How
Effective is Australian Policy?
The 1974 MOU recognises some form of
traditional fishing rights and attempts to regulate access for traditional
Indonesian fishermen in an area now under Australian control. However, in the
words of Fox (1998: 114), ‘numerous problems have arisen as a result of this
seemingly well-intended endeavour’ and led to a succession of ‘unintended
consequences’.
The MOU does not specifically identify who is
allowed access into the MOU area. Rather, access is open to any Indonesian
‘traditional’ fishermen as long as they comply with the regulations which
narrowly define ‘traditional’ methods and vessels. Access is not determined by
historically recognised use rights for specific groups who operated in the
region prior to Australian maritime expansion; any group of fishermen using a
sail-powered boat is allowed to fish in the region. By failing to identify the
specific groups who historically accessed the AFZ, the effectiveness and
original intention of the MOU has been undermined and its outcomes severely
attenuated.
The original purpose of excluding the use of
motorised vessels and methods in the face of increasing motorisation in the
small-scale perahu sector in Indonesia was to limit the
number of boats entering the area. This policy was designed to control the
level of resource exploitation and therefore function as a form of resource
management. The idea was that if the technology was unsophisticated or
‘primitive’ it could offer some protection for marine resources. But this
technological freeze has failed to achieve the desired outcome. By not
restricting the numbers of vessels or the amount of product taken, it opened
the area up to an unlimited number of fishermen in sail-powered vessels, of
which there is no shortage in eastern Indonesia, and this has resulted in
over-exploitation of resources in the MOU box area, particularly sedentary
species on reefs and inshore waters.
By not permitting the use of motorised
vessels in times of bad weather, the Government has also been accused of
enforcing a policy that subjects the fishermen to unnecessary risks (Campbell
and Wilson 1993; Fox 1998: 121). Over the last decade, a number of sailing
boats and their crews have been lost during cyclones in the MOU area. For
example, in April 1994, four Pepela-owned boats and their mostly Bajo crews
drowned during a cyclone in the Timor Sea. On the other hand, in periods of
little or no wind, or strong currents, when it is impossible to make any
headway in a sail-powered vessel, strong currents can easily drag a
sail-powered vessel beyond the permitted areas.
Legal fishing in the MOU box area can also be
seen as a gateway to illegal fishing (Fox 1998). The 1989 amendments that
created this area did not incorporate the most productive Bajo shark fishing
grounds. Apart from a few areas around reefs and islands and along the edges of
the MOU box, it is a relatively poor shark fishing ground (Wallner and
McLoughlin 1995a: 34). No motorised Type 3 perahu have
been apprehended for illegal shark fishing activity in this area.
Butonese and
Bajo fishermen from across eastern Indonesia who use motorised boats to target
shark prefer to concentrate their activities in the more productive waters to
the north and east of the MOU box (ibid.). Bajo fishermen often seek access to
these waters by passing through the MOU box, but in doing so they run the risk
of apprehension. Fishermen are forced to fish illegally outside the MOU box area
in an attempt to secure adequate returns. Illegal fishing and boat
apprehensions thus occur in direct response to the ineffectiveness of the MOU
itself.
Naturally, the borders of the MOU box area
cannot be marked or signposted. They only exist as lines on maps, unconnected
to any geographical features. Bajo navigation is based on reference to familiar
landmarks and sea features. Their sailing and fishing activities have, until
recently, never been confined to areas bounded by lines on maps. Even for the
most experienced navigators, it is difficult to determine exactly where the
boundaries of the MOU box are.
The MOU restricts access to fishermen using
‘traditional methods’ but expects the accuracy of modern navigation. Accurate
determination of latitude and longitude requires the use of marine charts and
sophisticated navigational equipment such as a Global Positioning System. Prior
to the early 1990s, fishermen found within an unspecified reasonable distance
of the permitted areas were generally warned but not apprehended. The tougher
approach adopted by AFMA in recent years has seen Bajo and other fishermen
apprehended as little as 5–8 nm outside the MOU box.
