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<strong>English</strong> <strong>Heritage</strong><br />

<strong>Stonehenge</strong> <strong>Environmental</strong> <strong>Improvements</strong><br />

<strong>Project</strong><br />

Phase II Botanical Surveys<br />

September 2008


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


CONTENTS<br />

SUMMARY<br />

1.0 INTRODUCTION<br />

2.0 METHODOLOGY<br />

3.0 RESULTS<br />

4.0 EVALUATION<br />

TABLES<br />

1. Criteria used in evaluating the relative botanical importance of habitats<br />

2. Results of the evaluation process for Site V<br />

3. Results of the evaluation process for Site W<br />

4. Results of the evaluation process for Site X<br />

5. Results of the evaluation process for Site Y<br />

6. Results of the evaluation process for Site Z<br />

FIGURES<br />

1.1 Location of Sites and Areas Surveyed Within Sites<br />

APPENDICES<br />

A. Botanical survey results, site V<br />

B. Botanical survey results, site W<br />

C. Botanical survey results, site X<br />

D. Botanical survey results, site Y<br />

E. Botanical survey results, site Z<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


SUMMARY<br />

A botanical survey was undertaken of targeted habitats within the shortlisted site options for new visitor<br />

facilities, currently being considered for the <strong>Stonehenge</strong> <strong>Environmental</strong> <strong>Improvements</strong> <strong>Project</strong>. The aims<br />

of the survey were to identify the plant species and communities present and to evaluate these in relation<br />

to their nature conservation importance.<br />

The survey identified species and communities of arable fields, improved and semi-improved grassland,<br />

unimproved calcareous grassland, scrub and coniferous and broadleaved plantations. The areas of<br />

greatest value for nature conservation in terms of their flora were areas of unimproved calcareous<br />

grassland within sites W, X and Z, which were evaluated to be of local (W and X) and international (Z)<br />

importance. However, other areas also had some value, for example unimproved or semi-improved<br />

calcareous grassland at sites W and Z, old broadleaved plantation at site X and arable fields that support<br />

an uncommon arable weed species at sites X and Z.<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


1.0 INTRODUCTION<br />

1.1 Purpose of the Survey<br />

1.1.1 This report sets out the results of a botanical survey for the <strong>Stonehenge</strong> <strong>Environmental</strong><br />

<strong>Improvements</strong> <strong>Project</strong>. The purpose of this study is to inform a baseline against which the<br />

effects of development options and proposals can be assessed in relation to impacts on<br />

ecological and nature conservation resources..<br />

1.1.2 The scope of the study includes:<br />

• Identification of plant species and communities present within and around shortlisted site<br />

option Appraisal Areas; and<br />

• Evaluation of the identified plant species and communities in relation to their nature<br />

conservation importance.<br />

1.2 Study Area<br />

1.2.1 The Study Areas within and around the shortlisted site options for new visitor facilities 1 chosen<br />

for the purposes of the botanical surveys are shown on Figure 1.1.<br />

1<br />

The Future of <strong>Stonehenge</strong> – Public Consultation (<strong>English</strong> <strong>Heritage</strong>, July 2008)<br />

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Chris Blandford Associates


2.0 METHODOLOGY<br />

2.1 Field Survey<br />

2.1.1 Botanical surveys were carried out from May to July 2008, and the methodologies used are<br />

described below. The locations of sites and parts of sites are illustrated in Figure 1.1.<br />

2.1.2 Nomenclature for plant species follows Stace 2 , except where this differed within National<br />

Vegetation Classification community names 3 .<br />

2.1.3 In each area surveyed, all species identified were recorded and a broad indication of their<br />

frequency and abundance was given using the DAFOR scale. In addition, in many areas, a<br />

quadrat or quadrats of a size appropriate to the habitat or community (in accordance with<br />

guidelines set out in the ‘National Vegetation Classification: Users Handbook’ 4 ) were placed in<br />

homogenous and representative stands of the different vegetation types present. The species<br />

present within the quadrat(s), and their abundance, were recorded using the DOMIN scale.<br />

Notes were also taken of the general features of the area, its appearance and structure. Where<br />

possible the plant communities present have been referred to the most appropriate National<br />

Vegetation Classification (NVC) community 2 .<br />

2.2 Evaluation<br />

2.2.1 Habitats and communities were evaluated using a combination of criteria, guidance and<br />

frameworks, such as those outlined by Ratcliffe 5 , including size, diversity, naturalness, rarity,<br />

geographical position and fragility, the criteria for the selection of sites for SSSI designation 6 ,<br />

criteria for the selection of County Wildlife Sites in Wiltshire 7 , criteria for the selection of<br />

Important Arable Plant Areas 8 and Wiltshire Habitat Action Plans 9 . Further detail regarding the<br />

criteria used in evaluating habitats within the site is provided in Table 1.<br />

2.2.2 Species were evaluated using the red data list for vascular plant species 10 , Scarce Plants in<br />

Britain.<br />

2<br />

Stace C. 1997 New Flora of the British Isles second edition. Cambridge University Press.<br />

3<br />

Rodwell, J.S. (ed) et al 1991-2000. British Plant Communities Volumes 1-5. Cambridge University Press.<br />

4<br />

Rodwell J.S. 2006 National Vegetation Classification: Users Handbook. JNCC<br />

5<br />

Ratcliffe, D., 1977. A Nature Conservation Review, Volume 1. Cambridge University Press.<br />

6<br />

Nature Conservancy Council , 1989. Guidelines for selection of biological SSSIs. Nature Conservancy Council.<br />

7<br />

Wiltshire and Swindon Biological Record Centre, 2004. The County Wildlife Sites <strong>Project</strong>: Criteria for site selection, 3 rd draft.<br />

Wiltshire and Swindon Biological Record Centre,<br />

8<br />

Byfield, A. and Wilson, P. (2005). Important Arable Plant Areas: Identifying priority sites for arable plant conservation in the<br />

United Kingdom. Plantlife International, Salisbury, UK.<br />

9<br />

Wilkinson, S. (ed) 2008. Wiltshire Biodiversity Action Plan. Wiltshire Biodiversity Action Plan Steering Group.<br />

10<br />

Cheffings, C.M. and Farrel, L. (eds.), 2005. The Vascular Plants Red Data List for Great Britain. JNCC.<br />

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Table 1 Criteria used in evaluating the relative botanical importance of habitats<br />

Value<br />

Examples of Evaluation Criteria<br />

International Importance • High importance and rarity, international scale and limited potential for<br />

substitution;<br />

• A internationally designated site (Special Area of Conservation SAC, Special<br />

Protection Areas SPA);<br />

• Presence of Internationally rare species;<br />

• Woodland: Semi-Natural Ancient Woodland greater than 20ha including a<br />

combination of type stands;<br />

• Grassland: Unimproved and species-rich grassland greater than 0.5 ha including<br />

internationally rare habitats;<br />

• Arable sites with threshold scores of more than 90 points 11 .<br />

National Importance • High importance and rarity, national scale, or regional scale with limited<br />

potential for substitution;<br />

• A nationally designated site (Sites of Special Scientific Interest (SSSIs), National<br />

