Biodiversity Data Journal :
Data Paper (Biosciences)
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Corresponding author: Jagoba Malumbres-Olarte (jagoba.malumbres.olarte@gmail.com)
Academic editor: Jeremy Miller
Received: 22 Oct 2019 | Accepted: 12 Dec 2019 | Published: 14 Jan 2020
© 2020 Jagoba Malumbres-Olarte, Mário Boieiro, Pedro Cardoso, Rui Carvalho, Luís Carlos Crespo, Rosalina Gabriel, Nuria Macías Hernández, Octávio Paulo, Fernando Pereira, Carla Rego, Alejandra Ros-Prieto, Isamberto Silva, Ana Vieira, François Rigal, Paulo Borges
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Malumbres-Olarte J, Boieiro M, Cardoso P, Carvalho R, Crespo LCF, Gabriel R, Macías Hernández N, Paulo OS, Pereira F, Rego C, Ros-Prieto A, Silva I, Vieira A, Rigal F, Borges PAV (2020) Standardised inventories of spiders (Arachnida, Araneae) of Macaronesia II: The native forests and dry habitats of Madeira archipelago (Madeira and Porto Santo islands). Biodiversity Data Journal 8: e47502. https://doi.org/10.3897/BDJ.8.e47502
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Here we present the data obtained from the samples collected as part of a large research project (MACDIV) which aims at understanding the drivers of spider (Araneae) community assembly in Macaronesian islands. To obtain the data, we applied the sampling protocol COBRA (Conservation Oriented Biodiversity Rapid Assessment), in twelve 50 m x 50 m native forest plots and five dry habitat plots on the island of Madeiraand in 5 dry habitat plots on the island of Porto Santo. Through this publication, we contribute to the knowledge of the arachnofauna of the Madeiran archipelago.
From the samples that we collected, we obtained a total of 14,902 specimens, of which 49% were adults (7,263). We identified these specimens to 87 species and 18 morphospecies (undescribed), belonging to 26 families. Species of the family Linyphiidae dominated the samples, with 24 (morpho)species. Out of the 105 recorded (morpho)species, 34 were endemic, 26 native non-endemic, 22 introduced and 23 species of unknown origin. We report seven new records of possibly recently introduced species in the Madeiran archipelago. We also present 21 new records for Madeira island and 32 for Porto Santo (33 for the whole archipelago).
Arthropoda, Araneae, Madeira, Porto Santo, native forest, dry habitat, exotic species, standardised sampling
The north Atlantic archipelago of Madeira is composed of the volcanic islands of Madeira, Porto Santo and the Desertas, as well several islets. At approximately 700 km from the African coast and at more than 400 km from the Canary Islands, it is the second most isolated Macaronesian archipelago, after the Azores. This intermediate distance, combined with an geological age of 5-27 My, has allowed frequent colonisation rates and enough diversification time to generate diverse species communities (
The laurisilva is indeed a unique and iconic ecosystem, that is often seen as representative of the Macaronesian archipelagos as a whole and contains a great deal of endemic species (
The need for an update in many taxa is exemplified by spiders. Although, according to the last available checklist (
This publication is the second of a series on Macaronesian spider fauna (see
We established twenty-two 50 m × 50 m plots, grouped according to habitat and between-plot distances. Twelve plots were located in areas covered with laurisilva and grouped in two sets of six. Within each set, plots were placed at increasing distances from a first, reference plot (Table
Plot name (island) |
Habitat |
Longitude |
Latitude |
Madeira d1 |
Dry |
-16.70261 |
32.74633 |
Madeira d2 |
Dry |
-16.70307 |
32.74691 |
Madeira d3 |
Dry |
-16.71886 |
32.74618 |
Madeira d4 |
Dry |
-16.75788 |
32.72623 |
Madeira d5 |
Dry |
-16.8138 |
32.66138 |
Madeira f1 |
Forest |
-16.9371 |
32.79582 |
Madeira f2 |
Forest |
-16.93654 |
32.79801 |
Madeira f3 |
Forest |
-16.9347 |
32.80462 |
Madeira f4 |
Forest |
-16.90233 |
32.78108 |
Madeira f5 |
Forest |
-16.88654 |
32.73302 |
Madeira f6 |
Forest |
-17.15781 |
32.82816 |
Madeira f7 |
Forest |
-17.15871 |
32.82706 |
Madeira f8 |
Forest |
-17.15336 |
32.82306 |
Madeira f9 |
Forest |
-17.11369 |
32.79154 |
Madeira f10 |
Forest |
-17.05499 |
32.7746 |
Porto_Santo 1 |
Dry |
-16.30453 |
33.09135 |
Porto_Santo 2 |
Dry |
-16.30536 |
33.0921 |
Porto_Santo 3 |
Dry |
-16.32426 |
33.09041 |
Porto_Santo 4 |
Dry |
-16.36452 |
33.07376 |
Porto_Santo 5 |
Dry |
-16.38267 |
33.03804 |
Location of plots on Madeira and Porto Santo islands. MF: Madeira forest habitat plots. MD: Madeira dry habitat plots. PSD: Porto Santo dry habitat plots. Numbers correspond to plot numbers.
