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Entries in GHR (356)

Monday
May072012

Little Grebe - 2003-07

The little grebe inhabits still fresh waters in the breeding season so is absent from the county’s fast flowing streams and rivers. It is secretive and inconspicuous around the breeding area and can easily be overlooked, however its distinctive far–carrying, whinnying call often betrays its presence. The nest is a floating platform of vegetation which is anchored to reeds and overhanging branches.

Comparison of the results of the two surveys indicates an almost four-fold increase in the number of occupied tetrads during the elapsed period. Most pairs were recorded on well-vegetated farm ponds used for irrigation, where there is an abundance of food in the form of small fish and invertebrates. Many of the ponds used in 2003-07 had only recently been constructed in the 1980’s but have subsequently matured, becoming vegetated and therefore suitable for Little Grebes.

Although most small waters are used by just one breeding pair, some tetrads encompass more than one such body of water and at Marloes Mere for instance, there have been four breeding pairs. Allowing for these variables, the county total was estimated to be about 70 pairs by 2007, compared to 12 pairs in 1988.   

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 31

Orange = breeding probable = 9

Yellow = breeding possible = 11

Total tetrads in which registered = 51 (10.4%)

Monday
May072012

Pheasant - 2003-07

The Pheasant is an Oriental species which was introduced into Pembrokeshire about 1586, and has since naturalised. Considerable numbers are reared and released each year for shooting purposes and this has been the case for many years. Some have survived the shooting seasons to breed in a wild state and this is the population which the local surveys have attempted to assess.

The 2003-07 survey found there had been a 21% increase in distribution since 1984-88, suggesting there were about 1,630 nests by the end of 2007 compared to 1,350 in 1988, using the mean of the estimate ranges. This is expressed as nests rather than pairs as male Pheasants habitually have several mates. They were absent from the higher parts of the Preseli Hills during both surveys.

Introduced to the islands of Skomer and Caldey, they were found there during both surveys.  They possibly bred on Ramsey during the 1984- 88 period, having presumably reached it unaided, but were not recorded there in 2003-07.

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 29

Orange = breeding probable = 225

Yellow = breeding possible = 54

Total tetrads in which registered = 308 (62.9%)

Monday
May072012

Quail - 2003-07

Small numbers of quail are detected in Pembrokeshire most summers. Usually they are located by call, only rarely are nests found and most probably do not attempt to breed. The number registered during the two five year surveys are typical of the normal level and pattern of occurrence in the county. Greater numbers are encountered during infrequent “invasion years”.  The last time this was experienced was in 1989 when at least 80 were recorded and both eggs and young were found.

Graham Rees

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 0

Orange = breeding probable = 11

Yellow = breeding possible = 1

Total tetrads in which registered = 12 (2.5%)

Monday
May072012

Grey Partridge - 2003-07

Considered to be fairly common in Pembrokeshire at the end of the 19th century, the grey partridge was in decline by the middle of the 20th century. By the time of the 1984-88 survey it was barely hanging on, surviving only because of additional birds released for shooting. The position remained precarious at the time of the 2003-07 survey and it is doubtful that a self sustaining population existed. Most modern farming practices produce conditions which do not suit Grey Partridges.

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 2

Orange = breeding probable = 0

Yellow = breeding possible = 3

Total tetrads in which registered = 5 (1%)

Monday
May072012

Red-legged Partridge - 2003-07

The county population of red-legged partridge is sustained by annual releases for the purpose of shooting. Those birds which survive the shooting season are able to breed but it is doubtful that a self sustaining population would endure without further releases. Comparing the results of the two surveys indicates a fivefold increase but in the absence of information on the scale of releases, which appears to be unregulated, it is impossible to meaningfully interpret these findings.

Graham Rees

Fieldwork 2003-07 (based on 490 tetrads)

large dots = breeding confirmed = 5

Medium dots = breeding probable = 8

Small dots = breeding possible = 12

Total tetrads in which registered = 25 (5.1%)

Monday
May072012

Tufted Duck - 2003-07

In the breeding season tufted ducks favour lowland fresh waters of moderate depths in the range two to five metres.

In Pembrokeshire, a wild bird bred with a captive one in 1988 but a fully wild pair hatched young at Marloes Mere in 1996 and again in 1997 and 1999. None were found breeding during the 1984-88 survey but in the 2003-07 period a pair produced a brood at Skomer in 2005 and again in 2006 and 2007. Probable breeding was also registered at Marloes Mere, Bosherston and Rosebush Reservoir with breeding season presence noted near St David’s.