Nature Reserves (NNRs) etc.;<br />

• A viable area of a priority habitat identified in the UK BAP, or of smaller areas of<br />

such habitat which are essential to maintain the viability of a larger whole;<br />

• Woodland: Semi-Natural Ancient Woodland greater than 5ha;<br />

• Grassland: Unimproved grassland greater than 10 hectares; over 10 positive or<br />

unimproved grassland indicators;<br />

• Arable sites with threshold scores of 45-89 points.<br />

Regional Importance • High or medium importance and rarity, local or regional scale, and limited<br />

potential for substitution.<br />

• Any regularly occurring, locally significant population of a Nationally Scarce<br />

species (occurs in between 16 to 100 10km squares of the national grid) or in a<br />

Regional BAP or relevant Natural Area on account of its regional rarity or<br />

localisation; or<br />

• Woodland: Semi-Natural Ancient Woodland between 2 and 5ha;<br />

• Grassland: Unimproved grassland greater than 0.5 hectares, over 10 positive or<br />

unimproved grassland indicators.<br />

County Importance • High or medium importance and rarity, local or regional scale, and limited<br />

potential for substitution. A site designated as being of County Importance i.e.<br />

County Wildlife Site (CWS);<br />

• A viable area of Key Habitat identified in the County BAP;<br />

• Any regularly occurring locally significant population of a species which is listed<br />

in a County Red Data Book, BAP or County Rare Plant Register on account of its<br />

regional rarity or localisation;<br />

• A regularly occurring locally significant number of a County important species;<br />

• Woodland: Semi-Natural Ancient Woodland greater than 0.25 ha with 10 or<br />

more AWIS;<br />

• Grassland: Unimproved grassland greater than 0.5 hectare with 6 positive or<br />

unimproved grassland indicators;<br />

• Arable sites with threshold scores of 30-44 points. Vascular ;<br />

• Plants: According to KWT 2005 12 , >150 points (locally scarce or rare in County<br />

= 25 points).<br />

11<br />

Byfield, A. and Wilson, P. (2005). Important Arable Plant Areas: Identifying priority sites for arable plant conservation in the<br />

United Kingdom. Plantlife International, Salisbury, UK.<br />

12<br />

Kent Wildlife Trust, 2005 Local Wildlife Sites in Kent Criteria for Selection and Delineation. Kent Wildlife Trust.<br />

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Value<br />

Examples of Evaluation Criteria<br />

Local Importance • Low or medium importance and rarity, local scale;<br />

• A site designated as being of Local Importance by Oxford City Council i.e. a Site<br />

of Local Interest of Nature Conservation (SLINC);<br />

• Any regularly occurring, locally significant population of a species listed as being<br />

Locally Scarce which occurs in 100-500 10km squares in the UK;<br />

• Areas of habitat identified as being of Local Value in the relevant Natural Area<br />

profile;<br />

• Woodland: Semi-Natural Ancient Woodland/ Mature plantation smaller than<br />

0.25 ha with 3 or more AWIS;<br />

• Grassland: Unimproved or rich semi-improved grassland greater than 0.5 hectare<br />

with 3-4 unimproved grassland indicators;<br />

• Vascular Plants: According to KWT 2005, >100 points (locally scarce or rare in<br />

County = 25 points);<br />

Parish Importance • Low or medium importance and rarity, local scale;<br />

• Areas of habitat considered to appreciably enrich the habitat resource within the<br />

context of the Parish or Neighbourhood e.g. species-rich hedgerows/ or adjacent<br />

to habitat of County Value or above;<br />

• Area of woodland with 2 or more AWIS species, or >0.25ha of mature<br />

plantation/semi-natural woodland;<br />

• 1-3 unimproved grassland indicators;<br />

• Vascular Plants: According to KWT 2005, >50 points (locally scarce or rare in<br />

County = 25 points).<br />

Negligible Importance • Very low importance and rarity, local scale;<br />

• Sites or areas, which support few or no habitats, communities or species<br />

populations of nature conservation interest.<br />

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3.0 RESULTS<br />

3.1 General<br />

3.1.1 The locations of sites and parts of sites are illustrated in Figure 1.1. Appendices A-E summarise<br />

the results of the botanical survey for sites V to Z respectively.<br />

3.2 Site V<br />

3.2.1 The southern part of Site V comprises the existing car parking areas for <strong>Stonehenge</strong> (Appendix<br />

A, S). The southern part of this is largely under hard standing but verges and banks of speciespoor<br />

amenity grassland are present. These are dominated by perennial rye-grass Lolium<br />

perenne and a small number of other common species of such grasslands, such as daisy Bellis<br />

perennis Dandelion Taraxacum officinale agg. and white clover Trifloium repens, and is<br />

referable to the NVC community MG7 Lolium perenne-Trifolium repens perennial rye-grasswhite<br />

clover grassland. Shrubs, mostly hawthorn Crataegus monogyna are also present in some<br />

of the grassland. The northern part of the car park has larger areas of species-poor amenity<br />

grassland very similar to that in the southern part.<br />

3.2.2 Immediately to the north of the car park is a pasture of poor semi-improved grassland<br />

(Appendix A, N), which supports a range of grass species and a small number of common<br />

grassland herbs.<br />

3.3 Site W<br />

Arable<br />

3.3.1 E 3 is an arable field. The arable weed flora is very species-poor and sparse throughout the<br />

majority of the field, although localised patches with a more species-rich and abundant<br />

community are present on some of the margins and corners, particularly the south west corner<br />

(where the quadrat was located). This supports a range of common arable weed species, such<br />

as barren brome Anisantha sterilis, common mouse-ear Cerastium fontanum, common poppy<br />

Papaver rhoeas, field pansy Viola arvensis and field speedwell Veronica persica, and is best<br />

referred to the NVC community OV3 Papaver rhoeas-Viola arvensis common poppy-field pansy<br />

community.<br />

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Grassland<br />

3.3.2 W3 is a species-poor improved or semi-improved pasture supporting a limited range of<br />

common grassland species that is referable to the NVC community MG6 Lolium perenne-<br />

Cynosorus cristatus perennial rye-grass-crested dog’s-tail grassland.<br />

3.3.3 E1 forms the banks of the track that bisects the Site from north to south. Although of variable<br />

species-richness they consist of coarse-grained unimproved calcareous grassland dominated by<br />

upright brome Bromopsis erecta, referable to the NVC community CG3 Bromus erectus upright<br />

brome grassland, and which is typical of low levels of grazing or cutting. Other species present<br />

that are characteristic of such grasslands include bird’s-foot trefoil Lotus corniculatus, greater<br />

knapweed Centaurea scabiosa and the Red Data Book Near Threatened species sanfoin<br />

Onobrychis vicifolia.<br />

3.3.4 E4 is a small species poor pasture referable to the NVC community MG7 Lolium perenne-<br />

Trifolium repens perennial rye-grass-white clover grassland.<br />

Plantations<br />

3.3.5 W1, W2 and E2 are coniferous plantations that are very similar in species composition. The<br />

canopy is dominated by Scot’s pine Pinus sylvestris and the shrub layer is variable in density,<br />

with hawthorn and elder Sambucus nigra the most common species. The field layer is speciespoor<br />

and quite grassy in places, although bramble Rubus fruticosus agg. is patchily abundant.<br />

