29G
CHAPTER-6
ANTARCTIC ENVIRONMENT RESOURCE DEVELOPMENT AND CONSERVATION
INTRODUCTION:
Antarctica is not prestine anymore. Exploitation in any form
threatens the balance of natural ecosystems and this is
especially true in Antarctic. There is little ice free ground
and man nJW competes for this with the animals and plants.
Increased activities in the Antarctic bring with them the
certainty of some level of pollution and the introduction of
alien species to this remote and biologically simple continent.
The Southern Ocean food chains dominated by the small crustacean
Krill are being heavily fished in some areas, for both squid and
fish. The whale stocks were irreparably damaged a long time ago.
Only intelligent and active management of the entire ecosystem is
essential if we wish to conserve the special features of the
Antarctic both for our continued use and, as I would like to put,
'for the health of the planet'.
The Antarctic provides us with at least three essential
features of global importance, all of which require these active
conservation measures. The first is the use of the continent as
a pollution monitoring post. Antarctic snow is generally cleane
than the distilled water in laboratories and provides us with a
baseline against which we can measure increasing global
pollution, both of biologically toxic compounds such as lead and
of pJtentially deletarious gases such as carbon dioxide. That
297
pJllutants can get into the Antarctic eventually is shown by the
DDT levels. in penguins and the layers 6f radioactive fallouts in
show.
The global changes associated with increasing carbon dioxide
and methane (green-house effect) are likely to show up their
impact first in the polar regions which are much more sensitive
to small changes in atmospheric temperatures than any other
latitudes. Increased melting of the icecap is virtually certain
if the world warms significantly and this will affect world sea
levels. To predict how quickly and by how much, we need more
information for a model of the energey balance of the ice sheet.
Any major expansion of activities, such as mining, which might
change the reflectivity of the snow could hasten melting at a
local level.
The
content
Southern Ocean plays a crucial role in the
of carbon dioxide. The cold waters have
atmospheric
both a high
solubility for the gas and the huge population of phytoplankton
mop up the carbon and deposit it in the marine sediments. In
these ways the Southern Ocean accounts for at least 35% of all
the carbon dioxide produced worldwide. In a period of shrinking
forests and spreading concrete elsewhere in the world we cannot
afford to lose the sink potential of the Southern
disruption of its food chain.
Ocean by
Secondly, to maintain and increase the levels of marine
living resources taken from the Southern Ocean we need a
management plan to ensure that toJ much is not taken away in any
o~e year, particularly of any one species or from any sensitive
area such as the breeding grounds. CCAMLR is already involved in
this field but it relies on data from Antarctic Scientists to set
catch limits and fishing areas.
Thirdly to provide protection for this very wild area of the
world we need to know enough about the Antarctic to assess
environmental impacts for scientific and other developments, to
predict rates of recovery from disturbance and to monitor
compliance with regulations on waste disposal etc.
So far, man's impact up~n the Antarctic environment has
been negligible, but t~ is concern that overharvestng of krill
and p~ssible marine pollution resulting from any future offshore
oil exploration may undermine the krill basis of the Antarctic
ecosystem. Environmental regulations wilt form an important part
of the legal regime for the exploration and exploitation of the
Antartic mineral resources, primarily oil and gas. The Antarctic
Treaty framework does not legally bind non-signatory states, but
under general international law all states are bound to refrain
from inflicting damage upon the planet's environment. Also some
marine pollution conventions apply to the Antarctic waters, and
the 1982 U.N. Convention on the Law of the Sea comprehensively
covers the protection and preservation of the marine environment
of all o~eans and seas. The preservation of the Antarctic
environment will remain a high priority irrespective of what
legal regime will g~vern Antarctica after 19~~ when the
Antarctic, Treaty may, and most probably will, be subject to
review.
288
299
In comparison with other cont~nents, this frozen continent
has been substantially less affected by man's activities.
Indeed, the natural conditions of sub-antarctic islands, lying on
and near the Antarctic convergence, have been deteriorating more
fastly due to increased human activities, mostly being governed
by western powers.
(a) Dumping:
Every year thousands of tonnes of cargo and millions of
gallons
little
of fuel brought in to Antarctic (90% by ship), but very
of this is ever removed. Most remain as buildings,
machinery, solid wastes, particulate matter, and gases. The main
products of burning millions of gallons of oil and gasoline each
year is heat, carbon-dioxide, nitrogen oxides, sulpur-dioxide,
hydrocarbons and other particles. whenever these products are
emitted, they increase background concentrations in the air and
become incorporated into the seas, ice, snow and soils. However,
because co~centrations of combustion products are low in
Antarctica the environmental effects are generally localized. The
general criteria for selection of a suitable site for a base are
reasonably level ground, free from permanent snow and ice, and
good access to the sea in summer. These same factors also make
such sites likely to support permanent plant
breeding grounds of sea-birds, or both. It
co~nunities, or
is therefore,
inevitable that such leases must have some impact, such as the
disturbance to nesting birds (close approach to penguins m3y
cause them to desert the nest and cease breeding for that year).
For example, at the Cape Royds, Adelie Penguin nests started to
A.t!onttc Oceor> A South
f f.
A
--- ~- . -,. ..
West • Antarctica . ,
: ,~ ~ ~------- •. 1_
L= I~E shelf
• qeg,on of mour.tJ "S
or,j exposej rcx:r
I _,. -' ..- II, 'T'>
East Antarcttca
300
\: ~ . ~ ..
·j~-'' / '-
,/ ~V.r.>es
)
,.-r· I
J-. ~' )
Map of Antarct1ca show1ng generalized reg1ons of mountarn5 and summer-snow and 1ce-free ground where terrestrial and mland water ecosy;,t(·rn,, c.<· develop ( al1er Tedrow and Ugollnt in Tedrow. 1966) A-A rs the brogeographrc boundary between the marrtrme Antarctrc to the West and the contr'1ert.; A:otarctrc to the East (from P1ckard and Seppelt 1984)
301
decline soon after the establishment of the research station at
McMurdo Sound, and the situation became worse when tourist
parties started visiting the area.
(b) Bases:
; major re3ult of human occupation of bases is the
accumulation of waste and the contamination of the environment by
it. A conspicuous feature of many Antarctic bases is their
associated dumps of worn out or abandoned equipment and
packaging. Whilst aesthetically displeasing such dumps h3ve
little biological effect. McMurdo sound, for example, is now
l~ttered with barrels, fuel lines tractors and bear cans. The
Antarctic Peninsula has been the scene of a great deal of human
activity over a long period. Man's impact on these areas, both
historical and recent is to be reviewed extensively.