Fishermen who are denied
the use of motors and sophisticated equipment under the MOU are treated in the
same fashion as an industrial foreign fishing vessel worth millions of dollars
caught illegally fishing in the AFZ.
Neither the 1974 MOU nor the Plan of
Management for Ashmore Reef National Nature Reserve (ANPWS 1989) makes any
mention of this reef’s cultural heritage value.
At least eight Indonesian
graves have been identified on West Island and others on East and Middle islets
(ANPWS n.d.), and fishermen are officially prohibited from landing on the
islands to visit these sites. [5] However, formal requests by fishermen
are made to the caretaker to obtain permission to visit and maintain the
graves, perform ceremonies and present offerings, and the caretaker often
accompanies the fishermen on these visits (personal communication, Paul Clark,
1999).
Indonesian fishermen have played no role in
shaping the MOU itself. The agreement makes some attempt at recognising their
rights but they have not been invited or allowed to participate in its
formulation or implementation. They are not alone, for the interests of
maritime peoples are often ‘ignored, dismissed or marginalised’ (Schug 1996:
210) in the formulation of international maritime boundaries and agreements
designed to protect their livelihood.
The case of the indigenous people of the Torres Strait is one example: the
boundaries between Papua New Guinea and Australia established under the Torres Strait
Treaty were developed
‘without sufficient consultation with the people who would be affected most
directly by the political division’, and this has ‘created an unstable
situation which threatens to undermine intention the Treaty’s efforts to
provide for the protection of the Strait’s marine environment’ (ibid.: 222).
In
the case of the MOU, dialogue may be effective at a government-to-government
level but other stakeholders, such as Indonesian fishermen, are unable to
participate.
The Australian Aid Program
Included in the minutes of the meeting between
Australian and Indonesian government officials in April 1989 is a provision
which states that:
Indonesian and Australian officials agreed to
make arrangements for cooperation in developing alternative income projects in
Eastern Indonesia for traditional fishermen traditionally engaged in fishing
under the MOU. The Indonesian side indicated they might include mariculture and
nucleus fishing enterprise scheme (Perikanan Inti Rakyat or P.I.R.). Both sides
mutually decided to discuss the possibility of channelling Australian aid funds
to such projects with appropriate authorities in their respective countries.
The ‘nucleus fishing enterprise scheme’ is a
transmigration program in the fisheries sector which is used to shift the rural
and/or fishing population from densely populated areas to those islands where
population density is low. No Australian aid was subsequently directed to the
Bajo fishermen who operate in the AFZ, and it was not until the late 1990s that
any official Australian delegations visited the villages of Mola, Mantigola or
Pepela. The idea of direct engagement with fishermen and an understanding of
the issues from their point of view appeared to be completely alien to the
Australian authorities.
The educational and information tours
undertaken by Australian officials to eastern Indonesia in 1995
were in response to high levels of incursion into the AFZ in 1994. During the visits,
maps were distributed in an
effort to explain the complex
maritime jurisdictions existing between Australia and Indonesia in the Timor
and Arafura seas and the MOU
area.
These were accompanied by two handouts in Indonesian entitled Pesan
Permerintah Australia untuk Nelayan (‘Message for Fishermen from the
Australian Government’) and Pesan Pemerintah Australia untuk Pemilik Perahu/Kapal dan Otorita Pelabuhan (‘Message for Perahu/Boat Owners andHarbour Authorities from the Australian Government’).[6] The Australian authorities seem to
think that their maps are readily understood by Indonesian fishermen and that
they can help them to determine where they can and cannot fish. Fishermen with
maps certainly have no excuse if found outside of the permitted areas.
However,
some Bajo captains, especially those who were illiterate, found the maps highly
confusing and difficult, if not impossible, to comprehend.
During the course of their awareness-raising
tours, officials from the Australian Agency for International Development
(AusAID) did explore the opportunities for delivery of aid to poor isolated
fishing communities. As a result AusAID has implemented some small projects,
but these have not been directed to fishermen whose activities are covered by
the MOU, but to people from Sinjai in South Sulawesi who were apprehended in
large numbers in 1994–95 following a wave of illegal trepang fishing activity
in the northern part of the AFZ.