The field layer includes very few characteristic woodland species. The woodland as a whole is<br />

not referable to an NVC community, although the shrub layer could be referred to W21<br />

Crataegus monogyna-Hedera helix hawthorn-ivy scrub.<br />

3.4 Site X<br />

Road verges<br />

3.4.1 The verges of the A344 comprise of relatively species-poor grassland dominated by false oatgrass<br />

Arrhernatherum elatius, referable to the NVC community MG1 Arrhernatherum elatius<br />

false oat-grass grassland.<br />

South Western Quadrant<br />

3.4.2 SW1 is a small area of species-rich unimproved calcareous grassland referable to the NVC<br />

community CG2 Festuca ovina-Avenula pratensis sheep’s fescue-meadow oat grass grassland. It<br />

September 2008 6 Phase II Botanical Surveys<br />

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supports a good range of characteristic species, including sheeps fescue Festuca ovina, upright<br />

brome, crested harir-grass Koeleria macrantha, meadow oat-grass Helictotrichon pratensis,<br />

dwarf thistle, Cirsium acaule, horseshoe vetch Hippocrepis comosa, salad burnet Sanguisorbia<br />

minor and common thyme Thymus polytrichus. It appears to be maintained by relatively heavy<br />

rabbit grazing, and this is reflected in the relatively high frequency of common ragwort Senecio<br />

jacobea and the presence of the Red Data Book Near Threatened species hounds-tongue<br />

Cynoglossum officinale. Scrub is present around the edges of the grassland, which includes<br />

hawthorn, wild privet Ligustrum vulgare, buckthorn Rhamnus catharticus and elder.<br />

3.4.3 SW2 is species-poor improved grassland (NVC MG7) dominated by a very small number of<br />

common grasses and herbs, such as soft brome Bromus hordaceous, perennial rye-grass, white<br />

clover and dandelion.<br />

South Eastern Quadrant<br />

3.4.4 SE1 is a developing broadleaved plantation that forms a southern extension of the Fargo<br />

Pantation. It has a canopy dominated by sycamore Acer pseudoplatanus, although beech Fagus<br />

sylvatica and ash Fraxinus excelsior are also present. Except on the edges there is little in the<br />

way of a shrub layer, although elder is locally abundant in the centre (and appears likely to<br />

pre-date the plantation). The field layer is species-poor with very few characteristic woodland<br />

species, and is patchily dominated by, for example, rough-meadow grass Poa trivialis and nettle<br />

Urtica dioica.<br />

3.4.5 SE2 is an area of developing grassland on an ex-arable field. The sward is patchy, with frequent<br />

bare patches which support a range of common arable weed species. Sheep’s fescue and<br />

upright brome are the most common grass species, with sanfoin, ribwort plantain Plantago<br />

lanceolata and white clover. With time this grassland may develop into CG2 or CG3 grassland,<br />

although many of the characteristic species are not currently present.<br />

North Eastern Quadrant<br />

3.4.6 NE1 is a plantation, of which the southern part has a canopy dominated by sycamore and ash.<br />

The shrub layer is variable in density with hazel Corylus avellana the most abundant species.<br />

The field layer is moderately species-rich and supports a number of woodland species such as<br />

wood speedwell Veronica montana and dog violet Viola riviniana. Although it is likely that this<br />

area was originally a plantation, it has now developed a relatively semi-natural structure and<br />

can be considered a relatively species-poor example of the NVC community W8 Fraxinus<br />

excelsior-Acer campestre-Mercurailis perennis ash-field maple-dog’s mercury woodland.<br />

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3.4.7 The northern part of NE1 is broadly similar in species composition, although (rather sickly<br />

looking) pine Pinus sp. forms an abundant component of the canopy here.<br />

3.4.8 NE2 is an area of relatively species-poor grassland that has developed on an area previously<br />

occupied by part of the Fargo Plantation.<br />

North Western Quadrant<br />

3.4.9 NW1 includes a number of different habitats and communities. The south western part is<br />

unimproved calcareous grassland very similar to that within SE1 on the southern side of the<br />

A344. The tumulus in the north eastern part supports species-poor grassland dominated by<br />

false oat-grass, and scrub is present in the north western corner and along the southern edge.<br />

3.4.10 NW2 is an arable field in which the arable weed flora is generally sparse and species-poor,<br />

although this is more abundant and species-rich on the margins and in corners. Here a range of<br />

common arable weed species are present, of which field speedwell, field forget-me-not<br />

Myosotis arvensis, cut-leaved crane’s-bill Geranium dissectum and field pansy are<br />

conspicuous. Of note is the presence of a small number of plants of the Red Data Book Near<br />

Threatened species dwarf spurge Euphorbia exigua. The community is best referred to the NVC<br />

community OV15 Anagallis arvensis-Veronica persica scarlet pimpernel-field speedwell<br />

community.<br />

3.5 Site Y<br />

Road Verges<br />

3.5.1 Grassy road verges (C) are present on either side of both the A344/A360/B3086. These are<br />

relatively similar in structure and species composition throughout. They are mostly speciespoor<br />

and dominated by false oat-grass. However, some areas, particularly where false oat-grass<br />

is less abundant, are more species-rich, including a number of species characteristic of<br />

unimproved calcareous grasslands, such as upright brome, common knapweed and burnet<br />

saxifrage Pimpinella saxifraga. These grasslands can be referred to the NVC community MG1<br />

Arrhernatherum elatius false oat-grass grassland. Small plantations of beech are present on the<br />

northern side of the A344, either side of the Airman’s Corner junction.<br />

North Western and South Western Quadrants<br />

3.5.2 NW and SW are arable fields. At the time of survey the crop in NW was at a relatively early<br />

stage of development so the arable weed flora was distributed more or less throughout the<br />

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field. It comprised a range of typical arable weed species, including black bindweed Fallopia<br />

convulvulus, shepherd’s purse Capsella bursa-pastoris, common fumitory Fumaria officinalis,<br />

field and grey speedwell Veronica persica and polita, and can be referred to the NVC<br />

community OV7 Veronica persica-Veronica polita field speedwell- grey speedwell community.<br />

3.5.3 The crop within SW was more fully developed and as a consequence the arable weed flora<br />

was very limited in extent and confined to small field margins and corners. It was broadly<br />

similar in species composition to that within NW, although some species, such as black grass<br />

Alopecurus myosuroides, cut-leaved crane’s-bill and ivy-leaved speedwell, that were absent<br />

from NW were present in relative abundance in SW.<br />

3.5.4 There is a recently planted relatively species-poor hedge dominated by hawthorn between the<br />

field in SW and the adjoining road verges of the A360/B3086.<br />

South Eastern and North Eastern Quadrants<br />

3.5.5 SE and NE comprise very species-poor grasslands dominated by perennial rye-grass and<br />

cocksfoot Dactylis glomerata respectively, which can be referred to the NVC community MG7<br />