However, a code of conduct was drawn up by the Antarctic
Treaty Nations in 1975, and covers the disposal of wastes by
~xpeditions and bases. It requires that for coastal bases, with
certain exceptions, liquid waste should be flushed to sea, non-
combustible dumped in the sea, combustibles burn, plastics,
rubber and rajioisotopes should be removed from the Treaty area.
However, it appears that little effort is made at many research
stations to observe this code.
(c) Others:
Although currently negligible, the first announcements in
1960s that DJT compounds had been detected in Antarctic wildlife
received publicity. Later organochlorine pollutants of
302
agricultural and industrial origin were also
highest residues records till 1980 in Antarctic
been DOE and PCB concentration of 46 ppm
confirmed.
wildlife
and 185
The
have
ppm
respectively, near Palmer Station. Recently the graveness of
hydrocarbons prensence was realised in local context, mainly by
local sources, but would have very little effect on the ecosystem
as a whole. However, further large-scale exploitation of natural
resources would certainly create an entirely different set of
circumstances. From what has been said earlier, it is apparent
that there is no immediate threat of mineral exploitation on land
and the exploration activities, which would precede exploitation
would have minimal environmental impact. Nevertheless, it must
be borne in min~ that if circumtances, in the future changes and
hard-rock minerals-exploitation on land becomes a reality, then
some of the resulting impacts would be severe eventhough they
might be localized. 'The key impact of physical altercation of
the land surface over large areas, the deposit of rockwaste and
tailings on land, the spread of dust over adjacent ice, altering
its albedo and perhaps causing melting, the washing of pollutants
such as fine tailings into freshwater lakes and coastal seas,
with considerable potential ecological effects, the accumulation
of wastes, including sewage, and pressures from recreational
activities and transport of personnel. Further in Antarctica the
sedimentary deposits in which oil might be found are premarily
confined to the narrow continental shelves, and it is these areas
having high biological productivity. The significant impact of
oil spills on Antarctic Environment is being feared, particu1arly
on krills. Flaring of naturalgas, disposal of wastes from
drilling platforms and other installations, the effects of
drill~ng muds, and accidents during operations are also importJnt
factors for environmental health assessment. Although
insufficient evidence exists about the toxicity, decomposition
chemistry, and inhibiting traits of crude oil deposit with surity
the precise impact or persistence rates of hydrocarbons in
Antarctic ecosystems.
Sewage and Waste Disposal System:
Technology used for waste disposal may create its own impact
upon the environment which may be greater than wastes themselves.
Because stations require resupply and relief on a regular basis
these supply shi'ps could be used for transporting waste from the
coastal stations, although it is costly and inconvenient.
Removal also allows for recycling of waste elsewhere. Further,
growing settlements also increase power consumption and excretory
waste production. Plans for big hotels for tourists are indeed
harmful. The need is for more compact environmental standards
and stricter ecologically concious safeguards in llcensing
qualifications. Special care should be taken for water quality,
solid waste disposal and toxic substances. For example, stations
like McMurdo have been criticized for adding pollutants to the
air, soil and water by burning solid wastes or dumping rubbish
and human waste on the ice or sea or chemical contamination of
land or ocean without appropriate treatment. In other cases,
debris, discontinued equipment, and even some station buildings
were abandoned. Uncontrolled dumping of waste from ships (e.g.
304
at Palmer station) has locally affected the population dynam1c of
benthic species. Nonscientific collecting and "souvnier hunting"
also have contributed to the degradation of Antarctic
environment.
In nutshell, at present research stations seems to be the
major cause of environmental damage in Antarctica. The vast
amount of packaging material used every year for transporting the
food, equipment, fuel and building materials necessary to support
the research means that sawdust and polystyrene granules have
been widely dispersed around the stations. Many of the buildings
are of wood and its abrasion by wind driven ice-particles has
resulted in the dispersion of wood fibres for considerable
distance downwind. The sewage effluent poses some difficult
problems too. Poor disposal techniques have produced unwanted
enrichment of habitats in nutrient-poor areas and has introduced
new bacteria to Antarctica. The increased sophistication of
Antarctic science now requires careful consideration to be given
to disposal of laboratory waste, which may contain a wide range
of toxic organic and inorganic chemicals. All Treaty nations
need to make much greater educational efforts to
awareness amongst their scientific and support staff
possible
the crash
environmental consequences of their
of DClO air crash on Mt Erebus and
actions.
recent
increase
of the
Further
crash of
American plane at Grationland near McMurdo station opened new
area of serious contaminants. However, no doubt, operating
safely in Antarctica is very expensive.
Guidelines to Limit Local Pollution:
Over the yeas, several attempts have been made
proper procedures for assessing and limiting the
Scientific research activities on the Antarctic
305
to develop
impact of
environment.
Voluntary guidelines to limit pollution around Antarctic bases
were adopeted in 1972 and a code of environmental conduct was
proposed in 1975:
It acknowledged that: "the majority of existing research
stations were established in their current localities because
these were the most convenient places for either logistical or
Scientific reasons and without giving thought for environmental
effects". It also affirmed that there was often significant
damage caused to the locality as a direct result of the stations
being built there. The report pointed out that environmental
impacts are not limited to the terrestrial ecosystem and living
organisms only.
It also claimed thtat the biggest and most consistent
problem is the disposal of waste. Solid wastes, such as
discarded machinery, are offensive to the eyes, but of little
biological significance. Plastic and rubber wastes carry long-
term consequences; small plastic particles are increasingly found
in the digestive tracts of seabirds. SCAR recommended that such
products "should, wherever possible, be removed from the area,
but otherwise dumped on land. It should not be burnt unless it
can be incinerated with adequate emission control."
Domestic and human wastes, kitchen refuse and natural wood
can all be disposed of by placing in the sea with minimum
treatment, SCAR recommended, but all radioative waste, wastes
containing high levels of heavy metals and harmful persistent
organic compunds, should be removed from the Treaty area.
The Scale of the Problem: Some Case Studies
Any base in Antarctica having yet to have the problems and
practicalities of waste desposal. is used to reduce the large
volume of combustible materials and refuse is dused with waste
fuel. Icy rubbish dumps were reported by SCAR member Dr.Ron Lewis
Smith in
appeared
Casey.
February, 1986. He commented that Wilkes Station
as it ·did when it was abandonded in 1969 in favour of
Many bases also place solid wastes in metal drums and
dispose of them at offshore dump sites. Larger pieces of
machinery are often placed on the ice and left to sink with the
summer thaw. One such dump site, off Me Murdo base, has been
described by divers as "essential1y dead, the sediment is so full
of DFA (diesel fuel additive) it almost appears combustible
Clearly there was a massive spill of sme sort and I doubt if that
amount of DFA will be broken down in the near future ... "
Nuclear Aspect
Though the treaty bans nuclear explosions as wel as the
disposal of nuclear waste in the Antarctic but it does not forbid
the use of nuclear power in the region.
