Ecological Assessment
Transcription
Ecological Assessment
20 15 /01{9 Homestead, Phase1 Ecological survey February2015 PteliminatyEcologicalAssessment (Extended Phase1 Ecological Survey), Land rear of the Homestead,Main Road, Austfey DocrrmentPreparedFebruary2015 SupervisingEcologist Dr. Stefan Bodnar MCIEEM Planning Coneultanc Simon Cheshire On behalf of clients: RECEIVED Repon Autlror: Dr. StefaoBodnarBSc (Hons)PhD MCIEEM 35 Post Offrce Road BaddesleyEnsor Warrvickshire CV9 2DD Email; stcthn.lrodnar{ )1(ri)ucxrglcrna ,c<-tn.r 0 I MAil?0i5 Ncrtl i \''.la| ;,,ickshiro survey Phase1 Ecological Homestead, February2015 Contenta 1.0.Inuoduction 1.1.Background 1.2,Site Location 1.3.Site Description 1.4.Brief Deectiption of Ptoiect 1.5.Data Searches 1.5,1,Statutory Nature Coneervation Sitee 1,5,2.Non Statutory Coneervationdesignatione 1.5,3.Protected SpeciesRecords 1,5.4.Interpretation of available biological data 2.0. Survey Methodology 2.1.Site, Iacation and Access 2.2. D*e and Time 2.3. Weather Conditione 2.4, Methodology 2.5.Fauna 2.6. Conrtrainte of Survey 3.0. Survey Results 3.1.Disuibution of Habitats 3.2. Ptotected and Notable Species 4.0, Discuesion 4.1. Conservation Context 4.2. Conclueion 5.0, Recommendations 5.1.Enhancing and Protecting the Ecological Value of the Site 5,2. Opportunities for enhancement APPENDICES: Appendix tPhase 1 Habitats Appendix 2: Photographs Appendix 3: SpeciesLists Appendix 4.11:Palette ofwildlife friendly plant species appendix 12: Grcat Creeted Newt Ecology 3 3 3 4 5 5 6 6 7 8 8 8 E I I 11 t2 t2 1i 19 t9 t9 2l 22 T2 Homestead,Phase1 Ecological survey Februarv 2015 1.0.Inroduction 1.1,Background At the tequest of Simon Chcshite, a Ptelirninary Ecol<>gicalAsscssmenr (Extcndcd Phase I Ecological Sun'ev )uas carded out at land ar the reat of The Homestead, \{ain Road, Ausuel to et'aluate rbe habitars, descdbe any further sun.eys requircd and indicare the level of rc<luired miugation/ compensation/ cnhancement in telation to thc proposed development of the sire. It excLudesthc garden arca of the main building 1.2, Site Location l|lcsitcislrtclrlt'rlitttlrcvi1lrrgclri\trstrel..\\.:rnr,'icksllir-c.Sct't.t't|Iitlcbrltttt<lln. R$IDNfl.{L DFII]'PME\T TO THI RE{R OF T1IE I IOIIF'TEAD,MAINIiCNq ,1|S'IRTI'. t: '' ' ,, 'i.t -.t' '' A .,n ^ ^!. -.--,i'-- =. survey Phase1 Ecological Homestead, February 2015 1.3,SireDescription Thc' site ties '$.ithin the village of -,\ustrev ,.\ustre\'is a village and civil parish in the North Varu,ickshire District of Wanr.ickshire, England. and rhc villagc hcs at the northem exttemio of the Countv*. The sire compnses an extended garden ro the rear of the Homestead. Nlain Road, rvhich is not included in the develoPment ProPosal. 'Ihe land is sloping ro the nonh, and comprises a meadow/grassland. v-ith remnants of a planted otchatd, a 'erboretum'. The w-oodcd elements cover nearh' half pool, and a range of landscapetrees, planted as a form of of the site. There are natile hcdgerows on the \''estem. eastern and southem boundanes' Landscape impacts: Habitat connecdviq' end bamers o Habitat connectir,in ftom thc Site rvas considered aterage. *'ith some dispening animals likelv to be dercrred bl the human int-luencero rhe immediate sorrth and east q,ithin the village of Ausucl, o 'lhe Site rvas set u,irh a rural landscapc of pastoral ficlds. Thcse pastoral ltelds were consideted to be connccted br- a good netu'ork of hedgerou's. -l'he lvl-12motor\trav, $,hich lay some 900m ro the north of thc Sire, may havc created a nraiot bartiet to the dispersal of animals ftom this direction and onto the Stre. o -l he data search rcvealed no sratuton dcsignated sitesvlthrn the l km search radius hos'evcr Austret Churchvard. Ecosite, was locatcd some 50m from thc Site . Homestead, Phase1 Ecological survey Februarv2015 SeePhotogra.phs(Appendix 2). A full specieslist of vascuJatplants is included at the end of this report (Appendix3). Appendix 1 showsthe Phaset habitatmap. 1.4.Brief Description of Pmiect The areais subject to a plannrng development (refer to planning applicetion). 1.5.Data Searches Information was gathered from a number of soutcesinduding Nature on the Web (Irlatural England Website),and a rangeofother soutcesof web.baseddata. The data seatchcoven the following areas: o Speciesof particular note o Local NatureReserves . Protected species@adger,grasssnake,great cresrednwvts, otter, water vole and bats 1.5,1, Statutory Nrone ConEervation SirEs Statutoty Nature Conservation Sites (this includes Sitesof SpecialScienti6c Interest, Local Nature Reserves, SpecialAreas of Concern) 2015 February survey Phase1 Ecological Homestead, 'fhere are no StatutorvNature Consen'ationsites'*'ithin Zkm of the site,and the sitelies oursideandl' SSSI imPactzones. 1.5.2.Non Statutory Consewation designations There is one non-sratuton designatedsitesrv-ithinlkm of the site,-\ustrel Chutch Ecosite,rvhichlies a short distanceto the south, 1,5.3.Pmtected SpeciesRecorde In relationro protectedspeciesthe follou'ingwererccordedand are presentedherewith rhe approximate distancesof the nearestrecord. Bat Species Species(Latin Name) Common Name Ilyotit duubentonii I{1oth ry1ti:anat / brandli Daubenton's bat \\"his kered,/Bra n d ts bat Nwta/n no"tula Nocrule Pibitt?ll r ripirtultt! Comm<>npipistrellc Soptano pipistrelle Brown long-eared bat Pibi ftlht.t eflaesr Eblesiu: semtinnt Serodne Approximate distance of nearest record from the survev Bite (km) -lkm South,3 km S\\' 1()km SW ?lunS 3kmS lkm S -l km S\I' 9 km S\X- Other Species Species(Latin Name) Common Name Me/esnelet 'I-/irary.t ,irtdtrr Badger Great Crested newt Apptoximate distance of nearest record from the survey site (km) .tkmS 3kmE Bird Species Species(Latin Name) Common Name Approximate distance of nearest recotd from the survey site (km) Tyto ulba Bam owl Breedinq 3.5 km S (aurhors own records) The Local Biologrcal Records providcd the followhg records uithin a I km radius. Onlv speciesscoped h to the sun'ev, rvhere records exist, are commented on w'i*rh the speciessection Terrestrial l{ammals Indeterminate pipistrelle (lipistrellus spp.) ..\mphibians none Reotiles none Homestead, Phase1 Ecological survey February 2015 1.5.4Interpretation of avail,ablebiologicd deta The availabledatasugests that thereis no evidenceofprotected speciesutilizing d1gsite,though a pipisrelle specieshas been tecorded r ithin 1 km. In addition, discussionswith local residentsindicate th atb^dgr. Meles mehs,ete presentrn the areain addition to bat speciesChinpha lp.. There are also unvedfied records of gteat ctested newts Tittrffi LriJlqtuJ. It conftrms that no Statutory designatedsites are adjacentor close to the site and that the dwelopment will haveno impact on thoseat further distances.There is one non-Statutorysitevery closeto the development, any potential impacts on which will be assessed in this report. February 2015 2.0. Survey Methodology 2.1, Site I-ocation and Accese Austre;-,\Varmckshire. Land at the Flomestead, All areasof rhe sitervereavailablefor access. 2.2, Date and Time of Suwey The sun'eyrvasconductedon 10th February2015 2.3, Weather Conditions The weatherconditionsduring the sun'eywererainv and ovcrcast. 2.4. Methodology The sun'evwas conductedbv carrvingout a s)'stematicwalkoverof the sitebv Dr. StefanBodnar NTCIEEM ro recordhabitars,species,and any notablefeanrresof interestu'rth regardto flora & Fauna.This is in accordancewith standardPhase1 suweytechniquesandis a methodologyrecommendedbv the Instituteof EnvironmentalAssessment(1995),and more recentguidancefrom CIEE\I (2013). 