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l3d1
Jun 26 2008 19:43:16
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# ---- Special Case Marine Ad for Marine Pages --- ?>
Ozone Hole FAQ
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Frequently Asked Questions about the Ozone Hole
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What is the Ozone Hole?
How big was the 2007 Ozone Hole, and is it getting bigger?
Has there been ozone loss in places besides Antarctica?
Has ozone destruction increased levels of UV-B light at the surface?
What are the human health effects of increased UV-B light?
Has ozone loss contributed to an observed increase in sunburns and skin cancer in humans?
What is the effect
of increased UV-B light on plants?
What is the effect
of increased UV-B light on marine life?
Is the worldwide decline in
amphibians due to ozone depletion?
Are sheep going blind in Chile?
What do the skeptics say about the ozone hole?
What are the costs
and savings of the CFC phaseout?
What steps have been taken to save the ozone layer? Are they working?
What replacement chemicals
for CFCs have been found? Are they safe?
When was the ozone hole discovered?
How do CFCs destroy
ozone?
Are volcanos
a major source of chlorine to the stratosphere?
What is ozone pollution?
Where can I go to learn more about the ozone hole?
What is the ozone hole?
The "ozone hole" is a loss of stratospheric ozone in springtime over
Antarctica, peaking in September. The ozone hole area is defined as the
size of the region with total ozone below 220 Dobson units (DU). Dobson
Units are a unit of measurement that refer to the thickness of the ozone
layer in a vertical column from the surface to the top of the
atmosphere, a quantity called the "total column ozone amount." Prior to
1979, total column ozone values over Antarctica never fell below 220 DU.
The hole has been proven to be a result of human activities--the release
of huge quantities of chlorofluorocarbons (CFCs) and other ozone
depleting substances into the atmosphere.
How big was the 2007 ozone hole, and is it getting bigger?
Every four years, a team of many of the top scientists researching ozone
depletion put together a comprehensive summary of the scientific
knowledge on the subject, under the auspices of the World Meteorological
Organization (WMO). According to their most recent assessment, (WMO,
2006), monthly total column ozone amounts in September and October
have continued to be 40 to 50% below pre-ozone-hole values, with up to
70% decreases for periods of a week or so. During the last decade, the
average ozone hole area in the spring has increased in size, but not as
rapidly as during the 1980s. It is not yet possible to say whether the
area of the ozone hole has maximized. However, chlorine in the
stratosphere has reached nearly constant levels and is expected to start
declining, so the ozone hole may have seen its maximum size. Annual
variations in temperature will probably be the dominant factor in
determining differences in size of the ozone hole in the near future,
due to the importance of cold-weather Polar Stratospheric Clouds (PSCs)
that act as reactive surfaces to accelerate ozone destruction.
The 2007 hole was fairly average when compared to those of the past 15 years. On September 13, 2007, the hole reached it maximum size of 24 million square kilometers (9.3 million square miles), a full 18% smaller than the 2006 hole. The 2006 hole reached its maximum size of 29 million square kilometers (11.3 million square
miles) on September 24, 2006, according to NASA. This
is very close to the record ozone hole size of September 10, 2000,
when it covered 29.2 million square kilometers (11.5 million square miles). The depth of the
hole, however, was greater in 2006 than in 2000. the amount of lost ozone amounted to 40 million
tons on October 2, beating 2000's record of 39 million tons. The lowest ozone value of 2006 was
102 Dobson units, compared to the record low of 88 Dobson units (observed in 1993). The graph
below, taken from NOAA's Climate
Prediction Center, compares the 2007 ozone hole size with previous years. The smaller size of
this year's hole is due to the warmer winter weather than occurred in 2006, leading to formation of fewer Polar Stratospheric Clouds (PSCs) than in 2006.
These clouds act as ozone destroying chemical factories. The U.N. Environment Program (UNEP) said in August 2006
that the ozone layer would likely return to pre-1980 levels by 2049 over much of Europe, North
America, Asia, Australasia, Latin America and Africa. In Antarctica, the agencies said ozone layer
recovery would likely be delayed until 2065.
Has there been ozone
loss in places besides Antarctica?
Yes, ozone loss has been reported in the mid and high latitudes in both
hemispheres during all seasons (WMO, 2006). Relative to the pre-ozone-hole
abundances of 1980, the 2002-2005 losses in total column ozone were:
About 3% in the Northern Hemisphere south of 60°N
About 6% in the Southern Hemisphere north of 60°S
Other studies have shown the following ozone losses:
About 12% at
Punta Arenas, Chile, the southernmost city in the world (Abarca and
Casiccia, 2002).