We applied two versions of the optimised and standardised COBRA protocol (Conservation Oriented Biodiversity Rapid Assessment) (
Madeira and Porto Santo islands, Madeira, Macaronesia, Portugal
32.66138 and 33.0921 Latitude; -17.15871 and -16.30453 Longitude.
Rank | Scientific Name | Common Name |
---|---|---|
order | Araneae | Spiders |
Sampling in the native forest occurred in August 2016. Sampling in dry habitats occurred in April 2017.
The following data table includes all the records for which a taxonomic identification of the species was possible. The dataset submitted to GBIF is structured as a sample event dataset, with two tables: event (as core) and occurrences. The data in this sampling event resource have been published as a Darwin Core Archive (DwCA), which is a standardised format for sharing biodiversity data as a set of one or more data tables. The core data table contains 562 records (eventID). One extension data table also exists with 3281 occurrences. An extension record supplies extra information about a core record. The number of records in each extension data table is illustrated in the IPT link. This IPT archives the data and thus serves as the data repository. The data and resource metadata are available for downloading in the downloads section.
Column label | Column description |
---|---|
Table of Sampling Events | Table with sampling events data (beginning of table) |
id | Unique identification code for sampling event data |
eventID | Identifier of the events, unique for the dataset |
samplingProtocol | The sampling protocol used to capture the species |
sampleSizeValue | The numeric amount of time spent in each sampling |
sampleSizeUnit | The unit of the sample size value |
samplingEffort | The amount of time of each sampling |
eventDate | Date or date range the record was collected |
eventTime | Time of the day the record was collected |
startDayOfYear | The earliest ordinal day of the year on which the event occurred |
endDayOfYear | The latest ordinal day of the year on which the event occurred |
year | Year of the event |
month | Month of the event |
day | Day of the event |
habitat | The surveyed habitat |
fieldNumber | The code given to each sample |
locationID | Identifier of the location |
islandGroup | Name of archipelago |
island | Name of the island |
country | Country of the sampling site |
countryCode | ISO code of the country of the sampling site |
stateProvince | Name of the region of the sampling site |
locationRemarks | Details on the locality site |
decimalLatitude | Approximate centre point decimal latitude of the field site in GPS coordinates |
decimalLongitude | Details on the locality site |
Details on the locality site | The reference point for the various coordinate systems used in mapping the earth |
coordinateUncertaintyInMetres | Uncertainty of the coordinates of the centre of the sampling plot |
coordinatePrecision | Precision of the coordinates |
georeferenceSources | A list (concatenated and separated) of maps, gazetteers or other resources used to georeference the Location, described specifically enough to allow anyone in the future to use the same resources. |
Table of Species Occurrence | Table with species abundance data (beginning of new table) |
id | Unique identification code for species abundance data |
type | Type of the record, as defined by the Public Core standard |
licence | Reference to the licence under which the record is published |
institutionID | The identity of the institution publishing the data |
collectionID | The identity of the collection publishing the data |
institutionCode | The code of the institution publishing the data |
collectionCode | The code of the collection where the specimens are conserved |
datasetName | Name of the dataset |
basisOfRecord | The nature of the data record |
dynamicProperties | The name of the scientific project funding the sampling |
