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t<br />
Cent re for<br />
Ecology & Hydrology<br />
N AT U RAL ENV I RO N M ENT RES EA RC H C O U N C I L
PLANTATT<br />
<strong>Attributes</strong> <strong>of</strong> <strong>British</strong> <strong>and</strong> <strong>Irish</strong> <strong>Plants</strong>:<br />
Status, Size, Life History,<br />
Geography <strong>and</strong> Habitats<br />
for use in connection with the<br />
New atlas <strong>of</strong> the <strong>British</strong> <strong>and</strong> <strong>Irish</strong> fl ora<br />
M. 0 . Hill, C. D. Preston & D. B. Roy<br />
Biological Records Centre<br />
NERC Centre for Ecology <strong>and</strong> Hydrology<br />
Centre tor Et ctotry entl Hydrology<br />
Bush Es te:e<br />
Penicuik<br />
Midlottna t<br />
6 326 OAS<br />
2004<br />
10 0 0 (T 4 - 2 0 0 1
@ NERC Copyright 2004<br />
Print ed in 2004 by Raven Marketing Group, Cambridgeshire<br />
ISBN I 870393 74 0<br />
The Cent re for Ecology <strong>and</strong> Hydrology (CEH) is one <strong>of</strong> t he Cent res <strong>and</strong> Surveys <strong>of</strong> the<br />
Nat ural <strong>Environment</strong> <strong>Research</strong> Council (NERC). Established in 1994, CEH is a mult idisciplinary,<br />
environmental research organisat ion wit h some 600 staf <strong>and</strong> well-equipped<br />
laboratories <strong>and</strong> fi eld facilities at nine sites t hroughout t he Unit ed Kingdom. CEH's<br />
mission is to "advance t he science <strong>of</strong> ecology, environmental microbiology <strong>and</strong> hydrology<br />
t hrough high quality <strong>and</strong> internationally recognised research leading to bett er<br />
underst<strong>and</strong>ing <strong>and</strong> quant ifi cat ion <strong>of</strong> the physical, chemical <strong>and</strong> biological processes relating<br />
to l<strong>and</strong> <strong>and</strong> freshwat er <strong>and</strong> living organisms wit hin t hese environments".<br />
The Biological Records Cent re is operated by CEH, based at CEH Monks Wood. BRC is<br />
joint ly funded by CEH <strong>and</strong> t he Joint Nature Conservation Committ ee (www.jncc.gov.uk),<br />
t he latter act ing on behalf <strong>of</strong> the statutory nat ure conservation agencies in Engl<strong>and</strong>,<br />
Scotl<strong>and</strong>,Wales <strong>and</strong> Nort hern Irel<strong>and</strong>. CEH <strong>and</strong> JNCC support BRC as an important<br />
component <strong>of</strong> t he developing National Biodiversity Network. BRC seeks to help<br />
nat uralists <strong>and</strong> research biologists to co-ordinate t heir eff ort s in studying the occurrence<br />
<strong>of</strong> plant s <strong>and</strong> animals in Britain <strong>and</strong> Irel<strong>and</strong>, <strong>and</strong> to make t he results <strong>of</strong> these st udies<br />
available to others.<br />
For furt her informat ion, visit www.ceh.ac.uk.<br />
Cover photograph shows the endemic plant Coincya wright ii on the cliffs <strong>of</strong> Lundy (courtesy <strong>of</strong><br />
Roger Key, English Nature).<br />
Published by<br />
Cent re for Ecology & Hydrology<br />
Monks Wood<br />
Abbot s Ripton<br />
Hunt ingdon<br />
Cambridgeshire<br />
PE28 2LS<br />
Copies can be ordered by writing to the above address or by telephoning<br />
0 1487 772400, or faxing 0 1487 772558.
CON TEN TS<br />
Int roduction<br />
Species, fam ilies, stat us <strong>and</strong> change 3<br />
Species <strong>and</strong> families . 3<br />
Native/afi en status . 3<br />
Conservation status . . . 3<br />
Rarity status . 3<br />
Change Index . 4<br />
Size <strong>and</strong> life history at tributes . . .<br />
Height <strong>and</strong> length .<br />
Perennation . 5<br />
Life form . . . . . 5<br />
Woodiness<br />
Clonality<br />
Geographic attributes<br />
European <strong>and</strong> wider distributions, <strong>and</strong> continentality . . 9<br />
Native distribution <strong>of</strong> species alien in Britain <strong>and</strong> Irel<strong>and</strong> . . . 10<br />
Counts <strong>of</strong> 10-km squares in the New Atlas . 10<br />
Climatic means 11<br />
H abitat att ributes . . . . . 12<br />
Coastal species . 12<br />
Broad Habitats . 12<br />
Ellenberg's indicator values . 14<br />
Light values (L) . 14<br />
Moisture values (F) . 15<br />
Reaction (R) . 16<br />
Nitrogen (N) . . . 16<br />
Sak tolerance (S) . . 17<br />
Listing <strong>of</strong> species with their attributes 18<br />
A ppendix 6 1<br />
Sources for plant height . . 6 1<br />
Defi nition <strong>of</strong> life forms . 6 1<br />
Examples <strong>of</strong> how fi fe-form criteria are applied . . 62<br />
Links between life forms <strong>and</strong> plant height . 63<br />
Clonality . 64<br />
Broad Habitats . 64<br />
Initial calculation <strong>of</strong> species' preferences for Broad Habitats . 68<br />
Extension <strong>and</strong> validation <strong>of</strong> species' preferences . 69<br />
Acknowledgem ent s 70<br />
Bibliography 7 1
IN TR OD UCTI ON<br />
In the course <strong>of</strong> our research on geographical distributions <strong>and</strong> climate change, we have<br />
frequent ly wanted to characterize the plants t hat const itute the wild fl ora <strong>of</strong> Britain <strong>and</strong> Irel<strong>and</strong>.<br />
Several sources <strong>of</strong> information were available, including t he Electronic Comparative Plant Ecology<br />
(Hodgson et al., 1994), t he Czech clonal plant database Clop la I (http.//www.butbn.cas.ce kfi mes/<br />
clopla I .htm), t he BSBI database (http://www.bsbi.org.uk/html/database.html), t he Ec<strong>of</strong>lora database<br />
(Fitter & Peat, 1994), <strong>and</strong> the indicator values <strong>of</strong> Ellenberg (Ellenberg et S., 1991). Inevitably, these<br />
sources were not sufi cient for our purposes, <strong>and</strong> we have gradually assembled our own set <strong>of</strong><br />
att ribute data, linked to t he database <strong>of</strong> the Biological Records Centre (BRC).<br />
The establishment <strong>of</strong> the National Biodiversity Network (NBN) provided an additional st imulus<br />
to the assembling <strong>of</strong> att ribute data, <strong>of</strong> ering a suitable platform for online searches for species<br />
att ributes. Some <strong>of</strong> the information published here is also available from the NBN gateway<br />
(www.searchnbn.net). In 2002, the publicat ion <strong>of</strong> the New Atlas <strong>of</strong> the <strong>British</strong> <strong>and</strong> <strong>Irish</strong> Flora (Preston,<br />
Pearman & Dines, 2002), toget her with results <strong>of</strong> a companion project to analyse change<br />
(Preston,Telfer et aL, 2002), allowed us to complete the dataset that is presented here.<br />
The dataset is partly old <strong>and</strong> partly new (Table 1). Biogeographic elements <strong>and</strong> Ellenberg values<br />
are taken with few modifi cat ions from earlier publications (Preston & Hill, 1997, 1999; Hill et<br />
1999). Information that depends directly on the New Atlas is either new or (Change Index) is<br />
taken from the text <strong>of</strong> the New Atlas. Data on t he Broad Habitats <strong>of</strong> plants are mostly drawn<br />
from an unpublished report (Preston et al., 2003). Information on plant height, perennat ion, life<br />
form <strong>and</strong> clonal growt h was assembled from a variety <strong>of</strong> fl oras <strong>and</strong> monographs, with some<br />
personal observation; it is a new compilat ion. Furt her details <strong>of</strong> t hese att ributes are provided in<br />
t he following pages. The attribute categories are tabulated (Tables 2- 13), with the numbe <strong>of</strong> taxa<br />
in each category listed in the column 'N='.
Table I . <strong>Attributes</strong>, codes <strong>and</strong> names listed as columns in PLA NTATT<br />
Colum n nam e<br />
(a) Status <strong>and</strong> taxonomic<br />
Taxon name<br />
Family<br />
Nat ive status<br />
Conservation status<br />
Rarity status<br />
Change Index<br />
(b) Size <strong>and</strong> life form<br />
Height (terrest rial)<br />
Length (aquatic)<br />
Perennation<br />
Life form<br />
Woodiness<br />
Clonal spread<br />
(c) Geography & climate<br />
Major Biome (European<br />
dist ribut ion)<br />
Eastern limit code<br />
Continentality in Europe<br />
O rigin <strong>of</strong> alien taxa<br />
Number <strong>of</strong> 10-km squares in<br />
Britain (including Isle <strong>of</strong> Man)<br />
Number. <strong>of</strong> 10-km squares in<br />
Irel<strong>and</strong><br />
Number <strong>of</strong> 10-km squares in<br />
Channel Isl<strong>and</strong>s<br />
January mean terhperature<br />
July mean temperature<br />
Annual precipitat ion<br />
(d) Habitat<br />
Coastal<br />
Broad Habitats<br />
Ellenberg indicator value<br />
A bbreviat<br />
ion<br />
Fam<br />
NS<br />
CS<br />
RS<br />
Chg<br />
Hght<br />
Len<br />
P I , P2<br />
LF1, LF2<br />
Clonel ,<br />
Clone2<br />
E I<br />
E2<br />
O rigin<br />
GB<br />
IR<br />
CI<br />
Tjan<br />
Tjul<br />
Prec<br />
Co<br />
Br Habitats<br />
Source or ot her comment<br />
Name in current flora (Stace, 1997)<br />
Stace (1997)<br />
New Atlas (Preston et al., 2002)<br />
Chefi ngs (2004)<br />
Calculated from New Atlas data<br />
New Atias (Preston et al., 2002)<br />
Several sources, listed below<br />
Several sources, listed below<br />
Mainly Clapham,Tutin & Warburg (1962)<br />
Clapham et al. ( 1962), heavily revised<br />
Mainly Clapham et al. ( 1962)<br />
Sources are listed below; clone2 is mainly blank<br />
Part <strong>of</strong> biogeographic element<br />
accor ding to Preston & Hill ( 1997)<br />
Part <strong>of</strong> biogeographic element<br />
according to Preston & Hill ( 1997)<br />
Preston & Hill ( 1997) plus additions<br />
New Atlas (Preston et al., 2002)<br />
New Atlas (Preston et al., 2002)<br />
New Atlas (Preston et al., 2002)<br />
New Atlas (Preston et al., 2002)<br />
Calculated from New Atlas plus climat ic data<br />
Calculat ed from New Atlas plus climat ic data<br />
Calculat ed from New Atlas plus climat ic data<br />
Calculated from New Atlas plus Ellenberg salt value<br />
Preston et al. (2003), plus previously unreported data<br />
for aliens<br />
L, F, R, N, S Hill et aL ( 1999)
SPE CIES, FAMILIES, S TA TUS A ND CHAN GE<br />
Species <strong>and</strong> families<br />
The list <strong>of</strong> 1885 taxa includes all nat ive <strong>British</strong> <strong>and</strong> <strong>Irish</strong> species, as well as natives <strong>of</strong> the Channel<br />
Isl<strong>and</strong>s not known from Britain or Irel<strong>and</strong>. There are no species restricted to the Isle <strong>of</strong> Man. All<br />
archaeophyt e species are included, plus a number <strong>of</strong> well-established neophytes.A small number<br />
<strong>of</strong> subspecies, hybrids <strong>and</strong> aggregate species are also included. The number <strong>of</strong> taxa has been<br />
slightly increased from the 1791 t hat were listed for Ellenberg indicator values (Hill et al., 1999).<br />
Most <strong>of</strong> t he addit ions are <strong>of</strong> neophytes, which, following the New Atlas (Preston et al., 2002), we<br />
now t hink t o be suffi cient ly common or potent ially interest ing to be included.<br />
The names <strong>of</strong> families have been abbreviated to four letters <strong>and</strong> follow Stace ( 1997).<br />
Native/alien status<br />
Species <strong>of</strong> uncertain stat us are classified as 'nat ive or alien'. Int roduced species have been<br />
classifi ed as archaeophytes, neophytes <strong>and</strong> casuals (Preston et al., 2002). Bot h archaeophytes <strong>and</strong><br />
neophytes are introduced species which are present in t he wild as naturalized populations, that is<br />
t hey are spreading vegetat ively or reproducing ef ectively by seed. An archaeophyte is a plant<br />
t hat became naturalized before AD 1500. A neophyte is one that was first int roduced after 1500,<br />
or was only present as a casual before 1500 <strong>and</strong> is naturalized now only because it was<br />
reint roduced subsequent ly. In contrast to archaeophytes <strong>and</strong> neophytes, a casual is a plant that is<br />
present only as populat ions which fail to persist in the wild for periods <strong>of</strong> more t han<br />
approximately fi ve years. Such a species is dependent on constant reint roduction (Macpherson et<br />
at , 1996).<br />
Hybrids between two alien parents which were introduced to the wild as hybrids (e.g. Crocosmia<br />
x crocosmiifl ora, Euphorbia x pseudovirgata) are classified as neophytes. Only hybrids between<br />
which have been formed spontaneously in the wild between two alien parents are classified as<br />
'AX'.<br />
Conservation status<br />
The conservat ion status <strong>of</strong> plant s is coded according to the system proposed by Hodgetts,<br />
Palmer & W igginton ( 1996); see also Palmer et al. ( 1997). This status is an assessment <strong>of</strong> threat<br />
rather t han rarity, alt hough closely related to rarity in that only species known at the time <strong>of</strong> the<br />
assessment in less t han 10 1 10-km squares have been allocated t o one <strong>of</strong> the categories listed.<br />
The stat us list ed is t hat given by Chefi ngs (2004). This replaces t he stat uses provided in the Red<br />
Data Book (W igginton, 1999) <strong>and</strong> Scarce plants in Britain (Stewart , Pearman & Preston, 1994).<br />
Cheffi ngs assigns a conservat ion status to nat ive species <strong>and</strong> archaeophytes, with only a few<br />
exceptions. PLA NTATT cannot be used to provide a complete list <strong>of</strong> threatened taxa as many<br />
subspecies listed by Cheffi ngs are not t reated separately by us.<br />
Rarity status<br />
Rarity status is based on counts <strong>of</strong> the number <strong>of</strong> 10-km squares in Britain <strong>and</strong> t he Isle <strong>of</strong> Man in<br />
which the plant was recorded as a nat ive in t he period 1987- 1999. Rare plants are those<br />
recorded in 1- 15 10-km squares during t his period; scarce plants are recorded in 16- 100.The<br />
t hresholds were those that were used in defining rare <strong>and</strong> scarce species for the Red Data Book<br />
<strong>and</strong> Scarce plants. Rarity status, however, is solely a measure <strong>of</strong> rarity rat her than threat, <strong>and</strong> is<br />
based on data from the New Atlas. Cheffi ngs assigns a conservat ion status to nat ive species <strong>and</strong><br />
archaeophyt es, with only a few except ions. PLANTATT cannot be used to provide a complete<br />
list <strong>of</strong> t hreat ened taxa as many subspecies listed by Cheffi ngs are not t reated separately by us.<br />
Alien species have by defi nition no nat ive records, <strong>and</strong> therefore are not given a rarity status.
Table 2. Nat ive stat us, Conservation stat us <strong>and</strong> Rarity stat us<br />
At tribute <strong>and</strong> codes N= Explanation<br />
(a) Native status<br />
(b) Conservation status<br />
(c) Rarity status<br />
(d) Change Index<br />
AC 12 Alien casual; many are crop plants<br />
A N 259 Neophyte, alien introduced after 1500<br />
A R 15 1 A rchaeophyte, alien introduced before 1500<br />
AX 1 Spontaneous hybrid between two alien parents<br />
1362 Native, not endemic<br />
NA 46 Native or alien (nat ive status doubtful)<br />
N E 47 Native endemic<br />
N H 7 Spontaneous hybrid between two native parents<br />
CR 20 Critically endangered<br />
D D I Data defi cient<br />
EN 34 Endangered<br />
EW 4 Ext inct in the wild<br />
EX 10 Ext inct<br />
VU 119 Vulnerable<br />
(values)<br />
933 Present, not rare or scarce<br />
234 Rare ( 1- 15 10-km squares in Britain, 1987- 1999)<br />
254 Scarce (16- 100 10-km squares in Britain, 1987- 1999)<br />
27<br />
(blank) 423 Alien taxa<br />
Absent from Britain <strong>and</strong> Isle <strong>of</strong> Man as a native, but native in<br />
Irel<strong>and</strong> or t he Channel Isl<strong>and</strong>s<br />
12 Apparently ext inct (not recorded since 1986)<br />
2 Insufi cient data available to assess rarity<br />
Change between 1930- 1960 <strong>and</strong> 1987- 1999<br />
Change Index<br />
The Change Index (Telfer et al., 2002) measures the relat ive magnitude <strong>of</strong> change, comparing the<br />
period 1930- 1960 with 1987- 1999. It is explained in more detail in t he Appendix. It ranges from<br />
-4.78 for the critically endangered Gahum tricornutum to 4.70 for t he much more frequent ly<br />
recorded Prunus laurocerasus. The Change Index has not been calculated for species not included<br />
in the fi rst Atlas <strong>of</strong> the <strong>British</strong> Flora (Perring & Walters, 1962). Consequent ly, several aliens such as<br />
Amsinckia micrantha <strong>and</strong> Crassula helmsii, which have increased spectacularly in the intervening<br />
period, lack a value for the Change Index.
SIZE A ND LI FE HIS TOR Y A TTRIB UTES<br />
H eight <strong>and</strong> length<br />
Heights, measured in cent imet res, are given for terrestrial (or emergent) plants <strong>and</strong> lengths (cm)<br />
for submerged aquatic plants. A few amphibious or emergent plants such as Persicaria amphibia<br />
are scored for both height <strong>and</strong> length.<br />
These values are int ended as a general indication <strong>of</strong> the size <strong>of</strong> the plant. For procumbent plants,<br />
heights are an indicat ion <strong>of</strong> the height <strong>of</strong> the less procumbent shoots. For scapose plants <strong>and</strong><br />
ferns, heights are not stem lengths but leaf lengths. Likewise, lengths for isoetids (i.e. linear-leaved<br />
rosette-forming root ed aquat ics) are in fact leaf lengths. For example Lobelia dortmanna has<br />
length 4 cm, which is certainly not the length <strong>of</strong> t he scape.<br />
Height <strong>and</strong> length values were drawn from a variety <strong>of</strong> sources, which are detailed in the<br />
Appendix.<br />
Perennat ion<br />
The categories are annual, biennial <strong>and</strong> perennial. Biennial is used as a short h<strong>and</strong> to denote also<br />
monocarpic perennials. For example Car /Ma vulgaris <strong>and</strong> Heracleum mantegazzianum normally<br />
take several years to reach maturity but are categorized as biennials. The sources <strong>of</strong> data for<br />
perennation are most ly t he same as t hose used for height <strong>and</strong> length. In a few cases (e.g. Linum<br />
catharticum), we have relied on personal communication <strong>and</strong> scientifi c papers rat her than fl oras.<br />
A relat ively small number <strong>of</strong> species fall into more t han one <strong>of</strong> these categories. The secondary<br />
category is intended to be either less frequent or equally frequent. Thus Poe annua has primary<br />
perennation category P I =annual <strong>and</strong> secondary category P2 = perennial. Several fl oras suggest<br />
t hat Cardamine flexuosa <strong>and</strong> Montia fontana can be annual, biennial or perennial. These have been<br />
coded as PI = p, P2 = a <strong>and</strong> PI = a, P2 = p respectively.<br />
Life form<br />
The Raunkiaer system <strong>of</strong> life forms was set out by Clapham,Tutin & Warburg (1962), who listed<br />
life forms for most species. Their assignments provide an excellent starting point but contain<br />
numerous inconsistencies. Life forms have been fully revised for PLANTATT. Following German<br />
<strong>and</strong> Swiss aut hors (e.g. Lindacher, 1995), the category <strong>of</strong> helophytes or marsh plants has been<br />
omitt ed. The majority <strong>of</strong> t hese can grow in places that are not permanently fl ooded in winter.<br />
The position <strong>of</strong> the overwintering buds in such situations is taken as a guide to t heir life form.<br />
An additional life form <strong>of</strong> annual water plants has been added, so t hat t he category t herophytes<br />
are all terrest rial.<br />
As with perennat ion, a secondary life form is given for some species. Details <strong>of</strong> how life forms<br />
were assigned <strong>and</strong> the relation <strong>of</strong> life form to plant height are given in t he Appendix.<br />
Woodiness<br />
Woodiness is an attribut e that applies to some chamaephytes, nanophanerophytes <strong>and</strong><br />
phanerophytes. All ot her life forms are t reated as herbaceous. Three categories are recognized,<br />
woody, semi-woody <strong>and</strong> herbaceous. Although we have been guided in part by Clapham,Tutin &<br />
W arburg ( 1962), we have not hesitated to express our own opinions where these diff er.
Table 3. Size <strong>and</strong> life history attributes other t han clonality; counts <strong>of</strong> primary<br />
att ributes are in the column N 1=, count s <strong>of</strong> secondary attributes are in N 2=<br />
Attribute or code N 1= N2= Explanat io n<br />
(a) Height (cm) Hght Height (leaf length for scapose plants <strong>and</strong> ferns)<br />
(b) Length (cm) Len Length (aquatic plants; leaf length for isoetids)<br />
(c) Perennation PI P2 Primary <strong>and</strong> secondary type <strong>of</strong> perennation<br />
a 455 14 Annual<br />
b 96 14 Biennial, including monocarpic perennials<br />
p 1334 42 Perennial<br />
(d) Life form L Fl LF2 Primary <strong>and</strong> secondary fi fe form (see Table Al )<br />
(e) Woodiness<br />
Ch 148 24 Chamaephyte<br />
Gb 32 Bulbous geophyte<br />
Gn 134 11 Non-bulbous geophyte (rhizome, corm or tuber)<br />
hc 8 11 50 Hemicryptophyte<br />
Hy 124 34 Perennial hydrophyt e (perennial water plant)<br />
H z 25 1 Annual hydrophyte (aquatic therophyte)<br />
Ph 108 15 Mega-, meso- <strong>and</strong> microphanerophyte<br />
Pn 73 2 1 Nanophanerophyte<br />
T h 430 14 Therophyte (annual l<strong>and</strong> plant)<br />
1651 Herbaceous<br />
sw 27 Semi-woody<br />
Vt 207 Woody<br />
Clonality<br />
Clonal growt h is defi ned here as vegetative reproduct ion combined with lateral spread. Like<br />
perennat ion, clonality may have more t han one value for a given species, refl ecting the various<br />
ways in which clonal growth may occur. In some species t here are varieties with clonal growt h<br />
(Arrhenatherum elatius van bulbosum, Caltha palustris var. radicans) while the normal form is not<br />
markedly clonal. In these two species, the variety with clonal growth is less frequent than the<br />
type variety, so that both plants are given Clone] = 0 (not spreading clonally) as the primary<br />
state, whereas Clone2 = D Rg <strong>and</strong> Sto12 respectively. Two species with proliferous<br />
infl orescences really ought to have been assigned to three categories, namely Juncus bulbosus<br />
(N ode2, Irreg <strong>and</strong> omitted DRi) <strong>and</strong> Butomus umbellatus (Rhiz2, DRg <strong>and</strong> omitted D Ri). It did<br />
not seem wort h having a third column just for these two, so the inflorescence character has<br />
been omitt ed.
Table 4. Cat egor ies <strong>of</strong> clonality; counts <strong>of</strong> primary attributes are in the column<br />
N 1=, count s <strong>of</strong> secondary attributes are in N 2=<br />
Attribute or code N 1 = N 2= Explanat io n<br />
(I) Clonafi ty Gone Clone2<br />
0 1228 Little or no vegetative spread<br />
Ogr 25 Tussock-forming graminoid, may slowly spread<br />
Ot b 26 Tuberous or bulbous, slowing cloning by <strong>of</strong> sets<br />
D Ra 20 10 Detaching ramets above ground (<strong>of</strong>t en axillary)<br />
D Rg 4 16 Detaching ramets at or below ground<br />
D Ri 11 Detaching ramets on infl orescence<br />
D R1 1 Detaching rarnets on leaves (Hammarbya)<br />
D Rp 1 Detaching ramets on prot hallus (Trichomanes)<br />
Frag 7 Fragmenting as part <strong>of</strong> normal growth<br />
Ir reg 38 17 Irregularly fragmenting (mainly water plants)<br />
Leaf 1 Plantlets formed on leaves (Cardamine pratensis)<br />
N ode l 19 20 Short ly creeping <strong>and</strong> rooting at nodes<br />
N ode2 76 9 Ext ensively creeping <strong>and</strong> rooting at nodes<br />
Rhiz l 152 8 Rhizome shortly creeping<br />
Rhiz2 209 15 Rhizome far-creeping<br />
Root 37 3 Clones formed by suckering from roots<br />
St ol l 14 Short ly creeping, stolons in illuminated medium<br />
St o12 26 5 Far-creeping by stolons in illuminated medium<br />
T ip 5 Tip rooting (the stems <strong>of</strong>ten turn downwards)<br />
The following comments may be helpful in distinguishing the clonal categories.<br />
I. The category Ogr is rather poorly defi ned. If a perennial graminoid (grass, sedge or rush) is<br />
repeatedly mown or heavily grazed, it may gradually form clones, even though this is not the<br />
normal condition.<br />
2. The category Ot b assumes that the ground is litt le disturbed. If there is regular disturbance,<br />
t he <strong>of</strong> sets will be dispersed to new sites <strong>and</strong> t he plant would then be indicated as DRg<br />
(detaching ramets at or below ground).<br />
3. The small category Frag applies to duckweeds <strong>and</strong> Azola<br />
4. The categories N ode (creeping <strong>and</strong> root ing at nodes), Rhiz (rhizomatous or with<br />
subterranean stolons) <strong>and</strong> Stol (stoloniferous in the illuminated medium, eit her air or<br />
water) are divided into two, according to whether they spread a short distance in a season<br />
or are far-creeping. For rhizomatous plants, a rule <strong>of</strong> t humb is that a species whose new<br />
shoots arise at a distance less t han a quarter <strong>of</strong> the height <strong>of</strong> the plant is short ly creeping,
while those that spread further are deemed to be far-creeping. Analogous distinct ions are<br />
made for N ode <strong>and</strong> Stol.<br />
5. The distinction between Node <strong>and</strong> Stol is that in N ode the horizontal or decumbent<br />
stem extends with indeterminate growth, rooting at the leafy nodes <strong>and</strong> not forming a new<br />
stem axis at each rooted position. In St ol, a new stem axis normally arises at the point <strong>of</strong><br />
root ing, or the stolon is determinate, bending upwards <strong>and</strong> not progressing with<br />
indeterminat e growt h.<br />
6. In the tip-rooting category, T ip, leafy stems that are not obviously stolons turn down at the<br />
apex <strong>and</strong> root there.
GE OGRAPHI C A TTRIB UTES<br />
Euro ean <strong>and</strong> wider distribut ions <strong>and</strong> cont inent alit<br />
The categorizat ion <strong>of</strong> taxa to biogeographic elements <strong>and</strong> their designat ion as 'continental' or<br />
ot herwise (Table 5) follow Preston & Hill ( 1997), with minor revisions <strong>and</strong> t he addit ion <strong>of</strong> the<br />
hyperoceanic category from a subsequent paper (Preston & Hill, 1999). Element s are provided<br />
for nat ive species <strong>and</strong> some archaeophytes; for archaeophyt es the classifi cation describes the<br />
archaeophyt ic range. In addition, some but not all alien species originat ing in Europe have also<br />
been assigned to biogeographic elements for PLANTATT <strong>and</strong> designated as continental.<br />
Geographic att ribut es are not provided for some hybrids.<br />
Table 5. European <strong>and</strong> wider dist ribution, <strong>and</strong> continentality<br />
Att ribut e<br />
<strong>and</strong> codes<br />
N = Ex planat io n
Native distribution o s ecies alien in Britain <strong>and</strong> Irel<strong>and</strong><br />
The native dist ribution <strong>of</strong> aliens (Table 6) is taken from the New Atlas. This information is<br />
provided for neophytes <strong>and</strong> some archaeophytes. In Table 6, taxa present in two areas are<br />
included in bot h totals but taxa are excluded from the totals if they are only doubtfully native in<br />
the relevant area.<br />
Table 6. Nat ive dist ribution <strong>of</strong> species alien in Britain <strong>and</strong> Irel<strong>and</strong><br />
Code N = Explanat ion<br />
Am 24 North America<br />
Am4 22 West ern North America<br />
Am6 5 Eastern North America<br />
As 10 Asia east <strong>of</strong> 60°E<br />
As I 24 Asia between 60°E <strong>and</strong> I 20°E<br />
As2 9 Asia E <strong>of</strong> I 20°E<br />
Aus 3 Aust ralia<br />
Crop 15 Crop plant, does not have a native range<br />
Eur 149 Europe<br />
Gard 13 Garden or igin, does not have a native range<br />
NHem 6 N Hemisphere (Europe,Asia <strong>and</strong> Nort h America)<br />
NZ 4 New Zeal<strong>and</strong><br />
SAf 5 Southern Africa<br />
SAm 20 South America <strong>and</strong>/or Cent ral America<br />
Unk 10 Unknown<br />
Counts o I O-km s uares in the New Atlas<br />
For each taxon, the number <strong>of</strong> 10-km squares in Britain, Irel<strong>and</strong> <strong>and</strong> the Channel Isl<strong>and</strong>s is.<br />
enumerated (Table 7). For most natives, only t he native distribution has been counted (blue dots<br />
in the New Atlas). For the small number <strong>of</strong> nat ive species in which it proved impossible even to<br />
attempt to delimit the nat ive range in the New Atlas, the count is for all squares. For alien taxa,<br />
all squares with records have been counted. Squares have been counted without regard to date,<br />
so that Otanthus maritimus, ext inct in Britain, is recorded from 23 squares t here.<br />
10
Table 7. Counts <strong>of</strong> squares <strong>and</strong> climat ic means<br />
Attribute<br />
(a) Counts<br />
GB<br />
Min Max Explanation<br />
IR 0 985 Irel<strong>and</strong><br />
Counts <strong>of</strong> 10-km squares<br />
0 2805 Great Britain <strong>and</strong> Isle <strong>of</strong> Man<br />
CI 0 14 Channel Isl<strong>and</strong>s<br />
(b) Climatic means Mean values for 10-km squares<br />
Tian - 1.3 7.0 January mean temperat ure (°C)<br />
Tjul 10.4 17.0 July mean temperature (°C)<br />
Prec 553 32 18 Annual precipitation (mm)<br />
Climatic means<br />
Climat ic values for plants were calculated as t he mean climate <strong>of</strong> the 10-km squares where they<br />
occur in Britain, Irel<strong>and</strong> <strong>and</strong> the Channel Isl<strong>and</strong>s, averaging over the squares enumerated for the<br />
counts. Climate data for 10-km squares were taken from baseline climate summaries <strong>of</strong> t he UK<br />
Climate Impacts Programme (Hu Ime & Jenkins, 1998). These baseline summaries were<br />
const ructed by interpolat ion <strong>of</strong> daily weat her measurements from individual met stat ions,<br />
averaged over the 30-year period 1961- 1990 (Barrow et al., 1993).
HA BI TA T A TTRIB UTES<br />
Coastal species<br />
Species are deemed to be coastal if 80% <strong>of</strong> occupied squares are on the coast <strong>and</strong> if they depend<br />
on coastal habitat. Most coastal species have Ellenberg salt values (S values, defi ned below)<br />
greater than 0. Those with Ellenberg S = 0 were scrutinized carefully to ascertain whether their<br />
habitat was indeed coastal.<br />
Broad Habitats<br />
The preferences <strong>of</strong> species for Broad Habitats <strong>of</strong> the UK BAP are listed in the column labelled Br<br />
Habitats. Species' main habitat (s) are_list ed. No species is deemed to have a preference for<br />
more t han four habitats. Minor habitats are ignored. For more informat ion about Broad<br />
Habitats <strong>and</strong> species' preferences, refer to the Appendix.