307
In the 1960s the US installed an experimental l.SMW
pressurrized water reactor, nicknamed "Nukey Poo", at its Me
Murdo base to find out a more economical way of providing heat
and power. It arrived by ship on 21 December 1961 and was
situated half-way up Observation Hill near Mount Erebus, an
active volcano. Power production began in July 1962 and, four
years later, the US Navy claimed that it had broken the record
for the longest continuous operation of a military nuclear
reactor. In 1971 the power output was increased by 10 per cent.
During the whole period they kept the reactor and claimed
that the only serious problem had occurred in 1962 when hydrogen,
a by-product from the reactor, caught fire but that there were no
injuries or release of radioactivity. In reality, the 10 years
of the reactor's opeation was an expenive story of shutdowns,
fire damage and radiation leakages. In 1972, a temporary
shutdown caused by coolant water leaking into the steam generator
tank coincided with a Navy cost-effectiveness study. They
concluded tha it would be too expensive to overhaul and upgrade
the plant, and, as a result, it was close down and demolished
over the next three Antarctic seasons at a cost of $ 1 million.
The reactor and 101 large drums of radioactive metals were
shipped back to the US for burial. Later, another 11,000m3 of
soil and rock were also removed and shipped back to the US. It
took further six years of cleaning up before the site was
declared to be "decontaminated to levels as low as reasonably
achievable", and it was finally released for unrestricted use in
May 1979.
308
(6) THE FRENCH AIRSTRIP
One of the focal point of Greenpeace's Antarctic campaign
has been its opposition to the French airstrip near the Dumount
d'Vrville base in Terre Adelie, due South of Tasmania which it
considers a breach of Antarctic Treaty rules. The Dumont
d'Vrville base was constructed in the 1950s after the previous
French base at Port Martin was destroyed by fire~ Ironically,
this site was chosen because of the richness of fauna and flora
in the area, which made it almost unique in the whole of
Antarctica, including as it does one of the very few emperor
penguin colonies outside the Antarctic Pensinsula. This means
that the French programme of research is limited compared to that
of other countries. Even after several times by SCAR, but no
specific proposals were put before the organization.
In the construction of their airstrip, the French have
been accused of breaching the Agree Measure in several respects:
Killing native birds without a permit: failing to minimize
harmful interference to the "normal living conditions of mammals
or birds'', and using explosives "close to concentrations of birds
and seals".
Greenpeace and other conservation groups have also
the project because of the likely long-term harm to the
of the region. Since studies of the emperor penguin
opposed
wildlife
colony
began, the number of couples has decreased from 6,500 to about
3,500, due in part to human presence. The airstrip will cut off
the emperors' favoured access to their breeding colony.
Many other bird species, including 2,500-3,000 paics of
Adelie penguins, 300 pairs of Cap pigeons, 100 pairs of snow
petrel and 100 pairs of Wison•s storm petrels will also be
directly harmed because of the construction.
Greenpeace protesters boarded the French-chartered vessel,
Polarbjorn, in Le Havre and occupied the mast for 56 hours in
protest. They claimed that it was carrying equipment for the
construction of the pronjected airstrip.
In November 1984, members of the prestigious International
Union for the Conservation of Nature and Natural Resources (IUCN)
passed a.resolution which called upon the French Government to
consider other options. The resolution requested that they and
the Antarctic Treaty Consultative Parties should "throughly study
the option of protecting Pointe Geologic from further
construction".
In December 1984, Greenpeace conducted a further action plan
against the Polarbjorn in Hobart, en route to the Antarctic,
involving Vega and six other boats. Demonstrations were also
held in Sydney and Melbourn.
1985, the French delegation
However, with no effect, in October
at
Consultative Meeting announced
the 13th Antarctic
that the construction
Treaty
of the
airstrip would proce&d but did not indicate when. On the other
hand, the ATCPs have exhibited little will to deal with the
problem. At least one government, New Zealand, is known to have
made direct representations to France over the issue, and the
Australian Government has reportedly made a formal determination
310
that a breach of the Agreed Measuere has occurred. But the
question has never been formally raised in the context of gO
Antarctic Treaty Consultative Meeting or in any other meeting ~f
the Treaty System. As a rsult, the French have never formally
been asked to explain the alleged violations.
In November 1987 the French government announced that work
on 1000m run-way at Terre Adelie, which was interrupted in 1984,
would last for about five years at a cost of 100 million franc
($10 million).
(c) IMPACT OF TOURISM
Besides permanent human settlements and scientific research
sites, the other human incursion in Antarctica is touris~, the
only commercial activity on the continent itself and one which is
proving increasingly popular.
Over the next two seasons, some 11,000 passengers overflew
the continent, an 11-hour journy of which some 90 minutes were
spent over Antarctica. Such flights ceased abruptly after an Air
New Zealand DC 10 crashed into Mount Erebus 28 November 1979,
killing all 257 passengers and crew. Also, cruise liners have
been operating in the area since 1958 and, and in the period up
to 1980, more than 80 voyages have been undertaken by passenger
liners from Germany, carrying an estimated total of 7,000
passengers.
The question of the effects of Antarctic tourism has been
addressed several times at meetings of Treaty members. Under the
311
various rulings and guidelines, it is the rsponsibility of e~ch
Consultative Party to ensure that any of its national who are
part of a tourist or non-governmental expedition abide by the
Agreed Measures. However, it is both politically unacceptable
and legally difficult for any Consulative Party to prevent any
non-governmental expedition from exploring or traversing the
frozen continent.
At least seven commercial tourist voyages and a number of
smaller expeditions have got into difficulties and required
assistance. ATCPs have expressed worries that tourism raises
the possibility of expensive disruptions to persoonnel at
research stations and a hazrd to life and, in some instances,
base equipment.
When the Air New Zealand DClO crashed on Mount Erebus, 20
hours of US Hercules Cl30 flying time and many hours of
helicopter time were diverted from the tightly scheduled
Scientific programmes. In January 1968 the tourist ship Magga
Dan ran grounded at McMurdo for several days and the Llndblad
Exokirer has twice run aground in the Antarctic Peninsula,
requiring expensive and disruptive reascue and repair operations
to be mounted.
Aside from the disruption caused to bases, by an influx of
tourists or by distress calls, there is the question of the
additional pleasure tourists place on the natural environment.