Lolium perenne-Trifolium repens perennial rye-grass-white clover grassland.<br />

3.6 Site Z<br />

Road verges<br />

3.6.1 Grassy road verges are present on either side of the B3086 and the Packway that are broadly<br />

similar in structure and species composition throughout. They are relatively species-poor NVC<br />

community MG1 Arrhernatherum elatius false oat-grass grassland. Small amounts of scrub,<br />

including bramble and blackthorn are also patchily present and trees have been planted on the<br />

northern side of the Packway to the south of Rollestone Camp.<br />

South Western and South Eastern Quadrants<br />

3.6.2 SW and SE are arable fields with very similar arable weed floras, which were largely confined<br />

to field margins and corners. The most abundant species throughout is cut-leaved crane’s-bill,<br />

although a range of other species is present, including barren brome, cleavers Galium aparine,<br />

thistles Cirsium spp., common poppy and knotgrass Polygonum aviculare. Of note was the<br />

presence of a small population of the Red Data Book Near Threatened species dwarf spurge<br />

Euphorbia exigua in the north western corner of NW.<br />

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North Eastern Quadrant<br />

3.6.3 NE1 is an area of apparently ungrazed unimproved calcareous grassland with scattered scrub.<br />

The grassland is dominated by upright brome and, although variable in species-richness and<br />

relatively course-grained, it still retains a good range of species characteristic of unimproved<br />

calcareous grasslands, including the Red Data Book Near Threatened species sanfoin. It can be<br />

referred to the NVC community CG3 Bromus erectus upright brome grassland. There are a<br />

number of patches in which Canadian goldenrod is locally dominant, particularly in the south<br />

western corner. The scrub is variable in density, but there are still many areas of open<br />

grassland. However, the presence of shrub seedlings and young plants in the sward indicates<br />

that scrub is continuing to develop and increase within the compartment, at the expense of the<br />

grassland. Hawthorn is the most abundant shrub species and bramble is locally abundant.<br />

3.6.4 NE2 was surveyed only from its southern and western boundaries and appears to be a semiimproved<br />

grassland in which crested dog’s tail Cynosorus cristatus, cocksfoot, perennial ryegrass,<br />

bulbous buttecup Ranunculus bulbosus and daisy are all frequent or abundant. A small<br />

number of species characteristic of unimproved calcareous grassland are present, including<br />

upright brome and salad burnet. It can best be referred to the NVC community MG6 Lolium<br />

perenne-Cynosorus cristatus perennial rye-grass-crested dog’s-tail grassland.<br />

North Western Quadrant<br />

3.6.5 NW comprises closely mown grassland within Rollestone Camp. It is variable in species<br />

composition but is mostly intermediate between unimproved calcareous grassland (CG2<br />

Festuca ovina-Avenula pratensis sheep’s fescue-meadow oat grass grassland) and more<br />

improved amenity type swards (MG6 Lolium perenne-Cynosorus cristatus perennial rye-grasscrested<br />

dog’s-tail grassland). A number of small areas on banks associated with structures set<br />

within the grassland support a more unimproved form of calcareous grassland which is<br />

referable to the NVC community CG2 Festuca ovina-Avenula pratensis sheep’s fescue-meadow<br />

oat grass grassland.<br />

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4.0 EVALUATION<br />

4.1 Site V<br />

4.1.1 Table 2 summarises the results of the evaluation of nature conservation value for the areas<br />

within Site V in terms of their flora.<br />

Table 2 Results of the evaluation process for Site V<br />

Area<br />

Importance<br />

(see Table 1)<br />

Comments<br />

S Negligible Small areas of species poor grassland with species-poor shrubs/scrub.<br />

N Negligible Species poor grassland<br />

4.2 Site W<br />

4.2.1 Table 3 summarises the results of the evaluation of nature conservation value for the areas<br />

within Site W in terms of their flora.<br />

Table 3 Results of the evaluation process for Site W.<br />

Area<br />

Importance<br />

(see Table 1)<br />

Comments<br />

W1 Parish Relatively varied shrub layer and moderate range of species.<br />

W2 Parish Relatively varied shrub layer and moderate range of species.<br />

W3 Negligible Species-poor grassland<br />

E1 Local Unimproved calcareous grassland with a range of characteristic species.<br />

E2 Parish Relatively varied shrub layer and moderate range of species.<br />

E3 Negligible<br />

Arable weed flora comprising common species, and of very limited<br />

extent.<br />

E4 Negligible Species-poor grassland<br />

4.3 Site X<br />

4.3.1 Table 4 summarises the results of the evaluation of nature conservation value for the areas<br />

within Site X in terms of their flora.<br />

Table 4 Results of the evaluation process for Site X.<br />

Area<br />

Importance<br />

(see Table 1)<br />

Comments<br />

C Negligible Species-poor grassland<br />

SW1<br />

Local<br />

Species-rich unimproved calcareous grassland, which represents one of<br />

the few areas of semi-natural habitat within the <strong>Stonehenge</strong> area.<br />

SW2 Negligible Species-poor grassland<br />

SE1 Negligible Species-poor plantation<br />

September 2008 11 Phase II Botanical Surveys<br />

11108605R_Botanical_DW_09-08<br />

Chris Blandford Associates


Area<br />

Importance<br />

(see Table 1)<br />

Comments<br />

SE2 Negligible Species-poor grassland, though has potential to increase in value.<br />

NE1<br />

Parish<br />

Moderately species-rich (including small number of ‘woodland species)<br />

old broadleaved plantation that has developed semi-natural structure.<br />

NE2 Negligible Species-poor grassland<br />

NW1 Local<br />

Includes an area of species-rich unimproved calcareous grassland, which<br />

represents one of the few areas of semi-natural habitat within the<br />

<strong>Stonehenge</strong> area.<br />

NW2 Parish<br />

Arable weed flora comprising common species, and of very limited<br />

extent. However, Red data Book Near Threatened dwarf spurge present.<br />

4.4 Site Y<br />

4.4.1 Table 5 summarises the results of the evaluation of nature conservation value for the areas<br />

within Site Y in terms of their flora.<br />

Table 5 Results of the evaluation process for Site Y.<br />

Area<br />

C<br />

SW<br />

Importance<br />

(see Table 1)<br />

Parish<br />

Negligible<br />

Comments<br />

Mostly species-poor grassland, but with some more species-rich parts<br />

supporting number of species of unimproved calcareous grassland.<br />

Arable weed flora comprising common species, and of very limited<br />

extent.<br />

SE Negligible Species-poor grassland.<br />

NE Negligible Species-poor grassland.<br />

NW Negligible Arable weed flora comprising common species.<br />

4.5 Site Z<br />

4.5.1 Table 6 summarises the results of the evaluation of nature conservation value for the areas<br />

within Site Z in terms of their flora.<br />

Table 6 Results of the evaluation process for Site Z.<br />

Area<br />

Importance<br />

(see Table 1)<br />

Comments<br />

C Negligible Species-poor grassland<br />

SW Negligible<br />

Arable weed flora comprising common species, and of very limited<br />

extent.<br />

SE<br />

Parish<br />

Arable weed flora comprising common species, and of very limited<br />

extent. However, Red Data Book Near Threatened dwarf spurge present.<br />

NE1 International<br />

Relatively species-rich unimproved calcareous grassland that forms part<br />

of the Salisbury Plain Special Area of Conservation (designated under<br />

European law) and Site of Special Scientific Interest (designated under<br />

UK law).<br />

NE2 International<br />

Semi-improved grassland that forms part of the Salisbury Plain Special<br />

Area of Conservation (designated under European law) and Site of<br />

Special Scientific Interest (designated under UK law).<br />

NW<br />

Parish<br />

Mostly semi-improved grassland, but includes significant elements of<br />

unimproved calcareous grassland.<br />

September 2008 12 Phase II Botanical Surveys<br />

11108605R_Botanical_DW_09-08<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


