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Invertebrates of
Moorend Common, Buckinghamshire
Prepared by Lawrence Bee*
With Lane End Conservation Group
Client: The Chilterns Conservation Board
Part of the Chilterns Commons Project
*Lawrence Bee - Ecological and Environmental Education Consultancy
7 Oakmead, Witney, Oxon OX28 1EF 07870854106 email: [email protected]
Contents
Introduction 1
Objectives 3
Survey methodology 4
Invertebrates recorded 8
Spiders
Beetles
Centipedes, Millipedes and Woodlice
Other Groups
Recommendations 11
Acknowledgements 14
References 15
Survey results
o Spiders 16
o Beetles 19
o Centipedes, Millipedes and Woodlice 21
o Other Groups 22
Front page: The ground beetle Agonum sexpunctatum – a NotableA species in the UK (see text
p.9)©entomart
1
Introduction
National Grid Reference: SU 801 907 (north section) & SU802905 (south section)
County: Buckinghamshire
Local authority: Wycombe District Council.
Parish: Lane End
Area: c. 21.58 ha
Moorend Common is a Site of Special Scientific Interest (SSSI) notified under Section 28 of
the Wildlife and Countryside Act 1981. The full S.S.S.I. citation provided by Natural England
is available online at:
http://www.sssi.naturalengland.org.uk/citation/citation_photo/1001497.pdf
The NE citation for Moorend Common states that, in addition to areas of secondary tree
growth, scrub and wetland, the key indicators are U4 acid grassland and W10 and W14
woodland. All are encompassed within the recognised habitat types of either Lowland
A view of Middle Meadow at Moorend
Common
©Rob Rowe - Natural England
2
Heathland and Acid Grassland or Woodland within the Buckinghamshire and Milton Keynes
Bio-diversity Action Plan (BAP).
U4 Grassland – a habitat composed of a mixture of grasses and herbs which exists on
acidic soils or substrates. This grassland type is increasingly rare within the Chilterns
and is diminishing as methods of land management have changed away from regular
grazing or mowing.
W10 Woodland – a habitat composed of oak woodland predominantly on acid soils
or substrates. Typical species, in the Moorend Common SSSI, include pedunculate
oak and silver birch, an understorey of hazel and hawthorn and a ground flora of
bracken and bramble.
W14 Woodland – a habitat composed of beech woodland on relatively base poor to
acidic soils and substrates. Typical species, in the Moor Copse, include beech and an
understorey of holly and bramble with a sparse ground flora owing to the dense
shade created by the mature beech canopy.
Detailed ecological information can be found within the ‘Heathland’ and ‘Woodland Habitat’
sections of the Buckinghamshire and Milton Keynes BAP of 2000 and the Chilterns
Conservation Board’s draft BAP of 2006. (LEPC & MCCC - Surveys Brief 2012-2015/1st draft
2012).
3
Objectives
The survey formed part of the Heritage Lottery funded Chilterns Commons Project managed by the
Chilterns Conservation Board. The work was part of a larger project which included historical
research and ecological studies alongside monitoring conservation practices to determine their
effectiveness.
The Lane End Parish Council and the Moorend Common Conservation Committee produced a
Management Plan in 2012 and within it there is mention of survey work being carried out on
butterflies, moths and aquatic macro invertebrates (LEPC & MCCC - Surveys Brief 2012-2015/1st
draft 2012). Survey work on other invertebrate groups was planned in 2010 but did not actually
occur. The survey reported in this document was designed to address this omission in covering
invertebrate groups where little or no records existed.
4
Survey Methodology
4 locations for siting pitfall traps were identified and established on 13 May 2013. Each location
comprised 4 separate pitfall traps set at corners of a square metre and it was agreed with the
volunteer team that traps would be emptied and reset approximately every 2 weeks through the
summer to finish around the beginning of September. For each location captures from the 4 traps
would be treated together but divided into separate containers of (1) spiders & harvestmen,
(2) beetles, (3) woodlice, centipedes & millipedes and (4) other miscellaneous captures.