Tourists could unwittingly spread bird or plant diseases and
introduce new kinds·of organisms to the Antarctic. The expansion
312
of tourist facilities may also have a significant impact. AL
present this is a small problem, but situation is rapidly
worsening. Under a World Park regime there would have to be
regulation of some sort viz.
(i) PROTECTED SITES (SPAs and SSSis)
The first attempt to preserve Antarctica's environment came
in 1960 at a meeting of SCAR at which a series of general rules
of conduct for expeditions operating in Antarctica were drawn up.
Four years later this led to a more elaborate set of Agreed
Measures for the Conservation of Antarctic Flora and Fauna, for
the whole area south 0 of 60 Cs was deemed to be a "special
conservation area". 2
This final measure was supplemented by the creation of a
network of Sites of Special Scientific Interest (SSSis),
beginning in 1975.
Such measures are presented as an ambitious experiment in
conservation. Yet there is no express prohibition on the
erection of a base within an SPA and, if there is a conflict
between a base siting and an area proposed as an SPA, the problem
has usually been slaved by "adapting" or terminating the SPA.
The best example of this occurred at the Fildes Peninsula SPA
where the Soviet Union and Chile both set up bases in 1968.
Their mere presence was bvound to have a damaging effect.
The other Consultative· Parties, instead of raising
objections at that year's Consultative Meeting, actually reduced
313
the SPA to a fraction of its former size in order to exclude the
Soviet Bellingshausen station and surrounding areas in which
travel and disturbance were inevitable. The original SPA
designation centred around several small lakes of outstanding
ecological interest. As a result of the 1968 decision, only the
most interesting one retained its protected status. This reduced
area was so affected by the presence of bases that its SPA
status was terminated in 1975.
(d) Marine Pollution Sources
The findings BIOMASS in terms of of FIBEX and SIBEX 1s of
great relevance. FIBEX was undertaken in the austral spring of
1981 and involved 17 ships from 10 nations who correlated weather
and ocean information with observations of animals and krill.
Its most
Melville,
Island.
several
spectacular finding was made by the US vessel RV
which sighted a ''superswarm" of krill near Elephant
Estimated at 10 million tonnes, the swarm occupied
square kilometers of sea to a depth of 180m (600 ft)
below the surface. Scientists estimated that this single swarm
was equal to about one-seventh of the world's total fish and
shellfish catch for a year. News of this unexpected and so-far
unrepeated discovery brought 35 Soviet fishing vessels to the
area in order to reap the benefits.
SIBEX phase I followed in 1983/84 and phase 2 in 1984/85.
Again, multidimensional observations were taken, ranging from the
temperature, salinity and oxygen concentration of sea water to
314
weather conditions, visibility and ice cover, and from tho
concentrations of krill and phytoplankton to sightings of whales,
seals and seabirds.
(e) Storage of data: Such as Honeywell storage of complete
information-gathering exercises BIOMASS data are to be welcomed
if we are to gain a fuller picture of the Southern Ocean
ecosystem.
(f) Oil and Other Mineral Resource Development Risks: The
greatest environmental risk from oil development is the leakage
of oil in coastal, ice-free waters from tanker spills or undersea
wells. Indeed, ~he effect of such an oil spill caught in coastal
waters could persist for years. The lighter hydrocarbons in the
oil would evaporate slowly while the heavier ones sank, possibly
coating the underside of the sea and pack ice or the "anchor" ice
on the sea bottom where many small organisms live. The report
concludes that repeated tanker losses en route to Antarctic ports
and tank storage farms - and not the offshore wells themselves
would be the most likely sources of oil pollution.
As the Ohio State report notes, "There is no question that
any resource exploitation will cause severe, and in many cases
permanent, local impact on the environment because of the
extremely slow rate of recovery that can be expected." Life in
the Antarctic moves slowly, the metabolism of organisms is slower
than in temperate climats; a footprint in the moss can last for
decades. Although the impacts of a mine or off loading port
HABITAT VULNERABILITY
~- -~-/
/ HYOROlAkBON / PENETRATION
f---·
\ HYDROCARBON \ PERSISTENCE
~/ ~I
C..,;
/',
0 ~~ PETROLEUM 7 IMPACT
A(UTf -CHRONIC POPUlATIOt-.; \
I TOXICITY RESPONSE
REPRODUCTION J \-------< \~HAL-SUBlETHAl
~-_____/ POPULATION SENSITIVITY
POPUlATION
IMMIGRATION /
COMMUNITY RECUPERABILITY
Figure Schematic representation of the impact of petroleum hydrocarbons on marine env1-
I
315
TABLE SOME COMPONENTS OF THE SYSTEM AFFECTI~G OIL EXPLORATION AND EXPLOITATION IN &~TARCTIC SEAS
Factors influencing site selection
*
" * *
*
*
*
Geological indications of oil potential
Bathymetry and structure of sea bed
Iceberg and pack ice condition
Currents (surface and deep)
Climate
Special biological features of s1te (and alternatives)
Costs of operation
Technological factors influencing L'11:Jacts . *
•
* *
*
*
Use of seismic explosives
Drilling processes
~ature of rigs or platforms
:-;at~..:re of wellhead completion (eg on or below seabed)
Nature of oil storage system
Nature of transport system
strc:cture
Nature of pollution control syste:.. (1nclud1ng ::-.anagener. t)
Nature of emergency procedures (ir.cluding tra1r.1ng)
Environnental factors affecting i..'11pacts
*
*
*
*
Types and concentrations of pollc:t~nts, especially oil, released
Rates of physical and biological je~radaticr. 8f oil and other pollutants
Rates and directions of dispersion of oil and ~oll~tar.ts
Relative location of emissions and l1ving targets (benthos, phytoplankton, krill and other zooplankton, fish, seabirds, seals, whales etc)
Sensitivity of living targets to c1l and other pollutants and to substances used in cleanup
317
might not be felt a few miles down the coast, the mosses,
lichens, birds, and marine organisms at the site might not
recover for decades.
The Ohio State study details three kinds of proposed
minerals activities and their environmental consequences. One is
an underground, platinum-group metals mine in the Dufek Massif,
capable of producing approximately 100,000 troy ounces of
platinum-group metals per year, with workers and processing
plants located underground and the output air-freighted to New
Zealand. The second is an inland chromite mine capable of
producing 100,000 tons of metallurgical grade chromite. Similar
to the first underground mine, it would be located closer to the
surface and use different processing facilities. Its output
would be carried by tractor sleds 2,400 kilometers to a coastal
port. The third case is a porphyry-copper deposit mine on the
northern Antarctic peninsula, producing 100,000 tons of refined
copper and molybdenum, gold, and silver. The copper would be
concentrated and refined on site and shipped directly to market.