occurrenceID | Identifier of the record, coded as a global unique identifier |
catalogNumber | Record number of the specimen in the collection |
recordedBy | Name of the person who performed the sampling of the specimens |
individualCount | Total number of individuals captured |
organismQuantityType | The unit of the identification of the organisms |
sex | The sex and quantity of the individuals captured |
lifeStage | The life stage of the organisms captured |
establishmentMeans | The process of establishment of the species in the location, using a controlled vocabulary: 'naturalised', 'introduced', 'endemic', "unknown" |
occurrenceStatus | Information about the presence/absence of the species |
eventID | A unique identifier of an occurrence |
identifiedBy | Name of the person who made the identification |
dateIdentified | Date on which the record was identified |
scientificName | Complete scientific name including author and year |
kingdom | Kingdom name |
phylum | Phylum name |
class | Class name |
order | Order name |
family | Family name |
genus | Genus name |
specificEpithet | Specific epithet |
taxonRank | Lowest taxonomic rank of the record |
scientificNameAuthorship | Name of the author of the lowest taxon rank included in the record |
We collected a total of 14,902 specimens – of which 49% were adults (7,263) - belonging to 105 (morpho) species and 26 families (Tables
Abundance, biogeographic category and previous records of (morpho)species in six of the forest plots on Madeira island. Abbreviations: Plot names: Madeira forest (MF); Madeira dry habitat (MD); Porto Santo dry habitat (PSD). Biogeographic category (Biog. cat): Endemic (END); Introduced (INT); Macaronesian (MAC); Native non-endemic (NAT); Unknown (UK). Previous records (Prev. Rec.): Madeira (M), Porto Santo (PS), Not recorded (No). Reference for previous records: List of Madeiran Fauna (LMF) (
Family |
Species |
Biog.Cat. |
Prev. Rec. |
MF1 |
MF2 |
MF3 |
MF4 |
MF5 |
MF6 |
Agelenidae |
Eratigena feminea (Simon, 1870) |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Agelenidae |
Synaphris saphrynis Lopardo, Hormiga & Melic, 2007 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Agelenidae |
Tegenaria domestica (Clerck, 1757) |
I |
M |
0 |
0 |
1 |
0 |
0 |
1 |
Araneidae |
Agalenatea redii (Scopoli, 1763) |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Araniella maderiana (Kulczyński, 1905) |
N |
M, PS |
0 |
0 |
0 |
2 |
0 |
0 |
Araneidae |
Argiope trifasciata (Forskål, 1775) |
UK |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Cyclosa maderiana Kulczyński, 1899 |
N |
M |
0 |
0 |
0 |
0 |
1 |
0 |
Araneidae |
Cyrtophora citricola (Forskål, 1775) |
I |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Mangora acalypha (Walckenaer, 1802) |
I |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Neoscona crucifera (Lucas, 1838) |
I |
M, PS |
1 |
1 |
5 |
3 |
7 |
2 |
Araneidae |
Zygiella x-notata (Clerck, 1757) |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Cheiracanthiidae |
Cheiracanthium albidulum (Blackwall, 1859) |
E |
M, PS |
15 |
5 |
28 |
2 |
8 |
12 |
Clubionidae |
Porrhoclubiona decora (Blackwall, 1859) |
N |
M, PS |
1 |
0 |
0 |
2 |
0 |
3 |
Dictynidae |
Lathys affinis (Blackwall, 1862) |
E |
M, PS |
0 |
1 |
8 |
0 |
11 |
0 |
Dictynidae |
Nigma puella (Simon, 1870) |
UK |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Dysderidae |
Dysdera coiffaiti Denis, 1962 |
E |
M |
0 |
1 |
1 |
0 |
0 |
0 |
Dysderidae |
Dysdera crocata C.L.Koch, 1838 |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Drassodes lutescens (C.L.Koch, 1839) |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus sp. 158 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus sp. 164 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus omissus (O. Pickard-Cambridge, 1872) |
N |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Heser hispanus Senglet, 2012 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Macarophaeus cultior (Kulczyński, 1899) |
