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Notwithstanding
these laudable statements, there are significant concerns
about implementing these actions. For example: the permissible
harvesting in wilderness areas, the inadequate zoning
of sensitive reefs and the number of poorly protected
sites of special sensitivity, value and interest within
the Park that require special protection (such as Black
Rock, Island Rock and certain reefs, etc.).
Conclusion
In conclusion we are very disappointed with the IMP
and suggest that it be rejected until such time that
a more inclusive and substantiated document can be compiled.
South Africa, and especially KwaZulu-Natal, has excellent
capacity and skill available to develop a much more
credible IMP. The fact that this opportunity for developing
a more inclusive and transparent process was not undertaken
is of little credit to the Authority and signals a potential
waste of scientific resources that have seen millions
of Rand invested in studies of the iSimangaliso Wetland
Park over the years.
We
thus suggest that the following issues are addressed
as a priority:
a)
Clarify the legal standing and relationship between
all legislation that pertains to the iSimangaliso Wetland
Park area. This to be done as an exercise that involves
the key stakeholders so as to ensure eventual wider
acceptance and improved collaboration in the future.
b)
The development of a factual status report on the Park,
with specific reference to the status of biodiversity,
ecological function and status, resources and visitor
numbers. Such a report to be substantiated by drawing
on the available literature and expertise.
DETAILED
COMMENTS
Pg
14
We strongly question both the validity and the wisdom
of section 1.2.5. EKZNW does have a Province-wide
mandate and should not be relegated to a junior partner
or service provider in terms of a (possibly weak) management
agreement. The Park is part of the Province of KZN and
should remain as such. This confusion over who is in
fact the responsible authority lies at the heart of
several issues, including research.
Pg
29
The description of the responses of the lake to salinity
fluctuations is misleading. It is a combination of evaporation
and low freshwater input that result in hypersaline
conditions which overall, do not 'impose a high
degree of biodiversity, both in time and space'. At
such times the system is impoverished and this further
highlights the importance of considering the SA Water
Act that stipulates a freshwater reserve to ameliorate
such circumstances that ultimately have a direct effect
on fisheries.
Pg
32
The 2nd last line refers to use of traditional fishing
methods in Kosi - but non-traditional fishing methods
(gill nets, fishing rods) are also used and these must
be acknowledged as significant.
There
is no mention of invertebrates (prawns and swimming
crabs in particular) which use St Lucia as a nursery
and underpin offshore resources.
No
mention is made of the critical and national importance
of St Lucia and Kosi estuaries as nurseries. This not
only relates to their large surface areas relative to
the majority of estuaries in the country, but also to
the degraded and ecological compromised state of other
KZN nurseries. It has been stated in the primary literature
for over 50 years that estuaries are not only important
connections between fresh and marine waters, but also
they are primarily important as nursery areas and migratory
conduits for fauna with obligatory marine or freshwater
phases.
Page
36/37
Certain statements pertaining to fauna found within
the Park are sweeping and some are clearly incorrect.
The
fish section is weak and lacks references and thus credibility.
The focus on brindle bass is inappropriate, especially
as it is not endemic. A species that is not endemic
but in critical and near-extinct status is the sawfish,
once common in St Lucia. It deserves the special attention
in the IMP context.
Pg
59
We dispute the commercial fish off-take of 14 000t p.a.
There are no commercial permits there in the first place
and there is no reference there to back up this statement.
The Lake previously was subjected to an annual 56t recreational
off-take and max 300t from illegal netting (Mann, 1995;
Mann et al 2002).
Pg
64
This section carries a suite of alleged constraints
mainly attributed to EKZNW. We feel this is a most unfortunate
section of the IMP and suggest that it is removed or
significantly altered and better substantiated.
We
cannot possibly agree that "there is little product
differentiation in and around iSimangaliso". A simple
Google search proves otherwise and indicates that the
opportunities offered for tourism are impressive - much
better than many other destinations in South Africa.