Table 8. Coastal species <strong>and</strong> preferences for Broad H abitats<br />
A ttribut e<br />
<strong>and</strong> codes<br />
N = Explanat io n<br />
(a) Co Coastal species<br />
Co 145 At least 80% <strong>of</strong> occupied squares contain sea at high tide<br />
(b) Br Nabs Broad Habitats<br />
3 10 Broad leaved, mixed <strong>and</strong> yew woodl<strong>and</strong><br />
2 32 Coniferous woodl<strong>and</strong><br />
3 543 Boundary <strong>and</strong> linear features (eg hedges, roadsides, walls)<br />
4 198 A rable <strong>and</strong> horticultural (includes orchards, excludes domest ic gardens)<br />
5 22 Improved grassl<strong>and</strong><br />
6 163 Neut ral grassl<strong>and</strong> (includes coarse Arrhenatherum grassl<strong>and</strong>)<br />
7 2 18 Calcareous grassl<strong>and</strong> (includes lowl<strong>and</strong> <strong>and</strong> montane types)<br />
8 89 Acid grassl<strong>and</strong> (includes non-calcareous s<strong>and</strong>y grassl<strong>and</strong>)<br />
9 10 Bracken<br />
10 83 Dwarf shrub heat h (cover <strong>of</strong> dwarf shrubs at least 25%)<br />
I I 254<br />
12 4 1<br />
Fen, marsh <strong>and</strong> swamp (not wooded; includes flushes, rush-pastures, springs <strong>and</strong><br />
mud communit ies)<br />
Bog (on deep peat; includes bog pools as well as acid lowl<strong>and</strong> valley mires on<br />
slight ly shallower peat)<br />
13 174 St<strong>and</strong>ing wat er <strong>and</strong> canals<br />
14 149 Rivers <strong>and</strong> st reams<br />
I S 103 Montane habitats (acid grassl<strong>and</strong> <strong>and</strong> heat h with montane species)<br />
16 292<br />
Inl<strong>and</strong> rock (heterogeneous - includes quarries, limestone pavement, clif s, screes<br />
<strong>and</strong> skeletal soils over rock)<br />
17 231 Built-up areas <strong>and</strong> gardens<br />
18 74 Supra littoral rock (does not include maritime grassl<strong>and</strong>)<br />
19 135 Supra littoral sediment (st r<strong>and</strong>lines, shingle, coastal dunes)<br />
2 1 65 Littoral sediment (includes saltmarsh <strong>and</strong> saltmarsh pools)<br />
23 1 Inshore sublittoral sediment (only Zostera marina)
Ellenbe s indicator values<br />
Ellenberg defi ned seven major scales, <strong>of</strong> which fi ve are presented here. The two that are<br />
omitted, T (temperat ure) <strong>and</strong> K (cont inentality), correspond quite closely to the major biome<br />
<strong>and</strong> east ern limit categories defi ned for European dist ribut ions by Preston & Hill (1997). Neither<br />
T nor K values are satisfactory in an oceanic climate such as that <strong>of</strong> Britain; t hose for K are<br />
particularly unreliable, especially as Ellenberg's defi nition was geographical rather than climat ic.<br />
The fi ve remaining scales have values defi ned in the tables that follow. The values are based on<br />
those <strong>of</strong> Ellenberg et at (1991). They are mostly reproduced from a previous publication (Hill et<br />
al., 1999), with some additions because <strong>of</strong> the ext ra species included here. A few example<br />
species are given for each value, by way <strong>of</strong> explanation.<br />
Light values (L)<br />
The full range <strong>of</strong> Ellenberg values for light (Table 9) is not represent ed in the <strong>British</strong> fl ora. For<br />
canopy t rees, light values refer to the tolerance <strong>of</strong> t he sapling stage <strong>of</strong> the life cycle.<br />
Table 9. Ellenberg values for light (L)<br />
Code N = Explanat io n<br />
0 Plant in deep shade (no examples for Britain or Irel<strong>and</strong>)<br />
2 4 Between 1 <strong>and</strong> 3 (Epipogium aphyllum, Neottia nidus-avis,Trichomenes speciosum)<br />
Shade plant, most ly less than 5% relative illuminat ion, seldom more than 30%<br />
3 20 illumination when t rees are in full leaf (Ga hurn odoraturn, Listera cordate, Mercurialis<br />
perennis)<br />
4 70 Between 3 <strong>and</strong> 5 (Circaea lutetiono, Lamiastrum galeobdolum, Poa nérnoralis)<br />
Semi-shade plant, rarely in full light, but generally with more than 10% relat ive<br />
5 120 illumination when t rees are in leaf (Carex pendula, Hyacinthoides non-scripta, Primula<br />
vulgaris)<br />
6 2 13 Between 5 <strong>and</strong> 7 (Anthriscus sylvestris, Digitalis purpurea, Teucriurn scorodonia)<br />
7 680<br />
8 576<br />
9 202<br />
Plant generally in well lit places, but also occurring in part ial shade (Arrhenatherurn<br />
elatius, Carex flacco, Poo trivialis,Vicia cracca)<br />
Light-loving plant rarely found where relat ive illumination in summer is less than 40%<br />
(Cardarnine hirsute, Orchis morio,Thymus polytrichus,Vacciniurn oxycoccus)<br />
Plant in full light, found mostly in full sun (Aster tripolium, Mel/ lotus albus, Poa compressa,<br />
Primula farinosa)<br />
14
M oisture values (F)<br />
Unlike the ot her Ellenberg values, moisture is on a scale <strong>of</strong> I to 12 (Table 10). We use the<br />
abbreviation F from the German Feuchtigkeit.<br />
Table 10. Ellenberg values for moisture (F)<br />
Code N = Explanat ion<br />
1 3<br />
Indicator <strong>of</strong> ext reme dryness, restricted to soils that <strong>of</strong>t en dry out for some time<br />
(Corynephorus canescens, Helianthemum apenninum, Koeleria vallesiana)<br />
2 28 Between 1 <strong>and</strong> 3 (Clinopodium acinos, Saxifraga tridactyfi tes, Sedum acre)<br />
3 168<br />
4 378<br />
5 492<br />
Dry-site indicator, more <strong>of</strong>t en found on dry ground than in moist places (Asplenium<br />
trichomanes, Centaurea scabiosa, Spergularia rubra)<br />
Between 3 <strong>and</strong> 5 (Arctium minus, Hefi ctotrichon pratense, Iris foetidissima,Thymus<br />
polytrichus)<br />
Moist-site indicator, mainly on fresh soils <strong>of</strong> average dampness (Anthriscus sylvestris,<br />
Euphorbia amygdaloides, Hyacinthoides non-scripta, Solarium nigrum)<br />
6 226 Between 5 <strong>and</strong> 6 (Agrostis stolonifera, Empetrum nigrum, Rumex crispus)<br />
7 14 1<br />
8 170<br />
9 126<br />
10 64<br />
I I 34<br />
12<br />
55<br />
Dampness indicator, mainly on constant ly moist or damp, but not on wet soils (Carex<br />
Dactylorhiza maculata, Pulicaria dysenterica, Ranunculus repens)<br />
Between 7 <strong>and</strong> 9 (Cardamine pratensis, Equisetum telmateia, Phalaris arundinacea, Schoenus<br />
nigricans)<br />
Wet-site indicator, <strong>of</strong>t en on water-saturated, badly aerated soils (Drosera rotundif<strong>of</strong>i a,<br />
Myosotis scorpioides,Vaccinium oxK occus, Viola palustris)<br />
Indicator <strong>of</strong> shallow-water sites that may lack st<strong>and</strong>ing water for ext ensive periods<br />
(Afi sma plantago-aquatica, Carex limosa, Ranunculus fi ngua,Typha latif<strong>of</strong>i a)<br />
Plant root ing under water, but at least for a time exposed above, or plant fl oat ing on<br />
t he surface (Lemna minor, Nuphar lutea, Sagit aria sagittifolia, Schoenoplectus lacustris)<br />
Submerged plant, permanently or almost constantly under water (Isoetes lacustris,<br />
Potamogeton crispus, Ranunculus circinatus, Zostera marina)<br />
15
Reaction (R)<br />
Reaction (Table I I) refers to environmental acidity, which would ordinarily be measured by pH.<br />
Except for water plants, R values refl ect preferences for soil acidity.<br />
Table I I . Ellenberg values for reaction (R)<br />
Code N = Ex planat io n<br />
Indicator <strong>of</strong> ext reme acidity, never found on weakly acid or basic soils (Andromeda<br />
polifolia, Lycopodium clavatum, Rubus chamaemorus, Ulex minor)<br />
Between I <strong>and</strong> 3 (Agrostis curtisii, Calluna vulgaris, Drosera rotundif<strong>of</strong>i a, Po lygala serpyllifolia)<br />
Acidity indicator, mainly on acid soils, but exceptionally also on nearly neutral ones<br />
(Agrostis vinealis, Dactylorhiza M a de ra, Ga lium saxatile, Pteridium aquilinum)<br />
Between 3 <strong>and</strong> 5 (Agrostis capillaris, Carex panicea,Juncus eff usus,Teucrium scorodonia)<br />
Indicator <strong>of</strong> moderately acid soils, only occasionally found on very acid or on neutral to<br />
basic soils (Cardamine pratensis, Cirsium palustre, Rubus idaeus, Ulex eumpaeus)<br />
Between 5 <strong>and</strong> 7 (Ammophila arenaria, Carex sylvatica, L<strong>of</strong>i um perenne, Ranunculus ficaria)<br />
Indicator <strong>of</strong> weakly acid to weakly basic conditions; never found on very acid soils<br />
(Agrimonia eupatoria,Atriplex prostrata, Nuphar lutea, Phleum pretense)<br />
Between 7 <strong>and</strong> 9 (Artemisia vulgaris, Carduus nutans, Iris foetidissima, Viola hirsuta)<br />
Indicator <strong>of</strong> basic reaction, always found on calcareous or other high-pH soils (Bunium<br />
bulbocastanum, Clinopodium calamintha, Dryopteris submontana, Primula farMosa)<br />
Nitrogen (N)<br />
Nitrogen values (Table 12) are in fact a general indication <strong>of</strong> preference for soil fert ility. They are<br />
closely correlated with t he st ress values <strong>of</strong> Grime ( 1979, 200 1), low N values corresponding to<br />
plants with high st ress tolerance (Grime et al., 1997) <strong>and</strong> vice-versa.<br />
Table 12. Ellenberg values for nitrogen (N)<br />
Code N= Explanat io n<br />
1<br />
84<br />
Indicator <strong>of</strong> ext remely infertile sites (Agrostis curtisii, Cli nopodium acinos, Drosera<br />
rotundifolia, Rubus chamaemorus)<br />
2 323 Between 1 <strong>and</strong> 3 (Aira praecox, Carex panicea, Linum catharticum, Scabiosa columbaria)<br />
3 286<br />
Indicator <strong>of</strong> more or less infert ile sites (Centaured scabiosa, Go lium saxatile, Pimpinella<br />
saxifraga,Teucrium scorodonia)<br />
4 245 Between 3 <strong>and</strong> 5 (Agrostis capillaris, Cirsium palustre, Plantago lanceolata, Primula vulgaris)<br />
5<br />
342<br />
Indicator <strong>of</strong> sites <strong>of</strong> intermediate fert ility (Angelica sylvestris, Digitalis purpurea, Iris<br />
foetidissima,Trifolium pratense)<br />
6 3 19 Between 5 <strong>and</strong> 7 (Cirsium arvense, Glyceria fluitans, Poa trivialis, Rumex crisp s)<br />
7 223<br />
Plant <strong>of</strong>ten found in richly fertile places (Atriplex prostrate, Epilobium hirsutum, Stellaria<br />
media,Typha latifolia)<br />
8 55 Between 7 <strong>and</strong> 9 (Beta vulgaris, Galium aparine, Lamium album, Urtica dioica)<br />
9 8<br />
Indicator <strong>of</strong> ext remely rich situat ions, such as cattle resting places or near pollut ed<br />
rivers (Arctium laPpa,Artemisia absinthium, Hyoscyamus niger, Rumex obtusifolius)
Salt tolerance (5)<br />
Values for salt tolerance (Table 13) start at zero, corresponding to no tolerance <strong>of</strong> salt.<br />
Table 13. Ellenberg values for salt tolerance (S)<br />
Explanat ion<br />
Absent from saline sites; if in coastal situations, only accidental <strong>and</strong> non-persistent if<br />
subjected to saline spray or water (85% <strong>of</strong> the fl ora)<br />
Slightly salt-tolerant species, rare to occasional on saline soils but capable <strong>of</strong> persisting<br />
in the present <strong>of</strong> salt (includes dune <strong>and</strong> dune-slack species where the ground water is<br />
fresh but where some inputs <strong>of</strong> salt spray are likely) (Calystegia sepium, Chenopodium<br />
album, Oenanthe crocata, Sedum angfi cum)<br />
Species occurring in both saline <strong>and</strong> non-saline situat ions, for which saline habitats are<br />
not stro ngly predominant (Atriplex prostrata, Elytrigia repens, Phragmites australis, Rumex<br />
crispus)<br />
Species most common in coastal sites but regularly present in freshwater or on nonsaline<br />
soils inl<strong>and</strong> (includes strictly coastal species occurring in sites such as cliff crevices<br />
<strong>and</strong> s<strong>and</strong> dunes that are not obviously salt-af ected) (Cakile maritima, Cochlearia <strong>of</strong>ficinalis,<br />
Juncus gerardii, Spergularia rupicola)<br />
Species <strong>of</strong> salt meadows <strong>and</strong> upper saltmarsh, subject to at most only very occasional<br />
tidal inundation (includes species <strong>of</strong> brackish conditions, i.e. <strong>of</strong> consistent but low<br />
salinity) (Atriplex littoralis, Elytrigia atherica, Glaux maritima,Triglochin maritimum)<br />
Species <strong>of</strong> the upper edge <strong>of</strong> saltmarsh, where not inundated by all tides (includes<br />
obligate halophytes <strong>of</strong> clif s receiving regular salt spray) (Aster trip<strong>of</strong>i um, Crithmum<br />
maritimum, Puccinellia maritima, Suaeda vera)<br />
Species <strong>of</strong> mid-level saltmarsh (Atriplex portulacoides, Cochlearia anglica, Limonium vulgare)<br />
Species <strong>of</strong> lower saltmarsh (Spartina anglica, Suaeda maritima)<br />
Species more or less permanently inundated in sea water (Zostera spp.)<br />
Species <strong>of</strong> extremely saline conditions, in sites where sea water evaporates,<br />
precipitating salt (Safi cornia europaea agg.; these could equally well be t reated as<br />
species <strong>of</strong> t he lower marsh)
LIS TIN G OF SPE CIES WI TH THEIR A TTRIB UTES<br />
The listing <strong>of</strong> species with their attributes has 32 columns. Codes used in these columns are set<br />
out in the foregoing tables. The short <strong>and</strong> full names <strong>of</strong> the columns are given here (Table 14), as<br />
are the pages on which the tables <strong>of</strong> codes appear<br />
Table 14. Plant attributes cross-referenced to tables <strong>and</strong> page numbers where t hese<br />
are described more fully<br />
Short name Attribute Table N o Page<br />
Taxon name Name in New At las 1 2<br />
Fam Family (4-letter abbreviation) 1 2<br />
NS Native status 2 4<br />
CS Conservation status 2 4<br />
RS Rarity status 2 4<br />
Chg Change Index 2<br />
Hght Height in cm (terrest rial) 3 6<br />
Len Length in cm (aquatic) 3 6<br />
PI Perennat ion - primary 3 6<br />
P2 Perennation - secondary 3 6<br />
LF 1 Life form - primary 3 6<br />
LF2 Life form - secondary 3 6<br />
Woodiness 3 6<br />
Clone 1 Clonal spread .- primary 4 7<br />
Clone 2 Clonal spread - secondary 4 7<br />
E I Major Biome (European di stribution) 5 9<br />
E2 Eastern limit code 5 9<br />
C' Continentality in Europe 5 9<br />
O rigin Origin <strong>of</strong> alien taxa 6 10<br />
GB Number <strong>of</strong> 10-km squares in Britain (including Isle <strong>of</strong> Man) 7 1 I<br />
IR Number <strong>of</strong> I 0-km squares in Irel<strong>and</strong> 7 I I<br />
CI Number <strong>of</strong> 10-km squares in Channel Isl<strong>and</strong>s<br />
7 I I<br />
Tjan January mean temperature 7 I I<br />
Tjul July mean temperature 7 I I<br />
Prec Annual precipitation 7<br />
Co Coastal 8 13<br />
Br Habitats Broad Habitats 8 13<br />
Ellenberg indicator value - light 9 14<br />
Ellenberg indicator value - moisture 10 15<br />
ft Ellenli erg indicator value - reaction I I 16<br />
Ellenberg indicator value - nit rogen 12 16<br />
Ellenberg indicator value - salt tolerance 13 17<br />
18
Taxo n name Fa m NS CS RS C hg Hght Len 1 P2 LF 1 LF2 W lo ne l C lo ne 2 E l E2 C Ori in G B IR C I r an r ul Prec Co Br Habitats L F R N S<br />
Acae na no vae-se l<strong>and</strong>iae Rosa A N 11 C h ode2 A us , NZ 82 9 3 .8 15 .2 83 1 3 , 10 , 18 , 19 8 3 6 3<br />
Acer campestre Acer N n 0 .35 15 00 Ph 7 3 1389 0 3 .6 15 .7 839 1, 3 5 5 7 6<br />
A cer plata noides Acer A N 3000 Ph 7 3 c Eur 14 19 43 3 .4 15 .2 903 1, 3, 17 4 5 7 7 '<br />
Ace r pseu dop latanus A cer A N -0 .40 3000 Ph 7 3 c Eur 2 59 9 942 1 3 .6 14 .6 1083 1, 3, 17 4 5 6 6<br />
Ace ras anthm pop hor um O rch N s -0 .76 40 G n 9 1 109 0 3 .6 16 .3 690 7 7 1 4 8 3<br />
Achillea millefolium A ste N n 0.29 45 C h h hiz2 5 5 277 4 968 1 3 .5 14 .5 110 3 6 7 5 6 4<br />
Ach illea ptarmica A ste N n -0.6 5 60 hc h hiz l 5 5 2 38 2 492 3 .3 14 .3 1146 11 7 7 5 3<br />
Acon itu m nap ell us Ranu NA 5 100 G n h hiz t 7 3 104 0 4 .0 15 .8 964 1, 3 . 14 , 17 5 7 7 6<br />
Acon iturn nap ellus se ns . lat. Ranu NA s 1.4 2 100 G n h hiz l 7 3 104 0 4 .0 15 .8 964 1, 3 , 14 , 17 5 7 7 6<br />
Acor us calam us A ra c A N 0.69 112 Hy h hiz2 Unk 5 15 17 3 .6 15 .8 770 13 , 14 8 10 7 71<br />
Actaea spica ta Ranu N s -0.44 60 G n h hiz l 4 6 33 0 2 .5 14 .3 10 54 16 3 5 8 6<br />
Adiantum cap illus- ven eris A dia N 5 0.54 30 hc 9 1 38 29 5 .2 15 .2 110 1 16 4 7 8 3<br />
Adonis annua Ranu A R V U -2.19 40 Th 9 1 234 3 3 .8 16 .0 745 4 7 4 7 4<br />
Adox a m osehatellin a Adox N n -0 .05 12 Gn h hiz l 5 6 1720 2 3 .3 14 .9 1005 1 4 5 6 5<br />
Aegopodium dagraria A pia A R -0 .45 100 hc h hiz2 7 4 Eur, A s 1 2533 8 19 1 3 .6 14 .6 1064 3, 17 6 5 6 71<br />
Aes culus hippoca stanum Hip p A N 1.0 8 32 00 Ph Eur 2 186 557 I 3.6 14 .8 10 14 3 , 17 5 5 7 7<br />
Aethusa cynap ium A pia NA n -0 .4 1 100 T h 7 3 164 0 0 3.6 15 .5 863 3, 4 , 17 6 4 7 6<br />
Agrimo nia eup atoria Ro sa N n -0 .89 60 hc 8 4 1859 532 3.8 15 .1 953 6 7 4 7 4<br />
Agrimo nia proc ere Ro sa N n -0 .38 100 hc 7 3 8 19 16 1 3.9 15 .1 10 26 1, 3 , 6 5 6 7 5<br />
Agros tem ma githago Cary A R EW -0 .75 10 0 T h Unk 8 15 96 3 .9 15 .6 852 4 7 5 6 5<br />
Agros tis can ine Po ac N n 60 hc to12 5 6 1609 36 1 3 .5 14 .5 1128 11, 13 7 7 3 3<br />
Agros tis can ine sen s.lat. Poac N n 1.3 2 60 hc iz2 St o12 5 6 19 37 44 3 3 .4 14 .3 114 5 8 , 11 7 6 3 3<br />
Agros tis cap illaris Poet N n 1.2 8 62 hc iz2 5 4 2758 922 1 3 .5 14 .5 1104 8 6 5 4 4<br />
Agro stis curtisii Poac N n -0 .26 60 he 8 1 207 0 4 .9 15 .8 1082 8 , 10 7 6 2 1<br />
Agros tis gigantea Poac A R 1.39 80 hc iz2 8 5 16 13 109 3 .6 15 .3 889 3, 4 7 6 6 71<br />
Agros tis stolonifera Poac N n 3 .66 4 5 hc to12 6 6 2 77 6 977 1 3 .6 14 .5 110 1 4, 6 7 6 7 6<br />
Agrostis vinea lis Poac N n 60 he iz2 7 3 1126 150 3 .3 14 .0 1200 8, 10 7 6 3 2<br />
Aire ca ryop hy llea Poa c N n -0 .52 25 Th 8 3 2046 6 56 1 3 .7 14 .6 1087 10 , 16 8 2 5 2<br />
Aire praeco x Po ac N n -0.19 10 Th 8 2 2450 6 59 1 3 .5 14 .3 1149 8 , 16 8 2 4 2<br />
Aj uga cha maep itys La mi NA V U r -0 .62 20 hc 8 3 43 0 3 .8 16 .5 7 13 4 , 7 71 4 8 2<br />
Aj uga py ramid alis La rni N 5 -0 .34 30 hc 4 3 106 8 3 .3 12 .6 1425 10 , 16 7 ' 5 5 2<br />
Aj uga reptans La m i N n -0 .56 30 hc to 12 7 3 2439 7 17 3 .4 14 .6 1095 1 5 7 5 5<br />
Alchem illa ac utiloba Ro sa N r 60 hc 5 3 c 15 0 1.6 13 .2 969 6 7 4 6 5<br />
Alch emilla alpina Ro sa N n -0 .6 1 15 hc 1 3 384 4 1.6 12 .1 1843 7 , 15 , 16 7 5 4 3<br />
Alch emilla filica ulis Ro sa N n 30 hc 4 3 1407 308 2 .9 14 .1 1185 7, 15 . 16 8 6 6 3<br />
Alch emilla glabra Ro sa N n 40 hc 5 3 127 1 223 2.6 13 .4 1338 6 , 15 . 16 7 6 6 4<br />
Alch emilla gla uce scens Ro sa N s 15 hc 5 3 c 20 3 2.0 13 .3 14 08 7 T 5 7 5<br />
Alch emilla glomerulans Ro sa N s 30 hc 2 3 57 0 0 .4 11.5 19 78 8 , 15 7 5 5 4<br />
Alchem illa micans . Ro sa N V U r 40 hc 5 3 c 4 0 2 .0 13 .5 10 56 7 7 5 7 5<br />
Alchem illa min ima Ro sa N E V U r 5 hc 4 1 3 0 1.7 13 .5 166 7 7 71 6 8 3<br />
Alchem illa mollis Rosa A N 60 hc Eur 805 17 3.5 15 .0 10 09 3 , 17 6 5 7 6<br />
Alchem illa monticola Rosa N r 35 hc 5 3 c 9 0 1.3 13 .0 10 84 6 7 4 6 4<br />
Alchem illa sub crena ta Rosa N EN r 35 hc 5 3 c 2 0 0 .9 12 .6 1125 6 7 4 6 5<br />
Alchem illa vulgaris agg . Rosa N n -0 .0 1 35 hc 5 3 19 35 496 3.1 14 .1 1179 6 , 7 , 15 , 16 T 5 6 4<br />
Alchemilla wichu rae Rosa N s 20 hc 4 3 6 5 0 0 .9 12 .0 1992 7 71 5 5 3<br />
Alchemilla xa nthoc hlora Rosa N n 40 . hc 7 3 1060 24 0 2 .8 13 .9 1174 6 , 7 6 5 6 4
Tax on name Fam NS CS RS Chg. Hght Len P1 P2 LF 1 LF2 W Clona l Clo ne2 El E2
S<br />
Taxon name Fam NS CS RS Chg Hght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tja n Tjul Prec Co Br Habitats L F R N<br />
Anthoxanthum aristatum Poac AN -2.65 40 Th 0 Eur 93 0 I 3.9 16.0 775 4, 17 7 4 4 5<br />
Anthoxanthum odoratum Poac N n 0.90 50 hc 0 6 4 2782 965 14 3.5 14.4 1106 6 7 6 4 3<br />
Anthriscus caucalis Apia N n -0.16 70 Th 0 7 3 659 471 12 3.9 15.71 747 3, 4, 8 71 5 6 5<br />
Anthriscus sylvestris Apia N n -0.19 100 hc 0 5 5 2480 805 5 3.6 14.6 1039 3 6 5 7 T<br />
Anthylris vulneraria Faba N n 0.45 60 he 0 5 3 1798 465 9 3.7 14.6 1030 7 8 4 7 2<br />
Anfi rrhinum maj us Scro AN 2.84 30 Ch 0 Eur 1043 84 8 3.9 15.7' 837 3, 17 8 3 7' 5<br />
Apera interrupta Poac AN 0.80 40 Th 0 8 4 Eur, As l 104 0 0 3.4 15.9 671 3, 4, 16 9 5 8 6<br />
Apera spica-venti Poac AR -0.21 100 Th 0 5 4 326 1 3 3.7 16.0 726 3, 4 7i 4 5 5<br />
Aphanes arvensis Rosa N n 10 Th 0 7 3 1608 432 4 3.7 15.0 956 4, 16 8 4 6 4<br />
Aphanes arvensis agg. Rosa N n -0.32 10 Th 0 7 3 2302 659 14 3.6 14.7 1038 4, 8, 16 7 4 6 4<br />
Aphanes australis Rosa N n 10 Th 0 7 3 1549 230 14 3.5 14.6 1070 8, 16 7 4 5 4<br />
Apium grayeolens Apia N n -0.63 80 hc 0 8 4 519 82 8 4.3 15.8 849 13 8 8 7 7<br />
Apium inundatum Apia N n -0.54 30 so Hy Irreg 7 2 9271 351 6 3.8 14.8 1023 11, 13 71 10 6 4<br />
Apium nodiflorum Apia N n -0.31 60 100 Hy Irreg 8 4 1661 855 12 4.0 15.2 961 14 7 10 7 7'<br />
Apium repens Apia N CR r 15 hc Node2 7 3 3 0 0 3.6 16.4 651 13 9 9 7 7<br />
Aquilegia vulgaris Ranu N n 1.70 100 hc 0 7 3 1504 197 5 3.6 15.0 986 1, 3, 16 6 4 6 5<br />
Arabidopsis thaliana Bras N n 1.21 30 Th 0 7 4 2218 509 13 3.5 14.8 1034 16, 17 8 3 6 2<br />
Arabis alpina Bras N EN r 15 Ch 0 1 4 1 0 0 2.5 11.8 3218 16 7 5 71 3<br />
Arabis glabra Bras N VU s -1.16 100 hc 0 7 4 151 0 1 3.5 16.0 686 8 7 3 8 5<br />
Arabis hirsuta Bras N n -1.02 40 p he 0 5 6 1042 143 4 3.3 14.6 1104 7, 16 7 5 8 3<br />
Arabis petraea Bras N s -0.64 25 Ch 0 1 5 78 2 0 1.7 11.9 1966 15, 16 9 3 8 1<br />
Arabis scabra Bras N VU r 20 Ch 0 9 3 1 0 0 4.4 16.5 844 16 7 3 8 2<br />
Arbutus unedo Eric N o 1.18 500 Ph w O 9 1 0 8 0 4.7 14.4 1335 1, 16 6 5 71 2<br />
Arctium lappa Aste AR 0.51 150 hc h 0 7 4 971 4 1 3.8 16.0 769 3 9 5 7 9<br />
Arctium minus Aste N n -0.41 150 hc h 0 7 5 2424 846 14 3.7 14.7 1051 3 6 4 7 5<br />
Arctostaphybos alpinus Eric N s -0.22 20 Ch w Node2 1 6 134 0 0 1.6 11.6 1750 15 7 6 2 2<br />
Arctostaphylos uva-ursi Eric N n -0.75 20 Ch w Node2 4 6 473 37 0 2.1 12.3 1615 10, 15 7 5 2 2<br />
Arenaria ciliata Cary N o 6 Ch 0 1 3 0 1 0 2.6 12.9 1454 15 9 5 8 2<br />
Arenaria norvegica Cary N r 0.21 6 a Ch Th 0 1 3 16 1 0 2.5 12.3 1904 16 9 3 8 2<br />
Arenaria serpyllifolia Cary N n -0.76 30 Th 0 8 4 2147 522 13 3.6 14.9 986 16 8 3 T 5<br />
Armeria arenaria Plum N o 20 Ch 0 8 2 0 0 5 6.1 16.9 843 Co 18, 19 8 3 6 2<br />
Armada maritima Plum N n -0. 14 15 Ch 0 3 6 1137 319 14 3.9 14.1 1265 Co 18, 21 8 7 5 5<br />
Armoracia rusticana Bras AR 0.05 150 hc Rhiz2 Crop 1532 111 10 3.8 15.6 850 3 8 5 7 Tj<br />
Arnoseris minima Aste AR EX -3.72 30 Th 0 7 3 83 0 0 3.6 16.1 685 4 7 4 3 3<br />
Arrhenatherurn elatius Poac N n 0.37 150 hc 0 DRg 7 3 2678 958 13 3.6 14.5 1089 3, 6 7 5 7 7<br />
Artemisia absinthium Aste AR -0.46 90 Ch sw 0 7 4 1005 41 6 3.8 15.6 861 3, 16, 17 7 4 7 9<br />
Art emisia campestris Aste N EN r -0,42 60 Ch sw Rhizl 7 4 c 9 0 0 3.3 16. 1 620 3, 8 8 3 6 5<br />
Artemisia norvegica Aste N VU r 8 hc h 0 1 3 3 0 0 0.9 10.9 1982 15 9 4 4 1<br />
Artemisia vulgaris Aste AR -0.20 150 hc h 0 7 4 2109 489 12 3.7 14.9 984 3, 17 7 4 8 7<br />
Arum italicum Arac N s 2.09 60 Gn h Rhizl 9 1 39 0 8 5.5 16.2 962 1, 3 4 5 6 6<br />
Arum maculatum Arae N n -0.28 50 Gn h Rhizl 7 3 1604 650 11 3.9 15.3 931 1 4 5 7 7'<br />
Asparagus <strong>of</strong> icinalis Lili N n 1.78 150 Gn h 0 7 1 17 7 7 5.4 15.9 953 3, 18, 19 7 5 6 5<br />
Asparagus <strong>of</strong> icinalis<br />
subsp.<strong>of</strong>ficinalis<br />
Lili AR 150 Gn h 0 7 4 5871 7 4 3.8 16.2 713 3 7j 5 6 5,<br />
Asparagus <strong>of</strong>i cinalis<br />
I<br />
subsp.prostratus Uh N VU r 30 Gn 0 7 1 171 7 7 5.9 15.9 950 18, 19 8 4 6 3
S<br />
Taxon name Fam NS CS RS Chg li ght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Asperula cynanchica Rubi N n -0.47 50 hc Rhiz2 7 3 329 47 3 4.0 15.9 842 7 7 8 2<br />
Asp leniurn adianturn-nigrum Asp N n 45 hc 0 7 3 2146 708 14 3.7 14.6 1110 3, 16 6 5 5<br />
Asp lenium adianturn-nigrum<br />
sens.lat Asp N n 0.35 45 hc 0 8 3 2146 708 14 3.7 14.6 1110 3 6 5 5<br />
Asp lenium marinum Asp N n 0.02 35 hc 0 8 2 530 172 12 4.4 14.0 1261 Co 18 9 5 5<br />
Asp leniurn obovatum Asp N s -0.18 30 hc 0 9 1 135 19 11 5.3 15.4 1197 16 5 4 3<br />
Asp lenium onopteris Asp N o 45 hc 0 9 1 0 34 0 4.6 14.5 1200 1, 3, 16 5 7 3<br />
Asp leniurn ruta-muraria Asp N n 0.15 12 hc 0 7 6 2184 898 11 3.7 14.7 1074 3, 16, 17 7 7 2<br />
Asp leniurn septentrionale Asp N s -0.08 15 hc 0 7 3 55 2 0 2.5 13.2 1825 16 8 2 2<br />
Aspleniurn trichomanes Asp N n 0.07 35 hc 0 8 6 2294 911 12 3.6 14.5 1121 3, 16, 17 5 8 2<br />
Asplenium viride Asp N n -0.21 20 hc 0 4 6 435 43 0 2.0 12.8 1701 15, 16 4 8 3<br />
Aster (alien N American taxa) Aste AN 150 hc Rhizl Am 1211 53 5 3.7 15.3 934 3, 17, 21 7 7 6<br />
Aster lanceolatus Aste AN 120 hc Rhizl Am6 211 5 0 3.9 15.8 844 3, 17 7 7 6<br />
Aster lanceolatus x novi-belgii<br />
(A. x salignus) Aste AN 150 hc Rhizl Gard 373 9 0 3.8 15.6 890 3, 17 7 7 6<br />
Aster linosyris Aste N r -0.10 50 hc 0 7 3 c 9 0 0 4.9 15.8 1006 Co 18 8 8 1<br />
Aster novae-angliae Aste AN 200 hc Rhizl Am6 83 0 1 3.9 16.1 806 3 7 7' 6<br />
Aster novi-belgii Aste AN 150 hc Rhir l Am6 557 12 3 3.7 15.2 936 3, 17 7 7 6<br />
Aster tripolium Aste N n -0.44 100 hc 0 7 5 703 267' 3 4.3 14,8 1109 Co 21 9 7 6<br />
Astragalus alpinus Faba N VU r 30 hc 0 1 6 4 0 0 -0.9 11.0 1275 7, 15 9 6 2<br />
Astragalus danicus Faba N n -0.88 30 hc 0 7 6 c 242 3 0 3.3 14.8 745 7 8 8 2<br />
Astragalus glycyphyllos Faba N n -0.36 100 hc 0 7 3 357 0 0 3.4 15.7 711 1, 3, / 6 6 7 3<br />
NJ<br />
1‘ ) Athyrium distentifolium Wood N s 0.38 30 hc 0 1 6 98 0 0 0.3 11.2 2098 15 6 3 4<br />
Athyrium filix-femina Wood N n 0.25 90 hc 0 5 6 2574 849 12 3.5 14.4 1132 1, 16 5 5 6<br />
Athyriurn flexile Wood NE VU r 20 hc 0 1 1 16 0 0 -0.9 10.7 1753 15, 16 7 3 4<br />
Atriplex glabriuscula Chen N n -0.93 33 Th 0 5 2 780 159 10 4.2 14.4 1163 Co 19 9 7 8<br />
Atriplex laciniata Chen N n 0.38 30 Th 0 7 1 418 92 13 4.5 14.8 979 Co 19 9 7 7<br />
Atriplex littoralis Chen N n 1.59 100 Th 0 7 6 362 36 3 4.2 15.4 822 Co 19 9 7 6<br />
Atriplex longipes Chen N s 90 Th 0 4 3 39 0 0 4.2 15.6 982 Co 21 9 7 8<br />
Atrip/ex patula Chen N n -0.34 87 Th 0 6 4 2318 787 12 3.7 14.8 1013 3, 4 7 7 7<br />
Atriplex pedunculata Chen N CR r 30 Th 0 7 4 20 0 0 3.9 16.4 603 Co 21 91 7 8<br />
Atriplex portulacoides Chen N n 0.06 80 Pn 0 9 1 322 68 10 4.6 15.7 869 Co 21 9 8 6<br />
Atriplex praecox Chen N s 10 Th 0 4 3 62 0 0 3.6 12.8 1503 Co 19 9 7 6<br />
Atriplex prostrata Chen N n 1.10 100 Th 0 6 4 1847 349 5 3.9 15.1 955 3, 4, 19, 21 8 7 7<br />
Atropa belladonna Sola N n -0.33 150 hc 0 7 3 414 0 0 3.6 16.1 717 1, 3 5 6 6<br />
Avena fatua Poac AR 1.17 150 Th 0 Eur 1556 170 5 3.71 15A 849 3, 4 71 7 7<br />
Avena sativa Poac AC 150 Th 0 Eur 728 131 4 3.9 15A 903 4 7 7 7<br />
Avena strigosa Poac AC -3.01 120 Th 0 Crop 270 72 6 4.0 14.6 1042 4 7 5 5<br />
Azol a filicuboides . Azol AN 2.76 1 Hy Frag Am4, SAm 660 21 9 4.0 16.0 774 13, 14 7 11 8 8<br />
Baldellia ranunculoides Alis N n -1.08 20 20 Hy 0 Sto12 8 2 536 344 6 4. 1 15.1 974 13, 14 8 10 6 2<br />
Bal ota nigra Lami AR -0.37 100 hc Rhiz2 8 3 1365 70 12 3.8 15.7 797 3 71 4 8 6<br />
Barbarea intermedia Bras AN 1.92 60 hc 0 Eur 735 207 7 3.7 15.0 975 4 8 5 6 7<br />
Barbarea stricta Bras AN 0.50 100 p hc 0 5 4 c Eur, Asl 104 1 0 3.7 15.9 705 11, 13, 14 8 7 7 8<br />
Barbarea verna Bras AN 1.34 90 b Th hc 0 Eur 514 28 7 4, 1 15.6 943 3 8 5 6 6<br />
Barbarea vulgaris Bras N n -0.02 90 p hc 0 7 4 1869 615 3 3.7 15.0 943 3, 14 7 6 7 8<br />
Bartsia alpina Scro N r -0.10 22 hc Rhizl 1 3 18 .".0 0 0.4 11.9 2069 7, 11, 15 5 8 71 2
S<br />
Taxon name Fam NS CS RS Chg Hght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tja n Tjul Prec Co Br Habitats L F R N<br />
Bell is pe rennis Aste N n 0.89 8 hc h Rhizl 7 3 2797 984 14 3,5 14.5 1105 6 8 5 6 4<br />
Berberis vulgaris Serb NA n -0 61 250 Pn w Rhizl 7 3 974 26 1 3.4 15.2 892 1, 3 7 4 8 3<br />
Baru la erecta Apia N n -0.02 100 Hy h Irreg 7 3 1111 265 1 3.8 15.5 843 11 7 10 7 7<br />
Beta vulgaris Chen N n 1.23 150 b he h 0 9 1 607 205 14 4.6 15.4 952 Co 18, 19 9 5 7 8<br />
Betula nana Betu N s -0.09 100 Pn w Rhizl 2 6 125 0 0 0.71 11.5 1585 10, 12, 15 7 8 1 1<br />
Betula pendula Betu N n -0.23 2500 Ph w o 5 4 2293 390' 0 3.3 14.6 1073 1 7 5 4 4<br />
Betula pubescens Betu N n 0.40 2000 Ph w 0 5 4 2399 779 0 3.4 14.4 1123 1 7 7 4 4<br />
Bidens cernua Aste N n -0.54 67 Th 0 7 6 874 281 2 3.9 15.5 883 13, 14 8 9 7 7<br />
Bide ns tripartita Aste N n -0.43 67 Th o 7 5 1055 222 5 3.9 15.5 884 11, 13 8 8 7 7<br />
Blacks tonia perfoliata Gent N n 0.12 45 Th 0 9 2 7871 198 2 4.0 15.8 812 7 8 5 8 2<br />
Blechnum spicant Blec N n -0.39 50 hc o 7 3 2159 831 9 3.5 14. 1 1198 1, 2, 10, 16 5 6 3 3<br />
Blysmus compressus Cype N n -1.28 37 hc Rhiz2 7 3 c 384 0 3.2 15.2 840 11 8 8 8 3<br />