Lane End Conservation Group Volunteers setting
pitfall traps
5
The 4 locations were chosen to represent different habitats and locations within the Moor End
Common site as a whole and were sited as follows (see Maps 1 & 2 ):
Site A – SU 80179056 – Just off the edge of the northern section of Middle Meadow amongst leaf
litter under mature oak
Site B – SU 80219049 – Open area of wet grassland within compartment F
Site C – SU 80099075 – Open grassland within North meadow
Site D – SU 79969062 – Amongst mature oaks adjacent to stream on N edge of compartment B
Site A Site B
Site C Site D
6
In addition to the pitfall trapping programme a number of yellow pan traps to capture flying insects
was supplied to the volunteer team to set up on site when pitfall traps were being emptied and
reset. As it turned out, time availability of the volunteer team made the setting and collection of
pan traps impractical and none were set by the volunteers. Just one pan trap was set on a collecting
visit made on 13 May 2013.
Map 1 : Compartment Map of Moorend Common. (LEPC & MCCC -
Surveys Brief 2012-2015/1st draft 2012).
8
Invertebrates Recorded
Spiders
60 species of spider were recorded during the survey period. As well as the pitfall samples, other
surveys were carried out on 18.10.12, 13.5.13, 5.8.13 and 18.9.13 - these consisted primarily of
suction sampling sessions with some sweeping of low vegetation and beating of gorse and lower
branches of oak. The pitfall samples were, surprisingly, not very productive for spiders and
harvestmen. During pitfall sampling at Chimney Meadows Reserve in Oxfordshire between 2005
and 2010 the traps yielded considerably more individual spider specimens with the total number of
species being e.g. 57 species recorded from 103 sample sets in 2009. At Moorend, even though the
total number of species recorded was similar in 2013 (to that for Chimney Meadows quoted above),
over half of these records came from collecting methods other than pitfall sampling. It is difficult to
explain why the pitfall traps captured such a low number of arachnids. In conversation with other
arachnologists they too had experienced low numbers of arachnids in pitfall surveys they had
conducted in 2013. Possible reasons for the low numbers were the very cool temperatures
recorded throughout the spring and early summer of 2013. One of the predominant spider families
collected from pitfall traps is the Lycosidae. These ground moving wolf spiders tend to reach
maturity in the late spring and early summer and cooler than average temperatures during this
period may well compromise the successful maturing of young spiders into mature adults.
Amongst the spiders recorded the following species is of interest:
• The jumping spider Marpissa muscosa. National Status ‘Notable B’: uncommon in Great
Britain and thought to occur in between 31 and 100 10km squares of the National Grid.
Collected from underneath the bark of a fallen branch in compartment G/South Meadow. The
species is recorded throughout south-eastern England with a few scattered records further
9
west and north. In Dorset it is common under flat stones on the tops of dry stone walls but
elsewhere it occurs mostly underneath loose bark on trees, on posts and paling fences.
Many specimens collected using the suction sampler were immature and therefore impossible to
identify down to species (apart from a very few instances of immature specimens having distinctive
markings enabling identification to species). These unidentified immatures indicate a richer spider
fauna for Moorend which, if further funding were available, could be surveyed in the future.
Beetles
41 species of beetle were recorded from the pitfall traps. Of these 22 were ground beetles and in
terms of numbers of individual beetles collected were by far the most dominant group. The three
commonest species were Pterostichus madidus with 393 specimens, Abax parallelepipedus with
241 specimens and Carabus problematicus with 116 specimens. Of particular interest was the green
and bronze ground beetle Agonum sexpunctatum. The national status for this species is ‘Notable A’
- uncommon in Great Britain and thought to occur in 30 or fewer 10km squares of the National
Grid. The preferred habitat for this species is ‘On damp open ground near water, on sandy soils in
heaths and open woodland’ (Luff 2007) which corresponds well with the location of site B – the
Jumping Spider Marpissa muscosa ©Andy Callow
10
only pitfall trap site where it was found. This record caused some excitement when it was identified
by Lloyd Garvey at the University Natural History Museum in Oxford where Lloyd was identifying
the beetles.