2.5 Fauna Dunng the sun'ev,emphasiswasplacedon seatchingfor evidenceof and potenualof habitatsand feanuessupporringprotectedor notablespecies,especialll'thoselistedundet the Consen'ationoI Habitatsand SpeciesRegulations2010,the V ildlifc & Countrl'sideAct 1981(asamended),the List of Species& I{abitatsof PrincipleImpottancefor Consen'ationof BiologicalDiwersityin Wales (\\'alesBiodir.ersitlParmership,200f and in local Biodiversitl Action Plans' T}e rangeof methodsusedwereas follows: Great Crested Newt HSI Habitat Suitability Index (Assessment) SeeAppendir 12 for generalguidanceon Great CrestedNewt ecolog'l'. The surveymethod emplotedis determinedby NanrralEngland'sStandingAdr.icefor Great CrestedNewt TitkB! nirtata (referto Natutal Englaodweb-site),recommendsthe following genericadvice: An initial sun'e1'ofrhe terrestrialhabitatsand qualig'of the ponds *ithin, and adiacentto, the development 'Ihis shouldideallvfollow the Habitat Sr.ltabilin'Index (HSI) methodologl' footprint is a usefulstartingpoint. Homestead, Phase1 Ecological survey February 2015 developed by Oldham et al. 2000 whjch looks at a number ofvariables including pond size, terresttial habitat, pond shading and w-ater<lualityto derive a probabili$ o[ newts being prescnt uithin a pond. Thrs is a helpful tr:ol for large schemes as it may help to ,rscope out" some ponds for more detailed sun'eys. Pleasenote thar HSI assessmenrsare nor an altemative to carrying out a morc detailed sun'ey should onc be required Habitat Suitability Asses6ment Any ponds werc tien assessedfor habitat suitabilin for great ctested new'ts,utilising the modificd Grear Ctested Newt Ilabitat Suitabrhq.'Index (Oldham ara/, ?000). The habitat suitabilio index provides a means of evaluating habitat quality.'Ihe Habirat Suitabiliw Inde:< (IJSI) is a numerical index benveen 0 and 1, where 0 indicates suitable habitat and 1 represents optimal habitat.'I'hc HSI score is thcn utilised to define the suitabiliry of the pond on a categorical scalc (fable 2.1). The system is not precise enough to allow rhe conclusion that a pond r.r,itha high score u'ill supporr great crested ncwts whilst those with a low score will not. See ApPendix 7 fot reference document of the Grear Cresred Nest Habrrat Suitabiliry Index. HSI Score Pond Suitabilit_v < 0.5 Poor 0.5- 0.59 Below avetage 0,6- 0.69 ,\verage o,7- o.7, Good > 0.8 F|icellent Table 2.1:HSI scoring for pond suitability Bats 'I'he trees within the sire rvere appraised for rheir potential surtabrJrtyto suppott bteeding, resting and h.ibemating bats in accordance with sun'el methods documented in the Bat Sun'eys: Good -frust Ptactice GuideLines(Bac Conservation 2(112),I.eatures o[medium and high potcntial for bats were searched for signs of use bv bars, such as droppings, urinc sraining and scratchesaround entranceholes etc, ,\ r.isual inspection of the trees from ground level with rhe aid of binoculars was undertaken to search fot evidence of acrual bats as well as signs of bats (droppings, feedhg remains. udne staining, scratch marks. noise and rhe remains of dead bats erc.). In addition, the trees were assessedfor the presence of fean-rreslikelv to be attractive to roosting bats, such as cavities or rot holes in the rrunk ot branches, splits in the tinber, delaminating bark. decp bark cre'vices,dead brancbes and dense iw cover etc. In accordancc s,ith the methodologv out[ned in the Bat February 2015 survey Phase1 Ecological Homestead, (lonsen'adon Trust's Bat Surtel's: Good Practice Guidelines (2012) trees u'ere assignedto the following categories: . Known or Conftmed Roost - signs of bats (droppings, erc) or actual bats recorded; or prerious records of bats in uee r High (Category li - trees with multiple, highly suitable features capable of supporting large roosts r Medium (Category 1) - a tree with dehnite bat porential; fewer feanres than category 1' or potential for single bats r Low (Category 2) - No obvious potential, although tree of size and age that elevated sun'evs mav result in cracks/crevices being found; or tree has some features which haqe limited potential to support bars . 'the Nil (Category 3) - no potent.ial to suPPort bats site was also assessedfor potential bat foraging areasand commuting routes. Feanues of medium and high potential for bats were searched for signs of use by bats, such as droppings, utne sraining and scratchesaround entrance holes ctc. T'he site was also assessedfor acmal and potential bat foragurg areasand cofiunudng routcs. There is a single building on site, and this was assessedextemallv for fieir suitabfitY to provide bat roosting features,in accordance uith the methodologr- oudined in the Bat Consen'ation Trust's Bat Sun'e1's:Good Practice Guidelines (2012) Reptiles The site *.as assessedfor its suitabiliry to supPort reptiles based upon the abundance of suitable habitats such as smrcturallv diverse habitats, hedgerows, scrub, rougb grassland w'ood piles, n:bble, banks and compost heaps etc. The site was assessedu'ith resPect to its potential for use fot hibemation and spring/summer use based on guidance provided in the Herpetofauna workers' Manual floint Nanue Consen'ation Comminee,2003) and the Reptile Nlanagement Handbook (Edgar. Foster & Baker 201l). Badgets The whole site was searchedsystematically,with panicular attcntion being paid to features likelY to support ba+er setts (e.g. earth embankmenis, s'ooded copses etc.). The location ofall badger signs such as runs, dung pits, prints, hair, foraging snuffle holes found during the sun'ev were 10 Homestead, Phase1 Ecological survey February2015 mapped and all setts characterisedas either main, anner, subsidiar;'or oudiers in accotdancevrith guidancegiven in SurveyingBadgen (Harris, Cresswel.l&JeFfedes, 1988). Birds All birds obserreddwing the Freldsuweywere recorded,in additionto featurescapableof supporting oesting birds (e.g.uees, hedgerows,buildings, bmmble beds,ruderal vegetation and roqh grasslandetc).The siteswasalsoassessed for its acnraland potentialsuitabilitvto support Schedule1 and BiodiversityAction PIan prioritv species. Othet Species The site was also assessedfor its actual and potentral suitab ity to suppott other protected or notable fauna in accotdancewith the Guidelines fot Pteliminary Ecological Appraisal (Chanered Instinrteof Ecologr and EnvironmsntalManagement,2013). 2.6. C.onetraintof Sunrey Owing to the time of vear the initial suwey took place it can be considered to provide a reasonable,though not exhaustiv€Plantlist- In particulatthe gtassland/meadowareaclassificationis tentative,and should ideally be tevisited in the spting to confirrn the classiEcation.This sun ey noted the habitat types on the site, and the dominant vegetation at dre time of the survey,which is likely to be constanr and a fair reflection of the habitat qualitypresent. 11 Februarv 2015 survey Phase1 Ecological Homestead, 3,0, Survey Reeults 3.1. Distribution of Habitate and Site Description The site comprises an extended gatden to the rear of tle Homestead. Ir{ain Road, which is not included in the development proposal. The land is sloping ro rhe nonh, and comprises a meadow/grassland, u'ith remnants of a plaoted orchard a 'arboretum'. The rvooded elements covet nearly half pool, and a range of landscape trees, planted as a form of of the site. There are native hedgerows on the westem, eastem and soutlrem boundaries. Nativc hedgetows: The hedgerows are a misture of hawth om Crataegusmorcg'na, elder SambaLvtnigm, andbranble Rfunt ptetdoplzlanut, silvet birch Benla pendala, aod .frulinns.Therc are in-hedge uees of svcamore -4 tur horsechestnut -,leghalus hippocalarcr mOrchatd A small area dominated bv mature apple vees Malu sp. Improved gtascland atea Improved grassland, dominated by Annual meadowgrass Poa aantaa,rough meadowgrass, l>oatittial*, percnnial negrass, L.okua pennne, Cocksfoot Dacgtb glomerata.Yorkshite fog, HoLw larutas and Creeping softgnss Hoftw mol/l Common hetbs present include ribwon planrain Ptanlagohnceolutu,and Creeping butlercup (RananrulasnPeu). Woodland/Arboretum atea A wide range of mature and semi-mature uees of a varieq' of speciesrncluding Chile pine, weeping ash, Horsechesmut, Silver birch, Tibean birch, Chery, Blue Fir, Eucahpnrs, weeping beech, Scot's pine, Beech, Cedar, N{agnolia and Goat willow. Pond The pond is butyl lined, and approximately' 200m in area. It is shaded ro around 700loand most of the surface is covered in emergent vegetation Gllveria maxina, and pwple loosestrife Libnm vlinria. (SeePhase 1 Habitars, Appeodix 1), and Photographs (Appendix 2). A full spe<ieslist of vascular plants is included at the end of this teport (ApPendlx 3). 