While the Montreal Protocol was a tremendous (and all too rare) successful instance of public policy actually following scientific consensus and addressing the
emergency of ozone depletion, the dirty little secret of that success is that the materials which replaced ozone depleting CFC's (chlorofluorocarbons) are HFC's (hydrofluorocarbons) very potent and very persistent greenhouse gases in their own right.
Many of these gases leaking out of all those 2005 Prius's air conditioners - the Prius user who thinks he or she is saving the world representing in my mind a case something like an alcoholic announcing that he is now no longer an alcoholic because he has switched from drinking Scotch to drinking beer - will still be present in earth's atmosphere 50,000 years from now, something like 5 times the distance, in time, between the period before writing was invented and today.
In terms of persistence, CFC's are not quite as bad as HFC's, but of course, the mechanism for the decomposition of CFC's destroys stratospheric ozone, whereas HFC's generally do not. The solution was to make something that doesn't, effectively, decompose at all. (Actually HFC's do decompose under irradiation, but with hardly the same alacrity as HFC's; they have long half-lives. The decomposition product of HFC's is the very toxic compound HF gas - also decomposition product with CFC's - and various acid fluorides, including fluorophosgene. Happily the concentration in the atmosphere is never very high, because the slow rate of formation allows HF to be neutralized by glass and carbonates before it can cause much harm.)
The global warming potential of one widely used HFC 1,1,1,2, tetrafluorethane, R-134a, is about 1600 times as high as carbon dioxide. This is actually not quite as bad as R-12, which has a global warming potential of 6700, which is hopefully irrelevant owning to the Montreal Protocol banning it.
Any substance that
has a half-life will, no matter how quickly it is formed, will come into equilibrium, at which time it will be destroyed at the same rate that it is created. The
position of the equilibrium has to do with the
rates of destruction and formation. Since R-134a has a low rate of decomposition, one can have higher concentrations of it in the atmosphere than one can have of R-12, which has a shorter half-life, if a more problematic decomposition route.
It would be nice therefore to have compounds with a short half life
and a
relatively benign mechanism of decomposition.
Actually it now understood that such compounds exist. They are the HFE's, hydrofluoro
ethers, which are pretty good refrigerants, are non-flammable, and decompose with a short half-life with a mechanism similar to that of HFC's, generating HF and fluorophosgene that can be neutralized by silica (glass) and carbonates before accumulating in toxic concentrations.
It might seem like a slam dunk, but, um,
not so fast. Although HFE's are effective, they are not as efficient. To wit, it takes more energy to make them work than it takes with HFC's.
This is discussed in the ASAP section of the American Chemical Society Journal
Environmental Science and Technology in a paper by Blowers and Landsbury out of the University of Arizona, where they should care about things like refrigerants.
http://pubs.acs.org/doi/abs/10.1021/es9023354">Here is the abstract of the article, and a link for use of subscribers and people in good scientific libraries.
Here are some excerpts of the article from the text:
This paper quantifies the environmental impacts of refrigeration for R-12 (the CFC CCl2F2), which was used prior to the Montreal Protocol, R-134a (the HFC CH2FCF3 ), and an emerging HFE (CF3OCH3), which has properties appropriate for drop-in replacement from a temperature and vapor pressure perspective. A review of the literature shows only one other HFE (CF3OCHF2) with suitable properties for low temperature cooling applications, but calculations showed that the chemical is not feasible for technical reasons...
...A refrigeration system involves a circulating working fluid called a coolant that removes heat from the refrigerator at low temperatures, vaporizing the fluid and absorbing energy. The vapor stream enters a compressor where the gas is pressurized, increasing the temperature. A secondary fluid, commonly water or air, is used to remove the heat from the refrigerant to form a saturated liquid stream at high pressure. The pressure is lowered to utilize the Joule-Thomson effect through partial vaporization, which drops the temperature to the point where the fluid can again be passed through the refrigerator. The compressor requires energy, which leads to off-site carbon dioxide emissions due to energy creation.
The bold is mine.
