The impacts of shoreline species collection
Introduction
Three quick reference
summary tables introduce this section. The first
two outline the potential causes of impact or conflict
with nature conservation interests and other coastal
users arising from intertidal species collection,
and the potential for mitigation of these effects.
The third illustrates the potential severity of
the impacts or conflicts caused by various methods
of shoreline species collection on a range of environmental
features and the activities of other user groups.
The summaries presented in these
tables have been drawn from a detailed review of
the impacts of the collection of shoreline species
presented in the following pages. These describe
the impacts of the most widespread collection methods
for common shoreline species on the target species,
non-target species, intertidal habitats, and other
shoreline users; present opportunities for mitigation,
and highlight shortfalls in knowledge. A tabulated
literature review (see Appendix)
provides details of relevant publications and other
sources of information, and brief summaries of their
contents.
There is a tendency for published
research and unpublished reports on the impacts
of bait collection activity to report significant
detrimental effects. The reasons for this are that
studies reviewing the impacts of bait collection
are usually only commissioned in locations where
a problem had been identified, possibly
with an aim to determining whether management was
required to mitigate the effect. Such studies are
most unlikely to be undertaken in locations where
there is no perception of damage being caused by
bait collection. Similarly, research is usually
published when it has identified significant
(in the statistical sense) results during analysis
of field data. Readers should, therefore, note that
there is much less published information on studies
that have shown no significant effects on wildlife
caused by bait digging.
Several of the issues identified
and mitigation possibilities suggested in the Tables
A and B may
potentially result in the management of intertidal
species collection. Management options available
range from the promotion of voluntary codes of conduct
or bag limits, to permits and licensing systems,
zonation of activities, or complete closure of areas
to collection. These are summarised in Table C.
Scale of bait collection activity
Availability of bait supplies
Hand digging
Bait pumping
Hand picking
Provision of crab shelters
Bait dragging
Worm dredging
References
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