Unfortunately, due to prolonged immersion in the propylene glycol solution many of the beetles
began to disintegrate and so preserving specimens was not possible. Lloyd did a great job in
identifying the material and only had problems distinguishing between 2 very similar species. The
entry in the species list for Pterostichus nigrita/rhaeticus is the one record where it was impossible
to distinguish between the 2 species – they are only separable by examination of the genitalia and
the fragmented state of the specimens made this impossible.
Centipedes, Millipedes and Woodlice
All but one of the centipede and millipede species recorded from the pitfall traps have the national
status of ‘Common’. The exception, the stone centipede Lithobius muticus, has a national status of
Notable B and is regarded as scarce nationally. In the Chilterns, however, it is a locally common
species, Moorend providing a suitable deciduous woodland habitat.
Five species of woodlice were recorded. The Carr Slater Ligidium hypnorum is locally common in the
Chilterns but is nationally only found in the south east and south central regions - not being
recorded north of a line between the Wash and the Bristol Channel. The other species are all
common nationally.
11
Other groups
In the pitfall traps other invertebrate groups were represented. One or two species were identified
but the majority of ‘others’ are still awaiting identification should expertise become available.
These unidentified specimens (approximately a dozen tubes containing predominantly flies -
Diptera) are stored in 70% alcohol, which should preserve them indefinitely. If there are
possibilities of identification then they can be transferred to appropriate specialists.
The slugs were half rotted, almost un-identifiable and it was impossible to quantify numbers. The 3
species recorded were all common, yet there were not any woodland Limacid slugs - eg Limax
cinereoniger or Malacolimax tenellus, in the samples, which would have been expected from this
type of deciduous woodland habitat in the Chilterns.
A small number of aculeate hymenoptera – bumble bees and solitary bees were recorded from a
pan trap put out on my first visit to the Common. Again, all were common species.
Recommendations
• For the jumping spider Marpissa muscosa – allow fallen branches and dead trees to remain
in situ to decompose and break down naturally.
• For the ground beetle Agonum sexpunctatum – maintain wetland habitat at pitfall trap site
B in Compartment F and the immediate surrounding area.
• During the limited survey time available it was apparent that the South Meadow was
probably the richest in terms of invertebrate diversity. Should any further funding become available
this area would benefit from additional survey work – in the form of pitfall trapping, suction
sampling and general collecting. As mentioned above there is potential for recording a much
greater number of spiders at Moorend and South Meadow would be a priority area for this.
12
• Throughout the whole site the maintenance and encouragement of a wide diversity of
vegetation structure is recommended. Many invertebrate groups benefit from a varied mosaic of
vegetation structure throughout the whole year during all stages of their life cycles. The greater the
diversity of plant species within a habitat or site the higher the structural diversity will be. Kirby
(1992) states ‘The importance to invertebrates of varied vegetational structure cannot be
overstated’ and ‘Vegetation structure is important to invertebrates in every aspect and at every
scale.’ Moorend contains a diversity of tree and plant species in varied habitat types ranging from
close canopy deciduous woodland to open meadow with additional variety resulting from the
varying moisture content of the soils. As a whole the site has a high diversity of vegetation structure
and this should be encouraged (see below). Gorse Ulex europaeus, for example, is one of the most
highly structured plants and its presence on Middle Meadow provides a habitat for a range of web
spinning spiders such as Agelena labyrinthica and Cyclosa conica which would probably not be
found at Moorend if the small areas of Gorse were not there.
Other site features can be described as structure and should be included here. For example, areas
of bare ground, however small, can be critical for some invertebrates, e.g. solitary bees, and if
present on site should be conserved in the management programme. Similarly, dead wood either
lying on the ground or still on the tree is an additional structure feature which should be conserved.
Simple survey techniques and management options can be introduced to monitor and further
record invertebrates if desirable:
Where grassland mowing is part of the management programme small areas of grassland
should not be mown and should be left to die off naturally thereby maintaining some of the
vegetation structure required by those invertebrates requiring specific overwintering sites in
dead meadow and grassland vegetation.
