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Berwickshire and North Northumberland
Coast candidate SAC, England
Budle Bay, Lindisfarne National Nature
Reserve, Northumberland
Boulmer Haven, Northumberland
Newton Haven, Northumberland
Collection of intertidal animals
takes place from both sediment and rocky shores
on the Berwickshire and North Northumberland Coast.
Bait digging in the area, mainly for lugworms, has
been the subject of extensive study and legal regulation
in the Lindisfarne National Nature Reserve and Boulmer
Haven. Additionally, virtually every accessible
intertidal reef is exploited by commercial and recreational
users who collect winkles, mussels and crabs by
hand.
There are some important case studies
on bait digging within this cSAC.
Budle Bay, Lindisfarne National
Nature Reserve, Northumberland.
Bait digging has been carried out
in the Lindisfarne National Nature Reserve (NNR)
since at least the 1960s, and probably much earlier.
This activity is concentrated in the winter months
which is the period of greatest demand for lugworm
as angling bait. In the late 1970s, concern was
voiced over the impact on bird populations of the
rising numbers of bait diggers operating both by
day and by night in Budle Bay, the sanctuary area
of the NNR. The Nature Conservancy Council proposed
banning bait digging in the area except by permit
for local fishermen with effect from October 1978.
The ban was deferred pending discussions with the
National Anglers Council and Northern Federation
of Sea Anglers Society (NFSAS), but it became apparent
that action was needed when local landowners complained
of crop damage by geese displaced from the Bay and
a lessor of part of the NNR threatened not to renew
his lease.
A compromise agreement was reached
with angling groups in the region to close Budle
Bay to bait digging for two years, from September
1982 to September 1984. Meanwhile, bait digging
would be permitted on Fenham Flats, on either side
of the main Lindisfarne Causeway. The effect of
the agreement on lugworm stocks and bird numbers
would be monitored throughout this period, and if
bait stocks on Fenham Flats were found to be inferior,
part of the Bay would be reopened for a two year
trial period. During the initial period of closure,
bird numbers increased in the Bay.
Because lugworm densities and worm
sizes were significantly lower on the Flats, and
this area also a longer journey for most anglers,
an experimental bait digging zone in Budle Bay was
reopened to bait digging in September 1984, with
support from the NFSAS. The initiation of the experiment
not only coincided with the autumn/winter season
of peak demand for bait and lowest natural population
density of lugworm, but also with a coal miners
strike during the first 6 months of the trial. The
result was high levels of commercial bait digging,
as well as collection by anglers visiting the area
from as far as 30-100 miles away. Intensive bait
digging (by up to 120 persons at one time) took
place, removing virtually all lugworm from the experimental
area within about eight weeks from reintroduction
of bait digging. Some 25% of bait diggers present
in January 1985 (and 50% of those in January 1987,
well after the miners strike) were observed
digging outside the agreed zone. Other infringements
of the agreement included a lack of backfilling
and use of artificial lights. Bird numbers using
the Bay also fell significantly, mainly because
of disturbance caused by the presence of bait diggers,
excluding the birds from feeding grounds, rather
than because of the effects of digging on their
infaunal prey items (the areas of mudflat favoured
by feeding birds coincide with those favoured by
bait diggers). Unanticipated impacts of bait digging
at this site included damage to commercial mussel
beds operated under licence in the Bay and the mobilisation
of heavy metals (lead and cadmium) in the deep sediment,
which were then taken up by burrowing invertebrates.
The experiment clearly demonstrated
that bait digging activity was incompatible with
the aims of the sanctuary area and Budle Bay was
closed again to bait digging from September 1987.
This was effected under the NNR byelaws, made in
1968, which prohibit various acts except as authorised
by permit, including molesting or wilfully
disturbing, injuring or killing any living creature,
and was largely effective. Despite the virtual depletion
of dug areas, lugworm numbers recovered very rapidly
after bait digging ceased at the site, as a result
of immigration of adults from adjacent unexploited
sites. Bird numbers using the area after the second
closure also rose considerably.
The 1992 judgement in Anderson
v. Alnwick District Council, that bait digging for
personal use was ancillary to the right to fish
(see below), nullified the NNR byelaw 2(1)(a) as
regards bait digging for personal use, and identified
problems with the seaward extent of the NNR byelaws.
