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EAST LOTHIAN COUNCIL
LANDSCAPE AND COUNTRYSIDE
JOHN MUIR COUNTRY PARK
Annual Report 2009
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1.
2009 ANNUAL REPORT
1.1
This is the thirty third Annual Report for John Muir Country Park
covering the period of 1st April 2009 to 31st March 2010 and charts the
progress made in relation to the Objectives set out in the Prescriptive
Management Plan.
1.2
The Countryside Commission for Scotland registered the Country
Park in 1976. The Country Park currently extends to 713.5 hectares and
comprises of a variety of habitats. The majority of the Country Park is a Site of
Special Scientific Interest, with original designations that pre-date the Country
Park status by some twenty-four years. These were designed to help protect
the biological, geological and geomorphological features found within this
environment. Two further, more recent, nature conservation designations
have been put in place. The site is now incorporated into the Firth of Forth
Special Protection Area and has also been notified as a Ramsar Site.
(Ramsar Convention on Wetland of International Importance as a Waterfowl
Habitat, 1982. Under this convention Scotland has agreed to promote the
conservation of these habitats with specific regard to their ornithological
importance). All of the above are designed to give protection to special
aspects of the natural environment and the creatures living within or relying
upon it in some way.
1.3
According to the Countryside (Scotland) Act 1967, (the enabling act for
the creation of the Country Park), a country park is “a park or pleasure
ground in the countryside which by reason of its position in relation to
major concentrations of population affords convenient opportunities to
the public for enjoyment of the countryside or open-air recreation”. The
landscape features, especially the vast expanses of sand, exposed when the
tide recedes, have made this area a favourite location for a wide variety of
recreational pursuits. Through the years since its establishment, visitor
numbers have risen steadily, though poor summers in both 2007 and 2008
resulted in slight declines from the peak record returned in 2006.
1.4
The diversity of habitats within the Country Park is one reason why this
area has proven such a focus for public recreation. There has always been a
realisation that the interface between the visitor and the natural environment
needs to be managed. Since its inception, the Country Park has had a
Management Plan, which continues to evolve by taking into account everchanging opportunities and pressures.
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2.
THE MANAGEMENT PLAN
2.1
The overall management aim is:
To manage public recreation and conserve the geomorphology, geology
and landscape, and sustain the biodiversity of the Country Park.
2.2
In order to make this aim achievable the management plan strives
towards the following seven objectives through a series of specific
prescriptions and actions;
Objective 1 To provide those recreational facilities which will enhance
visitors' enjoyment of the Country Park consistent with the Aim
Objective 2 To maintain and enhance the role of the estuary as a feeding
and roosting area for wildfowl and waders
Objective 3 To conserve the mosaic of geomorphological features within the
Country Park
Objective 4 To conserve habitats, communities and species and in particular
those that are deemed special in relation to agreed criteria
Objective 5 To conserve the geological integrity of the Country Park
Objective 6 To maintain and enhance the Country Park as a suitable
breeding area for birds and in particular those deemed to be special in relation
to defined criteria
Objective 7 To conserve the landscape and character of the Country Park
2.3
The Landscape and Countryside Division of the Department of
Community Services manages the Country Park. An Advisory Group
comprised of external agencies, landowners and community organisations
provides advice. Management, on a day-to-day basis is through the
Countryside Ranger Service.
2.4
The Countryside Ranger Service operates over the whole of East
Lothian and receives operational funding from Scottish Government. In order
to meet its targets the Countryside Ranger Service has four main areas of
remit. The Country Park’s objectives are encapsulated within the Countryside
Ranger Service area of remit and therefore allow the report to be written in a
generic format.
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3.
SUMMARY OF THE YEAR

Monitoring of flora and fauna continued this year in line with the
prescriptive management plan

Control of invasive species was undertaken at the Biel Burn, Seafield
Pond area, and Spike Island with giant hogweed removed to ensure visitor
safety. Within Whitberry Point and Spike Island pine sapling and sea
buckthorn control was carried out to protect these habitats. Pirri-pirri bur
was dug out from a path within Hedderwick plantation

Travelling people set up a camp (four vehicles) at Shore Road for two
weeks in August 2009. One van parked in the bus turning area for four
days during September

Car park improvements and installation of directional signs for crossing the
salt marsh were completed at Linkfield.

Bridges were trialled over the creeks of the “horse” path over the salt
marsh to redirect traffic over this sensitive habitat

Site maintenance work was completed as required

Monitoring of user groups and their interactions was regularly undertaken
to gauge use of the site

The Advisory Group would like to thank all those groups of individuals who
volunteered their time during the year, to work on management projects
within the Country Park
4.
PROVIDING A WELCOME FOR VISITORS
Public contact and all it entails forms a very large proportion of the work at the
Park mainly by patrolling and liaising with the visitor, listening and responding
to complaints or inquiries. Maintaining open paths, undertaking minor repairs,
strimming, painting and ensuring a clean and tidy site are all aspects of
providing a positive visitor experience.
4.1
Improvements to the surface of the car park at Linkfield were
undertaken to provide more hard standing area for parking and to encourage
people to the eastern end of the car park for access to the beach over the salt
marsh.
4.2
Work along the “horse path” crossing the salt marsh was completed
(using volunteers) to bridge the creeks to provide a safer and drier route for
horses and pedestrians alike. These bridges proved successful in
encouraging horse riders to cross in the correct place. However, the bridges
did not withstand the high autumn tides and are being replaced with more
robust structures. One of these bridges has been in place since November
(again as a trial) and has survived strong storms and tides with no damage.
4.3
New signage was installed to encourage and inform users of the
improved path.
4.4
Following an encampment of travelling people in November,
extensive clearing up of the site by contractors was required, coupled with
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repairs to the access gate to Linkfield car park and the wooden barriers
around the horse parking area.
4.5
Work continued on replacing the seaward fence at Shore Road.
4.6
The dog bag dispenser at Linkfield car park continues to be well used
and the Countryside Ranger fills this on a regular basis. However, the
practice of irresponsible dog owners lifting their dog faeces only to then
incorrectly dispose of the bag continues to be a problem.