Note that the Joule-Thompson coefficient of all real gases, with the exception of hydrogen, helium and neon is positive, meaning that all real gases except these are potentially used as refrigerants. Indeed, liquid nitrogen is often made using the auto-refrigeration of compressed air being allowed to expand.
The problem is that using nitrogen to refrigerate itself involves an energy penalty. If energy is cheap, liquid nitrogen is cheap. If energy is expensive, liquid nitrogen is expensive.
These thermodynamic facts - like all thermodynamic facts - translate into environmental effects, since energy and the environment are inextricably connected, which is why energy
storage always involves an environmental penalty.
To continue with excepting the paper, they consider - unlike an anti-nuke daydreaming about putative "someday" solar and wind systems with brazillions of battery packs - where energy comes from:
A compressor efficiency of 75% was assumed. The implications of these decisions on the analysis analyses are explored later.We used standard chemical engineering equations and principles for calculating entropies,heat duties,work requirements,and Joule-Thomson cooling effects (11). Details are shown in the Supporting Information. Carbon dioxide emissions were estimated for both direct and indirect contributions. For direct GWP contributions, we assumed a refrigerant leakage rate of 9%/year (8). We selected coal as the fuel source to evaluate indirect contributions due to the rapid growth of coal as a primary fuel for electricity generation. Coal produces 39% of electricity in the U.S. and is the dominant source of electricity worldwide (12). It should be noted that there are a range of values available in the literature for the emissions factor for CO2 for electricity from coal. Schreiber, et al. (13), performed an LCA for coal-fired power plants in Germany and found CO2 emissions to be 0.796 kg/kWh when they considered impacts due to materials procurement, coal supply, combustion, and some post-combustion treatment. It is unclear how they handled details about transport as this was not discussed in their paper. Odeh and Cockerill examined coal combustion for UK coal-fired power plants, including coal mining, transport, and power generation in their analyses and found emissions to be 0.957 kg/kWh (13) or 0.984 kg/kWh (14). Similar values were reported by Spath (15) for U.S. coal-fired plants and Hondo (16) for Japanese plants, with values of 1.042 and 0.975 kg/kWh, respectively...
Note that coal use is likely to get worse not better although many attempts will be made to
pretend otherwise, by building as a red herring one or two tiny coal gasification plants that
could someday, possibly - if we really, really wanted to do it, even though we don't - be applied to sequestration, to distract attention from the huge new
traditional coal plants. This is what I call the "Florida Power and Light Solution" which is marginally better than the German solution which is to announce that new coal plants don't count because they're, um,
new. (It also helps to announce that you intend to use useless solar and wind power even as you build new coal and gas plants, another practice of the Germans who are in the process of replacing all of their nearly pollution free nuclear plants with "green" coal and gas plants.)
Now for the results of the paper:
The refrigerant GWPs suggest that switching to the HFE would be desirable to prevent global climate change through greenhouse gas emissions. However, our results in Table 2 show the drop-in replacement HFE for R-134a is unfavorable from an overall use-to-disposal life cycle perspective. Unfortunately, there is an increase of indirect emissions through both the increased compressor requirements and increased cooling water needs.The compressor significantly contributes to greenhouse gas emissions with between 69 and 72% of the electricity needs, which make up between 76 and 98% of the total CO2-equivalents. The primary reason that the HFE leads to larger compression needs is that the heat of vaporization of the HFE is the lowest among the refrigerants, resulting in the largest vaporization fraction across the valve due to the Joule-
Thomson effect. This leads to a larger required mass of refrigerant that must be transported throughout the refrigeration loop, which increases the overall work duty of the compressor. In fact, the work per mole is lower for the HFE but the need for higher flow rates to meet the cooling requirements leads to higher electricity usage.
The bold is, again, mine.
Note that HFE's become a
reasonable and workable replacement for HFC's
if and only if electricity is freely available without the generation of greenhouse gases.
This is entirely feasible with known technology, but regrettably, ignorance and mysticism prevent full application of the technology.