E |
No |
0 |
0 |
2 |
0 |
0 |
0 |
Gnaphosidae |
Micaria pallipes (Lucas, 1846) |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Setaphis carmeli (O.P.-Cambridge, 1872) |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Trachyzelotes holosericeus (Simon, 1878) |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Trachyzelotes lyonneti (Audouin, 1826) |
UK |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Zelotes aeneus (Simon, 1878) |
I |
No (LMF), M (WSC) |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Zelotes tenuis (L.Koch, 1866) |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Zimirina lepida (Blackwall, 1859) |
E |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Agyneta canariensis Wunderlich, 1987 |
N |
No (LMF), M (WSC) |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Agyneta fuscipalpa (C.L.Koch, 1836) |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Canariellanum sp. 21 |
E |
No |
0 |
0 |
0 |
0 |
0 |
10 |
Linyphiidae |
Centromerus variegatus Denis, 1962 |
E |
M |
0 |
0 |
0 |
2 |
0 |
0 |
Linyphiidae |
Ceratinopsis sp. 111 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Ceratinopsis acripes (Denis, 1962) |
N |
M |
3 |
1 |
2 |
2 |
4 |
2 |
Linyphiidae |
Ceratinopsis infuscata (Denis, 1962) |
E |
M |
0 |
0 |
0 |
1 |
2 |
0 |
Linyphiidae |
Ceratinopsis sp. 233 |
E |
No |
0 |
0 |
1 |
0 |
0 |
0 |
Linyphiidae |
Ceratinopsis sp. 58 |
E |
No |
0 |
0 |
1 |
0 |
0 |
0 |
Linyphiidae |
Diplocephalus graecus (O.P.-Cambridge, 1873) |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Entelecara schmitzi Kulczyński, 1905 |
UK |
M |
2 |
5 |
5 |
0 |
5 |
0 |
Linyphiidae |
Frontinellina dearmata (Kulczyński, 1899) |
E |
M |
6 |
4 |
3 |
7 |
62 |
0 |
Linyphiidae |
Frontiphantes fulgurenotatus (Schenkel, 1938) |
E |
M |
0 |
0 |
1 |
0 |
3 |
4 |
Linyphiidae |
Lepthyphantes mauli Wunderlich, 1992 |
E |
M |
0 |
0 |
1 |
0 |
0 |
0 |
Linyphiidae |
Microctenonyx subitaneus (O.P.-Cambridge, 1875) |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Microlinyphia johnsoni (Blackwall, 1859) |
N |
M, PS |
3 |
6 |
7 |
12 |
21 |
8 |
Linyphiidae |
Ostearius melanopygius (O.P.-Cambridge, 1880) |
I |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Palliduphantes schmitzi (Kulczyński, 1899) |
N |
M |
5 |
0 |
1 |
10 |
0 |
17 |
Linyphiidae |
Parapelecopsis nemoralioides (O. Pickard-Cambridge, 1884) |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Pelecopsis inedita (O.P.-Cambridge, 1875) |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Tenuiphantes sp. 259 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Tenuiphantes tenebricoloides (Schenkel, 1938) |
E |
M |
0 |
0 |
0 |
1 |
1 |
0 |
Linyphiidae |
Tenuiphantes tenuis (Blackwall, 1852) |
I |
M, PS |
50 |
35 |
53 |
43 |
34 |
66 |
Linyphiidae |
Turinyphia maderiana (Schenkel, 1938) |
E |
M |
0 |
0 |
0 |
0 |
5 |
1 |
Liocranidae |
Mesiotelus cf. grancanariensis Wunderlich, 1992 |
N |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Lycosidae |
Hogna insularum (Kulczyński, 1899) |
E |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Lycosidae |
Hogna schmitzi Wunderlich, 1992 |
E |
PS |
0 |
0 |
0 |
0 |
0 |
0 |
Lycosidae |
Pardosa proxima (C.L.Koch, 1847) |
N |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Mimetidae |
Ero aphana (Walckenaer, 1802) |
N |
M, PS |
0 |
0 |
1 |
0 |
0 |
1 |
Mysmenidae |
Trogloneta madeirensis Wunderlich, 1987 |
E |
M |
0 |
2 |
3 |
4 |
1 |
13 |
Nesticidae |
Eidmannella pallida (Emerton, 1875) |
I |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Oecobiidae |
Oecobius similis Kulczyński, 1909 |
N |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Oonopidae |
Gamasomorpha insularis Simon, 1907 |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Oonopidae |
Oonops cf. pulcher Templeton, 1835 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Oonopidae |
Opopaea concolor (Blackwall, 1859) |