We
question the validity of the statement that "recent
major road development" has overcome visitor access
problems. Proper data needs to be provided. Similarly,
a number of other unsubstantiated and "hearsay" claims
are made, concerning crime, medical services, branding,
etc. Malaria is seen as a past impediment, but no data
is provided and it is noted that many African countries
continue to draw good tourist numbers despite prevailing
malaria.
We
find paragraph 3.3.3.2 outrageous. EKZNW operated as
most other South African nature conservation bodies
have done, and mostly as SANPARKS still does in Kruger
National Park. To apportion blame and call it a "state
monopoly" is disingenuous, counterproductive and we
believe insulting to those who made great efforts to
promote tourism. We challenge the Authority to provide
reliable visitor numbers over the past 15 years to validate
the assumptions made. Our records show that for a period
in the 1990s, Sodwana and other resorts attracted enormous
visitor numbers to the extent that it cross-subsidised
other KZN Parks. It is politely pointed out that since
that time the Authority has been the responsible agency
- so any poor performance may be a constraint directly
attributable to the Authority itself.
We
acknowledge that there are other factors that may have
retarded visitor flow to the iSimangaliso Wetland Park,
such as competition with Mozambique, affordable cruises,
other destinations and of course the drought. Has any
in-depth analysis been undertaken over the past eight
years?
Pg
76
We
question the use of the term "optimal" in Management
Goal 2 - if this is not linked to ecological sustainability.
Pg
83
The IMP states in Strategic Driver 2 that the Authority
will set its own conservation policy. We question the
expertise and multi-disciplinary support for this.
Pg
86
Conservation Operation Plan cost/hectare. This is a
narrow definition and cannot be applied to the marine
environment. Monitoring must be stressed.
Pg
89
The intention is to only "manage" currently unauthorized
developments (by 2010) - these developments should not
be "managed", they should be removed now. This intended
approach proves that the authority does not assist EKZNW's
initiatives to prevent illegal activities (including
stopping of gill-netting in Kosi).
Why
develop new (and potentially conflicting) policies and
regulations when the MLRA and its regulations are already
place?
There
is scant reference to NGOs in resource management (2.8.3)
- despite the fact that NGOs have often provided the
primary source of data and advice. This is contrary
to co-management and transparency.
Pg
99
We strongly question the statement: "the Authority is
committed to open engagement with stakeholders both
proactively and reactively". The supposed interaction
with research stakeholders has been exceptionally poor
to date. How does the Authority intend to improve on
this? (also see pg 156).
Pg
101
We would insert point 5.6.4 to deal with monitoring
and research relationships - which have to date been
exceedingly poor.
Pg
104
Why initiate (duplicate) a new environmental education
programme when EKZNW in collaboration with MCEN already
exists and can be a source of support, collaboration
and even funding. How will the effectiveness of the
education programme be measured?
Pg
106
Strategic drivers are a useful concept. However, we
would argue that these need to be prioritised and that
Strategic Driver 7 should be ranked as Number 1, in
terms of management goals presented in Section 4.4.
Research
priorities are to be "set by the authority". Is this
done unilaterally in isolation? Will there be capacity
to do this? Experience over the past eight years calls
this into doubt and there is no evidence provided of
the Authority's capabilities/capacity in this regard.
The
last paragraph refers. We recognise that the Authority
needs to monitor its own achievements. However, monitoring
should be much wider-based and seen in the context of
other monitoring activities already in place. The Marine
Park is not a system in isolation, but shared with other
parts of South Africa.
There
should be fora for feedback and mechanisms for deliberating
the results on a wider scale. Remember that the Park
is equally dependent on (marine) resources elsewhere
in the region, so isolation will not be beneficial.
Pg
114 - 117
We do not support any form of harvesting in Pristine
Wilderness areas as this runs contrary to everything
else in the wilderness definition. The distinction between
restricted and controlled in terms of activities is
not clear.