About 8% in summer in southern Australia (Manin et. al., 2001).
About 10-15% in summer in New Zealand (McKenzie et. al., 1999).
In the Arctic, some recent cold winters have led to 30% losses in total
column ozone in early spring. Ozone loss in the Arctic is highly
dependent on the meteorology, due to the importance of cold-weather
Polar Stratospheric Clouds (PSCs) that act as reactive surfaces to
accelerate ozone destruction. For this reason, the warm Arctic winter of
1998/1999 saw very little ozone loss due to the lack of PSCs, while the
cold 1999/2000 winter saw a 20-25% loss of ozone. A future Arctic
ozone hole similar to that of the Antarctic appears unlikely, due to
differences in the meteorology of the polar regions of the northern and
southern hemispheres
(WMO, 2002). However, a recent model
study (Rex et. al., 2004), indicates that future Arctic ozone
depletion could be much worse than expected, and that each degree
Centigrade cooling of the Arctic may result in a 4% decrease in ozone.
This heightened ozone loss is expected due to an increase in PSCs. The
Arctic stratosphere has cooled 3°C in the past 20 years due the combined
effects of ozone loss, greenhouse gas accumulation, and natural
variability, and may cool further in the coming decades due to the
greenhouse effect (WMO, 2002). An additional major loss of Arctic (and
global) ozone could occur as the result of a major
volcanic eruption (Tabazadeh, 2002).
Has ozone
destruction increased levels of UV-B light at the surface?
Yes, ozone destruction has increased surface
levels of UV-B light (the type of UV light that causes skin damage). For
each 1% drop in ozone levels, about 1% more UV-B reaches the Earth's
surface (WMO, 2002). Increases in UV-B of 6-14% have been measured at
many mid and high-latitude sites over the past 20 years (WMO, 2002,
McKenzie, 1999). At some sites about half of this increase can be
attributed to ozone loss. Changes in cloudiness, surface air pollution,
and albedo also strongly influence surface UV-B levels. Increases in
UV-B radiation have not been seen in many U.S. cities in the past few
decades due to the presence of air pollution aerosol particles, which
commonly cause 20% decreases in UV-B radiation in the summer (Wenny et
al, 2001).
Modeled and observed surface UV-B light changes as a function of ozone loss
Source: World Meteorological Organization, Scientific
Assessment of Ozone Depletion: 1998, WMO Global Ozone Research
and Monitoring Project - Report No. 44, Geneva, 1998.
What are the human health effects of increased UV-B light?
From the outset it should be pointed out that human behavior is of primary
importance when considering the health risks of sun exposure. Taking proper
precautions, such as covering up exposed skin,
using sunscreen, and staying out of the sun during peak sun hours is of
far greater significance to health than the increased UV-B due to ozone loss
is likely to be.
A reduction in ozone of 1% leads to increases of up to 3% in some
forms of non-melanoma skin cancer (UNEP, 1998). It is more difficult to
quantify a link between ozone loss and malignant melanoma, which
accounts for about 4% of skin cancer cases, but causes about 79% of skin
cancer deaths. Current research has shown that melanoma can increase
with both increased UV-B and UV-A light, but the relationship is not
well understood (UNEP, 2002). In
the U.S. in 2003, approximately 54,200 persons will have new diagnoses
of melanoma, and 7,600 will die from the disease, and more than 1
million new cases of the other two skin cancers, basal cell carcinoma
and squamous cell carcinoma, will be diagnosed (American Cancer Society,
2002) . Worldwide, approximately 66,000 people will die in 2003 from
malignant melanoma, according to the World Health Organization.
However, the significant rises in skin cancer worldwide can primarily be
attributed human behavioral changes rather than ozone depletion (Urbach,
1999; Staehelin, 1990).
On the positive side, UV light helps produce vitamin D in the skin,
which may help against contraction of certain diseases. Multiple
sclerosis has been shown to decrease in the white Caucasian population
with increasing UV light levels. On the negative side, excessive UV-B
exposure depresses the immune system, potentially allowing increased
susceptibility to a wide variety of diseases. And in recent years, it has
become apparent that UV-B damage to the eye and vision is far more
insidious and detrimental than had previously been suspected (UNEP, 2002).
Thus, we can expect ozone loss to substantially increase the
incidence of cataracts and blindness. A study done for Environment Canada
presented to a UN meeting in 1997, estimated that because of the
phase-out of CFCs and other ozone depleting substances mandated by the
1987 Montreal Protocol, there will be 19.1 million fewer cases of
non-melanoma skin cancer, 1.5 million fewer cases of melanoma, 129
million fewer cases of cataracts, and 330,000 fewer skin cancer deaths
worldwide.