13
To encourage solitary bee and wasp activity it would be well worth establishing a few
patches of bare ground by simply lifting small patches of turf to expose the underlying soil,
particularly in areas open to the sun where there may be the possibility of the bare ground
drying out.
The installation of solitary bee nest boxes is also a useful method of monitoring and
recording activity of these invertebrates. Specifically designed nest boxes can be purchased
or they can be simply constructed – for further information see
http://www.foxleas.com/bee_house.htm
Ground moving invertebrates will shelter under shaded areas on the ground surface.
Artificial shelter areas can be established by laying down small sections of corrugated metal
sheeting or old pieces of carpet on the ground in selected locations around the site. These
would provide an undisturbed retreat for a range of invertebrates particularly beetles and
spiders. The metal sheeting also is a favourite shelter site for slow worms and grass snakes –
particularly if located in areas exposed to direct sunlight.
14
Acknowledgements
Thanks are due to:
Steve Gregory for identification of the centipedes, millipedes, woodlice and slugs.
Lloyd Garvey for identification of the beetles.
Ivan Wright for identification of the aculeates.
The following volunteers from the Lane End Conservation Group: Alan Gudge, Sandy and
Marion Gill, Andrew Mactavish, Tim Grout-Smith, Helen and Mike Hall, Vivienne Ball,
Margaret Bolton and Shirley Schreiber for the sterling work in emptying and resetting the
pitfall traps over the late Spring and Summer of 2013 and for the sorting of the pitfall ‘soup’
into the various invertebrate groups.
Katy Dunn for providing a ‘holding facility’ for equipment, pitfall catches awaiting collection
etc. - without this voluntary assistance the survey could not have taken place. Also, for use
of the photograph showing ‘Lane End Conservation Group Volunteers setting pitfall traps ‘
Margaret Bolton for providing photos of the pitfall trap sites
Rob Lowe from Natural England for permission to use the photo of Moorend Common –
Middle Meadow.
Ross Osborn and the Lane End Parish Council and the Moorend Common Conservation
Committee(LEPC & MCCC) for permission to use information from the Surveys Brief 2012-
2015 for Moorend Common
The Heritage Lottery Fund and the Moorend Common Conservation Group for financial
support to the survey which was part of the Chilterns Commons Project managed by Rachel
Sanderson on behalf of the Chilterns Conservation Board.
15
References
Gregory, S. 2009 Woodlice and Waterlice (Isopoda: Oniscidea & Asellota) in Britain and Ireland.
Field Studies Council
Harvey, P.R., Nellist, D.R. & Telfer, M.G. (eds) 2002. Provisional atlas of British spiders (Arachnida,
Araneae), Volumes 1 & 2. Biological Records Centre.
Kirby, P. 1992 Habitat Management for Invertebrates: a practical handbook. Royal Society for the
Protection of Birds
Luff, M. L. 2007 RES Handbook, Volume 4, Part 2: The Carabidae (Ground Beetles) of Britain and
Ireland Field Studies Council
16
Moorend Invertebrate Survey 2012/2013 - Spiders and Harvestmen (1)
Common Name
27.
5.13
7.6.
13
25.6
.13
8.7.
13
21.8
.13
2.9.
13
26.5
.13
10.6
.13
23.6
.13
10.7
.13
27.7
.13
5.8.
13
18.8
.13
8.9.
13
30.5
.13
6.6.
13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
12.7
.13
5.8.
13
18.8
.13
2.9.
13
18.1
0.12
13.5
.13
5.8.