72 Februarv 2015 Homestead,Phase1 Ecological survey 3.2. Protected and Notable Species Badger Duting the survey a number of mammal pathways were obscrved throughout the sun'ey site. Thesc w-ete possiblv attdbutable to domestic car (Fe/i^- donutiar) ard fox (l'apu ralqn) bur also badger (illelu nelu). Snuffle holes \!ere apparent in some areas of the site. In terms o[ badgers, it can be confirmed that at the time of survey there appear to be no evidence of badgcrs on site, including nrnways and droppings, and no setts or possible sctts were noted either within the proposed development sites or within 30m of these site boundaries. there are signs of bx l.'u/pet ulpet including recent signs of a blackbird kill. Badger runs \r:ere noted from thc nearb_vEcosite. Bats It is possible for the site to have some potential as bat foraging site and the manrre hedgcrorx'sand tlees as bat commuting routes. None of the on-site trees have features thar could be utitzed by roosting bats. Other species The site has some Potential fot other species.Nfammals recorded included molc (falpa eumpea)and field vole (Minvlat agre it).In terms o[ reptiles, thc site is suitable only for grass snake Na/z.v rulix. though there are no oearbv records of this species. Birds A small number of common birds werc acnrall)' recorded on rhe sire itself, and a number of othcr species rverc noted rvirhin the surrounding areas and habitats and thesc are lilielv to forage within the site. Some of the scnrb/slrub areas and trees within tl're sun'ev site also provide suitnble nesting habitat fot a number of common bird specieslisted below. The birds noted during suwev included blackbird ('htrdu.tnen/a),6lue rir (Cyunittescaenleut),goldhnch (Cardtelir urdueli,r),jackdaw (Conat nontdula),b<''ustspar':, ru (/),r,.,,,r' ,/azrr,l,zr,),collated dove (Sneptopelia denttlo), magpie (Pira pira), duntock (Pnnel/u no&tlait), grcefftnch (Cnduelit thkrit), $e t ut (Patur mEb4,i^y Canlar glandariat starlitrg 1rlizrzz' rz,q,ai,1. song thrush ('l ur&t plti/onelot), mallatd ,4nat plu\rlTnthot, pheasart Phainu.r cvhhiat tobin (Eithaur rabualu) carrior' crow ((nntat nrute), pied wagtai-l (hIot,t,i//a alba yaere/h1, greater spotted '*oodpecker De mropn najot lesser spottcd woo dpecket Derdmtuputminor, woodpigeoo (Colanba paknbat), raven Conw ,vrax and wren (Tryqk{te! ln-qhbtci). a former nesr of a song thrush is apparent in one of the on-srte rees. Given the development sites location, sittratcd within an irrea of predominarely agricultural land use it might also be appropriate to assume that there could be speciessuch as chitTchaff (l)l1ylosrEtrn//yhita,1,, blackcap (Slhtia atrinpi//a),Buzzard. (llrnt /r,r,tz;. whitethroat (-fyhiu ,vnntnit), chaf5nch (l-rirgilb toclz/L).sparowhawk (,.laipinr nirar), swallow (Himndn ras#ia/,house martin (De/ithon urbiu), swift (-'1pusapat), feral pigeon Cohtnba litiu uar., mistle thnsh (Tardat tduonir), T'awny owl (.lrnx d! Lo).and long-tailed tit (,,lgi nlrr uudalar) which may utilize and breed on this site. Invasive plant species 13 February 2015 survey Homestead, Phase1 Ecological None are prescnt. Great Cr€Bt€dNewt In tems of habitas for great crestedne\F't(fiturur iritrortrl the habitatshave some potential,The nearest k-oownrecordsare near, it is considereda requirementfot this speciesto be consideredfurther here,and a Habitat SuitabiliryAssessmentwasundertaken. Great Crested Newts Gteat crestednews are protecteduoder Schedule5 of the Niddlifc and Counwside Act (1981)asameoded and Schedule2 of the Conservadon$iatural Habitatsetc)Regulations1994S.egulation38).Becauseof their rarity they are alsoprotectedunder AnnexesIla and IVa of the Habiuts and SpeciesDirective and under the Beme Convention.In 2007,the ConservadonQ',laturalHabitatsetc)Regulatioos199'{was amended particularlvin relation ro designatedEuropearProtectedSpecies(EPS)which includesgreatcrestednewt and under the Conservadonof Habitatsand SpeciesRegulations(2010).In this was further strengthened particular,recentamendmentsremovethe requirementfor actionsto be intentionalor recklessin ordet for an offenceto be committed, Langton etalia(2001)makethe point that: 'Taken togetlur,rhe.4el andlhe Regt.lationr "Thewordiryin tbe 1981.4 and 1994P,egtlatiouit tlight!1diflerent." (bllovingthcCROV ,4d 2000) nske it ilbgal to: Intentiorul!1or dzliberah$t:aptarcor kill, or intentione$injan Sndt Lwtedttuh. . Dcliberaxlyditurb greotdvlted,,eptror inhntionalfior rctklest! + di urt then in a pku uvdJor thelnr orpmtection. . Damogeor delml a bnedingsiteor ntingplarc. . lntentiorulll or rcckler:l!dana3e,furlmJor obrhrd ac.vlrto aplacemd.lbr thelterorpftrediott . PoJte$agj,tatouhd n€pr,or aa^pltrl oJir, rnhst acquindlaw[a$'. , Se//,banenexfiaageor lranqtorTor oficr./brule 3nat nzrhd ntprr 0/ Pdrlr of rhem. *Rttktut ofeatesweeaddedb1theComrTsideandNght of lVa1,'4tt 2000, a)hichuPplies on! to Enghada On-site water featuree sizedpool within the surveysire.this is evaluatedaspool 1 Qelow). Thereis a moderatel,v 14 Vaht". February 2015 Homestead, Phase1 Ecological survey Pool3 Pool1 Pool2 Pool4 'l'hcre ate -1pools and rvacerbodics locared widrin 5(X)nrof rhe site, shou'n on rhc annorared aerial photograph below. in addition to rhc on-sire pool. sho\ur below: _t) survey Homestead,Phase1 Ecological Pond I HSI lndlcq! Attrlbuto Scor€ Pond2 Attrlbut€ Scoro Pond3 Attrlbute Score Pond4 Attrlbuio Score GridReference sr1- Geographic location ,1 1 I I Sl2 - Pondarsa to near€st 50m?(m'?) 150 Sl3 - Pond oryrng (frequency) Sl4 - Water quality Sl5 - Pond shading(%) 0.0s 0.3 48 0.05 500 1 1 N6vea 09 Never 0.9 Sometimes 0.5 0.67 Moderate 0.67 Moderate 0.67 Pooa 0.33 700k 0.7 s0% 1 500/o 1000/" o.2 Minor 0.67 Absent 1 Absent Maior 0,01 Absent Moderate N€ver 500,6 Wat€r SI7 - Fish Abs€nt 1 Minor Minor Absent SIE - Pond density 1 1 st9Surrounding tenestrialhBbitat Modeiate Good s t t 0- 0.67 Moderat€ Good 0.67 Mac.ophyte (aqualic plant) density(%) 20% HSt SCORE CATEGORY 0.5 0.737 Good 400/o OYo 0.378659 Poor 0.7 0.67989 Averaq6 10% 0.4 0.598787 Below Averags The sun ev concluded that all of thc nearbr saterbodies are of tlle belorv averageor poor categon for great cresred newts, rith the exception of pool 1 (oo-site) rvhich has a good categon and pool 3 (reported as gteat crested newts Dresent)which is averaqe, lo 0.: 2015 February Homestead, Phase1 Ecological survey The survev concluded that all of rhe nearbv warerbodies are of the below averageor poor category for gteat ctestedne$ts, E-ith the cxception of pool 1 (on-site)which hasa good categon and pool 3 (reponed as gteat cfestednefis pfesent)which is avetage. 16 Homestead,PhaseL Ecological survey February 2015 Pool 3 (rvithin 10m of site) Pool 2 (within lOm of site) Pool 4 (150m from sire) t7 2015 February survey Phase1 Ecological Homestead, Pool 5 (400m ftom aite) Conclueion The surr.el,concluded that all of the nearb,vwaterbodiesare of the below averageor Poor categotl for greatcresrednewts,with the excepdooofpool 1 (on-sire)which hasa good categoryand pool 3 (repofiedasgreatcrestednewtspresent)which is average. o tool, it is likelvthat greatcrestedneu/tswill be impacted Using Natural England'sRapidassessment b1'the development. I There may be a requirementfor licensing,dependanton the further survevsin resPectofgreat crestednep1s, r A oumber of sitecautionsarerecommendedduring the constructionphase' 18 Homestead,Phase1 Ecological survey February 2015 4.0. Diecussion 4.1. Conservation Context The site basicallyconsistsof five elements(Appendix 'le): o r o o o 'fhe Natir'-especiespoor hedgerow-s, somes.ith maturein-hedgetrees Improved grassland Orchard Pond Woodland/arboten:m value of the site in terms of ecological value ro 'w.ildlifeis generally moderare. The retention and prorection of the maturc uees and cohancement of the hedgerows and the trees of good <1ualiftas kev boundaq and site landscape fearures are importanr in rcrms of mainraining connectirr feaures of the site and screeuing of anl dewelopment. Separatedetail has been prepared section 5.0 Recommendations in respect of protection and enhancement of the Eees and hedgeror*'su'ithin the site. Species should be selected, rbat are both rvildlife friendly and are sympatl,edc to its rural setting, focusing on measures to encoulage farmland birds and foraging bats, wherever possible. 4,2. Conclusion 'fhis Phase1 Ecologv Report conFrrmsthat the ConsrnrctionZones are of 'lorv ecologicalvalue'consisting primarily of grazed improved lfassland, long grass and native hedgerows. The following obseryadons/recommendations are made: r IlLd nesting season:clearancerxill have to be outside mid \{arch to midJulv as tie areav'ill have substantive numbers of bteeding birds ptesent. o I'hete are no Statutory or Non-Starutorl Designated Narure Consen'ation Sires within the ste or that will be impaced by this developmenr. . From the Biologrcal Data Scarch no protected species were recorded wirh.in the site, and the €xteoded Phase 1 Ecobgv suwey concludes that there is at least one Protected species (great crested newt) liliely to be impacred by developmenr of rhe area. r The close proximitv of some bat rccords and thc maturc hedgerows, &ee-lincs and $crub areaswirhin the sire indicatc that these elements mav have signiEcancefor bar foraging and commuring. F'urther survers are recommended to determine the likeh presence ofgreat cresred nest, via a field suncy for the spec-ies,as foll<.rws: 'I'he survev method emploved is determned by Natural England's Standing Advice for this species (refer to Narural England rveb-site). recommends the follouing generic advice: 1.4 Fieldsunry An initial stnnl ol n temstial habitatsandqaalityol'theplndr uilbin, andddjutentto, thedewlopnert.footpint i a xseJulstadingpoint.TbisshouldidealfifollowtheI'labitat SaitabiliryIndex (HSI) nethodology denlopea a1 Oldhan eta/. 