Has ozone loss contributed to an observed increase in sunburns and skin cancer in humans?
Yes, Punta Arenas, Chile, the southernmost city in the world (53°S), with
a population of 154,000, has regularly seen high levels of UV-B radiation
each spring for the past 20 years, when the Antarctic ozone hole has moved
over the city (Abarca,
2002). Ozone levels have dropped up to 56%, allowing UV-B radiation
more typical of summertime mid-latitude intensities to affect a population
unused to such levels of skin-damaging sunshine. Significant increases in
sunburns have been observed during many of these low-ozone days. During
the spring of 1999, a highly unusual increase in referrals for sunburn
occurred in Punta Arenas during specific times when the ozone hole passed
over the city. And while most of the worldwide increase in skin cancer
rates the past few decades has been attributed to people spending more time
outdoors, and the use of tanning businesses (Urbach, 1999), skin cancer
cases increased 66% from 1994-2000 compared to 1987-1993 in Punta Arenas,
strongly suggesting that ozone depletion was a significant factor.
What is the effect
of increased UV-B light on plants?
UV-B light is generally harmful to plants, but sensitivity varies widely
and is not well understood. Many species of plants are not UV-B sensitive;
others show marked growth reduction and DNA damage under increased UV-B
light levels. It is thought that ozone depletion may not have a
significant detrimental effect on agricultural crops, as UV-B tolerant
varieties of grains could fairly easily be substituted for existing
varieties. Natural ecosystems, however, would face a more difficult time
adapting. Direct damage to plants from ozone loss has been documented in
several studies. For example, data from a spring, 1997 study in Tierra del
Fuego, at the southern tip of Argentina, found DNA damage to plants on
days the ozone hole was overhead to be 65% higher than on non-ozone-hole
days (Rousseaux et. al., 1999).
What is the effect
of increased UV-B light on marine life?
UV-B light is generally harmful to marine life, but again the effect is
highly variable and not well understood. UV-B radiation can cause damage
to the early developmental stages of fish, shrimp, crab, amphibians and
other animals (UNEP, 2002).. Even at current levels, solar UV-B
radiation is a limiting factor in reproductive capacity and larval
development, and small increases in UV-B radiation could cause significant
population reductions in the animals that eat these smaller creatures. One
study done in the waters off Antarctica where increased UV-B radiation has
been measured due to the ozone hole found a 6-12% decrease in
phytoplankton, the organism that forms the base of the food chain in the oceans (Smith et. al., 1990). Since the ozone hole lasts for
about 10-12 weeks, this corresponds to an overall phytoplankton decrease
of 2-4% for the year.
Is the worldwide decline in
amphibians due to ozone depletion?
No. The worldwide decline in amphibians is just that--worldwide. Ozone depletion has not
not yet affected the tropics (-25° to 25° latitude), and that is where much of the
decline in amphibians has been observed. It is possible that ozone depletion in
mid and high latitudes has contributed to the decline of amphibians in those areas,
but there are no scientific studies that have made a direct link.
Are sheep going blind in Chile?
Yes, but not from ozone depletion!
In 1992, The New York Times reported ozone depletion over southern Chile
had caused
"an increase in Twilight Zone-type reports of sheep and rabbits with cataracts" (Nash, 1992).
The story was repeated in many places, including
the July 1, 1993 showing of ABC's Prime Time Live. Al Gore's book, Earth in the Balance, stated that
"in Patagonia, hunters now report finding blind rabbits; fishermen catch blind salmon" (Gore, 1992).
A group at Johns Hopkins has investigated
the evidence and attributed the cases of sheep blindness to a local infection ("pink eye") (Pearce, 1993).
What do the skeptics say about the ozone hole?
Ever since the link between CFCs and ozone depletion was proposed in
1974, skeptics have attacked the science behind the link and the policies
of controlling CFCs and other ozone depleting substances. We have compiled
a detailed analysis of the arguments of
the skeptics. It is interesting to note how the skeptics are using the
same bag of tricks to cast doubt upon the science behind the global
warming debate, and the need to control greenhouse-effect gases. It is
also worth visiting the Anti-Environment Myth web site.
What are the costs
and savings of the CFC phaseout?
The costs have been large, but not as large as initially feared. As the
United Nations Environment Programme (UNEP) Economic Options Committee
(an expert advisory body) stated in 1994: "Ozone-depleting substance
replacement has been more rapid, less expensive, and more innovative
than had been anticipated at the beginning of the substitution process.