Local impacts would be felt at the sites of the inland mines
and along their overland routes, although none so severe as those
occurring in closed basins and near rookeries and breeding
grounds along the coast. Exploratory drilling on- and offshore
would introduce drilling muds and circulating fluids, there would
be minimal impact if procedures were used like those now followed
in Antarctica's dry valleys. The Ohio State report recommends
that exploration be avoided, if possible, in enclosed basins, the
dry valleys, and in coastal rookeries and breeding grounds.
Suggested framework for the development of research projects atmed 31
Improving predictions of the possible impact of hydrocarbon exploration ~nd exploitation In the Antarctic
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,,..~, l'"""""'' U•tno<l~ ol da\Jrlg lctbelg ICOVII
Alltasctic 1om& lolo<,o f
Otl•nlti.oo ol ~ altvct~• of Funt•er dehnltlon ol 1n. IJ\llvenc. ol pack Ice on lhe lhOse typ.a ol marine a~lure ol those typea ol W1Jc1Uit &lld dynam.~ ol ecoayslema. wi#\i.n tr>a tOo'NTlUilO t>. I &00 m~t>Oo~iul &1\l&tclic ecoayat.m u a ecoay•tems lilo.ely lobe communi!Lea who .... likely lobe at1ect•d by al1tcltd by hydt~tbon hydroc.&lbo<l •JtP:Orallol'l ar>d • -4>10'• 1.>0n aoo uplol a tion; t x;>loi 1 at i.on IIT'o9"o"'e<S 0- aJ
ur.deral~ of poputet~. commi.K">l ty &00 .coay:otem Cy~ In ~ gic and loc.aJ 1/Uhol e ~.~ .... Almo~tt• &lld ~cap Otlarmlt'\•lk>n ol 0..J.el.u1e
poiiutanl ...... 1. ~e .... t, ol hydlourtx>n cont&IJUn&Uofl WI ttpita.lll&Uvt compOI"\tn~ ol ~ mann. ~ytltm (lrd~ing bitdt &1\d ~)
Fllat and ~ Older el~ c11 of .- at1cxl• lund • and ~V•Iiol\l ol hyal~a &1\d QU\er pollut&nla on "'I ~1\~ ol tM 11\&/N .COiyat.ma
~ t&l& ol vvlo4.u hyOI'~rt>onl u~r anlar'l.ic ..-.w~laJ COI\OiliON ~&O&Uon. ~kal uptakt and ~lc.aJ d~raaJ)
0.~ ol monlloling ' pr09fama b&U<S on ~alol
1~1 UIUIUvt \o ~ oncn.l\l&J polution
·---IV
·---lnlotmitkln 1 • c;v:r:r.g r,,
tl.ICI\ .,. ~ •• •
1..01\.S h ••• D¥ adC:itlonal re prou>eclive 1 • ~ betn Ldanllfl~
Otllrllt.W O.WI Glli oc.a~.
en'IVONn• (I) wal•
(cull•nta (\i)ua
( .......... (~) llo.ll
lPKr. ica
s .. bo (I) mot~
bathym•ll (ll)s.ol (W) alai (i>') ... ~
~(In<
ua••~~
Ch&t~
r~n&l ol <U
~ O.larn
~nl• ot ln. .... , • bol\orll I
·--lt~&nl
ale.&~
mtnl.J .. ) ace •t•t•
·lcln~)
• '•Q.nlo• .c., •• )
ve••• I
yna.m.n
ol Ice:;••<;
~~·
~ or J>d dtfii\II.V"
~ ~
lion ol ~·'"'' ~·'"
~and .own.nt.J
··-----Source: ''Report ot t\pcrh.'' 1n .·lntunic Ju11rnul of the Umted Stutes. Vol. .XIV (De, 1979), p 16
318
319
1'r-c mait-o: cn.v1.cOi11'l'!e,...1- .. l na.z&J!'ds et unde.rgrot.Htd ll\\nHtt ~A'HI!~;l Ht:i
felt by the relativeiy unstudied and unmapped 1\nta~.G:ft.C
permafrost. Most of the effects of an overland route to move the
ores to port would be eliminated, eventually, by further
snowfall. The report recommends using forms of transportation
that have least contact with the ground, such as aircraft or air
cushioned vehicles. Of course, local damage would occ·.Jr ·.·:!:·- 1'• ·
ports and tank farms were built.
The Ohio State report distinguishes, however, between
localized impacts some of which occur already in places of
heavy activity such as McMurdo Station - and "maintaining the
integrity of the Antarctic environment as a whole" (For example,
if offshore oilfields, mines, and ports used an area as large as
132,090 square kilometers, they would utilize only 1 percent of
the Antarctic continent's area. This would be analogous to
developing an area the size of Maine and Vermount, while leaving
the rest of the United States and Mexico intact. Local oil
spills, for example, would probably be carried away from the
continent by powerful currents and dispersed into the Southern
Ocean. On the other hand, the report warns that the sum of local
impacts could be severe.
Air pollution from open-pit mining or by particulates from
refineries could pose a key problem for the Antarctic
environment. It could alter the pattern of snowfall wh1le the
buildup of particulate matter in the atmosphere could alter the
region's radiation balance affecting the rate of ice melt. The
fact that the Antarctic interior is used to monitor global
pollution levels also should be considered.
As subsequent treaty recommendations and SCAR discussions
have indicated, the minerals issue means a new agenda for
Antarctic research. Zumberge wrote, "Even at the present level
of effort, hundreds of man-years of scientific studies will be
required before the components of the Antarctic environment and
the interdependent relationships will be sufficiently understood
to permit a reasonably confident assessment of the impact, man's
activities may have on the marine and terristrial environment in
Antarctica and the rest of the world.
The cost of cleaning up contaminated sites in Antarctica is
very high in terms of both dollars and human anxiety, if the
continent has to be preserved as a datum point for all scientific
and global pollution measures. In effect and meagre efforts by
participating consultative countries since their expeditions,
have failed to control the problem in true scientific forms in
Antarctica. Removal of contaminated portion and prevention of
further contamination has become a major problem. Also, we must
resolve the problems created by old, abandoned, and faulty
disposal
some of
sites. The time has reached when we must also examine
the new management practices that are being asked to
control and to keep track of wastes. However, it is difficult to
correct problems that were caused by the thoughtless dumping
practices of the past. Further, disagreements have developed
over the degree of risk that results from exposure to different
320
321
chemicals. These problems are compounded by the great number of
chemicals that are currently in use.