It resulted in an upsurge of digging during the
late summer and autumn of 1993. English Nature initially
considered simply amending the byelaws to take account
of this judgement, but because this would take some
time, issued a Nature Conservation Order (NCO) in
October 1993 to restore control over baitdigging
in Budle Bay immediately. The NCO was seen to be
largely effective after a few weeks. The NCO and
the proposed amendment to the Lindisfarne NNR byelaws
were opposed by representatives of four sea angling
federations, and a Public Inquiry held in March
1994. The Inspector, however, upheld the Nature
Conservation Order and modifications suggested by
English Nature, which included defining the Orders
seaward extent to a vertical depth of 6m m
below the low water mark, and broadening the restriction
to include "removal of fauna for use of bait
whether by digging or by any means" (thus covering
the use of, e.g. bait pumps - and incidentally peeler
crabs) (Langton 1994).
Because the worm stocks at Fenham
Flats, to which baitdiggers were provided open access,
are not as good a source of bait as Budle Bay (although
possibly adequate for personal bait, if not for
commercial collection), and were further to the
north, on occasions that Budle Bay has been closed
to bait digging (particularly in 1982 and 1985),
some bait digging activity has been redirected to
other southern locations. Notable among these were
Boulmer Haven and Newton Haven (see below), where
bait digging had not previously been such a problem.
This redirection of bait collection activity to
other sites in the area (up to or exceeding a distance
of 100 miles away) is likely to take place whenever
restrictions are imposed at a favoured site. This
case study also demonstrates the major limitation
of voluntary agreements with user groups - not all
individuals undertaking bait collection activity
are members of these groups and/or willing to for
their activities to be restricted in this way.
Boulmer Haven,
Northumberland
Bait digging in Boulmer Haven has
been a source of concern to local fishermen launching
their cobles across the beach for many years. The
holes and rocks left on the shore by bait diggers
make launching difficult, and are potentially damaging
to boats and tractors. For this reason, the Northumberland
Estates (owners of the foreshore) placed notices
prohibiting bait digging in the launching area,
but permitted bait digging anywhere else on foreshore
owned by the Duke of Northumberland. An upsurge
in digging activity occurred when the Budle Bay
bird sanctuary area was closed to bait diggers in
1982 and again in the winter of 1984/85. During
the latter period, up to 100-200 people a day were
reported collecting lugworm in the Haven.
As a result of the increased problems
being caused to local fishermen, in 1985 the Alnwick
District Council adopted Section 82 of the Public
Health Acts Amendment Act (1907) to enable the enactment
of a byelaw stating that without lawful right
or authority no person shall in any part of the
restricted area dig for ragworms or for any form
of fishing bait. The restricted area was defined
in the text as such parts of the Boulmer Haven
as lie above the low-water line. Before approving
these byelaws the Secretary of State asked for a
map of the prohibited area. The District Council
provided a copy of the Ordnance Survey map of the
area, with the area of restriction hatched. This
area extended down to the line printed on the map
as the low water mean meridian tide line.
The approved byelaws were returned in March 1996
with the map attached, and published with a reproduction
of it.
During a period of extreme low
water spring tide in February 1990, bait digging
took place in an area of exposed beach lying just
below the mean low water mark as defined on the
Ordnance Survey map. A bait digger was charged with
fishing within the restricted area identified
in the byelaws and convicted by the Alnwick
Justices in November 1990. The bait digger appealed
to the Newcastle Crown Court against this judgement.
His appeal included the following submissions: that
the geographical scope of the byelaws should be
interpreted by reference to the map, and that he
was not digging within the area hatched on the map;
that the byelaws were prohibitory, not regulatory,
because they banned baitdigging throughout the Haven
and not just in the launching area; and that baitdigging
for personal use was a common law right, making
the byelaws repugnant to the laws of the land.
This appeal was heard by the Crown
Court in May 1991, and dismissed, upholding the
conviction. The Court decided, inter alia,
that: the foreshore or seashore lies between the
high water mark and the low water mark, wherever
that may be, and the map did not form part of the
byelaws; the byelaws were not prohibitory, merely
regulatory of the beaches within the local authority
area; if there is a public right to fish in the
sea, the right to dig bait on the foreshore is not
ancillary thereto; and the byelaws were not repugnant
to the common law.
A second appeal was heard in December
1992 (Anderson v. Alnwick D.C., 1992 - 1 WLR 1156).
The judges concluded that the map did form part
of the byelaws, and allowed the appeal on this basis.
However, they also agreed that, in the absence of
such a map, the restricted area defined by the text
of the byelaws would extend to the fluctuating low
water line as it is at any time, not just at mean
low water.