APPENDIX A<br />

BOTANICAL SURVEY RESULTS, SITE V<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


Area S N<br />

Habitat<br />

Amenity<br />

grass and<br />

shrubs<br />

Poor semiimproved<br />

grassland<br />

DAFOR or DOMIN DAFOR DAFOR<br />

NVC Communities<br />

MG7<br />

W21<br />

Species<br />

Crataegus monogyna Hawthorn D<br />

Ligustrum vulgare Wild privet R<br />

Prunus domestica Plum R<br />

Rhamnus cathartica Buckthorn R<br />

Sambucus nigra Elder R<br />

MG7<br />

Arrhenatherum elatius False oat-grass O<br />

Bromopsis erectus Upright brome O<br />

Bromus hordeaceus Soft brome F/LA<br />

Dactylis glomerata Cocksfoot F F/LA<br />

Festuca rubra Red fescue F/LA<br />

Helictotrichon pubescens Downy oat-grass R<br />

Holcus lanatus Yorkshire fog O<br />

Lolium perenne Perennial rye-grass D O<br />

Poa annua Annual meadow-grass F LA<br />

Poa pratensis Smooth meadow-grass O F/LA<br />

Achillea millefolium Yarrow R<br />

Bellis perennis Daisy O F<br />

Cerastium fontanum Common mouse-ear O<br />

Cirsium vulgare Spear thistle O<br />

Glechoma hederacea Ground ivy R O<br />

Plantago lanceolata Ribwort plantain R<br />

Plantago major Greater plantain R<br />

Ranunculus bulbosus Bulbous buttercup O F<br />

Taraxacum officinale agg. Dandelion O O<br />

Trifolium repens White clover O F/LA<br />

Urtica dioica Nettle R<br />

Veronica chamaedrys Germander speedwell R<br />

Veronica serpillifolium Thyme-leaved speedwell R<br />

DAFOR scale<br />

D Dominant<br />

A Abundant<br />

F Frequent<br />

O Occasional<br />

R Rare<br />

L Locally<br />

Domin scale<br />

10 91-100% cover<br />

9 76-90% cover<br />

8 51-75% cover<br />

7 34-50%cover<br />

6 26-33% cover<br />

5 11-25% cover<br />

4 4-10% cover<br />

3


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


APPENDIX B<br />

BOTANICAL SURVEY RESULTS, SITE W<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


Area E3<br />

W3<br />

E4<br />

E1<br />

W1 W2 E2<br />

Unimproved<br />

Improved<br />

calcareous<br />

Coniferous Coniferous Coniferous<br />

Habitat Arable Improved grassland grassland<br />

grassland<br />

plantation plantation plantation<br />

DAFOR or DOMIN DAFOR DOMIN DAFOR DOMIN DAFOR DAFOR DAFOR DAFOR DAFOR<br />

NVC Communities<br />

MG7/<br />

Species<br />

OV3 OV3 Species<br />

MG6 MG6 OV23 Species<br />

CG3d Species<br />

NA NA NA<br />

Alopecurus myosuroides Black grass R 2 Anisantha sterilis Barren brome R Crataegus monogyna Hawthorn R Acer pseudoplatanus Sycamore R<br />

Anisantha sterilis Barren brome O/LA 5 Arrhenatherum elatius False oat-grass R O/LA Rubus fruticosus agg. Bramble O Fraxinus excelsior Ash R<br />

Arrhenatherum elatius False oat-grass R Dactylis glomerata Cocksfoot F 6 F/LA Sambucus nigra Elder R Larix decidua Eurpoean larch O R<br />

Poa annua Annual meadow-grass F Festuca rubra Red fescue F/LA O Pinus sylvestris Scots pine D D D<br />

Poa trivialis Rough meadow-grass R 4 Holcus lanatus Yorkshire fog R Arrhenatherum elatius False oat-grass F/LA Sorbus aucuparia Rowan R R<br />

Lolium perenne Perennial rye-grass R F/LA Bromopsis erectus Upright brome A Sorbus intermedia Swedish whitebeam R<br />

Anagallis arvensis Scarlet pimpernel R 1 Phleum bertolonii Small cat's-tail A 5 Dactylis glomerata Cocksfoot O Taxus baccata Yew O<br />

Arctium minus Lesser burdock R Poa trivialis Rough meadow grass F/LA 6 Fetuca ovina Sheeps fescue F<br />

Cerastium fontanum Common mouse-ear R 3 Poa pratensis Smooth meadow-grass F Crataegus monogyna Hawthorn F F A<br />

Cirsium vulgare Spear thistle R Anagallis arvensis Scarlet pimpernel R Ilex aquifolium Holly R<br />

Euphorbia helioscopa Sun spurge R/LO 1 Carduus nutans Musk thistle LO Achillea millefolium Yarrow R Ligustrum vulgare Wild privet R<br />

Fumaria officinalis Common fumitory R Centaurium erythrea Common centaury R Agrimonia eupatoria Common agrimony R Prunus spinosa Blackthorn O<br />

Galium aparine Cleavers O 1 Cerastium fontanum Common mouse-ear O Anthriscus sylvestris Cow parsley O/LA Rhamnus cathartica Buckthorn O O<br />

Geranium dissectum Cut-leaved crane's-bill R 1 Cirsium arvense Creeping thistle O Centaurea scabiosa Greater knapweed O Rosa canina Dog rose O R O<br />

Geranium pyrenaicum Hedgerow crane's-bill R Cirsium vulgare Spear thistle R R Cirsium acaule Dwarf thistle R Rubus fruticosus Bramble F/LA A/LD O/LA<br />

Geranium robertianum Herb Robert R Daucus carota Wild carrot R Cirsium vulgare Spear thistle O Rubus idaeus Raspberry R<br />

Geum urbanum Wood avens R Erodium cicutarium Common stork's-bill R Galium aparine Cleavers O Sambucus nigra Elder F F F<br />

Hypericum perforatum Perforate St. John's wort R Galium verum Lady's bedstraw R Galium verum Lady's bedstraw R Ulmus glabra Wych elm R<br />