Question of Environmental Persistence:
Proper management of waste hinges on an evaluation of
certain key properties of waste. Those properties include the
degree of hazard and the persistence of the waste in the
environment. The degree of hazardness that a waste poses depends
upon its corrosivity, reactiity, ignitability, or toxicity. Some
hazardous wastes are particularly trouble some because they tend
to persist in the environment. Further, environmental
persistence of hazardous materials enter food webs. they
bioaccumulate as they pass from one trophic level to the next
higher trophic level. Biodegradable wastes, such as paper, laws
clippings, and wood from demolition and non-biodegradable
elements, such as mining and mineral wastes, viz. lead, mercury,
cadmium and heavy metals pose both short term and long term
problems.
Question of Waste Disposal Methods:
Virtually all our activities generate waste. However, waste
reduction lowers collection and disposal costs and lessens
demands on raw materials and energy.
Main disposal techniques applied now-a-days are
1. Sanitary Landfills - sealing wastes (in mining areas)
between accessive layers;
(a) Trench lawfills
322
(b) Area lawfills
(c) Mounded II
2. Incineration (burning combustile solid wastes and melt
3.
4.
5.
6.
certain noncombustible materials)
Ocean Dumping
Reuse Techniques
Waste Reduction
Management of Radioactive and other hazardous wastes
Reclaimation
Magnetic Separation
Composting
Hydropulping conversion Pyrolysis.
The 3 principal methods of disposal of hazardous wastes have
provided an dispose of hazardous wasts are:
1. Secure landfills
2. Incineration
3. Deep-well injection (for oil exploration and
extraction)
Unfortunately, the much higher disposal costs and hazardous
wastes have provided on incentive for "might report dumps mid-
night dumpers" to dispose of hazardous waste illegally.
The key to safe disposal is proper isolation of wastes. And
eliminating or minimizing migration of water through disposal
sites is the most important factor to control. Although new
disposal technology should reduce future problems and clean old,
leaky, environmentally unsound disposal sites. Waste exchanges
and chemical recovery are techniques used to reduce the quantity
of hazardous wastes. The technology to dispose of radioactive
323
wastes. At present, deep underground storage is the preferred
method. Undoubledly, opposition will be voiced concerning any
repositionary site that is chosen.
The Ozone Question
A poisonous, highly reactive compound of three oxygen atoms
- in contrast to the two-atom molecules (02
) that make up
the bulk of the oxygen in our atmosphere - ozone is concentrated
into a 50 km (30 mls) thick layer that begins 16 kms (10 miles)
above the ground at the lower edge of the stratosphere. It
shields life on Earth from the damaging effects of ultra-violet
radiation.
The existence of a "hole" or depletion, in this essential
protecting layer over Antarctica each spring was noticed by the
scientists from the British Antarctic Survey in 1981, working at
Halley Bay, and later confirmed by satellite observations. Since
then, the size of the "hole" has steadily increased, and in 1987,
the layer was half as thick as at the same time of the year 1970. 3
It is widely accepted that the natural rate at which ozone
is destroyed is being increased mainly by the presence of free
chlorine atoms which are released by the decomposition of
chlorofluorocarbons (CFCs) above the ozone layer. This family of
chemicals is used as a coolant in refrigerators and air
conditioners, as a blowing agent in the manufacture of foam, and
also as a blowing agent in the manufacture of foam, and also as a
propellant in aerosols. At present, 770,000 tonnes of CFCs are
.324
produced every year. Free chlorine atoms, or radicals, sink down
into the ozone layer and attack the ozone (03
) to form chlorine
monoxide (ClO) and o2 . The ClO then combines with a free oxygen
atom to form o2
and a chlorine atom. This catalytic reaction
continually repeats itself, so that for every chlorine atom
released, an estimated 100,000 molecules of ozone are removed
from the atmosphere. Other radicals react in similar ways.
The damaging effect of cholrine on the ozone layer appears
to be enhanced in the Antarctic region by the extreme cold during
the three months' darkness of the Antarctic winter. In these
conditions, chlorine and other gases accumulate in inert forms.
The ultraviolet light of the spring sun initiates a sequence
of complex reactions in which the chlorine and other ozone-
consuming gases suddenly become active, a reaction speeded up by
the presence of clouds of ice particles. The rapid creation of a
"hole" in the ozone layer is the result and this is deepening
every year.
In 1987, the American $16 million Airborne Antarctic Ozone
Experiment, which included European scientists, made the most
detailed study yet of the atmosphere over Antarctica by flying
aircraft through the ozone "hole" for the first time.
This international effort reflects the growing concern among
many scientists, environmentalists and politicians, that, what we
are seeing in Antarctica may be the beginning of a much wider
breakdown in the ozone layer.
-1.4-,------.--------.,-------r------~---
-123 -330 •
• -199
60
-342 -270 -21
-400 -300 -200 -100 0 100
Scale in thousands of years before ( -) and after ( +) present
Fig. 118 Long-term variations of climate (effectively of world temperature) over the past 400,000 years and calculation for the next 60,000 years, based on th~ orbital variables. Crosses show how far the part of the curve relating to the past agrees with oxygen isotope measurernents from deep ocean bed cores. The numbers give the dates in thousands of years before and after the present time of key points on the curve. (Reproduced by kind permission from Professor Berger's article in Vistas in Astrononzy ( 1980)- ~ce footnote in text.)
Fears
radiation
are already being voiced that
may not only harm humans,
increased
but will
ultraviolet
also
deleterious effects on Antarctic phytoplankton, with
reaching ecological consequences in the Southern Ocean.
have
far-
The crucial efect of CFCs on the ozone layer has now been
widely accepted, and the first international treaty to limit
their production was intially signed by some 40 countries in
September 1987. Given that a large proportion of CFCs now
present in the atmosphere will still be there in 100 years' time,
much more drastic cuts in production will be needed if the ozone
layer is to continue to shield the Earth.
Thus this tenuous layer of gas, tens of kilometers above our
heads, is an essential part of the ''life support system" of
Planet Earth. Without the ozone layer, it is doubtful that there
would be any life on land. Although ozone is constantly being
manufactured in the stratosphere, human activities may still tilt
the balance of the reactions so that the concentration of ozone
falls. The usual analogy concerns a tub of water that is being
filled by a tap at a constant speed, but the tub has a hole in
its bottom through which water escapes at the same speed. The
level of water in the tub (equivalent to the concentration of
ozone) stays the same. If we make the hole in the tub bigger,
the first thing that happens is that more water flows out. As it
does so, the level of water in the tub drops. As the level
drops, the pressure of water at the hole drops, and the flow from
the tub slows down. At some point, a new equilibrium is reached,
with the level of water in the tub constant at a lower level.