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed =1 

Orange = breeding probable = 3

Yellow = breeding possible = 1

Total tetrads in which registered = 5 (1%)

Monday
May072012

Shoveler - 2003-07

Shoveler have nested at several localities in the county in the past but in the last twenty years seem to have become confined to three places. During the 1984-88 survey breeding was confirmed at Skomer and Marloes Mere. The 2003-07 survey found confirmed nesting at Skomer and probable breeding at Skokholm and Marloes Mere.

Graham Rees

 

Fieldwork 2003-07

Red = breeding confirmed = 1

Orange = breeding probable = 1

Total tetrads in which registered = 2

Monday
May072012

Mallard - 2003-07

Mallard nest largely around fresh water but have shown a capability to use sites well away from water. They have also readily adapted to artificial sites, perhaps epitomised here in Pembrokeshire, by sitting on eggs aboard a working lobster–fishing boat throughout its mobile working days.

An estimate of 400 nests was made during the 1984-88 survey, though at the time this was thought to be a little conservative. Interpolation from the findings of 1988-91 National Atlas provides a figure of 460 nests for Pembrokeshire. The BBS suggests there has been a 15% decrease in population in Wales over the period 1994–2007. However, the evidence from the 2003-07 county survey is of a 27% expansion in distribution, suggesting there could have been about 500 nests by 2007. The estimates are expressed as nests rather than pairs, as male Mallards normally take no part in incubation or tending young.

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 100

Orange = breeding probable = 57

Yellow = breeding possible = 76

Total tetrads in which registered = 233 (47.6%)

Monday
May072012

Teal - 2003-07

Historically the teal has only sporadically bred in Pembrokeshire. It was found breeding at just one locality during the 1984-88 survey. None were found nesting during the survey of 2003-07, although there was a single record of a bird displaying at Marloes Mere.

Graham Rees

Monday
May072012

Gadwall - 2003-07

In the breeding season gadwall favour lowland, shallow, eutrophic waters. They were suspected of attempted breeding at Marloes Mere from 1996 but it was not proven. Breeding was confirmed at Skomer in 2000, 2001 and 2004, the latter during the 2003-07 survey, when they also probably bred at Bosherston, though no ducklings were seen.

Graham Rees

 

Fieldwork 2003-07

Red = breeding confirmed = 1

Orange = breeding probable = 1

 

Total tetrads in which registered = 2

Monday
May072012

Pembrokeshire Breeding Bird Atlas 2003-07

The Pembrokeshire Breeding Bird Atlas 2003-07 provides an update to the 1994 Birds of Pembrokeshire, covering the breeding species.

The Atlas of Breeding Birds of Pembrokeshire 2003-2007 is available as a print-on-demand publication by clicking here

 

THE MAKING OF THE ATLAS

Introduction

The county of Pembrokeshire is some 158,000 hectares (613 square miles) in extent, with its southern, western and northern boundaries all coastal. The climate is maritime, with strong oceanic influences found also in the type and distribution of fauna and flora.

A review of all the species of birds recorded in the county in all seasons is to be found in the "Birds of Pembrokeshire" by Jack Donovan and Graham Rees, published in 1994 and including a breeding bird atlas based on fieldwork done in 1884-88. This important publication provided a baseline on which to compare mapped distributions and population estimates of different species within the county.

The populations of any animals that can walk, fly, swim or crawl will change in numbers and distribution over a period of time, so that any atlas will become out of date over a period of years, decades or centuries. 

Biodiversity is the buzzword, and the need to know what species are where has become important, indeed a requirement, for planning and conservation purposes.

Trends towards milder and windier winters, and towards cloudier, wetter summers, may herald longer term climate change.  But there is already anecdotal evidence, as well as indications from country-wide surveys, that there are other changes happening in the natural world.

At a local level, it was decided that the "Birds of Pembrokeshire" should be updated.  This breeding birds atlas is first stage in that process.  It does, indeed, show that there have been changes, both losses and gains, within the 15 to 20 years between the two fieldwork periods

 

Methodology

On the 2nd September 2002 the Pembrokeshire Bird Group convened a meeting at “The Patch”, Furzey Park, Haverfordwest, to discuss the desirability of producing a new avifauna for Pembrokeshire.  All interested parties were invited to attend and those interested but unable to attend were encouraged to communicate their views.