Blysmus rufus Cype N n -0.53 37' hc Rhiz2 4 3 367 7 0 3.8 13.6 1371 Co 21 8 8 7 4<br />
Bo lboschoe nus maritimus Cype N n 0.00 100 Hy Rhizl DRg 8 4 766 21 7 4.3 15.1 1020 Co 21 8 10 8 7'<br />
Bo trychium lunaria Ophi N n -0.43 15 Gn 0 5 6 1109 13 1 3.0 13.8 1259 7, 16 8 4 6 2<br />
Brachy podium pinnatum Poac N n 0.15 90 he Rhizl 7 4 612 2 0 3.6 15.9 745 7 7 3 8 3<br />
Brachy podium sylvaticum Poac N n -0.17 95 he 0 7 3 2310 78 12 3.7 14.7 1062 1 6 5 6 5<br />
Brassica napus Bras AN 2.88 130 b Th hc 0 Gard 1758 14 7 3.6 15.1 914 3, 4, 17 7 4 7 7<br />
Brassica nigra Bras NA n -0.02 150 Th 0 7 3 1080 5 11 4.0 15.8 822 3, 4 8 5 7 6<br />
Brassica oleracea Bras NA s 0.90 130 Pn sw 0 8 2 98 1 4.9 15.6 922 17, 18 8 4 71 8<br />
Brassica rapa Bras AR 0.74 100 b Th hc 0 7 4 1407 63 7 3.9 15.0 993 4 7 5 7 6<br />
Briza maxima Poac AN 62 Th 0 0 3 Eur 239 11 4.6 15.8 932 3, 17, 19 7 3 4 2<br />
Briza media Poac N n 0.75 62 he Rhizl 7 3 1853 58 2 3.5 14.9 971 7 8 5 7 3<br />
Briza minor Poac AR 0.28 55 Th 0 9 1 92 8 5.2 16. 1 919 4 7 4 5 5<br />
Bromopsis benekenii Poac N s 0.25 105 hc 0 7 3 c 64 0 3.0 15.3 896 1 5 5 7 5<br />
Bromopsis erecta Poac N n -0.01 110 hc 0 7 3 798 4 3 3.7 15.9 764 7 7 4 5 3<br />
Bromopsis inermis Poac AN 1.71 150 hc Rhiz2 7 4 Eur, Asl 263 0 3.6 15.9 757 3 8 4 8 5<br />
Bromopsis ramosa Poac N n -0.18 170 hc 0 7 3 1887 45 0 3.5 14.9 995 1 4 6 7 7<br />
Bromus commutatus Poac N n 1.07 95 Th 0 7 3 675 3 0 3.9 16. 1 772 3 7 4 8 6<br />
Bromus hordeaceus Poac N n -0.37 80 Th o 8 3 2406 83 14 3.71 14.7 1051 4, 6 8 4 71 4<br />
Bromus racemosus Poac N n 0.74 95 Th 0 7 3 516 7 0 4.0 15.8 852 3, 6 6 6 7 8<br />
Bromus secalinus Poac AR -1.15 90 Th 0 Unk 403 1 4 3.9 15.8 816 4 6 4 5 4<br />
Bryonia dioica Cucu N n -0.50 400 Gn 0 9 2 1004 4 3.6 16.0 726 3 7 5 7 7<br />
Bu ddleja davidii Budd AN 3.73 500 Ph w 0 As 1434 26 14 3.9 15.4 930 3, 17 7 5 7 5<br />
Bu nium bulbo cas tanum Apia N r 0. 14 50 Gn 0 8 2 13 0 3.3 16.3 633 4 71 4 9 4<br />
Bupleururn baldense Apia N EN r 10 Th 0 9 1 3 8 6.1 16.5 808 Co 18, 19 9 3 8 2<br />
Bupleurum falcatum Apia AN 100 hc 0 8 5 Eur, As 8 0 3.4 16.0 776 3 6 3 9 3<br />
Bupleurum rotun difolium Apia AR EW -4.58 30 Th 0 Eur? 287 1 3.8 16.0 753 4 8 3 9 4<br />
Bupleurum tenuissimum Apia N s -0.97 50 Th 0 8 3 161 0 4.2 16.4 684 3, 6 9 7 8 4<br />
Butomus umbellatus Buto N n -0.04 150 150 Hy Rhiz2 DRg 7 4 685 0 3.71 16.0 715 13, 14 7i 11 71 71<br />
Buxus sempervirens Buxa N r 2.54 500 Ph w O 9 2 2 0 3.7 16.6 716 1, 3 4 4 8 5<br />
Cakile maritima Bras N n -0.38 30 Th h 0 6 3 576 131 13 4.4 14.6 1011 Co 19 9 6 7 7<br />
Calamagrostis canescens Poac N n -0.33 120 hc h Rhiz2 5 4 c 293 0 0 3.4 157 723 11 7 9 7 5<br />
Calamagrostis epigej os Poac N n 0.47 200 hc h Rhiz2 5 5 936 9 4 3.7 15.7 812 3, 11 7 7 7 6<br />
Calamagrostis purpurea Poac N r 150 hc h Rhiz2 4 4 10 0 0 1.6 13.1 1346 1, 11 71 8 6 3<br />
Calamagrostis scotica Poac NE VU r 100 hc h Rhizl 4 1 1 0 0 3.6 12.8 888 11 8 8 6 4
Taxon name Fam NS CS RS Chg_ Hght Len P1 P2 LF1 LF2 W Clonel Clone2 E1 E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Calamagrostis stricta Poac N r -0.74 100 hc Rhiz1 2 6 22 6 0 2.9 14.2 928 11 9 9 4 2<br />
Calendula <strong>of</strong>ficinalis Aste AN 50 a Th 0 Unk 764 24 10 4.0 15.7 822 3, 17 8 5 7 7<br />
Callitriche brutia Cal N 25 a Hz Node2 9 1 213 63 3 4.1 14.9 1087 13 8 10 5 5<br />
Ca Ilitriche hamulata Cal N 80 a p Hz Hy Node2 Irreg 5 2 1758 282 6 3.3 14.2 1162 13, 14 7 11 6 5<br />
Callitriche hamulata sens.lat Cal N 1.12 25 80 a p Hz Hy Node2 lrreg 6 3 1758 282 6 3.3 14.2 1162 11, 13, 14 7 10 5<br />
Callitriche hermap hm ditica Cal N 0.21 50 p Hy Irreg 4 6 392 115 0 3.1 13.7 1120 13 7 12 7 5<br />
Callitriche obtusangula Cal N 1.35 60 Hy Irreg 8 2 757 157 4 4.1 15.7 840 13, 14 7 11 7 6 1<br />
Ca llitriche platycarpa Cal N 15 100 p Hz Hy Node2 lrreg 7 3 1006 173 5 3.7 15.1 947 11, 13 6 10 7 7 0<br />
Callitriche stagnalis Cal N 15 60 p Hz Hy Node2 Irreg 7 3 1488 346 5 3.71 14.6 1083 13 7 10 6 6 1<br />
Ca & riche stagnalis sens.lat Cal N n 1.51 15 80 p Hz Hy Node2 Irreg 7 3 2647 769 11 3.5 14.4 1105 11, 13, 14 6 10 6 6<br />
Callitriche truncata Cal N s 0.47 20 Hz 0 Irreg 9 1 52 1 2 4. 1 16.1 719 13, 14 7 12 7 7<br />
Eric N n -0.64 60 Ch Pn 0 Nodel 5 3 2434 905 11 3.5 14.3 1157 10, 12 7 6 2 2
Taxon name Fan/ NS CS RS Chg Hght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Carex binervis Cype N n -0.17 90 hc 0 7 / 1927 647 3 3.3 14.0 1243 8, 10, 16 7 6 3 2<br />
Carex buxbaumii Cype N VU r 70 hc Rhizl 4 4 c 3 1 0 3.3 13.5 1410 11 8 8 7 2<br />
Carex capillaris Cype N s -0.35 40 hc Ogr 2 6 120 0 0 1.2 11.9 1636 7 9 6 8 2<br />
Carex caryophyllea Cype N n -0.20 15 hc Rhizl 7 4 1866 437 11 3.4 14.7 1079 7 7 4 7 2<br />
Carex chordorrhiza Cype N VU r 40 hc Rhiz2 2 6 c 4 0 0 1.4 11.9 1176 11 9 9 4 3<br />
Carex curia Cype N n 0.17 50 hc Rhizl 4 6 1190 219 0 2.7 13.6 1303 11 8 9 3 2<br />
Carex davalliana Cype N EX x 25 hc 0 7 3 c 1 0 0 4.0 16.3 833 11 9 9 8 2<br />
Carex depauperata Cype N CR r 60 hc Rhizl 9 2 9 1 0 4. 1 15.8 823 3 5 4 71 4<br />
Carex di<strong>and</strong>ra Cype N n 0.22 60' hc Rhizl 5 6 378 294 0 3.6 14.4 1042 11 8 9 5 3<br />
Carex digitate Cype N s 0.04 15 hc 0 5 3 c 39 0 0 3.3 15.5 859 1, 16 5 5 8 4<br />
Carex dioica Cype N n -0.35 30 hc Rhizl 2 6 1100 204 0 2.7 13.2 1404 11 8 9 6 2<br />
Carex distans Cype N n -0.47 72 hc 0 8 3 814 213 9 4.3 15.0 1039 Co 21 8 6 7 5<br />
Carex disticha Cype N n -0.03 90 hc Rhiz2 7 4 12271 48 1 3 3.6 15.0 910 11 7 8 6 4<br />
Carex divisa Cype N s -0.35 70 hc Rhizl 9 2 162 1 4.4 16.4 727 6 8 7 7 6<br />
Carex divulsa Cype N n 82 hc 0 8 4 780 24 4.2 15.8 844 3, 6, 7 7' 4 7 6<br />
Carex echinata Cype N n -0.75 40 hc 0 5 3 2100 78 3.4 14.1 1207 11, 12, 14 8 8 3 2<br />
Carex elate Cype N n -0.32 95 Hy hc 0 7 5 294 22 3.8 15.2 903 11 7 10 7 5<br />
Carex elongate Cype N s 0.06 80 hc 0 5 4 c 72 1 3.6 15.5 899 1 5 8 6 6<br />
Carex erk etorum Cype N s -0.46 17 hc Rhizl 5 4 c 33 2.9 15.3 801 7 6 4 7 1<br />
Carex extensa Cype N n -0.23 40 hc Ogr 8 3 440 19 4.5 14.5 1228 Co 21 8 7 7 5<br />
Carex filiformis Cype N r 0.23 50 hc Rhiz2 7 4 c 13 3.5 16.3 708 6, 7 7 7 8 5<br />
NJ Carex /lam a Cype N n 0.53 50 hc Rhiz2 8 3 2706 95 3.5 14.5 1104 7, 11 7 5 6 2<br />
in Carex fi ava Cype N VU r 70 hc 0 5 3 1 3.2 14.7i 1585 1, 11 7i 9 8 2<br />
Carex hirta Cype N n 0.17 70 hc Rhiz2 7 3 1958 57 3.7 15.0 963 6 T 7 7 6<br />
Carex hostiana Cype N n -0.05 57 hc 0 7 3 1578 42 3.2 13.8 1290 11 8 9 6 2<br />
Carex humifi s Cype N s -0.01 10 hc Ogr 7 5 c 30 3.9 16. 1 845 7 8 3 8 2<br />
Carex lachenalii Cype N r -0.22 20 hc Rhizl 1 6 9 -1.1 10.4 1948 11, 15 8 7 4 1<br />
Carex laevigata Cype N n -0.01 120 hc 0 7 1 1012 29 3.6 14.4 1240 1, 16 5 8 5 4<br />
Carex lasiocarpa Cype N n 0.73 120 Hy hc Rhiz2 4 6 461 16 3.1 13.6 1383 11 8 10 6 3<br />
Carex fi mosa Cype N n 0.14 40 Hy hc Rhiz2 4 6 423 19 3.3 13.4 1431 11, 12 8 10 4 1<br />
Carex magellanica Cype N s -0.02 40 hc Rhizl 4 6 131 1.7 12.8 1808 12 9 9 2 1<br />
Carex marifi ma Cype N s -1.34 18 hc Rhiz2 1 6 83 3.6 12.9 964 Co 19 9 8 7 2<br />
Carex microglochin Cype N VU r 12 hc Rhiz2 1 3 1 -0.7 11.0 1855 11 9 9 8 2<br />
Carex montane Cype N s 0.68 35 hc Rhizl 7 3 c 48 4.0 15.5 1193 6, 8 7 6 4 1<br />
Carex muricata Cype N n 85 he 0 8 4 912 6 1 3.8 15.4 939 3, 7, 8 T 4 6 4<br />
Carex nigra Cype N n -0.01 70 hc Rhiz2 5 4 2582 87 3.5 14.3 1131 11 7 8 4 2<br />
Carex norvegica Cype N VU r 30 hc 0 1 6 6 -0.8 10.8 1901 15 8 7 7 2<br />
Carex ornithopoda Cype N r 0.28 15 hc 0 4 3 15 0 2.1 13.8 1272 7, 16 8 3 9 3<br />
Carex otrubae Cype N n -0. 14 100 hc 0 8 4 1636 40 9 4.0 15.3 939 11 6 8 7 7<br />
Carex Ova rls Cype N n -0.21 90 hc 0 5 4 2422 74 7 3.4 14.3 1138 3, 10 7 7 5 4<br />
Carex pallescens Cype N n -0.51 60 hc 0 5 4 1596 18 1 3.0 14.2 1236 1 6 6 5 4<br />
Carex panicea Cype N n -0.31 50 hc Rhiz2 5 3 2526 89 6 3.5 14.3 1139 11 8 8 4 2<br />
Carex paniculata<br />
Cype N n -0.11 150<br />
hc Hy 0 7 3<br />
1516 50 5 3.7 14.9 1036 1, 11 6 9 6 6,<br />
Carex pauciflora<br />
Cype N n -0.59 25'<br />
hc<br />
Rhizl 4 6<br />
377 0 1.7 12.1 1789 12<br />
8 9 1 1<br />
Carex pendula Cype N n 1.30 150 hc 0 8 3 1409 30 10 3.9 15.3 928 1, 14 5 8 7 6<br />
Carex pilulifera Cype N n -0.04 35 hc 0 7 3 2111 44 8 3.3 14.1 1197 8 7 5 3 2
R N<br />
6 6<br />
5 2<br />
7 3<br />
3 2<br />
7 5<br />
6 6<br />
7 7<br />
4 2<br />
7 2<br />
7 3<br />
6 4<br />
7 6<br />
6 5<br />
6 3<br />
5 4<br />
6 2<br />
onel Clone2 El E2 C Origin GB IR CI Tjan Tjul Pree Co Br Habitats L F<br />
7<br />
8,<br />
9<br />
8<br />
8<br />
4<br />
71<br />
8 1<br />
8<br />
8<br />
7<br />
3<br />
4<br />
7'<br />
8 1<br />
8<br />
754 11<br />
1239 11, 16<br />
1125 Co 18<br />
1541 15<br />
936 11<br />
1063 1, 14<br />
814 11, 14<br />
1193 11<br />
1699 15, 16<br />
2262 15<br />
823 3, 6, 7<br />
841 1, 14<br />
1050 1<br />
1904 15<br />
1072 11<br />
1169 11, 14, 19<br />
16.0<br />
13.9<br />
15.4<br />
10.6<br />
13.1<br />
14.8<br />
15.7<br />
14.0<br />
11.5<br />
11.3<br />
15.7<br />
15.7<br />
14.8<br />
11.3<br />
14.6<br />
14.2<br />
3.8<br />
3.3<br />
5.3<br />
-1.2<br />
3.1<br />
3.7<br />
3.9<br />
3.3<br />
0.7<br />
0.3<br />
3.6<br />
3.8<br />
3.6<br />
-0.1<br />
3.3<br />
3.5<br />
3<br />
4<br />
7<br />
0<br />
0<br />
5<br />
41<br />
0<br />
0<br />
0<br />
1<br />
0<br />
2<br />
0<br />
1<br />
9<br />
72<br />
656<br />
42<br />
0<br />
0<br />
675<br />
160<br />
731<br />
0<br />
0<br />
48<br />
102<br />
608<br />
0<br />
230<br />
855<br />
672<br />
1874<br />
56<br />
17<br />
4<br />
1879<br />
1186<br />
1924<br />
31<br />
71<br />
1043<br />
417<br />
1899<br />
83<br />
913<br />
2337<br />
7 4<br />
7 2<br />
8 2<br />
1 6<br />
4 1<br />
7 3<br />
7 4<br />
5 6<br />
1 6<br />
1 6<br />
7 3<br />
7 2<br />
7 5<br />
2 6<br />
5 6<br />
5 6<br />
hizl<br />
hizz21 h<br />
hiz2<br />
hiz2<br />
hIz21 h<br />
hiz2<br />
hizl<br />
a,<br />
84 2 1<br />
1200 11,14<br />
13.9<br />
3.1<br />
2<br />
434<br />
1168<br />
7 3<br />
2 0<br />
7 3 1<br />
8 6 0<br />
7 2 0<br />
s 6 0<br />
4 5 3<br />
7 6 1<br />
4 2 0<br />
s 5 0<br />
7 71 1<br />
7 3<br />
7 2<br />
7 3<br />
6 5<br />
6 5<br />
8 3<br />
6 3<br />
a 3<br />
8 3<br />
5 2 0<br />
8<br />
8<br />
7<br />
8<br />
4<br />
9'<br />
8<br />
7<br />
5<br />
6<br />
9<br />
a<br />
7<br />
7<br />
71<br />
8<br />
8<br />
9<br />
8<br />
9<br />
8<br />
8<br />
4<br />
s<br />
4<br />
9<br />
7<br />
1194 14<br />
1278 11, 19<br />
731 13<br />
947 7<br />
895 1<br />
962 Co 18, 19<br />
868 3, 6, 17<br />
1578 11, 14<br />
950 1<br />
936 13, 14<br />
1027 Co 18<br />
878 7, 17<br />
744 3<br />
836 3, 4, 17<br />
1093 6, 7<br />
632 6, 7<br />
980 7, 19<br />
1063 Co 19, 21<br />
841 Co 21<br />
1170 10<br />
825 Co 18<br />
896 3, 16, 17,<br />
763 1<br />
1166 1<br />
797 1<br />
2003 15, 16<br />
2178 . 15, 16<br />
14.2<br />
13.9<br />
16.4<br />
15.3<br />
15.4<br />
15.9<br />
15.0<br />
13.9<br />
15.2<br />
15.0<br />
15.1<br />
15.5<br />
16.1<br />
15.4<br />
14.5<br />
15.6<br />
15.1<br />
14.3<br />
16.1<br />
15.4<br />
16.5<br />
15.5<br />
16.2<br />
14.7<br />
16.2<br />
11.4<br />
11.3<br />
3.4<br />
3.8<br />
3.9<br />
3.9<br />
3.6<br />
5.7<br />
3.6<br />
3.4<br />
3.6<br />
3.8<br />
4.8<br />
4.1<br />
4.0<br />
3.8<br />
3.6<br />
3.8<br />
4.0<br />
3.8<br />
4.4<br />
5.8<br />
5.5<br />
4.0<br />
3.7<br />
3.7<br />
3.8<br />
0.4<br />
0.8<br />
6<br />
5<br />
0<br />
10<br />
9<br />
10<br />
2<br />
1<br />
12<br />
3<br />
14<br />
10<br />
3<br />
5<br />
11<br />
2<br />
14<br />
0<br />
8<br />
0<br />
2<br />
14<br />
0<br />
0<br />
0<br />
0<br />
0<br />
761<br />
179<br />
0<br />
243<br />
52<br />
8<br />
30<br />
42<br />
140<br />
304<br />
172<br />
494<br />
1<br />
56<br />
975<br />
125<br />
710<br />
3<br />
17<br />
0<br />
0<br />
357<br />
0<br />
31<br />
0<br />
0<br />
0<br />
2203<br />
477<br />
24<br />
1131<br />
1488<br />
79<br />
303<br />
296<br />
1693<br />
955<br />
463<br />
1216<br />
153<br />
884<br />
2658<br />
1239<br />
1811<br />
111<br />
457<br />
3<br />
3<br />
1361<br />
233<br />
131<br />
10<br />
77<br />
46<br />
c<br />
5 2<br />
5 3<br />
7 4<br />
7 4<br />
7 3<br />
SAf<br />
Eur?, Asl ?<br />
ode2<br />
8 1<br />
Eur<br />
5 3<br />
9 1<br />
9 2<br />
ode2<br />
Eur<br />
7 3<br />
7 2<br />
7 4<br />
8 3<br />
7 3<br />
a 4<br />
8 0<br />
9 1<br />
18<br />
Eur<br />
7 3<br />
7 3<br />
7 3<br />
1 3<br />
1 3<br />
odel<br />
hizl
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tja n Tjul Prec Co Br Habitats L F R N S<br />
Cerastium arvense Cary N n -1.05 30 p Ch Rhiz2 5 6 814 39 0 3.3 15.3 773 8 8 4 5. 3 0<br />
Co a st/UM brachypetalum Cary AN 30 a Th 0 8 3 Eur 2 0 0 3,4 16.3 657 3, 7 9 3 8 2 0<br />
Cerastiurn cerastoides Cary N s -0.05 12 p Ch Nodal 1 3 29 0 0 -0.4 10.8 1994 15 8 8 5 4 0<br />
Cerastiurn diffusum Cary N n 0.38 23 a Th 0 7 3 1174 247 12 4.0 14.6 1062 Co 18, 19 9 4 61 3 1<br />
Cerastium fontanum Cary N n 1.40 30 p Ch Rhizl Nodal 5 4 2805 985 14 3.5 14.4 1106 6 7 5 5 4 0<br />
Cerastium glomeratum Cary N n 1.44 30 a Th 0 8 3 2631 823 14 3.6 14.5 1079 3, 5 7 5 6 5 0<br />
Cerastium nigrescens Cary NE VU r 5 p Ch 0 4 1 2 0 0 3.0 11.5 1256 16 9 3 5 1 0<br />
Cerastiurn pumilum Cary N s -0.171 11 a Th 0 7 3 87 0 0 4,1 16.2 806 7 8 2 8 1 0<br />
Cerastium sernidec<strong>and</strong>rum Cary N n 0.50 14 a Th 0 7 3 1117 61 12 3.7 15.3 846 8, 18, 19 8 3 6 3 0<br />
Cerastium tomentosurn Cary AN 2.97 30 p Ch Rhiz2 Node2 Eur 1303 140 8 3.7 15.2 898 3, 17, 19 8 3 7 5 1<br />
Ceratocapnos claviculata Furna N n 0.57 75 a Th ' 0 7 1 1122 20 2 3.3 14.6 1111 1, 9 5 5 4 5 0<br />
Ceratochloa carinata Poac AN 2.09 80 p hc 0 Am4 183 1 2 3,8 16. 1 744 3, 4 8 5 6 6 0<br />
Ceratoch/oa cathartica Poac AN 0.63 100 p hc 0 Am, SAm 184 0 9 4.2 16.1 796 3 , 4 7i 4 5, 5 0<br />
Ceratophyllum demersum Gera N n 0.87 100 p Hy Irreg 6 6 927 62 1 3,7 15.8 770 13 7 12 7 7<br />
Ceratophyllum submersum Cera N n 0.39 100 p Hy Irreg 7 4 208 3 5 3,9 16.3 705 13 7 12 8 8<br />
Ceterach <strong>of</strong> icinarum AspI N n -0.30 20 p he 0 9 2 1093 787 9 4.0 15.0 1061 3, 16 7 3 8 1<br />
Chaenorhinum minus Scro AR -0.63 25 a Th 0 7 3 1468 170 0 3.6 15.3 899 3, 4, 17 8 4 7 4<br />
Chaerophyllum temulum Apia N n -0.64 100 b hc 0 7 3 1786 0 5 3.6 15.4 890 3 6 5 71 7i<br />
Chamaecyparis lawsoniana Cupr AN 4100 p Ph w 0 Arn4 827 46 4 3.6 15.3 965 17 5 5 6 4<br />
Chamaemelum nobile Aste N n -0.92 30 p hc h Node2 8 2 308 115 13 4.6 15.7 990 8 8 7 5 5<br />
Charnerion angustifolium Onag N n -0.01 150 p Gn hc h Root 5 6 2603 650 10 3.4 14.5 1075 3, 17 6 5 6 5<br />
Chelidonium rnaj us Papa AR -0.72 90 p he h 0 7 5 1662 220 9 3.7 15.3 905 3 6 5 8 7<br />
Chenopodium album Chen N n 100 a Th h 0 6 5 2340 782 14 3.7 14.8 1018 4 7 5 71 71 1<br />
Chenopodium album agg. Chen N n -0.73 100 a Th h 0 6 5 2340 782 14 3.7 14.8/ 1018 4 7 5 7 7 1<br />
Chenopodiurn bonus-henricus Chen AR -1.79 50 p hc h 0 Eur 1363 81 1 3,4 15.2 883 3 8 5 7 8 0<br />
Chenopodium<br />
chenopodioides Chen N s -0.17 30 a Th h 0 7 4 39 0 2 4.2 16.7 612 Co 6, 21 8 7 7 8 4<br />
Chenopodiurn ficifoliurn Chen AR 1.90 90 a Th h 0 7 4 745 11 7 3.9 16. 1 745 4 7 6 6 7 0<br />
Chenopodiurn glaucurn Chen AR -1.32 50 a Th h 0 7 6 157 2 2 4.0 16. 1 724 17 8 6, 7i 9 3<br />
Chenopodiurn hybridum Chen AR -0.32 100 a Th h 0 7 6 285 0 1 3.7 16.2 695 4 7 4 7 7 0<br />
Chenopodiurn murale Chen AR -1.63 100 a Th h 0 8 4 412 8 13 4.2 16.0 797 4 8 6 6 7 0<br />
Chenopodiurn polyspermum Chen AR 0.62 50 a Th h 0 7 4 998 8 12 3.9 16.0 794 4 7 6 7 8 0<br />
Chenopodiurn rubrum Chen N n' 1.00 70 a Th h 0 7 4 1267 142 8 3.8 15.7 800 4, 11 7 7 7 8 1<br />
Chenopodiurn urbicurn Chen AR 1 -4.57 100 a Th h 0 7 4 239 1 0 4.0 16.1 762 4 71 5 71 7t<br />
Chenopodiurn Chen AR VU -2.60 35 a Th h 0 8 4 180 0 6 4. 1 16.1 752 Co 15, 19 7 4 7 9<br />
Chrysanthemum segetum Aste AR -1.80 60 a Th h 0 8 3 1682 471 10 3.8 14.8 1022 4 7 5 6 5<br />
Chrysospleniurn alternifolium Saxi N n 0.62 20 p he h Sto12 3 6 790 0 0 2.8 14.4 1042 11, 14 5 8 6 6<br />
Chrysosplenium<br />
oppositifolium Saxi N n -0.36 15 p Ch hc h Node2 7 2 2067 688 6 3.4 14.3 1168 1, 14 5 9 5 5<br />
Cicendia filiformis Gent N s -0.70 10 a Th h 0 9 2 66 371 5 5.4 15.6 1063 10 9, 8 3 2<br />
Cicerbita alpina Aste N VU r 130 p hc h Rhiz2 4 3 4 0 0 -1.3 10.5 1375 15, 16 7 6 6 6<br />
Cicerbita rnacrophylla Aste AN 175 p hc h Rhiz2 Eur 724 42 0 3.3 14.9 920 3, 17 7 5 6 6<br />
Cichorium intybus Aste AR . -1.27' 110 p hc h 0 8 4 1312 60 10 3.8 15.5 840 3 5 4 7 5<br />
Cicuta virosa Apia N s 0.55 150 p Hy h 0 5 5 c 139 139 0 3.5 14.8 926 1/ , 13, 14 7 10 7 5<br />
Circaea alpina Onag N 5 . 30 p Gn h Rhiz2 4 6 40 0 0 2.2 13.0 1836 1 4 71 5; 5<br />
tJ
Taxon name Fam NS CS RS Ch Hght Len P P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI T an T'ul Prec Co Br Habitats L F R N S<br />
Circaea alpina x lutetiana (C<br />
x intermedia) Onag NH n 0.48 45 Gn Rhiz2 7 3 570 49 0 2.7 13.4 1477 1 6 6<br />
Circaea lutetiana Onag N n -0.38 60 Gn Rhiz2 7 3 2053 748 8 3.7 14,9 1041 1 6 6<br />
Cirsium acaule Aste N n -0.52 15 hc Rhial 7 3 734 0 3 3.7 16.1 742 7 4 3<br />
Cirsium arvense Aste N n 0.47 120 Gn Root 7 5 2736 968 14 3.6 14.5 1092 3, 4, 6 6 6<br />
Cirsium dissectum Aste N n -0. 14 60 hc Rhizl 7 1 539 553 2 4.0 15.0 1043 11 8 2<br />
Cirsium eriophorum Aste N n -0.08 150 hc 0 7 3 447 0 0 3.6 16.0 745 7 4 5<br />
Cirsium heterophyllum Aste N n -0.44 120 he Rhizl 4 4 761 1 0 2.0 12.9 1476 6, 16 6 5<br />
Cirsium palustre Aste N n 0.15 175 hc 0 5 4 2697 95 12 3.5 14.5 1105 11, 14 8 4<br />
Cirsium tuberosurn Aste N VU r 0.41 80 hc o 8 2 17 0 3.9 16.1 882 7 6 3<br />
Cirsium vulgare Aste N n 0.80 150 hc 0 7 4 2789 98 14 3.5 14.5 1103 3, 5, 6, 7 5 6<br />
Cladium mariscus Cype N n 0.11 200 Hy Gn Rhir l 8 4 232 25 1 4.1 14.7 1085 11 10 4<br />
Claytonia perfoliata Port AN 0.50 30 a Th 0 Am4 704 10 3.6 15.6 768 4, 17, / 9 6 5<br />
Claytonia sibirica Port AN 1.28 40 a p Th hc 0 As2, Am4 1166 2 6 3.2 14.4 1092 1, 3 7' 6<br />
Clematis vitalba Ranu N n 0.00 3000 p Ph 0 7 3 954 0 4.0 16.0 815 3 4 5<br />
Clinopodium acinos Lami N n -1.59 22 a Th 0 7 3 551 0 3.6 15.8 778 16 2 1<br />
Clinopodium ascendens Lami N n 0.04 60 P hc Rhizl 7 3 657 6 2 4.2 15.9 854 3, 16 5 6<br />
Clinopodium calamintha Lami N s -0.31 60 P hc Rhiz2 9 2 129 4 3.7 16.4 641 3 3 3<br />
Clinopodium menthifolium Lami N EN r 60 p hc Rhizl 7 3 1 0 4.8 16.3 844 1 5 5<br />
Clinopodium vulgare Lami N n -0.67 77 P hc Rhizl 7 6 1317 2 3.5 15.4 880 7 4 4<br />
Cochlearra anglica Bras N n 0.02 40 b hc 0 7 1 297 9 0 4.5 15.6 917 Co 21 8 6<br />
Cochlearia atlantica Bras NE DD r 20<br />
t.. )<br />
P he 0 4 1 2 0 4.4 12.8 1830 Co 18 6 5<br />
CO Cochlearia danica Bras N n 3.31 25 a Th 0 7 1 588 13 14 4.5 14.9 1056 Co 3, 18 6 5<br />
Cochlearia micacea Bras NE s 10 b p hc 0 1 1 32 0 0.2 11.4 2221 15 2<br />
Cochlearia <strong>of</strong>ficinalis Bras N n 30 P hc 0 3 6 1051 27 2 3.9 14.0 1246 Co 18, 21 6 5<br />
Cochlear la <strong>of</strong>ficinalis sens.lat Bras N n -0.18 30 b p hc 0 3 6 1245 30 3 3.7 13.9 1287 18 7 i 4<br />
Cochleada pyrenaica Bras N s 30 b p hc 0 1 3 124 0 1.5 12.9 1567 11, 16 7 3<br />
Coeloglossum viride Orch N n -1.34 22 P Gn 0 4 6 964 21 0 3.2 14.1 1148 7 4 2<br />
Coincya monensis Bras N s 0.43 50 b hc 0 8 2 61 3 4.2 14.8 1037 3, 17, 19 4 3<br />
Coincya wrightii Bras NE VU r 90 P Ch hc 0 7 1 1 0 5.8 15.7 986 Co 18 4 3<br />
Colchicum autumnale Li li N n -0. 14 35 p Gn Dtb 7 3 301 1 0 3.6 15.8 809 6 6 4<br />
Colutea arborescens Faba AN 400 p Ph 0 Eur 166 0 3.7 16.3 671 3, 17 4 3<br />
Conium maculatum Apia AR -0.02 250 b hc 0 8 4 1847 47 13 3.9 15.2 915 3 8<br />
Conopodium maj us Apia N n -0.19 40 a Gn 0 7 1 2520 75 7 3.5 14.5 1102 1, 6 5 5<br />
Consolida aj acis Ranu AN 60 a Th 0 Eur 360 7 3.8 16.2 703 3, 4, 17 4 4<br />
Convallaria maj alis Li li N n 0,25 25 P Gn Rhiz2 5 3 439 0 3.3 15.5 831 1, 7 5 5<br />
Convolvulus arvensis Cony N n -0.70 100 P Gn Rhiz2 8 4 1841 43 14 3.8 15.2 929 3, 4 4 6<br />
Conyza canadensis Aste AN 1.12 100 a Th 0 Am 1048 11 10 3.8 16.0 766 3, 4, 17, 19 4 6<br />
Corallorhiza trifida Orch N s 0.61 22 p Gn 0 4 6 c 102 0 0 2.5 13.5 956 1, 2 5 4<br />
Cori<strong>and</strong>rum sativum Apia AN 50 a Th 0 Eur? 201 2 3 3.9 16.0 763 3, 17 4 5<br />
Cornus sanguinea Corn N n -0.06 400 P Ph Root 7 3 1179 52 1 3.7 15.8 810 1, 3 5 6<br />
Cornus sericea Corn AN 300 p Pn Ph 0 Nodal Am 421 111 0 3.5 15.0 936 1, 3, 17 7 6<br />
Cornus suecica Corn N n -0.42 20 p hc Rhiz2 2 3 218 0 0 0.9 11.6 1853 10, 15 6 1 2<br />
Coronopus didymus Bras AN 1.77 18 a Th 0 Unk 1284 315 14 4.1 15.5 921 4, 17 5 6 7<br />
Coronopus squamatus Bras AR 0.33 25 a Th 0 8 3 1290 149 9 4.0 15.7 821 3, 4 5 7 7<br />
Corrigiola litoralis Cary N CR r -0.96 25 a Th 0 8 2 2 0 0 6.2 16.0 1052 Co 19 7 5 5
S<br />
,<br />
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Corylus avellana Beth N n -0.54 600 p Ph w 0 7 3 2470 870 5 3.5 14.6 1094 1, 3 4 5 6 6<br />
Cory nephorus canes cens Poac N r 0.01 32 P hc h 0 8 3 22 0 3 4. 1 16.2 649 Co 19 9 1 3 1<br />
Cotoneaster bullatus Rosa AN 400 p Ph w 0 As l 237 10 0 3.7 15.3 965 1, 3, 16, 17 7 4 7 4<br />
Cotoneaster cambricus Rosa AN EN 150 p Pn vv 0 7 1 Eur 1 0 0 5,4 15.5 796 7, 16 8 3 7 2<br />
Cotoneaster horiz ontalis Rosa AN 100 p Pn w 0 As 1 855 63 2 3.8 15.5 933 3, 16, 17 8 3 8 4<br />
Cotoneaster integrifolius Rosa AN 100 p Pn w 0 As l 537 103 2 3.9 14.7 1194 3, 17 7 3 7 4<br />
Cotoneaster microphyllus<br />
agg. Rosa AN 1.54 100 Pn w 0 Asl 576 135 3 3.9 14.7 1174 3, 16, 17 7 3 7 4<br />
Cotoneaster simonsii Rosa AN 3.55 300 Pn Ph w 0 Asl 973 122 5 3.7 14.9 1086 3, 10, 16, 17 6 5 6 4<br />
Crambe maritima Bras N n 0.29 62 hc h 0 7 3 25 1 46 11 4.8 15.5 938 Co 19 9 5 8 7<br />
Crassula aquatica Cras NA VU 8 a Hz h 0 Nodel 7 6 c 2 0 0 3.2 14.0 1459 14 8 9 5 5<br />
Crassula helmsii Cras AN 10 30 p Hy Ch h Irreg Node2 Aus, NZ 604 8 8 3.8 15.8 826 13, 14 7 10 6 7<br />
Crassula tillaea Cras N $ 0.86 5 a Th h 0 9 2 104 0 11 4.1 16.2 734 3 8 7 4 2<br />
Crataegus laevigata Rosa N n 0.32 1000 Ph w 0 7 3 597 0 1 3.5 16.2 674 1 5 5 7 5<br />
Crataegus m onogyna Rosa N n -0.76 1000 Ph w 0 7 3 2496 946 13 3.6 14.7 1073 1, 3 6 5 7 6<br />
Crepis biennis Aste N n -0.02 120 hc 0 7 3 288 th 0 3.7 16.3 711 3, 6 8 5 7 6<br />
Crepis capillaris Aste N n -0.17 75 a b Th hc 0 7 3 2525 907 14 3.6 14.6 1074 7 7 4 7 4<br />
Crepis foetida Aste AR EN 60 a hc Th 0 8 4 33 0 2 4.0 16.4 707 Co 19 9 4 6 3<br />
Crepis morns Aste N r -1.20 60 hc 0 7 3 c 75 0 0 1.7 13.2 1079 7 8 5 7 5<br />
Crepis paludosa Aste N n -0.27 80 hc 0 5 3 1162 357 0 2.7' 13.4 1334 11, 16 6 7 6 4<br />
Crepis praemorsa Aste N EN 60 hc 0 7 4 c 1 0 0 1.71 13.3 1333 7 8 3 9 3<br />
Crepis vesicaria Aste AN 0.60 80 hc 0 Eur 1227 302 14 4.1 15.7 858 3, 5, 6, 17 8 5 7 7<br />
Crithmurn maritimum Apia N n 0.23 45 hc 0 9 1 301 138 14 5.1 15.4 1042 Co 18 9 6 7 5<br />
Crocosmia aurea x poli sh (C.<br />
x crocosmiiflora) Irid AN 3.11 60 Gn Rhizl ORg Gard 1446 731 12 4.0 14.6 1129 1, 3, 17 7 6 4 4<br />
Cruciata laevipes Rubi N n -0.77 60 hc Rhiz2 7 4 1475 0 1 3.2 15.2 892 6 6 5 7 5<br />
Cryptogramma crispa Adia N n -0.63 15 hc 0 4 3 466 23 1.8 12.9 1678 10, 15, 16 7 5 2 3<br />
Cuscuta epithyrnum Cuse N n -1.28 1 a Th Sto12 8 4 494 27 1 4.3 15.9 846 10 7 6 2 2<br />
Cuscuta europaea Cusc N s 0.04 2 a Th Sto12 7 4 126 0 3.7 16.4 679 14 6 7 6 7<br />
Cymbalaria muralis Scro AN<br />
-0.10 8,<br />
Ch<br />
Node2<br />
Eur 2059 619 1 3.7 15.0 990 3, 16, 17, 19 7 5 7 6<br />
Cynodon dactylon<br />
Poac NA VU r -0.10 30<br />
hc<br />
Rh1z2 Node2 8 5<br />
2 0 6.4 15.6 1156 3, 5, 17 8 4 7 5<br />
Cynoglossum ge rmanicurn Bora N VU r -0.52 75 hc 0 7 3 c 50 0 3.71 16.5 676 1 6 5 8 71<br />
Cynoglossum <strong>of</strong>i cinale Bora N n -1.09 75 hc 0 7 4 718 42 3.9 15.8 780 7, 19 8 4 8 6<br />
Cynosurus cristatus Poac N n 0.02 75 hc 0 7 3 2745 962 1 3.5 14.5 1103 6 7 5 6 4<br />
Cyperus fuscus Cype N VU r -0.32 20 a Th 0 8 4 11 0 4.4 16.6 758 13 9 8 5 4<br />
Cyperus longus Cype N s 2.22 100 he Rhizl 8 3 33 0 1 5.7 16.1 943 11, 13 8 9 7 5<br />
Cypripedium calceolus Orch N CR r 30 Gn Rhizl 5 6 c 22 0 2.2 13.9 1270 7 5 4 8 4<br />
Cystopteris dickie ana Wood N VU r 20 hc 0 ? ? 5 0 0.9 12.3 1379 16 5 7 8 2<br />
Cystopteris fragilis Wood N n -0.69 20 hc 0 3 6 1118 191 2.6 13.5 1361 16 6 7 8 4<br />
Cystopteris montana Wood N r -0.25 15 hc Rhiz2 4 6 22 0 -0.2 11.3 2151 15, 16 5 7 9 2<br />
Cytisus seopar/us Faba N n 0.00 200 Pn w 0 7 3 2288 553 1 3.4 14.6 1085 3 8 5 4 4<br />
Daboe cia cantabrica Eric N o 0.12 50 Ch Pn w 0 8 1 0 33 4.5 14.4 1265 10 8 5 3 2<br />
Dactylis glomerata Poac N n -0.06 120 he h 0 8 4 2707 981 1 3.6 14.5 1091 6 7 5 7 6<br />
Dacty/orhiza fuchsii Orch N n 0.33 50 Gn h 0 7 4 2214 774 3.5 14.7 1063 11 7 8 7 3<br />
Dactylorhiza incarnata Orch N n -0.33 45 Gn h 0 5 4 1189 331 3.6 14.4 1127 11 8 9 6 2<br />
Dactylorhiza lapponica Orch N s 21 Gn h 0 4 3 15 0 3.2 12.5 1910 11 5 8 6 2
F R N S<br />
77 53 23 0 0<br />
6 7 3<br />
8 7 2 0<br />
6 7 2 1<br />
10 5 3 0<br />
Br Habitats<br />
12<br />
11<br />
11<br />
11<br />
11<br />
13<br />
7, 8<br />
1<br />
1<br />
17<br />
6, 7<br />
17<br />
1, 6<br />
8, 10<br />
12, 13<br />
4<br />
3, 16<br />
7<br />
16<br />
15<br />
8, 9<br />
3, 4, 17<br />
3, 4, 17<br />
15<br />
10<br />
3, 4, 16, 17<br />
3, 16, 17<br />
3, 6, 17<br />
3, 6, 17<br />
1, 3, 16<br />
3, 18, 19<br />
1, 3<br />
16<br />
7, 16<br />
3, 16<br />
15, 16<br />
11, 12<br />
12, 14<br />
12<br />
7, 16<br />
1, 16<br />
1, 16<br />
1<br />
11 .<br />
1, 2<br />
1, 15, 16<br />
El E2 C Origin GB IR CI Tjan Tjul Prec Co<br />
1221<br />
1237<br />
849<br />
1244<br />
978<br />
707<br />
1160<br />
760<br />
890<br />
796<br />
989<br />
913<br />
1099<br />
1177<br />
1211<br />
738<br />
805<br />
797<br />
979<br />
2845<br />
1120<br />
777<br />
783<br />
1686<br />
1465<br />
810<br />
790<br />
863<br />
863<br />
729<br />
898 Co<br />
921<br />
1191<br />
1584<br />
1151<br />
2311<br />
1422<br />
1337<br />
1269<br />
1734<br />
1373<br />
1160<br />
1075<br />
659<br />
1114<br />
1772<br />
W Clonel Clone2<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
w 0<br />
w 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0 DRi<br />
h Ogr<br />
h 0<br />
h 0<br />
LF2<br />
65 74 2 5 0<br />
5 7 6 0<br />
4 7 8 0<br />
4 71 3 1<br />
65 75 8 4<br />
5 2 3<br />
9 2 1<br />
4 7i 6<br />
5 3 5 3 2<br />
2 7 1<br />
3 4 1<br />
6 4 5<br />
4 5 5<br />
4 5 5<br />
5 2 2<br />
4 1 2<br />
4 71 6<br />
h 0<br />
0<br />
0<br />
sw<br />
sw<br />
w 0<br />
h 0<br />
h 0<br />
h 0<br />
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1<br />
40 p Gn<br />
30 p Gn<br />
50 p Gn<br />
25 p Gn<br />
30 p Gn<br />
30 a Hz<br />
40 p hc<br />
100 p Pn<br />
100 p Pn<br />
100 a Th<br />
100 b hc<br />
120 b hc<br />
150 p hc<br />
60 p hc<br />
70 p hc<br />
100 a Th<br />
60 a Th<br />
37 p Ch<br />
20 p Ch<br />
6 p Ch<br />
150 b hc<br />
35 a Th<br />
50 a Th<br />
10 p Ch<br />
8 p Ch<br />
60 a Th<br />
80 p Ch<br />
200 b hc<br />
200 b hc<br />
150 b hc<br />
9 p Ch<br />
80 p hc<br />
10 p Ch<br />
35 b hc<br />
50 a Th<br />
5<br />
Ch<br />
13<br />
hc<br />
5<br />
hc<br />
5<br />
hc<br />
10<br />
Ch<br />
60<br />
hc<br />
80<br />
he<br />
80<br />
hc<br />
60<br />
hc<br />
150<br />
hc<br />
80<br />
hc<br />
f.a<br />
c)<br />
57 77 76<br />
sw Rhiz2<br />
sw Rhiz2<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
hc<br />
76 78 7 7<br />
3 4 5<br />
5 6 5<br />
4 9 3<br />
5 7 2<br />
6 7 6<br />
5 71 3<br />
99 22 1 1<br />
9 2 1<br />
4 7 2<br />
6 2 3<br />
6 5 5<br />
8 5 4<br />
9 4 4<br />
6 4 5<br />
6 3 2<br />
h 0<br />
sw Node2<br />
Rhizl<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
w Node2<br />
0<br />
0<br />
0 Rhizl<br />
0<br />
0<br />
0
N<br />
IR<br />
Origin<br />
LF2<br />
1 P2<br />
Chg<br />
RS<br />
n<br />
n<br />
n<br />
x<br />
s<br />
CS<br />
5<br />
5<br />
2<br />
4<br />
3<br />
8<br />
5<br />
4<br />
4<br />
5<br />
5<br />
5<br />
1<br />
4<br />
5<br />
2<br />
4<br />
2<br />
R<br />
6 5<br />
6 5<br />
5 2<br />
6 4<br />
5 9,<br />
5 7<br />
3 5<br />
4 7<br />
5<br />
5<br />
7<br />
9 5<br />
NS<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
AR<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
AN<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
AN<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
NE<br />
N<br />
N<br />
Fam<br />
Dry o<br />
Taxon name<br />
Dryopteris filix-mas<br />
0.03<br />
0.24<br />
NHem<br />
LF1<br />
hc<br />
hc<br />
he<br />
hc<br />
he<br />
Th<br />
hc<br />
hc<br />
Hz<br />
Hz<br />
Hy<br />
hc<br />
hc<br />
Hy<br />
hc<br />
hc<br />
hc<br />
Hy<br />
Hy<br />
Hy<br />
he<br />
he<br />
he<br />
hc<br />
Ch<br />
hc<br />
he<br />
he<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
he<br />
hc<br />
hc<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Hght Len<br />
120<br />
120<br />
50<br />
80<br />
60<br />
120<br />
67<br />
90<br />
5 10<br />
5 10<br />
10<br />
60<br />
35<br />
60<br />