The alternative technologies already adopted have been effective and
inexpensive enough that consumers have not yet felt any noticeable
impacts (except for an increase in automobile air conditioning service
costs)" (UNEP, 1994). A group of over two dozen industry experts
estimated the total CFC phaseout cost in industrialized counties at $37
billion to business and industry, and $3 billion to consumers
(Vogelsberg, 1997). A study done for Environment Canada
presented to a UN meeting in 1997, estimated a total CFC phaseout cost
of $235 billion through the year 2060, but economic benefits totaling
$459 billion, not including the savings due to decreased health care
costs. These savings came from decreased UV exposure to aquatic
ecosystems, plants, forests, crops, plastics, paints and other outdoor
building materials.
What steps have been taken to save the ozone layer? Are they working?
In 1987, the nations of the world banded together to draft the Montreal
Protocol to phase out the production and use of CFCs. The 43 nations
that signed the protocol agreed to freeze consumption and production of
CFCs at 1986 levels by 1990, reduce them 20% by 1994, and reduce them
another 30% by 1999. The alarming loss of ozone in Antarctica and
worldwide continued into the 1990's, and additional amendments to
further accelerate the CFC phase-out were adopted. With the exception of
a very small number of internationally agreed essential uses, CFCs,
halons, carbon tetrachloride, and methyl chloroform were all phased out
by 1995 in developing countries (undeveloped countries have until 2010
to do so). The pesticide methyl bromide, another
significant ozone-depleting substance, was scheduled to be phased out in
2004 in developing countries, but a U.S.-led delaying effort led to a
one-year extension until the end of 2005. At least 183 counties are now
signatories on the Montreal Protocol.
The Montreal Protocol is working, and ozone depletion due to human
effects is expected to start decreasing in the next 10 years. Observations show that levels of ozone depleting
gases at a maximum now and are beginning to decline (Newchurch et. al., 2003). Provided the Montreal
Protocol is followed, the Antarctic ozone hole is expected to disappear by
2050.
What replacement chemicals
for CFCs have been found? Are they safe?
Hydrofluorocarbons (HFCs), hydrochlorofluorocarbons
(HCFCs) and "Greenfreeze" chemicals (hydrocarbons such as
cyclopentane and isobutane) have been the primary substitutes.
The primary HFC used in automobile air conditioning, HFC-134a, costs about 3-5
times as much as the CFC-12 gas it replaced. A substantial black market
in CFCs has resulted.
HCFCs are considered a "transitional" CFC substitute, since they
also contribute to ozone depletion (but to a much less degree than
CFCs). HCFCs are scheduled to be phased out by 2030 in developed
nations and 2040 in developing nations, according to the Montreal
Protocol. HCFCs (and HFCs) are broken down in the atmosphere into
several toxic chemicals, trifluoroacetic acid (TFA) and
chlorodifluoroacetic acid (CDFA). Risks to human health and the
environment from these chemicals is thought to be minimal (UNEP/WMO,
2002).
HFCs do not
cause ozone depletion, but do contribute significantly to global
warming. For example, HFC-134a, the new refrigerant of choice in
automobile air conditioning systems, is 1300 times more effective over
a 100-year period as a
greenhouse gas than carbon dioxide. At current rates of HFC manufacture
and emission, up to 4% of greenhouse effect warming by the year 2010 may result from
HFCs.
"Greenfreeze" hydrocarbon chemicals appear to be the best substitute, as they do
not contribute to greenhouse warming, or ozone depletion. The
hydrocarbons used are flammable, but the amount used (equivalent to two
butane lighters of fluid) and safety engineering considerations have
made quieted these concerns. Greenfreeze technology has captured nearly
100% of the home refrigeration market in many countries in
Europe, but has not been introduced in North America yet
due to product liability concerns and industry resistance.
When was the ozone hole discovered?
Ozone depletion by human-produced CFCs was first hypothesized in 1974 (Molina and Rowland, 1974).
The first evidence of ozone depletion was detected by
ground-based instruments operated by the British Antarctic Survey at Halley
Bay on the Antarctic coast in 1982.
The results seemed so improbable that researchers
collected data for three more years before finally publishing the first
paper documenting the emergence of an ozone hole over Antarctica (Farman, 1985). Subsequent analysis of the data
revealed that the hole began to appear in 1977. After the 1985 publication
of Farman's paper, the question arose as to why satellite measurements of
Antarctic ozone from the Nimbus-7 spacecraft had not found the hole. The
satellite data was re-examined, and it was discovered that the computers
analyzing the data were programmed to throw at any ozone holes below 180
Dobson Units as impossible. Once this problem was corrected, the satellite
data clearly confirmed the existence of the hole.