4.7
The Countryside Ranger continues to approach members of the public
when she sees them letting their dogs foul and gives them poop scoops.
4.8
During the summer months there were several complaints about the
smell from some of the rubbish bins following the disposal of dog bags.
The Countryside Ranger empties the bins on a regular basis (on occasion
twice a day,) however the smell can still be a problem. The larger dog-fouling
bin put in place at Linkfield is being well used and a further rubbish bin was
sited next to it. This has helped with the problem of the dog-fouling bin
overflowing, especially at weekends. The bin is currently emptied twice a
week on a Monday and Thursday. The Countryside Ranger obtained stickers
to put on the lids of the other bins on site stating that dog waste can be
disposed on in these bins.
4.9
The dispensers for both paper litterbags and leaflets also continue to
be well used but in November were destroyed by vandals. The remains were
removed from site and repairs carried out.
4.10 Repairs to site furniture were undertaken over the year including
fences, marker posts, gates, bridges and benches.
4.11 Removal of several undercut trees along the estuary edge of the
plantation was required over the winter following high tides and winds.
5.
INTERPRETATION AND FACILITIES
5.1
For the sixteenth consecutive year Belhaven Bay was awarded the
Seaside Award (Keep Scotland Beautiful), in the Rural Beach Award
category. During the bathing water season, however, periods of heavy rain
resulted in a number of low water quality results recorded Belhaven Bay, with,
on a number of occasions, large amounts of sewage related debris being
recorded along the tide line. The Countryside Ranger liaised with Scottish
Water and SEPA to ensure that this problem was addressed as quickly as
possible, with Scottish Water sending out a cleansing squad to remove the
debris.
5.2
The barbecue site was booked on 15 occasions. Before the arrival of
each group a stock of firewood was left beside the fire-pit and the grills and
site were checked to ensure they were clean and tidy. The banks around the
BBQ site were frequently strimmed and the vegetation cut to ensure that it
was maintained in a safe and presentable condition. The drop in number of
BBQ bookings may be due to the band on alcohol consumption in public
places (which includes JMCP). The local area office reported that on several
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occasions before booking members of the public had asked if alcohol was
allowed. Once they were told no they did not book the site.
5.3
Tide tables were posted monthly on the metal bridge at Shore Road to
inform the public of the times the bridge would not be accessible during high
water. There is also a warning notice to this effect at the information board at
Shore Road car park.
6.0
SITE MONITORING
6.1
Due to a breakdown in the car counter retrieval equipment, it has
been impossible to assess accurately visitor numbers for the three car parks
(Tyninghame Links, Linkfield, Shore Road). A replacement monitoring system
has been identified as a priority purchase for 2009-10, in order to continue to
monitor annual visitor number fluctuations.
6.2
Appendix 1 shows the historical data for visitor numbers.
6.3
The pressure pad pedestrian counter located on the estuary footpath
recorded a total of 6171 passes over the period of January to November
2009. Due to the cold weather in December a reading was not be taken as
the ground is frozen.
7.
VOLUNTARY GROUPS
7.1
Nine groups / individuals volunteered their services during the course
of the year. In addition people serving on the Community Service for
Offenders Programme completed several tasks equating to c.65 hours work.
Tasks included litter picking, strimming and cutting back vegetation.
7.2
Belhaven beach was adopted by the Belhaven Surf Club, (as part of
the Marine Conservation Society’s ‘Adopt-a-Beach’ campaign), in an effort to
increase the cleanliness of the area. They undertook extensive litter picks
during May and September 2009. This was of great help to the Countryside
Ranger as they were able to carry back large items from the shoreline.
7.3
Details of all volunteer work can be found in Appendix 4. This work
contributed greatly to the successful completion of a number of management
tasks.
8.
ENVIRONMENTAL INTERPRETATION
Our aim is to provide an experience and promote a greater understanding of
the countryside through environmental interpretation. This is aimed not just at
the local community but to the wider audience of visitors from around the
globe.
8.1
SUMMER EVENTS AND VISITING GROUPS
8.1.1 The Countryside Ranger led four events from the Summer Events
Programme. Following the success of linking events with the John Muir
Birthplace in previous years this was repeated. Unfortunately, due to the wet
summer the events were not as well attended as would have been predicted.
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8.1.2 The addition of drop-in events where people could come along for a
short period of time was very successful, helping to make people aware of
what the Countryside Ranger Service does and at getting across the message
of responsible access while targeting regular users of the site and daytrippers.
8.2
SCHOOL GROUPS
8.2.1 39 groups visited the park as part of formal education. The
Countryside Ranger was involved with 35 of these groups. Further
information on the schools, the topics studied and the numbers involved can
be found in Appendix 2. A number of school classes visit the Park under the
guidance of their teachers. The Countryside Ranger Service is often unaware
of these visits and they therefore go unrecorded.
8.3
RESEARCH APPLICATIONS
The list of research projects undertaken within JMCP, are outlined in
Appendix 5, several of these projects have come to an end and the
Countryside Section is awaiting information prior to issuing any extensions. It
is unfortunate that we do not always get copies of these final reports. The
knowledge generated by these individuals is likely to be useful in the review
and production process of each new 5-year Management Plan.
9.
SURVEY AND MONITORING
Increasingly important in the decision making process is the need to collect
data, which, over a time frame, can show trends or fluctuations in the
presence or absence of species. Changes in the natural environment are
equally as important and an indication of their cause and effect allows
management to take place in a sustainable manner since each part of our
environment interacts with each other.
9.1
WILDFOWL AND WADERS
9.1.1. Twelve high water wader and wildfowl counts were carried out on a
monthly cycle to monitor the fluctuating pattern of water bird life on the
estuary. These counts are submitted to the national count database of the
Wetland Bird Survey (WeBS). Counts of the birds on the Tyne estuary have
been carried out since 1969 and form the longest running species dataset for
the Park. Results for the Annual Report year are shown in Appendix 6. In
addition, as part of a 5-yearly survey of the Outer Forth region, four low-water
counts were conducted on a monthly basis between November 2009February 2010. The results are presented in Appendix 6 and will be similarly
submitted to the Wetlands Birds Survey team for analysis.