The meeting agreed to go ahead with such a project and that it should encompass a breeding birds survey using a tetrad (2km x 2km) grid. To this end an Avifauna Committee was elected, comprised of Graham Rees (chair), Annie and Bob Haycock, Jane Hodges, Trevor Price, and Mike Young-Powell.

At their first meeting, the committee decided that the breeding survey should be the first aspect to be addressed. It was to run from 2003 to 2007 and to take the same form as the 1984-88 survey so that the two would be directly comparable.  The 1984-88 survey was the first in the county to use as fine a scale as the tetrad grid.  It was also the first attempt made to estimate the size of the breeding population of each species in the county.

Recording forms and accompanying instructions (see appendix IV) were printed and distributed in time for field work to begin in 2003. 

Data from completed recording forms, representing some 30,000 records from 490 tetrads, were entered on computer by a small team comprising John and Marion Best, Annie and Bob Haycock, Fiona and Trevor Price, using the computer software package MapMate. A summary of the records from the 1984-88 survey was similarly entered, so that comparable maps could be generated.

The methods used for atlas fieldwork followed those of The Atlas of Breeding Birds in Britain and Ireland (Sharrock 1976) but recorded at the tetrad level rather than hectad (10km x 10km) level. For our local atlas however, adjustments have been made in as much as the islands of Grassholm, Caldey, Skokholm and Ramsey have been regarded as occupying one tetrad each, while Skomer and Middleholm have been treated as a composite tetrad. As in that first national atlas, the final maps are populated with small dots to indicate that a species was present during the breeding season, medium-sized dots to show that it probably bred, and large dots to show that breeding was confirmed, as shown in figure 1:

The example map above shows the data entry record card in MapMate that helps generate distribution maps. Records entered this way gradually build up a growing series of distribution dots on a map, Each record entered represents a breeding registration for a particular species in a particular tetrad. The species in this case is House Martin and the tetrad is SN04L (SN0442 Trwyn y Bwa).

The more visits that are made to a particular tetrad, the more information there is behind each dot providing an eventual final outcome - in this case the largest dot showing confirmed breeding.  In other tetrads medium dots represent probable breeding (e.g. bird showing territorial behaviour or visiting potential nest site, and probably went on to breed successfully) while the small dots show that the species was present in a tetrad at some time during the survey, but no evidence was found to indicate that it was doing more than feeding or resting there.

Another team of volunteers, comprising Graham Rees, Bob Haycock, Jane Hodges, Steve Sutcliffe, Paddy Jenks and Richard Dobbins wrote the individual species accounts.  Annie Haycock then assembled the maps and texts into this volume.

The map below shows the tetrads covered in the 1984-88 atlas (in yellow) and 12 extra tetrads (blue dots) covered during the 2003-07 period.  These were all peripheral tetrads, either coastal or along the county boundary, and including only a small amount of land.

Population estimates

The 2003-07 Pembrokeshire breeding survey was deliberately undertaken using the same methodology as the previous 1984-88 survey, so that the two were directly comparable. It should, therefore prove useful in assessing biodiversity, species distribution changes and perhaps in evaluating the effects of changes in weather patterns over the period.

However, there are limitations to the information gathered by this kind of survey.  It is basically a presence or absence survey, with some additional value in terms of proving whether or not species was breeding throughout the area.  Nonetheless, it does give a reasonable indication of the spatial distribution of each species, and whether a species is localised, is widespread occurring in most tetrads, or is widespread but scattered.

The results take no account of time spent in the field in each tetrad, or of observer bias or competence. Figure 2 shows the number of species recorded in each tetrad in each atlas period (all species are included, whether or not they showed signs of breeding).  In the later period there appears to have been a shift away from the north, with more species recorded in the south-east and on the St. David's peninsula.  While some of this shift may be genuine, some of it is likely to be observer bias as people inevitably record closer to their home areas unless directed to do otherwise.

People were not asked to count birds whilst recording in tetrads during the main 2003-07 survey.  The limited population data collected as part of the BAP breeding survey applied to nature reserves and other special areas, and so was not directly applicable to the county as a whole. 