Some support from the Direct Assistance
Program of the Australian Ambassador to Indonesia was given to other fishing
communities, including Pepela, but the outcome was somewhat ironic. In one
instance the money was used to purchase a perahu lambo on
the understanding that the proceeds from fishing would be distributed among the
community, but the perahu (the
Bintang Pagi) was subsequently apprehended, confiscated and destroyed in
Darwin.
There is a serious inconsistency here.
Australia has a policy commitment to deliver aid to eastern Indonesian
fishermen operating under the terms of the MOU, yet retains a policy of
confiscating and destroying the sources of livelihood of these very same
people. In February 1995, an ABC journalist interviewed a representative from
the Australian Embassy in Jakarta and a senior officer from the WA Fisheries
Department who had just returned from the first educational tour of eastern
Indonesia.
The embassy representative explained that the Australian Government
was exploring opportunities for the delivery of aid for ‘isolated poor fishing
communities in eastern Indonesia … who need, for their livelihood, to gain
income to support their families and are ready and willing … to often engage in
some risky fishing activities south of the border’ (ABC Radio National 1995:
2). In the same interview, the fisheries officer discussed the effectiveness of
the deterrence policy:
From our experience … we’ve found the only
real deterrent is to continue prosecuting them and to take their boats off them
and just fly them home.… I think this is the only real way we can deter them is
to continually confiscate and burn their boats, so they lose all their boats and all their fishing equipment, and fly them
home back to Indonesia. And just continually do that (ibid.: 5).
As Fox (1998: 131) noted, it is an ‘outright
contradiction’ for the Australian Government to fund aid projects to alleviate
poverty in eastern Indonesia while burning vessels belonging to some of the
poorest inhabitants of the region.
The Record of Apprehensions
For over a decade, the policy of apprehension
and confiscation of boats, catch and equipment as a form of deterrent to
further illegal activity has been in place. Between 1988 and 1993, there was an
overall decline in the number of boat apprehensions, which gave the impression
that the policy of apprehension and confiscation was working.
However, there
was a dramatic increase over the course of the next four years, and this
included an increase in the apprehension of Type 2 perahu using longline gear (see Figure 8-1).
Of the total number of Indonesian boats apprehended between 1975 and 1997,
approximately 22 per cent or 134 boats were Type 2 vessels.
Figure
8-1: Total number of boat apprehensions and total number of Type 2 boat
apprehensions, 1975–97
The educational and information campaigns of
the 1990s seem to have introduced the AFZ to coastal peoples who may not have
previously been aware of the existence of the MOU and the permitted areas. The
campaigns themselves may therefore have contributed to larger numbers of boats
from eastern Indonesia beginning to engage in illegal activity. If we look at
the proportion of Bajo Type 2 perahu among
the total number of Type 2 perahu apprehended
in those years when there were any apprehensions of such vessels, we can see
that the proportion declined in those years when the total number of
apprehensions suddenly began to increase (Table 8-1). In 1996, when 49 Type 2 perahu were apprehended, only 18 of them were
Bajo perahu.
The present enforcement and prosecution
approach costs the Australian taxpayer millions of dollars each year. Expenses
include the costs of towing the vessels to Darwin or Broome, carrying out
immigration, quarantine and customs checks, maintaining crews and vessels until
the completion of court hearings, repatriation of fishermen and destruction of
forfeited boats. The costs incurred for each apprehension boat crew depend on
the length of time the fishermen are detained, and this in turn depends on the
prosecution process. [7] It is difficult to obtain official
government figures on these expenses because there is a reluctance to place
such information in the public domain and many different government departments
and agencies are involved in the process.
Table 8-1: Total number of Type 2 apprehensions and Bajo Type 2
apprehensions, 1975–97.
Year
|
Total
Type 2
|
Bajo
Type 2
|
1975
|
3
|
3
|
1980
|
2
|
0
|
1985
|
5
|
5
|
1988
|
3
|
0
|
1990
|
4
|
4
|
1991
|
5
|
5
|
1992
|
3
|
3
|
1993
|
9
|
0
|
1994
|
12
|
8
|
1995
|
8
|
1
|
1996
|
49
|
18
|
1997
|
31
|
15
|
Total
|
134
|
62
|
Source: AFMA Apprehension lists, Northern
Territory and Western Australia.