9.1.2 Once a fortnight, counts were completed of birds on Seafield Pond.
During the wildfowling season water bird counts were carried out on the River
Tyne upstream of the Park boundary. These counts supplement the WeBS
data, and are important when analysing the bag returns submitted by those
individuals who hold permits that allow them to shoot at the Country Park.
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9.1.3 Over the years it has been noted that there is a sizeable passage flock
of ringed plover present within the Park. On the 11 May 223 birds were
recorded.
9.2
VEGETATION MONITORING
9.2.1 Targeted plant species were scheduled for monitoring this year in-line
with the requirements of the management plan. The steep gradient and very
overgrown condition of the banking, made it particularly difficult this season to
monitor the cowslip (Primula veris) population. The cutting of these bankings
is outlined as a prescription within in the management plan however, due to
health and safety implications this prescription is no longer being undertaken.
9.2.2 Primrose (Primula vulgaris), common twayblade (Listera ovata), and
early purple orchid (Orchis mascula,) which are all found on the semi-natural
grassland bankings surrounding Winterfield Golf Course Clubhouse, were
monitored. Once again the overgrown nature of the banking made accurate
counts difficult. In addition, eel grass (Zostera spp), hairy violet (Viola hirta)
and rush-leaved fescue (Festuca arenaria) were also monitored in line with
the recommendations of a botanical consultant (Ben Averis) who reported on
the monitoring of undertook a study of vascular plant species within the Park.
9.2.3 Over the five-year period of the current management plan (2004-2009),
17 of the 19 species recommended in the above report have been monitored.
The presence and distribution of several of these species has in turn been
recorded in map format, albeit hand-drawn. It is hoped that these can be
digitised in time to make the information more available.
9.2.4 Two species, however, fern-grass (Catapodium rigidum) and leafy rush
(Juncus foliosus) could not be located at previously identified localities. The
Countryside Ranger will continue to check for these species, and, should they
re-appear, undertake monitoring of them as per the overall botanical
monitoring strategy.
Summary of vegetation monitoring during the 2004-2009 five year
Management Plan:
Species
Comments
Bog pimpernel
(Anagallis tenella)
New species for this management plan. This species was
mapped within the undulating wet habitat at Hedderwick
plantation. There were two small patches present within
the area. Ad-hoc recoding showed throughout the last four
years this species is still present. To be monitored once
every 5 years.
Saltmarsh flat-sedge
(Blysmus rufus)
New species for this management plan. This species has
a healthy population within the salt marsh on the landward
side of Spike Island and was mapped for the first time
during this management plan period. Healthy population
at present. To be monitored once every 5 years
Sea bindweed
(Calystegia
This species has been part of the long term monitoring
programme within JMCP. It is found in one location in the
Page 8 of 27
soldanella)
marram grass of Spike Island. The area of cover is
expanding slowly. To be monitored once every 5 years
Grey hair-grass
(Corynephorus
canescens)
This species was monitored by SNH in the past. It is
located in Young’s Knowe. The individual number of plants
was recorded. There is a healthy population of this
species, which is expanding slowly. A second location
on the salt marsh/sand dune margin was found in 2007
however, this has not been seen again since. This may be
due to the area now holding water for longer, which is not
suitable for this species. To be monitored once every 5
years
Rush-leaved fescue
(Festuca arenaria)
This species has been part of the long term monitoring
programme within JMCP. It covers an extensive area of
Spike Island and continues to have a healthy population
within the dune system. To be monitored once every 5
years
Scots lovage
(Ligusticum scoticum)
This species has been part of the long term monitoring
programme within JMCP. It is found on the seaward
margin of Whitberry Point. Flowering Spikes area counted
to establish the size of the population – this species is
increasing in both the number plants and the area it
covers. To be monitored once every 5 years
Sea hard-grass
(Parapholis strigosa)
This species has been part of the long term monitoring
programme within JMCP. This plant occurs within the
Belhaven Bay salt marsh. There has been an increase in
the area covered by this species. This may be due to
the salt marsh lying wetter - possibly due to wet summer
over the last few years - therefore becoming a more
suitable habitat. To be monitored once every 5 years
Sea wormwood
(Seriphidium
maritinum)
This species has been part of the long term monitoring
programme within JMCP. The area covered and
abundance of this species has increased since this
species was first recorded on the site and is now wide
spread on both sides of the estuary. To be monitored once
every five years
Strawberry clover
(Trifolium fragiferum)
This species has been part of the long term monitoring
programme within JMCP. There has been an steady
increase in the range of this species within the salt marsh
at Belhaven Bay, this species is now wide spread within
the salt marsh and can be seen to be concentrated in
areas adjacent to paths crossing the salt marsh. To be
monitored once every five years
Hairy violet (Viola
hirta)
This species has been part of the long term monitoring
programme within JMCP. This species is no longer found
at two of the locations it was recorded in the past –
Ravensheugh dunes and Sandy Hirst - this may be due
to these areas being overgrown with marram grass at
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Ravensheugh and sea buckthorn and other scrub species
at Sandy Hirst. Both of these locations only had small
populations of this species. The remaining site is along
the northern margin at Hedderwick Plantation. This is still a
healthy population that is slowly increasing in extent
within this area. To be monitored once every five years.
Narrow-leaved
Eelgrass (Zostera
angustifolia)
This species has been part of the long term monitoring
programme within JMCP. This species is located to the
seaward side of Sandy Hirst. There are some areas of
very dense growth and others of sparse growth – this is
expected due the habitat it is located within having some
areas of more suitable substrate. The population is
healthy and appears to remain stable with some
increase in area covered to the eastern end of Sandy
Hirst. To be monitored once every five years.
Dwarf eelgrass
(Zostera noltei)
This species has been part of the long term monitoring
programme within JMCP. This species is located in the
inner estuary towards the southern edge of the mud flats.
Again this is a healthy population with some dense
patches. The overall extent of cover is also increasing. To
be monitored once every five years.
Common twayblade
(Listera ovata)
This species has been part of the long term monitoring
programme within JMCP and is currently monitored
annually. Located on the semi-natural grasslands at
Winterfield golf course this species appears to be
remaining stable in population.