2000 whih looksal a nunberoJaaiabhsintludingpondiry, Ienwtial habiraLpondshadingantl 19 2015 February survey 1 Ecological Phase Homestead, beingpnnntwithina pond.Thisis a helpfultoolJbr laryenbenesasit vaterqualiryto deriwa pnbabiliy oJ'newts arvnolan alknatiw nE hefi to ,smpeotrl" romepondsJornon futailedunrys. Plearcnulcrhat HSI atse$menls be nqaind. d*aibd nnrl shonldone lo tdrDtingouta ,110n 1.5 Pnsenu/ Dke! Abnna Sunel Efort Pondt h) 'Muhod: Thnenng ncth\h (fthttedJrvnnettin&torcbstmgs, eg seanhetandbottblrapping)fioall be enploydPcr tuit. Effurt:1 tisilr in s itahh nnathetnndilioat. airi* thirg nid-.4priltonid-ME andtlxtctho d bcrpnad frning aid-Marchtonid-lnne, vitb at hatt tuooJthese tbmryhtbenng periodtomaxinintfu chanuoJf ingzeat if theJdn Lringtheplt'd(r)' . A pre-conrmencement badger survey is recommended and carefrrl site clearance of scrub undet an agteed method statement. o A further check on tle status of the grassland is recommended betweeo April and August to confirm 'lmproved' that has been made. the initial assessment of r A 855837:2012 Pre-dwelopment tree suwey is recommended' 20 Homestead,Phase1 Ecological survey February 2015 5.0.Recommendations It is importanr that this Pmposed development Ehould demonstrate no net los6 of biodiversity from the 6ite' This is a dun placed on Local Authorities in the Natural Environment and Rural Communities Act 'Ihete 2006, Secton 40. atc requirements noted for this under thc Nadonal Planning policy framework (2012) rvhich refers to compensarion/ mitigation, Ir is confirmed rhat the enhancement. mir(ation and compensation within ttris section rvill compl.v with all the relevant UK and LIU legrslauon relating to ptotecuon and enhancement of ccologr,-. This section states how rhe negative impacts ofdevelopment can be addresscd. 5,1. Protecting the Ecological Value of the Site. 1'he hedgerow and marure trees that exist'qiithin the development areas should be retained and enhanced. Following the built developmcnr there will be opportunities for enhancemcnr of the sitc's ccological value bv 'fhis landscaping measures designed to encoutage wiJdlife into the site. is covered more in section 5,3 Trees and Scrub AII effort should be made to retain the maure trees wirhin the plans especially those on the site edges. Scrub and tree lines on the site contributc to co unurcr routes and foraging areas for local bat populahons and these fearures should thercfore be protected as mucb as p<tssible.Si?rerc trees are unavoidablv lost to accommodate the scheme. suitable compensation planting should be carried out. As bats react advetsely to intense lighting. extemal lighting provision within the dcvelopment should bc a possible, bearing in m:nd rhe safetr requirements of the occupiers of the building. Erremal slighting should be da directional downLighters, of low lux and where possible, on dmers to ensure as htde light spill as possible from thc developmenr. the hedgerows and scrub on site arc particularh suitable for breeding birds and potentiallv will have a number of nests during the breeding season.Therefore, all site clearanceshould ideally rake place ourside of the bird breeding season.Bird bteeding season is between mid Match and mid July, although certain species can breed outside these months and if breeding birds are found then work should ceaseand the advice of an ecologrst sought. If clearance is undertaken within thc bkd brceding season then all site fearures should prefetably be checked immediatelv prior to clearancebv a suitablv qualified ecologist. Badgers A further bat sun'ey is recommended prior to cofiunencement of works to ensure no badger setts have been formed on site. Follot'ing the advice below will help der.elopers to avoid comrnirring offences. In accordance qith the Protection ofBadgers Act (1992) precautionarr'-meAsuresthat should be taken ro minimise disturbance and interference with badgers include; . Drsturbance in the vicinity ofa setr vhere breeding is conftrmed or expected is to be avoided during 1" December - 30th-lune. Badgers are panicularlv wulnerable ar this time of year and sett interference can result in dependent cubs being abandoned. ,\ protecuon zone is to be establishedat 30m radius around used setts. 21 February 2015 survey Phase1 Ecological Homestead, a a a a a Distubances,suchasloud noisesor vibrations,that might agitatebadgersoccup;ing a sett shouldbe avoidedor limited to ateasrvellawayfrom the sen. Noise in rhe viciniq of protectionzone is to cease2 hours beforesunset' Badgertunnelscan exrcndto 20m &om the entranceholesand are locatedbetween0.2 ald several metersdeep,dependingon the soil topography.Excavationwork and heaq'machinerysbould be kqrt well awar ftom whereit could result in damageto the sett or disturbanceto an;-badger occupyingthe sen. Anv securiry)ighnngis to be directedawayfrom setts. Firesand chemicalsshouldnot be usedrvithin 20 metresof sett. Trenchesand exca$ationsare to be cor'eredar the end of eachworking da,r,or includerampsasa meansof escapefor any-animal ialling in. Any temporarvexposcdopen pipe systemshouldbe cappedro prevenrbadgersgainingaccess. Gteat Crested Newt Furrhersurveysarc recommendedto determinethe lilielv presenceof greatcrestednewt,via a fie1dsun'ery for rhe species,as Follow-s: The surr-eymethod employcdis determinedby Natural England'sStandingAdvice for this sPecies(tefer to NanrralEnglandweb-site),recommendsthe following genericadvice: 4.1 Field sm'cy An inirial sanel oJ'thehflertial babiatr and qualiri ol thepondsvithin, and adjun to, the deaelopnentJoorpint is a aselultaing point. Thit shoutdideatllfoltow the Habitat Suitabilig Index (IISI) netlndolog dnehped b1 Oldban et al. 20(i0 ubich looks at a nunberoJ uriables intludingpond siie, temrtial babitat,pond adingand as il uarcr qaaliA to deit7 a pnbabiliry oJ'newt:beingpnnnl vitbin a pond. Thit is a hePJaltoolJbr laryt scbemes 8n altenatite ng^ heh to ,,Jtnpenat" nme pondsJormon dctaibd sangt.r.Phasenoturhat HSI ariellmefllsan no! to L:anJittgo t a mlle drtdiledrrnEJ sbo d onebe nquirud 1.5 Pnsenn/ Likef Absenn Sung Eibt (al Pondt ]llethod: Thne vnel nethldr (relet'ted Jivlrt nelting torchsunE:, eg seanhesand hottlettapfiry) thould be enployd per uisit. ElIltl: 1 uiitr in suitabh uealbercondilinnr. 'I:iniry viritr dtring nid--'lpil to nid-trtE andtbev shorldbespnad nid-hIanb to nid- urc, witb at h,rt tt'o oJ'rhe:e lhmaghrbeuncy periodta natinit tberhanrvoJfndingnwtt il thel ar uinlthe pond(s)' 5.2 Oppomrnities for enhanc€ment: lie in threeateas: T1reopporruniticsfor enhancement e Retentionand enhancementof valueof existingmature treesand hedgerowsand the on-sitepool. To include Supplemenraq'plantingwith native specieswithin the boundarl hedgefeatr:res,panicularly where there are gapswithin the hedge-lineto increascthe areaoF this valuableand prioriry habitat and to improve connecrivitt for wildlife. Inuoduction of bat and bird friendly native planting schemes,hibemacula,and wildflower hedgerou'edgemix seediog' 22 H o m e s t e a dP, h a s e1 E c o l o g i c saul r v e y F e b r u ray 2 0 1 5 o Irrrroductiorroil)at an(l brd ltorcs rxr suitaltlcrrces. o Sclcctiotroi r,,ildlitc-iiiendll plrnting specicsai l)^it ()[ rhe terrcsrrirl lnndsorping schcnrc r'"'ithinthc de. clopnrcnt. 5.2.1.Details of Ecological Landscaping 'lhc spccitrcattortshould incltrdc 5 clcnrcnrs of lanrlsc:rpingtlctails (tirrthcr iltonrrarion can bc k:Lrnd rrr ,\l.rpcndiccs{,I l): o -l o rcc specrcsro ltc planlctl as speclmcn5. Shrrrl>/plan Lingnrixnrrcs o \\ iklflorver sccclingareas o Bircl ncsting [>()\cs1rndl)it lroscsatrachcclro the rctrrinedn]ltturc lrees. . Rclcnti()nand cnhnncemcntoI on-sitc ;to,rl tor grcat crestcdt]c\\'r. 23 February 2015 survey Homestead, PhaseI Ecological AppendixI Phase1 Habitats .t1 .a (l0vr ah t\ \Jr' -wir.../-/,' rd .,,''. ,,4, @H; 24 February 2015 H o m e s t e a dP, h a s e1 E c o l o g i c saul r v e y Appendix 2 Photographs 25 2015 February survey PhaseI Ecological Homestead, 26 Homestead,PhaseI Ecological survey February 2015 February2015 survey Phase1 Ecological Homestead, Appendix 3 Specieslists FloraspeciesList(woodyl Commonname scientificname Ash Froxinusexcelsior Apple Molussylvesttis Leyland cypress Cupressocyporis IeyIondii Lawson s cypress Chomoecyporis Iowsoni oni i Blackthorn Prunusspinoso Elde r nigro Sombucus Hawthorn Crctoegusmonogyno Sycamore Acerpseudoplotonus Goatwillow Sdlixcopreo Holly llex oqulifolium Weepingbeech FogussylvoticoPendulo Weepingwillow Solixx bobylonico Weepingash Froxinus excelsior PenduIo Chilepine Aroucorioourucono Tibetanbirch Prunusserrula Bluefir Piceopungens Eucalyptus sp. Eucolyptus Beech Fogussylvoticd