In its submission to the Joint Standing
Committee on Foreign Affairs, Defence and Trade (JSCFDAT) in 1991, AFMA
reported that the costs associated with the apprehension of Indonesian vessels
in 1989–90 was A$ 750 499 (Fox 1998: 132). A senior AFMA official has
stated that his organisation spent around A$ 3 500 000 on 124
foreign fishing apprehensions, of which 113 were Indonesian, in the financial
year 1997/98. This amount included the salaries of 15–20 fisheries officers on
AFZ patrolling duties and other fisheries support functions and the costs of
caretaking and security operations while fishermen are in detention.
In Darwin
the contracting caretakers receive about A$ 1000 a day from AFMA for each
vessel and crew in their care. This amount covers staff salaries and the cost
of providing food, medical treatment, and transport for the fishermen who have
been detained. Legal Aid lawyers say that the cost of legal representation for
the fishermen is also around A$ 1000 a day.
From Darwin, fishermen are
normally repatriated to Kupang on a Merpati flight. A one-way ticket costs A$ 244–319
depending on the time of year. Repatriation from Broome is more expensive. For
those few fishermen who are able to pay security bonds and return to Indonesia
in their boats, the Australian authorities incur several thousand dollars in
additional costs by towing the vessels to the international border.
The effectiveness of the policy of
apprehension in deterring illegal activity was questioned by the JSCFDAT in
1993. The committee concluded that was a drop in the price of trochus shell,
and not surveillance and enforcement, that had caused a decline in illegal
trochus harvesting in the AFZ in the early 1990s. The committee also considered
that similar enforcement and prosecution approaches were ‘unlikely to be
effective’ against illegal shark fishing while the price of shark fin remained
high (JSCFDAT 1993: 129).
ILLEGAL SHARK
FISHING DEVASTATES POPULATIONS IN NORTHERN AUSTRALIA
The MoU BOX
Indonesian fishermen have visited the coasts and
offshore reefs of northern Australia for centuries, targeting shark fin,
trepang (sea cucumber) and trochus shell. In recognition of this long-standing
practice, the Australian and Indonesian governments negotiated a memorandum of
understanding (MoU 74) which allows Indonesian fishermen to access 50 000 km2 within
the Australian Exclusive Economic Zone (EEZ). Within this area (called the MoU
Box) are six coral reef systems, the northern most of which are Ashmore and
Cartier Reefs.
Indonesian fisherman can legally access the
resources within the MoU box.
While there has been concern over the status of reef
resources in the MoU Box for some time, the condition of shark stocks remains
largely unknown. Until recently the most common method of counting mobile
marine organisms like sharks and fishes was the underwater visual census (UVC)
method, a technique that relies on diver observation and thus restricts the
census to relatively shallow waters (usually <20 m depth) for short periods
of time.
In order to achieve more accurate census by including
sharks in deep water habitats, AIMS uses of a fleet of baited remote underwater
video stations (BRUVS) which can be deployed in water as deep as 100m. Using
this technique, it is possible to obtain accurate and reliable estimates of the
type, number and size of sharks.
In 2003 and 2005, AIMS used BRUVS to survey abundances
of sharks at reefs within the MoU Box and at the Rowley Shoals to the south
west. The Rowley Shoals reefs are closed to all types of fishing that target
sharks.
Surveys by BRUVS showed a striking difference in the abundance and
species richness of sharks between the fished and unfished reefs. When
corrected for sampling effort, sharks were on average from 4 to 17 times more
abundant at the Rowley Shoals than at most reefs within the MoU Box. Analysis
of BRUVS tapes also showed that it took twice as long (up to 50 min more) for
sharks to appear at reefs in the MoU Box compared to protected reefs.