Early-purple orchid
(Orchis mascula)
This species has been part of the long term monitoring
programme within JMCP and is currently monitored
annually. Located on the semi-natural grasslands at
Winterfield golf course this species in the past has shown
fluctuations in number of flowering spikes year on year
with the population never remaining stable. Over the last
five years there has been a drop in the number of plants
present, with NONE recorded for 2009. This is most likely
due to the banking no longer being strimmed over winter
due to health and safety implications. The lack of cutting
has resulted in a change in the vegetation structure
causing over-shading and greater competition for this
species. This is the only location within JMCP that this
species has been recorded.
Cowslip (Primula
veris)
This species has been part of the long term monitoring
programme within JMCP and is currently monitored
annually. Located on the semi natural grasslands at
Winterfield golf course this species has shown a decrease
in the number of flowering spikes. Again this is most
likely due to the bank no longer getting cut and therefore
becoming overgrown. The overgrown nature of this very
steep bank has also made it very difficult to monitor this
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species.
Primrose (Primula
vulgaris)
This species has been part of the long term monitoring
programme within JMCP and is currently monitored
annually. Located on the semi natural grasslands at
Winterfield golf course this species has shown a decrease
in the total area covered. Again this is most likely due to
the bank no longer getting cut and therefore becoming
overgrown.
Reflexed salt marsh
grass (Puccinellia
distans)
New species for this management plan. This plant is
located around the margin of Seafield Pond and was
monitored for the first time in 2008. The population
appears to be healthy. To be monitored once every five
years.
Fern-grass
(Catapodium rigidum)
NOT monitored there were records for this species at
Seafield Pond however they could not be located.
Leafy rush (Juncus
foliosus)
NOT monitored there were records for this species at
Seafield Pond however they could not be located.
9.3
MONITORING TARGETED ANIMAL SPECIES - BIRDS
9.3.1 Sand martin colonies at the Country Park were monitored on a regular
basis. On 16 June a nest count was made at Winterfield and at Hedderwick
Sands. Unfortunately, following the successful re-colonisation at Winterfield in
2005, no nests were recorded in this area. At Hedderwick Sands, 18 active
nests were recorded which is the highest number in the last five years. The
following graph shows that the nest count for this species fluctuates yearly.
This is often due to weather conditions during their migration. Local factors,
such as erosion of the sandy cliff front that they nest in at Hedderwick, may
also be a factor.
Total number of nests
Number of Sand martin (Riparia riparia) nests 2005-2009
at Hedderwick
20
15
10
5
0
2005
2006
2007
2008
2009
Year
9.3.2 The annual kittiwake nest count was carried out on June 5th.
Appendix 10 shows the number and distribution of nests at the colony. The
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count of 933 nests represented an overall drop in nest numbers of 62 nests
from 2008. Prolonged wet and windy weather at the beginning of the nesting
season may explain the reduction in nesting pairs.
The following graph illustrates the total number of nests over time at the
colony. Sporadic data is available from 1979 to 1985. Since 1986 annual
counts have been undertaken. The data shows a steady increase in numbers,
with a peak in 2000. Since then, the number has fluctuated in the region of
900-1100 nests.
20
09
20
07
20
05
20
03
20
01
19
99
19
97
19
95
19
93
19
91
19
89
19
87
19
85
19
83
19
81
1400
1200
1000
800
600
400
200
0
19
79
Number of Nests
Total Number of Kittiwake (Rissa tridactyla) nests at Dunbar Castle
1979-2009
Year
The kittiwake colony is of interest since it is one of the few accessible,
mainland colonies. The birds are confiding and have lent themselves to
close academic study. A productivity-monitoring plot has been long
established, conducted by the Countryside Ranger Service. In addition, a
long-term monitoring programme is in place, and on the 18 July the annual
ringing was undertaken. Due to the cool and wet weather only adults were
ringed this season with the young being left in the nests.
Over the summer period dead birds found beneath the nests were collected
by the Countryside Ranger with any rings being removed and the birds
disposed of. This year, the mortality rate of chicks was very low and a large
proportion of the chicks appeared to reach fledgling size. It was also noted
that feeding also seemed better this year with large shoals of sand eels often
being seen in the harbour. An examination of nests during the ringing
programme revealed very few pipe fish carcasses.
9.3.2 The annual count of non-breeding swans, completed 11 April 2009,
recorded 44 individuals. A separate count of the moult flocks of mute
swans was undertaken on the 25 July 2009, with 5 individuals recorded. The
estuary is a safe habitat for both the moult flock from predation and the nonbreeding flock from competition from breeding pairs.
9.3.3 Three autumn goose counts were undertaken on behalf of the
Wildfowl and Wetland Trust as part of their national monitoring scheme. This
data is used to under taken assessments of data in relation to wildfowling on
site.
9.3.4 Once a year the foreshore between the Peffer Burn and Dunbar
harbour is searched for dead birds. The information is forwarded to the Royal
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Society for the Protection of Birds who collate the data and produce a digest
of national statistics. On the 27th February 2010 one whooper sawn carcass
was found in addition to the wings and legs of one black headed gull and one
herring gull.
9.4
INFORMAL OBSERVATIONS
9.4.1 Casual records were also made of any other wildlife. These include
several badger sightings in Tyninghame woods; barn owls and tawny owls
at Lime-tree Walk (early mornings and dusk while checking wildfowlers);
foxes and otters at Moss House point and Seafield Pond and roe deer at
several localities. A pod of 8 bottle nosed dolphin (Tursiops truncatus) were
seen off Whitberry point and two Orca (Orcinus orca) at Belhaven Bay.
9.5
BUTTERFLIES
9.5.1 A weekly butterfly transect is conducted during April – September.
Due to wet weather at the beginning of the season only 15 of the usual 28
transects were possible to complete. The transect data is entered into the
Butterfly conservation database so that it can be compared to national data.
9.5.2 The methodology follows that devised by the Institute of Terrestrial
Ecology for their national butterfly-monitoring scheme. This provides a
standardised means of recording the yearly flight dates of the butterflies within
the Park.