cedar Cedrussp. Magnolia Mognoliosp. Scotspine Pinussylvestris Bluefir Piceopungens 28 Homestead, Phase1 Ecological survey February 2015 Norwaymaple Acerplotdnoides Fieldmaple Acer compestre Hazel Corylusovellono Cherrysp. Prunussp. Wildcherry Prunusovium Specieslist (non-woody| Commonname Scientificname Annualmeadowgrass Pooonnuo Roughmeadowgrass Poo triviolis Bramble RubusJruticosus ogg Bluebell Hyacinthoides sp. Barberry berberissp. Broadleaved dock Rumexobtusifolius Cleavers Goliumoporine Commonbent Agrostiscopiloris Commonragwort jdcobeo Senecio Commonmouseear Cerostium fontonum Commonfieldspeedwell Veronicopersico Commonvetch vicio sotivo Cocksfoot Dactylisglomerota Cowparsley Anthriscussylvestris Creeping buttercup Ronunculus repens Creeping thistle Cirsiumotvense Herbrobert Gercniumrobertionum 29 February2015 survey Phase1 Ecological Homestead, Cutleavedcranesbill Geroniumdissectum Dandelion Toroxicumolficinole Daisy Bellisperennis Dogrose Rosoconino Fieldhorsetail Equisetumsp. Falseoatgrass Arrhenothorumsp, Groundsel Seneciovulgotis Greaterwillowherb Epilobiumhirsutum Herbrobert Geroniumrobertionum Hedgegarlic Alliotio petioloto Hedgebindweed Colystegidsepium Hogweed sphondylium Herocleum Lordsandladies orummoculotum lvy Hederohelix Meadowbuttercup Ronunculusocris Redclover Trifoliumprotense Reddeadnettle Lomiumobld Perennial ryegrass Loliumpercnne willowherb Rosebay Chomerion ongustifuli um Ribwortplantain Plontogolonceoloto nettle Stinging Urtico dioico Spearthistle Cirsiumvulgore Snowdrop Golanthussp. Softrush Juncuseffusus Sunspurge Euphorbiohelioscopio 30 Homestead, Phase1 Ecological survey February 2015 Smoothsowthistle Sonchusoleroceous Whiteclover Trifoliumolbum Woodavens Geumurbonum Yarrow Achilleomillefolium Yorkshire fog Holcuslonotus Creepingsoftgrass Holcusmollis Cyclamen Cyclomensp. Primrose Primulosp. Purpleloosestrife Lothrumsolicorid Reedsweetgrass Glycetiomoximo 31 2015 February survey Phase1 Ecological Homestead, Appendix 4 '0tqi_u /,1 --. gmlh '.dirE Ta€ea- XrmrE r|d Gaorig cdEldL Tob.|!| Oitrs. ttr Erd d.i-.Itr.l r b ffidd.g.a -r tqln atr{ . m rtdlt d nlrr|g (* @Ert Jt lr.d Buddleia X weyeriana cultivats you car planr the orange-flou,ered B. X rveveriana h1'brids *ith a clear conscience as thet'don't aPPear to procluce r.iable sced, thcv also atracr a broad spcctrum of insects including both burtertlies and bees, and thes 'Lochinch' with silver leaves is flotver late into the seasonwhen oectar is scarce.'l'he beautifirl B. x fallowiana aruactive to burrcrflies and is also said not ro produce seeds. The orange ball Buddlela @. globosa) ftom South America seems to atract bees rather rhan buderflies Bupleutum ftuticoeum ('Shrubby Hare's Ear') A shrubbv evcrgreen umbcllifer from Sourl,em l'iurope, where it is otieo culdvated. It has leat]rerv aromaric foliage and umbcls of vellorrish floT 'ers, a bir likc rhosc of Fennel' that are verl' attractilc ro hoverflies and other small insects. \\'ell wonh grou'ing for this reason. 32 Homestead, Phase1 Ecological survey February 2015 Ceanothus X 'Gloire de Versaillcs' Ceanothuscome from the lV-estemUnited States,N{osrCeanothushave bunchesof very small florversthat don't seemven'attractiveto insects.'Gloire de Versailles'ho,r'everis a hvbrid with loosebunchesof paleblue tubular flor*'ersthat are verr-artractivero butterfliesand bees. Caryopteris X clandonensis 'Kew Blue' A deciduous shrub from China for a sunny posidon, has small rubular blue flowers attractive to insects. Clethra alnifolia (rSweet Peppet Bush') A deciduous shrub from the Eastem united Staresthar lilies damp, acid or *'oodland soil. Has spikes of small scentedvhite flowers attracrive ro moths and butrelflies. Hebe X'Great Orme' and H. X rMidsummer BeauN' IJebes are close relatires of the herbaceous genus Veronica, and come from New Zealand. Some are much more atttactive to insects than othels. 'Gteat Orme'is a medium-sized hybrid with pale pink flowers thar are atuactive to burterflics, It is a distinctive cultivar and available true ro name in the nurserv trade, 'N{idsummer Beauq,' seems to be more of a gencric namc for a serieso[ large shmbs with blue or grev blue flowers irr long spikes, attracti'e to borh bees and bunerflies. There are a number of other blue and white flowercd Hebes thar seem very popular s,ith bumblebces. Myrtus communis (rEuropean Myrtler) An attractive evergreen shrub from the South of Francc and Spain with small evergreen aromatic leaves.It has been grorvn io our gardens for cenruries, but is susceptible ro hard frost and prefers a site against a wAlrn sunnv wall, Fluffr white flowers in early summer are bumblebees' heaven. Purplish berries follos'later which are stripped bv blackbirds in January. Amelanchier epeciee(rShad Bush') Shrubs urth white chern-lilie blossoms earlv in rhe vear, followed by blackish bcrries in late summer. Valuablefot the berriesasa sourceof food for bern -carhg birds rvhenmosr orher bcrricsarenot yet ripe. Edca terminalis('CorsicanHeath') 'lhe A shmbby heather-Like plant popular utth bumblebees. Comish l{eath, Erica vagans,from the Adantic fringesof Europe is alsoa good beeplant. Edca manipuhflora,from 33 Phase1 Ecological survey Homestead, February 2015 SouthemEurope,and its h.vbridErica X griffithii havefragranrllorverstlat attractbutterflies. Eupatorium ligustrinum A late-floweringevelgreenbush that looks vert' like a privet, but has bunchesof wtute fluf$' flowers in Septemberaod Ocrober.Theseflou'ersseemven attracdveto rangeof insects,especiallyhoverflies. Ribes sanguincum ( Flowering Currant) It is a ven. good early florver f<.rrbumblebees,as indeedare thc flowers of the closelvrelatedblackcurrants and gooseberriesAppendix 6: Plants good fot moths. with sPecies of moth they encourage beside Bird's Foot Ttefoil (lotus comicula tus) - BaneL Belnd Beanty,C)hilk Carpet,l-n iud Heather tsladdet Campion (silene mlgaris)- Carnpion,lvlarbhd (onnet, itietth Pag ltIarthd Cloaer,Dark Bmtade, ,fandy Carpet Botagc @otago officinalis) - Cinson Spetkled Chives (allium schoenprasr,rm) 'fvirqot Carpet \?ild Clan (salvia horminoid es) Birrg Stonecrop (sedum acre) \illow Nngcd CarPel,Notlben Il rli' Cou'slip (primula vens) - Plain Clary, Nortben Rttti' Daisy - BordendStraw Dropwon (fiLipendulahexapetala)- Salr Pug Evemng Pnmrose (oenothera biennis) - Ekphanl tlawk Field Scabious ftanutia an.ensis) l\lursb Fitt/k1y, Narmw BordendBeeHau,k, L)ne SpeckPag Sbaded Pug Foxglove (digralis purpurea) - Itsser \\llow Lindenting,I;o.xg/otePtg Golden Rod (solidago) - Linc .Spe&Pug BhathedPug, Co/den llod, LY/onn*nodP4g L/ Pu3 Greater Stitchn'on (stellaria holos rea) - Dart, \'e/lou l.l ndetwing,l4arsh Pag Plain Clary Hedge Bedstarv (galLium mollugo) - fuiddy Carpel, RoTallllantk, C)onnon Carpet' Iy/00dCarper,Water Carpel, Buth Greet Carpcl, llolthd Gn1, Gnen Catpel Hedge Woundwon (stach,vssylvatica)- Roy fuislir',Plain Golden\', S -angledlV'arc Hemp Agrimon,v (eupatorium cannabrnum) - l%omunodPzg L' Pug,I)ne Spuk P4, |+[arshPag,Cm, SLurL:c B rniJhed Herb Bennet @eum urbanum) - Nhand Waue Hetb Robert (geranium robenianum) - Bamd Carpa Hollyhock (akhzea rcsea) - itlal/ow Krdney Vetch (anthyllis r'r,rlnerana)- 6-hlted (hanatng Ladv's Bedstrarv (gallium verum) - Hmningbird Llawk, Snall [lleS>bantl-lawk, Calliun Carpet,Plain Vatc, Nband llj'arc, BedstrawHavk, tTrcher't Dat7, I*d Clxtnat, fudd1 Carpet,Rolal Man e, Common Cdrpel, Ilrakr CarryL Bnth Gnen Carfet. RedTvin,fpot Carpct, ll''ood CurPet,i otlhd Cn-1, Gnen Carpet Ladr"s lr{ande (alchernilla molts) - RedCarpel Lcsser Knapweed (centauea niga) - Sihar\', I-ine SpetkPtg Satyr Pag Lesser lUeadorv Rrse - Marsb Carpet Nlaiden Pink (dianthus deltoides) - i\larbhd Comnet Nfaqoram (majorana orignaum) - Sfu-anghdll'aue,Itn Border N{arshmallop-(althea officrnalis) - lllarbnallow Homestead, Phase1 Ecological survey February 2015 tr{eadow Clary (sah'ra pratensis) - Bman Spot Pinion, I lebna CLard er, Poadtt4edpaaker, Enpenr i\'Ieadowswect(fiIipendula ulmaria) Mwllen - Mulhin, Stnped\1 tnis Navelwott (umbilicus rupestris) - lVeaaer'.r l{/ne Pnk - Hauk -L-nP/c Ptimrose (primula !rulgarit - l>earlBordend Yellow ('nderuing Doabh Squan Spot, Gnen Athel SPottedClary, IngrainedClary, Silaer Gnand Carptt Purple Loosestrife (lythrum salicana) - Enpemr, Snoll Elepbant Hawk, Powdend.Quake Ragged Robin (,u-chmsflos cucult) - Canpion, Lythnit, Twin-got Carpet,Marbkd Clowr Red Campion (melandrium rubrum) - Rirult, Campion,Ljhni4 Twin-.y>otCarpet,.f andyClarpat,Mafiled C/awr Red Clover (trifolium pratense) - l-attttud Healb, Cha/k Carpet,BeId Bcauty,ltfothr Skipton,.f baded Bmad Bar, Nanta'bordercd f-rpo! Ban er Red Valenan (centranthus rubct) - Elepbant Hawk Rock