While there are signs that some shark species may be
recovering at reefs that were once in the MoU Box but are now protected from
fishing, there is no evidence of recovery for sharks that are particularly
valuable in the fin trade, such as silvertip reef sharks (Carcharhinus
albimarginatus), the tiger shark (Galeocerdo cuvier), or hammerhead
sharks (Sphyrna lewini and S. mokarran) despite almost
20 years of protection.
The demise of shark stocks in areas open to Indonesian
fishing within the EEZ, coupled with an increasing demand for shark fin may
account for the major problem of illegal shark fishing on the reefs surrounding
the MoU Box and throughout northern Australia. Recent studies of shoals and
banks beyond the MoU Box (Sahul and Kharmt Shoals) show that the patterns of
shark depletion are being repeated and may be driving illegal fishers further
towards the coast of mainland Australia and into the Gulf of Carpentaria.
STATE-OF-THE-ART
AIRBORNE IMAGING PRODUCES THE FIRST DIGITAL MAP OF NINGALOO MARINE PARK
Scientists
from AIMS are using new state-of-the-art aerial imaging to produce the world’s
most detailed digital map of a coral reef. More than 3400 km2 of the pristine Ningaloo Marine Park
was surveyed in a collaborative initiative funded by BHP Billiton. The aerial
images will be digitally processed and converted into maps that indicate the
location of different habitat types in the marine park. These maps will be
useful in guiding future research projects and management initiatives in the
region.
This project builds on the
Western Australian Marine Science Institution (WAMSI) programme to improve
understanding of the marine resources of Ningaloo. AIMS lead scientist in WA,
Dr Andrew Heyward, said the programme’s first success, the hyperspectral
survey, will provide enormous benefits for future scientific studies.
"Surveys of this calibre are quite expensive and beyond the fiscal
capacity of current research programmes. The BHP Billiton-AIMS effort has lead
to the largest aerial survey of its kind, providing collaborating scientists in
Western Australia with an opportunity to take a world lead in using this type
of data for coral reef understanding and management."
A BIRD'S EYE VIEW OF THE REEF
Scientists from AIMS are using new state-of-the art
aerial imaging to view the reef in a new light. Digital images have been
collected for more than 3400 km2 of the pristine Ningaloo
Marine Park to produce the world’s largest and most detailed digital map of a
coral reef.
Using the latest technology, hyperspectral aerial
photographs (left) are digitally processed to separate spectral signatures
(right) which indicate a variety of marine habitats.
Photo: Hy Vista
The technology, called hyperspectral imaging uses a
highly specialised ‘super camera’ or spectrometer mounted to an aircraft to
collect images of the land and sea below. Similar to a bird’s eye, which can
detect UV and infrared light, the spectrometer captures 720 more wavelengths
than the human eye can see and has a spatial resolution of 3.5 m (from an
altitude of 1400 m).
Different substrate and habitat types reflect light
differently, each giving off a unique photo-signature or spectral
‘fingerprint’. Sand, for example, is highly reflective, while the deep waters
of Ningaloo absorb light. Chlorophyll containing plants and algae have
distinctive colour signatures which can indicate areas of high primary
productivity (of interest to marine managers).
By analysing the images,
scientists can pinpoint areas dominated by different types of corals and can
even identify important oceanographic information such as surface waves.
AIMS scientist and project leader Dr Andrew Heyward
explained that the images collect more information than our eyes can see and
that even habitats below the surface of the water can be identified from the
data.
"The hyperspectral data contains far more
information than normal colour photographs and is fully digital, permitting
various combinations of spectral signal to be combined or contrasted.
This
enables us to distinguish features not apparent to the naked eye, using
computer processing. We take a geographic position on the image and match the
colour to the information gathered at the same location underwater to establish
the meaning of the colour."
While the aircraft works the aerial perspective, AIMS
scientists are busy sampling the seafloor. Information collected from
biological surveys including dive expeditions and investigations of deeper
waters where researchers use video; sled sampling; and acoustic echo sounders,
is cross referenced to the aerial images. Dr Heyward expects the technology to
provide a strategy for rapidly identifying habitat types in areas that haven’t
yet been physically surveyed.
"If one image depicts a substantial area of pink
and purple which we know is an area dense with table corals, where we see these
shades elsewhere along the vast tract of the reef, we can assume there are
table corals in that region."