9.5.3 One comma butterfly (Polygonia c-album) was recorded at
Tyninghame Links, and one speckled wood (Pararge aegeria) was recorded
at Hedderwick plantation. Uncommonly high numbers of common blues
(Polyommatus icarus) were also recoded over a period of warmer weather in
July. In addition large numbers of six-spot burnet moths (Zygaena
filipendulae) were also recorded in July with 95 being counted on one transect
in July.
9.6
CONTROL OF INVASIVE SPECIES
9.6.1 Spraying of giant hogweed (Heracleum mantegazzianum) was
undertaken along the Beil burn and around Seafield Pond. The Countryside
Ranger dug out three additional plants from Spike Island. Japanese
knotweed (Fallopia japonica), now established below ( thought to be garden
escape) the glebe on the cliff top trail, was also controlled.
9.6.2 The pirri-pirri bur (Acaena ovalifolia) found in 2007 within Hedderwick
plantation was monitored on a regular basis and removed by hand pulling to
try and prevent the spread of the small (approximately 1m x 2m) patch.
9.6.3 Scots pine (Pinus sylvestris) seedling removal continued on Spike
Island and Whitberry Point with help from Secondary School work placement
students. The removal of these self-generating pines is undertaken to
preserve the natural succession of Spike Island and the coastal heath at
Whitberry point. No rhododendron (Rhododendron ponticum) control was
required on Whitberry Point this year.
9.6.4 Sea buckthorn (Hippophae rhamoides) was cut down on Whitberry
Point to open up the paths. This was done with help from Secondary School
work placements, volunteers and Countryside Rangers.
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9.6.5 The large sea buckthorn stand on Spike Island mechanically
removed in February 2007/8 continues to be monitored. Further removal of
the small plants around the perimeter of the original stand was carried out
using volunteers.
10.
MONITORING GEOMORPHOLOGICAL CHANGES
10.1 The extensive blow-out at Ravensheugh dune has remained in much
the same state as the previous year possibly due to the dune being eroded far
enough to be held in place by the vegetation at the back.
10.2 The Countryside Ranger continues to monitor changes along Sandy
Hirst where the sea, during high tides and storms, is breeching the landward
end of the spit on a more frequent basis. At present there does not appear to
be any detrimental effect from this increased inundation of the salt marsh of
Heckies Hole with salt water. Following a visit from Scottish Natural Heritage
it was recommended that no action was needed as this represented a natural
process.
10.3 The condition of the salt marsh between Linkfield and Spike Island
has become a cause for concern. Extensive tracking across desire lines have
produced braided paths across the feature, which, in turn have become
stripped of vegetation cover. In other areas damage from horses has resulted
in yet further erosion of the vegetation. Anecdotal evidence suggests the
feature is changing, developing more of a vertical profile, with the
consequence that certain areas are now holding water for prolonged periods,
whilst others may be drying out. The installation of a recommended path (at
the eastern end of the marsh) supported by advisory signage is anticipated to
reduce the damage cause by the tracking. Monitoring will continue.
11.
MONITOR/ENFORCING WILDFOWLING SYSTEMS
2008/2009 Wildfowling Season Summary:
11.1 233 permits were issued with a total of 564 visits being made to the
estuary. This is the lowest recorded number of visits for John Muir Country
Park (JMCP) since the permit system was first established in 1982.
11.2 Details of distribution of the permits issued can be found in Appendix 8
with the breakdown of the number of birds shot through the season appearing
in Appendix 9.
11.3 Comparison of the number of visits against the number of birds shot
gives an indication of wildfowling success against effort expended, but does
not necessarily reflect the presence or absence of quarry species, or their
numbers. On a month-by-month basis, November proved to be the most
productive, with an average of 0.86 birds shot per visit, followed by
September and December with averages of 0.73 and 0.72 respectively.
January and February were the least successful with averages of 0.61 and
0.62. There has been a steady drop in the return for effort expended
calculation since the 2003/04 season when it was averaging very nearly one
bird per visit.
Page 14 of 27
11.4 Geese were shot in each month of the season. The total number of
geese shot was 130 (50 Pink-foot, 72 Greylag, 8 Canada), which equates to
the highest geese bag ever recorded.
11.5 Wigeon returns were lower than the 2007/08 season with 122 birds
shot. This is the lowest recoded wigeon bag for JMCP. Teal returns were
also lower than last season with 51 individuals being shot in comparison to 91
and is on the third lowest bag return. Mallard numbers fell from 86 for
2007/08 to 66 individuals for this season which is the second lowest bag
return for mallard. The woodpigeon bag of only 20 birds being represents
the lowest return since the permit system came into force.
2009/2010 Wildfowling Season adverse weather:
11.6 Following fourteen consecutive days below freezing in late
December 2009 early January 2010 a compulsory fourteen day ban of
shooting was imposed on wildfowling. During this period notices were put up
on site to inform both the wildfowlers and general public. No incidents of
shooting were recorded in this time.
12.
TERN BREEDING MEASURES
12.1 Sadly, no little terns nested within the Country Park. Following the
decision made in 2003 the tern fence was not erected. During the time where
the terns would normally have started to nest on Spike Island the Countryside
Ranger closely monitored the site for any activity and to assess whether
protection measures are required. A pair of arctic terns nested at the tip of
Spike Island laying 2 eggs though the nest was washed away prior to
hatching.
12.2 12th June one pair Arctic tern found nesting on the sands beyond the
tip of Spike Island nest contained two eggs. Unfortunately nest failed due to
inundation by subsequent high tide.
13.
SITE SAFETY
13.1 An adequate level of water at Seafield Pond ensured successful
breeding by swans, moorhen, mallard and coot. However, the heavy rainfall
on occasion and large amount of snow in December 2009 and January 2010
resulted in a temporary pump once again being required to prevent flooding of
the caravan park. The water level was significantly reduced to allow for the
melt water.
13.2 Throughout the year, monthly water samples were taken and
submitted to the Public Analyst’s Office in Edinburgh for routine analysis for
water quality. In general the water samples returned unsatisfactory levels of
faecal coliforms (origin unknown) and the pond was closed to water sports for
most of the year. An enhanced sampling regime has been put in place in
order to ascertain underlying causes.
13.3 From October - mid November the Pond was found to have another
outbreak of blue-green algae. Notices were erected to warn the public and
once again the Pond was closed to water sports.