N |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Oonopidae |
Orchestina sp. 160 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Oxyopidae |
Oxyopes sp. 80 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Philodromus insulanus Kulczyński, 1905 |
E |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Philodromus MAD266 |
UK |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Thanatus vulgaris Simon, 1870 |
UK |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Pholcidae |
Pholcus madeirensis Wunderlich, 1987 |
E |
M |
3 |
1 |
7 |
0 |
0 |
0 |
Salticidae |
Chalcoscirtus sublestus (Blackwall, 1867) |
N |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Macaroeris cf. desertensis Wunderlich, 1992 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Macaroeris cf. diligens (Blackwall, 1867) |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Macaroeris diligens (Blackwall, 1867) |
N |
M, PS |
3 |
0 |
1 |
1 |
2 |
0 |
Salticidae |
Macaroeris sp. 8 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Pellenes maderianus Kulczyński, 1905 |
N |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Scytodidae |
Scytodes velutina Heineken & Lowe, 1832 |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Segestriidae |
Ariadna maderiana Warburton, 1892 |
E |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Segestriidae |
Segestria florentina (Rossi, 1790) |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Tetragnathidae |
Meta stridulans Wunderlich, 1987 |
E |
M |
8 |
7 |
9 |
1 |
2 |
15 |
Theridiidae |
Cryptachaea blattea (Urquhart, 1886) |
I |
No |
3 |
0 |
13 |
9 |
3 |
0 |
Theridiidae |
Dipoenata longitarsis (Denis, 1962) |
E |
M |
0 |
0 |
0 |
1 |
0 |
0 |
Theridiidae |
Echinotheridion gibberosum (Kulczyński, 1899) |
N |
M |
37 |
28 |
63 |
4 |
32 |
7 |
Theridiidae |
Enoplognatha diversa (Blackwall, 1859) |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Enoplognatha sattleri Bösenberg, 1895 |
N |
M |
0 |
0 |
0 |
0 |
1 |
0 |
Theridiidae |
Episinus maderianus Kulczyński, 1905 |
N |
M |
182 |
59 |
160 |
42 |
33 |
84 |
Theridiidae |
Kochiura aulica (C.L.Koch, 1838) |
N |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Laseola sp. 268 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Macaridion barreti (Kulczyński, 1899) |
N |
M |
55 |
63 |
112 |
1 |
60 |
15 |
Theridiidae |
Paidiscura orotavensis (Schmidt, 1968) |
N |
M |
0 |
13 |
1 |
2 |
0 |
0 |
Theridiidae |
Rhomphaea nasica (Simon, 1873) |
I |
M |
0 |
1 |
2 |
0 |
0 |
1 |
Theridiidae |
Rugathodes madeirensis Wunderlich, 1987 |
E |
M |
48 |
2 |
2 |
156 |
8 |
96 |
Theridiidae |
Steatoda grossa (C.L.Koch, 1838) |
I |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Steatoda nobilis (Thorell, 1875) |
N |
M, PS |
1 |
1 |
4 |
0 |
1 |
0 |
Theridiidae |
Theridion hannoniae Denis, 1945 |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Theridion musivivum Schmidt, 1956 |
N |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Theridion sp. 89 |
E |
No |
4 |
2 |
2 |
2 |
11 |
1 |
Thomisidae |
Misumena cf. nigromaculata Denis, 1963 |
E |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Thomisidae |
Misumena spinifera (Blackwall, 1862) |
N |
M, PS |
1 |
1 |
2 |
0 |
0 |
1 |
Thomisidae |
Thomisus onustus Walckenaer, 1805 |
I |
No |
0 |
0 |
0 |
0 |
0 |
0 |
Thomisidae |
Xysticus nubilus Simon, 1875 |
UK |
M, PS |
0 |
0 |
0 |
0 |
0 |
0 |
Uloboridae |
Hyptiotes flavidus (Blackwall, 1862) |
N |
M |
13 |
3 |
3 |
11 |
40 |
0 |
Uloboridae |
Uloborus walckenaerius Latreille, 1806 |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Zodariidae |
Zodarion styliferum (Simon, 1870) |
UK |
M |
0 |
0 |
0 |
0 |
0 |
0 |
Species richness |
21 |
22 |
32 |
24 |
25 |
21 |
Abundance, biogeographic category and previous records of (morpho)species in five of the forest plots and two of the dry habitat plots on Madeira island. Abbreviations: Madeira forest plot (MF), Madeira dry plot (MD).