Rose (lrclianthemum mummularium) - Annlet, Ciin Fonster,.lilky W'ate,,'Lhaofth'r llrlrtiL, 'ffuer, Atgtl lVood Northem Bmpn Rosebav \Willowh erb - Twin-.pot C)arpet,Snall Phoen\, ly/hite Bandtd Carpet Small Scabious (scabiosacolumbaria) - L)ne S4e& Pa.g,ShadedPnj Soapwort (saponariaofficinaLis)- Marb/edClouer StJohn's Wort - Tnbh Bar Sweet Rocket (hesperismatronalis) Sweet Violct (r'iola odorata) - Bmad Bordend Ye/loa l:nderuing, ltxer Bmad Bordend Yelloa Llndeping Tansy (tanacetum r'-ulgare) - Ijs*^- Emerald Tbrift (armena mariuma) - Analet, leathtnd Rantnt us, Thnli Chantiry, B/a& Banded 'l'ltyne Thvme Pry, Sajr Pag Larc Border Toadflax (inaria r.ulgaris) - Toudlax Pug Mafiled (lorcr Valerian (valeriana officinalis) - l/ahian Pug l-.ts.ter(.nam W'atv Viper's Bugloss (echrum vulgare) \{trite Campion (silcne larifolia al6a) Marlthd (onnL t\,larhledCloter, SandyCarpc! WiId Basil (chnopodrum vulgate) Wild Clematis (clemans vrtalnba) - I)ne,fpetk Prg, I laworth's Pug,Snu/l Enerald, Tlte Pem, Prctl Cbulk CaQet, l,.ean Carpet, Pag Cbalk Carpet,Snall ll/awd [:mber lfhite Clover (uifolium repens) - C/oud-ylVing Skipptr, Orange,Clonded.fn/pfur Wild Pansv ('i<>latncolor) l>lawa Wild Strawbetry (fragarra vesca) - Annkt, \i//ow.f hr//, BeauttJulCur/>et,Dark Marbled Carpet lt/ana Carpel Wild Wallflower Wormrvood (artemesiaabsrnthium) - WormwoodPuq Yarrorv (achillea m lefolium) - E.rrx Emerald, Iine .fpnk Pag Strav Belh, WonnwoodPug fuibl Ttgen Yarnw Pug L/ Pa,q Suxe.xEmerald, Gn1 Pag 7-awn1.tpcckledPa3, (.ommonPug ll hin lt'ate ' Itllow Flag Ins (iris pseudacorus)- BeltedBeaary, der Ermint -fis.rue, Barberry - .furn Vheul Blackthom/Sloe - lvlanlt, CommonEmenld, Uttle llneral.d, Mottkd Pug, lreatheredTbon, Onnge, Scalloped l Iaryl, Sulloped Oak, Aryrst T.hon, Bimstone.Ear/y'l'hon, Pah Bindhd Beaaty,Blm BordendCarpet, Bmken Bamd Carp:|, Nowmben lhle Norcmben Uzinter.SloePug,Gnen l'u.g Sharp,,7ng/edl'earotk, Tbe llagtn Btoom - Crast Emetald, Tbe Stnak, BmonJip, Ltad lltlh, SpanishCarpet, I.mtud \bl/ow Dog Rose - L' Pag L)nle'fhon, .fhould* Stipe, Baml Ycl/oa, .ftrcanter Hawthorn - Marh, CommonI'jnera/d, Utth Emerald, Nonmher, l>aleNoumher, lVinlen 140/thdPu& Pinion February 2015 Homestead, Phase1 Ecological survey BnndhdBcaul, PaleBindled Beaury.FearhendTlnn, Snlloped Spotted P4, Connon Pug Gry Pug Peppend, Haiel,'f heMagpte,Snlbqxd Oak, Lzryr Thom,Early'760-, Oak Tne l>tg, Bnken Bamd Carpu CloadedBordenBamd Linben Winhr, PaleNouember Hazel - Oak Beaat;y, Snall W'hin IVaw.TheA4agpte, Oak Beang,Bindhrt Beaug,PaleBindltd Buury, Ozk - BindledPug Oak Tnc Pug,.flting LlshenPePPend, Parplt'|bon, SmllopedHai.el,SullapedOak, Featbend'fhon, Orange, Ittnar'l'hon, Sna// Bindled Bear4, .leptemberTbon, PahNoaember WinnnMarb, SwnhedWing Lzry: Tbon,Atgust Thom,Noaember, Emerald,Unle Enerald, Iialv A4otha,il'laiden'tBlult, Alarthd ng Rcd-gyen B/otthedEnerald,Common Carper,Bnken Bamd Carpet Rowan - OrangeLtndewingWelthlVaw,tr4otthdPag,kd-gnu Cultel Stibed, \'ellowBamd Bindh. Snall Bloodtryin Wild Pnvet - Iilat Beauh,Bamd Tootbed Appendix 7: Plants and habitats to anract bats Flower Botderc and Las'ns Lan'ae and adults of many insects s'ill be catered for br introducing a wide range of food, in the form of nectat, seedsand fruit as well as r-egeation. . Grow nrght scented flowers. These anract moths and other night flyrng insects of particular importance to bars. o Plant herbs and old fashioned conage-gardenannuals attractive to insects. . Leave part of vour law'n un-morvn from about mid Nfav to encourage insect lan'ae *hich feed on grass.Allou'to seed before cuning, and rake up the hay afterq'ards. . Sorv sild flower seedcollections in your borders. Ttees and Shrubs At voodlaod edges space and sunshine combine with the $ees to gi\.e shelter and varmth, and insects rvill concenuate there. So er.en in the smallest garden trv to har.e at least one uee ot shrub. Native uees are more attracdl'e to insects than foreign species. If space is limited, silver btch and goat willorv are quick grorving and are host to many insect visitors. With a litde more space, rv to make a bank of vegeation to give vow garden a woodland edge strucrure. Shelter Belts Rows of bushes or rrees can be created or improved, encouraging concentradons of insects and providing a feeding area for bats, . . Plant up gaps in narural hedges, A row of fast-growing clpress can be yaluablc. JO Homestead, Phase1 Ecological survey February 2015 . Tiain climbets using battens agarnst a wall or fence, to provide possible roosting sltes. . Cteate a sheltered comer by using any combination of walls, fences, hedges or woodland edge at two angles. Scented hetbs Chives, Borage, Lemon balm, Ma{oram, Mint - many varieties Night border (in apptoximate order of flowering) Ecented flowerc for the Beddiag Plante Nottingham catchfly Silenenutans Night-scenredcatchfly S. noctiflora Bladdercampion S, v-ulgaris Night-scentedstock Matdriola bicomis Sweetrocket Hesperis natronalis Evening prirnrose Oenotherabiennis Tobaccoplant Nicotianaafhnis Heliotropun x hybndurr Soapwott Saponariaofficina.lis Climben Europeanhonevsuckle Lonicera captifolium July-November Italian honepuckle L. etruscasupetba July-August Japanesehoneysuckle L, japonicahalliana August-October Honeysuckle(native) L. pedclyrnenum... Julv-August White iasmine Jasminium otiicina-le Dogrose Rosacanina Sweetbdar R, rubiginosa Fieldrose R. arvensis h1 Hedera helir 37 February 2015 survey Homestead,Phase1 Ecological Bramble- many species Large tees. smzll ttees znd shrubs Oak Quercusrobur & Q. petrea .\sh Frarinusexcelstor Silverbirch Benrlapendula Field maple Acet campestre Hawthom Crataegusmonogvna Alder Ainus glutinosa Goat willow Sali-xcaprea Guelderrose Vibumum opulus Flazel Con llus avellana Blackthom Prunusspinosa EIder Sambucusnigra Buddleiadavidir Rock plaats for walls h-l-leavedtoadflax Cvmbanamwalis Vall pennl'wort Llmbilicusrupestris Stonecrop Sedumacrebertianum Appendix 9: Plants to feed birds. N{anv shrubs, climbers, uees, garden and'*-ild' plants provide food, direcdv ot rndftecdy, through berdes, seedsor the insects thev aruact. Berry ot frutt bearing trees and shn:bs will attfact members of the Thrush familV, Blackbird, Fieldfare, N{istle and song Thfush, Redwing and Robin. Also Stadrngs and, in some winters, Wa-xwing and er.en some Varblers, e.g., Blackcaps who eat berries ur the earl,l'auturnn before they migrate. Llnlessmentioned, the berries attract aU the abor-c buds plus others as specified. Shrulrst ttb llcrrics, . . . Arorua arbutifolia ff,ed Chokeberry) : bright red fruits Betberis: most forms have black/putple berdes, especiallyloved bv Blackbirds. 'Profusion': brieht violet coloured berries. Callicatoa Homestead,Phase1 Ecological survey . . o . . o . o r February 2015 Comus pogwood): blue tinted white berries (not C.N{as). Cotoneaster : prolifrc red, orange or 1'ello'*'berries - birds often choose red fust, through otange to vellow last. (..lote bernes are poisonous to humans). Euonymous eutopaeus (spindleberrv: large bright red fruits which open to emit orange red seeds.(I.,loteberries are poisonous to humans). Ilex (Hol!): red, orange or r,-ellou'benies - red berries preferred (need parmer to fruit).(ltJote berries are poisonous to humans). I{ahonia: decomtive black berries. Rosa rugosa : large red hips, particular\' attractive to (ireenfinches u'hich pick out the seeds. Sambucus (Elder): ted or black berdes - over 32 spccies rcported eating them, especi.ally Blackcap and, occasionallv,Collar Doves. Vibumum opulus (Guelder Rose) : translucent bernes Viscum album @{isdetoe): famdiar white globular bernes of this parasite that grorvs in trees, especialh'apple, are a good food source for Blackbitds. (.lirrrl>crs\\'ith llcrrics. . . o . . 'I rcesrvith llcrrics or l rr.rirs. o o . . r 'l Chaenomeles (Flowering Quince/Cydorua): r\urumn Quinces. Hedera (Ir.n) : shiny.'black berries Lonicera (Honeysuckle: tcd or black beries attact Thrushes plus Bullfinches and IUa$h and Willow Tits. Q',loteberries are poisonous to humans). P,viacantha(F'irethom) :ted, otange or vellorv berries - choose red for the birds to eat before Chnsmras usuallv with orange or vellorv to follow in a hard winter. Clematis r-italba (Old Nlan's Beard): seed heads are enjoved b,v manv brds. CrataegusmonoBrna (Hau'thom : red berries. lValus (Ctab Apple: red fruited varieties are best for birds. Prunus (Cherries): frurts quickly picked off. Sorbus aucuparia (,\{ountain Ash/Rorvan) :red, onnge or pink flushed r-hite berries. 'lhe darker the fruits the mote attiacdve they are to birds. Occasionall,vbring Spotted Flycatchcts to the garden. Taxus ft"ew): spatse red berties attracr a wide range of birds. Atttactive also to Badgers.