The judges also held "that
a public right to take worms from the foreshore
is recognised by the common law and may be properly
be described as ancillary to the public right to
fish. ... But it does not follow that the right
is unrestricted or that it may be exercised by any
member of the public at any time or place ... This
means that in our judgement, that the taking of
worms must be directly related to an actual or intended
exercise of the public right to fish. Taking for
commercial purposes such as sale clearly is not
justified in this way. ...The rule, as we would
state it, is that bait-digging on the foreshore
is justified by the public right to take fish, when
the bait is taken on or on behalf of persons who
require it for use in the exercise of that right."
This judgement caused a temporary increase in bait
digging activity at Budle Bay, Lindisfarne NNR,
where one of the original NNR byelaws was nullified
by the judgement (see above).
Finally, the court concluded that
the Alnwick byelaws were regulatory, not prohibitive,
because Boulmer Haven was only a limited area, a
small part of the foreshore within the local authority
area, and an even smaller part of the Northumbrian
foreshore. Although the area affected was larger
than fishermen would like, it did not "prohibit
them obtaining worms reasonably close by".
These judgements are summarised in Evans, L.J. and
Macpherson of Cluny J. (1993).
Following this judgement, the District
Council has not been attempting to enforce the existing
byelaw, which has not yet been repealed. Instead,
a number of meetings have been organised between
the District Council, the Duke of Northumberland
Estate, local police, national and regional sea
angling organisations, the Environment Agency and
local fishermen from Boulmer in an attempt to resolve
the situation. The local fishermen who launch from
the Haven had been most severely inconvenienced
by bait digging activity and were strongly in favour
of a complete ban on the activity over the whole
beach. Angling representatives, however, stated
that they would litigate against such a ban. A satisfactory
solution for all parties now appears to have been
reached, with good publicity having been obtained
in the specialist angling and national press. The
District Council has drawn up a new byelaw dividing
the beach into two parts. The demarcation line to
be established across the beach will be marked not
only on a map, but also by a line of painted boulders
on the shore (these are necessary for enforcement
because so much digging is carried out at night).
Bait digging for personal use by anglers will be
permitted to the south of this line, but prohibited
to the north where launching of fishing vessels
and the lifeboat takes place and moorings are located.
No commercial bait digging will be tolerated anywhere
on the shore.
The new draft byelaw has been approved
by the Home Office and forwarded by the local police
to the Crown Prosecution Service (CPS), with a request
that the CPS (rather than the District Council)
undertake any necessary prosecution of offenders
once the byelaw is made. If the CPS also approve
the draft, it will be made by the District Council
and advertised for comment. Following the previous
detailed consultation with fishermen and anglers,
the District Council does not anticipate any serious
objections. Once any objections have been considered,
and resolved as necessary, the byelaw will be sent
to the Home Office for approval by the Secretary
of State. Signs will be erected in the village and
the markers established on the shore.
This case study is a very good
example of a compromise solution that appears to
fulfil the needs of all parties. It is therefore
a useful model for resolving the needs of bait collectors
and other users within a single site through zonation,
with the backing of legislation enabling the agreement
to be enforced. In the latter respect, it differs
from the case study at Budle Bay where the zonation
agreement was entirely voluntary and could not be
enforced, resulting in complete closure of this
area of shore to bait collectors. However, the case
study also highlights one of the drawbacks of resorting
to legal means to enforce zonation: it takes many
years of consulation before such byelaws can be
made.
Acknowledgements: Tony Farrell,
Legal Department, Alnwick District Council.
Newton Haven,
Northumberland
The National Trust leases land
and foreshore at Newton Haven, where a small beach
has attracted bait diggers in the past. Numbers
increased following the introduction of controls
at Budle Bay in 1982, to up to 15 diggers at a time
(a significant number in such a small area) travelling
20 to 50 miles to the site. A ban using standard
National Trust byelaws in 1983 and an attempted
prosecution reduced the number of diggers to an
average of about four. These bait diggers worked
below the level of low water of spring tides (outside
the original limits of the leased area) where damage
was caused to populations of burrowing sea urchins,
razor shells and associated fauna that were of scientific
interest. The National Trust subsequently applied
successfully to the Crown Estates Commissioners
for a lease of the seabed in order to control yacht
moorings in the Haven and bait digging carried out
at the bottom of the shore.
A small amount of bait digging
still occurs in the Haven, where policy is now for
National Trust wardens to approach baitdiggers,
explain that the byelaws exist, that the low shore
areas are of scientific interest, and ask them to
dig elsewhere. No recent attempts have been made
to prosecute bait diggers because of the expense
of prosecutions and potential difficulty of success.
Recently, a meeting has been held with a number
of anglers representatives, and a proposal
for management has been received. The National Trust
will consider this in consultation with anglers
and with other recreational, nature conservation
and local authority representatives.
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References
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