lower toxicity than most other chlorinated solvents.

Probably the most controversial of the halogenated solvents, from the point of view of health and safety, is n-propyl bromide. This is because it has not been used industrially for more than 10 years in any great quantity and we do not have sufficient experience to provide valid epidemiological studies. Animal tests, which are not necessarily able to be extrapolated to humans, have shown that the solvent attacks both the reproductive and central nervous systems. The little experience that we do have would seem to indicate similar effects in humans subjected to heavy exposures. Anecdotal evidence has shown that there is a great risk of absorption through the skin, potentially causing neuropathic lesions. Until we gain more knowledge about the effect of nPB on humans, it would seem wise to reduce the exposure to a minimum, or not to use it at all. This lack of knowledge is shown by different manufacturers recommending time weighted average operator exposure levels as low as 5 ppm and as high as 100 ppm. Some authorities have made recommendations of the 10 ppm and 25 ppm but none of these values are binding upon users, because national permitted exposure levels have not been promulgated. The use of the solvent is forbidden in a few places.

All halogenated solvents are classed as volatile organic compounds by the EU and other authorities. It is therefore possible that they may contribute to the formation of tropospheric ozone and smog, both of which have negative impacts on the health of the population at large. It is therefore necessary to ensure that their use is such that emissions are reduced to an absolute minimum, no matter what other effects they may have on the environment or on the people using them.



 
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