Family |
Species |
MF7 |
MF8 |
MF9 |
MF10 |
MF11 |
MF12 |
MD1 |
MD2 |
Agelenidae |
Eratigena feminea (Simon, 1870) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Agelenidae |
Synaphris saphrynis Lopardo, Hormiga & Melic 2007 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Agelenidae |
Tegenaria domestica (Clerck, 1757) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Agalenatea redii (Scopoli, 1763) |
0 |
0 |
0 |
0 |
0 |
0 |
7 |
22 |
Araneidae |
Araniella maderiana (Kulczyński, 1905) |
3 |
0 |
3 |
0 |
0 |
1 |
0 |
0 |
Araneidae |
Argiope trifasciata (Forskål, 1775) |
0 |
0 |
0 |
0 |
0 |
0 |
10 |
17 |
Araneidae |
Cyclosa maderiana Kulczyński, 1899 |
0 |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
Araneidae |
Cyrtophora citricola (Forskål, 1775) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Araneidae |
Mangora acalypha (Walckenaer, 1802) |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
Araneidae |
Neoscona crucifera (Lucas, 1838) |
2 |
1 |
1 |
1 |
1 |
2 |
0 |
0 |
Araneidae |
Zygiella x-notata (Clerck, 1757) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Cheiracanthiidae |
Cheiracanthium albidulum (Blackwall, 1859) |
34 |
11 |
36 |
9 |
15 |
43 |
0 |
0 |
Clubionidae |
Porrhoclubiona decora (Blackwall, 1859) |
2 |
0 |
3 |
2 |
0 |
1 |
1 |
2 |
Dictynidae |
Lathys affinis (Blackwall, 1862) |
6 |
1 |
2 |
2 |
0 |
3 |
0 |
0 |
Dictynidae |
Nigma puella (Simon, 1870) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Dysderidae |
Dysdera coiffaiti Denis, 1962 |
3 |
1 |
2 |
0 |
0 |
0 |
0 |
0 |
Dysderidae |
Dysdera crocata C.L.Koch, 1838 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
5 |
Gnaphosidae |
Drassodes lutescens (C.L.Koch, 1839) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus sp. 158 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus sp. 164 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Haplodrassus omissus (O. Pickard-Cambridge, 1872) |
0 |
0 |
0 |
0 |
0 |
0 |
13 |
1 |
Gnaphosidae |
Heser hispanus Senglet, 2012 |
0 |
0 |
0 |
0 |
0 |
0 |
35 |
23 |
Gnaphosidae |
Macarophaeus cultior (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Micaria pallipes (Lucas, 1846) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Setaphis carmeli (O.P.-Cambridge, 1872) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Trachyzelotes holosericeus (Simon, 1878) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Trachyzelotes lyonneti (Audouin, 1826) |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
2 |
Gnaphosidae |
Zelotes aeneus (Simon, 1878) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Zelotes tenuis (L.Koch, 1866) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Gnaphosidae |
Zimirina lepida (Blackwall, 1859) |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
0 |
Linyphiidae |
Agyneta canariensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Agyneta fuscipalpa (C.L.Koch, 1836) |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
9 |
Linyphiidae |
Canariellanum sp. 21 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Centromerus variegatus Denis, 1962 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Ceratinopsis sp. 111 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
Linyphiidae |
Ceratinopsis acripes (Denis, 1962) |
2 |
1 |
1 |
1 |
4 |
6 |
0 |
0 |
Linyphiidae |
Ceratinopsis infuscata (Denis, 1962) |
0 |
2 |
8 |
0 |
1 |
0 |
0 |
0 |
Linyphiidae |
Ceratinopsis sp. 233 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Ceratinopsis sp. 58 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Diplocephalus graecus (O.P.-Cambridge, 1873) |
0 |
0 |
0 |
0 |
0 |
0 |
103 |
375 |
Linyphiidae |