8<br />
30<br />
60<br />
45<br />
300<br />
300<br />
110<br />
105<br />
55<br />
125<br />
30<br />
20<br />
10<br />
4<br />
75<br />
150<br />
60<br />
75<br />
75<br />
60<br />
75<br />
75<br />
75<br />
30<br />
80<br />
60<br />
45<br />
42<br />
65<br />
60<br />
22<br />
90<br />
0.10<br />
0.75<br />
0.36<br />
-0.24<br />
1.07<br />
0.66<br />
-0.11<br />
,<br />
n<br />
n<br />
s<br />
n<br />
r<br />
n<br />
n<br />
r<br />
n<br />
n<br />
n<br />
F<br />
EN<br />
Hy<br />
p<br />
he<br />
9 4<br />
6<br />
9 71<br />
9 7<br />
9 7<br />
4<br />
L F<br />
5<br />
5<br />
7<br />
6<br />
8<br />
6<br />
9<br />
8<br />
7 10<br />
71 10<br />
7 10<br />
8<br />
8<br />
8 10<br />
6<br />
9<br />
8<br />
8 11<br />
W Clonel Clone2 El E2 C<br />
0 7 6<br />
0 5 6<br />
0 4 2<br />
0 4 3<br />
0 9 3<br />
0<br />
0 9 1<br />
0 7 4<br />
0 Nodel 7 3<br />
0 Nodel 5 4 c<br />
Rhiz2 5 6<br />
Rhiz2 4 3<br />
0 7 2<br />
Rhiz2 6 5<br />
Rhiz2 7 3<br />
Rhizl 5 3<br />
Rhiz2 7 6<br />
Irreg 8 1<br />
Irreg<br />
Irreg<br />
0 5 4<br />
Rhiz2 8 3<br />
Rhiz2 8 3<br />
Rhiz2 6 4<br />
w Node2 2 6<br />
Rhizl 1 3<br />
Stoll 1 6<br />
Node2<br />
0<br />
Rhiz2 8 5<br />
0 9 2<br />
0 7 3<br />
0 7 3<br />
Rhizl 5 6<br />
0 7 3<br />
0 7 4<br />
0 7 4<br />
0 5 4<br />
0 7 5<br />
hc<br />
0.47<br />
0.91<br />
0.00<br />
0.02<br />
0.60<br />
0.37<br />
0.37<br />
VU<br />
67<br />
8<br />
6<br />
6<br />
7<br />
1<br />
4<br />
3<br />
3<br />
6<br />
71<br />
5<br />
6<br />
5<br />
3<br />
5<br />
7<br />
5<br />
1<br />
4<br />
4<br />
3<br />
4<br />
4<br />
3<br />
4<br />
6<br />
771<br />
7<br />
7<br />
7<br />
7<br />
2<br />
6<br />
6<br />
4<br />
6<br />
71<br />
6<br />
6<br />
5<br />
5<br />
71<br />
7<br />
5<br />
8<br />
7<br />
9<br />
7<br />
7<br />
8<br />
5<br />
7i<br />
6<br />
7 6 11<br />
7<br />
9<br />
9<br />
7<br />
7<br />
8<br />
8<br />
7<br />
7<br />
71<br />
7<br />
6<br />
6<br />
7<br />
71<br />
6<br />
6<br />
7<br />
4<br />
3<br />
8<br />
3<br />
2<br />
3<br />
2<br />
7<br />
Co Br Habitats<br />
1, 2<br />
1, 2<br />
15, 16<br />
1, 2<br />
16<br />
17<br />
4<br />
7<br />
13<br />
13<br />
13, 14<br />
13, 14<br />
11, 12, 13<br />
11<br />
Co 21<br />
11<br />
11<br />
11<br />
13, 14<br />
13, 14<br />
1, 3<br />
Co 19, 21<br />
Co 19<br />
3, 4, 19<br />
10, 12, 15<br />
11, 16<br />
11, 15<br />
14, 15, 16<br />
3, 4, 17<br />
11, 14<br />
3, 16, 17<br />
3, 16, 17<br />
11, 14<br />
11, 14<br />
11<br />
1, 3, 14, 17<br />
3, 17<br />
16<br />
1, 7<br />
1<br />
11<br />
1<br />
1<br />
1<br />
1<br />
3, 4<br />
Prec<br />
1096<br />
1096<br />
1810<br />
1998<br />
1527<br />
785<br />
848<br />
822<br />
1365<br />
1072<br />
924<br />
1348<br />
1348<br />
1098<br />
1130<br />
1323<br />
1182<br />
1259<br />
936<br />
836<br />
981<br />
863<br />
1050<br />
1046<br />
1381<br />
1832<br />
1880<br />
1357<br />
972<br />
971<br />
937<br />
1091<br />
1104<br />
1146<br />
996<br />
893<br />
834<br />
1328<br />
946<br />
808<br />
915<br />
774<br />
728<br />
820<br />
721<br />
1087<br />
Tjul<br />
14.5<br />
14.5<br />
12.6<br />
13.4<br />
13.7<br />
16.0<br />
15.9<br />
15.6<br />
14.2<br />
14.71<br />
15.2<br />
13.2<br />
14.0<br />
14.5<br />
15.3<br />
13.5<br />
14.4<br />
14.2<br />
15.1<br />
15.8<br />
14.9<br />
15.9<br />
14.5<br />
14.6<br />
13.2<br />
11.9<br />
11.6<br />
13.6<br />
15.0<br />
15.0<br />
16.0<br />
14.5<br />
14.5<br />
14.3<br />
14.9<br />
15.5<br />
15.9<br />
13.8<br />
15.3<br />
15.7<br />
15.3<br />
16.0<br />
16.3<br />
14.3<br />
16.1<br />
14.5<br />
CI Tjan<br />
13 3.5<br />
13 3.5<br />
0 1.9<br />
0 2.7<br />
0 2.1<br />
10 4.0<br />
7 4.7<br />
9 3.8<br />
3 3.7<br />
0 3.6<br />
1 3.6<br />
0 1.4<br />
7 3.7<br />
10 3.5<br />
0 4.6<br />
4 3.1<br />
2 4.0<br />
3 3.7<br />
3 3.6<br />
3 3.7<br />
0 3.3<br />
8 4.6<br />
9 4.4<br />
13 3.6<br />
0 2.7<br />
0 1.0<br />
0 0.9<br />
2 3.0<br />
9 3.7<br />
12 3.8<br />
12 4.4<br />
10 3.5<br />
8 3.5<br />
3 3.4<br />
11 3.8<br />
0 3.6<br />
7 3.9<br />
0 3.0<br />
0 3.6<br />
0 3.6<br />
3 3.9<br />
0 3.8<br />
0 3.6<br />
0 2.8<br />
0 3.6<br />
12 3.5<br />
928<br />
928<br />
5<br />
1<br />
0<br />
4<br />
0<br />
41<br />
79<br />
19<br />
89<br />
0<br />
330<br />
756<br />
5<br />
267<br />
95<br />
286<br />
424<br />
15<br />
122<br />
41<br />
180<br />
837<br />
236<br />
1<br />
0<br />
423<br />
400<br />
795<br />
0<br />
894<br />
758<br />
812<br />
824<br />
24<br />
0<br />
13<br />
161<br />
0<br />
160<br />
9<br />
0<br />
0<br />
0<br />
921<br />
GB<br />
2650<br />
2650<br />
308<br />
1<br />
33<br />
370<br />
79<br />
1066<br />
212<br />
33<br />
366<br />
14<br />
962<br />
2577<br />
15<br />
1236<br />
574<br />
889<br />
1696<br />
808<br />
1669<br />
370<br />
572<br />
2530<br />
1359<br />
218<br />
236<br />
1226<br />
2005<br />
2036<br />
371<br />
2630<br />
2347<br />
2417<br />
2070<br />
937<br />
1171<br />
60<br />
1218<br />
86<br />
447<br />
134<br />
235<br />
10<br />
8<br />
2666<br />
Am<br />
Am<br />
0.27<br />
0.32<br />
-0.28<br />
-0.01<br />
-0.29<br />
-0.41<br />
-0.76<br />
1.42<br />
3.88<br />
0.12<br />
0.07<br />
-0.39<br />
0.38<br />
-0.18<br />
-0.41<br />
-0.25<br />
1.66<br />
0.16<br />
0.08<br />
0.26<br />
-0.39<br />
0.19<br />
-0.08<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
NZ<br />
Am<br />
Ch<br />
0Rhiz2 7 7 43<br />
0 7 3<br />
0 7 3<br />
0 7 1<br />
Rhiz2 4 5<br />
Rhiz2 3 6<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
s<br />
n<br />
s<br />
n<br />
s<br />
n<br />
r<br />
x<br />
n<br />
EN<br />
CR<br />
0.39
F R N S<br />
10 6 4<br />
78 76 6 3<br />
7 5 4<br />
4 8 5<br />
8 5 5<br />
8 7 6<br />
8 8 3<br />
5, 7 6<br />
1 P2 LF1 LF2 W<br />
Gn Hy<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Chg<br />
0.42<br />
0.30<br />
0.18<br />
0.11<br />
RS<br />
n<br />
n<br />
n<br />
s<br />
-0.35<br />
0.41<br />
-0. 12<br />
1.59<br />
-0.11<br />
-0.94<br />
n<br />
n<br />
s<br />
Gn<br />
7 1 1<br />
56 22 2 2<br />
8 2 1<br />
8 2 1<br />
6 4 1<br />
5 7 3<br />
5 7 2<br />
3 7 2<br />
3 8 2<br />
11 4 1<br />
CI<br />
8<br />
0<br />
8<br />
0<br />
0<br />
0<br />
3<br />
0<br />
0<br />
0<br />
13<br />
0<br />
0<br />
2<br />
0<br />
5<br />
0<br />
11<br />
1<br />
E2 C Origin<br />
6<br />
6<br />
6<br />
6<br />
5 Eur, As<br />
6<br />
3<br />
6<br />
Eur<br />
1<br />
1<br />
1<br />
0<br />
2<br />
1<br />
6<br />
4<br />
SAm<br />
Eur<br />
0<br />
6<br />
6 c<br />
3<br />
6<br />
4<br />
4<br />
2<br />
2<br />
1<br />
Ch Pn<br />
Ch Pn<br />
Pn<br />
Ch Pn<br />
Ch Pn<br />
Pn<br />
b Th hc<br />
Ch<br />
Ch<br />
Ch<br />
Hy<br />
hc<br />
hc<br />
hc<br />
hc<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
hc<br />
hc<br />
Th<br />
Ch Pn sw<br />
Ph<br />
hc<br />
Ch<br />
hc<br />
Fight Len<br />
100<br />
100<br />
60<br />
60<br />
120<br />
90<br />
180<br />
60<br />
15<br />
60<br />
60<br />
120<br />
60<br />
60<br />
80<br />
50<br />
20<br />
25<br />
20<br />
20<br />
60<br />
60<br />
60<br />
50<br />
40<br />
40<br />
15<br />
20<br />
40<br />
9<br />
9<br />
10<br />
10<br />
60<br />
75<br />
60<br />
90<br />
60<br />
600<br />
150<br />
70<br />
40<br />
r<br />
n<br />
o<br />
o<br />
n<br />
r<br />
n<br />
r<br />
-0.91<br />
-0.07<br />
0.33<br />
-0. 11<br />
2.37<br />
1.52<br />
0.18<br />
-0.79<br />
-0.20<br />
0.36<br />
-0.36<br />
99 44 21<br />
9 7 2<br />
8 2 1<br />
4 6 4<br />
4 6 4<br />
4 7 2<br />
4 6 6<br />
4 6 5<br />
3 7 3<br />
3 7 3<br />
3 6 3<br />
3 7 3<br />
4 7 7<br />
3 6 3<br />
4 6 5<br />
5 7 7<br />
4 8 5<br />
5 8 5<br />
8 6 7<br />
5 6 6<br />
3 7 3<br />
4 8 5<br />
Br Habitats L<br />
11<br />
1, 11, 14<br />
11<br />
11<br />
6<br />
1, 16<br />
11<br />
11<br />
1, 3, 17<br />
10, 12<br />
10<br />
10, 13, 14<br />
10, 12<br />
10, 12<br />
10<br />
3, 16<br />
15, 16<br />
3, 16, / 7<br />
3, 16<br />
13<br />
12<br />
11<br />
11<br />
12<br />
19<br />
19<br />
19<br />
18, 19<br />
3, 4<br />
3, 16, 17<br />
3, 16, 17<br />
3, 16, 17<br />
3, 16, 17<br />
3, 16<br />
3, 5<br />
19<br />
3, 4<br />
3, 16, 17<br />
1, 3<br />
11<br />
1<br />
3, 4, 7, 19<br />
Prec Co<br />
1116<br />
1108<br />
1091<br />
1406<br />
740<br />
1269<br />
950<br />
1224<br />
716<br />
1011<br />
1226<br />
1395<br />
1593<br />
1230<br />
1047<br />
774<br />
1653<br />
904<br />
1121<br />
1435<br />
1194<br />
1006<br />
1394<br />
1307<br />
902<br />
902<br />
959 Co<br />
996 Co<br />
880<br />
997<br />
844<br />
918<br />
1011<br />
809<br />
856<br />
1010 Co<br />
804<br />
848<br />
904<br />
974<br />
827<br />
838<br />
Tjul<br />
14.4<br />
14.0<br />
14.5<br />
12.7<br />
16.3<br />
13.7<br />
15.2<br />
14.0<br />
15.6<br />
15.9<br />
14.0<br />
14.0<br />
13.7<br />
14.0<br />
15,5<br />
15.9<br />
10.6<br />
15.9<br />
14.5<br />
14.1<br />
14.1<br />
15.4<br />
13.6<br />
13.6<br />
15.2<br />
15.2<br />
15.5<br />
15.6<br />
15.8<br />
14.9<br />
15.5<br />
15.2<br />
14.7<br />
15.9<br />
16.1<br />
152<br />
15.7<br />
15.6<br />
15.4<br />
15.2<br />
16. 1<br />
15.6<br />
Tjan<br />
3.5<br />
3.0<br />
3.4<br />
1.8<br />
4.1<br />
2.9<br />
3.8<br />
3.4<br />
3.4<br />
5.7<br />
3.5<br />
4.3<br />
4.0<br />
3.4<br />
6.0<br />
3.8<br />
-1.2<br />
4.6<br />
3.3<br />
4.4<br />
3.4<br />
4.5<br />
2.7<br />
3.1<br />
3.8<br />
3.8<br />
5.0<br />
5.3<br />
4.6<br />
3.5<br />
3.7<br />
3.6<br />
3,4<br />
IR<br />
847<br />
112<br />
704<br />
35<br />
0<br />
334<br />
426<br />
129<br />
0<br />
0<br />
712<br />
24<br />
10<br />
781<br />
1<br />
80<br />
0<br />
34<br />
55<br />
70<br />
831<br />
14<br />
100<br />
560<br />
167<br />
167<br />
13<br />
33<br />
80<br />
40<br />
11<br />
177<br />
423<br />
25<br />
1<br />
106<br />
80<br />
97<br />
483<br />
410<br />
0<br />
2<br />
GB<br />
2494<br />
238<br />
2534<br />
170<br />
2<br />
1561<br />
1248<br />
170<br />
614<br />
19<br />
1999<br />
0<br />
0<br />
1962<br />
6<br />
974<br />
10<br />
292<br />
341<br />
8<br />
2134<br />
17<br />
575<br />
1516<br />
1666<br />
1666<br />
74<br />
195<br />
338<br />
359<br />
123<br />
1074<br />
2180<br />
141<br />
46<br />
291<br />
929<br />
907<br />
1254<br />
1715<br />
704<br />
369<br />
Clonel Clone2 El<br />
Rhiz2 5<br />
Rhiz2 5<br />
Rhiz2 5<br />
Rhiz2 4<br />
Rhiz2 8<br />
Rhiz2 5<br />
Rhiz2 8<br />
Rhiz2 2<br />
0<br />
w 0 8<br />
w 7<br />
w 8<br />
w 0 7<br />
w Nodel 7<br />
w O 8<br />
0 5<br />
0 1<br />
0<br />
0<br />
Rhizl DRa<br />
Rhiz2<br />
Rhiz2<br />
Rhiz2<br />
Ogr<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
r<br />
n<br />
r<br />
n<br />
n<br />
n<br />
n<br />
s<br />
n<br />
n<br />
s<br />
n<br />
n<br />
NS CS<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
N<br />
N<br />
N<br />
AN<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N VU<br />
AN<br />
AN<br />
N<br />
N<br />
N VU<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AR<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
AR VU<br />
N<br />
AR<br />
AR<br />
N<br />
N<br />
N<br />
AN<br />
Taxon name Fam<br />
Equi<br />
Equi<br />
Equi<br />
Equi<br />
Equi<br />
Equi<br />
Equi<br />
Equi<br />
Ranu<br />
Eric<br />
Eric<br />
Eric<br />
Eric<br />
Eric<br />
Eric<br />
Aste<br />
Aste<br />
Aste<br />
Orob<br />
Eno<br />
Cype<br />
Cype<br />
Cype<br />
Cype<br />
Gera<br />
Gem<br />
Gem<br />
Gera<br />
Gem<br />
Bras<br />
Bras<br />
Bras<br />
Bras<br />
Bras<br />
Apia<br />
Apia<br />
Bras<br />
Bras<br />
Cela<br />
Aste<br />
Euph<br />
Euph<br />
1<br />
1<br />
-0.11<br />
1<br />
1<br />
0.38<br />
0.47<br />
11<br />
8 4<br />
0 3,9<br />
2 4.6<br />
4.7<br />
2 3.7<br />
8 4.0<br />
0 3.9<br />
3.9<br />
9 4.1<br />
2 3.6<br />
Eur<br />
11<br />
8 3<br />
8 3<br />
0.52<br />
-0.02<br />
-0.41<br />
-0.80<br />
-0.65<br />
1.05<br />
0.15<br />
-0.15<br />
-0.22<br />
0.98<br />
n<br />
Unk<br />
Gard<br />
7 3<br />
7 3<br />
7 3<br />
7 3 c Eur<br />
11<br />
w Root<br />
h Rhizl<br />
h 0<br />
h Root<br />
n<br />
n<br />
n<br />
4 71 5<br />
3<br />
4<br />
4, 17<br />
715<br />
783<br />
973<br />
16.1<br />
15.8<br />
14.9<br />
1 3.7<br />
3 3.9<br />
12 3.8<br />
0<br />
125<br />
642<br />
169<br />
1039<br />
2114<br />
Eur<br />
5 6 6<br />
8 3<br />
8 5<br />
h Root<br />
h 0<br />
h 0<br />
hc<br />
Th<br />
Th<br />
80<br />
20<br />
40<br />
-1.18<br />
-0.77<br />
AN<br />
AR<br />
AR<br />
Euph<br />
Euph<br />
Euph
F R N S<br />
5 57 45 0<br />
7 5 3<br />
7 5 3<br />
0<br />
0<br />
3<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
1<br />
0<br />
3<br />
,<br />
Taxon name Fam NS CS RS Chg_ Hght Len P1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L<br />
Euphorbra hyberna Euph N VU r 52 p hc 0 8 2<br />
2 137 0 5.2 14.9 1203 1, 3 5<br />
Euphorbia lathyris Euph AR 2.16 120 b Ch 0 8 3<br />
956 21 13 3.8 15.8 804 3, 16, 17 6<br />
Euphorbia paralias Euph N n -0.35 52 Ch 0 9 1<br />
182 65 8 5./ 15.6 987 Co 19 9<br />
Euphorbia peplis Euph N EW x -1.49 5 Th 0 9 1<br />
26 1 8 5.8 16. 1 969 Co 19 9<br />
Euphorbia peplus Euph AR -0.17 30 Th 0 8 3<br />
1911 52 14 3.8 15.1 950 4, 17 7<br />
Euphorbia platyphyllos Euph AR -0.24 70 Th 0 8 3<br />
248 0 3.9 16.3 733 4 7<br />
Euphorbia portl<strong>and</strong>ica Euph N n -0.09 35 Ch 0 8 /<br />
148 8 14 5.3 15.4 1060 Co 18, 19 8<br />
Euphorbia serrulata Euph NA VU r 1.20 65 Th 0 8 3<br />
13 0 4. 1 16.3 812 1, 3 5<br />
Euphrasia anglica Scro NE n 20 Th 0 7 1<br />
375 5 0 4. 1 15.3 1081 10, 16 71<br />
Euphrasia arctica Scro N n 30 Th 0 5 1<br />
1095 47 0 3.2 13.6 1315 6, 11 7<br />
Euphrasia cambrica Scro NE VU r 8 Th 0 1 1<br />
5 0 2.8 13.2 2458 15 8<br />
Euphrasia campbelliae Scro NE r 10 Th 0 4 1<br />
11 0 4.0 12.5 1638 10, 11 8<br />
Euphrasia confusa Scro N n 20 Th 0 5 1<br />
970 3 3 3.2 13.8 1267 7, 8, 16 8<br />
Euphrasia foulaensis Scro N s 6 Th 0 4 1<br />
143 0 3.6 12.4 1263 Co 18, 21 8<br />
Euphrasia frigida Scro N s 20 Th 0 1 4<br />
118 0 1.5 11.8 1981 15, 16 81<br />
Euphrasia heslop-hanisonii Scro NE r 15 Th 0 4 1<br />
20 0 3.7 12.6 1695 Co 21 8<br />
Euphrasia marshallii Scro NE r 12 Th 0 4 1<br />
39 0 3.8 12.3 1334 Co 18 8<br />
Euphrasia micrantha Scro N n 25 Th 0 7 3<br />
941 19 0 3.0 13.2 1400 8, 10 7<br />
Euphrasia nemorosa Scro N n 35 Th 0 7 3<br />
1498 20 71 3.6 14.8 1037 7, 10<br />
Euphrasia <strong>of</strong>i cinalis agg. Scro N n -1.61 30 Th 0 6 3<br />
2600 87 12 3.5 14.4 1131 6, 7, 8, 10 8<br />
Euphrasia ostenfeldii Scro N r 12 Th 0 2 1<br />
85 1 2.8 12.2 1694 16 9<br />
Euphrasia pseudokerneri Scro NE s 20 Th 0 7 1<br />
167 0 3.7 16.1 753 7 7'<br />
Euphrasia rivularis Scro NE r 15 Th 0 4 1<br />
14 0 2.3 13.2 2450 15, 16 7<br />
Euphrasia rostko viana Scro N n 35 Th 0 5 3<br />
29 1 12 1 3.7 14.3 1336 6 71<br />
Euphrasia rotundifolia Scro NE EN r 10 Th 0 4 1<br />
4<br />
3.5 12.4 1004 Co 18 8<br />
Euphrasia salisburgensis Scro N o 12 Th 0 2 3<br />
0 3 4.6 14.7 1134 16 7<br />
Euphrasia scottica Scro N n 25 Th 0 4 3<br />
601 7 2.5 12.8 1575 10, 15 8<br />
Euphrasia tetraquetra Scro N n 15 Th 0 7 1<br />
313 10 1 4.7 14.9 1105 6, 10 8<br />
Euphrasia vigursii Scro NE VU r 20 Th 0 7 1<br />
33<br />
5.4 15.3 1263 10<br />
Exact, /um pusillum Gent N o 8 Th 0 8 2<br />
0<br />
6.8 16.7 712 19 9<br />
Fagopyrum esculentum Poly AN -0.53 60<br />
Th 0<br />
Asl ? 501<br />
3.8 15.8 788 4 8<br />
Fagus sylvatica Faga N n -0.62 3000<br />
Ph sAf<br />
7 3 2397 79 3.5 14.7 1061 1 3<br />
Fallopia convolvulus Poly AR -1.31 100<br />
Th 0<br />
6 4 2139 51 3.7 14.9 971 3, 4 7<br />
Fallopia dumetorum Poly N s -0.33 200<br />
Th 0<br />
7 5 69<br />
3.9 16.4 784 1, 3 6<br />
Fallopia j aponica Poly AN 1.83 200<br />
Gn Rhiz2<br />
As2 2060 68 1 3.7 14.8 1043 3, 14, 17 6<br />
Fallopia sachalinensis Poly AN 1.05 300<br />
Gn Rhiz2<br />
As2 507 6 3.7 15.3 976 3 6<br />
Festuca altissima Poac N n 0.83 120<br />
hc 0<br />
7 3 241 8 2.6 13.6 1410 1, 16 3<br />
Festuca arenaria Poac N S 75<br />
hc Rhiz2<br />
7 1 108<br />
4.2 15.4 828 19 8<br />
Festuca armoricana Poac N o 40<br />
hc 0<br />
7 1 0<br />
6.2 16.9 796 19 8<br />
Festuca arundinacea Poac N n 1.71 120<br />
hc 0<br />
8 4 2082 55 7 3.6 14.9 980 6, 7 8<br />
Festuca filiformis Poac N n 35<br />
hc Ogr<br />
7 2 821 6 4 3.0 14.3 1100 8 8<br />
Festuca gigantea Poac N n 0.46 125<br />
hc 0<br />
7 3 1885 35 0 3.6 15.1 981 1 5<br />
Festuca huonii Poac N a 25<br />
hc 0<br />
7 0 0 7 6.4 16.5 780 16, 18 8<br />
Festuca lemanii Poac NA r 66<br />
hc 0<br />
7 1 71 1 3.4 15.3 1079 7, 8, / 6 8<br />
Festuca longifolia Poac N VU r 40<br />
hc 0<br />
7 1 15 6 4.8 16.2 751 8 8<br />
Festuca ovina Poac N n 43<br />
hc Ogr<br />
5 5 1788 5 4 3.5 14.5 1109 7, 8 7<br />
3<br />
0
NS CS RS Chg_ Hght Len P1 P2 LFI LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
n -0.15 45 p hc h Ogr 3 6 2718 726 13 3.5 14.4 1118 7, 8 7 5 4 2 0<br />
n -0. 16 80 p hc h O 5 4 1976 569 4 3.6 14.9 985 6 7 6 6 6 0<br />
Taxon name Fam<br />
Festuca ovina agg. Poac<br />
Festuca pratensis Poac<br />
Festuca pratensis x Lolium<br />
perenne (x Festulolium<br />
6 71 6<br />
5 6 5<br />
62 35 2 2<br />
3 4 2<br />
3 4 2<br />
4 7 3<br />
a<br />
a<br />
a<br />
a<br />
a<br />
48 6 4 5<br />
4 8 2<br />
5 8 5<br />
5 6 4<br />
5 6 7<br />
8 5 5<br />
8 8 5<br />
6 7 6<br />
8 7 4<br />
6 5 5<br />
4 6 6<br />
4 6 71<br />
790 80 3.5 15.5 851 6<br />
iz2 3 6 2799 974 1 3.5 14.5 1104 3, 5, 6, 2/<br />
iz2 3 6 2799 974 1 3.5 14.5 1104 6<br />
gr DRi 2 6 801 182 2.7 12.7 1592 15, 16<br />
Eur 21 0 3.8 16.4 647 3, 4<br />
7 3 85 0 3.71 16.4 660 3, 4<br />
7 3 788 105 1 3.6 15.1 904 16<br />
9 2 132 0 3.8 16.3 687 4<br />
8 3 980 78 3.8 15.5 832 3<br />
iz2 5 5 2692 967 3.5 14.5 1105 11<br />
izl DRg 7 4 578 8 3.6 15.8 776 7<br />
0 3 Eur 961 60 1 4.1 15.9 823 3, 16, 17<br />
oI2 7 4 2380 819 3.5 14.6 1091 1, 7<br />
ol2 Gard 740 20 3.7 15.5 863 3, 17<br />
7 4 712 56 3.8 15.8 881 1<br />
8 2 58 0 4.4 16.5 680 Co 19, 21<br />
7 3 2459 930 1 3.6 14.7 1069 1<br />
7 3 98 0 3.6 16.3 688 6<br />
SAm 367 542 4.3 14.3 1223 3, 17<br />
9 1 423 330 1 4.5 14.8 1086 4<br />
9 2 482 180 11 4.2 14.9 997 3, 16<br />
8 3 307 16 0 3.6 15.5 763 4<br />
8 1 1200 368 13 4.0 14.9 1004 4<br />
7 1 31 0 0 6.5 15.8 1073 3, 4<br />
8 3 1978 304 12 3.6 15.0 912 3, 4<br />
8 3 128 0 0 3.6 16.1 703 4<br />
7 1 191 37 2 4.1 14.8 978 3, 4<br />
8 1 Eur 13 0 1 5.4 16. 1 958 ' 3, 4, 17<br />
7 4 116 0 0 3.5 16.2 702 4<br />
b DRa 8 3 c 1 0 0 2.9 14.7 1008 16<br />
Otb DRg 7 3 c 212 0 0 3.0 15.1 861 1, 3, 14, 16<br />
Otb DRg 8 3 Eur 1763 36 5 3.5 15.2 919 1, 3, 17<br />
0 7 3 c Eur 352 0 1 3.7 16.2 725 3, 17<br />
0 7 3 616 43 0 3.8 15.8 791 4, 16<br />
0 5 5 1135 138 1 3.6 14.9 1011 4<br />
0 7 2 32 01 0 3.7 15.6 789 4<br />
0 5 4 999 84 0 3.1 14.5 1043 4<br />
0 5 3 1725 409 1 3.6 14.8 1025 3<br />
0 5 5 2508 623 4 3.5 14.5 1073 3<br />
0 SAm 429 2 9 3.8 16. 1 721 4, 17<br />
0 SAm 524 5 6 3.8 16.0 778 3, 4, 17<br />
0 7 3 2672 960 14 3.6 14.6 1080 3, 4, 17<br />
hc<br />
hc<br />
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Th<br />
Th<br />
Th<br />
hc<br />
hc Gn<br />
hc<br />
hc<br />
hc<br />
Ph<br />
Ch<br />
Ph<br />
Gb<br />
Pn<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Gb<br />
Gb<br />
Gb<br />
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loliaceum) Poac NH n 65<br />
Festuca rubra Poac N n 72<br />
Festuca rubra agg. Poac N n 2.96 72<br />
Festuca vivipara Poac N n 0.13 44<br />
Filago gallica Aste AR CR 0.01 20<br />
Filago lutescens Aste NA VU s -0.34 25<br />
Filago minima . Aste N n -0.91 20<br />
Filago pyramidata Aste AR EN -1.14 30<br />
Filago vulgaris Aste N n -1.20 35<br />
Filipendula ulmaria Rosa N n -0.10 120<br />
Filipendula vulgaris Rosa N n -0.07 50<br />
Foeniculum vulgate Apia AR 1.17 250<br />
Fragaria vesca Rosa N n -1.09 30<br />
Fragaria x ananassa Rosa AN 0.42 40<br />
Frangula alnus Rham N n -0.16 500<br />
Frankenia laevis Fran N s 0.03 8<br />
Fraxinus excelsior Olea N n -0.73 2500<br />
Fritillaria meleagris Lili NA s 0.86 30<br />
Fuchsia magellanica Onag AN 1.85 150<br />
Fumaria bastardii Fuma N n 0.39 75<br />
Fumaria capreolata Fuma N n 0.31 100<br />
Fumaria densillora Fuma AR -0.37 52<br />
Fumaria muralis Fuma N n 1.75 100<br />
Fumaria occidentalis Fuma NE s 0.04 100<br />
Fumaria <strong>of</strong>i cinalis Fuma AR -0.34 52<br />
Fumaria parvillora Fuma AR -0.55 471<br />
Fumaria purpurea Fuma N s 0.25 60<br />
Fumaria reuteri Fuma AN -0.62 100<br />
Fumaria vaillantii Fuma AR -0.51 42<br />
Gagea bohemica Lili N VU r 9<br />
Gagea lutea Lili N n 0.16 25<br />
Galanthus nivalis Lili AN 3.01 22<br />
Galega dfi cinalis Faba AN 150<br />
Galeopsis angustifi lia Lami AR -3.31 50<br />
Galeopsis bifida Lami N n 100<br />
Galeopsis segetum Lami AR EX 50<br />
Galeopsis speciosa Lami AR -1.82 100<br />
Galeopsis tetrahit Lami N n 100<br />
Galeopsis tetrahit agg. Lami N n -0.61 100<br />
Galinsoga parVillora Aste AN 0.63 80<br />
Galinsoga quadriradiata Aste AN 1.071 80<br />
Garium aparine Rubi N n -0.09 150<br />
La)<br />
35 86 65<br />
4 6 5<br />
5 7 6<br />
4 8 5<br />
4 6 5<br />
4 6 5<br />
3 8 5<br />
2 5 2<br />
6 7 7<br />
6 7 7<br />
5 7 8<br />
2 8 4<br />
5 6 6<br />
4 3 3<br />
5 7 7<br />
5 6 6<br />
5 6 6<br />
4 6 7<br />
5 6 6<br />
6 7 8<br />
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S<br />
Taxon name Fan/ NS CS RS Chg li ght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Galiurn boreale Rubi N n -0.52 45 hc h Rhiz2 5 6 561 101 0 2.2 12.8 1580 7, 16 7 5 7 3<br />
Galium conshictum Rubi N r 40 hc h Rhizl 9 1 12 0 5 5.0 16.5 799 13 8 9 3 2<br />
Galium mollugo Rubi N n 0.04 112 hc h Rhiz2 5 3 1665 0 14 3.5 15.3 905 7 7 4 7 4<br />
Galiurn odoratum Rubi N n -0.62 45 hc h Rhiz2 7 3 1836 350 1 3.4 14.7 1086 1 3 5 71 6<br />
Gahm palustre Rubi N n 0.07 75 hc h Rhizl 5 4 2652 932 9 3.5 14.5 1105 11 7 9 5 4<br />
Galium parisiense Rubi NA $ -0.57 30 Th h O 9 2 63 0 0 3.7 16.3 693 3 8 3 7 2<br />
Galium pumilum Rubi N r -1.32 35 hc h Nodel 7 3 65 0 0 3.7 16.2 754 7 7 4 8 3<br />
Galium saxatile Rubi N n -0. 15 30 hc h Node2 7 2 2489 793 9 3.5 14.3 1148 8, 9 6 6 3 3<br />
Galturn spurium Rubi AN -1.871 100 Th h O 7 6 c NHem 55 0 0 3.9 16.1 755 4 71 5 8 5<br />
Galiurn sterneri Rubi N n 0.69 30 hc h Nodel 4 2 273 35 0 2.0 13.0 1457 7, 16 9 4 7 1<br />
Galium tricomutum Rubi AR CR -4.78 50 Th h 0 8 4 386 1 0 3.8 16.1 736 4 7 4 7 4<br />
Galium uliginosum Rubi N n -0.14 60 hc h Rhizl 5 5 1435 102 0 3.2 14.9 96 1 11 7 9 6 4<br />
Galium verurn . Rubi N n -0.85 75 hc h Rhiz2 5 5 2516 730 14 3.5 14.6 1045 7 7 4 6 2<br />
Gastridium ventricosum Poac NA $ -0.48 50 Th h o 9 1 159 0 2 4.6 16.3 839 4, 7 9 3 8 2<br />
Gaudinia fragilis Poac NA s 45 Th h 9 2 47 0 2 4.5 16.2 865 3, 6 8 5 6 6<br />
Gaultheria shallon Eric AN 150 Pn w Rhiz2 Am4 179 14 1 3.6 14.9 1077 1, 10 3 4 4 3<br />
Genista anglica Faba N n -1.09 50 Ch Pn wi 0 7 1 858 0 0 3.0 14.6 1019 10 8 5 3 2<br />
Genista pilosa Faba N r -0.26 40 Ch Pn wo 0 7 3 23 0 0 5.0 15.6 1011 10 8 5 4<br />
Genista tind oria Faba N n -0.77 60 Ch Pn w 0 7 3 932 0 1 3.6 15.6 880 6 8 6 71 2<br />
Gentiana nivalis Gent N VU r 15 Th 0 1 3 4 0 -0.5 11.2 1853 15, 16 9 5 7 3<br />
Gentiana pneurnonanthe Gent N s -0.31 40 hc 0 7 4 130 0 3.7 15.7 806 8, 10 8 7 4 1
Taxo n name Fam NS CS RS Chg._ Hght Len P1 P2 LF 1 LR2 W Clona l Clo ne2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Hordelymus europaeus Poac N s 0. 12 120 p hc 0 7 3 185 1 0 3.2 15.5 788 1 6 4 7 7 0<br />
Hordeum distichon Poac AC 75 a Th 0 Cro p 714 76 3 3.8 15.4 898 3, 4 8 4 7 7 0<br />
Hordeum distichon sensi at Poac AC 87 a Th 0 Crop 714 76 3 3.8 15.4 898 3, 4 8 4 71 7 0<br />
Hordeum j ubatum Poac AN 60 p hc 0 As2, Am 349 6 1 3.5 15.4 800 3, 5 9' 6 7 6 2<br />
Hordeum marinum Poac N s -0.85 37 a Th 0 9 1 146 0 1 4.3 16.4 720 6 9 6 8 6 4<br />
Hordeum murinum Poac AR I -0.04 60 a Th 0 8 4 1497 48 14 3.8 15.6 817 3, 17 8 4 7 6 0<br />
Hordeum secalinum Poac N n -0. 19 70 p he 0 7 3 926 30 0 3.8 16.0 742 5 8 6 7 6<br />
Hordeum vulgare Poac AC 100 a Th 0 Cro p 196 8 1 3.8 15.6 833 3, 4 9 4 71 7<br />
Hornungia petraea Bras N s 0.31 10 a Th 0 7 3 56 0 3 3.5 14.8 116 1 16 9 2 8 1<br />
Hottonia palustris Prim N n -0 .63 120 p Hy brag 7 3 463 2 0 3.6 16.0 697 13 7 11 7 5<br />
Humulus lupu/us Cann N n -0 .09 450 p hc Rhiz2 7 4 1273 0 8 3.8 15.8 833 3 6 7 7 8<br />
Huperzia selago Lyco N n -0 .41 10 p Ch sw 0 2 6 989 234 0 2.7 13.2 1472 15, 16 7 6 2 2<br />
Hyacinthoides hispanica Lili AN L 60 p Gb OM Eur 847 76 12 3.9 15.5 866 1, 3 , 17 5 4 6 6<br />
Hyacinthoides non-scripta Lili N n -0.4 1 50 p Gb Ot b 7 1 243 9 760 13 3.6 14.6 1092 1, 9 5 5 5 6<br />
Hydrilla vert icillata Hydr N r 100 p Hy DRa DRg 8 5 c 2 1 0 3.5 14.2 1555 13 6 12 9 3<br />
Hydrocharis morsus-ranae Hyd r N n -0 .89 50 p Hy Stoll 7 4 323 84 2 3.9 15.8 772 13 7 11 7 7<br />
Hydrocotyle ranunculoides Apia AN 20 40 p Hy lrreg Am 43 0 0 4.0 16.6 680 13, 14 7 10 7 7<br />
Hydrocotyle vulgaris Apia N n -0 .53 20 p hc Node2 8 2 2091 842 10 3.7 14.4 1126 11 8 8 6 3<br />
Hymenophyllum tunbrigense Hym e N n -0 .54 8 p hc Rhiz l 7 0 197 112 0 3.8 14.0 1567 16 4 6 2 3<br />
Hymenophyllum wilsonii Hyme N n -0 .87 10 p hc Rhiz l 5 0 577 176 0 3.1 13.1 1685 1, 16 5 5 3 3<br />
Hyoscyamus niger Sob AR , - 1.38 80 b hc<br />
0<br />
8 4<br />
796 87 5 4.0 15.7 799 4<br />
8 4 7 9<br />
Hypericum <strong>and</strong>rosaemum Clus N n 0.78 80 p Pn w 0<br />
9 2<br />
1139 744 8 4.0 14.8 1184 1, 3<br />
S 6 6 , 5<br />
Hypericum calycinum Clus A N<br />
0.74 60 p Ch Pn w Rhiz2<br />
Eur<br />
702 63 2 4.0 15.6 884 3<br />
5 71 5, 5<br />
Hypericum canadense Clus AN<br />
20 a Th<br />
0<br />
Am<br />
0 3 0 4.6 14.4 1252 11, 14 8 9 2 2<br />
Hypericum elodes Clus N n -0 .46 20 40 hc Hy Node2 7 1 583 260 7 4.2 14.8 1194 11 8 10 3 2<br />
Hypericum hirsutum Clus N n -0 .18 100 hc 0 7 4 1276 10 0 3.3 15.3 832 6, 7 6 5 7 5<br />
Hypericum humilusum Clus N n -0 .40 10 Ch 0 7 3 1732 428 12 3.6 14.8 1085 3 7 6 4 3<br />
Hypericum Iinadilolium Clus N r 0.09 40 hc Ch 0 8 1 14 0 9 5.5 15.8 1069 16 71 3 3 2<br />
Hypericum maculatum Clus N n 2.11 60 hc Rhiz2 5 3 1180 300 0 3.6 15.0 1016 1, 3 , 16 6 6 5 5<br />
Hypericum montanum Clus N n -0 .49 80 hc 0 7 3 269 0 0 3.8 15.6 867 1, 3 7 4 8 2<br />
Hypericum co l oratura Clus N n 80 hc Rhiz2 Root 8 4 1906 385 6 3.6 15. 1 95 1 7 7 4 7 5<br />
Hypericum pulchrum Clus N n -0.32 60 hc 0 7 2 2427 887 9 3.5 14.3 1148 10, 16 6 5 4 3<br />
Hypericum tetrapterum Clus N n -0 .41 60 hc Stoll 7 3 2 101 842 11 3.71 14.9 1025 11 71 8 6 4<br />
Hypericum undulatum Clus N s -0 .12 60 hc Stol l 8 1 81 0 0 5.6 15.5 1152 11 8 8 4 2<br />
Hypochaeris glabra Ast e N n - 1.01 20 a Th 0 8 3 270 5 14 4.0 15.9 754 8 8 4 4 2<br />
Hypochaeris maculata Aste N VU r -0 .10 60 p hc 0 7 4 c 17 0 1 3.9 16.1 710 7 8 4 8 3<br />
Hypochaeds radicata Aste N n 0.6 1 60 p hc 0 8 3 272 5 977 14 3.5 14.5 1104 6 8 4 5 3<br />
/beds amara Bras N s - 1.21 35 a Th 0 8 2 471 0 0 3.5 16.3 710 7 71 4 8 3<br />
Ilex aquifolium Aqui N n -0. 16 1500 p Ph w 0 8 2 235 3 86 1 14 3.6 14.7 1079 1 5 5 5 5<br />
Illecebrum vedicillatum Cary N r -0 .60 20 a Th h 0 Nodal 8 2 37 ' 0 0 5.6 15.7 1062 3, 13 8 7 3 2<br />
Impatiens capensis Bals AN 0.71 60 a Th h 0 Am6 323 1 0 3.7 16.2 723 13, 14 7 9 7 6<br />
Impatiens gl<strong>and</strong>ulifera Bals AN 1.85 200 a Th h 0 As l 1599 286 6 3.7 15.1 957 14 6 8 7 7<br />
Impatiens noli-tangere Bals N s -0 .77 60 a Th h 0 7 5 2 1 0 0 2.6 13.9 1833 1 4 71 71 6<br />
Impatiens p<strong>and</strong>fi ora Bals AN<br />
0.10 100 a Th h 0<br />
AO 470 1 0 3.5 15.7 82 1 1<br />
4 5, 7 8<br />
/nu/a conyzae<br />
Ast e N n -0 .15 125 p hc h 0 7 3<br />
860 0 7 3.9 15.9 82 1 7, 16<br />
7 3 8 3<br />
Mula crithmoides Ast e N e 0.09 95 p hc Ch h 0 9 1 121 19 8 5. 1 16.1 869 Co 18 9 6 7 5<br />
l a<br />
V
Taxon name Fam NS CS RS Chg_ Hght Len P1 P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats F R N<br />
Mu la helenium Aste AR -0.80 150 p hc 0 Eur, As l 631 100 3 4.0 15.1 973 3, 17 6 5<br />
Mu la salicina Aste N o 60 p hc Rhiz2 7 5 c 0 3 0 4.7 14.9 1017 16 9 3<br />
Iris foetidissima Ind N n 1.47 80 p hc Rhizl 8 2 728 0 14 4.2 16.1 821 1 8 5<br />
Iris germanica Ind AN 95 p hc Rhizl Gard 211 1 3 3.9 16.0 734 3, 17 6 4<br />
Iris pseudacorus Irid N n 0.16 150 p Gn Hy Rhiz2 8 3 2563 959 10 3.7 14.6 1081 11 6 6<br />
(sail s tinctoria Bras AR 1.08 150 b p hc 0 Eur, As 102 2 1 3.8 16.0 733 3, 16 8 3<br />
Isoetes echinospora Isoe N n 0.65 15 p Hy 0 4 6 178 32 0 3.2 13.0 1613 13 1 5 2<br />
Isoetes histrix lsoe N r 4 p hc 0 9 1 3 0 5 6.6 16.2 829 16 5 1<br />
Isoetes lacustris Isoe N n 0.95 25 p Hy 0 4 4 522 147 0 2.8 12.9 1660 13 1 4 1<br />
Iso lapis cernua Cype N n 0.23 15 a p Th hc 0 9 1 242 215 10 4.8 14.8 1181 11 5 3<br />
(so lapis setacea Cype N n 0.53 15 a p Th he 0 7 4 2038 638 10 3.5 14.4 1149 11, 14 5 3<br />
Jasione montana Camp N n -1.08 50 hc 0 7 3 1076 420 14 4.0 14.8 1152 8, 10 4 2<br />
Jug bans regia Jugl AN 2400 Ph w 0 Eur?, Asl ? 803 11 3 3.7 15.9 779 1, 3 8 7<br />