(f.,loteberries arc poisonous to humans). rccs rvirh Scccl(-,rncs. . . Alnus glutinosa (Alde!, and Betula (Birch): seedsfrom cones enjoycd by Goldfinches, 'I'its. Greenfinches, Redpolls, Siskins and Pinus s,vlvestris(Scotspine) : pine cones from which Crossbills arid Great Spotred Woodpeckers ptise seed. 39 February 2015 survey Phase1 Ecological Homestead, 'l recs* ith llL rssotrr. Although not alwavs welcome, Bullfinches stip the buds of fruit tlees in late wintet and eadY sPring' . ( iartlcn l'lrrnts. . Crocus: vellow and orange flowem are atuactive to Sparrows because they contain yellow catotene to brighten up their plumage for the breeding season' pigment -Ec-hinops nuo (Globe Thistle: seed heads are eaten by Goldfinches end flower heads attract insects. Helianthus (Sunflower: seed heads afe eaten by Green6nches. The necar attracts a wide . . tange ofinsecrs. Lavandula pavender): flowers going to seed aie attractive to Gold6nches' Primula @olyanthus/Primtose): vellow and orange flowets are atEactive to Spartows, . . Wilcl l)lanrs. to you can ptol.ide a haven for wild plants to exist in their own right recteating a wild .meadow 'u/ild' nursery giown Plants atftact in;ects rvhich, in tum, atract birds and other wildhfe. We sell of garden. srild in a comer vout can go so tlat,r'ou throughout the 1'ear . . o . . Berony. Bird's Foot Trefoil. Common Poppv - seedsare favourite food of Finches. Field Scabious. Great€r Knapweed. . r . . . . . . . N'IeadowCranesbill. lvfusk l[al.[ow. Ox Eye Dars).. Oxlip. Pdmrose. Rough Harvkbit. Self Heal. Teasel - seed heads are a favourite food of Goldfinches. Wild Srawberry l hc i-arvrr. This is one of the principal soutces of food for birds '*'ho enioJ- feeding on insects including-:Ants eaten by Gteen woodpeckets; Leatheriackets b,v Starlings; Snails by Song thrushes; Slugs by Toads and Worms bv Blackbirds, Robrns and Thrushes. (,rlvcr ancl l)rotcctl<ltt. 40 Homestead, Phase1 Ecological survey February 2015 By suttounding yow garden by thick and often pdckly hedging and dotting suitable shtubs around, you cao provide safe lgsdng b4vens that ate protected &om manuding cats and even the unwelcome .ttention of rmftiendly hurans. The most successfulshrubs and trees for this purpose include:. o o r o o r e r Conifets especiallychamaecypads,Taxus Sew) and Thuja Placaa. Crataegus. Eleagnus. Hedem (Ivy) up a ree. Ligustrum (Privet) especiallyfor Blackbirds. LonicemftIoneysuckle). Pittosporum. Salix caprea(!?eeping Kilmamock Willow). Vibumum. Appcndix 10:Native Plane for Bees Nativeplantsshouldbe -r'ourfusr choiceto hc"lporrrnativcbees.Listedbelorvaresomeplantsthataregrod sourcc'sofncctar or pollcn tor bccs. Iloth thc commor ;rnd l,adl oamcs of rhc plant gr:nus arc giren. This list is uot cxhauslivei there are rnanl o rer plarrts grx;rl tirr bces. lodividLral spccies have not been induded becausc rte hope the list rvill be useful across the Ll.S. N<.rtall ol these gcnera vilJ hare spccies in vour local area, bur thev do rcprescnt planm rhar vrll grov,' in a varie$' of cnviroruncnts. LTsea wildfl<ru,'crguide or contact local nursc.dcsto fird 1.out local spccies. . r . . . . e e o o . . o r r . r . r . r o Astcl.'l,r/rr Black-c)-edSusan Pslbe,kia Caltrop K itnvcmia Creosetc bush lr.tza Cun'ant lUluer El<let.fumhuuu (loldenrod.tofidu.g Ilucklcbctt I ittrinitn Joe-p1.e rveed linpatoiam I tpine l,.u|iat.t Otegcnr grape l3ethait Penstemot Pet unot Purplc cotefl<twcr L:,thiaaqu Rabbir-brusb ( )I4,.,otlutnrul Rhotfodcn<lron Ntododendnt SzBe Sah'id Scorpion-w'eed ltltuc/ir Snou'lxn)' -lyntphaiuryo.t Strnccrop .f,,y',azr Sunflr>rvcr Llelitntltut \\rild buckvheat fiiagonun \t ild-lilac Ciuttotltu 4T February2015 survey Phase1 Ecological Homestead, \\illorv .l',/rt Garden plante fot beee l,brvcr beds in gardens,businesscampuses,and parks are gteat placesto have bee-tricndll'planrs' Native plauts s.ill createa beautifulgardenbut somepeopleprefcr "grclcn" plants.Ir'lanvgardenplantsate varieties of native planrs,so this lisr on\- includesplants ftom other countries-"exoiic" plants--andshould be usedas a supplementto rhe nariveplanr lisr.-\s uith the natir.eplants,this list is trot exhaustive. . . r o o o . r . . tsasil Odnrun Cotoncasteraolo|?tl rr English lavender lzuttdula Giant hyssop.'lqxlache Globe rhistlc lihitoPt Hvssop Ff r:raPr* ltlatioram Orilunan Rosemag.Ronniwt \\!allflo'*'er F'4imtn Zinnia Zimia Appendix 11 Othet rccommended epecies Stendrd aative tlece Field maple Field maple AErMnFtln Comrnon Alder Silvet Birch Aliutt glttirrota Betrlapndilz ptfusnrs Bctula Catpint bclaltt Dowrry Birch Hombeam SweetChesmut Beech Ash Ash Common Walrut Comrnon Larch Amcarrrm Ca$ancasatitta Fagn ghntica Fruttittrc cxnltior Frwcinu cxekior Black Mulberry ScotsPine Wild Cheny Jaglawngia I-4ix d.ddu Mons gra Pin* ghuttrit Pmnxsavfum Bird Chetry SessileOgrk Pnrr i Padar ptmttptmea Peduncllate Oak Common Whitebeam paawrnfur Sorfuiana Rowan SorbwaauParit Sotbtsfuaettiu ServiceTree 42 Homestead, Phase1 Ecological survey Wild ServiceTree \0fych Elrn February 2015 Sorbrctominatit Ulnn glabm Native hedgerow Hawthom Guelder Rose Hazel Cmteagatmongna VibernunopaLu Corylas awllana Netive Shrubs Barberry' Dogwood Ber*ert aalgdrit Hazel Comutungaizea Corylatanllaru Ivlidland Hawthom Cmtacgus lawigtta Ha.*thom Broom Crataegrcmomgna Cjtitrcwpius Spindle Eaonlmu ewupaeat Prangtlaalnrc Hanalus lnPdn Alder Buckthom HoP Holly Common Pdvet Honeysuckle Ilcx aqnJolian Blackthom Buckthom Pmnrctptnota Field Rose Dog Rose Eldet Rosaamensi.t Rotarzaiaa Sanbucarnigra Ulex ermpaus Gorse Wayfaring Trce GuelderRose Lignstmn aulgn Ladinra peritlmewn Rhamntlscathartica Vibanam la am Vibnun opalut Fruiting rees Apple'Btamley'sSeedling' 'Cox's Apple Self Ferule' 'Early Apple Victoria' Apple James Gneve' Damson'Merr'.weather' Mahssp. Malu rp. Malartp. Malasg. Malu g. Malu sp. P*nussp. Pnansr darnertita rp. Plum Victotia' Pnut Peartseth' U*ttp. Apple l-arton's Superb' Apple 'Spartan' Cherry 'Stella' domeslitatp. 4t suNey PhaseI Ecological Homestead, 'Conference' Fig U*t tP. Fiac caim Apricot Prarut amte au Almond Pmnu d$bir Pear The above is a sugested list, there may be other varieties. Fruiting shrubs Blackcurant Nbu nigan Blackberry' RtbasJfttimra sP. Nbesutrip Gooreberry Raspber4' Redcurrant St!a$/berry Rrfut idacut Nbcsrubmn Fmgariax ananara The above is a sugested List,there are many other altematives' Ornamental Shrube Aucubajaponica'Ctotonifolia' Amelanchiet Canadensis Buddleia altemifolia Cdlistemoncittinus'Splendens' Camellia'Inspiration' 'Alba SimPlex' Camellia japonica Blue' clandonensis'Heavenly Car,vopsis Ceanothus'AurumnalBlue' 'Blue Mound' Ceanothus Ceanothusthrysifloms rePens 'Aztec Pearl' Choisya temata Cistus x corbatiensis 'Si.lverPink' Cistus Comus Canadensis Daphne x butkwoodii Escdlonia'CdmsonSpire' 'Silver Euonymus fortunei Queen' japonica Fatsia Garria elliptica JamesRoof Hebe x franciscanaBIue Gem' Hebe 'Mrs li'inder' Hebe rakienss 'Blue Wave' Hydnngea macrophvlla 'G Hy&angea paniculata randiflora' February 2015 Homestead, Phase1 Ecological survey February 2015 l{vpericurnx moseranurn LavandulaangustifoliaVera' kvcesteria Formosa Lonicetanitida'Maign-rn' Ivlahoniaaquifolium Ivlahoniajaponica Oleria x haastii Perovskiaatriplicifohatslue Spite' Philadelphus'BelleEtoile' Philadelphus'BouquetBlanc' 'Red Potentilla r\ce' Prunusx cistena Pytacantha'Orange Glow' Pyracantha'So[eld'Or' RosmarinusofEcinalis Rubusoderah.rs Rubusphoenicolasius Sarcococca confuse Skimmiajaponica'Foremanii' Skimmiajaponica'Rubella' Spireax bumalda 'Goldflame' Sl'mphoricarposx chenauldi'Hancock' Viburnum bodnantense'Dawn' Vibumum x butkwoodii Vibumum davidii V'ibumumopulus'Sterile' \ribumum pLicatum'Mariesii' I'ibtnan tinrs l/ibsnan tinh 'Eve Price' Wildflowet seeding areas: seed mixtures, Landlife 'Country Lane' mixture and Landlife 6Butterfly borded mixture. Theee to be supplemented by plug planting of the speciesdefined below. Landlife Butterfly mixture: Birdsfoot trefoil Comflower Eveningprimrose Field scabious Ladysbedstmw Lesserknapweed Ox-eyedais.v Red campion Foxglor.c Vipers bugloss 45 survey Phase1 Ecological Homestead, February 2015 Landlife Botder mixture: Agnmon,v Cow parslev Foxglove Hedgebedsrau' Hedge garlic Lesserknapweed Nleadowsu.'eet Oxevedaisy Netde leavedbellflou'er Red campion St.Johnswort \\' od avens Plug plants; 50 each of: L,esser knapweed Kidney vetch Birdsfoot trefoil Appendix 12: Great CreetedNewt Ecology (A Summary) Like all Bnush amphibians, grent crested newts relv on waterbodies for breeding but other*ise tbey spend much of their Liveson land (see F-igure1: The ne.r.t year). Some adult great crested ne$Is corunence mrgration to rheir breeding ponds as earh' as the Frrstfrost-free davs in lateJanuary',but most move later, v'ith rhe majority reaching rhe ponds by mid N{arch.This mosement, Iilie most ovedand dispersal in the great crested neul is influenced by a range of factors, notablv evening temPeraturesand rain. Great crested newts are ectotherms (ie thcy re\.on extemal heat sources to raise their bod1.'temperature to a level that allows actiriry) and have permeable skins, so most movement occuls when the air tempelatute is above around 5oC and there is, or has recendy been, rain. Nfovement at night ma'1'reducepredation risk, and certainlv makes desiccation (dehvdration) lesslikel,v.T'his gradual migration to the breeding pond is in conuast to the shonet period of mrgration to ponds observed in frop and toads. 