13
18.9
.13
18.9
.13
Araneidae
Dysderidae Dysdera erythrina 1
Mimetidae Ero cambridgei 1
Theridi idae Anelos imus vi ttatus 1
Theridi idae Neottiura bimaculatum 1
Theridi idae Enoplognatha ovata 1
Theridi idae Robertus l ividus 1 1
Linyphi idae Ceratinel la brevis 1
Linyphi idae Walckenaeria acuminata 1
Linyphi idae Walckenaeria antica 2
Linyphi idae Entelecara acuminata 1
Linyphi idae Gongyl idium rufipes 1
Linyphi idae Dismodicus bi frons 7 1
Linyphi idae Pocadicnemis juncea 1
Linyphi idae Oedothorax retusus 1
Linyphi idae Ceratinops is s tativa 1
Linyphi idae Gongyl idiel lum vivum 1
Linyphi idae Diplocephalus picinus 1 1 1 3 1
Linyphi idae Erigone atra 1 1
Linyphi idae Agyneta subti l i s 1
Linyphi idae Centromerus sylvaticus 1f
Linyphi idae Saaris toa abnormis 2
Linyphi idae Macrargus rufus 1 1
Linyphi idae Microneta viaria 1 1
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA
(Na)or Notable B (Nb)
SUCTION
SAMPLING &
BEATING/
SWEEPING
A B DC
PITFALL TRAPS
17
Moorend Invertebrate Survey 2012/2013 - Spiders and Harvestmen (2)
Common Name
27.
5.13
7.6.
13
25.6
.13
8.7.
13
21.8
.13
2.9.
13
26.5
.13
10.6
.13
23.6
.13
10.7
.13
27.7
.13
5.8.
13
18.8
.13
8.9.
13
30.5
.13
6.6.
13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
12.7
.13
5.8.
13
18.8
.13
2.9.
13
18.1
0.12
13.5
.13
5.8.
13
18.9
.13
18.9
.13
Araneidae
Linyphi idae Bathyphantes graci l i s 1 9 2 3 1
Linyphi idae Bathyphantes nigrinus 1
Linyphi idae Lepthyphantes tenuis 1 1 15 7 6 29
Linyphi idae Lepthyphantes zimmermani 1 1 2 1
Linyphi idae Lepthyphantes cris tatus 1 1
Linyphi idae Lepthyphantes flavipes 3 1 3f 1 1 1 2
Linyphi idae Linyphia triangularis 1 1
Linyphi idae Neriene montana 3
Linyphi idae Neriene clathrata 7 3 16
Linyphi idae Neriene peltata 3
Tetragnathidae Pachygnatha clerki 2 9
Tetragnathidae Pachygnatha degeeri 1 2 15 3 3 4 4 44 2
Tetragnathidae Metel l ina segmentata 1 2 7 4
Tetragnathidae Metel l ina mengei 4
Araneidae Araneus diadematus Garden spider 1 1
Araneidae Araniel la cucurbitina 1
Araneidae Cercidia prominens 1
Araneidae Cyclosa conica 2
Lycos idae Pardosa pul lata 1 2 1 2
Lycos idae Pardosa prativaga 2 1 1
Lycos idae Pardosa amentata 3 1 3 1 1
Lycos idae Pardosa sa l tans 1 1 5 3 1 1 1
Lycos idae Pardosa lugubris 1
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA
(Na)or Notable B (Nb)
PITFALL TRAPS
SUCTION
SAMPLING &
BEATING/
SWEEPING
A B C D
18
Moorend Invertebrate Survey 2012/2013 - Spiders and Harvestmen (3)
Common Name
27.
5.13
7.6.
13
25.6
.13
8.7.
13
21.8
.13
2.9.
13
26.5
.13
10.6
.13
23.6
.13
10.7
.13
27.7
.13
5.8.
13
18.8
.13
8.9.
13
30.5
.13
6.6.
13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
12.7
.13
5.8.
13
18.8
.13
2.9.
13
18.1
0.12
13.5
.13
5.8.