Juncus acutiflorus Junc N n 1.16 100 he Rhiz2 7 3 2498 845 11 3.5 14.5 1115 11 4 2<br />
Juncus acutus Junc N s 0.01 150 hc Ogr 9 1 41 28 12 5.4 15.7 1031 Co 19 7 3<br />
Juncus alpinoarticulatus June N $ -0. 12 30 hc Rhizl 4 6 53 0 0 0.7 12.1 1477 11 7 2<br />
Juncus ambiguus Junc N n 17 Th 0 8 3 175 50 1 4.4 14.9 999 Co 19, 21 71 5<br />
Juncus articulatus Junc N n 1.26 60 hc IRhiz2 8 4 2740 956 11 3.5 144 1108 11 6 3<br />
Juncus balticus Junc N s -0.34 45 Gn Rhiz2 2 6 92 0 0 3.3 13.1 1012 Co 19 5 2<br />
Juncus bigIumis June N s -0.17 12 hc Ogr 1 6 37 0 0 0.5 11.4 2194 11, 15 8 2<br />
Juncus bufonius June N n 25 Th 0 6 6 1986 724 3 3.6 14.6 1102 3, 11, 13, 14 6 5<br />
Juncus bufonius sensi at. Junc N n 1.13 25 Th 0 6 6 2736 937 14 3.5 14.5 1105 3, / , 13, 14 6 5<br />
La<br />
co Juncus bulbosus June N n 0.34 30 90 hc Hy Node2 Irreg 5 3 2250 827 8 3.5 14.2 1180 14 1 4 2<br />
Juncus capitatus Junc N 5 Th 0 8 3 12 0 10 6.3 16.1 889 10 5 1<br />
Juncus castaneus Junc N s -0.40 30 he Rhiz2 1 6 44 0 0 0.1 11.2 2291 15 7 3<br />
Juncus compressus Junc N n -1.09 30 Gn Rhizl 7 4 430 4 1 3.6 15.9 746 6, 11 7 5<br />
Juncus conglomeratus Junc N n 0.84 100 hc Ogr 7 3 2622 798 4 3.5 14.4 1117 11 4 3<br />
Juncus effusus Junc N n 1.06 120 hc Ogr 8 3 2753 974 13 3.5 14.4 1108 8, 11 4 4<br />
Juncus filiformis Junc N s 0.79 30 hc Ogr 4 6 32 0 0 2.3 13.6 1530 13 6 4<br />
Juncus foliosus Junc N n 25 Th 0 8 2 218 88 2 4.3 14.7 1241 11, 13 6 6<br />
Juncus gerardii June N n -0. 13 30 hc Rhiz2 6 6 919 271 11 4.2 14.4 1174 Co 21 7 6<br />
Juncus infi exus Junc N n 0.04 90 hc Ogr 8 4 1758 631 9 3.8 15.2 925 6, 11 71 5<br />
Juncus maritimus June N n -0.26 100 Gn Ogr 8 3 390 196 11 4.7 15.1 1081 Co 21 8 5<br />
Juncus pygmaeus Junc N EN r 8 Th 0 9 1 4 0 0 6.7 15.9 965 3 4 2<br />
Juncus squarrosus Junc N n 30 p hc Ogr 7 2 1849 484 0 3.1 13.8 1254 8, 12 2 2<br />
Juncus subnodulosus Junc N n 0.15 120 p hc Rhizl 8 3 680 224 2 3.9 15.5 838 11 8 4<br />
JUnCUS tenuis Junc AN 0.83 40 p hc Ogr Am, SAm 1053 145 3 3.6 14.6 1267 1, 3, 13 5,1 4<br />
Juncus trifidus Ju nc N n -0.38 30 p hc Ogr 1 4 177 0 0 1.0 11.5 2162 15 2 2<br />
Juncus triglumis Junc N n -0.38 20 p hc Ogr 1 6 200 0 0 0.9 11.8 2085 11, 16 6 2<br />
Jun/penis communis Cupr N n -0.42 500 p Ph Ch w O 5 6 1020 145 0 2.8 13.4 1380 7, 10, 15, 16 5 3<br />
Kickxia elatine Scro AR -0.18 25 a Th 0 8 3 911 41 11 4.1 16.0 813 4 6 5<br />
Kickxia spuria Scro AR -0.071 25 a Th 0 8 3 622 0 2 3.9 16.2 737 4 7 5<br />
Knautia arvensis Dips N n -0.88 100 p hc 0 7 4 1707 478 4 3.8 15.2 919 6, 7 8 4<br />
Kobresia sitnpliciuscula Cype N r 0.58 20 p he 0 1 6 18 0 0 -0.1 11.5 2044 11, 15 6 1<br />
Koeleria macrantha Poac N n -0.29 50 p hc 0 7 6 1250 266 7 3.7 14.7 989 7 7 2<br />
Koeleria vallesiana Poac N r 40 p hc 0 8 2 4 0 0 4.5 16.4 868 7 8 1
S<br />
L F R N<br />
8 9 6 1<br />
6 5 7 7<br />
8 4 7 6<br />
8 5 7 6<br />
8 4 7 7<br />
6 12 7 6<br />
4 5 7 6<br />
7 5 7 8<br />
7 4 7 6<br />
7 5 7 7<br />
71 5 7 6<br />
5 6 7 8<br />
6 5 7 7<br />
6 4 7 7<br />
7 4 6 3<br />
Br Habitats<br />
11, 16<br />
3, 17<br />
19<br />
3, 17<br />
3, 16<br />
13<br />
1<br />
3, 17<br />
3, 4<br />
4<br />
4<br />
3, 17<br />
3, 4, 17<br />
3, 17<br />
1, 2, 17<br />
LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co<br />
2175<br />
884<br />
601 Co<br />
741<br />
693<br />
839<br />
855<br />
911<br />
842<br />
1097<br />
877<br />
869<br />
1027<br />
1059<br />
1049<br />
LF1<br />
Th<br />
Ph<br />
Th<br />
hc<br />
hc<br />
Hy<br />
Ch<br />
hc<br />
Th<br />
Th<br />
Th<br />
hc<br />
Th<br />
Th<br />
Ph<br />
1 P2<br />
Taxon name Fam NS CS RS Chg Hght Len<br />
6<br />
700<br />
75<br />
200<br />
200<br />
300<br />
60<br />
60<br />
30<br />
25<br />
30<br />
35<br />
30<br />
95<br />
4600<br />
7j 6, 5 3<br />
7 6 5 3<br />
3 6 7 6<br />
7 3 8 4<br />
9 5 7 6<br />
71 4 8 3<br />
6 5 4 3<br />
8 6 7 6<br />
7 9 7 4<br />
7 6 6 5<br />
71 4 8 2<br />
6 5 7 6<br />
6 5 7 6<br />
9 6 7 8<br />
9 4 5 5<br />
8 9 8 71<br />
7 4 7 4<br />
7 11 7 8<br />
7 11 7 6<br />
7 11 7' 7<br />
71 12 71 5<br />
8 6 6 4<br />
8 4 7' 3<br />
8 5 6 3<br />
7 4 7 6<br />
8 4 8 6<br />
7 4 5 4<br />
8 5 7 8<br />
9 4 7 7'<br />
2, 17<br />
2, 17<br />
1, 3<br />
4, 7<br />
19<br />
3, 18<br />
8, 15<br />
3, 6, 7<br />
11<br />
6<br />
3<br />
3<br />
3, 17, 18, 19<br />
18<br />
3, 4, 16<br />
13<br />
4<br />
13<br />
11, 13<br />
13, 14<br />
11, 13<br />
6<br />
7<br />
7<br />
3, 4, 17<br />
3, 19, 21<br />
3<br />
6<br />
3, 17<br />
1134<br />
1133<br />
955<br />
718<br />
886 Co<br />
782<br />
1172<br />
742<br />
823<br />
1079<br />
835<br />
776<br />
942<br />
1023 Co<br />
875<br />
766<br />
717<br />
739<br />
986<br />
787<br />
832<br />
1103<br />
918<br />
960<br />
801<br />
786<br />
1074<br />
629<br />
757<br />
Ph<br />
Ph<br />
Gn<br />
Th<br />
Gn<br />
hc<br />
Gn<br />
Th<br />
hc<br />
hc<br />
hc<br />
Gn<br />
Ph<br />
Pn<br />
Th<br />
hc<br />
Th<br />
Hy<br />
Hy<br />
Hy<br />
Fly<br />
hc<br />
hc<br />
hc<br />
Th<br />
hc<br />
hc<br />
hc<br />
Th<br />
3000<br />
3700<br />
30<br />
60<br />
20<br />
300<br />
40<br />
75<br />
120<br />
80<br />
200<br />
120<br />
600<br />
300 b<br />
100 a<br />
90<br />
30<br />
0.5<br />
0.4<br />
0.3<br />
1<br />
60<br />
35<br />
20<br />
40<br />
60<br />
50<br />
120<br />
40<br />
LO<br />
0<br />
p<br />
3
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Clonal Clone2 E/ E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Lobelia dortm anna Camp N n -0.05 - 4 p Hy h 0<br />
4 3<br />
570, 178 0 3.0 12.9 1635 13<br />
8 12 5 1<br />
Lobelia urens Camp N VU r -0. 19 70 p hc h 0<br />
8 1<br />
12 0 0 4.7 16.1 988 8, 10<br />
8 8 4 2<br />
Lobularia maritima Bras AN ' 2.34 30 a p Th hc h 0 0 3 Eur 738 33 13 4.0 15.71 854 18, 19 9 3 71 4<br />
Loiseleuria procum bens Eric N n -0.58 25 p Ch w Node2 1 6 182 0 0 0.9 11.4 1994 15 9 5 2 2<br />
Lolium multifl orum Poac AN : -1.06 100 a b Th hc h 0 Eur 2069: 340 10 3.6 14.9 968 5 7 5 7 7<br />
Lolium perenne Poac N n -0.29 50 p hc h 0 8 3 2743 964 14 3.6 14.5 1096 3, 6 8 5 6 6<br />
Lolium te m ulentum Poac AR -4.05 90 a Th h 0 Eur 341 37' 7 4.0 15.6 855 4 7 4 8 7<br />
Lonice ra p ericlym e num Capr N n -0.11 600 p Ph w 0 Node2 8 2 2622 943 14 3.6 14.5 1102 1 5 6 5 5<br />
Lonicera xylosteum Capr AN 0.58 200 p Pn w 0 7 4 Eur, As1 242 16 0 3.4 15.2 874 1, 3 5 5 7 6<br />
Lotus angustissimus Faba N $ -0.23 30 a Th h 0 8 3 55 0 12 5.7 16.2 952 8 8 3 4 3<br />
Lotus corniculatus Faba N n 1.09 40 p hc h 0 8 5 2801 975 14 3.5 14.5 1104 6, 7 7 4 6 2<br />
Lotus glab er Faba N n -0.55 90 p hc h 0 8 3 509 0 4 3.9 16. 1 732 3, 6, 7 7 7 7 5<br />
Lotus pe dunculatus Faba N n -0.06 60 p he h 0 Rhizl 7 3 2380 729; 13 3.6 14.7i 1072 11 7 8 6 4<br />
Lotus s ubbillorus Faba N s 0.22 30 a Th h 0 8 2 861 8 14 5.8 16.0 987 8 7 5 6 5<br />
Ludwigia palustris Onag N r 0. 19 15 p Th Hy h Node2 8 3 11 0 3 4.6 16.6 812 13 8 9 4 4<br />
Lupinus arboreus Faba AN 1 1.84 200 Pn w 0 Am4 341 21 11 4.2 15.7 825 3. 19 9 4 7 3<br />
Lupinus polyphyl/us Faba AN : 150 hc h 0 Am4 215 3 1 3.2 15.2 828 3, 14, 17 7 5 5 5<br />
Luron ium natans Alis N s 0.24 50 Hy h Sto12 7 2 91 3, 0 3.3 14.71 1229 13, 14 8 11 5 3<br />
Luzula arcuata Junc N r -0.43 10 he h Rhizl 1 3 22 0 0 0.0 10.8 2044 15, 16 9 5 2 2<br />
Luzula campestris Junc N n -0.18 15 hc h Rhiz2 7 3 2725 835 14 3.5 14.5 1100 6 7 4 5 2<br />
Luzula forsteri Junc N n 0.25 35 hc h 0 9 2 309 0 5 4.2 16.2 859 1 4 4 5 2<br />
Luzula multillora Junc N n 0.28 50 hc h 0 3 6 2451 834 7 3.5 14.3 1148 8 7 6 3 3<br />
Luzula pallidula Junc N VU r 30 hc h 0 5 5 c 2 0, 0 3.4 16.3 553 1, 11 7f 7 5 2<br />
Luzula pilosa June N n -0.35 32 hc h 0 5 4 2132 266 1 3.2 14.4 1127 1, 2 5 5 5 3<br />
Luzula spicata June N n -0.72 25 hc h Rhizl 1 3 189 0 0 1.0 11.5 2085 7, 15, 16 8 5 3 2<br />
Luzula sylvatica Jun c N n -0.02 80 hc h Rhizl 7 3 2058 621 4 3.3 14.1 1208 1, 16 5 5 4 4<br />
Ly chnis alpina Cary N VU r 20 Ch h 0 2 3 2 0 0 0.5 12.0 1640 15 8 3 4 2<br />
Lychnis flos-cuculi Cary N n -0.79 75 he h 0 7 4 2569 765 9 3.5 14.5 1095 11 71 9 6 4<br />
Lychnis viscaria Cary N VU r 0.01 45 Ch h 0 7 4 c 28 0 0 2.2 13.8 926 16 8 3 4 2<br />
Lycium Sola AN 0.13 250 Pn w Root As 1104 68 9 3.8 15.7 784 3, 19 8 5 7 4<br />
Lyciurn barbarum Sola AN 250 Pn w Root As 3, 19 8 5 7 4<br />
Lycium chinense Sola AN 250 Pn Ph w Root As 3, 19 8 5 7 4<br />
Lycop e rsicon e sculentum Sola AN 150 a Th h 0 SAm 523 41 4.0 15.6 876 17 71 5 71 8<br />
Lyc opodie lla inundata Lyco N s -0.65 5 Ch h Nodal 5 3 233' 18 3.5 14.9 1122 10, 12 9 9 2 1<br />
Lycopodium annotinum Lyco N s -0.38 10 Ch sw Node2 2 6 171 0 0.7 11.7 1760 10, 15 6 6 3 3<br />
Lycopodium clavatum Lyco N n -0.52 15 Ch sw Node2 5 6 948 81 2.4 13.3 1368 10 7 5 1 2<br />
Lycopus europaeus Lami N n -0.01 100 hc h Rhizl 7 4 1689 347 3.8 15.2 995 11 7 8 7 6<br />
Lysichiton am ericanus Arac AN 110 hc h Rhizl Am4 174 24 3.9 15.1 1073 13, 14 4 9 6 8<br />
Lysimachia nem orum Prim N n -0.46 20 Ch hc h Node2 7 2 2217 740 3.4 14.4 1150 1 5 7 4 5<br />
Lysimachia nummularia Prim N n -0.02 5 hc Ch h Node2 7 3 1266 227 3.7 15.5 895 6, 11, 14 5 7 5 5<br />
Lysimachia punctata Prim AN , 4.62 120 hc h Rhiz1 Eur 1127 48 3.5 15.1 999 1, 3, 17 6 6 7 5<br />
Lys ima chia thyrsillora Ri m N s 0.38 70 hc Hy h Rhiz2 4 6 51 0 2.7 14.2 1200 11, 13 8 10 4 3<br />
Lysimachia vulgaris<br />
Prim N n 0.22 105<br />
hc h Rhiz2<br />
7 5<br />
1227f 288 3.71 15.2 943 11<br />
7i 9 71 5,<br />
Lythrum hyssopifolium Lyth AR VU -1.12 15<br />
Th h 0<br />
8 4<br />
112 3 3.9 16.0 777 4<br />
8 6 6 4<br />
Lythrum portula Lyth N n 0.32 8 Th Hz h 0 Nodel 7 3 1262 321 3.8 14.8 1084 11, 13 8 9 5 3<br />
Lythrum salicaria Lyth N n -0.08 120 hc h 0 7 5 1692 827 4.0 15.0 1024 11 7 9 7 5
Taxon name Fam NS CS RS Chg_ Hght Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Mahonia aquifoliurn<br />
Berb AN 1.61 150 Pn w Rhiz2 Am4 991 4 2 3.4 15.6 786 1, 3 4 6 5<br />
Maianthemurn bifolium Li li NA VU r 0.32 20 Gn h Rhiz2 5 5 0 4 0 0 2.9 15.0 753 1, 2 5 3 3<br />
Malus domestica Rosa AR 1000 Ph w 0 Gard 1532 327 8 3.7 15.0 975 3 5 6 7'<br />
Malus sylvestris sens.lat. Rosa N n 0.57 1000 Ph w 0 7 3 2023 598 11 3.7 15.0 975 1, 3 5 6 6<br />
Malus sylvestris sens.str. Rosa N n 1000 Ph w 0 7 3 1335 218 0 3.7 15.1 964 3 5 6 6<br />
Ma Iva moschata Maly N n -0.04 80 hc h 0 7 3 1423 0 10 3.7 15.6 871 6 3 7 4<br />
Ma Iva neglecta<br />
Maly AR -0.22 60 Th h 0 7 3 1196 70 14 3.8 15.7 781 3 4 8 71<br />
Melva pusilla Maly AN 50 a Th h 0 7 5 c Eur, As 107 6 1 4.1 16.0 788 3, 17, 19 5 5 5<br />
Ma Iva sylvestris Maly AR -0.30 150 p he h 0 8 4 1788 354 14 3.8 15.3 899 3, 17 4 8 7<br />
Marrubium vulgere Lami N s -2.02 60 p hc h Rhizl 8 4 46 0 0 4.6 16.1 861 7 5 7 8<br />
Matricaria discoidea Aste AN -0.49 35 a Th h 0 As2?, Am? 2677 945 14 3.6 14.5 1086 3, 4 5 7 7<br />
Matricaria recutita Aste AR 0.92 60 a Th h O 8 3 1588 51 11 3.7 15.5 868 3, 4 5 7 7<br />
Matteuccia struthiopteris Wood AN 60 p hc h O 4 6 c NHem 74 4 3.2 14.7 1108 1 8 7 7<br />
Matthiola incana Bras AN 0.75 80 p Pn sw O 9 1 Eur 107 2 5.0 15.9 874 Co 18, 19 3 5 2<br />
Matthiola sinuata Bras NA VU r 60 b hc h O 9 1 19 8 5.4 15.6 1089 Co 18, 19 3 7 2<br />
Meconopsis cambrica Papa N s 2.36 60 p hc h O 5 1 54 77 3.5 14.0 1321 1 5 7 5<br />
Medicago arabica Faba N n 0.69 60 a Th h O 9 2 744 0 1 4.2 16.2 781 3, 17 5 6 5<br />
Medicago lupulina Faba N n -0.43 50 a p Th hc h o 7 4 2064 686 1 3.8 15.0 963 7, 17 4 8 4<br />
Medicago minima Faba N s -1.97 20 a Th h O 8 4 54 0 3.9 16.5 623 8 3 7 2<br />
Medicago polymorphe Faba N s -1.34 60 a Th h o 9 2 118 0 1 5.0 16.4 801 8 4 5 5<br />
Medicago sativa Faba N s -0.56 90 p hc h 0 Rhir l 8 4 c 54 0 3.5 16.2 604 3, 6 4 6 5<br />
Medicago sativa<br />
subsp falcata Faba N s 60 hc h Rhizl 8 4 c 541 01 3.51 16.2 604 3 3 7 3<br />
Medicago sativa subsp.sativa Faba AN 90 hc h 0 Crop 1065 17 3.8 15.8 768 3, 6 4 6 5<br />
Melampyrum arvense Scro AN -0.49 60 a Th h 0 7 3 c Eur 50 0 3.6 16.2 692 3, 4, 16 4 8 3<br />
Melampyrum cristatum Scro N r -0.88 50 a Th h 0 7 4 c 62 0 3.4 16.3 606 3 3 8 2<br />
Melampyrum pratense Scro N n -0.88 60 a Th h 0 5 4 1696 323 3.2 14.3 1220 1, 2 5 2 3<br />
Melampyrurn sylvaticum Scro N r -0.58 35 a Th h 0 4 3 75 20 1.5 12.5 1532 1, 16 5 2 2<br />
Merica nutans Poac N n -0.17 60 hc h Rhiz1 5 5 c 408 0 1.9 13.0 1483 1, 7, 16 5 7 3<br />
Merica uniflora Poac N n -0.04 60 hc h Rhir l 7 3 1511 246 3,5 15.0 1015 1 5 7 5<br />
Mehlotus elbus Faba AN -0.20 150 a hc Th h 0 Eur?, Asl ? 913 15 3.7 15.8 778 3 3 7 4<br />
Mefi lotus altissimus Faba AR 0.73 150 hc h 0 7 3 1122 16 3.8 15.8 785 3, 17 6 7 7<br />
Melilotus indicus Faba AN -1.59 40 Th h 0 Eur, As 1 427 12 1 3.8 15.7 790 3, 17 5 71 71<br />
Melilotus <strong>of</strong>i cinalis Faba AN 0.02 150 hc h 0 Eur?, Asl ? 1142 26 3.7 15.7 790 3, 17 5 7 5<br />
Melissa <strong>of</strong>ficinalis Lami AN 1.73 60 hc h Rhizl Eur 667 36 4.1 15.9 854 3, 17 5 7 6<br />
Melittis melissophyllum Lami N s -0.47 60 hc h Rhizl 7 3 119 0 5.1 15.7 1091 1, 3 4 7 5<br />
Menthe aquatica Lami N n -0.11 90 hc h Rhiz2 7 3 2475 922 3.7 14.7 1065 11 8 7 5<br />
Mentha arvensis Lami N n -1.30 60 hc h Rhiz2 5 6 1965 428 3.6 14.9 1017 4, 11 7i 71 6<br />
Mentha pulegium Lami N VU r -0.70 30 hc h Rhiz2 8 3 242 45 4.4 15.9 869 6, 13 7 5 7<br />
Mentha spicata Lami AR 1.69 90 hc h Rhiz2 Crop 1563 74 3.5 15.0 942 3, 17 5 7 7<br />
Menthe suaveolens Lami N $ -0.32 100 hc h Rhiz2 9 2 118 0 5.4 15.5 1151 3 8 6 6<br />
Menyanthes trifoliata Meny N n -0.04 30 150 Gn Hy h Rhiz2 5 6 1905 756 3.4 14.1 1201 11 10 4 3<br />
Mercurialis annua Euph AR 0.28 50 Th h 0 9 2 793 55 1 4.0 16.0 779 3, 4, 17 5 7 7<br />
Mercurialis perennis Euph N n -0.65 40 hc h Rhiz2 7 3 2214 4 3.2 14.8 1045 1 6 7 7<br />
Mertensia maritima Bora N s -0.53 60 hc h 0 2 3 222 29 3.8 13.4 1083 Co 19 5 T 7<br />
Mespilus germanica Rosa AR 900 Ph w o Eur 98 1 4.4 16.1 861 1, 3, 17 4 6 6
Taxon name Fam NS CS RS Chg. Hght Len P1 P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tja n Tjul Prec Co Br Habitats L F R N S<br />
Meum athamanticum Apia N s -0.40 60 p hc 0 4 3 164 0 0 1.6 12.9 1459 3, 6 8 5 4 3<br />
Mibora minirna<br />
Poac N r -0.01 8 a Th<br />
0<br />
8 2<br />
7, 0 10 5.8 16.1 861 Co 19<br />
9 3 71 1<br />
Milium effusum<br />
Poac N n 0.31 150 p hc<br />
0<br />
5 6<br />
1391 91 0 3.6 15.3 928 1<br />
4 5 6 5<br />
Milium vernale Poac N 0 5 a Th 0 9 1 0 0 2 6.8 16.6 718 19 9 3 6 2<br />
Mimulus Scro AN -0.47 50 p hc Node2 Am4, SAm 1767 237 5 3.2 14.3 1106 13, 14 7 9 6 5<br />
Mimulus guttatus Scro AN 50 p hc Node2 Am4 996 44 4 3.2 14.5 1020 13, 14 7 9 6 6<br />
Mimulus guttatus x luteus (M<br />
x robert sin<br />
Scro AN<br />
50 p hc<br />
Node2<br />
Gard<br />
473, 125 0 3.1 14.0 1162 13, 14 7 8 7i 5<br />
Mimulus luteus<br />
Scro AN<br />
50 p hc<br />
Node2<br />
SAm<br />
186 5 0 2.8 13.6 1144 13, 14 7 9 5 5<br />
Mimulus moschatus Scro AN 40 p hc Node2 Am4 361 13 2 3.3 14.6 1099 13, 14 7 8 5 5<br />
Minuartia hybrida Cary N s -1.70 20 a Th 0 9 2 294 0 1 3.5 16.0 716 7 9 3 8 3<br />
Minuartia recurva Cary N o 5 p Ch 0 1 3 0 1 0 4.8 14.2 1414 15 8 4 3 1<br />
Minuartia rubella Cary N r 0.01 6 p Ch 0 1 6 71 0 0 0.8 11.2 1679 15 8 4 7 1<br />
Minuartia sedoides Cary N s -0.75 8 p Ch 0 1 3 76' 0 0 1.2 11.4 2095 15 8 5 4 2<br />
Minuart ia stricta Cary N EN r 10 p Ch 0 1 6 1 0 0 0.4 12.1 1443 11 9 9 5 2<br />
Minuartia verna Cary N s -0.42 15 p Ch 0 4 5 139 30 0 2.7 13.9 1215 7, 16 8 4 7 1<br />
Misopates orontium Scro AR -0.89 50 a Th 0 8 4 488 24 11 4.3 15.9 864 4 7 5 6 6<br />
Moehringia trinervia<br />
Cary N n -0.40 40 a Th<br />
0<br />
7 3<br />
1990 259, 4 3.5 15.0 982 1<br />
4 5 7 6<br />
Moenchia erecta<br />
Cary N n -0.65 12 a Th<br />
0<br />
8 2<br />
418 0 14 4.2 16.0 823 8<br />
9 4 4 3<br />
Molinia caerulea Poac N n -0.34 130 p hc Ogr 5 4 2244 897 6 3.5 14.2 1179 12 7 8 3 2<br />
Moneses uniflora Pyro N VU r 0.14 4 p hc Rhizl 4 6 27 0 0 2.0 13.0 985 2 4 5 4 1<br />
Monotropa hypopitys Mono N<br />
-h.<br />
n -1.09 30 p Gn Rhizl 7 6 288 24 0 3.7 15.8 817 1 4 5 6 2<br />
to Montia fontana<br />
Port N n 0.14 20 a p Th Hy Nodal<br />
5 3<br />
21971 547, 14 3.4 14. 1 1198 11<br />
71 9 5 3<br />
Muscari neglectum<br />
Lili NA VU r 1.55 30 p Gb<br />
Gib DRg 8 4<br />
13 0 0 3.3 16.3 590 3, 8<br />
7 3 7 5<br />
Mycelis muralis Aste N n 0.01 100 p hc 0 7 3 1302 0 0 3.3 15.2 944 1, 16 4 5 7 5<br />
Myosotis alpestris Bora N r -0.22 25 p hc 0 1 6 7 0 0 -0.1 11.6 1623 7, 15, 16 8 4 8 2<br />
Myosotis arvensis Bora AR -0.34 40 a Th 0 5 4 2577 748 8 3.5 14.6 1056 3, 4 7 5 6 6<br />
Myosotis discolor Bora N n 0.14 25 a Th 0 7 3 23171 521 14 3.5 14.4 1088 6 7 5 5 3<br />
Myosotis taxa Bora N n 0.65 40 b hc 0 5 6 2409 757 8 3.5 14.5 1085 11 7 9 6 5<br />
Myosotis ramosissima Bora N n 0. 11 25 a Th 0 8 3 1174 52 14 3.8 15.5 823 8, 16 8 3 6 3<br />
Myosotis scorpioides Bora N n -0.77 57 p hc Hy Stoll 7 4 2291 662 3 3.5 14.7 1037 11, 14 7 9 6 6<br />
Myosotis secunda Bora N n 0.52 55 p hc Stoll 7 1 1736 498 6 3.3 14.0 1237 11 6 9 5 4<br />
Myosotis sicula Bora N o 15 a Th 0 9 1 0 0 2 6.2 17.0 794 19 6 7 6 3<br />
Myosotis stolonifera Bora N s 0.77 20 p hc Stoll 4 1 115 0 0 1.6 13.2 1362 11, 14 8 9 5 4<br />
Myosotis sylvatica Bora N n 2. 18 47 p hc 0 7 5 1690 24 4 3.4 15.1 931 1 6 5 7 5<br />
Myosoton aquaticum Cary N n 0.00 100 p hc Nodal 7 4 927 0 0 3.6 16.0 747 11, 13, 14 7 8 7 8<br />
Myosurus nnnimus Ranu NA n -0.66 8 a Th 0 7 3 339 0 2 3.8 16.3 691 4 8 7 6 5<br />
Myrica gale<br />
Myri N n -0.75 150 p Pn<br />
Rhiz2<br />
5 2<br />
976, 553 0 3.4 13.8 1353 12<br />
8 9 3 2<br />
Myriophyllum alternifl orum Halo N n 1.00 120 p Hy<br />
Irreg<br />
5 2<br />
1390 327 3 3.2 13.8 1299 13, 14 7 12 5 3<br />
Myriophyllum aquaticum Halo AN ,<br />
200 p Hy<br />
Irreg SAm 268 2 7 4.3 16.1 838 13<br />
7 12 5 3<br />
Myriophyllum spicatum Halo N n 0.63 250 p Hy<br />
Irreg 7 5<br />
1409 373 7 3.7 15.1 907 13, 14 7 12 7 7<br />
Myriophyllum verticillatum Halo N n -0.89 300 p Hy Irreg DRa 7 6 360 130 0 3.8 15.7 765 13, 14 7 12 7 7<br />
Mynt is odorata<br />
Apia AN<br />
-0.25 180 p hc<br />
0<br />
Eur 1152 147, 0 3.0 14. 1 1084 3, 17<br />
7 6 7 71<br />
Naj as flexilis<br />
Naja N s 0.48 30 a Hz<br />
0 4 6<br />
28 28 0 4.1 13.8 1338 13<br />
6 12 7 4 1<br />
Naj as marina Naja N VU r 97 a Hz 0 8 6 c 4 0 0 3.9 16.1 600 13 5 12 9 6 0<br />
Narcissus pseudonarcissus Lili N n 0.87 35 p Gb Otb 8 2 646 0 3 3.7 15.6 920 3 7' 5 6 5 0
Fam NS CS RS Chg_ Hght Len 1 P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Lili Poac N n -0.32 -0.68 45 40 he hc 0 Rhizl 5 3 1 2051 1628 560 716 3 0 33.3 2 14.0 13.8 1226 1296 8 12 79 32 21 0<br />
Orch N EX n x -0.91 47 30 Gn 0 7 9 4 1 742 1 99 24 0 3.5 4.7 15.2 14.8 1107 938 7, 1 16 4 87 25 0<br />
Lami AR -1.23 100 he Rhizl 7 4 478 6 1 3.7 15.9 761 3, 7 4 7 6 0<br />
Nymp N n -0.13 150 Hy Rhizt 5 4 1140 452 0 3.6 15.1 975 13, 14 11 7 6<br />
Nymp N s 0.87 150 Hy Rhizl 4 6 68 0 0 1 7 12.5 1680 13 11 6 4<br />
Nymp N n 1.02 150 Hy Rhizl 7 3 1511 340 5 3.6 14.8 1090 13 11 6 4<br />
Meny N s 2.81 200 Hy Irreg Rhiz2 7 5 45 0 0 3.5 16.4 603 13, 14 11 7 6<br />
Apia Scro N n -0.35 -0.46 150 50 Th 0 7 5 2320 865 7 3.7 14.7 1047 6 5 6 5 0<br />
p Hz Hy 0 7 4 505 183 0 3.8 15.6 792 11 10 7 6<br />
Apia N n -0.04 150 he Hy 0 8 2 1599 633 12 4.0 14.8 1124 11, 14 ' 9 6 7<br />
Apia N n -1.18 0.19 100 80 Hy hc Hy 0 Node2 7 3 1 804 235 101 45 6 0 3.9 3.7 15.8 16.0 771 718 11 14 10 9 78 6 0<br />
Apia N n -0.36 0.48 100 hc 0 9 8 2 1 241 551 118 0 0 3 4.3 4.4 15,4 16.2 957 849 6 11 87 86 53 3 0<br />
Apia N s 0.37 100 hc 0 8 3 76 0 0 3.7 16.3 661 6 9 7 5 0<br />
Onag AN 1.02 100 hc 0 Am, SAm 1185 38 11 3.9 15.8 839 3, 16, 17, 19 4 6 4 0<br />
Onag AN 100 hc 0 Am? 614 9 2 3.9 15.9 777 3, 16, 17, 19 4 6 4 0<br />
Onag AX 100 hc 0 125 2 1 3.7 15.9 798 3, 16, 19 3 6 5 0<br />
Onag AN 80 he 0 Am? 217 0 4.2 15.9 921 3, 16, 17, 19 4 6 3 0<br />
Onag AN 100 he 0 Am 966 24 1 4.0 15.9 832 3, 16, 19 4 6 5 0<br />
Faba N NA VU n r -0.76 0.27 60 15 a Th he 0 9 7 4 1 265 10 0 5,6 3,6 15.8 16.2 999 710 Co 7 1 8 42 8 32 0 1<br />
Faba N n -0.45 60 Ch he sw Rhiz2 7 3 1664 178 1 3.8 15.3 878 7 4 6 3 0<br />
Aste Faba AR N n -0.82 0.66 200 70 Ch hc hc sw 0 87 4 724 778 0 5 3.6 3.7 16.0 15.9 718 733 6, 3, 7 17 4 86 37 0<br />
Ophi N s 10 Gn Root 5 2 72 12 4.3 13.3 1252 8 6 5 2 1<br />
Ophi N VU r 4 Gn Root 9 1 1 0 6,7 16.2 848 8 6 5 2<br />
Ophi N n 30 Gn Root 7 6 1474 209 3.6 15.1 964 6, 7 7 7 3<br />
Ophi N n 0.72 30 Gn Root 7 6 1474 209 3.6 15.1 964 6 7 7 3<br />
Orch N VU n r 0.83 45 35 Gn 0 9 2 936 6 182 0 3,9 4.0 15.7 16.4 807 766 7 4 89 23<br />
Orch N n -1.34 60 Gn 0 7 3 264 31 3.7 15.8 803 1. 7, 11 5 9 2<br />
Taxon name<br />
Nardus stdcta<br />
Narthecium ossifragum<br />
Neotinea maculata<br />
Neottia nidus-avis<br />
Nepeta cataria<br />
Nuphar lutea<br />
Nuphar pumila<br />
Nymphaea alba<br />
Nymphoides pe/tata<br />
Odontites vernus<br />
Oenanthe aquatica<br />
Oenanthe crocata<br />
Oenanthe fistulosa<br />
Oenanthe fluviatilis<br />
Oenanthe lachenalii<br />
Oenanthe pimpinelloides<br />
Oenanthe silaifolia<br />
Oenothera<br />
Oenothera biennis<br />
Oenothera biennis x<br />
glazoviana (0 . x fallax)<br />
Oenothera cambrica<br />
Oenothera glazioviana<br />
Onobrychis<br />
Orionis reclinata<br />
Orionis repens<br />
Ononis spinosa<br />
Onopordum acanthium<br />
Ophioglossum azoricum<br />
Ophioglossum lusitanicum<br />
Ophioglossum vulgatum<br />
Ophioglossum vulgatum<br />
sens.lat<br />
Ophrys apifera<br />
Ophrys fuciflora<br />
Ophrys insectifera<br />
Ophrys sphegodes<br />
Orchis laxiflora<br />
Orchis mascula<br />
Orchis militaris<br />
Omhis morio<br />
Orchis purpurea<br />
Orchis simia<br />
Orchis ustulata<br />
Oreopteris limbosperma<br />
Origanum vulgare<br />
Orch N s o -Oi l 20 50 Gn 0 98 2 4 c 62 0 0 8 1 4.0 6.4 16.3 16.7 729 800 6, 7 11 49 98 3 2<br />
Orch N n -0.72 40 Gn 0 7 3 1962 475 9 3.5 14.7 1073 1, 7, 16 5 7 4<br />
Orch N VU n r -0.98 45 20 Gn 0 7 4 3 c 931 19 124 0 0 8 3,4 3.9 16.3 15.8 694 801 6, 7 7 43 7 9 3 2<br />
Orch N s -0.56 50 Gn 0 7 3 36 0 1 4.0 16.5 748 1 4 8 3<br />
Orch N VU<br />
Orch N s r -1.77 30 15 Gn 0 87 3 265 10 0 0 3.8 3.5 16.4 15.7 697 777 7 34 8 2<br />
Thel N n -0.18 90 hc 0 7 3 1585 138 0 2.8 13.7 1323 1, 16 6 4 3<br />
Lami N n -0.10 65 Ch hc 0 Nodal 8 5 1148 179 0 3.7 15.3 898 7, 16 4 7 4
S<br />
P2 LF1 LF2 W Clonel Clone2 E1 E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Gb Mb DRg 8 3 Eur 1139 8 12 3.7 15.5 848 1, 3, 7, 8 8 3 6 4<br />
Th Gb Otb 0 9 7 2 1002 33 20 0 12 0 3,6 3.9 15.5 16.2 773 935 8 1, 3 5 71 5 4 7 5<br />
4 3<br />
p Th Gn 0 8 7 2 3 92 3 42 0 7 2 4.0 7.0 16.4 13.7 1493 832 8, 16 10 8 3 3 7 2<br />
3 6 0 0 4.5 16.5 753 Co 18 8 4 8 5<br />
34 0 2671 5 0 0 4.1 3.6 16.4 16.2 782 713 3, 18 7 8 3 98 2 3<br />
2 160 122 11 4.9 15.5 1004 1, 3, 16 4 5 6 5<br />
3 800 0 14 4.0 16.1 774 4, 5 7 4 8 6<br />
3 25 0 12 4.9 16.3 776 3, 6 7 4 7 2<br />
2 422 30 4 4.1 15.7 890 10 7 5 3 2<br />
3 c 71 0 0 3.1 15.3 666 3, 7 71 6 71 6<br />
6 228 7 0 1.4 12.2 1568 2, 10, 16 5 51 5 3<br />
2 735 576 4 4.2 14.5 1225 1, 11 6 9 5 4<br />
5 1 2393 23 791 6 2 3 3.4 5.1 14.4 16.0 1138 874 Co 1, 19 2, 16 4 9 26 4 5 2 4<br />
8<br />
7<br />
7<br />
9<br />
8<br />
7<br />
8<br />
7<br />
4<br />
8<br />
9<br />
5<br />
SAm 541 65 14 4.4 15.8 861 3, 17, 19 7 3 4 2<br />
Unk 998 32 11 3.9 15.8 843 3, 17 7 4 6' 5<br />
SAm 137 10 12 4.3 16.1 784 3, 17 7 4 6 8<br />
Aus, NZ 323 11 8 3.8 15.7 782 3, 17 7 4 6 4<br />
SAT 146 5 11 4.6 15.8 927 3, 17 6 5 6 5<br />
SAm 67 1 11 5.1 16.1 892 3, 17 6 5, 6 5<br />
SAl 10 0 10 5.9 16.1 861 3, 4 7 4 6 5<br />
As2, Am 396 27 4 3.8 15.7 895 3, 17 6 5 6 5<br />
6 311 24 0 1.7 12.1 1940 15, 16 7 6 5 3<br />
5 c 3 0 0 0.4 11.5 1392 7 9 4 8 2<br />
3 16 0 0 2.5 12.9 1141 7, 18, 19 9 3 8 2<br />
Crop 359 6 6 4.0 16.0 787 1, 4, 17 9 3 7 6<br />
3 874 48 6 3.7 15.7 759 4 7 4 6 5<br />
4 1875 402 13 3.7 15.0 910 3, 4 7 5 6 5<br />
2 357' 33 6 4. 1 15.9 776 4 7 4 8 4<br />
3 1712 370 14 3.8 15.3 877 3, 4 71 5 71 6<br />
3 Eur? 1600 190 12 3.7 15.3 868 3, 4, 17 7 4 7 8<br />
1 109 / 5 4.4 16.4 709 Co 18, 19, 21 9 6 7 4<br />
2 1 347 165 101 63 11 5 5.1 4.5 15.4 15.7 1129 876 Co 3, 21 5 7 8 67 7 6 5<br />
2 1336 3171 14 4.1 15.6 865 16, 17 71 4, 8 5<br />
4 714 0 0 3.2 15.3 877 1 3 61 7 6<br />
6 1091 302 0 3.0 13.7 1236 11 8 8 7 3<br />
4 1011 0 7 3.8 16.0 774 3, 6, 7 7 4 7 5<br />
3 1744 583 1 3.3 14.0 1226 11 8 8 5 2<br />
3 2118 744 9 3.4 14.1 1202 10, 12, 14 8 8 3 2<br />
Eur 1753 88 11 3.6 15.2 915 1, 3, 17 6 5 6 7<br />
6 2013 644 11 3.7 14.9 986 11, 13 7 10 6 6<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
Rhiz1<br />
0<br />
Rhiz2<br />
Rhiz1<br />
Rhiz1<br />
Node2<br />
DRg<br />
Node2<br />
DRa<br />
DRg<br />
DRg<br />
Rhiz1<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
Rhiz2<br />
0<br />
0<br />
0<br />
0<br />
0<br />
Rhiz2 klieg<br />
p Th Gn<br />
a Gn Th<br />
Gn<br />
a Gn Th<br />
p Th Gn<br />
a Gn Th<br />
Gn<br />
a Gn Th<br />
Ch<br />
hc<br />
hc<br />
hc<br />
hc<br />
a hc Th<br />
Gb<br />
a hc Th<br />
Gb<br />
Gb<br />
Gb<br />
Th<br />
hc<br />
hc<br />
hc<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
hc<br />
Gn<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
Hy hc<br />
Taxon name Fam NS CS RS Chg Hght Len<br />
Ornithogalum angustifolium Li li AN : 1.05 30<br />
Ornithogalum pyrenaicum Li li N s 0.14 75<br />
Ornithopus perpusillus Faba N n -0.18 10<br />
Ornithopus pinnatus Faba N r 8<br />
Orobanche alba Orob N s -0.38 25<br />
Orobanche artemisiaecampestris<br />
Orob N EN r 60<br />
Orobanche caryophyllacea Orob N VU r 0.01 40<br />
Orobanche elatior Orob N n -0.33 75<br />
Orobanche he derae Orob N n 0.20 60<br />
Orobanche minor Orob N n -0.20 60<br />
Orobanche purpurea Orob N VU r 0.50 45<br />
Orobanche rapum-genistae Orob N s -0.35 85<br />
Orobanche reticulata Orob N r 60<br />
Odin ha s ecunda Pyro N n -0.40 5<br />
Os m unda regalis Osmu N n 0.56 160<br />
Otanthus maritimus Aste N EX x -1.49 30<br />
Oxalis acetosella Oxa N n -0.74 10<br />
Oxalis art iculata Oxa AN 25<br />
Oxalis corniculata Oxa AN 1.62 15<br />
Oxalis de bilis Oxa AN 20<br />
Oxalis exilis Oxa AN 5<br />
Oxalis incarnata Oxa AN 20<br />
Oxalis latifolia Oxa AN 20<br />
Oxalis pes-caprae Oxa AN 30<br />
Oxalis stricta . Oxa AN -0.09 40<br />
Oxyria digy na Poly N n -0.71 30<br />
Oxytropis campestris Faba N VU r. 20<br />
Oxytropis hail ed Faba N r 0.16 13<br />
Panicum mil aceum Poac AC 100<br />
Papaver argemone Papa AR -1.79 45<br />
Papaver dubium Papa AR 0.23 60<br />
Papaver hybridum Papa AR -0.35 50<br />
Papaver rhoeas Papa AR -0.41 60<br />
Papaver s om nife rum Papa AR . 2.54 100<br />
Parapholis incurva Poac N s, 0.09 10<br />
Parapholis strigosa Poac N n 0.14 25<br />
Parentucellia viscosa Scro N n 0.64 50<br />
Parietaria j udaica Urti N n1 0.08 52<br />
Paris guadrifolia Lili N n1 -0.68 40<br />
Parnassia palustris Saxi N n; -0.84 20<br />
Pastinaca sali va Apia N ni -0.39 180 b<br />
Pedicularis palustris Scro N n -0.88 60 b<br />
Pedicularis sylvatica Scro N n -1.28 25 P<br />
Pentaglottis sempervirens Bora AN , 1.81 100 p<br />
Persicaria amphibia Poly N n 0.27 60 200 p
F R N S<br />
77 6 6<br />
6 71 7<br />
CI Tja n<br />
0 3.3<br />
9 3.7<br />
10 3.7<br />
12 3.6<br />
1 3.6<br />
1 3.8<br />
0 1.6<br />
0 3.8<br />
0 2.8<br />
12 4. 1<br />
2 3.6<br />
5 5.3<br />
0 3.8<br />
5 5.3<br />
10 4.2<br />
3 4.1<br />
IR<br />
43<br />
740<br />
434<br />
934<br />
93<br />
31<br />
5<br />
145<br />
10<br />
582<br />
569<br />
0<br />
0<br />
0<br />
42<br />
0<br />
GB<br />
1355<br />
2041<br />
1881<br />
2578<br />
296<br />
203<br />
446<br />
390<br />
335<br />
1328<br />
1825<br />
6<br />
5<br />
6<br />
401<br />
482<br />
10<br />
184<br />
47<br />
2449<br />
1102<br />
80<br />
10171<br />
33<br />
219<br />
1927<br />
26<br />
2294<br />
2429<br />
2182<br />
2115<br />
3<br />
14<br />
55<br />
8<br />
1460<br />
1144<br />
1191<br />
885<br />
1343<br />
3<br />
LF2 W Clonal Clone2 E1 E2 C Origin<br />
Rhiz1 5 5<br />
0 7 6<br />
0 8 6<br />
0 7 5<br />
0 7 5<br />
0 7 3<br />
Rhizl 2 6<br />
Rhiz2 As 1<br />
Rhiz2 Eur<br />
Rhiz2 Eur<br />
Rhiz2 7 3<br />
0 8 2<br />
0 7 3 Eur<br />
0 8 3<br />
0 Crop<br />
0 8 2<br />
0 8 3<br />
0 Eur<br />
0 5 4 c<br />
Gn Rhiz2 5 6<br />
0 Eur?<br />
0 9 1 Eur<br />
Rhiz2 5 6<br />
Rhir / 2 6<br />
0 8 3<br />
0 8 3<br />
0 7 4 c<br />
0 7 4<br />
0 8 4<br />
Gn Rhiz2 6 6<br />
0 7 3<br />
w 0 1 3<br />
h 0 7 3<br />
h 0 5 3<br />
h 0 7 3<br />
w 0 4 5 c Eur, As<br />
w 0 Am4<br />
he h 0 8 3<br />
h 0 7 5<br />
h Rhiz2 Sto12 4 3 Eur<br />
h Sto12 5 3 c<br />
LF1<br />
hc<br />
Th<br />
Th<br />
Th<br />
Th<br />
Th<br />
he<br />
Gn<br />
Gn<br />
Gn<br />
Gn<br />
Th<br />
Th<br />
Th<br />
hc<br />
hc<br />
hc<br />
he<br />
he<br />
Hy<br />
Th<br />
Th<br />
Gn<br />
hc<br />
Th<br />
hc<br />
hc<br />
hc<br />
hc<br />
Hy<br />
he<br />
Ch<br />
hc<br />
hc<br />
hc<br />
Ph<br />
Ph<br />
Th<br />
hc<br />
hc<br />
hc<br />
1 P2<br />
6 8 65 7 8<br />
8 6 9<br />
6 6 2<br />
4 5 6<br />
5 5 7<br />
5 6 6<br />
7 7 7<br />
2 6 1<br />
3 5 2<br />