The spectral image can also be used to measure water
depth and to quantify issues such as sedimentation and run-off, providing
scientists with a unique ability to monitor the marine park over time.
The data
collected for Ningaloo will provide a benchmark assessment of the area against
which future changes can be measured.
The next step of the project will involve further
processing of the images by researchers from Murdoch and Curtin Universities
and the production of detailed maps. Creating the maps will be no small feat as
each image has 125 bands or channels, each channel records light in 1024 levels
(or shades from black (0) to white (1023)) so the total amount of information
possible for any one point (or pixel) is 1024125.
The images contain
so much information that a specialised computer costing $200 000 is required to
process them into maps.
The Minister for Education, Science and Training, the
Hon Julie Bishop MP, said that programmes such as these demonstrate how
effectively industry, the research sector and the general community can work
together, capturing new knowledge to secure our natural heritage into the
future.
FISH SURVEYS
DEMONSTRATE BENEFIT OF NEW REEF ZONING PLAN
After more than a decade of surveys on the Great Barrier Reef an
AIMS Long-term Monitoring study indicates that the number and size of fishes in
‘no-take’ green zones has nearly doubled in less than two years. This result is
exciting news for managers and fishermen alike as the increasing numbers of
adult fishes in protected areas are expected to yield offspring which will
replenish populations of commercially important fish species on the reef.
GREENHOUSE
GASSES ARE TURNING THE OCEANS ACIDIC
Rising levels of greenhouse
gases in the atmosphere (mostly CO2), responsible for global
warming, are also changing the acidity of oceanic waters. Researchers from AIMS
and the Australian National University have obtained new historical insights
into changes in ocean acidity using geochemical information stored in coral
skeletons. If current CO2 emission
rates are sustained, corals could be in hot water within the next few decades.
CORAL GIVES NEW INSIGHT INTO CHANGING OCEAN ACIDITY
Since
the beginning of the industrial revolution, greenhouse gasses in the atmosphere
(mainly CO2) have increased by approximately 40%, rising rapidly to
a level unprecedented in the last 420000 years. About 30% of the excess CO2,
which is also responsible for global warming, has been absorbed by the world’s
oceans. Our seas, however, are approaching their maximum capacity for
absorption of CO2 and
they are becoming more acidic then they have been in hundreds of thousands of
years.
Massive corals found throughout Australia's tropical waters, act
like living libraries with with coral samples providing historical information
on weather patterns, water quality and oceanic conditions of the past. Photo: E. Matson
Although
the full consequences of increasing ocean acidity are not well
understood, marine scientists are particularly concerned about the
potential effect on corals, which provide habitat and food for countless
tropical species. Increased ocean acidity is likely to reduce the ability of
many marine calcifying organisms, including reef-building corals, to produce
their skeletons.
Researchers
from AIMS and the Australian National University are looking backwards in time
to understand how historical changes in ocean acidity have affected coral
growth.
The
scientists analysed a core sample from a 300-year-old massive coral on Flinders
Reef in the western Coral Sea. The coral’s growth rings were sampled in
five-year increments and levels of boron isotopes (which indicate acidity) were
measured along with coral calcification (or growth) rates.
Their
results, published in the journal Science, showed that ocean acidity at
Flinders Reef rose and fell approximately every 55 years coinciding with
periodic fluctuations in global climate.
The
relatively large variations in seawater acidity detected at Flinders Reef,
suggest that in the past, corals may have been resilient to the shorter term
effects of ocean acidification on reefs. However, in the coming decades many
reefs are likely to experience unnaturally acidic conditions.
Analysis
of boron isotopes in corals is providing improved understanding of past
responses of coral reefs to increased acidity.
Historical information is
urgently needed to better understand how coral reefs will respond to the
continued acidification of the world's oceans. If current acidification rates
are maintained, scientists warn that corals could be in a state of emergency
within the next few decades - particularly given other threats to reefs such as
coral bleaching, declining water quality and overfishing.
Penulis :
Drs.Simon Arnold Julian Jacob
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