Page 15 of 27
13.4 The emergency throw lines located at Shore Road, Belhaven Bay
and Seafield pond were unravelled on several occasions. To ensure the throw
lines were in place and in good condition the Countryside Ranger checked
these twice a week.
13.5
The emergency phone was checked on a weekly basis.
13.6 Tide tables were put up regularly on the metal bridge at Shore Road,
to inform members of the public when the bridge is likely to get cut-off due to
high water.
13.7 Following heavy winds, several trees within Hedderwick plantation
blew over. The council forestry team cleared fallen / hung-up trees when
required.
13.8 On the 4th June there was a fire at the eastern end of Spike Island
the fire brigade was called and successfully extinguished it. An area of
approximately 50m by 20m was damaged. In the centre of the fire area were
two disposable BBQ’s, which are thought to have been the source of the
incident. The area is, however, regenerating well, with the first flush of
rosebay willow herb being seen within weeks, marram grass has successfully
re-colonised the area.
13.9 Unfortunately, over the year the Coastguard and RNLI have been
called to four incidents within JMCP. Two bodies were recovered; one from
Belhaven Bay and one from beneath the Cliff top Trail. In addition, a kitesurfer had to be rescued after ditching his kite in the water. The RNLI inshore
lifeboat also overturned during a training exercise in Belhaven Bay. No
injuries were sustained, however, the boat was damaged and had to be
recovered from the beach. In addition to these recorded incidents the
Countryside Ranger has been informed of further instances of surfers getting
into trouble in the water and one getting struck by their board. Other surfers
assisted the casualties.
13.10 There were also reports of several surfers being stung by weaver fish.
Weaver fish have always been present at Belhaven Bay with reports in the
past. However, the larger number of surfers now in the water may have
resulted in more incidents being reported.
13.11 On a regular patrol the Countryside Ranger assisted one visitor who
had been stung by a lion’s main jellyfish.
14.
MONITORING HORSE USE
14.1 Monitoring horse use within the Country Park is ongoing, with the
Countryside Ranger talking to riders, explaining the background to the new
panels and leaflet and collecting details of any riders who are not on the new
list. When the riders were not available to talk to, vehicle registrations were
checked against the master list of riders for the Country Park. Holding an upto-date list of email addresses has meant that horse riders are able to be
informed of any relevant issues in a quick manner.
14.2 The board at the horse parking area enabled the Countryside Ranger
to display tide tables to inform riders of suitable times for accessing the
Page 16 of 27
foreshore. Unfortunately, the practice of not keeping to preferred routes to
cross the salt marsh continued, despite the best efforts of the Countryside
Ranger to talk to riders and provide them with information.
15.
USER GROUP INTERACTIONS The Belhaven Bay User Group met
on one occasion to discuss any issues on site. Discussions about the
increased number of surfers using the site sparked interest in working towards
ensuring that access across the salt marsh is responsible and sustainable.
16.
BAIT DIGGING Bait digging was observed on several occasions within
the Park. When possible the Countryside Ranger speaks to bait diggers to
encourage back filling of the holes. Bait diggers seen at Tyninghame digging
in the mussel beds are of particular concern, and are encouraged to use other
areas.
17.
PERIWINKLE COLLECTION
17.1 During the Autumn / Winter the rocky foreshore was targeted at low
water by travelling people illegally camping at countryside sites within East
Lothian. They collected vast quantities of edible periwinkles (Littorina
littorea). Winterfield foreshore and Whitberry Point were the main areas
targeted. Access to the rocky shore from the wildfowlers’ car park is still
prevented by two large tree stumps that may have helped to reduce the
number of visits by vehicles onto the shore at this site.
17.2 The nature of collection followed a similar pattern to previous years.
No riddling for size took place instead bags complete with small immature
specimens were harvested for sale. It is believed that if this practice continues
unchecked it will result in a significant change in the ecology of the shore.
17.3 Small-scale collection of periwinkles in the Winterfield area by people
local to the Dunbar continues. Typically, these collectors remove only a small
amount of periwinkles from the foreshore, riddling for marketable sized
individuals as they go.
17.4 The Countryside Ranger continues to monitor the amount of collection
within the Park, these records in turn are added to observations taken across
the entire East Lothian coastline, with a view towards shaping a future policy
on shellfish management.
18.
ENFORCING BYELAWS/MANAGEMENT RULES
18.1 During the summer a number of disposable BBQs were used at the
site. The practice of not disposing of the trays in a responsible manner
continued, with people leaving them on the beach, on picnic tables and in the
play park and car parks. Hot BBQs were also placed in rubbish bins in
Linkfield car park causing them to catch fire.
Page 17 of 27
18.2 When the Countryside Ranger deemed people to be having BBQs in
inappropriate areas she encouraged users to move to the beach below the
strand line.
18.3 A total of 209 incidents were recorded of occasions when discarded
disposable BBQs were found on site disposed of by the rubbish bins, buried
on the beach/dunes or left in the car park or on picnic tables. This total is
significantly higher than last season (93 in 2008).
19.
ACCESS ISSUES
The ethos of the Country Park has always assumed a freedom to roam within
its boundaries. On occasion there is a requirement to restrict access to
control an activity, which may prejudice the success of an event or irreparably
damage features within the environment.
19.1 The crossing of the salt marsh contrary to recommended routes (on
display in the car park and on the horse riders riding permit), continues to be a
cause for concern (see section 10.3), but is partly understandable given
changes in the nature of the salt marsh itself. The recommended horse path
at the eastern end of the salt marsh is no longer suitable for horses due to
deep holes and widening creeks caused by tidal inundation and the ground
becoming much softer. It is hoped that the continuing work to improve this
path will resolve this problem.
19.2 The erection of fencing along the back of the dunes in the
Ravensheugh – Peffer Burn locality has been the cause for some concern,
with regards to access. It is believed the fencing is to allow for grazing and, by
reducing the height of the sward in this location, could improve the habitat for
ground nesting birds including Skylark and Meadow pipit. The Access Officer
is currently in discussion with the landowner.