Lamium album White deadnettle R Geranium dissectum Cut-leaved crane's-bill R Geranium dissectum Cut-leaved crane'sbill R Viburnum lantana Wayfaring tree R<br />

Lamium purpureum Red deadnettle R/LF 1 Geranium molle Doves-foot crane's-bill O Geranium pyrenaicum Hedgerow crane'sbill R<br />

Myosotis arvensis Field forget-me-not R/LF 4 Geum urbanum Wood avens R Hypericum perforatum Perforate St. John's wort R Hedera helix Ivy R<br />

Papaver rhoeas Common poppy O 2 Hypochaeris radicata cat's-ear R Knautia arvensis Field scabious O<br />

Persicaria aviculare Knotgrass O Leontodon autumnalis Autumn hawkbit O Lamium album White deadnettle R Dryopteris dilatata Broad buckler fern R<br />

Senecio vulgaris Groundsel R Linaria vulgaris Common toadflax R Lamium maculatum Red deadnettle R<br />

Silene alba White campion R Medicago lupulina Black medick O Lathyrus pratensis Meadow vetchling R Anisantha sterilis Barren brome F F/LA R<br />

Sonchus asper Prickly sowthistle O/LA 4 Myosotis arvensis Field forget-me-not R Linaria vulgaris Toadflax R Arrhenatherum elatius False oat-grass F/LA R R<br />

Sonchus oleraceous Smoth sowthistle R/LF 3 Ranunculus bulbosus Bulbous buttercup R Lotus corniculatus Bird's-foot trefoil F Brachypodium sylvaticum False brome R<br />

Stellaria media Chickweed O/LA 4 Rumex crispus Curled dock R Medicago lupulina Black medick O Bromus erectus Upright brome R R<br />

Taraxacum officinale agg. Dandelion R 1 Rumex obtusifolius broad-leaved dock R Onobrychis vicifolia Sanfoin F Dactylis glomerata Cocksfoot F/LA<br />

Urtica dioica Nettle R 1 Senecio jacobea common ragwort R Ononis repens Restharrow O Festuca rubra Red fescue R<br />

Veronica arvensis Wall speedwell O/LF 3 Silene alba White campion R Plantago lanceolata Ribwort plantain O Poa annua Annual meadow-grass LF<br />

Veronica persica Field speedwell F/LA 5 Sonchus asper prickly sowthistle O Ranunculus bulbosus Bulbous buttercup O Poa trivialis Rough meadow-grass LA<br />

Viola arvensis Field pansy O/LF 5 Taraxacum officinale agg. Dandelion O Sanguisorbia minor Salad burnet R<br />

Torilis japonica Upright hedge-parsley R Senecio jacobaea Ragwort O Agrimonia eupatoria Common agrimony R<br />

Crop 7 Trifolium pratense Red clover O Taraxacum officinale agg. Dandelion O Anthriscus sylvestris Cow parsley O<br />

Trifolium repens White clover F 4 F Trifolium pratense Red clover R Arctium minus Lesser burdock R<br />

Urtica dioica Nettle O/LF O/LA Trifolium repens White clover O Cicerbita macrophylla Blue sowthistle R<br />

Veronica arvensis Wall speedwell R Urtica dioica Nettle O Cirsium arvense Creeping thistle F/LA<br />

Veronica chamaedrys germander speedwell R Vicia cracca Tufted vetch R Cirsium vulgare Spear thistle R R<br />

Veronica persica Field speedwell F 3 Vicia sativa Common vetch R Conium maculatum Hemlock R<br />

Dipsacus fullonum Teasel R<br />

Positive indicator for unimproved calcareous grassland (National Vegetation Classification communities CG2, 3, 4 and 5) Galium aparine Cleavers F/LA F/LA O<br />

Red Data Book Near Threatened Geranium robertianum Herb Robert O R O/LA<br />

Geum urbanum Wood avens O O O<br />

DAFOR scale Domin scale Glechoma hederacea Ground ivy O R O/LA<br />

D Dominant 10 91-100% cover Heracleum sphondyllium Hogweed O<br />

A Abundant 9 76-90% cover Lamium album White deadnettle R<br />

F Frequent 8 51-75% cover Myosotis arvensis Field forget-me-not R<br />

O Occasional 7 34-50%cover Senecio jacobaea Ragwort R<br />

R Rare 6 26-33% cover Silene vulgaris Bladder campion R<br />

L Locally 5 11-25% cover Solanum dulcamara Bittersweet O F<br />

4 4-10% cover Taraxacum officinale agg. Dandelion O<br />

3


APPENDIX C<br />

BOTANICAL SURVEY RESULTS, SITE X<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


Area C SW1 SW2 SE1 SE2 NE1 NE2 NW1 NW2<br />

Poor semiimproved<br />

grassland<br />

Unimproved<br />

calcareous<br />

grassland<br />

Poor semiimproved<br />

grassland<br />

Poor semiimproved<br />

grassland Scrub Arable<br />

Improved<br />

Broadleaved Poor semi-improved<br />

Arable Arable<br />

Habitat<br />

Scrub grassland Broadleaved plantation<br />

plantation grassland<br />

(margin) (corner)<br />

DAFOR or DOMIN DAFOR DAFOR DOMIN DAFOR DAFOR DAFOR DOMIN DAFOR DAFOR DOMIN DAFOR DOMIN DAFOR DAFOR DAFOR DOMIN DOMIN<br />