3 6 2<br />
4 7 5<br />
5 8 6<br />
5 8 4<br />
5 71 7<br />
ChQ Hght Len<br />
-0.44 80<br />
-0.41 75<br />
-0.04 100<br />
-0.95 80<br />
-0.06 40<br />
-0.90 75<br />
-0.58 30<br />
0.59 150<br />
0.01 70<br />
0.80 30<br />
-0.15 120<br />
50<br />
50<br />
-0.68 50<br />
-0.34 75<br />
0.12 100<br />
0.29 200<br />
0.03 100<br />
-0.07 150<br />
0.23 200<br />
-0.32 120<br />
45<br />
-0.22 40<br />
-0.30 50<br />
-0.56 17<br />
50<br />
-0.10 60<br />
150<br />
-0.33 100<br />
0.43 270<br />
0.45 60<br />
20<br />
0.07 120<br />
-0. 16 50<br />
-0.73 80<br />
4600<br />
5500<br />
0.771 80<br />
-0.06 95<br />
20<br />
13<br />
RS<br />
n<br />
n<br />
n<br />
n<br />
n<br />
s<br />
n<br />
n<br />
r<br />
n<br />
0 0 4.1<br />
21 0 2.6<br />
0 3.6<br />
6 3.6<br />
10 3.7<br />
6 4.1<br />
8 0 2.4<br />
0 -0.7<br />
6 9 4.5<br />
8 4 3.5<br />
0 3.3<br />
3 3.5<br />
10 3.5<br />
11 3.7<br />
14 3.8<br />
0 -1.1<br />
0 5.4<br />
0 3.9<br />
0 4.1<br />
2 3.2<br />
1 3.2<br />
10 3.9<br />
8 3.8<br />
6 4 3.4<br />
0 3.5<br />
n<br />
r<br />
9 7 5 7<br />
4 7 6<br />
5 6 5<br />
6 4 4<br />
5 6 4<br />
3 5 3<br />
s<br />
n<br />
75<br />
6<br />
n<br />
s<br />
n<br />
n<br />
r<br />
n<br />
n<br />
n<br />
n<br />
r<br />
r<br />
s<br />
r<br />
Taxon name Fam NS CS<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
AN<br />
AN<br />
N<br />
N EN<br />
AN CR<br />
N<br />
AR<br />
N<br />
N<br />
AR<br />
N<br />
N<br />
AN<br />
AN<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N VU<br />
N VU<br />
N<br />
NA VU<br />
AN<br />
AN<br />
AR<br />
N<br />
AN<br />
N<br />
-C.<br />
G.%<br />
43 78 4 2<br />
5 71 6<br />
Br Habitats<br />
6<br />
11, 13, 14<br />
4, 11<br />
3, 4<br />
13, 14<br />
13, 14<br />
7, 15<br />
3<br />
1, 3<br />
3<br />
14<br />
19<br />
8<br />
8, 19<br />
3, 17<br />
3, 4<br />
19<br />
5<br />
11<br />
11, 14<br />
3, 17<br />
4, 17<br />
1, 16<br />
11, 15<br />
19<br />
3, 6<br />
8<br />
3, 6<br />
3, 6<br />
11<br />
1, 16<br />
10, 15<br />
1, 10<br />
7<br />
1, 3<br />
2<br />
2<br />
3, 4<br />
7<br />
3, 17<br />
3, 16<br />
Prec Co<br />
1021<br />
1093<br />
958<br />
1077<br />
1003<br />
780<br />
1588<br />
1149<br />
1000<br />
941<br />
1002<br />
774 Co<br />
613<br />
774<br />
819<br />
751<br />
599 Co<br />
1127<br />
631<br />
1044<br />
856<br />
760<br />
1515<br />
1770<br />
918 Co<br />
942<br />
621<br />
1023<br />
1047<br />
1055<br />
1048<br />
1829<br />
1279<br />
806<br />
826<br />
1054<br />
1223<br />
795<br />
781<br />
985<br />
1153<br />
Tjul<br />
14.8<br />
14.8<br />
15.1<br />
14.6<br />
15.2<br />
15.9<br />
12.2<br />
14.8<br />
13.9<br />
15.3<br />
14.8<br />
16.7<br />
16.5<br />
16.7<br />
15.8<br />
16.2<br />
16.7<br />
13.5<br />
16. 1<br />
14.6<br />
15.5<br />
15.9<br />
13.1<br />
10.8<br />
15.3<br />
15.1<br />
16.2<br />
14.8<br />
14.7<br />
14.7<br />
14.8<br />
10.6<br />
15.5<br />
16.3<br />
16.4<br />
14.7<br />
14.1<br />
15.9<br />
16.0<br />
14.9<br />
11.5<br />
10 5 7 6<br />
67<br />
71<br />
78<br />
93<br />
54 73 5 2<br />
5 4 4<br />
4 8 3<br />
5 6 5<br />
6 3 4<br />
7 2 2<br />
5 71 6<br />
12<br />
21<br />
2<br />
b<br />
4 86 3 2<br />
4 7 4<br />
5 6 3<br />
n<br />
n<br />
4 7 4<br />
16<br />
1153<br />
11.5<br />
0 3.5<br />
3<br />
h Sto12 4 1<br />
hc<br />
13<br />
r<br />
NE VU<br />
4 7 2<br />
3<br />
7<br />
786<br />
1094<br />
14.9<br />
14.5<br />
0 3.0<br />
12 3.5<br />
89<br />
72<br />
2629<br />
h Sto12 Eur<br />
h Sto12 7 3<br />
hc<br />
hc<br />
13<br />
-0.59 12<br />
n<br />
AN<br />
N
CI Tja n<br />
12 5.2<br />
3 3.6<br />
0 3.6<br />
0 3.6<br />
0 3.0<br />
0 5.1<br />
0 3.9<br />
0 3.0<br />
2 3.3<br />
6 3.7<br />
0 0.8<br />
2 4.0<br />
14 4.1<br />
14 3.5<br />
14 3.5<br />
8 3.8<br />
0 3.5<br />
1 3.5<br />
0 3.4<br />
0 0.6<br />
6 3.7<br />
14 3.5<br />
6 4.6<br />
1 3.1<br />
2 3.6<br />
0 -0.6<br />
0 1.1<br />
5 3.4<br />
13 5.9<br />
5 3.2<br />
2 3.7<br />
10 3.5<br />
2 3.6<br />
11 3.6<br />
0 1.9<br />
14 6.3<br />
1 2.8<br />
0 3.7<br />
11 3.4<br />
3.5<br />
3.6<br />
3.1<br />
1.2<br />
1 3.7f<br />
3.7<br />
1 3.6<br />
IR<br />
0<br />
24<br />
109<br />
391<br />
0<br />
74<br />
309<br />
484<br />
116<br />
25<br />
0<br />
10<br />
303<br />
985<br />
975<br />
405<br />
0<br />
308<br />
251<br />
2<br />
0<br />
985<br />
0<br />
3<br />
0<br />
0<br />
0<br />
297<br />
0<br />
0<br />
12<br />
928<br />
423<br />
903<br />
0<br />
0<br />
0<br />
0<br />
717<br />
665<br />
0<br />
0<br />
0<br />
480<br />
819<br />
906<br />
GB<br />
11<br />
312<br />
584<br />
1938<br />
1<br />
0<br />
500<br />
1523<br />
444<br />
1009<br />
65<br />
137<br />
1445<br />
2804<br />
2766<br />
1295<br />
1243<br />
949<br />
1163<br />
72<br />
83 1<br />
2792<br />
72<br />
169<br />
1063<br />
8<br />
62<br />
1865<br />
54<br />
1960<br />
132<br />
2766<br />
1637<br />
2721<br />
16<br />
16<br />
18<br />
153<br />
2150<br />
2176<br />
268<br />
48<br />
10<br />
19371<br />
2030<br />
2605<br />
Origin<br />
Clone2 El E2 C<br />
5 2<br />
7 2<br />
7 3<br />
' 7 4<br />
1 4<br />
7 1<br />
7 1<br />
4 6<br />
W Clonel<br />
h Sto12<br />
h Rhiz2<br />
h 0<br />
h 0<br />
h O<br />
h O<br />
h o<br />
h 0<br />
w 0<br />
w 0<br />
w 0<br />
0<br />
0<br />
Rhiz1<br />
0<br />
0<br />
Rhiz1<br />
0<br />
0<br />
0<br />
Rhiz2<br />
0<br />
0<br />
0<br />
Rhiz2<br />
0<br />
0<br />
Rhiz2<br />
0<br />
0<br />
0<br />
Rhiz2<br />
Rhiz2<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
Rhiz2<br />
Rhiz2<br />
Rhiz2<br />
0<br />
0<br />
0<br />
LF2<br />
LF1<br />
hc<br />
Hy<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
Ph<br />
Ph<br />
Ph<br />
Th<br />
hc<br />
hc<br />
he<br />
hc<br />
hc<br />
Gn<br />
Gn<br />
hc<br />
hc<br />
Th<br />
hc<br />
hc<br />
hc<br />
hc<br />
hc<br />
he<br />
Th<br />
he<br />
he<br />
hc<br />
hc<br />
hc<br />
hc<br />
Th<br />
Ch<br />
Ch<br />
Ch<br />
Ch<br />
Gn<br />
Gn<br />
Gn<br />
Th<br />
Th<br />
Th<br />
1 P2<br />
Hght Len<br />
9<br />
10 10<br />
100<br />
70<br />
5<br />
8<br />
3<br />
8<br />
2500<br />
4200<br />
3000<br />
200<br />
6<br />
15<br />
15<br />
15<br />
6<br />
40<br />
50<br />
40<br />
70<br />
20<br />
35<br />
100<br />
50<br />
22<br />
40<br />
30<br />
10<br />
75<br />
100<br />
58<br />
75<br />
70<br />
90<br />
25<br />
10<br />
10<br />
15<br />
25<br />
80<br />
40<br />
80<br />
20<br />
30<br />
30<br />
Chg<br />
0<br />
0<br />
-0.03<br />
-0.16<br />
-0.31<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
0<br />
2<br />
0<br />
0<br />
3<br />
0<br />
0<br />
0<br />
0<br />
0<br />
1<br />
R N<br />
8 2<br />
4 2<br />
7 6<br />
7 3<br />
8 2<br />
4 2<br />
4 2<br />
6 2<br />
5 2<br />
5 2<br />
2 2<br />
7 7<br />
6 4<br />
6 4<br />
6 7<br />
6 4<br />
7 3<br />
6 2<br />
71 4<br />
7 3<br />
7 5<br />
6 7<br />
5 2<br />
6 5<br />
7 4<br />
3 2<br />
6 3<br />
6 4<br />
5 5<br />
6 5<br />
7 6<br />
6 5<br />
6 5<br />
6 6<br />
7 6<br />
6 4<br />
9 1<br />
8 2<br />
2 2<br />
6 3<br />
7 6<br />
7 3<br />
5 5<br />
71 6<br />
6 7<br />
7 6<br />
F<br />
3<br />
10<br />
5<br />
4<br />
8<br />
8<br />
8<br />
8<br />
5<br />
3<br />
6<br />
4<br />
6<br />
5,<br />
5<br />
7<br />
4<br />
6<br />
5<br />
5<br />
5<br />
5<br />
3<br />
5<br />
4<br />
5<br />
5<br />
6<br />
4<br />
5<br />
9<br />
5<br />
5<br />
6<br />
5<br />
4<br />
6<br />
3<br />
71<br />
5<br />
5<br />
3<br />
5<br />
5<br />
51<br />
5<br />
L<br />
8<br />
8<br />
7<br />
71<br />
9<br />
7<br />
8<br />
8<br />
7f<br />
7<br />
7<br />
7<br />
8<br />
71<br />
7<br />
8<br />
8<br />
6<br />
5<br />
7<br />
7<br />
7<br />
8<br />
5<br />
9<br />
6<br />
7<br />
8<br />
8<br />
4<br />
7<br />
7<br />
7<br />
7<br />
5<br />
9<br />
9<br />
7<br />
8<br />
8<br />
4<br />
5<br />
4<br />
71<br />
7<br />
7<br />
Br Habitats<br />
7, 16<br />
13<br />
6<br />
7<br />
11<br />
10, 12<br />
10, 11<br />
11, 12<br />
2<br />
1, 2, 17, 19<br />
2<br />
3, 4<br />
3, 6, 18<br />
6, 7<br />
3, 5<br />
15, 21<br />
7<br />
1, 10<br />
1, 6<br />
15<br />
7, 8<br />
3, 4, 5, 6<br />
19<br />
1<br />
3<br />
15, 16<br />
15, 16<br />
6, 19<br />
3<br />
1<br />
11, 13, 14<br />
3, 5, 6, 7<br />
3, 5, 6, 7<br />
1, 3, 6<br />
16<br />
3, 4, 17<br />
7<br />
7<br />
8, 10, 12<br />
7<br />
1<br />
1, 16<br />
1<br />
3, 4<br />
4, 17<br />
3, 4, 17<br />
Prec Co<br />
871<br />
1040<br />
819<br />
958<br />
752<br />
1270<br />
1475<br />
1305<br />
1302<br />
889<br />
1930<br />
896<br />
1065<br />
1105<br />
1102<br />
1248 Co<br />
804<br />
1235<br />
1147<br />
2142<br />
790<br />
1105<br />
741 Co<br />
959<br />
850<br />
1907<br />
2252<br />
1134<br />
935<br />
1015<br />
948<br />
1102<br />
1017<br />
1095<br />
1246<br />
923<br />
1037<br />
783<br />
1200<br />
1114<br />
829<br />
1091<br />
1061<br />
1008<br />
1039<br />
1073<br />
Tjul<br />
16,1<br />
14.8<br />
15.5<br />
15.0<br />
13.6<br />
14.7'<br />
13.7<br />
13.6<br />
14.0<br />
15.5<br />
11.7'<br />
15.6<br />
14.8<br />
14.5<br />
14.5<br />
14.0<br />
15.6<br />
14.3<br />
14.7<br />
11.5<br />
15.8<br />
14.5<br />
16.4<br />
14.5<br />
15.6<br />
10.5<br />
11.6<br />
14.3<br />
16.3<br />
14.8<br />
15.2<br />
14.5<br />
14.8<br />
14.5<br />
13.9<br />
16.3<br />
15.0<br />
16.2<br />
14. 1<br />
14.4<br />
16.0<br />
15.1<br />
13.1<br />
14.9<br />
14.8<br />
14.6<br />
-0.83<br />
-0.76<br />
RS<br />
e<br />
S.<br />
n<br />
n<br />
x<br />
o<br />
n<br />
n<br />
Am4<br />
Eur<br />
0.40<br />
'<br />
s.<br />
Eur<br />
4 5<br />
0 3<br />
8 4<br />
8 4<br />
6 5<br />
3 4<br />
7 5<br />
5 5<br />
7 3<br />
DRi 1 6<br />
8 6<br />
6 4<br />
DRi 8 4<br />
0.16<br />
1.35<br />
0.09<br />
-0.28<br />
-0.79<br />
-1.67<br />
-0.88<br />
-0.31<br />
hc<br />
p<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n<br />
n1<br />
s<br />
ni<br />
e<br />
s:<br />
0.83<br />
0.63<br />
-0.05<br />
0.21<br />
7 3<br />
1 3<br />
2 6<br />
7 ?<br />
9 1<br />
5 6<br />
5 6<br />
6 6<br />
6 6<br />
Nodel 6 4<br />
5 4 c<br />
9 1<br />
5 3 c<br />
8 1<br />
7 2<br />
7 3<br />
7 3<br />
7 5<br />
4 3<br />
6 5<br />
6 6<br />
6 6<br />
n.<br />
r :<br />
s<br />
n.<br />
s'<br />
n<br />
n.<br />
n<br />
n<br />
r<br />
r '<br />
r ,<br />
n.<br />
n<br />
n<br />
n<br />
s<br />
r<br />
Taxon name Fam NS CS<br />
N VU<br />
N<br />
N<br />
N<br />
NA EX<br />
N<br />
N<br />
N<br />
AN<br />
AN<br />
N<br />
AC<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
N<br />
N VU<br />
N<br />
N<br />
N<br />
N<br />
AN<br />
N<br />
N<br />
N<br />
N<br />
NA<br />
N VU<br />
N<br />
N<br />
N<br />
N<br />
N<br />
N VU<br />
AR<br />
N<br />
N<br />
Eur<br />
-0.48<br />
NHem<br />
1.33<br />
0.27<br />
-1.55<br />
0.60<br />
1.10<br />
1.17<br />
-0.04<br />
-0.10<br />
-0.37<br />
-0.50<br />
-1.14<br />
0.27<br />
0.34<br />
-0.70<br />
n:<br />
n1<br />
I
Taxon name Fam NS CS RS Chg_ Hght Len P1 P2 LF1 LF2 W Clonal Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Polygonum boreale Poly N $ 20 a Th 0 4 2 109 0 0 3.6 12.4 1084 4 7 5 6 0<br />
Polygonum maritimum Poly N EN r 0.21 20 p Ch 0 9 1 16 1 4 6.0 16.2 950 Co 19 9 3 4 3<br />
Polygonum oxyspermum Poly N n 0.01 20 a Th 0 6 3 305 75 9 4.6 14.8 1102 Co 19 9 6 8 3<br />
Polygonum runvagum Poly AR 20 a Th 0 7 3 274 0 4 3,9 16. 1 738 4 8 4 5 0<br />
Polypodiurn cambricum Poly N n 40 P hc Gn Rhizl 9 1 196 157 1 4.4 15.1 1102 3, 16 6 5 3 0<br />
Polypodiurn inte rje ctum Poly N n 40 p hc Gn Rhizl 7 2 1188 487 12 3.9 14.9 1074 1, 3, 16 5 5 3 0<br />
Polypodium vulgare Poly N n 40 P hc Gn Rhizl 5 3 1795 523 1 3.5 14.3 1158 1, 3, 16 5 5 3 0<br />
Polypodiurn vulgare sens.lat Poly N n -0.03 40 p hc Gn Rhir l 6 3 2496 916 12 3,5 14.4 1133 1 5 5 3 0<br />
Polypogon rnonspeliensis Poac N $ 0.60 80 a Th 0 9 1 45 0 0 4.3 16.6 661 6 8 8 6 3<br />
Polystichum aculeaturn Dryo N n 0.54 60 p hc 0 7 5 1618 314 3 3.2 14.4 1145 1, 16 5 5 5 0<br />
Polystichurn fonchitis Dryo N n -0.76 30 p hc 0 4 6 181 20 0 1.4 12.1 1857 7, 15, 16 6 5 3 0<br />
Polystichurn setiferurn Dryo N n 1.47 120 p hc 0 9 2 1249 748 10 4,1 15.0 1032 1 4 5 6 0<br />
Populus alba Sail AN 2000 p Ph w Root Eur, As 1 1531 116 10 3.6 15.3 867 3, 17, 19 6 6 6 0<br />
Populus alba x tremula (P. x I<br />
cane s ce ns) Sali AN 0.97 3000 p Ph w Root Eur 1145 110 7 3.8 15.6 819 1, 3 6 6 5 0<br />
Populus nigra sens.lat Sali N n 0.65 3000 p Ph w Root 7 4 692 66 2 3.6 15.7 800 3, 14 6 8 7 0<br />
Populus tremula Sall N n 0.88 2000 p Ph w Root 5 5 2248 414 7 3.3 14.5 1102 1, 16 6 5 6 0<br />
Potarnogeton acutifolius Pota N VU r 0.05 100 p Hy DRa 7 3 35 0 0 4.0 16.4 702 13 7 12 6 0<br />
Potamogeton alpinus Pota N n 0.30 280 p Hy lrreg DRa 4 6 5371 142 1 3.1 14.1 1188 13 71 12 5 1<br />
Potamogeton be rchto ldii Pota N n 1.66 60 p Hy DRa 5 6 1461 317 3.6 14.7 1027 13, 14 7 12 5 0<br />
Potarnogeton co/oratus Pota N s 0.03 70 p Hy Meg Rhiz2 8 3 142 140 4.1 15.1 893 13 7 11 5 0<br />
Potamogeton compressus Pota N s -1.68 90 p Hy DRa 5 5 134 0 3.4 15.9 697 13 7 12 4 -<br />
Potamogeton crispus Pota N n 150 p Hy Rhiz2 DRa 8 5 1541 358 3.7 15.2 893 13, 14 7 12 6 /<br />
Potamogeton epihydrus Pota N VU r 0.11 190 p Hy lrreg DRa 5 0 2 0 4.5 13.0 1288 13 8 12 / 0<br />
Potamogeton filiformis Pota N s 0.63 30 p Hy Rhiz2 DRg 4 6 161 63 3.6 13.3 1109 13 7 12 5 1<br />
Potamogeton friesii Pota N $ -1.06 150 p Hy DRa 5 6 270 43 3.6 15.4 782 13 7 12 5 0<br />
Potamogeton gramineus Pota N n 0.67 80 p Hy lrreg Rhiz2 5 6 473 163 3.3 13.8 1170 13, 14 7 12 3 0<br />
Potamogeton grarnineus x<br />
lucens (P. x zizii) Pota NH S 120 p Hy Meg Rhiz2 100 92 3.5 14.3 1138 13, 14 7 12 4 0<br />
Potamogeton grarnineus x<br />
perfoliatus (P. x nite ns) Pota NH n 250 p Hy Irreg Rhiz2 216 113 3.5 13.6 1257 14 7 12 5 1<br />
Potarnogeton lucens Pota N n 0.25 250 p Hy Irreg Rhiz2 7 4 456 171 I 3.7 15.5 832 13, 14 7 12 6 0<br />
Potarnogeton natans Pota N n 100 p Hy Irreg Rhiz2 5 6 2340 648 6 3.5 14.5 1091 11, 13, 14 7 11 4 0<br />
Potamogeton nodosus Pota N r -0.18 250 p Hy Me g Rhiz2 8 6 15 0 0 3.9 16.4 761 14 6 12 5 0<br />
Potamogeton obtusifolius Pota N n 0.96 190 p Hy DRa 5 6 601 155 0 3.4 14.7 994 13 7 12 5 0<br />
Potarnogeton pectinatus Pota N n 230 p Hy Rhiz2 DRg 6 6 1165 242 4 3.8 15.3 844 13, 14 6 12 7 2<br />
Potarnogeton perfoliatus Pota N n 300 p Hy Meg Rhiz2 5 6 1056 275 0 3.5 14.6 1026 13, 14 7 12 5 1<br />
Potam ogeton polygonifolius Pota N n 10 70 p Hy hc Irreg Rhiz2 7 2 1841 582 5 3.3 13.9 1254 11, 12, 13 8 10 2 0<br />
Potamogeton praelongus Pota N n -0.26 300 p Hy lrreg Rhiz2 4 6 252 90 0 3.2 14.1 1178 13 7 12 5 1<br />
Potamogeton pusillus Pota N n 0.77 70 p Hy DRa 8 6 806 146 1 3.6 15.1 877 13 7 12 6 1<br />
Potamogeton rutilus Pota N r 0. 18 45 p Hy DRa 4 3 13 0 0 3.8 12.9 1115 13, 14 7 12 5 0<br />
Potarnogeton trichoide s Pota N n 0.57 100 p Hy DRa 8 4 185 0 1 3.8 16.2 739 13, 14 6 12 6 0<br />
Potentil la anglica Rosa N n 0.11 25 p hc Sto12 7 3 1248 733 4 4.0 15.0 1045 6 7 5 5 0<br />
Potent) Ila ans erina Rosa N n -0.23 25 p hc Sto12 5 6 2662 973 12 3.6 14.6 1083 6 8 7 6 2<br />
Potentilla argentea Rosa N n -0.78 30 p hc 0 7 4 323 0 5 3.6 16.0 704 3, 8 8 3 2 0<br />
Potent" Ila crantzir Rosa N s -0.21 20 p hc 0 2 4 98 0 0 0.7 12.0 1855 7, 16 8 5 2 0<br />
Co
,<br />
Taxon name Fam NS CS RS Chg Fight Len 1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N S<br />
Potent/ ha erecta Rosa N n -0.50 25 hc h 0 5 4 2700 947 12 3.5 14.4 1118 8 7 7 3 2<br />
Potentilla fruticosa Rosa N r 1.44 100 Pn w 4 6 8 7 0 2.8 13.7 1366 16 8 6 8 2<br />
Potentilla ne um anniana Rosa N s -0. 17 10 hc h 0 7 3 128 0 0 3.1 14.7 994 7, 16 7 3 8 1<br />
Potentilla palustris Rosa N n -0.21 50 Gn Hy h Rhiz2 5 6 1672 721 'I 3.4 14.0 1186 11 8 9 5 3<br />
Potentilla reptans Rosa N n -0.62 30 hc h Sto12 8 4 1882 769 11 3.8 15.1 959 6 71 5 7i 5<br />
Potent/ Ila rupestris Rosa N VU r 60 hc h 0 9 3 4 01 0 3.0 13.8 934 16 7 4 6 2<br />
Potentilla sterilis Rosa N n -0.30 15 hc h Stoll 7 2 2167 742 8 3.6 14.7 1071 1 5 5 5 5<br />
Primula elatior Prim N s 0.01 20 hc h 0 7 3 c 38 0 0 3.3 16.3 591 1 4 5 7 6<br />
Primula farinosa Prim N s -0.46 5 hc h 0 4 5 103 0 0 2.2 13.8 1194 7, 11 9 8 9 2<br />
Primula scotica Prim NE e -0.18 5 hc h 0 4 1 42 0 0 3.6 12.4 1026 Co 6, 19 9 4 71 2<br />
Primula veris Prim N n -0.32 15 hc h 0 7 4 1632 369 6 3 7 15.2 900 6, 7 7 4 7 3<br />
Primula vulgaris Prim N n 0.16 15 hc h 0 7 3 2651 934 11 3.5 14.5 1108 1, 16 5 5 6 4<br />
Prune lla vulgaris Lami N n 0.60 30 hc h Nodel 6 6 2783 970 14 3.5 14.4 1106 6, 7 7 5 8 4<br />
Prunus avium Rosa N n 1.29 2500 Ph w Root 7 3 2136 431 7 3.4 14.8 1024 1 4 5 6 6<br />
Prunus cerasifera Rosa AN 3.43 800 Ph w Eur, As 1 900 11 4 3.7; 15.8 803 1, 3, 17 6 5 7 6<br />
Prunus cerasus Rosa AR 0.90 800 Ph w Root Eur 706 339 7 3.9 15.2 961 1, 3 6 5 6 5<br />
Prunus domestica Rosa AR 2.19 800 Ph w Root Eur 1656 406 8 3.7 15.2 928 3, 17 7 5 7 6<br />
Prunus laurocerasus Rosa AN 4.70 600 Ph w Eur 1253 345 4 3.8 15.3 953 1, 17 4 6 5 6<br />
Prunus lusitanica Rosa AN , 800 Ph w Eur 468 31 1 3.8 15.5 876 1, 17 6 5 7 6<br />
Prunus padus Rosa N n 0.58 1500 Ph w 5 5 1089; 189 2.71 13.8 1240 1 5 6 6 71<br />
Prunus spinosa Rosa N n 0.40 400 Ph w Root 7 3 23081 917 3.7 14.8 1032 3 6 5 7 6<br />
Pseud<strong>of</strong>umaria lutea Furna AN 0.59 30 hc h 0 Eur 1425 39 3.6 15.4 876 3, 17 6 6 8 5<br />
-le<br />
C . Ps e udorchis albida Orch N n -0.88 20 Gn h 0 4 3 385 110 2.6 13.0 1534 7, 8 8 5 6 2<br />
Pseudotsuga menziesii Pina AN ! 5800 Ph w Am4 900 13 3.4 15.0 1035 1, 2, 17 6 6 4 4<br />
Pteridium aquilinum Denn N n -0.71 150 Gn Rhiz2 7 6 2685 964 / 3.5 14.5 1109 1, 9 6 5 3 3<br />
Puccinellia dis tans Poac N n 3.02 60 hc 0 5 4 405 39 4.1 14.9 859 3, 21 8 8 7 7<br />
Puccinellia fasciculata Poac N s -0.51 50 hc 0 8 2 97 11 4.5 16.4 722 6 8 7 7 7<br />
Puccinellia maritima Poac N n -0.27 80 hc Node2 5 1 788 201 4.1 14.4 1162 Co 21 9 8 7 6<br />
Puccinellia rupestris Poac N s -0.40 40 b Th hc 0 8 1 148 0 4.5 16.2 756 Co 6, 19 9 7 7 5<br />
Pulicaria dysenterica Aste N n -0.08 80 hc Rhiz2 8 4 14971 391 1 4.0 15.5 885 6, 11 71 71 7 4<br />
Pulicaria vulgaris Aste N VU r -0.551 45 Th 0 7 4 121 0 4.0 16.5 696 8 9 8 6 7<br />
Pulmonaria longifolia Bora N s -0.01 40 hc 0 7 1 21 0 4.7 16.5 810 1, 3 6 4 6 5<br />
Pulmonaria obscura Bora N VU r,<br />
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1 0 3.2 16. 1 577 1<br />
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Pulmonaria <strong>of</strong>i cinalis Bora AN<br />
1.77 30<br />
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0 7 3 c Eur<br />
682 8 3.4 15.3 922 1, 3, 17 5 5 8 6<br />
Pulsatilla vulgaris Ranu N s -0.50 30 hc 0 7 3 c 691 0 3.3 16.0 664 7 71 3 8 3<br />
Pyrola media Pyro N 5 -1.09 10 hc Rhizl 4 4 258 47 2.2 13.0 1197 2, 10 5 4 5 2<br />
Pyrola rninor Pyro N n -0.55 7 hc Ch Rhizl 4 6 558 50 2.6 13.9 1089 1, 16 5 5 4 2<br />
Pyrola rotun difolia Pyro N s' -0.08 12 hc Rhizl 5 4 155 13 2.9 14.2 1072 2, 19 6 7 7 3<br />
Pyrus communis sens.lat Rosa AR 1.49 1500 Ph w Root Eur?, As l ? 781 6 3.8 15.9 801 1, 3, 17 7 5 6 7<br />
Pyrus cornm unis sens.str. Rosa AR 1500 Ph w Root Gard 3, 17 7l 5 6 71<br />
Pyrus cordata Rosa NA EN r 400 Ph w Root 7 1 9 0 5.4 15.9 1129 3 6 5 5 4<br />
Quercus cerris Faga AN 2.32 3500 Ph w Eur 1247 42 1 3.8 15.6 862 1, 3, 17 6 4 6 6<br />
Quercus ilex Faga AN ' 2.37 2500 Ph w 9 1 Eur 802 22 1 4.1 15.9 824 1, 17, 19 6 3 7 4<br />
Quercus petraea Faga N e 0.14 3000 Ph w 7 3 1832 549 3.5 14.6 1136 1 6 6 3 4 0<br />
Quercus robur Faga N n -0.60 3000 Ph w 7 3 2310 663 1 3.5 14.71 1049 1, 3 71 5 5 4 0<br />
Radio/a linoides Lina N n -0.87 6 a Th h 0 7 3 548 115 I I 4.2 14.7 1061 10 8 7 4 2 1<br />
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Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Ranunculus acris Ranu N n 0.30 - 75 p hc 0 3 5 2780 968 13 3.5 14.4 1106 6 6 4<br />
Ranunculus aquatilis Ranu N n 90 a Hz 0 Irreg 7 3 1123 157 4 3.6 15.2 860 13, 14 1 7 5<br />
Ranunculus aquatilis sens.lat Ranu N n -1.37 90 a Hz 0 Irreg 6 3 1830 430 6 3.6 15.3 860 13, 14 1 7 5<br />
Ranunculus arvensis Ranu AR -3.771 60 a Th 0 8 4 824 2 3 3.7 15.9 742 4 7 6<br />
Ranunculus auncomus Ranu N n -0.33 40 p hc 0 5 3 1379 226 1 3.3 15.1 922 1 6 5<br />
Ranunculus baudotii Ranu N n -0.04 60 a Hz 0 Node2 8 3 361 61 5 4.4 15.3 905 13 1 7 6<br />
Ranunculus bulbosus Ranu N n -0.48 40 p hc 0 6 3 2259 616 14 3.6 14.8 1004 6, 7 7 4<br />
Ranunculus circinatus Ranu N n -0.34 75 p Hy Irreg 7 5 575 76 0 3.7 15.8 753 13, 14 1 7 7<br />
Ranunculus ficaria Ranu N n 0.16 25 p Gn Otb DRa 8 3 2648 820 14 3.6 14.5 1084 1, 3 6 6<br />
Ranunculus flammula Ranu N n -0.60 50 p hc Hy Nadel 7 3 2651 938 11 3.5 14.4 1122 11 5 3<br />
Ranunculus fluitans Ranu N n 1.96 300 p Hy 1rreg Node2 7 3 373 3 0 3.3 15.4 798 14 1 7 6<br />
Ranunculus he derace us Ranu N n 0.10 9 23 a p Hz Hy 0 Node2 8 2 1703 551 8 3.6 14.5 1093 11, 13 1 5 5<br />
Ranunculus lingua Ranu N n 1.70 120 p hc Hy Rhiz2 7 4 537 210 0 3.7 15.2 868 11 1 6 7<br />
Ranunculus muricatus Ranu AN 40 a Th 0 0 3 Eur 18 1 0 5.0 15.6 864 4 5 5<br />
Ranunculus omiophyllus Ranu N n 0.52 9 25 a p Hz Hy 0 Node2 8 2 813 151 1 3.7 14.7 1180 11 1 5 4<br />
Ranunculus ophioglossifolius Ranu N EN r 40 a Th 0 8 3 4 0 2 4.9 16.5 824 13 7 5<br />
Ranunculus paludosus Ranu N o 40 p he Rhizl 9 1 0 0 4 6.1 16.9 843 6 6 3<br />
Ranunculus parviflorus Ranu N n -0.08 40 a Th 0 6 2 497 0 11 4.3 16.0 834 6 6 5<br />
Ranunculus peltatus Ranu N n 90 a Hz 0 Irreg 6 3 990 151 5 3.5 15.2 908 11, 13, 14 I l 5 6<br />
Ranunculus penicillatus Ranu N n 180 p Hy Irreg 7 3 706 284 0 3.8 15.2 942 14 1 8 5<br />
Ranunculus repens Ranu N n 0.55 60 p hc Sto12 5 5 2784 983 14 3.5 14.5 1105 3, 6 6 7<br />
Ranunculus reptans Ranu N EN r 10 p hc Hy Sto12 4 6 9 0 0 2.6 13.7i 1467 13 6 2<br />
Ranunculus sardous Ranu NA n 0.24 45 a Th 0 7 3 544 0 12 4.1 15.9 800 3, 6, 13 6 7<br />
Ranunculus sceleratus Ranu N n -0.05 60 a Th 0 5 6 1492 353 6 3.8 15.4 861 11, 13, 14 8 8<br />
Ranunculus trichophy llus Ranu N n -0.07 60 a Hz 0 Wag 3 6 1121 259 6 3.7 15.2 861 11, 13 1 6 6<br />
Ranunculus tripartitus Ranu N VU s -1.09 9 25 a p Hz 0 8 1 79 1 0 5.2 15.8 1024 13 1 6 3<br />
Raphanus raphanistrum Bras N n -1.39 70 a p Th hc 0 8 3 1862 259 13 4.6 15.0 1079 4, 19 6 6<br />
Raphanus raphanistrum<br />
subsp.maritimus Bras N 80 b p hc 0 9 1 325 108 13 4.7 15.1 1093 19 7 5<br />
Raphanus raphanistrum<br />
s ubsp.raphanistrum Bras AR 60 p he 0 8 3 1797 237 8 3.6 15.0 941 4 6 6<br />
Reseda lutea Rese NA n 0.39 75 hc 0 8 3 1276 0 7 3.6 15.7 808 3 7 5<br />
Reseda luteola Rese AR 0.69 150 hc 0 8 4 1660 428 12 3.8 15.3 879 3, 17 8 6<br />
Rhamnus cathartica Rham N n -0.04 600 Ph 0 7 4 857 88 0 3.6 15.8 783 1, 3 7 6<br />
Rhinanthus angustifolius Scro AN -0.10 60 a Th 0 5 4 Eur, As 1 90 0 0 3.1 14.6 809 3, 4, 7 7 2<br />
Rhinanthus minor Scro N n -0.49 50 a Th 0 5 3 2629 850 6 3.5 14.4 1115 6 6 4<br />
Rhodode ndron ponticum Eric AN 1.83 500 Ph 0 Nadel Eur 1966 507 6 3.5 14.6 1111 1, 10, 16 3 3<br />
R hynchospora alba Cype N n -0.43 30 hc Rhizl 5 6 624 407 0 3.6 14.0 1400 12 2 1<br />
R hy nch osp ora fusca Cype N s 0.02 30 hc Rhiz2 5 2 46 94 0 4.4 14.7 1205 12 3 1<br />
Ribes alpinum Gros N s 0.45 200 Pn Ph 0 4 3 50 0 0 2.3 14.2 1084 1, 3, 16 8 6<br />
R ibe s nigrum Gros AN 1.76 200 Pn 0 5 4 Eur, As1 1749 213 2 3.4 14.9 995 1, 3, 14 6 6<br />
Ribes rubrum Gros NA n 1.79 200 Pn 0 7 2 1874 0 2 3.3 15.1 944 1 7 6<br />
Ribes spicatum Gros N 5 -0.12 200 Pn 0 5 3 c 118 0 0 2.0 13.2 1095 1, 16 7 6<br />
Ribes uva-crispa Gros AN 0.72 100 Pn 0 7 3 Eur 2130 312 4 3.4 14.8 1006 1, 3 7 6<br />
Robinia pseudoacacia Faba AN 2700 Ph Root Am6 566 1 4 3.7 16.0 748 3, 17 6 6<br />
Romulea columnae hi d N VU r 6 Gn Otb 9 1 2 0 14 6.2 16.5 842 Co 18, 19 5 2
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Taxon name Fam NS CS RS Chg Hght Len<br />
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Taxon name Fam NS CS RS Chg Hght Len 1 P2 LFI LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan T'ul Prec Co Br Habitats L F R N<br />
Samolus valer<strong>and</strong>i Prim N n -0.42 45 hc 0 8 6 845 411 12 4.3 15.1 1013 11 8 8 8 5<br />
Sanguisorba minor Rosa N n -0.16 50 hc 0 8 4 1216 84 6 3.7 15.6 844 7 7 4 8 3<br />
Sanguisorba <strong>of</strong>fi cinalis Rosa N n -0.23 120 hc 0 5 6 946 12 0 3 2 15.1 938 6 7 7 6 5<br />
Sanicula europaea Apia N n -0.98 40 hc o Rhizl 7 3 2025 634 0 3.5 14.7 1090 1 4 5, 7 5<br />
Saponaria <strong>of</strong>ficina(is Cary AR 0.29 90 hc Rhiz2 7 3 1246 256 9 3.9 15.5 890 3, 17 8 5 6 6<br />
Sarcocornia perennis Chen N s -0.22 30 Ch 0 9 1 80 4 1 4.4 16.4 702 Co 21 9 8 8 6<br />
Saussurea alpina Aste N n -0.51 45 hc Stoll 1 5 237 21 0 1.6 11.9 20 10 7, 15, 16 8 6 6 3<br />
Saxifraga aizoides Saxi N n -0.61 20 Ch Node2 1 3 422 17 0 1.7 12.3 1799 7, 11, 15, 16 8 9 6 2<br />
Saxifraga cernua Saxi N VU r 15 hc DRa DRi 1 6 5 0 0 0.5 11.7 2265 15, 16 6 6 7 1<br />
Saxifraga cespitosa Sax/ N VU r -0. 10 10 Ch 0 1 6 13 0 0 -0.4 10.7 2003 15, 16 71 5 71 1<br />
Saxifraga granulate Saxi N n -0.26 36 hc DRa 7 3 975 6 0 3 1 15.1 853 6, 7 8 5 6' 4<br />
Saxifraga hirculus Saxi N VU r -0.30 20 hc Rhiz/ 2 6 20 16 0 2.4 13.2 1253 11 8 9 6 2<br />
Saxifraga hirsuta Saxi N o 1.39 30 hc Stoll 7 1 0 36 0 5.0 14.6 1334 1, 15, 16 6 7 5 2<br />
Saxifraga hypnoides Saxi N n -0.54 20 Ch Node2 4 1 406 61 0 2.0 12.8 1697 7, 15, 16 7 5 6 3<br />
Saxifraga nivalis Saxi N s -0.50 15 hc 0 1 6 72 1 0 0 6 11.5 2099 15, 16 6 6, 71 3<br />
Saxifraga oppositifolia Saxi N n -0.45 3 Ch Node2 1 6 276 22 0 1.8 12.1 1980 7, 15, 16 8 6 8 2<br />
Saxifraga rivularis Saxi N r 0.19 10 hc Rhizl DRa 1 6 21 0 0 -0.3 10.8 1941 11, 15 6 9 5 2<br />
Saxifraga rosacea Saxi N EW x 20 Ch 0 4 2 2 31 0 4.4 14.3 1312 16 7 4 8 4<br />
Saxifraga spathularis Saxi N o 40 hc Ch Stoll 7 0 0 137 0 4.7 14.4 1328 16 6 8 3 2<br />
Saxifraga stellaris Saxi N n -0.58 20 hc Ch o 1 3 440 61 0 1.8 12.3 1811 11, 15, 16 8 8 5: 3<br />
Saxifraga tridactylites Saxi N n -0.12 10 Th 0 8 3 985 316 11 3.9 15.3 921 16 7 2 7 2<br />
Scabiosa columbaria Dips N n -0.71 70 hc 0 7 3 804 0 0 3,5 15.6 831 7 8 3 8 2<br />
Sc<strong>and</strong>ix pecten-veneris Apia AR -3.65 50 Th 0 8 4 780 94 6 3.8 15 7 792 4 7 4 7 4<br />
S che uchz e ria palustris Sche N VU r 22 hc Rhiz2 4 6 c 14 1 0 2.2 13.9 1380 12 9 9 3 1<br />
Schoenoplectus lacustris Cype N n 0 .47 2 10 Hy Rhizl 6 4 1202 535 0 3.7 14.9 1013 13. 14 8 11 71 6<br />
Schoenoplectus pungens Cype NA r 60 Hy Rhizl 7 3 0 0 1 6.1 16.7 869 Co / 9 8 10 7 7'<br />
Schoenoplectus<br />
tabemaemontani Cype N n 0.67 150 Hy Rhizl 8 5 702 192 4.2 15.3 917 11, 13 9 10 8 7<br />
Schoenoplectus ttigueter Cype N CR r 125 Hy Rhizl 7 5 8 3 4.7 16.5 799 14 8 10 7 7<br />
Schoenus ferw gineus Cype N VU r 40 hc o 4 3 3 0 0 4 12.4 1113 11 8 9 7 2<br />
Schoenus nigricans Cype N n -0.53 75 hc 0 8 4 763 484 3.9 13.9 1261 11 8 8 71 2<br />
Scilla autumnatis Lili N s -0.37 20 Gb Otb 9 1 49 0 1 5.9 16.2 939 Co 10, 18 9 3 6/ 1<br />
Scilla Verna Lili N n 0.12 10 Gb Otb DRg 7 1 310 29 4.6 13.9 1103 6, 10 8 5 5 3<br />
Scirpoides holos choenus Cype N VU r 0.21 100 hc 0 8 4 3 0 5.2 16.3 909 Co 19 8 8 7 6<br />
Scirpus sylvaticus Cype N n 0.02 120 hc Rhizl 7 4 871 102 3.4 15.2 921 1, 11 6 8 6 6<br />
S cleranthus annuus Cary N n -2.68 20 Th 0 7 3 983 69 3.6 15.2 883 4, 8, 10, 16 71 4 4 4<br />
S cleranthus perennis Cary N EN r -0.11 20 Ch o 7 3 11 0 3 3 16.0 656 8, 16 81 3 4 2<br />
Scorzonera humilis Aste NA VU r 50 hc 0 7 3 4 0 4 8 16. 1 1097 6 8 7 5 2<br />
Scrophularia auriculata Scro N n -0.21 120 hc 0 8 2 1490 504 3.9 15.4 918 11, 14 7 8 7 7<br />
Scrophularia nodos a Scro N 6 -0.37 100 hc 0 7 4 2327 850 3.6 14.7 1069 1, 3 5 6 7 6<br />
Scrophularia s corod onia Scro AN , 0.75 100<br />
hc<br />
0 8 1 Eur 68 0 1 5.8 16.0 1033 3, 16, 18 71 4 6 6<br />
Scrophularia umbrosa Scro N n 0.72 100<br />
hc<br />
0 7 4 c<br />
196 14 3.1 14.9 868 1, 14<br />
7 9 7 7<br />
Scrophularia vernalis Scro AN . 0.54 65 p hc 0 Eur 192 0 3.3 15.3 769 1, 3 5 5 7 7<br />
Scutellaria galericulate Lami N n -0.39 50 hc Rhizl 5 4 1751 212 3.6 14.9 1055 11 7 8 6 5<br />
Scutellaria minor Lami N 6 0.03 20 hc Rhizl 8 2 803 136 4.1 14.9 1191 11 7 9 4 2<br />
Secale cereale Poac AC , 150 Th 0 Eur 134 71 4.0 15.8 852 3, 4 8 5 71 7<br />
/
Taxon name Fam NS CS RS Chg Hght Len 1 P2 LF1 LF2 W Clone') Clone2 El E2 C Origin GB IR CI T an T ul Prec Co Br Habitats L F R N S<br />
Sedum acre Cras N n -0.24 10 Ch Node2 Irreg 7 3 2108 504 12 3.7 14.9 995 16 8 2 7 2 1<br />
Sedum album Cras AR 2.41 20 Ch Node2 Irreg 9 2 1603 517 13 3.8 15.1 948 3, 16, 17 8 3 6 2 0<br />
Sedum anglicum Cras N n -0.21 5 Ch Node2 Irreg 7 1 988 393 14 4. 1 14.3 1321 16, 18 8 3 4 2<br />
Sedum forsterianum Gras N s 1.54 20 Ch Node2 Irreg 8 1 122 0 0 3.6 14.8 1239 3, 16 7 3 5 1<br />
Sedum rosea Cras N n -0.41 35 hc 0 1 6 524 82 0 21 12.6 1728 15, 16 7 6 6 3<br />
Sedum rupestre Gras AN 2.20 30 Ch Node2 Irreg Eur 1212 70 4 3.7 15.5 905 3, 16 7 2 5 4<br />
Sedum telephium Cras N n -0.34 60 hc 0 7 5 1197 0 0 3.5 15.0 1032 1, 3, 16 7 5 7 5<br />
Sedum villosum Cras N s -0.76 10 Ch 0 2 3 211 0 0 1.6 12.9 1273 11 8 9 6 2<br />