Tara Sykes, John Muir Country Park Countryside Ranger
Page 18 of 27
Appendix 1 – HISTORICAL CAR PARK FIGURES
Count Period
1st January – 31st December 1992
1st January – 31st December 1993
1st January – 31st December 1994
1st January – 31st December 1995
1st January – 31st December 1996
1st January – 31st December 1997
1st January – 31st December 1998
1st January – 31st December 1999
1st January – 31st December 2000
1st January – 31st December 2001
1st January – 31st December 2002
1st January – 31st December 2003
1st January – 31st December 2004
1st January – 31st December 2005
1st January – 31st December 2006
1st January - 31st December 2007
FM foot and mouth
Linkfield
135,513
147,998
152,640
164,549
180,159
185,164
193,303
206,964
207,142
114,172
171,559
187,438
194,057
188,801
199,242
198,455
Shore Road
102,147
112,584
115,220
118,561
121,565
117,801
122,385
116,444
116,223
122,117
133,609
143,631
145,831
142,527
149,092
128,801
Page 19 of 27
Tyninghame Links
56,765
59,323
56,796
59,837
58,768
59,252
59,392
60,295
61,564
49,343
60,926
67,540
71,515
68,577
85,847
83,487
Total
294,425
319,905
324,656
342,947
360,492
362,217
375,080
383,703
384,929
315,632 FM
336,094
398,609
411,385
399,905
434,181
410,743
Appendix 2 – VISITING GROUPS
Date
Group
Activity
Number
1 April
Wallyford Primary
Team building
31
2 April
Wallyford Primary
Team building
30
13 April am
Musselburgh Burgh
Beach scavenger hunt
30
13 April pm
Musselburgh Burgh
Beach scavenger hunt
30
14 May
West Barns Primary
Nature trails
20
18 May
Athelstaneford Primary
Birds in their habitats
23
20 May
Musselburgh Burgh
Beach scavenger hunt
30
27 May
Green Team – Green Shoots
Buckthorn clearance Spike Island
11
1 June
Pathead Primary
Coastal processes and management
30
2 June am
Dunbar Primary
History of Harbours and Castle
25
2 June pm
Dunbar Primary
History of Harbours and Castle
25
3 June
Springfield Primary
Designs for Living
30
4 June am
Dunbar Primary
History of Harbours and Castle
25
4 June pm
Dunbar Primary
History of Harbours and Castle
25
10 June
Edinburgh Academy
Rockpooling
55
13 June
Haddington Cubs and Scouts
Environmental Orienteering
35
15 June
Law Primary
Activity week
25
16 June
Law Primary
Activity week
25
17 June
North Berwick High School
Land management, tourism and land use
42
18 June
Law Primary
Activity week
25
30 June
Ranger Event
Ranger Box of tricks
6 July
Tranent summer diversion
group
Team building and orienteering
8
7 July
East Lothian Youth Exchange
Conservation Task
12
8 July
Pathhead and Kinross Youth
team
Nature walk
10
9 July
Ranger Event
Squiggly Wigglies
17 July
Ranger Event
Trees and Wine
1 August
Ranger Event
Wildlife Crime (with Police)
4 Septmeber
Outdoor Education
S4 Challenge
14 September
Green Team – Green Shoots
Buckthorn clearance Spike Island
11
1 October am
West Barns Primary
River dipping
25
1 October pm
West Barns Primary
River dipping
25
5 October
Haddington Infants
Nature Trail
25
6 October
Haddington Infants
Nature Trail
25
7 October
Haddington Infants
Nature Trail
25
8 October
Haddington Infants
Nature Trail
25
Page 20 of 27
13 October
West Barns Primary
Woodland studies
25
14 October
West Barns Primary
Woodland studies
25
21 October
Ranger Event
Dunbar Delights
3 November
Wallyford Primary
Litter pick
12
10 November
Wallyford Primary
Woodland study
12
12 November
Knox academy
Advanced Higher Geography Sand Dune
Succession
7
17 November
Wallyford Primary
Bird ID
12
3 December
Ormiston Primary
River studies
24
17 December
West Barns Primary
Bird Boxes and Bird feeders
54
10 January
Outdoor Education
Staff Training – blokarts – SELF LED
10 February
Outdoor Education
Schools Orienteering
Appendix 3 – SPECIAL EVENTS
Date
Group
Activity
8 March
Belhaven Hill School
Preparatory School cross country
championships SELF LED
21 June
East Lothian Orienteers
Competition and BBQ SELF LED
27 June
Open University
Geology field trip SELF LED
17 September
Belhaven Surf Club
Litter Pick SELF LED
20 December
Peebles Pony Club
Rideout SELF LED
28 December
East Lothian Orienteers
Festive Frolic
Appendix 4 – VOLUNTARY TASKS AND COMMUNITY SERVICE
Date
Group
Activity
All year (rain or shine!)
John Lindsay SELF LED
Litter picking
All year
Communitry service
Litter picking, general maintenance,
strimming
31 August
Franklin Templeton Investments
Seaward fence at Shore Road
May and September
Belhaven Surf club
Adopt a beach - beach clean
19 January -23 January
General tasks
March
Tim McKenzie
General Tasks
November
Dilan Anderson
Schools placement week - General
tasks and monitoring
November
Jordan Curry
Schools placement – General tasks
and monitoring
November and
December
Neil Mitchell
Monitoring
December, January,
Amander Souter
General maintenance tasks – hours
Page 21 of 27
February
24 February
for Duke of Edinburgh award
Telford college field trip
Page 22 of 27
John Muir award and buckthorn
clearance
Appendix 5 - RESEARCH APPLICATIONS
Name
Title
Comments
J Coleman
Kittiwake Ringing at Dunbar Harbour
Permission granted until August
2008
M Sinclair
Preparation of a Coleoptra species list for
John Muir Country Park
Permission granted until 31
December 2008
Dr W Cresswell
How Does The Risk of Death Vary
Between Individuals Within a Group On
Attack by a Predator?