Pg
124 + 126
"Pelagic" species is ambiguous and a non-scientific
term - it needs to be defined and species listed as
it can have huge implications for fishers. The proposed
regulations are not workable.
Pg
154
It would have been useful if ORI had been given an opportunity
to deliberate on some of the proposed measures and to
have sight of the underlying rationale. For example,
swimming, etc. in wilderness areas may be totally inappropriate
- especially over New Year.
Pg
158
2nd para. - It is bizarre that the communities are considered
a resource - humans are the prime users of resources.
Pg
160
We strongly oppose the notion that the Authority can
conduct its own internal scoping process as indicated.
There must be an independent body with oversight authority.
The Authority cannot be the judge and the jury at the
same time.
SPECIFIC
ISSUES
Launch
sites at nearly every point
Quite regardless of the fact that few points along the
coastline are graded and officially registered as launch
sites, nearly every point in the north is designated
as a public or concession launch site. This flies in
the face of the preservation of "sense of place" that
is considered desirable in the Park, and ignores the
safety aspects of sites already deemed dangerous by
official launch site committees. It is also in contrast
to the more precautionary approach adopted elsewhere
in KZN.
Research
The experience of ORI and other researchers in KZN is
that the Authority does not encourage research or provide
conducive research support. ORI has been waiting on
the Authority for many years to have an MOU and research
agreement confirmed. While we recognise that scientific
work needs to be managed and co-ordinated the "highly
regulated research permits", excessive rules and controls
over research projects, effective demands for the intellectual
property rights and the total hand over of all raw data
are seriously restrictive. Properly accredited research
institutions should be encouraged to work in the iSimangaliso
Wetland Park, rather than having to resort to working
in other regions and countries. Some, such as ORI, have
generated several million Rand of external funding to
support essential research in the Park. Research in
the Park should be encouraged - not spurned.
Measurable
outcomes and standards
There is a growing international thrust for management
effectiveness of Marine Protected Areas (MPAs). This
development is especially driven by the IUCN and South
African contributions have been included. The Durban
Accord, WSSD and other international agreements all
recognise this need. Modern ISO standards are currently
being developed and proposed for implementation in MPAs.
We feel that the IMP does not address this issue. While
"monitoring" is mentioned in several places, there are
no targets, optimal standards and thresholds provided.
From a marine, (we presume also terrestrial) biodiversity
and resource point of view this is not acceptable. We
see this as an inherent weakness in the IMP, especially
as there is adequate capacity in KZN and South Africa
to develop such standards.
Bio-prospecting
The proposed policy of isolation of the Park in terms
of bio-prospecting is short-sighted and may well deny
the Park, the people of South Africa and possibly the
world from potential benefits of natural products in
its resources. Geographic variation in natural product
generation would necessitate the study of organisms
distributed both in the Park and adjacent regions.
Zonation
We consider that overall zonation could be better structured
(pg 112) so that the main two divisions are terrestrial
and aquatic, the latter subdivided into freshwater and
marine components.
A
wealth of information regarding the need for reef zonation
is available in the literature (see reference list below),
and has been presented at symposia and was communicated
to the designated conservation authority of the park.
This outlines the need for further marine sanctuary
areas to meet the biodiversity targets of the Park.
All of this has been totally ignored in the IMP.
As
an example, the offshore sanctuary area in the northern
complex has been located at the N30 Beacon where it
provides no protection to Kosi Reef. The entire reef
lies to the south and the location of a sanctuary to
the north of N30 is totally meaningless. Some of the
most damage-sensitive coral communities in southern
Africa are found on Kosi Reef and will thus go unprotected.
Similarly, unique communities on the southern reaches
of Mbibi Reef, on Five-mile Reef and on Nine-mile Reef
will not be afforded protection in terms of the biodiversity
targets of the IsiMangaliso Wetland Park. The Wright
Canyon may justify incorporation in a 5-Mile Reef Sanctuary
to provide better protection for the coelacanths. It
is essential that these issues be rectified.
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