5.1.3 Generic
management options
To assist in determining
what type of actions need to be taken in
managing activities which may affect the
bottlenose dolphins, a series of broad
management responses has been drawn up
and agreed by the sites relevant authorities.
These are shown in Table
7. below.
Following consultation
of the draft management plan the sites
relevant authorities agreed the following
general approach that they would take when
considering what changes, if any, to existing
management of activities is required.
Where there is a lack
of information about existing activities
(i.e. there is insufficient information
to determine whether or not they are adversely
impacting the bottlenose dolphins) then
there should be some investigation (research)
for possible impacts. In the absence of
evidence one way or the other, it should
not be assumed that the conservation of
the dolphin population is compatible with
current site use. However, the pattern
of existing use has to be recognised. Therefore,
the existing level of the activity should
be maintained (as far as is possible) at
current levels or less (i.e. not increased)
until there is some conclusion as to what
levels are acceptable.
An increase in intensity
of a current activity, significant change
in distribution of a current activity or
the development of a new activity should
be treated as or in a way analogous to
that for a plan or project. i.e. the increase
or change should not be viewed as acceptable
until it has been shown that it will not
adversely affect site integrity.
Surveillance and / or
monitoring of activities is required for
activities that are known to adversely
affect the bottlenose dolphins or for which
there is uncertainty but a mechanism for
effect is known. This will allow some early
warning of potential increases in activity
and provide a baseline of information if
there is ever a need to investigate the
cause of a loss of favourable condition.
It was appreciated that
the degree to which each relevant authority
could conduct surveillance or monitoring
would vary, being influenced by available
resources and the scope of the activity.
The degree to which existing statutory
and institutional arrangements enabled
activities to be “maintained at current
levels” would also vary. This was
particularly noted as being the case for
fisheries and also various recreational
activities not subject to formal management
or regulation.
Where a management response
requires some form of action this is given
in section
5.2 or section
5.3 after the rationale for each factor.
A summary of all actions, comprising all
of the actions generated in section 5 is
provided in section
6.
For most factors there
is considerable uncertainty as to whether
they are, or are not, having an effect
on the bottlenose dolphins. Showing irrefutably
that an activity is adversely affecting
the bottlenose dolphins is very difficult
indeed; the low level of knowledge, scientific
capabilities and available resources all
conspire to hinder this. Even where there
is some information - for example through
examination of the few bottlenose dolphin
strandings suitable for autopsy - it is
very difficult to determine the factors
contributing to a dolphin’s death.
A high parasite burden may, for example
be as a result of natural causes, anthropogenic
causes such as pollution induced immunosuppression,
or a combination of both.
It
is essential that the ‘precautionary
principle’ [103]
is followed on behalf of the dolphins,
to take actions early enough to minimise
potentially serious or irreversible effects.
Management decisions will need to take
into account reasonable predictions of
likely affects of human activities on the
animals, despite a paucity of supporting
scientific evidence
Table
7. Generic
Management Options
Code |
Judgement |
Management |
F1 |
The
activity constitutes a plan or project. |
· Apply Habitats
Regulations 48-53. |
F2 |
There
is no known mechanism for the activity
to affect the feature, and no evidence
that it is having a significant adverse
effect. |
· Not considered further at present. |
F3 |
There
is no known mechanism for the activity
to affect the feature, but there
is evidence that it is having a significant
adverse effect. |
· Research
· Activity surveillance
· Experimental or trial management
· Identify and implement operational
limits. |
F4 |
There
is a known mechanism for the activity
to have an effect, but there is insufficient
evidence at present to determine
whether or not it is having a significant
adverse effect. |
· Activity surveillance.
· Precautionary management including
use of operational limits.
· Research to determine whether
there is an effect or not and
inform operational limit setting. |
F5 |
There
is a known mechanism for the activity
to have an effect, but evidence shows
that it is not having a significant
adverse effect at present. |
· Activity surveillance.
· Identify and implement operational
limits. |
F6 |
There
is evidence to suggest that an activity
is having a significant effect on
the feature, but it is outside management
control (i.e. natural process, or
there is no current mechanism for
management) |
· Activity/factor surveillance.
· If necessary, seek appropriate
management mechanism, then implement
appropriate management. |
F7 |
There
is evidence to suggest that an activity
is having a significant adverse effect
and the mechanism is known. |
· Identify and implement management
measures.
· Identify and implement operational
limits. |
[103]
Precautionary Principle: Even if
it has not been demonstrated, but an activity
is considered likely to have
a significant impact on the feature, appropriate
actions should be taken to manage that
activity to prevent the impact. (This
is just one of many differing definitions
of the Precautionary Principle.
Whilst most of the sites relevant
authorities sign up to this definition
it should not be taken that all relevant
and competent authorities relevant to Cardigan
Bay cSAC site management would also.) |