NVC Communities<br />

MG1 CG2d CG2d W21 MG7 NA NA MG6c/CG3 W8 MG1/MG6 MG1 W21 OV15<br />

Species<br />

Acer pseudoplatanus Sycamore D 8 (3, sdlngs) F/LA 7 O<br />

Betula pendula Silver birch R O 4 R<br />

Fagus sylvatica Beech O 4 R<br />

Fraxinus excelsior Ash F 7 F/LA 7 R<br />

Malus sp. Apple species R<br />

Pseiodotsuga mensiezii Douglas fir R<br />

Pinus sp. Pine sp. LA<br />

Tilia cordata Small-leaved lime R<br />

Cornus sanguinea Dogwood O<br />

Corylus avellana Hazel O A 7 O O<br />

Crataegus monogyna Hawthorn F O O 1 O A<br />

Euonymus europaeus Spindle O O R R<br />

Ligustrum vulgare Wild privet O R A<br />

Rhamnus catharticus Buckthorn O R<br />

Rubus fruticosus agg. Bramble O F/LA 1 O/LA A/LD<br />

Sambucus nigra Elder O F/LA 4 R O/LA<br />

Viburnum lantana Wayfaring tree O R<br />

Viburnum opulus Guelder rose O<br />

Hedera helix Ivy O/LA<br />

Agrostis stolonifera Creeping bent F/LA 4<br />

Anisantha sterilis Barren brome O O O<br />

Anthoxanthum odoratum Sweet vernal-grass R<br />

Arrhenatherum elatius False oat-grass D O/LA 3 D R 2<br />

Brachypodium sylvaticum Wood false brome O R<br />

Briza media Quaking grass O R<br />

Bromopsis erectus Upright brome F 3 F/LA<br />

Bromus hordaceous Soft brome O O A O O<br />

Dactylis glomerata Cocksfoot O R O F 4 R<br />

Festuca ovina Sheeps fescue A 8 F O<br />

Festuca rubra Red fesce F/LA A 8<br />

Helictotrichon pratensis Meadow oat-grass O<br />

Helictotrichon pubescens Downy oat-grass O<br />

Holcus lanatus Yorkshire fog O R F/LA 3 R<br />

Koeleria macrantha Crested hair-grass O 2<br />

Lolium perenne Perennial rye-grass R F O<br />

Poa annua Annual meadow-grass O O R<br />

Poa trivialis Rough meadow-grass A F/LA 3 O O<br />

Carex flacca Glaucus sedge F 3<br />

Carex spicata Spiked sedge R<br />

Achillea millefolium Yarrow F 3<br />

Anagalia arvensis Scarlet pimpernel LF 3<br />

Aphanes arvensis Parsley-piert R<br />

Arctium minus Lesser burdock R R R<br />

Artemisia vulgaris Mugwort R<br />

Arum maculatum Lords and ladies R O<br />

Bellis perennis Daisy O<br />

Bryonia dioica White bryony R<br />

Centaurea scabiosa Greater knapweed R F 3<br />

Cerastium fontanum Common mouse-ear O O O F O<br />

Chamanerion minus Small toadflax R 1<br />

Cirsium acaule Dwarf thistle O 3 O<br />

Cirsium arvense Creeping thistle F/LA R R R LA F 1 O 1<br />

Cirsium vulgare Spear thistle R R<br />

Conium maculatum Hemlock R R<br />

Convulvulus arvensis Field bindweed F<br />

Crepis vesicaria Beaked hawks-beard R R<br />

Cynoglossum officinale Hounds tongue R R<br />

Epilobium sp. Willowherb sp. R<br />

Euphorbia exigua Dwarf spurge R<br />

Fallopia convulvulus Black bindweed LF 4<br />

Filipendula vulgaris Dropwort R 3<br />

Fumaria officinalis Common fumitory O 3<br />

Galium aparine Cleavers O F/LA 1 O O/LF O<br />

Galium mollugo Hedge bedstraw O<br />

Galium verum Lady's bedstraw F 4 R<br />

Gentianella amarella Autumn gentian R<br />

Geranium dissectum Cut-leaved crane's-bill R F 3<br />

Geranium robertianum Herb robert F/LA 6<br />

Geranium sp. Crane's-bill sp. R<br />

Geum urbanum Wood avens O 2 F/LA 5 R<br />

Glechoma hederacea Ground ivy F 3 F/LA 4 O/LA O 1 O/LF<br />

Helianthemum nummularium Common rock rose A R<br />

Heracleum sphodylium Hogweed O<br />

Hieracium pilosella Mouse-eared hawkweed F/LA<br />

Hippocrepis comosa Horseshoe vetch F/LA 5<br />

Hypericum perforatum Perforate St. John's wort R<br />

Lamium album White deadnettle O F F/LA O<br />

Lamium purpureum Red deadnettle R<br />

Lapsana communis Nipplewort O<br />

Leontodon autumnalis Autumn hawkbit F 1<br />

Leontodon hispidus Rough hawkbit O 2<br />

Lepidium draba Hoary cress R<br />

Leucanthemum vulgare Ox-eye daisy R<br />

Linaria vulgaris Toadflax R R R<br />

Linum catharticum Fairy flax O 3<br />

Lotus corniculatus Birds-foot trefoil F/LA O<br />

Medicago lupulina Black medick O 1 O O 1<br />

Myosotis arvensis Field forget-me-not R O R O O/LF F 3<br />

Onobrychis vicifolia Sanfoin F/LA<br />

Pastinaca sativa Wild parsnip O O O<br />

Plantago lanceolata Ribwort plantain O F 3 F/LA F 3 R<br />

Plantago media Hoary plantain R R<br />

Potentilla reptans Cinquefoil F/LA O/LF<br />

Prunella vulgaris Self-heal F 3<br />

Ranunculus bulbosus Bulbous buttercup R O F R<br />

Rumex acetosa Common sorrel R R<br />

Rumex obtusifolius broad-leaved dock R R<br />

Rumex sanguineus Wood dock R<br />

Sanguisorbia minor Salad burnet F 3<br />

Scabiosa columbaria Small scabious R<br />

Senecio jacobaea Ragwort F 2 O F 1<br />

Senecio vulgaris Groundsel R R<br />

Sherardia arvensis Field madder R F 2<br />

Silene alba White campion F R O R R R<br />

Silene vulgaris Bladder campion R<br />

Sissymbrium officinale Hedge mustard O 3<br />

Sonchus arvensis Perennial sowthistle R<br />

Sonchus asper Prickly sowthistle R F 1 1<br />

Succisa pratensis Devil's-bit scabious R<br />

Taraxacum officinale agg. Dandelion F 3 A O F F<br />

Thymus polytrichus Common thyme O/LA<br />

Trifolium pratense Red clover R 1<br />

Trifolium repens White clover R F/LA F/LA F 2<br />

Urtica dioica Nettle F/LA F/LA F/LD 9 F/LA 4 O/LD<br />

Verbascum thapsus Mullein R<br />

Veronica arvensis Wall speedwell R<br />

Veronica chamaedrys Germander speedwell F/LA 3 O O<br />

Veronica hederifolia Ivy-leaved speedwell F 1 O/LF<br />

Veronica montana Wood speedwell O<br />

Veronica persica Field speedwell R F/LA 4 5<br />

Vicia cracca Tufted vetch R<br />

Viola arvensis Field pansy R LF 2<br />

Viola hirta Hairy violet O<br />

Viola odorata Sweet violet R<br />

Viola riviniana Dog violet O<br />

DAFOR scale Domin scale Positive indicator for unimproved calcareous grassland (National Vegetation Classification communities CG2, 3, 4 and 5)<br />

D Dominant 10 91-100% cover Red Data Book Near Threatened<br />

A Abundant<br />

9 76-90% cover<br />

F Frequent<br />

8 51-75% cover<br />

O Occasional<br />

7 34-50%cover<br />

R Rare<br />

6 26-33% cover<br />

L Locally<br />

5 11-25% cover<br />

4 4-10% cover<br />

3


APPENDIX D<br />

BOTANICAL SURVEY RESULTS, SITE Y<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