327
328
Present concern about the ozone layer centres on the
possibility that human activities may be making the "hole in the
tub" bigger, speeding up the rate at which the ozone is being
destroyed in the stratosphere, while the production rate stays
the same.
This could also happen if molecules such as Nitrous Oxide NO
are produced by human activities and reach the ozone layer. The
first concern about possible human impacts on the ozone layer
came in the 1970s when plans were being made for large fleets of
supersonic aircraft, flying higher than Concorde. The jet
engines of such aircraft, sucking in air to provide the oxygen
they needed, would inevitably have produced NO (and other oxides
of nitrogen) since so much of the air is nitrogen. These
aircrafts never flew, but that concern might still apply if
hypersonic vehicles. The discovery of a "hole" in the ozone over
Antarctica shows that the atmosphere may respond in a "non
linear" way to this kind of disturbance.
What seems to have happened over Antarctica is that the
buildup of chlorine had very little effect on the ozone layer
until some critical threshold was reached. Then, a very small
increase in the amount of chlorine caused a very big change in
the chemistry of the stratosphere.
According to one opinion, the unique meteorology of the
Antarctic means that there is little prospect that the hole in
the sky there will spread to cover the rest of the world. But
there is now concern that some separate nonlinear effects may be
2.5 ,_ - 2.5
>-~
c ·-.u 2.0 r- - 2.0 0
~
'-Q)
Q) u Ol c c ::I c ~
u 1. 5 Q)
..... ::I ~
0 ..... Q)
0.
E
Other trace
-gases~
-I Ozone
f Nitrous_o)(jde-
I Me_!_h~n~ _
-0
, .5 Q)
Ol c: 0
0:::
Q) 1.0 .... r- - 1.0 Q) ChLorofluorocarbons u 0 -..... -----::I
(./')
0.5 ..... - 0.5
Carbon dioxide
0 0
Figure 1.3 Cumulative equilibrium surface temperature warming due to increase in carbon dioxide and other trace gases from AD 1980 to 2030 as computed by a one-dimentional model. (After Ramanathan et al.. 19H5.) Due to fcedha<.:k mecha- · nisms as revealed hy general <.:irculatior) models (d. sub-section 4.4.3 and Chapter 5) expected changes arc O.H---2.6 times the values given in this figure
32~)
330
at work in the other parts of the world, and that other holes in
the ozone layer might appear, most probably over the North Pole,
which appeared this year but possibly anywhere. According to
Environmental Protecting Agency of USA, every 1 per cent increase
in the concentration of ozone in the stratosphere there would be
a 5 per cent increase in the number of non-malignant skin cancers
each year. Radiation with wavelengths in the band from 240 to
290 nanometers, known as UV-C, does not reach the ground at all
today, so its effects on life are harder to predict. We cannot
be certain, though that under different conditions it might not
reach the ground. In the laboratory, radiation within these
wavelengths destroys nucleic acids (RNA and DNA) and protein
the basic molecu~es of life.
A team of scientists from the US conducted studies at Thule,
Greenland, in late February this year, where they recorded the
ultra-violet and visible spectra of moonlight and scattered
sunlight. Fortune cooperated with the team's efforts and a polar
vortex swirling in the lower stratosphere lingered near Thule at
77 degrees North during the team's two-week observation period.
The vortex provides the coldest temperatures in the
and hence provided the best conditions for detection
destroying chemicals. The team detected chlorine
stratosphere
of ozone-
dioxide in
"disconcertingly large amounts". Over Antarctica in late
winter, there is two to five time as much chlorine dioxide as
seen in the Arctic. The Thule team also found very low levels of
nitrogen dioxide over the Arctic region - about the same amount
as seen over the Antarctica in early spring.
331
Wayne Evans, of Environment Canada, 4 government research a
organization, first observed the phenomenon over northern
Scandinavia and the Soviet Union in March 1986. Like the
Antarctic hole, the Arctic hole forms inside a vortex of low-
pressure air and stratospheric ice clouds. the Arctic hole has
what Evans describes as "strange layers" 20 kilometers above the
ground in which roughly half the normal amount of ozone is
present.
Although the Arctic hole appears to be structurally similar
to the Antarctic hole, it is only half its size.
size of Greenland, whereas the southern hole,
extent, cover the entire continent of Antarctica.
It is about the
at its maximum
An important difference between the two holes, says Evans,
is that the behaviour of the Arctic hole is more unpredictable
and harder to study than that of the Antarctic. This is because
the more active weather systems in the northern hemisphere
complicate the formation of the hole.
The real concern about the Antarctic ozone hole is that it
represents a new loss of ozone from the atmosphere" said Evans,
who fears that the Arctic hole might become a similar "sink" for
the northern hemisphere. A preliminary investigation with a
high-flying aircraft that "nudged" the Arctic vortex in February
found elevated levels of chlorine monoxide. This gas is widely
regarded as the "smoking gun" which shows that chlorine from CFCs
is destroying ozone.
However, the most popular theory by K.K. Tung claims that as
sun returns to Antarctica in early spring, a 'diabatic'
circulation with upward motion at high latitudes and downward
motion at mid-latitudes will take place. This circulation will
tend to redistribute ozone in spring with lower values over the
pole and higher values at mid-latitudes.
According to West German Scientist, K. Labitzta, Vortices
over both Arctic and Antarctic have become stronger since 1979
and thus the timing of the final warming over Antarctica has been
simultaneously delayed as a result of increased stratospheric
aerosol content following recent volcanic eruptions.
The scientific evidence and policy concerns outlined in this
report have generated substantial momentum toward new
restrictions on CFCs in recent months. In March 1986, EPA
Administrator Lee Thomas stated that "we may need to act in the
near term to avoid letting today's risk become tomorrow's
crisis." ln <J. separate st<J.tement, the DuPont company noted that
"Neither the marketplace nor regulatory policy... has provided
the needed incentives" to justify investment in alternatives to
CFCs.
The scientific community has also added its voice to the
call for action. The Advisory Group on Greenhouse Gases,
sponsored by the World Meteorological Organization (WMO),
International Council of Scientific Unions (ICSU), and U11ited
Nations Environment Programme (UNEP), stated in July 1986 that
many uses of CFCs "can hardly be considered essential" and
332
333
"international action to reduce release[s] ... is technically
possible, and if achieved, would be a valuable precautionary and
preventive measure both to slow climate warming and to protect
the ozone layer."