Entelecara schmitzi Kulczyński, 1905 |
1 |
0 |
2 |
5 |
2 |
7 |
0 |
0 |
Linyphiidae |
Frontinellina dearmata (Kulczyński, 1899) |
7 |
1 |
4 |
8 |
32 |
43 |
0 |
0 |
Linyphiidae |
Frontiphantes fulgurenotatus (Schenkel, 1938) |
14 |
0 |
1 |
0 |
2 |
1 |
0 |
0 |
Linyphiidae |
Lepthyphantes mauli Wunderlich, 1992 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Microctenonyx subitaneus (O.P.-Cambridge, 1875) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
Linyphiidae |
Microlinyphia johnsoni (Blackwall, 1859) |
2 |
3 |
4 |
8 |
8 |
27 |
0 |
0 |
Linyphiidae |
Ostearius melanopygius (O.P.-Cambridge, 1880) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Palliduphantes schmitzi (Kulczyński, 1899) |
3 |
0 |
0 |
5 |
1 |
3 |
0 |
0 |
Linyphiidae |
Parapelecopsis nemoralioides (O. Pickard-Cambridge, 1884) |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
3 |
Linyphiidae |
Pelecopsis inedita (O.P.-Cambridge, 1875) |
0 |
0 |
0 |
0 |
0 |
0 |
10 |
15 |
Linyphiidae |
Tenuiphantes sp. 259 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Linyphiidae |
Tenuiphantes tenebricoloides (Schenkel, 1938) |
0 |
0 |
0 |
0 |
1 |
1 |
0 |
0 |
Linyphiidae |
Tenuiphantes tenuis (Blackwall, 1852) |
31 |
58 |
13 |
49 |
25 |
56 |
0 |
4 |
Linyphiidae |
Turinyphia maderiana (Schenkel, 1938) |
0 |
2 |
0 |
1 |
4 |
0 |
0 |
0 |
Liocranidae |
Mesiotelus cf. grancanariensis Wunderlich, 1992 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
Lycosidae |
Hogna insularum (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
60 |
49 |
Lycosidae |
Hogna schmitzi Wunderlich, 1992 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Lycosidae |
Pardosa proxima (C.L.Koch, 1847) |
0 |
0 |
3 |
0 |
0 |
0 |
0 |
0 |
Mimetidae |
Ero aphana (Walckenaer, 1802) |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
Mysmenidae |
Trogloneta madeirensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
Nesticidae |
Eidmannella pallida (Emerton, 1875) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Oecobiidae |
Oecobius similis Kulczyński, 1909 |
0 |
0 |
0 |
0 |
0 |
0 |
8 |
10 |
Oonopidae |
Gamasomorpha insularis Simon, 1907 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Oonopidae |
Oonops cf. pulcher Templeton, 1835 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Oonopidae |
Opopaea concolor (Blackwall, 1859) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Oonopidae |
Orchestina sp. 160 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Oxyopidae |
Oxyopes sp. 80 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Philodromus insulanus Kulczyński, 1905 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Philodromus MAD266 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Philodromidae |
Thanatus vulgaris Simon, 1870 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
6 |
Pholcidae |
Pholcus madeirensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Chalcoscirtus sublestus (Blackwall, 1867) |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
Salticidae |
Macaroeris cf. desertensis Wunderlich, 1992 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Macaroeris cf. diligens (Blackwall, 1867) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Salticidae |
Macaroeris diligens (Blackwall, 1867) |
4 |
1 |
8 |
5 |
0 |
1 |
0 |
0 |
Salticidae |
Macaroeris sp. 8 |
0 |
0 |
0 |
0 |
0 |
0 |
5 |
5 |
Salticidae |
Pellenes maderianus Kulczyński, 1905 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
Scytodidae |
Scytodes velutina Heineken & Lowe, 1832 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Segestriidae |
Ariadna maderiana Warburton, 1892 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Segestriidae |