Selaginella selaginoides Se la N n -0.47 9 Ch Nodal 4 6 988 288 0 2.8 13.0 1443 7, 11 8 7 6 2<br />
Selinum carvifolia Apia N VU r 100 hc 0 7 3 3 0 0 3.4 16.1 595 11 7 7 8 4<br />
Sempervivum tectorum Cras AN 40 Ch Stoll Eur 500 42 2 3.5 15.3 871 3, 17 8 2 4 1<br />
Senecio aquaticus Aste N n -0.92 80 p hc 0 7 3 2304 919 1 3.6 14.5 1109 11, 14 7 8 6 5<br />
Senecio cambrensis Aste NE r 30 hc 0 7 1 14 0 0 3.6 15.0 804 3, 17 8 5 7 7<br />
Senecio cineraria Aste AN<br />
2.73 60<br />
Ch Pn sw 0<br />
0 3 Eur 256 8 5 4.4 15.9 837 3, 17, 18, 19 9 3 7 3<br />
Senecio erucifolius Aste N n -0.03 120<br />
hc<br />
Rhizl<br />
7 4<br />
1276 30 0 3.8 15.8 783 3, 6<br />
7 5 7 5<br />
Senecio fluviatilis Aste AN<br />
0.03 150<br />
hc<br />
Rhiz2<br />
7 4 Eur, As l 184 25 0 3.3 14.6 1018 1, 11, 13, 14 7 8 6 7<br />
Senecio j acobaea Aste N n 0.11 125<br />
b hc<br />
0 Root 7 4<br />
2725 982 14 3.6 14.5 1102 3, 6, 7, 8 7 4 6 4<br />
Senecio paludosus Aste N CR r 175 hc 0 7 4 c 7 0 0 3.4 16.2 573 11, 13 7 9 7 6<br />
Senecio smithii Aste AN 100 hc 0 SAm 62 0 0 3.4 12.3 1072 3, 6 8 7 6 7<br />
Senecio squalidus Aste AN 0.771 50 a p Th Ch 0 Gard 1494 75 4 3.7 15,5 850 3, 17 8 4 7 7<br />
Senecio sylvaticus Aste N n 0,09 70 a Th 0 7 3 1853 238 12 3.6 14.9 987 2, 8, 9 7 5 5 6<br />
Senecio viscosus Aste AN 0.63 60 a Th 0 7 3 Eur 1747 69 1 3.4 15.1 920 3, 17, 19 8 5 7 6<br />
Senecio vulgaris Aste N n -1.08 37 a Th 0 8 3 2630 942 14 3.6 14.6 1075 3, 4, 17 7 5 7 7<br />
Serapias parviflora Orch NA r 30 p Gn 0 9 1 1 0 0 6.0 16.2 1048 6 8 4 7 3<br />
Seriphidium maritimum Aste N n -0.42 50 p Ch hc Rhiz2 7 2 222 20 1 4.3 15.8 783 Co 21 9 7 8 6<br />
Serratula tinctoria Aste N n -0.21 70 p hc 0 7 3 945 0 2 3.8 15.5 965 7 7 6 6 2<br />
Seseli libanotis Apia N VU r 60 b hc 0 7 5 c 4 0 0 3.7 16.4 645 7 7 4 8 3<br />
Sesleria caerulea Poac N s -0.09 45 p he 0 5 3 76 89 0 3.1 13.9 1262 7, 16 7 6 8 2<br />
Setaria viridis Poac AN 0.80 70 a Th 0 Unk 431 27 5 3.9 15.9 798 3, 4, 17 7 4 7 7<br />
Sherardia arvensis Rubi N n -0.94 40 a Th 0 8 3 1635 369, 12 3.9 15.2 916 7, 16 7 4 6 4<br />
Sibbaldia procumbens Rosa N s -0.75 5 p hc 0 1 6 133 0 0 0.4 11.3 2109 15 8 5 4 3<br />
Sibthorpia europaea Scro N s -0.14 5 p Ch Node2 7 1 107 9 8 5.3 15.5 1189 3, 14 5 7 5 5<br />
Silaum silaus Apia N n -0.42 100 p hc 0 7 4 963 0 0 3.6 15.8 743 6 8 5 7 4<br />
Silene acaulis Cary N n -0.47 10 p Ch 0 1 3 236 9 0 1.9 11.8 1937 7, 15, 16 8 5 6 1<br />
Silene conica Cary N $ -1.05 35 a Th 0 5 4 59j 0 10 4.0 16.0 702 8, 19 8 3 4 2<br />
Silene dioica Cary N n -0.44 90 hc Ch 0 5 3 2514 263 14 3 4 14.6 1065 1 5 6 6 7<br />
Silene gallica Cary AR -2.78 45 a Th 0 9 2 455 31 11 4,2 15.7 877 3, 4 7 4 5 5<br />
Silene latifolia Cary AR -0.88 100 p hc 0 8 4 1954 211 13 3.6 15,1 911 3 7 4 7 6<br />
Silene noctiflora Cary AR -2.04 50 a Th 0 7 3 686 22 1 3.7 15.8 736 4 7 4 7 6<br />
Silene nutans Cary N $ -0.39 80 p hc 0 7 4 52 0 10 4.3 15.7 883 16 5 3 8 4<br />
Sfi ene <strong>of</strong>i tes Cary N r -0.36 80 p hc 0 7 3 c 18 0 0 3.2 16.1 625 3, 8 8 3 7 2<br />
Silene uniflora Cary N n -0.39 28 p hc 0 5 2 943 236 13 4.0 14.1 1263 Co 18 8 6 6 4<br />
Silene vulgaris Cary N n -1.26 80 p hc 0 8 5 1710 280 8 3.7 15.3 897 3, 6 7 4 8 5<br />
Silybum marianum Aste AR -0.07 100 b a hc Th 0 0 3 Eur 552 64 6 4.0 15.8 781 3 8 4 8 6<br />
Simethis planifolia Lili N o 42 p Gn 0 5 2 0 4 0 5.7 15.1 1324 10 71 5 4 3<br />
Sinapis alba Bras AR -0.90 90 a Th 0 8 3 1082 162 10 3.8 15.5 832 3, 4 7 4 7 6
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Cb nel Clone2 El E2 C Origin GB IR CI Tian Tjul Prec Co Br Habitats L F R N S<br />
Sinapis aneensis Bras AR , -1 76 90 a Th h 0 7 4 2373 772 11 3.7 14.7 1012 3, 4, 17 8 5 7 7'<br />
Sison amomum Apia N n -0.19 100 b hc h 0 9 2 790 0 0 3.9 16.2 756 3 7 4 7 5<br />
Sisymbrium altissimum Bras AN -0,84 100 a Th h 0 Eur 614 29 3 3.7 15.6 771 3, 17 8 5 6 4<br />
Sisymbrium <strong>of</strong>i cinale Bras AR i -0.21 95 a b Th hc h 0 8 3 21171 775 13 3.8 15.0 973 3, 4, 17 71 4 7 7<br />
Sisymbrium orientale Bras AN -0.24 80 Th h 0 Eur 864 75 10 3.8 15.6 815 3, 17 7' 4 7 5<br />
Sisyrinchium be rm udiana Irid N o -1.80 23 hc h 0 6 0 0 43 0 4.5 14.4 1290 6, 13 8 8 6 3<br />
Sium latifolium Apia N s -1.83 200 Hy h 0 7 4 259 34 0 3.7 15.9 702 11, 14 7 10 7 7<br />
Smyrnium olusatrum Apia AR 0.66 150 he h 0 Eur 803 327 13 4.4 15.5 907 3 T 5 7 7<br />
Solanum dulcamara<br />
So la N n -0.11 225<br />
Pn Ch sw Node2<br />
8 5<br />
1918, 533 14 3.8 15.2 945 3, 11, 14 71 8 71 7<br />
Solanum nigrum<br />
So la NA n 0.44 60<br />
Th<br />
0<br />
8 5<br />
1258E 0 14 3.9 15.9 809 4<br />
7 5 7 8<br />
Solanum sarachoides So la AN 60 a Th 0 SAm 88 0 4 3.8 16.1 696 4, 17 7 4 7 7<br />
Solanum tubemsum So la AN 100 Gn Rhiz1 SAm 625 56 5 3.9 15.4 883 4 7 4 6 7<br />
So leiro lia soleirolii Urti AN 2.36 10 Ch Node2 0 2 Eur 773 130 11 4.3 15.7 906 3, 17 4 8 7 6<br />
Solidago canadensis Aste AN 200 hc Rhiz1 Am 981 24 3.6 15.6 833 3, 17 8 5 6 6<br />
Solidago gigantea Aste AN 200 hc Rhiz1 Am 645 1 3.5 15.5 854 3, 17 8 5 5 6<br />
Solidago virgaurea Aste N n -0.89 70 he 0 5 5 2043 492 3.4 14.2 1217 10, 16 5 5 4 3<br />
Sonchus arvensis Aste N n -0.12 150 hc Rhiz2 7 4 2320 806 3.8 14.8 1013 4 8 6 7' 6<br />
Sonchus asper Aste N n 0.78 150 a Th 0 8 3 2584 961 1 3.7 14.6 1070 3, 4 T 5 7 6<br />
Sonchus oleraceus Aste N n -0.42 150 Th 0 8 3 2358 924 1 3.71 14.8 1031 3, 4 71 5 71 71<br />
Sonchus palustris Aste N s, 0.18 250 he 0 7 4 51 0 3.8 16.4 615 11 7 8 7 7'<br />
Sorbus anglica Rosa NE VU r 200 Pn w 0 7 1 14 1 3.8 15.2 1082 1, 16 6 4 8 4<br />
Sorbus aria Rosa N n 1500 Ph w 0 7 3 225 2 3.8 16.3 774 1 6 4 7 4<br />
u-i<br />
u, Sorbus aria agg, Rosa N n' 0.82 1000<br />
Ph w 0<br />
7 3<br />
341 75 3.8 16.3 780 17<br />
6 5 7 4<br />
Sorbus arrane nsis Rosa NE VU r<br />
750<br />
Ph w 0<br />
4 1<br />
1 0 2.5 12.1 1530 16<br />
71 4 4 3<br />
Sorbus aucuparia Rosa N n 0.86 1500 Ph w 0 5 5 2472 749 3.4 14.4 1128 1, 2, 16 6 6 3 4<br />
Sorbus bristoliensis Rosa NE EN r , 1000<br />
Ph w 0<br />
7 1<br />
1 0 4.4 16.5 844 1, 16<br />
6 4 8 4<br />
Sorbus de von iensis Rosa NE s , 1500<br />
Ph w 0<br />
7 1<br />
32 11 5.0 15.4 1171 1, 3<br />
6 5 6 5<br />
Sorbus domestica Rosa N CR r 1 500<br />
Ph w Root<br />
3<br />
4 0 4.5 16.5 857 16<br />
6 4 8 3<br />
Sorbus e minens<br />
Rosa NE VU r 600<br />
Ph w 0<br />
7<br />
8, 0 4.4 16.2 878 1<br />
6 5 71 5<br />
Sorbus hibernica<br />
Rosa NE o 600<br />
Ph w 0<br />
7<br />
0' 63 4.5 14.6 1035 1, 3, 16 6 5 7 5<br />
Sorbus intermedia Rosa AN 1000 Ph w 0 Eur 686 17 3.5 15.2 901 1, 3, 17 6 6 8 7<br />
Sorbus lanc as triensis Rosa NE r 500 Ph w 0 7 9 0 3.3 14.8 1285 16 8 4 7 3<br />
Sorbus leptophylla Rosa NE CR r 300 Pn Ph w 0 7 3 0 2.9 14.5 1501 16 5 5 7 5<br />
Sorbus leyana<br />
Rosa NE CR r<br />
200<br />
Pn w 0<br />
7<br />
2 0, 2.5 14.0 1687 16<br />
7 5 8 4<br />
Sorbus minima<br />
Rosa NE VU r ' 300<br />
Pn Ph w 0<br />
7<br />
1 0' 2.2 14.0 1523 16<br />
6 4 8 3<br />
Sorbus porrigentiformis Rosa NE 5 , 500<br />
Ph w 0<br />
7<br />
30 0 3.8 15.2 1273 16<br />
7' 5 7' 5<br />
Sorbus ps e udotennica Rosa NE VU r<br />
700<br />
Ph w 0<br />
4<br />
1 0 2.5 12.1 1530 16<br />
7 4 4 3<br />
Sorbus rupicola Rosa N s 200 Pn w 0 4 2 98 13 2.9 13.6 1405 16 8 4 7 3<br />
Sorbus subcuneata<br />
Rosa NE VU r 1000<br />
Ph w 0<br />
7 1<br />
4, 0 4.0 14.9 1380 1<br />
6 5 4 4<br />
Sorbus torminalis<br />
Rosa N n 0.22 1900<br />
Ph w Root<br />
7 3<br />
573 0 3.9 16.0 804 1<br />
4 5 6 5<br />
Sorbus vexans Rosa NE VU r 600 Ph w 0 7 1 4 0 4.2 14.9 1409 1, 16 6 5 4 4<br />
Sorbus wilmottiana Rosa NE CR r 600 Ph w 0 7 1 1 0 4.4 16.5 844 1, 16 6 4 8 3<br />
Sparganium angus tifolium Spar N n 1.66 100 Hy h Rhiz2 4 3 652 207' 3.0 12.9 1571 13 8 11 4 2<br />
Sparganium emersum Spar N n 0.61 60 Hy h Rhiz2 5 6 1426 393 3.6 15.0 982 13, 14 7 11 7 6<br />
Sparganium erectum Spar N n 0.48 150 Hy h Rhiz2 7 6 2129 766 3.7' 14.9 1000 11, 13 7' 10 7 7<br />
Sparganium natans Spar N n : -0.13 50 Hy h Rhiz2 5 6 508 267 3.3 13.8 1303 13 7 11 6 3
S<br />
Taxon name Fam NS CS RS Chg_ Hght Len P1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tian Tjul Prec Co Br Habitats L F R N<br />
Spartina alternitiora Poac AN -0.22 110 p hc Rhiz2 Am 12 0 0 4.1 15.7 760 Co 21 9 9 8 7<br />
Spartina anglica Poac NE n 0.11 130 p hc Rhiz2 7 1 251 71 1 4.6 15.7 904 Co 21 9 9 8 6<br />
Spartina maritima Poac N s -0.55 50 p hc Rhiz2 8 2 571 0 0 4.1 16.6 625 Co 21 9 9 8 5<br />
Spergula arvensis Cary N o -2.30 30 a Th 0 6 4 0 0 9 6.3 16.7 811 4 7 4 5 5<br />
Spergularia bocco ne i Cary AN -0.22 10 a Th 0 9 1 Eur 18 0 9 5.9 16.3 901 16, 17, 19 9 4 6 7<br />
Spergularia marina Cary N n 1.83 10 a Th 0 8 6 680 185 8 4.3 14.6 1094 Co 3, 21 8 8 8 6<br />
Spergularia media Cary N n -0.24 15 p Ch 0 8 4 659 186 0 4.2 14.6 1125 Co 21 8 8 8 5<br />
Spergularia rubra Cary N n 0.05 15 a Th 0 8 3 1363 66 13 3.5 14.9 983 8, 17 8 3 4 2<br />
Spergulatia rupicola Cary N n 0.30 10 Ch 0 7 0 239 169 13 5.2 15.1 1105 Co 18 9 6 6 5<br />
Spiranthes aestivalis Orch N EX x 40 hc 0 7 3 1 0 2 5.6 16.5 822 11 9 8 8 2<br />
Spiranthes romanz <strong>of</strong>fi ana Orch N s 0.45 25 hc 0 4 0 21 44 0 4.4 14. 1 1248 11 8 8 6 4<br />
Spiranthes spiralis Orch N n -0.95 15 hc 0 8 3 655 117 13 4.4 15.9 884 7 8 4 6 3<br />
Spirodela polyrhiza Lemn N n -0.18 0.8 Hy Frag 8 6 535 991 2 3.9 15.9 768 13 71 11 7 7<br />
Stachys alpina Lami AN 100 hc 0 7 3 Eur 3 0 0 3.1 14.7 1007 1, 3 7 5 8 7<br />
Stachys arvensis Lami AR -1.17 25 Th 0 8 2 1418 206 13 4.0 15.3 964 3, 4 8 5 5 5<br />
Stachys germanica Lami N EN r -0.27 80 hc 0 7 3 10 0 0 3.4 16. 1 66 1 3 7 3 8 5<br />
Stachys <strong>of</strong>ficinalis Lami N n -0.62 60 he 0 7 3 1571 38 4 3.6 15.4 940 6, 7 7 5 5 3<br />
Stachys palustris Larni N n 0.01 100 Gn Rhiz2 5 6 2346 919 9 3.71 14.6 1079 11, 14 7 8 7 7<br />
Stachys palustris x sylvatica<br />
(S. x ambigua) Lami NH n 100 hc Rhiz2 1020 1171 4 3.5 14.7 1086 3, 14 7 6 6 6<br />
Stachys sylvatica Lami N n -0.49 100 hc Rhiz2 7 4 2462 806 12 3.6 14.7 1064 3 6 6 7 8<br />
Stellaria graminea Cary N n -0.02 80 hc Rhizl 5 4 2446 852 8 3.5 14.6 1065 6 7 6 5 4<br />
i n<br />
cn Stellaria holostea Cary N n -0.56 60 Ch Rhiz1 Nodel 7 4 2372 671 7 3.5 14.7 1058 1 5 5 6 6<br />
Stellaria media Cary N n 50 Th 0 Nodel 6 5 2749 962 14 3.6 14.5 1095 3, 4 7 5 6 7<br />
Stellaria nemorum Cary N n 0.21 60 hc Rhizl 5 3 432 0 0 2.7 14.2 1027 1, 14 4 6 6 7<br />
Stellaria media egg. Cary N n 0.03 50 Th 0 Nodal 6 5 2749 962 14 3.6 14.5 1095 3, 4 7 5 5 6<br />
Stellaria neglecta Cary N n 0.42 80 Th 0 Nodel 7 3 775 4 0 3.9 15.6 911 1, 3 6 7 6 7<br />
Stellaria pallida Cary N n 1.17 50 Th 0 Nodel 8 4 593 27 13 4.0 15.8 766 3, 19 7 4 4 4<br />
Stellaria palustris Cary N n -0.89 60 hc Rhizl Nodel 5 5 389 73 1 3.6 15.5 793 11 7 8 6 4<br />
Stellaria uliginosa Cary N n -0.10 40 he Rhizl 7 3 2570 798 9 3.5 14.4 1128 11, 14 7 8 5 5<br />
Stratiotes ab ides Hydr NA r 1.65 50 Hy Stoll DRa 5 4 c 65 0 0 3.5 16.1 596 13 7' 11 7 6<br />
Suaeda maritima Chen N n -0.47 30 Th 0 8 5 525 141 6 4.3 14.9 1094 Co 21 9 8 8 6<br />
Suaeda vera Chen N s -0.11 120 Pn w 0 9 1 47 0 1 4. 1 16.4 620 Co 19, 21 9 7 8 5<br />
Subularia aquatica Bras N n 0.73 6 Hz h 0 4 6 324 33 0 2.4 12.6 1789 13 7 11 5 2<br />
Succisa pratensis Dips N n -0.57 100 he h 0 Rhizl 7 4 2633 934 2 3.5 14.4 1124 6 7 7 5 2<br />
Symphoricarpos albus Capr AN 1.74 200 Pn w Rhiz2 Am 2067 744 4 3.6 14.9 992 1, 3, 17 5 5 6 7<br />
Symphytum asperum x<br />
<strong>of</strong> icinale (S. x upl<strong>and</strong> icum) Bora AN 135 hc h 0 Eur 1924 399 8 3.6 15.0 952 3 6 5 7 7<br />
Symphy tum <strong>of</strong>ficinale Bora N n 0.34 135 hc h 0 7 3 1263 189 10 3.7 15.4 871 11 7 7 7 8<br />
- -<br />
Symphytum orientale Bora AN 1.83 70 hc h 0 Eur 442 2 3 3.71 16.0 719 3 6 4 7 6<br />
Symphytum tuberosum Bora N n 0.11 55 hc h 0 7 3 407 0 0 2.5 13.5 1047 1, 3 6 6 6 6<br />
Sybnga vulgaris Olea AN 4.48 700 Ph w Rhir l Eur 1296 163 4 3.6 15.3 881 3, 17 6 5 6 5<br />
Tamus communis Dios N n -0.41 400 Gn h 0 9 2 1421 0 4 3.8 15.7 850 1, 3 6 5 7 6<br />
Tanacetum parthenium Aste AR 0.23 54 Ch hc h 0 Eur 2126 413 11 3.5 14.9 980 3, 17 7 4 7 6<br />
Tanacetum vulgare Aste N n -0.23 120 hc h Rhizl 5 5 2004 0 10 3.5 15.0 958 3 7 6 7 7<br />
Taraxacum Aste N n 0.43 30 hc h 0 6 6 2778 974 14 3.5 14.5 1104 3, 5, 17 7 5 7 6
W Clonel Clone2 El E2 C Origin GB IR CI Tja n Tjul Prec Co Br Habitats L F R N S<br />
w 0<br />
7 3 1881 260 7 3 5 15.1 976 1 4 4 7 5 0<br />
h 0<br />
7 3 509 11 12 3 4 15.0 949 8 8 3 2 2 0<br />
h 0<br />
Am4 308 20 2 3.6 15.2 974 1, 3, 17 3 8 6 4 0<br />
h 0<br />
3 6 c 99, 0, 0 3 71 16. 1 774 7 71 3 8 3 0<br />
h 0<br />
3 6 26 0 0 3.6 16. 1 617 13 7 9 7 6 0<br />
h 0<br />
7 3 c Eur 12 0 0 3.6 16.3 767 3, 4, 7, 16 9 2 8 2 0<br />
sw Rhizl<br />
8 3 c Eur 72 2 0 4.2 15.7 856 3, 7, 16 8 2 8 1 0<br />
h Rhiz2<br />
8 4 24 12 I 4.0 15.8 740 11, 13, 14 7 8 8 4 1<br />
h Rhiz2<br />
8 2 2322 588 1 3.5 14.5 1150 1, 9, 16 6 4 4 3<br />
h Rhiz2<br />
1 6 409' 23 2.0 12.1 1845 7, 11, 15, 16 8 7 6 3<br />
h 0<br />
5 4 669 91 3.7 15.8 762 11 7 8 7 5<br />
h Rhiz2<br />
5 5 504 89 3.4 14.0 1185 16, 19 7 4 6 3<br />
h Rhiz2<br />
7 6 171 54 3.9 15.5 869 1, 11 6 8 7' 5<br />
h 0<br />
7 1 145 0 3 6 16.2 762 7 8 3 8 3<br />
h 0<br />
7 5 1600 143 1 3 7 15.3 858 3, 4 7 4 7 6<br />
h 0<br />
4 3 70 0 2 0 13.5 1314 16 8 4 6 1<br />
h 0<br />
8 4 9 0 3,3 16.0 732 3, 16 8 4 8 2<br />
w 0<br />
Am4 574 7 1 3.6 15.4 977 2, 17 4 5 5 4<br />
sw Node2<br />
5 3 2246 486 1 3.4 14.2 1175 7, 16 8 4 6 2<br />
sw Node2<br />
7 3 455 3 3.7 16. 1 752 7 8 4 8 2<br />
sw Node2<br />
5 3 c 9 0 3,3 16.2 606 8 8 2 5 2<br />
w 0<br />
7 4 896 5 20 0 2.4 3 5 15.5 14.4 1064 873 1 5 5 6 5 6<br />
R<br />
B<br />
B<br />
B<br />
C<br />
L<br />
T<br />
7 3 84 0 3.3 15.6 816 1 4 5 7 6<br />
1 6 156 0 0 6 11.6 1964 7, 11 8 9 7 2<br />
Am4 267 11 3.2 14.3 1131 1 3 6 7 7<br />
Eur 11 1 4.0 16.3 739 6 7 3 6 5<br />
8 4 389 0 3.7 16.2 707 4 8 4 8 4<br />
7 5 2178, 824 3.71 14.9 1004 3 7 5 7 71<br />
9 1 708 77 4. 1 15.9 792 3, 6 8 5 7 6 1<br />
7 4 1749 124 1 3.6 15.3 87 1 6 8 4 7 5 0<br />
DRp 7 0 162 62 3.8 14.2 1390 16 2 7 7 3 0<br />
4 6 c 1 0 2.8 14.0 858 12 8 9 2 2 0<br />
4 6 1553, 629 0 3.2 13.71 1312 10, 12 8 8 2 1 0<br />
DRg 4 6 514 0 0 1,8 12.6 1277 1, 2, 10 5 6 3 3 0<br />
8 4 1205 56 14 3.8 15.5 84 1 8 9 3 5 2 1<br />
9 1 3 0 2 6 5 16.2 867 16 9 4 5 2 0<br />
8 4 1996 381 14 3.7 15.1 939 3, 16, 19 8 4 6 4 0<br />
7 3 2548 942 14 3 6 14.6 1072 6 71 4 6 5, 0<br />
8 4 7531 42 6 4.0 16.0 764 6 8 7 7 6 2<br />
9 1 148 5 13 4.6 16.3 767 8 9 3 5 2 0<br />
Eur 1940 214 11 3.5 15.0 943 3, 5 7 5 7 6 0<br />
9 1 3 0 4 6.4 16.4 883 3, 18 8 2 5 2 1<br />
w 0<br />
w 0<br />
h Rhizl<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h Rhizl<br />
h Rhizl<br />
h Ogr<br />
h Rhiz2<br />
h 0<br />
h 0<br />
h 0<br />
h 0<br />
h Node2<br />
h 0<br />
h 0<br />
h 0<br />
h<br />
T<br />
T<br />
Crop 196 1 5 4.0 16. 1 780 3 7 4 6 5 0<br />
h O
Taxon name Fam NS CS RS Chg Hght Len P1 P2 LF1 LF2 W Clonal Clone2 El E2 C Od in GB IR CI T an T uI Prec Co Br Habitats I. F R N S<br />
Trifolium incamatum<br />
subsp.molinerti Faba N VU r 20 Th 0 9 1 3 0 4 6 4 16.4 883 Co 18 6 2 51 2<br />
Trifolium medium Faba N n -0.53 45 hc 0 5 4 2050 208 2 3.4 14.8 1008 6 7 4 6 4<br />
Trifolium micranthum Faba N n 0.62 7 Th 0 9 2 909 52 13 4.1 15.9 848 8, 17 8 5 5 5<br />
Trifolium occidentale Faba N a 10 hc Ch Node2 7 0 21 9 12 6.3 15.9 940 Co 18 9 4 6 2<br />
Trifolium ochroleucon Faba N s -0.84 45 he 0 7 3 1271 0 0 3.4 16.3 595 3. 6 7 5 8 2<br />
Trifolium om ithop odioide s Faba N n 0.42 12 Th 0 8 2 281 18 14 4.8 16. 1 874 8 9 6 5 3<br />
Trifolium pratense Faba N n -0.18 45 hc 0 7 4 2745 976 14 3.6 14.5 1100 6. 7 7 5 7 5<br />
Trifolium repens Faba N n 1.31 20 hc Ch Node2 5 4 2798 981 14 3.5 14.5 1105 6 7 5 6 6<br />
Trifolium scabrum Faba N n -0.39 20 Th 0 9 2 390 12 11 4.5 15.9 831 8 9 3 7 2<br />
Trifoliurn sguamosum Faba N s -0.32 40 Th 0 9 1 116 0 6 4.5 16.5 757 Co 6, 19 9 6 7 6<br />
Trifolium striatum Faba N n -0.11 20 Th 0 8 3 848 31 12 4.0 15,7 805 8 8 3 5 2<br />
Trifolium strictum Faba N VU r 15 Th 0 9 2 4 0 2 5.8 15.9 874 16 9 2 5 2<br />
Trifolium subterraneum Faba N n -0. 10 10 Th 0 9 2 337 1 13 4.5 16.2 805 8, 18 8 3 4 2<br />
Trifolium suffocatum Faba N s 0.14 5 Th 0 9 1 96 0 13 4.8 16.4 774 8 8 4 4 2<br />
Triglochin maritimum Junc N n -0.44 55 hc Rhizl 5 6 8371 251 5 4.2 14.3 1181 Co 21 8 7 7 5<br />
Triglochin palustre Junc N n -0,22 55 hc Rhiz2 5 6 2196 71 5 3.4 14.2 1145 11 8 9 6 2<br />
Trinia glauca Apia N r 0.12 20 hc 0 8 3 6 0 4.9 16.4 889 7 9 2 8 1<br />
Tripleurospermum inodorum Aste AR 60 Th 0 7 4 2119 42 12 3.6 14.9 967 4. 17 8 5 6 6<br />
Tripleurospermum maritimum Aste N n 60 Ch hc 0 3 6 757 27 3 4.4 14.5 1132 Co 18, 19 8 5 6 6<br />
Tnpleurosp ennum maritimum<br />
sens.lat. Aste N n 0.3 1 60 p Th hc 0 3 6 757i 27 3 4.4 14,5 1132 4, 17 18, 19 8 5 6 6<br />
tri<br />
co Trisetum flavescens Poac N n -0.13 80 he 0 7 3 1734 36 6 3.6 15.2 900 6, 7 7 4 7 4<br />
Triticum aestivum Poac AC 150 Th 0 Crop 741 5 4 3.8 15.6 861 3, 4 8 5 7 7<br />
Trollius europaeus Ranu N n -0.73 60 hc 0 4 3 856 0 2.2 13.0 1517 11, 16 7 7 6 4<br />
Tsuga he terophylla Pina AN 4600 Ph w 0 Am4 598 1 0 3.4 14.9 1102 1, 2, 17 6 6 3 3<br />
Tuberaria guttata Cist N VU r 15 Th h 0 9 1 5 1 4 5.71 15.5 1069 10 9 2 5 1<br />
Tussilago farfara Aste N n -0.65 30 Gn h Rhiz2 5 4 2618 90 7 3.5 14.5 1085 16 7 6 6 6<br />
Typha angustifolia Typh N n 0.35 300 Hy h Rhiz2 7 4 776 6 6 3.7 15.8 775 11 8 10 7 7<br />
Typha latifolia Typh N n 1.01 275 Hy h Rhiz2 8 6 1860 68 9 3.8 15.1 958 11 8 10 7 7<br />
Ulex europaeus Faba N n -0.34 200 Pn w 0 7 1 2518 95 14 3.6 14.6 1090 10 7 5 5 3<br />
(fl ex gallii Faba N n 0.20 150 Pn w 0 7 1 918 38 11 4.1 15.0 1099 10 7 6 3 2<br />
Ulex minor Faba N n 0.20 100 Pn w 0 8 1 197 4 3.9 16.4 745 10 8 6 1 2<br />
Ulmus glabra Ulrna N n -0.28 3000 Ph w 0 7 3 2338 60 0 3.4 14.7 1056 1 4 5 7 6<br />
Ulmus minor Ulrna N n 0.75 3100 Ph w Root 7 3 641 9 3.9 16. 1 764 1, 3 5 5 7 7<br />
Ulmus plotii Ulma NE s 2000 Ph w Root 7 1 128 0 3.4 16.0 667 3 5 5 7 7<br />
Litmus procera Ulma NA n -0.48 3300 Ph w Root 7 3 13171 0 3.7 15.8 819 3 5 5 8 6<br />
Umbilicus rupestris Cras N n -0. 12 38 hc h 0 9 1 784 65 i 14 4.3 14.9 1125 3, 16 6 4 5 4<br />
Urtica dioica Urti N n 0.28 150 hc h Rhiz2 Sto12 5 4 2773 98 13 3.6 14.5 1102 3, 14, 17 6 6 7 8<br />
Urtica urens Urti AR -0.70 60 Th h 0 8 4 1924 28 14 3.7 15.0 914 4, 17 8 5 6 8<br />
Utricularia australis Lent N s 60 Hy h DRa 5 5 162 5 0 4.0 15.0 1120 13 7 12 5 3<br />
Utricularia intermedia<br />
sens.lat. Lent N n 0.40 20 Hy h DRa 4 6 412 15 0 3.1 13.2 1545 11, 12, 13 8 12 4 2<br />
Utricularia intermedia<br />
sens.str. Lent N n 20 Hy h DRa ? ? 13 8 12 4 2<br />
Utricularia minor Lent N n 0.20 40 Hy h DRa 5 6 628 377 1 3.6 13.9 1321 11, 12 8 12 4 2
S<br />
Taxon name Fam NS CS RS Chg_ Hght Len P2 LF1 LF2 W Clonel Clone2 E1 E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N<br />
Utricularia ochroleuca Lent N i 20 Hy h DRa ? ? 11, 13 8 12 3 1<br />
Utricularia stygia Lent N i 20 Hy h DRa ? ? 11, 13 8 12 5 2<br />
Utricularia vulgaris seno lat. Lent N n 0.47 100 Hy h DRa 5 5 744 301 0 3.6 14.4 1148 13 7j 12 6 4<br />
Utricularia vulgaris sens.str. Lent N s 100 Hy h DRa 7 4 159 77 0 3.8 15.3 874 11 7 12 7 4<br />
Vaccinium microcarpum Eric N s 0.81 30 Ch h Node2 4 6 100 0 0 0.9 11.9 1339 12 7 8 1 1<br />
Vaccinium myrtillus Eric N g -0.61 50 Ch Pn w Rhiz2 4 4 1886 701 1 3.3 13.9 1243 10, 16 6 6 2 2<br />
Vaccinium oxycoccos Eric N n 0.28 30 Ch h Node2 4 6 725 246 0 3.0 14.0 1229 12 8 9 2 1<br />
Vaccinium uliginosum Eric N n -0.39 50 Ch Pn w Rhiz2 2 6 252 0 0 1.1 11.7i 1897 12, 15, 16 71 6 2 2<br />
Vaccinium vitis-idaea Eric N n -0. 18 30 Ch w Rhiz2 2 6 938 89 0 2.2 12.9 1474 2, 10, 15 6 5 2 2<br />
Valeriana dioica Vale N n -0.67 35 hc h Sto12 7 3 1171 0 0 3.2 15.3 896 11 8 8 6 3<br />
Valeriana <strong>of</strong>i cinalis Vale N n -0.64 175 hc h 0 Rhizl 5 5 2408 808 0 3.4 145 1115 11 6 8 6 5<br />
Valeriana pyrenaica Vale AN -0.35 110 hc h 0 Eur 195 8 0 2.7 13.8 1151 1, 3 5 7 5 5<br />
Va lerianella carinata Vale AR 2.15 15 Th h 0 8 3 547t 66 13 4.3 15.8 93 1 3, 17 8 4 8 4<br />
Valerianella dentata Vale AR -1.86 15 Th h 0 7 3 600 45 4 3.9 15.7 800 4 8 4 7 4<br />
Valerianella eriocarpa Vale AN -0.69 15 Th h 0 9 2 Eur 59 0 6 4.5 16.0 826 3, 16 8 3 8 3<br />
Valerianella locusta Vale N n -0.11 15 Th h 0 7 3 1358 238 9 3.9 15.3 925 3, 16, 19 8 4 6 4<br />
Valerianella rimosa Vale AR CR -2.55 15 Th h 0 7 3 181 27 0 4.3 15.9 860 4 8 4 8 3<br />
Verbascum lychnids Scro N s -0 .23 150 hc h 13 7 3 42 0 0 4.1 16.5 790 3, 7 71 3 71 3<br />
Verbascum nigrum Scro N n -0.12 120<br />
hc h 0<br />
7 4<br />
479, 0 8 3.9 16.2 742 3<br />
7 4 7 6<br />
Verbascum pulverulentum Scro NA s 0.94 135<br />
hc h 0<br />
9 2<br />
51 0 0 3.4 16.1 624 3, 16<br />
8 3 7 5<br />
Verbascum thapsus Scro N n 0.27 200 hc h 0 7 4 1874 375 12 3.7 15.2 918 3 7 4 7 5<br />
Verbascum virgatum Scro AN 0.35 100 hc h 0 8 2 Eur 339 13<br />
in<br />
3 4.2 15.8 870 3, 5, 17, 19 8 4 5 5<br />
so Verbena <strong>of</strong>i cinalis Verb AR -0.43 67 hc h 0 8 5 8571 90 10 4 1 15.8 859 3, 16 8 5 71 6<br />
Veronica agrestis Scro AR -0.38 10 a Th h 0 7 3 1715 177 9 3.5 15.0 963 3, 4, 17 7 6 6 7<br />
Veronica alpina Scro N s -0 .29 12 Ch h 0 1 4 35 0 0 -0.7 10.9 1783 15 8 6 5 2<br />
Veronica anagallts -aquabca Scro N n 0.05 50 a p Hz Hy h Nodel 8 5 1225 459 3 3.7 15.1 899 13, 14 7 10 7 7<br />
Veronica arvensis Scro N n 0.48 25 a Th h 0 8 3 2614 793 14 3.5 14.6 1077 3, 4, / 6 8 4 6 5<br />
Veronica be cca bunga Scro N n -0.31 45 Hy Ch h Nodel 7 4 2333 912 9 3.6 14.7 1034 11, 14 7f 10 6 6<br />
Veronica catenata Scro N n 0.37 50 a p Hz Hy h Nodel 7 6 956 249 4 3.8 15.6 816 13, 14 8 10 7 8<br />
Veronica chamaedrys Scro N n -0.50 30 Ch hc h Node2 5 4 2609 945 14 3.5 14.5 1095 1, 3, 6 6 5 6 5<br />
Veronica Milormis Scro AN 2.69 5 hc Ch h Node2 Eur 2013 397 9 3.6 14.9 990 3, 17 7 6 7 7<br />
Veronica froticans Scro N s 0.11 14 Ch sW 0 1 3 26 0 0 -0 .5 11.2 182 1 15, 16 8 5 7 2<br />
Veronica hecieriforia Scro AR 0.57 30 a Th h 0 8 3 1944 346 14 3.71 15.1 918 1, 3, 4, 17 6 5 7j 6<br />
Veronica m ontana Scro N n 0.48 15 Ch h Node2 7 3 1808 506 0 3.6 14.9 1029 1 4 6 6 6<br />
Veronica <strong>of</strong> icinalis Scro N n -0.84 23 Ch h Nodel 5 3 2507 754 8 3.4 14.4 1125 7, 8 6 5 4 4<br />
Veronica persica Scro AN -0.37 30 a Th h 0 Nodal Eur 2232 722 13 3.7 14.9 993 3, 4, 17 6 5 7 7<br />
Veronica polka Scro AN 0.07 10 a Th h 0 8 4 Eur, Asl 1237 107 8 3.8 15.5 867 4, 17 7 4 7 5<br />
Veronica praecox Scro AN 15 a Th h 0 8 3 c Eur 6 0 0 3.3 16.3 618 3, 4, 8 8 2 8 1<br />
Veronica scutellata Scro N n -0.06 25 hc h Nodel 5 4 1877 576 3 3.4 14.3 1129 11, 13 8 9 5 3<br />
Veronica serpyllifolia Scro N n 0.80 10 hc h Node2 5 6 2652 884 11 3.5 14.5 1104 3, 5, 11 7 5 6 5<br />
Veronica spicata Scro N s 0.13 45 hc Ch h Nodel 7 4 c 28 0 0 3.7 15.3 949 7, 16 8 3 7 2<br />
Veronica triphyllos Scro AR EN -0.82 15 a Th h 0 7 3 c 33 0 0 3.5 16.1 690 3, 4 7 4 7 3<br />
Veronica vema Scro N VU r -0.64 15 a Th h 0 7 4 c 71 0 0 3.3 16.2 618 8 8 2 5 1<br />
Viburn um lantana Capr N n 0.37 600 Ph w 0 7 3 537 0 0 3.8 16.2 763 1, 3 7 5 7 5<br />
Viburnu m opulus Capr N n -0.15 400 Ph w 0 7 6 1854 565 1 3.6 15.0 1019 1 6 7 6 6<br />
Vicia bithynica Faba N s -0.52 60 hc h 0 9 1 74 0 4 4.4 16. 1 827 3 7 4 6 4
Taxon name Fam NS CS RS Chg. Hght Len P1 P2 LF1 LF2 W Clonel Clone2 El E2 C Origin GB IR CI Tjan Tjul Prec Co Br Habitats L F R N $<br />
Vicia cracca Faba N n -0.37 120 p hc Rhir l 5 5 2647 938 10 3.6 14.5 1083 3, 11 7 6 5 0<br />
Vicia laba Faba AN 100 a Th 0 Cro 377, 5 2 3.71 16.1 734 4, 17 8 4 71 0<br />
Vicia hirsuta Faba N n 0.05 80 a Th 0 7 3 1925' 285 12 3.7 15.2 926 3, 6 7 5 6 0<br />
Vicia lathyroides Faba N n -0.36 10 a Th 0 7 3 501 27 11 3.8 15.2 808 8, 19 8 3 3 0<br />
Vicia lutea Faba N s -0.85 50 a Th 0 9 2 58 0 7 4.8 15.9 844 Co 18, 19 7 4 5 1<br />
Vicia orobus Faba N s -0.34 60 p hc 0 7 2 214 15 0 3.0 13.8 1410 16 7 5 4<br />
Vicia parvillora Faba N s -1.05 60 a Th 0 9 2 136 0 0 3.9 16.3 695 3, 4 7 5 5<br />
Vicia sativa Faba N n 0.19 90 a Th 0 8 3 1930 472 14 3.7 14.9 991 6 7 4 4<br />
Vicia sepium Faba N n -0.43 60 p hc Rhizl 5 4 2615 945 4 3.5 14.5 1095 3, 6 6 5 6<br />
Vicia sylvatica Faba N n -0.71 150 p hc Rhizl 5 4 623 57 0 3.1 14.3 1119 1, 3, 16 7 5 5<br />
Vicia tetrasperma Faba N n 0.45 60 a Th 0 7 3 1159 0 10 3.9 15.9 804 3, 4, 6 7 5 6<br />
Vicia villosa Faba AN 150 a Th 0 8 3 c Eur 147, 2 3 3.8 16.1 757 3, 4 7 4 5<br />
Vinca maj or Apoc AN 1.49 35 p Ch Tip Eur 1336 231 12 4.0 15.6 873 1, 3, 17 5 6 6<br />
Vinca minor Apoc AR 0.48 15 p Ch Node2 Eur 1359 12 8 3.7 15.3 893 1, 3, 17 4 6 7<br />
Viola arvensis \do AR -0.29 40 a Th 0 7 4 2065 33 11 3.6 15.0 940 4 8 4 6<br />
Viola canina Vio N n -0.87 18 p hc 0 5 4 1030. 18 3.5 14.7 1008 8, 10 8 4 2<br />
Viola hilt s<br />
Vio N n -0.46 15 P hc<br />
0 Rhir l 7 4<br />
964, 1 3.7 15.71 795 7<br />
7 4 2<br />
Viola kitaibeliana<br />
\do N VU r<br />
10 a Th<br />
0 8 3<br />
2<br />
6.7 16.6 814 19<br />
9 3 2<br />
Viola lactea Vio N s -1.08 15 hc 0 7 1 183 2 5.0 15.8 1025 10 7 6 2<br />
Viola lutea Vio N n -0.69 20 hc Rhiz2 4 3 536 1 2.0 13.3 1281 7, 8, 16 8 5 2<br />
Viola odorata Vio N n -0.19 15 hc Sto12 7 3 1340 9 3.8 15.7 833 7 5 5 7<br />
Viola palustris Vio N n -0.30 15 hc Rhiz2 5 3 1880 56 3.3 13.9 1262 11, 14 7 9 2<br />
a,<br />
0 Viola persicifolia Vio N EN r -0.62 25 hc 0 7 4 c 18 1 3.9 15.4 826 11 7 8 3<br />
Viola reichenbachiana Vio N n 0.20 13 hc 0 7 3 1128 28 3.8 15.5 869 1 4 6 5<br />
Viola riviniana Vio N n 1.07 18 hc 0 Root 7 3 2741 96 1 3.5 14.4 1112 1, 7, 16 6 5 4<br />
Viola rupestris Vio N r 5 hc 0 7 5 c 7 1,6 13.3 1393 7 8 3 2<br />
Vio/a tricolor Vio N n -1.52 20 p Th hc 0 7 3 1691 24 3.4 14.6 992 4, 8, 19 8 4 4<br />
Viscum album Vise N n 0.97 100 Ch Pn w 0 7 3 923 3.8 15.9 788 3, 17 7 5 5<br />
Vulpia bromoides Poac N n 0.18 37 Th 0 9 2 1777 51 1 3.8 15.0 1006 3 8 4 3<br />
Vulpia ciliata Poac N s 0.78 37 a Th 0 9 1 109 4.0 16.3 716 8 9 2 2<br />
Vulpia fasciculata Poac N s 0.37 55 a Th 0 9 1 109 1 5.0 15.8 911 Co 19 9 3 2<br />
Vulpia myuros Poac AR 1.55 62 a Th 0 8 4 1134 11 i 3.9 15.6 866 3, 17 8 3 3<br />
Vulpia unilateralis Poac AN -0.56 35 a Th 0 9 2 Eur 39 3.6 16.2 705 3, 7 9 3 2<br />
Wahlenbergia hederacea Camp N n -0.30 5 p hc Node2 8 1 314 4 4.1 14.9 1280 11, 14 6 8 3<br />
Wolfi a arrhiza Lemn N s -0.03 0.1 p Fly Frag 8 4 48 4.4 16.6 752 13 7 11 7<br />
Woodsia alpina Wood N r 0.11 8 p hc 0 2 6 22 0.4 11.6 2371 15, 16 7 4 2<br />
Woodsia ilvensis Wood N EN r -0.10 10 p hc 0 2 6 14 1.3 12.4 2108 16 7 3 2<br />
Zannichellia palustris Zann N n 0.17 50 p Hy Irreg Rhiz2 8 6 1196 20 3.8 15.5 820 13, 14 7 12 7<br />
Zea mays Poac AC 300 a Th 0 Crop 92 1 1 4.0 15.9 820 4, 17 8 3 7<br />
Zostera angustifolia Zost N s -0.68 30 p Hy Rhiz2 ? ? 131 27 6 4.3 15.0 926 Co 21 7 12 5<br />
Zostera marina Zost N n -0.86 50 p Hy Rhiz2 6 6 296 68 13 4.5 14.6 1156 Co 21, 23 6 12 6<br />
Zostera noltei Zost N s -0.51 12 p Hy Rhiz2 8 5 159, 36 4 4.2 14.9 1020 Co 21 8 11 5
A PPE NDIX<br />
Sources or Mot hei ht<br />
Plant heights have been calculated from a range <strong>of</strong> sources <strong>and</strong> have been subject to personal<br />
adjust ment . The main sources were Clapham,Tut in & Warburg ( 1962), Stace ( 1991, 1997) <strong>and</strong><br />
Sell & Murrell ( 1996). Values that were thought to be too big, especially the height <strong>of</strong><br />
procumbent species, were modifi ed using informat ion in Butcher (1961).<br />
A nearly complet e set <strong>of</strong> additional height values was taken from sources including Flora lberica<br />
(Cast roviejo et al., I 986-), a Czech fl ora (Dostal, 1958) <strong>and</strong> BSBI h<strong>and</strong>books such as Crucifers <strong>of</strong><br />
Great Britain <strong>and</strong> Irel<strong>and</strong> (Rich, 1991). Other such sources included Aeschimann & Burdet ( 1994),<br />
Hutchinson & Thomas ( 1966), Jermy, Chater & David (1982), Mei kle ( 1984), Page ( 1997) <strong>and</strong><br />
Preston ( 1995). The new values were checked against t hose derived from the main sources. For<br />
t hose species where t here was a dif erence <strong>of</strong> more than a factor <strong>of</strong> 1.5 between the two<br />
sources, the discrepancy was resolved by making a judgement as to which seemed most suitable<br />
for <strong>British</strong> conditions. In addition, all heights <strong>of</strong> pteridophytes <strong>and</strong> <strong>of</strong> trees <strong>and</strong> shrubs exceeding<br />
5 m have been critically examined.<br />
A difi culty with creeping or procumbent plants is that the fl oras give shoot lengt h but not plant<br />
height. For several such plants, the canopy height was estimated by Hill, using descriptions <strong>and</strong><br />
personal experience. Likewise Preston estimated t he heights <strong>of</strong> Aizoaceae (cf Preston & Sell,<br />
1989).<br />