Building the international consensus necessary to phase out
CFC emissions will take time. In the short term, it is more
realistic to expect that participants in the Convention process
can agree to reduce global CFCs emissions by an amount roughly
equal to current use in aerosol sprays, or abou~ one third. The
United
adopting
and a
States could meet this target despite its aerosol ban by
the measures. This move would be a major stepforward
clear ·signal to industry to begin searching for
alternatives.
Individual actions by the U.S. and by other leading nations
may also be necessary, even if an international protocol is
adopted. Beyond the inherent difficulty of enacting
international agreement with meaningful restricti.ons,
any
the
Convention's effectiveness may also be compromised by the absence
(or delayed participation) of some countries and the likelihood
that not all ozone-depleting substances would be covered. Even
bringing CFC production down to one third below recent levels
an ambitious goal will not eliminate some significant
environmental risks and may not induce investment in new
chemicals, which will require considerable start-up capital and
assurances of large markets.
334
Should further U.S. action prove necessary, a tax should be
imposed on CFCs, phasd in over five years to assure producers of
a future price high enough to justify producing chemical
alternatives. This tax should be supported by import
restrictions to assure that domestic manufacturers do not suffer
competitive disadvantage.
It is very important to find out how marine and terrestrial
organisms respond to UV, and to assess their sensitivity. There
is a short food chain in Antarctica and if these organisms should
be wiped out, there may not be anything to replace them.
The Montreal Protocol on "substances that deplete the ozone
layer" was adopted on 16 September 1987 when it was signed by the
UK, the European Community and 23 other countries. It is due to
enter into force on 1 January 1989. The protocol provides for
the production and consumption of CFCs 11, 12, 113, 114 and 115
to be reduced by 50 per cent in three stages by 1999.
requires production and consumption of halons 1211,
2402 to be frozen.fr.om 1992.
It also
1301, and
Main points brought to light by Stratospheric Ozone Review
Group after research (Stratospheric Ozone, 1988), are In 1987,
the springtime depletion of ozone over Antarctica (the ozone
hole) was more severe, and lasted longer, than previously. At
altitudes between 14 km and 18 km the concentration of ozone was
depleted by over 95% on occasions, and the total column of ozone
was reduced to about 40% of its pre-1975 thickness.
335
There is now evidence of a year-round reduction of ozone of
about 5% since 1979, poleward of 60°s. This may be linked to the
springtime Antarctic ozone depletion.
A major reanalysis of global ozone data has been made by the
NASA/WMO Ozone Trends Panel. Goundbased measurements between 30N
and 64N indicate that, after allowance has been made for the
effect of solar and other cycles, the annual mean column ozone
decreased by 1.7 to 3% between 1969 and 1986. Within these
latitudes the depletion is greatest between 53 N and 64 N in
winter months, amounting to about 7%. 5
CONCLUSION
Thus we may say that apart from its unique natural features
which make Antarctica especially important as a scientific
laboratory, the global regulation of climate, and thereby, the
planet's natural balance at large - the southern Continent and
its surrounding ocean constitute one fragile ecosystem with
interdependent components, all of them in turn intimately related
to their physical components.
It is true that, apart from once nearly extermination marine
mammals in the Antarctic waters, man's impact upon the Antarctic,
at ecosystem level, has been minimal. Localized pollution caused
by scientific stations and tourists along coastal areas, has been
noted, however, and occasional cases of disturbing the fauna has
occurred. Serious concern is being voiced about the overall
repurcussion resulting from even an adverse impact of offshore
33C
drilling on even large scale alterations of continental geology,
has been predicted.
The major inadequacy of the Treaty-related framework for
environmental protection is that it fails legally to bind third
parties, omitting some potential users of the Antarctic living
resources, for example, South Korea. However, the legal analysis
demonstrates,
international
even ponparties are bound
law to refrain from inflicting
under general
environmental and
ecological damage upon Antarctica. This is a broad injunction
which must be further implemented in a forceful way, particularly
against third parties, i.e. erga omnes. One realistic way of
avoiding conflicts, of course, would be to widen adherence to all
relevant environmental agreements (list given), particularly of
the Antarctic regime, promoting precisely what the consultative
parties consider a "desirable international objective''. However,
making Antarctic Treaty System an 'Objective regime' binding to
even nation in a truly functional way, still remains 3 dream.
More and more popular consideration of Antarctica as CHM or
global
of N-S
binding
commons or extra-territorial region within the framework
Dialogue or NIEO, is of course, making the ATS less
to the third parties. Recent events in the UN intimate
that certain states in the Third World are interested in securing
more direct influence for developing countries in Antarctic
Affairs. It is still too early to predict with confidence either
the political impact of the legal significance of this movement.
Even where the national interests of the Treaty Powers itself
have conflicted with local ecological requirements, the former
337
have prevailed most of the time. In all these cases, it will be
only a matter of time before the Antarctic falls victim to man's
self serving rapacity and myoper avarice. Such a course of
events would indeed be regrettable and would stand as a tragic
commentary on the perverted "progress" of man's domination over
nature. Given the lessons of the past and incentives for the
future, it is still not too late to overt that eco-catastrophe.
Increased
organitations,
serious
mainly
involvement of
like International
non-governmental
Union for the
Conservation of Nature and Natural Resources (IUCN). Greenpeace
International and Antarctic and Southern Ocean Coalition (ASOC),
demanding for ''interactionlising" the Area" or "creating a world
Park'' or opening up the Antarctic system" still remains to be
seen as becoming a major motivating force for complete
conservation of Antarctica. In fact, their mixed demands and
unrealistic approach has come into their own way of fulfilling
their said five objectives of public accountability, non-
discrimination, international inequity, conservation and living
resource conservation.
Consideration of Antarctica as special conservation areas
and application of environmental impact assessment (EIA)
procedures to Antarctic science and ligistics, has stressed upon
the need for a more informative system about the activities
tabling place in ATC check on on-regulated tourist activities,
avoiding overcrowding or concentration of station activities.
338
NOTES
1. The Greenpeace book on Antarctica, Greenpeace International, UK, 1988.
2. B.A. Boczek, The Protection of the Antarctic Ecosytem: A Study in the International Environmental Law, Ocean Development and International Law, 13(3), pp.350-380.
3. John Gribbin, The Ozone Layer, New Scientist L, 5 May 1988, No.1611, pp.l-3.
4. S. Dayton, Canadians Confirm Ozone Hole in Arctic, New Scientist, 9 June, 1988, No.l616, pp.47-48.
5. A.S. Miller, and I.M. Mintzer, The Sky is the Limit: Strategies for Protecting the Ozone Layer, World Resources Institute, Research Reprint, 3, Nov.l986, pp.30.