Permission granted until 1 March
2009
Dr K Heal
Quantify methyl bromide emissions from
different environments, in particular saltmarsh, forests and agricultural soils
Permission granted until 31
December 2008
Elaine Tooth
Monitoring Environmental change and
ecosystem health using seabird guano
chemistry
Permission granted until December
2008
Page 23 of 27
Appendix 6 – MONTHLY HIGH TIDE WILDFOWL AND WADER COUNTS
F
Mute Swan
Whooper
Swan
Pink-foot
Goose
Greylag
Shelduck
Wigeon
Teal
Mallard
Eider
Goldeneye
Red-bmerganser
Goosander
Oystercatcher
Ringed Plover
Grey Plover
Lapwing
Knot
Sanderling
Dunlin
Snipe
Bar-t-godwit
Whimbrel
Curlew
Redshank
Greenshank
Turnstone
M
3
A
44
M
27
83
J
15
1
2009
J
A
5
3
S
23
O
21
N
2
D
67
1
32 3
71
755 594 64
11
53 19 6
118 121 74
4
2
10
9
2
768
16
197
3
25
1
330
12
60
9
69
7
6
38
2
3
273 186 102
72 352 37
77
2
1
84
56
2
1
37
3
2
1
4
283 65
52 12
7
1
2
602
11
80
55
52
37
10
3
430
187
11
2
3
613 469
14
84 130
23
7
10
Pink-foot goose
Greylag goose
Wigeon
Teal
Mallard
Month
October
August
January
December
October
Page 24 of 27
766 320 421
123 113 322
52
12 66 135
2
2
348 211 457 701 257
23
1
125
150
1
32
Appendix 7 - PEAK COUNTS OF WILDFOWL 2008/09
2008/2009
season
501
231
1036
167
71
330 340
62
38 15
6
3
27 53
3
5
302 313 753 695 905 558
7
2
10 30
3
25 62 2
14 82 28 33
118 172 165 69 26 50 102 71 216
1
10 9
12
8
4
6
68 35 63
366 123 91 235 227 594
5
72 5
169
180 43
55
3
6
14 9
40
11
2
7
34
112
6
183
64
66
2
59
2010
J
F
2
2007/2008
Season
1172
222
1251
265
180
46
90
146 73
69 236
1
16 13
125 102
20
87
1
57
62
49
68
Appendix 8 - GEOGRAPHICAL DISTRIBUTION OF WILDFOWLING
PERMIT HOLDERS 2008/09 SEASON
No of
permits
issued
Dunbar
West Barns
East Linton
East Lothian
excluding above
Edinburgh mid/west
Lothian and Borders
Rest of Scotland
England
% of
total
Permits
returned
Permits
used
No of visits
08/
09
22
08/09
08/09
Am pm
9
07/
08
20
15
13
59
25
47
49
24
43
52
23
35
40
9
94
8
92
3
40
8
91
7
79
201
197
07/
08
25
08/
09
22
60
233
231
Totals
Shaded columns =2007/08 Season
Figures
Total No of
visits
104
07/
08
175
08/
09
117
56
108
161
164
24
50
90
146
140
5
33
15
65
8
55
131
23
120
23
199
365
636
564
Appendix 9 - NUMBER OF BIRDS SHOT 2008/09 SEASON
Species
Pink-foot goose
Greylag Goose
Canada Goose
Wigeon
Teal
Mallard
Goldeneye
Snipe
Sept
5
3
8
17
9
22
Subtotal
Woodpigeon
5
Totals
2007/08 Season Figures
Oct
Nov
Dec
Jan
Feb
5
13
14
11
12
12
2
16
12
17
29
12
7
1
25
11
12
2
1
29
8
16
15
9
7
7
6
2
1
2
7
4
2
0
Page 25 of 27
07/08
season
52
37
2
155
91
86
1
1
08/09
season
50
72
8
122
55
66
4
1
425
47
472
378
20
398
Appendix 10 – KITTIWAKE NEST COUNTS
1
2
3
4
5
6
Castle
Inner
Castle
S Harbour
Entrance
N Harbour
Entrance
Magazine
Leisure Johnston's Johnston's 2 Rock
Sea
Pool
1
Outcrop 1 Wall
96
65
33
4
222
1982 Jun-01
147
89
29
7
272
1983 Jun-01
159
81
38
8
286
1986 Jun-19
171
122
36
21
350
1979
24
7
8
9
10
11
12
Rock
Outcrop 2
Johnston's
3
1987 Jun-15
TOTAL
479
1988 Jun-08
217
180
41
20
458
1989 May-31
269
174
56
60
559
1990 Jun-13
278
173
59
67
577
1991 Jun-04
337
217
73
54
681
1992 Jun-22
364
285
97
104
850
1993 Jun-07
394
223
95
84
796
1994 Jun-11
358
222
91
58
729
1995 Jun-07
484
267
115
93
6
2
6
973
1996 Jun-12
451
9
243
108
79
17
2
5
914
1997 Jun-10
418
22
227
117
123
34
3
7
951
1998 Jun-11
324
93
175
88
77
42
3
8
810
1999 Jun-11
365
130
182
77
100
82
5
8
949
2000 Jun-07
351
182
258
90
139
130
5
19
12
5
2001 Jun-13
326
168
171
86
92
68
3
11
10
0
1
3
939
2002 Jun-12
314
172
175
97
129
92
6
18
13
2
0
7
1025
2003 Jun-09
320
162
164
90
107
99
6
17
11
0
0
0
976
2004 Jun-11
319
199
193
91
142
105
8
23
12
0
0
3
1095
2005 Jun-10
311
222
167
83
152
100
3
17
18
5
0
8
1086
Page 26 of 27
1191
Appendix 10 – KITTIWAKE NEST COUNTS CONTINUED
2
1
3
4
Castle
Inner
Castle
S Harbour
Entrance
N Harbour
Entrance
2006 Jun-09
332
253
189
2007 June-15
318
252
292
267
2008 Jun-13
2009 Jun-05
6
5
7
9
10
8
11
12
Magazine
Leisure Johnston's
Rock
Sea
Pool
1
Johnston's 2 Outcrop 1 Wall
Rock
Outcrop 2
Johnston's
3
TOTAL
67
153
110
1
17
17
1
2
9
1151
177
66
160
121
2
18
20
2
9
10
1155
240
120
67
125
102
0
10
19
0
10
10
995
207
120
57
136
97
1
13
21
0
7
7
933
Page 27 of 27