'I he peak coutship and eggJaving period is normallv from mid-lvlarch to rrud-N{a1'.During this time, adult 'dance', w'hich mav result in the female taking males attract females bv undertaking a compLicatedcourtship up his sperm (in the form of a packet called a spermatophore) into hcr cloaca. Following this, the female lays eggs individually. mosdv on r}e leavesof submerged plants. She mav lay'around 200 eggs Per season,ove! a period of severalweeks. The larvae hatch out after around 3 weeks, and then take another 2 to 3 months to complete lawal der-elopmeot. Dunng this rime they feed on a range of pre,v,including small crustaceans,fly larvae, frog and toad tadpoles and othcr newt larvae. .{dult nests generallv leave the breeding ponds ftom late NIay onrvards, dris dispersal being gradual arrd ne$ts may ren11noccasionally to feed. Adult males tend to remain in the pond for longer than females. Homestead, Phase1 Ecological survey February 2015 Once the lan'ae haue completed metamorphosis (the traosition &om aquatic lan'ae to land-adapted juveniles, also called efts), thev emerge from the pond This emergencegenerally begins in eatly August and lasts for around two months. lt then takes between 2 and 4 vears ro reach sexual maturity, during rvhich rime the immature newts *'ill be largely teffestrial @asedon land). Adults and immature newts spend the wioter in places that afford protection from frost aod flooding, often underground amongst tree roots, in mamrnal burrow's, or abor.e gtound under suitable refuges like deadwood or rubble piles. Hibemation may lasr from October to Februan'. !(trilst on land and outsideof the hibemationpetiod, geat crestednews requirerefugefrom exttemesof weathet,meaningthat during the day theywi.[ rest in dcnsevegeration,undet refuges,or undergtound.Thev will also fonge on land, rakinga rangeof invcrtebrateprcv. For their size, great crested ne$ts are relatir'-elyIong-Livedanimals. There is often a high monality during the egg and lan-al stage (indeed, 50o..i'of all cgp dic before hatching due ro a chromosome abnormality), but once on Iand year to year sun-ival is relatively high. Post meranrorphic grear cresred newts have to{ns in their skins u'hich make them unpalatable to maov predators, and this mav aid sunival. Exceptionally, adults can live for over 15 vears, but the majotity will sun-ivc onlv a few rears past sexual maruriry..[uvenile and immatue animals normallv outnumbet adults considerably, *rough someumes a cohort (the collectivc name for all animals hatched in a single vear) may be reduced or absent becauseofpoor sun'ival, perhaps due to earl.r'- ponddrying. Great crested newts in a given area often form a metapopulation, ie a series of sub-populatioff that are linked bv dispersal of individuals. This ststem often applies to specieswhich depend oo habitats which var;. rn qualirl,-over rime, aod n'here the disttibution of suitable habitats mav change. Great crested nesits ofte o inhabit ponds that are part of a 'pond clusrer', and individuals (and hcnce genes) may movc befween ponds with raning ftequencl. This ability to shift between locations is beneficial, for example, if a pond were ro become less suitable for breeding through prolonged droughq as grear crested nerr.tsmav move to newly created or restored ponds. Small, isolated populations based on a single pond are normallv less lkelt'ro persist in the long tcrm.'I'o some extenq the merapopularion concept complicatcs the srudv and conse.\,'atron of this species,since impacts on a single pond may have knock-on effects on ncw'ts in nearby ponds. Though adult newts often rerum to rhe same breeding sitc. they may also move beween differenr ponds both within and between years.Adults mav occasionally skip a reproductive seasonin order to mol.e to a nerv pond. Dispersal to new sites mat thus occur br- both adult and immaturc netts. However, it would bc wen- unusual for a given pond thar rvas previouslv the centrc of breeding actir.iry for a r.iablepopulation, ro suddenly'bse'its ncwts (unlessa major catasrophe occutted,such as predatory fish 2015 February survey PhaseI Ecological Homestead, introducrion). Even if orhcr, good qualiw sites u'ere crcated nearby'it is likell' that a population would remarn ar rhe original sire, but rhat some dispersa.lwould occur tesulting in brecding in the new ponds. Great crested neuts har.e been found to move over considerable distances (up to l.3km from breeding sites). However, the vast majoriq,' of newts urill inhabir an area much closer to the pond, and the exact distribution and migration pattems of oewts on land depends on a varieh o[ facton. The qualiry of terresuid habitat near to breeding ponds is imporrant, as are the lack ofbarriers to dispersal (such as fast-flowing rivers, or very -fhe distriburion of ponds and hibemation oppom.rnities mat' also influence movements. Onlv busy roads). deta.iledsunev at a given site will rel'eal the direcdon and amount ofdispenal that occuts, Several studies har.e been conducted $'hich reveal a grear deal of variation, but gleat crested newts commool-v move bet*'een ponds that arc u'ithin around 250m of each other. To summarise habitat requiremenrs, great crested newts require u'aterbodies to be able to reproduce effectively, and these are Spicallv ponds. Various tvpes of ponds are used; most cornmonl1 medium sized ones, such as field ponds, clav pits, mad pits, moats, Iarge ditches and quarrl'ponds. Great ctcsted nevts are mosr commonlv fourrd in lowland. neutral ro high pl I ponds, v'hich are rvell-vegetaredand not too shaded Ponds that occasionally d4. our in summcr, even if this kills lan'ae, mav still be suitable The presence of predatorl Esh and a high deosity of warerfowl reduces the value of ponds, often to the point where they will not be used for breeding. Ponds not used bv great crested neu'ts for breeding can still be of importance for the population as thet ma,vsupport prel (for instaoce, temporan: ponds uscd bl frogs mav be visitcd b,vadult ncwts). Terrestrial habitats are required for feeding, dispersal and hibemation, and trpicallv this would include 'wasteground' or quarn' floors. The kev factors seem to be the grassland,scmb, \loodland. hedgerou's, ar.ailabilin of ptev speciescombined with the presence of dense gound vegetation or voids in tle substrate ro allor.refuge; shelters on t}te surface, such as logs and rocks, are also valuable. Great crested newts often occur in metapopuladons, so connecdons betw'eenponds (and betwecn populations more distant) are also uTrPorranr, Note rhat populations will be influenced by factors such as altirude, \,eather, geology, vegetation aod disrurbance. For instance, it is knovn that at some sites, low numbers of adults remain in the pond to over vinter, and that i1 some populations (particularly in cool, upland, low nutrient areas)lan-ae regularly overwinter, ro emcrge the follow-ing spnng The upper r\a.odiaffams show the changesin the numbers of nerts found in dre breeding pond and in the surrounding rerresrial habitat. The thickness of the bar indicates the proponion of individuals; a tlotted line indicates that small numbers of individuals follow this pattem at some sites.The lower diagram illusyates the riming of key actir.itiesin the ne*t life clcle based on npical, lowland, central England activiry. Figure t Upper two diagrams modified after BHS (1996). 48 2015 February survey Phase1 Ecological Homestead, FEB MtR IPR N.iTYJUN JUL tUG SEP OCT NOV OBC POI{D EOGS LARVTE I I\4IIATURES AI'IJLT' LAIID JW!+ \4113 ADULTS KEYACTIVITIES I ||ltiianqr lclJll atlli6Ela E. loa-laYltl6 UtvAL ciswl|{ + D!VELO"CNT at!!l r,iEaallorl Fio$ tot{o iflltiattFlF]!r JUrt||LtgaeRAno{ JAN FE MARAPRT,IAYJUTIJUI AuG 6EP OCT NOVOEC (tinglish Nature, (20()l) (irear Crcsted Net't Nfitigation (iuidelincs) 49
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