13
18.9
.13
18.9
.13
Araneidae
Lycos idae Alopecosa pulverulenta 1
Lycos idae Trochosa terricola 1 2 1 1 2 2 1 2 2
Lycos idae Trochosa spinipalpis 1 1
Lycos idae Arctosa leopardus 2
Lycos idae Pirata hygrophi lus 2 1 1 1 1 1
Pisauridae Pisaura mirabi l i s Nursery web spider 1
Agelenidae Agelena labyrinthica Labyrinth spider 1
Hahni idae Lathys humi l i s 2
Amaurobidae Amaurobius fenestra l i s 1
Zoridae Zora spinimana 1
Phi lodromidae Phi lodromus a lbidus 1
Thomis idae Xysticus cris tatus 1f 3 1
Thomis idae Ozypti la atomaria 2
Salticidae Marpissa muscosa Nb 2
Salticidae Neon reticulatus 1
Opilionidae
Nemastomatidae Nemastoma bimaculatum 1
Phalangi idae Ol igolophus tridens 1 1 3
Phalangi idae Lacinius ephippiatus 2 15 5
Phalangi idae Mitopus morio 3 5
Phalangi idae Platybunus triangularis 2 4 1 4 9 2 5 2
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA
(Na)or Notable B (Nb)
PITFALL TRAPS
SUCTION
SAMPLING &
BEATING/
SWEEPING
A B C D
19
Moorend Invertebrate Survey 2012/2013 – Beetles (1)
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA (Na)or
Notable B (Nb)
Common Name
27.
5.13
7.6.
13
25.6
.13
8.7.
13
21.8
.13
2.9.
13
26.5
.13
10.6
.13
23.6
.13
10.7
.13
27.7
.13
5.8.
13
18.8
.13
8.9.
13
30.5
.13
6.6.
13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
12.7
.13
5.8.
13
18.8
.13
2.9.
13
Coleoptera
Carabididae Carabus problematicus 2 3 6 1 4 3 1 2 4 3 9 5 7 2 4 13 5 12 14 16
Carabididae Carabus violaceus Violet Ground Beetle 2 3 1 2 1 1
Carabididae Cychrus caraboides 1 2 2 1
Carabididae Nebria brevicol l i s 4 4 1 17 7 3 17 6 5 1 1 2 2 8
Carabididae Nebria sa l ina 8
Carabididae Notiophi lus biguttatus 2 1
Carabididae Notiophi lus germinyi 1
Carabididae Notiophi lus rufipes 1 1
Carabididae Loricera pi l icornis 2 2 2 1 2 1
Carabididae Elaphrus cupreus 2 2 4 1
Carabididae Pterostichus madidus 8 13 26 10 11 15 6 2 2 1 3 2 3 6 9 7 3 18 16 27 56 26 44 49
Carabididae Pterostichus niger 1 1 4 7 4 5
Carabididae Pterostichus nigri ta 21 13 19 7 15 3
Carabididae Pterostichus nigri ta/rhaeticus 14 2
Carabididae Pterostichus s trenuus 1
Carabididae Abax para l lelepipedus 8 11 22 16 3 4 7 12 12 2 5 3 3 6 1 7 10 17 9 3 8 3 8 19 20 11 11
Carabididae Calathus rotundicol l i s 2 6 3 2 1 6 1 3
Carabididae Paranchus a lbipes 1
Carabididae Agonum sexpunctatum Na 1 10 1 1 1
Carabididae Amara eurynota 1 8
Carabididae Amara ovata 5 10 1
Carabididae Harpalus latus 1
PITFALL TRAPS
SITE A SITE B Site C Si te D
20
Moorend Invertebrate Survey 2012/2013 – Beetles (2)
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA (Na)or
Notable B (Nb)
Common Name
27.
5.13
7.6.
13
25.6
.13
8.7.
13
21.8
.13
2.9.
13
26.5
.13
10.6
.13
23.6
.13
10.7
.13
27.7
.13
5.8.
13
18.8
.13
8.9.
13
30.5
.13
6.6.
13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
12.7
.13
5.8.
13
18.8
.13
2.9.