How do CFCs destroy
ozone? CFCs are extremely stable in the lower atmosphere,
only a negligible amount are removed by the oceans and soils. However, once CFCs
reach the stratosphere, UV light intensities are high enough to
break apart the CFC molecule, freeing up the chlorine atoms in them.
These free chlorine atoms then react with ozone to form oxygen and
chlorine monoxide, thereby destroying the ozone molecule. The chlorine atom
in the chlorine monoxide molecule can then react with an oxygen atom to free
up the chlorine atom again, which can go on to destroy more
ozone in what is referred to as a "catalytic reaction":
Cl + O3 -> ClO + O2
ClO + O -> Cl + O2
Thanks to this catalytic cycle, each CFC molecule can
destroy up 100,000 ozone molecules. Bromine atoms can also
catalytically destroy ozone, and are about 45 times more effective
than chlorine in doing so.
For more details on ozone depletion chemistry, see the
Usenet Ozone FAQ.
Are volcanos
a major source of chlorine to the stratosphere?
No, volcanos contribute at most just a few percent of the chlorine found
in the stratosphere. Direct measurements of the
stratospheric chlorine produced by El Chichon, the most important eruption of
the 1980's (Mankin and Coffey, 1983), and Pinatubo, the largest volcanic
eruption since 1912 (Mankin et. al., 1991) found negligible amounts
of chlorine injected into the stratosphere.
What is ozone
pollution? Ozone forms in both the upper and the lower
atmosphere. Ozone is helpful in the stratosphere, because it absorbs most
of the harmful ultraviolet light coming from the sun. Ozone found in the
lower atmosphere (troposphere) is harmful. It is the prime ingredient for
the formation of photochemical smog. Ozone can irritate the eyes and
throat, and damage crops. Visit the Weather Underground's ozone pollution page, or our ozone action page for more information.
Where can I go to learn more about
the ozone hole?
The following sources were most helpful when constructing the ozone hole FAQ:
Environmental Protection Agency ozone depletion pages (best source of info on the Internet)
World Meteorological Organization 2006 scientific assessment
Latest satellite measurements from NOAA
United Nations Environment Programme 2002 Assessment
Usenet FAQ
Ozone Hole Tour from the University of Cambridge
References
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under the Antarctic ozone hole: southern Chile, 1987-2000,"
Photodermatology, Photoimmunology & Photomedicine, 18,
294, 2002.
American Cancer Society. Cancer facts & figures 2002. Atlanta: American
Cancer Society, 2002.
Farman, J.C., B.D. Gardner and J.D. Shanklin, "Large losses of total
ozone in Antarctica reveal seasonal ClOx/NOx Interaction,
Nature, 315,
207-210, 1985.
Gore, A., "Earth in the Balance: Ecology and the Human Spirit", Houghton Mifflin, Boston, 1992.
Manins, P., R. Allan, T. Beer, P. Fraser, P. Holper, R. Suppiah, R. and K. Walsh. "Atmosphere, Australia State of the
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Mankin, W., and M. Coffey, "Increased
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Mankin, W., M. Coffey, and A. Goldman,
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McKenzie, R., B. Connor, G. Bodeker, "Increased summertime UV radiation
in New Zealand in response to ozone loss", Science, 285,
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Molina, M.J., and F.S. Rowland, Stratospheric Sink for
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Nash, N.C., "Ozone Depletion Threatening Latin Sun Worshipers", New York Times, 27 March 1992, p. A7.
Newchurch, et. al., "Evidence for slowdown
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Pearce, F., "Ozone hole 'innocent' of Chile's ills",
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Rex, M. et. al., "Arctic ozone loss and climate change", Geophys. Res.
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Szwarcberg-Bracchitta, P.S. Searles, M.M. Caldwell, S.B. Diaz, "Ozone
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and Costs of the Montreal Protocol on Substances that Deplete the Ozone
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Smith, R., B. Prezelin, K. Baker, R. Bidigare, N. Boucher, T. Coley, D.
Karentz, S. MacIntyre, H. Matlick, D. Menzies, M. Ondrusek, Z. Wan, and K.
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Staehelin, J., M. Blumthaler, W. Ambach, and J. Torhorst, "Skin
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Tabazadeh, A., K. Drdla, M.R. Schoeberl, P. Hamill, and O. B. Toon,
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Protocol on Substances that Deplete the Ozone Layer", UNEP, Nairobi,
Kenya, 1994.
United Nations Environmental Programme (UNEP), "Environmental Effects of
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United Nations Environmental Programme (UNEP), "Environmental Effects of
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Urbach, F. "The cumulative effects of ultraviolet radiation on the skin:
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