For the 1984-88 atlas, population estimates were compiled from survey results combined with extensive personal experience (of the authors) within the county (Donovan & Rees 1994). These estimates provided a baseline used to inform population estimates for the 2003-07 atlas. For example, an increase in the number of tetrads recorded for a species was assumed to have the same proportional increase in population. For a few species, e.g. Yellowhammer, anecdotal evidence indicated that has there has been a thinning out of the population, while for others, such as Chough, long term surveillance of nest sites showed there has been an increase in the breeding density, at least in some areas.  This approach therefore has limitations.

It will be noticed in the accounts for many species, that the results of the 1988-91 National Atlas  (Gibbons et al) have been used in testing the original estimates made following the pioneering 1984-88 local atlas.  For a few species, this has resulted in a revision of the original local population estimate and is explained in the individual species text.

The BTO/JNCC/RSPB Breeding Bird Survey (BBS), which came into being in 1994, also provides a useful tool for estimating populations. This survey is carried out nationally, and provides indices of the populations of birds in Britain in summer.  These indices are based on both the changes in numbers of each species counted along two parallel 1km transects in a 1km square, and on changes in the percentage of squares in which they occur. 

For most species in this atlas, a new population size has been estimated, based on a combination of data from the 1984-88 fieldwork, the 2003-07 distribution maps, the results from the 1988-91 National Atlas, and the BBS indices for Wales.  The current National Atlas (fieldwork in progress at the time of this publication), backed by extensive information from other bird research and survey, will undoubtedly become useful in further refining these population estimates in due course. This new information will be considered in the more comprehensive Pembrokeshire Avifauna.

For other species, notably seabirds, chough and peregrine, more specific data are collected annually and this allows a more detailed assessment of population size to be made. Seabirds on the Islands and the Castlemartin coast are counted annually for the Seabird Monitoring Programme administered by the JNCC (www.jncc.gov.uk/page-1550).  For all these species, there is more discussion about the population changes in the species accounts.

Density of recorded species in each atlas period

1984-88 density map. The smallest dots represent 2 species, the largest represent 86 species.  The counts include non-breeding species.

2003-07 density map. The smallest dots represent 2 species, the largest represent 81 species. The counts include non-breeding species.

The average number of species per tetrad is 35.

 

INTERPRETING THE SPECIES ACCOUNTS

For those species of particular conservation concern, the designation of red or amber-listing, or UK BAP or LBAP is given in the title line.  Further information about these designations is given in appendix III.

A brief introduction is given for each species, followed by comments about changes in distribution and population, and a discussion of problems with calculating such changes.

Maps are not reproduced for all species, where the breeding distribution is so limited that it can readily be expressed in the text, e.g. Gannet. For some scarcer and legally protected (Schedule I of the Wildlife and Countryside Act) species, maps are provided at a 10 kilometre square level.

For the majority of species, a table shows the total number of tetrads in which the species was found, plus the numbers of tetrads that registered “confirmed”, “probable” or “possible” breeding during each atlas period.  Note that for some species, for example rooks and other colonial nesting species, birds foraging in fields or in flight do not give any indication of the location of their nest sites, which may be some distance away, and therefore such "possible" breeding records have been excluded.  For other species, for example skylark, the distribution was based largely on birds singing on more than one date in the same place to show they are holding territory. In these instances the maps show mostly probable breeding.

Monday
May072012

Mute swan - 2003-07

Largely introduced into Pembrokeshire to grace ornamental waters, the mute swan has now become naturalised. Habitat requirement is for a supply of aquatic plants, sufficient room to be able to take off and a suitable bank or reed bed in which to place its bulky nest. Formerly nesting on saltings, this practice had ceased by the time of the 1984-88 survey. During the 2003-07 survey they had reoccupied this niche at Cosheston Pill, the Haroldston region of the Western Cleddau and the tidal upper limit of the Eastern Cleddau. Otherwise all nests were found on fresh waters.

Ten pairs were breeding in the county during the 1984-88 survey, 22 breeding pairs were found during the 2003-07 survey. The increase was accompanied by an expansion in distribution to the east and an increase in the number of pairs in the south of the county, particularly at Pembroke Mill Ponds.

Graham Rees

 

Fieldwork 2003-07 (based on 490 tetrads)

Red = breeding confirmed = 14

Orange = breeding probable = 5

Yellow = breeding possible = 4

Total tetrads in which registered = 23 (4.7%)