Many diffi culties in assigning height to a plant remain. The height <strong>of</strong> a fern is taken to be the<br />
length <strong>of</strong> its fronds. Scapose plants such as Pinguicula lusitanica may be very small except for their<br />
scape. In several scapose genera (e.g. Bellis, Pilosella, Pinguicula, Plantago, Primula, Pyrola), t he length<br />
<strong>of</strong> the leaves is used as a measure <strong>of</strong> size. On the other h<strong>and</strong>, rosette plants with substantial<br />
infl orescences (e.g. Sempervivum tectorum) have been accorded t he height <strong>of</strong> their infl orescence<br />
rather t han t he lengt h <strong>of</strong> t he leaves. It was impossible to be completely consistent. Maximum<br />
height is a general indication <strong>of</strong> the size <strong>of</strong> the plant rather than a precise measure.<br />
The result ing table is inevitably a complex result <strong>of</strong> cited values <strong>and</strong> personal judgement. It was<br />
clear that aut hors repeat each ot her <strong>and</strong> that their informat ion is <strong>of</strong>t en wrong. Overestimates<br />
abound because botanists take pleasure in ext reme values. For example, <strong>British</strong> authors <strong>and</strong> Flora<br />
Europaea (Tutin et al., 1964- 1980) give t he height <strong>of</strong> Ulmus glabra as 40 m, higher than any ot her<br />
elm. This is clearly unrealistic, but authors' copying <strong>of</strong> height data has meant that the value 40 m<br />
is constantly repeated. Fortunately Bean ( 1950- 1951) indicates a more realist ic value <strong>of</strong> 30 m,<br />
which has been used here. We have in many ot her cases t ried to drive height s down from<br />
ext reme to typical values, by selecting the publication with the lowest values.<br />
De tuition o Ii e orms<br />
Life forms (Raunkiaer, 1934) are an example <strong>of</strong> what are now called 'plant funct ional types' (cf.<br />
Box, 1996). A modifi ed version <strong>of</strong> Raunkiaer's system was set out by Clapham,Tutin & Warburg<br />
( 1962), who specifi ed a life form for almost all species. Their assignments are a valuable starting<br />
point but contain many inconsistencies. For PLANTATT, they have been comprehensively<br />
revised. The categories were partially redefi ned (Table A l).<br />
6 1
Table A I . Life form categor ies from Clapham ,Tutin & W arburg ( 1962) <strong>and</strong> revised<br />
categories<br />
Category<br />
(CTW )<br />
Phanerophyte,<br />
mega-, meso-<br />
Phanerophyte,<br />
micro-<br />
Phanerophyte,<br />
nano-<br />
Defi nition (CTW ) PLA NTAT T Defi nit io n (database)<br />
>8 m Ph Mega-, meso- <strong>and</strong> microphanerophyte<br />
2-8 m Ph (combined with taller phanerophytes)<br />
25 cm-2 m Pn Nanophanerophyte<br />
Chamaephytes 0-25 cm Ch Chamaephyte<br />
Hemicryptophytes<br />
W intering buds at soil<br />
surface<br />
hc Hemicryptophyte<br />
Herbs with wintering<br />
Geophyt es buds below the soil Gb, Gn Geophytes<br />
surface<br />
Helophyt es Marsh plants (not recognized)<br />
Hydrophytes Water plants Hy<br />
Therophytes<br />
Passing unfavourable<br />
season as seeds<br />
Hz<br />
T h<br />
62<br />
Perennat ing buds submerged during<br />
winter<br />
Annual water plant<br />
Annual l<strong>and</strong> plant, including those living<br />
on summer mud<br />
The redefi ned categories are generally self-explanatory. As the database contains plant heights,<br />
the dist inctions between phanerophytes <strong>and</strong> chamaephytes, <strong>and</strong> distinct ions within<br />
phanerophytes, are not ent irely necessary. If required, new categories can be derived using<br />
combinations <strong>of</strong> character's. For example German authors such as Mueller-Dombois & Ellenberg<br />
( 1974) generally allow chamaephytes to be up to 50 cm tall <strong>and</strong> distinguish a category <strong>of</strong> dwarf<br />
shrubs (denot ed by Z - Zwergstraucher). These are woody or semi-woody chamaephytes. It<br />
would be possible to reconstruct t his category from our database, allowing for t he fact that<br />
ordinary maximum heights <strong>of</strong> many <strong>of</strong> these bushes might be up to 100 cm.<br />
Ot her categories included by Mueller-Dombois & Ellenberg ( 1974) are lianes, epiphytes <strong>and</strong><br />
errant hydrophytes (unattached water plants). They defi ne Hemicryptophytes as plants that die<br />
back to near the ground in the unfavourable season. Although worked out in some detail, their<br />
scheme remains somewhat tentative <strong>and</strong> we have not adopted it.<br />
Exam les o how li e- orm criteria are a lied<br />
The criteria given above result in many discrepancies between our defi nit ions <strong>of</strong> life for m <strong>and</strong><br />
those <strong>of</strong> Clapham,Tutin & Warburg ( 1962). For example, t he distinction between geophytes <strong>and</strong>
hemicryptophytes is <strong>of</strong>ten hard to apply with rhizomatous perennials. In principle, plants whose<br />
new shoots penet rate the surface before the advent <strong>of</strong> winter are hemicryptophytes, while those<br />
whose shoots remain well buried are geophytes. Thus Phragmites australis, with a relatively deep<br />
rhizome (Preston & Cr<strong>of</strong>t , 1997), has the life forms perennial Hy <strong>and</strong> Gn. In Carex acutiformis,<br />
however, many new shoots have already emerged by the autumn (Preston & Cr<strong>of</strong>t, 1997). It is<br />
also less strongly aquatic. It is t herefore given the life forms hc <strong>and</strong> Hy.<br />
In general, biennials have been classifi ed as hemicryptophytes, but a few such as Euphorbia lathyris,<br />
which are elongated from the beginning, are chamaephytes.<br />
It is inst ructive to consider some ot her cases (Table A2), which will not be discussed in detail.<br />
Table A 2. Som e cases where life-form ( LF) is difficult to apply or where our concept<br />
dif ers from t hat <strong>of</strong> C lapham,Tut in & W arburg ( 1962)<br />
Links between Ii e orms <strong>and</strong> lent hei ht<br />
Because chamaephytes <strong>and</strong> our two categories <strong>of</strong> phanerophytes are defi ned on the basis <strong>of</strong><br />
height, an eff ort was made to defi ne life forms consistently by reference to plant height (Table<br />
A3). Sometimes, as in Artemisia campestris, t he overwintering buds are at a substantially lower<br />
height t han the height <strong>of</strong> the mature plant. Therefore, this scheme has not been followed exact ly<br />
but has been used as a guide.<br />
63
These defi nitions are necessarily imprecise. However, knowing that Ca !tuna vulgans has a typical<br />
maximum height <strong>of</strong> 60 cm suggests that it will <strong>of</strong>ten grow as a chamaephyte <strong>and</strong> <strong>of</strong>t en as a<br />
nanophanerophyte. This is indeed the case; C. vulgaris is the classic dwarf shrub.<br />
Table A 3. Chamaephyte <strong>and</strong> phanerophyte categories in relation to plant height<br />
Typical maximum<br />
plant height (cm )<br />
3-39 Ch<br />
40-69 Ch<br />
70-299 Pn<br />
300-399 Pn<br />
400- Ph<br />
Primary life form Secondary life form<br />
Cionality<br />
Clonality can be defined in various ways. In an enumeration for Cent ral Europe, Klime§ et al.<br />
( 1997) defi ned clonal growt h as synonymous with vegetat ive multiplicat ion, which results in t he<br />
production <strong>of</strong> new, genetically identical descendants (ramets) with the potential to become<br />
independent <strong>of</strong> t he mot her organism. According to this definition, plants that produce a new<br />
ramet each year but do not spread laterally (for example many orchids) are clonal. Klime§ et aL<br />
recognize 21 diff erent clonal types. These are described in Klimet 's excellent website Clopla<br />
(http://wwri butInn.cas.cz/klimes/clopla .htm); all species <strong>of</strong> Central Europe, including the majority <strong>of</strong><br />
<strong>British</strong> <strong>and</strong> <strong>Irish</strong> plants, are assigned to one or more clonal types.<br />
Here we adopt a more familiar defi nit ion <strong>of</strong> clonal growth, namely vegetative reproduction<br />
combined with lateral spread — i.e. spreading through the formation <strong>of</strong> clonal patches or clumps,<br />
or through fragmentation <strong>and</strong> subsequent dispersal <strong>of</strong> plant parts.<br />
Broad Habit ats<br />
The Broad Habitat Classifi cation, developed as part <strong>of</strong> the UK Biodiversity Action Plan (Jackson,<br />
2000; UK Biodiversity Group, 1998; UK Biodiversity Steering Group, 1995), provides a<br />
comprehensive framework for surveillance <strong>of</strong> the UK countryside.We categorized the habitats <strong>of</strong><br />
plants by t heir preferences for Broad Habitats.<br />
In the UK Biodiversity Action Plan (UK Biodiversity Steering Group, 1995), 37 Broad Habitat<br />
categories were defi ned. These included some habitats, such as limestone pavements, that are<br />
quite narrow but were specified because t hey are priority habitats for conservat ion. In a later<br />
publication (UK Biodiversity Group, 1998), the number <strong>of</strong> terrest rial <strong>and</strong> freshwater Broad<br />
Habitats was reduced to 17. Limestone pavements were included in the Broad Habitat inl<strong>and</strong><br />
rock. Ten coastal <strong>and</strong> marine Broad Habitats were added shortly aft erwards (UK Biodiversity<br />
Group, 1999). Out <strong>of</strong> the 27 Broad Habitats, 2 1 support vascular plants (see Table 8, above).<br />
64<br />
Pn<br />
Ph
Broad Habitats are intended to be comprehensive <strong>and</strong> exclusive. In other words, every place in<br />
which a vascular plant is found ought to belong to one <strong>and</strong> only one Broad Habitat. Although<br />
the defi nit ions <strong>of</strong> Broad Habitats are in many cases obvious, t here was a need for more precise<br />
circumscript ion to defi ne t he boundaries between them. For terrest rial <strong>and</strong> freshwater habitats<br />
this guidance is now available (Jackson, 2000). The guidance not only gives writt en defi nit ions, but<br />
relates Broad Habitat s to the units <strong>of</strong> t he National Vegetation Classifi cation (NVC; Rodwell,<br />
1991-2000).<br />
Jackson's (2000) notes for guidance are the basis <strong>of</strong> the cross-reference <strong>and</strong> defi nitions used here<br />
(Table A4). In a small number <strong>of</strong> cases, we have diverged from her interpretations. The basis <strong>of</strong><br />
our disagreement was <strong>of</strong>t en the scale at which we wished to view the vegetation. Thus we have<br />
t reated bog pools as st rictly bog features (not as open water) <strong>and</strong> we treat rock-free maritime<br />
grassl<strong>and</strong> as neut ral grassl<strong>and</strong> (not as supralitt oral rock). Ot her interpretat ions are possible but<br />
result in fl orist ically less homogeneous Broad Habitats.<br />
Table A 4. Assignment <strong>of</strong> N VC com munities to Broad Habitats for t he purpose <strong>of</strong><br />
ascribing habitat preferences. Sequential runs <strong>of</strong> numbers are indicated by hyphens, e.g. 2 1-<br />
23, which signifi es t he sequence 2 1,22,23. Some NVC communit ies were assigned to two Broad<br />
Habitats; where this is t he case, the community is marked by an asterisk, to show that it is also<br />
listed under another Broad Habitat.<br />
N o Nam e N VC com munities<br />
Broad leaved, mixed <strong>and</strong> yew W I- 17,19<br />
woodl<strong>and</strong><br />
2 Coniferous woodl<strong>and</strong> W I8<br />
3 Boundary <strong>and</strong> linear feat ures W 2 I-23,24*; OV I 8*, I 9*,21*,22*,24*,25*,27<br />
4 A rable <strong>and</strong> horticult ural O V I- 11, 13, 14- 17, 18* , 19*,2 1* ,22*,36<br />
5 Improved grassl<strong>and</strong> MG6*,7; OV 12,23*,25*<br />
6 Neutral grassl<strong>and</strong> W 24; MC9- 1 2; MG I-5,6*; MG8- I 3; 0 V28*<br />
7 Calcareous grassl<strong>and</strong> CG I- 14<br />
8 Acid grassl<strong>and</strong> U I - 6,19<br />
9 Bracken U 20; W 25<br />
10 Dwarf shrub heath H I- 10,12,16,18,2 1; M I5*,16; 0 V 34<br />
11 Fen, marsh <strong>and</strong> swamp M4- 14,22-24,25*,26-38; S - I 9,20*,22-28; OV 26,28*,29-<br />
12 Bog M 1-3,15*, 17-21,25*<br />
13 St<strong>and</strong>ing water <strong>and</strong> canals A I-7,8*,9*,10,(11- 16)* , 19*,20*, 21-24<br />
14 Rivers <strong>and</strong> st reams A 8*,9*,( 1 I - I 6)*,17,18,19*,20*<br />
15 Montane habitats H I 3- 15,17,19,20,22; U7- I5,18; W 20<br />
16 Inl<strong>and</strong> rock U 16, 17,2 1; 0 V37-40,4 I*<br />
17 Built-up areas <strong>and</strong> gardens 0 V 20,23*,24*,41* ,42<br />
18 Supralittor al rock MC 1-8<br />
19 Supralittor al sediment H I I; SD I- 19<br />
2 1 Littor al sediment 520,21; SM I-28<br />
65
It is pertinent here to consider the defi nitions, drawing attention to less obvious features <strong>and</strong> to<br />
where we have dif ered from Jackson (2000).<br />
BH I Broad leaved, mixed <strong>and</strong> yew woodl<strong>and</strong><br />
Broad leaved woodl<strong>and</strong> is defi ned as woodl<strong>and</strong> with broadleaved trees having at least 20% canopy<br />
cover. In practice, most woodl<strong>and</strong> has closed canopy. Juniper scrub is included in this type if it is<br />
large enough to result in a woodl<strong>and</strong> understorey (W 19). Other scrub types are treated as edge<br />
features (BH3), because hedges are <strong>of</strong>ten where they occur. The underscrub community W 24 is<br />
shared between woodl<strong>and</strong> (BH1) <strong>and</strong> neutral grassl<strong>and</strong> (BH6).<br />
8 H 2 Coniferous woodl<strong>and</strong><br />
This category is clearly defi ned <strong>and</strong> corresponds to nat ive pine woodl<strong>and</strong> (W 18) in the NVC.<br />
St<strong>and</strong>s <strong>of</strong> planted conifers normally have a subset <strong>of</strong> the normal broadleaved woodl<strong>and</strong> fl ora<br />
growing under them. There is no corresponding NVC type. Planted conifers have therefore<br />
been under-represented, <strong>and</strong> the fern Dryopteris dilatata, which is t he commonest vascular plant<br />
in upl<strong>and</strong> conifer plantations, did not appear as a conifer specialist in our fl oristic database, but its<br />
preference was added by us later<br />
BH 3 Boundary <strong>and</strong> linear feat ures<br />
Apart from scrub that forms hedges, boundary <strong>and</strong> linear features are not directly crossreferenced<br />
to the NVC. They include hedges, t ree-lines, walls, earth banks, grass strips <strong>and</strong> dry<br />
ditches. Note that roads, t racks <strong>and</strong> railways in urban areas belong to the urban BH I7.<br />
BH 4 A rable <strong>and</strong> horticultural<br />
Commercial orchards are included here, as well as fi eld crops. Note that hort iculture here is<br />
defi ned as commercial hort iculture <strong>and</strong> does not include domestic gardens <strong>and</strong> allotments, which<br />
are included in BH 17. The NVC communit ies classifi ed as OV 1- 11,13-19,2 1,22,36 are included<br />
here.<br />
BH 5 Im proved grassl<strong>and</strong><br />
This has few characteristic species, <strong>and</strong> is typically dominated by sown ryegrass Lolium perenne or<br />
clover Trifolium repens. OV I2, the Poo annua-Myosotis arvensis community, is indicated in <strong>British</strong><br />
Plant Communities (Rodwell, 1991-2000) as being mainly a disturbed element in improved pasture<br />
<strong>and</strong> has been included here.<br />
8 H 6 N eutral grassl<strong>and</strong><br />
The mesot rophic grassl<strong>and</strong> types MG I-6,8- 13 are the core <strong>of</strong> t he neutral grassl<strong>and</strong> category.<br />
Coastal grazing marsh is included here. Four <strong>of</strong> the coastal clif grassl<strong>and</strong>s, MC9- I2, are not<br />
necessarily or normally rocky <strong>and</strong> have been included here in BH6. OV28, an inundation<br />
grassl<strong>and</strong>, is shared between BH6 <strong>and</strong> BH 1 I.<br />
BH 7 Calcareous grassl<strong>and</strong><br />
By convention, this includes all NVC types included in the CG class. As a result, montane<br />
calcareous vegetation is in BH7, along with chalk grassl<strong>and</strong>.<br />
BH 8 Acid grassl<strong>and</strong><br />
Only lowl<strong>and</strong> <strong>and</strong> subalpine grassl<strong>and</strong> are included here; vegetation types that would normally be<br />
found above the timberline are in BH I5. Communities U I-6 form the core <strong>of</strong> this type. The<br />
fern community U 19 is treated in BH8. It is usually a mosaic element in grassl<strong>and</strong>, though it also<br />
occurs on steep banks by rivers <strong>and</strong> could therefore be included also in the broad defi nit ion (not<br />
used here) <strong>of</strong> BH I4.<br />
66
BH 9 Bracken<br />
This is small type, defi ned as unwooded l<strong>and</strong> dominated by bracken Pteridium aquilinum. 8H9 has<br />
few characterist ic species, because it is usually a derivative <strong>of</strong> grassl<strong>and</strong> or forest. Just two NVC<br />
types, U20 <strong>and</strong> W 25, are included here.<br />
BH 10 Dwarf shrub heat h<br />
The heath type BH 10 includes vegetation with at least 25% cover <strong>of</strong> Ericaceae or dwarf gorse<br />
Ulex minor. Coastal heath is included in this category, except for dune heath, which is assigned to<br />
BHI9. Dwarf shrub communit ies on blanket bogs are st rictly included in BH I2, but this is a<br />
relat ively minor habitat for them <strong>and</strong> has not been recognized in t he cross-reference. The<br />
st<strong>and</strong>ard heathl<strong>and</strong> communities H 1- 10,12,16,18,21, toget her with the wet heath communities<br />
M 15,16 form the core <strong>of</strong> this community. The bizarre 0 V34, a chive M um schoenoprasum<br />
community forming a mosaic element on shallow soils in coastal heath, is included here.<br />
B14 1 I Fen, marsh <strong>and</strong> swamp<br />
This is a very wide category <strong>and</strong> includes reedbeds, swamps, tall-herb fens, fl ushes, springs,<br />
marshes, rush-past ures <strong>and</strong> wet grassl<strong>and</strong>. Mud communities <strong>of</strong> dried-up ponds <strong>and</strong> riverbeds<br />
(e.g. 0 V30) have been included here, although they belong more st rictly to BH I3 <strong>and</strong> BH I4<br />
unless they are very ext ensive (>0.25 ha). Types M4- 14,22-38, all swamp communities except<br />
Scirpus maritimus S2 1, <strong>and</strong> OV 26,28-33,35 are included. We have excluded the bog-like<br />
communities (Erico-Sphagnion) that are found in very acid lowl<strong>and</strong> valley-mires.<br />
BH I 2 Bog<br />
Bogs are defi ned strictly only as ombrot rophic bogs. However, we have lumped all Erico-<br />
Sphagnion vegetation, including M21, in BH 12 even if it the vegetation occurs in valley mires,<br />
toget her with bog pool vegetation M 1-3. This is to prevent the characteristic species <strong>of</strong> BH 11<br />
being too heterogeneous. The NVC types included are M1-3,15,17-21,25.<br />
BH I 3 St<strong>and</strong>ing water <strong>and</strong> canals<br />
Only aquatic vegetat ion has been cross-referenced to this type, i.e. communit ies A l - 16,19-24.<br />
Mud communities <strong>and</strong> marginal vegetation are referred to BH11.<br />
BH I 4 Rivers <strong>and</strong> st reams<br />
This Broad Habitat is t reated in much the same way as BH I3. According to t he strict defi nition,<br />
all vegetation between the banks <strong>of</strong> a river counts as belonging to BH I4. For the purposes <strong>of</strong><br />
defi ning characteristic species, river-bank vegetat ion has been t reated as belonging to other types<br />
such as inl<strong>and</strong> rock. Thus t he communities included in BHI4 are A8,9,11-20. Several <strong>of</strong> these<br />
communities are also characteristic <strong>of</strong> B1-113.<br />
BH 1 S Mont ane habit at s<br />
This type is defined by having distinctive arctic-alpine species, provided that they are not<br />
calcicolous. Calcareous montane vegetation is included in BH7. BH 15 includes montane heaths<br />
H I3- 15,17,19,20,22, grassier types U7- I5,18, <strong>and</strong> a willow scrub type W 20.<br />
BH I 6 Inl<strong>and</strong> rock<br />
This heterogeneous Broad Habitat includes limestone pavement, cliff s, caves, scree, quarries <strong>and</strong><br />
vegetation on skeletal soils over rock. Communities U 16,17,2 1 <strong>and</strong> 0 V37-4 1 are assigned to<br />
BH 16.<br />
BH I 7 Built-up areas <strong>and</strong> gardens<br />
Urban habitats were largely ignored by the NVC surveyors. Most <strong>of</strong> the characteristic species<br />
are neophytes, while t he commonest species are widespread nat ives <strong>and</strong> archaeophytes (Hill, Roy<br />
67
& Thompson, 2002). Very few NVC communities are really characteristic <strong>of</strong> the built<br />
environment. Pavement <strong>and</strong> wall communities 0 V20,42 are assigned wholly to BH I7;<br />
0 V23,24,4 I are assigned to BH 17 but shared with other Broad Habitats.<br />
BH 18 Supra littoral rock<br />
It is clear from the Habitat Statement for supralitt oral rock (UK Biodiversity Group, 1999) that<br />
maritime grassl<strong>and</strong> is not included. For that reason, MC9- 11,12 have been treated as neutral<br />
grassl<strong>and</strong>, BH6. Only MCI-8 are included in BH I8.<br />
BH 19 Supralittoral sedim ent<br />
This includes str<strong>and</strong>lines, shingle, machair <strong>and</strong> coastal dunes. It includes all the NVC types SD I-<br />
19, toget her with the dune heath type H I I .<br />
BH 20 Littoral Rock<br />
Intert idal rock normally lacks vascular plants <strong>and</strong> no vascular-plant species or vegetat ion type is<br />
characterist ic <strong>of</strong> it.<br />
BH 2 I Littoral sediment<br />
This includes saltmarshes <strong>and</strong> saltmarsh pools.<br />
BH 23 Inshore sublittoral sediment<br />
One vascular plant. Zostero marina, occurs in this habitat, which is not considered furt her<br />
Initial calculation o s ecies' re erences or Broad Habitats<br />
For the majority <strong>of</strong> species, habitat preferences were based on quadrat data. Two major datasets<br />
were available, the original data used to derive the association tables in <strong>British</strong> Plant Communities<br />
(NVC; Rodwell, 1991-2000) <strong>and</strong> quadrat samples collected for Count ryside Survey 2000,<br />
CS2000 (Haines-Young et aL, 2000).<br />
The quadrat data used to create the NVC categories were supplied by JNCC as an MS Access<br />
database. This had been created from fi les in the format <strong>of</strong> the VESPAN package (Malloch, 1985).<br />
There was no information on the NVC community to which each quadrat had been assigned.<br />
Therefore, the computer program TABLEFIT (Hill, 1996) was used to assign 312 16 quadrats to<br />
NVC communities using species' Domin scores. The median goodness-<strong>of</strong>-fi t was 67%. Only four<br />
samples had no fi t; t hese were assigned to a community by personal judgement . NVC plant<br />
communit ies were then attributed to Broad Habitats using the cross-reference outlined above<br />
(Table A4). All CS2000 samples had been allocated to BAP Broad Habitat types in the fi eld.<br />
Aft er quadrats had been assigned to Broad Habitats, species' frequencies in each Broad Habitat<br />
were calculated. Frequencies were used to calculate preferences for Broad Habitats. For each<br />
species s <strong>and</strong> BH h, we calculated an odds-ratio index:<br />
Qsh<br />
= observed odds for species s in habitat h / expected odds<br />
nsh<br />
/ (ns+ "sh + 0.5)<br />
esh/ Os+ esh)<br />
where<br />
nsh = observed number <strong>of</strong> occurrences <strong>of</strong> species s in BH h<br />
ns+ = 1h nsh = total number <strong>of</strong> occurrences <strong>of</strong> speCies s<br />
esh = expected number <strong>of</strong> occurrences <strong>of</strong> species s in BH h.<br />
68
The expected number <strong>of</strong> occurrences<br />
where<br />
esh<br />
= ns N h / N +<br />
Nh = number <strong>of</strong> quadrat samples in BH h<br />
N 4. = E h N h = total number <strong>of</strong> quadrat samples.<br />
Species s was deemed to have a preference for BH h if<br />
Qsh 4.<br />
Extension <strong>and</strong> validation o s ecies' re erences<br />
Many rare, scarce or uncommon native species are not represented either in the NVC quadrats<br />
or in CS2000 samples. Furt hermore, t here was the possibility that uneven sampling <strong>of</strong> Broad<br />
Habitats could have resulted in some wrong indications <strong>of</strong> preference.<br />
First, we ext ended the list <strong>of</strong> BH preferences to species not adequately sampled by the NVC or<br />
CS2000, using the text prepared for the New Atlas, together with other literature sources (e.g.<br />
Stewart, Pearman & Preston, 1994; W igginton, 1999). Much <strong>of</strong> the initial work was done by Bill<br />
Meek (CEH); t he resulting table <strong>of</strong> preferential species was checked by D.A. Pearman (BSB1), as<br />
well as by ourselves <strong>and</strong> ot her CEH staf . In addition, preferences were checked against ot her<br />
data in PLANTATT For example, species attributed to BH I3 (St<strong>and</strong>ing water <strong>and</strong> canals) <strong>and</strong><br />
BH 14 (Rivers <strong>and</strong> streams) were checked for their Ellenberg moisture (F) values. Those for<br />
which F
A CKN O WLED GEMEN TS<br />
Much <strong>of</strong> the work presented here was support ed by funding from the W ildlife <strong>and</strong> Countryside<br />
Division <strong>of</strong> Defra <strong>and</strong> its predecessor DETR. The immediate stimulus was a project to interpret<br />
the New Atlas <strong>of</strong> the <strong>British</strong> <strong>and</strong> <strong>Irish</strong> Flora (Preston et al., 2003). A requirement for non-spatial<br />
attributes <strong>of</strong> plants was written into the 2002 programme <strong>of</strong> work for the National Biodiversity<br />
Network (NBN). Informat ion on native status was prepared for the New Atlas <strong>and</strong> presented<br />
there (Preston, Pearman & Dines, 2002). The Ellenberg indicator values were developed under<br />
the DETR-funded ECO FACT programme <strong>and</strong> published separately (Hill et al., 1999).<br />
The other main ot her source <strong>of</strong> funding was from our parent body the <strong>Natural</strong> <strong>Environment</strong><br />
<strong>Research</strong> Council. Not only have they generously support ed the Biological Records Centre<br />
(BRC) <strong>and</strong> NBN over the years, but they have allowed us to fi nd additional t ime to work our<br />
data up into publishable form. The geographical classifi cat ion <strong>of</strong> European distributions (Preston<br />
& Hill, 1997) was developed with support from NERC's special programme on global<br />
environmental change,TIGER.<br />
Some elements <strong>of</strong> t his work have been funded by the Joint Nat ure Conservation Committee<br />
through t heir joint sponsorship <strong>of</strong> BRC. Other aspects were supported by t he Countryside<br />
Council for Wales, English Nat ure, Scottish <strong>Natural</strong> Heritage, <strong>Environment</strong> <strong>and</strong> Heritage Service<br />
(Northern Irel<strong>and</strong>) <strong>and</strong> Plantlife as part <strong>of</strong> the analysis <strong>of</strong> New Atlas data.<br />
Publication <strong>of</strong> this booklet has been jointly funded by CEH <strong>and</strong> Defra.<br />
We are grateful to the following for particular help:<br />
De fra<br />
Andrew Stott (overall guidance <strong>and</strong> long-term support)<br />
Debbie Boobyer (Broad Habitats <strong>and</strong> analysis <strong>of</strong> New Atlas data)<br />
BSBI<br />
David Pearman (Broad Habitats)<br />
Cambridge University<br />
Peter Sell (unpublished fl ora draft s)<br />
English Nature<br />
Roger Key (Cover photograph)<br />
JNCC<br />
Ian St rachan (NVC quadrat data)<br />
CEH<br />
Bob Bunce (Ellenberg values)<br />
Jon Cooper (liaison with NBN)<br />
Julie Gaunt (graphic design)<br />
Bill Meek (Broad Habitats)<br />
Owen Mountford (Ellenberg values, European fl oras, species attributes)<br />
Peter Rothery (Change index)<br />
Mark Telfer (Change index)<br />
70
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