Area C SW SE NE NW<br />

Field<br />

margin Arable Improved grassland Improved grassland Arable<br />

Habitat Poor semi-improved grassland<br />

DAFOR or DOMIN DAFOR DOMIN DOMIN DAFOR Present DOMIN DAFOR DOMIN DAFOR DOMIN DAFOR DOMIN<br />

NVC Communities<br />

MG1 MG1 OV7 MG7 MG7 OV7 OV7<br />

Species<br />

Agrostis stolonifera Creeping bent O 5<br />

Alopecurus myosuroides Black grass F + 4<br />

Anisantha sterilis Barren brome F O 1<br />

Arrhenatherum elatius False oat-grass A/LD 9 5 A R LA<br />

Bromopsis erectus Upright brome O/LA 3<br />

Bromus hordaceous Soft brome O 2 O<br />

Dactylis glomerata Cocksfoot F/LA 4 5 A A 9<br />

Elytrigia repens Common couch R<br />

Festuca arundinacea Tall fescue O/LA<br />

Festuca ovina Sheep's fescue O<br />

Festuca rubra Red fescue O/LA 5 O<br />

Lolium perenne Perennial rye-grass F D 9 A 5<br />

Phleum pratense Timothy F 3<br />

Poa annua Annual meadow-grass R + 2<br />

Poa trivialis Rough meadow-grass R O O<br />

Achillea millefolium Yarrow O 1 R<br />

Agrimonia eupatoria Common agrimony O<br />

Anthriscus sylvestris Cow parsley O 4<br />

Aphanes arvensis Parsley piert O<br />

Artemisia vulgaris Mugwort O R<br />

Atriplex prostrata Spear-leaved orache R<br />

Capsella bursa-pastoris Shepherds purse + 1 O 2<br />

Centaurea nigra Common knapweed O<br />

Centaurea scabiosa Greater knapweed O/LF 4 R<br />

Cerastium fontanum Common mouse-ear R<br />

Chenopodium album Fathen R 1<br />

Cirsium arvense Creeping thistle O R<br />

Cirsium vulgare Spear thistle R R<br />

Coronopus squamatus Common swinecress + R<br />

Fallopia convulvulus Black bindweed + F/LA 4<br />

Filipendula vulgaris Dropwort R<br />

Fumaria officinalis Common fumitory + 1 O 2<br />

Galium aparine Cleavers O + 1<br />

Galium verum Lady's bedstraw O<br />

Geranium dissectum Cut-leaved crane'sbill O R + 5<br />

Geranium pyrenaicum Hedgerow crane'sbill R<br />

Glechoma hederacea Ground ivy O<br />

Heracleum sphondyllium Hogweed O/LA 5 O 1 O<br />

Hypochaeris radicata Cat's-ear R<br />

Lamium album White deadnettle O 3<br />

Lamium purpureum Red deadnettle O<br />

Leontodon autumnalis Autumn hawkbit O<br />

Linaria vulgaris Common toadflax R<br />

Lotus corniculatus Bird's-foot trefoil R<br />

Matricaria discoidea Pineappleweed +<br />

Medicago lupulina Black medick R R 2<br />

Myosotis arvensis Field forget-me-not O +<br />

Onobrychis vicifolia Sanfoin R<br />

Papaver rhoeas Common poppy + 1 O 1<br />

Pastinaca sativa Wild parsnip LF 2 R<br />

Persicaria aviculare Knotgrass + O 1<br />

Pimpinella saxifraga Burnet saxifrage LF<br />

Plantago lanceolata Ribwort plantain F 5<br />

Potentilla reptans Cinquefoil R<br />

Prunella vulgaris Self-heal R<br />

Ranunculus bulbosus Bulbous buttercup R<br />

Ranunculus repens Creeping buttercup O R<br />

Reseda lutea Mignonette R<br />

Rumex acetosa Common sorrel O<br />

Rumex crispus Curled dock R R<br />

Rumex obtusifolius Broad-leaved dock O 4 R<br />

Senecio jacobea Common ragwort R<br />

Senecio vulgaris Groundsel O + 1<br />

Sherardia arvensis Field madder + O 1<br />

Silene alba White campion R<br />

Silene vulgaris Bladder campion R<br />

Sonchus asper Prickly sowthistle O 1<br />

Sonchus oleraceous Smooth sowthistle R<br />

Stellaria media Chickweed O<br />

Taraxacum officinale agg. Dandelion F 1 F/LA 4 F 1 R 1<br />

Torilis nodosa Knotted hedge-parsley + 1<br />

Tragopogon pratensis Goat's-beard R<br />

Trifloium pratense Red clover O 4 R<br />

Trifolium repens White clover O 2 F/LA 3 R O<br />

Tripleurospermum inodorumScentless mayweed + 1<br />

Urtica dioica Nettle F/LA 3<br />

Veronica arvensis Wall speedwell + R<br />

Veronica hederifolia Ivy-leaved speedwell + 5<br />

Veronica persica Field speedwell + F 2<br />

Veronica polita Grey speedwell + 1 O 3<br />

Vicia sativa Common vetch R O<br />

Viola arvensis Field pansy O 1<br />

Crop 9<br />

DAFOR scale Domin scale Positive indicator for unimproved calcareous grassland (National Vegetation Classification communities CG2, 3, 4 and 5<br />

D Dominant 10 91-100% cover Red Data Book Near Threatened<br />

A Abundant<br />

9 76-90% cover<br />

F Frequent<br />

8 51-75% cover<br />

O Occasional<br />

7 34-50%cover<br />

R Rare<br />

6 26-33% cover<br />

L Locally<br />

5 11-25% cover<br />

4 4-10% cover<br />

3


APPENDIX E<br />

BOTANICAL SURVEY RESULTS, SITE Z<br />

September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


September 2008<br />

11108605R_Botanical_DW_09-08<br />

Phase II Botanical Surveys<br />

Chris Blandford Associates


Area C SW/SE NE1 NE2 NW<br />

Habitat<br />

Poor semiimproved<br />

grassland Arable<br />

Unimproved<br />

calcareous grassland<br />

Semiimproved<br />

grassland Semi-improved grassland<br />

DAFOR or DOMIN DAFOR DAFOR DAFOR DOMIN DAFOR DAFOR DOMIN DOMIN DAFOR scale Domin scale<br />

NVC Communities<br />

OV3/ CG3d<br />

CG2 CG2<br />

D Dominant 10 91-100% cover<br />

Species MG1 OV15 W21 CG3d MG6 MG6 MG6 CG2<br />

A Abundant 9 76-90% cover<br />

Crataegus monogyna Hawthorn R F/LA 1 F Frequent 8 51-75% cover<br />

Euonymus europaeus Spindle R O Occasional 7 34-50%cover<br />

Ligustrum vulgare Wild privet O R Rare 6 26-33% cover<br />

Malus sylvestris Apple species R L Locally 5 11-25% cover<br />

Prunus spinosa Blackthorn LA<br />

Rhamnus catharticus Buckthorn O 4 4-10% cover<br />

Rosa canina Dog rose R 3


South East Office The Old Crown High Street Blackboys Uckfield East Sussex TN22 5JR T 01825 891071 F 01825 891075 E mail@cba.uk.net W www.cba.uk.net<br />

London Office 1 Swan Court 9 Tanner Street London SE1 3LE T 020 7089 6480 F 020 7089 9260<br />

Directors<br />

C J Blandford BA DipLD MLA FLI • M E Antonia BSc EnvSci RSA DipPA • M Holland BA DipLA MLI • D Watkins BSc MSc AMIEnvSci<br />

Chris Blandford Associates is the trading name of Chris Blandford Associates Ltd Registered in England No 3741865. Registered Office: 29 High Street Crawley West Sussex RH10 1BQ

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