13
Coleoptera
Leiodidae Catops chrysomeloides 1
Leiodidae Catops ful iginosus 1
Leiodidae Catops nigricans 1 1
Si lphidae Si lpha atrata 1 2 3 6 7 2 4 5 1 2
Si lphidae Nicrophorus vespi l loides 1 1 2 5
Staphi l inidae Tachinus s ignatus 1 1 5 1
Staphi l inidae Phi lonthus decorus 1 3 1 1
Staphi l inidae Phi lonthus tenuicornis 8 2 1 6 14 12 8
Staphi l inidae Ocypus olens Devi l 's Coach-horse 1 1 6
Staphi l inidae Tasgius mors i tans 1
Staphi l inidae Quedius curtipennis 3
Staphi l inidae Quedius ful iginosus 1
Scarabaeidae Serica brunnea Brown Chafer 2
Scarabaeidae Hopl ia phi lanthus Welsh Chafer 1
Byrrhidae Byrrhus pi lula Pi l l Beetle 1 1
Elateridae Athous haemorrhoidal is 1
Elateridae Agriotes obscurus 1 1
Elateridae Agriotes sputator 1 1
Curcul ionidae Strophosoma melanogrammum Nut Leaf Weevi l 1 1
PITFALL TRAPS
SITE A SITE B Site C Si te D
21
Moorend Invertebrate Survey 2012/2013 – Woodlice, Centipedes & Millipedes
Order Fami ly
Scientific Name
+ National Status where
recorded as NotableA (Na)or
Notable B (Nb)
Common name
7-6
25-6
8-7
5-8
21-8
2-9
26-5
10-6
27-7
30-5
17-6
1-7
15-7
31-7
12-8
27-8
6-9
28-5
7-6
24-6
8-7
22-7
5-8
18-8
Chilopoda
Geophi l idae Geophi lus easoni an earth centipede 1 3
Lithobi idae Li thobius microps a s tone centipede 3
Lithobi idae Li thobius muticus Nb a s tone centipede 4 1 5 1 1
Lithobi idae Li thobius variegatus a s tone centipede 2 2
Diplopoda
Jul idae Cyl indroiulus punctatus Blunt-ta i led Mi l l ipede 3 1 1
Jul idae Ophyiulus pi losus a jul id snake mi l l ipede 2 2 1 2 1
Jul idae Tachypodoiulus niger White-legged Mi l l ipede 1 2 1 1
Polydesmidae Brachydesmus superus a flat-back mi l lepede 1
Polydesmidae Polydesmus angustus a flat-back mi l lepede 1 2 1 4 3 2 5
Isopoda
Ligi idae Ligidium hypnorum Carr Slater 10 28 16 2 1 1 4 8 2
Oniscidae Oniscus asel lus Shiny Woodlouse 1 2 1 1
Phi losci idae Phi loscia muscorum Striped Woodlouse 2 4 5 9 6 2 1 2 3 13 17 8 6 2 2 1 2 11 14 13 2
Porcel l ionidae Porcel l io scaber Rough Woodlouse 1 2 22 3
Trichoniscidae Trichoniscus pus i l lus agg. Common Pygmy Woodlouse 1
PITFALL TRAPS
A B C D
22
Moorend Invertebrate Survey 2012/2013 – Other Groups
Pan Trap
Order
Family
Scientific name Common name
30.5
.13
17.6
.13
1.7.
13
15.7
.13
31.7
.13
12.8
.13
27.8
.13
6.9.
13
28.5
.13
7.6.
13
24.6
.13
8.7.
13
22.7
.13
5.8.
13
18.8
.13
13.
5.13
Dermaptera
Forficul idae Forficula auricularia Common Earwig 1 1 1
Diptera
Rhagionidae Chrysopi lus as i l i formis a snipe fly 1
Rhagionidae Rhagio scolopacea a snipe fly 1 2
Syrphidae Platycheirus a lbimanus a hoverfly 1m 1f
Syrphidae Chei los ia a lbi tarsus White footed Hoverfly 1m
Aculeata
Apidae Bombus pratorum Early Bumblebee 1 queen
Apidae Nomada goodeniana Gooden's Nomad Bee 1m
Megachi l idae Osmia bicornis Red Mason Bee 4m
Andrenidae Andrena haemorrhoa Early Mining Bee 1m
Andrenidae Andrena chrysosceles 1m
Andrenidae Andrena subopaca 1m 1f
Mollusca
Arionidae Arion ater agg. Great Black Slug x x x x
Arionidae Arion hortens is agg. Garden Slug x x x x
Arionidae Arion subfuscus Dusky Slug x x 2 x x
C D
Pitfall Traps
x Records presence of species - majori ty of s lugs were hal f rotted and uncountable