Segestria florentina (Rossi, 1790) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Tetragnathidae |
Meta stridulans Wunderlich, 1987 |
3 |
1 |
3 |
10 |
2 |
1 |
0 |
0 |
Theridiidae |
Cryptachaea blattea (Urquhart, 1886) |
2 |
3 |
5 |
3 |
6 |
3 |
1 |
0 |
Theridiidae |
Dipoenata longitarsis (Denis, 1962) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Echinotheridion gibberosum (Kulczyński, 1899) |
39 |
3 |
9 |
1 |
22 |
71 |
0 |
0 |
Theridiidae |
Enoplognatha diversa (Blackwall, 1859) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Enoplognatha sattleri Bösenberg, 1895 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Episinus maderianus Kulczyński, 1905 |
64 |
14 |
41 |
38 |
18 |
11 |
0 |
0 |
Theridiidae |
Kochiura aulica (C.L.Koch, 1838) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Laseola sp. 268 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Macaridion barreti (Kulczyński, 1899) |
14 |
0 |
17 |
19 |
19 |
119 |
0 |
0 |
Theridiidae |
Paidiscura orotavensis (Schmidt, 1968) |
3 |
1 |
1 |
15 |
2 |
0 |
0 |
0 |
Theridiidae |
Rhomphaea nasica (Simon, 1873) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Rugathodes madeirensis Wunderlich, 1987 |
1 |
1 |
0 |
0 |
5 |
6 |
0 |
0 |
Theridiidae |
Steatoda grossa (C.L.Koch, 1838) |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
4 |
Theridiidae |
Steatoda nobilis (Thorell, 1875) |
6 |
7 |
2 |
0 |
2 |
0 |
0 |
0 |
Theridiidae |
Theridion hannoniae Denis, 1945 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Theridiidae |
Theridion musivivum Schmidt, 1956 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
Theridiidae |
Theridion sp. 89 |
4 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
Thomisidae |
Misumena cf. nigromaculata Denis, 1963 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Thomisidae |
Misumena spinifera (Blackwall, 1862) |
1 |
0 |
4 |
0 |
0 |
2 |
0 |
0 |
Thomisidae |
Thomisus onustus Walckenaer, 1805 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Thomisidae |
Xysticus nubilus Simon, 1875 |
0 |
0 |
0 |
0 |
0 |
0 |
9 |
2 |
Uloboridae |
Hyptiotes flavidus (Blackwall, 1862) |
10 |
1 |
5 |
2 |
15 |
8 |
0 |
0 |
Uloboridae |
Uloborus walckenaerius Latreille, 1806 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Zodariidae |
Zodarion styliferum (Simon, 1870) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Species richness |
26 |
21 |
24 |
22 |
22 |
24 |
22 |
26 |
Abundance of (morpho)species in three of the plots on Madeira island and in the plots on Porto Santo island. Abbreviations: Madeira dry plot (MD), Porto Santo plot (PS).
Family |
Species |
MD3 |
MD4 |
MD5 |
PSD1 |
PSD2 |
PSD3 |
PSD4 |
PSD5 |
Total |
Agelenidae |
Eratigena feminea (Simon, 1870) |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
1 |
Agelenidae |
Synaphris saphrynis Lopardo, Hormiga & Melic, 2007 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
19 |
19 |
Agelenidae |
Tegenaria domestica (Clerck, 1757) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Araneidae |
Agalenatea redii (Scopoli, 1763) |
2 |
28 |
19 |
1 |
1 |
0 |
0 |
0 |
80 |
Araneidae |
Araniella maderiana (Kulczyński, 1905) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
9 |
Araneidae |
Argiope trifasciata (Forskål, 1775) |
1 |
38 |
4 |
0 |
0 |
0 |
0 |
1 |
71 |
Araneidae |
Cyclosa maderiana Kulczyński, 1899 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
Araneidae |
Cyrtophora citricola (Forskål, 1775) |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
1 |
Araneidae |
Mangora acalypha (Walckenaer, 1802) |
1 |
7 |
22 |
1 |
0 |
0 |
0 |
0 |
33 |
Araneidae |
Neoscona crucifera (Lucas, 1838) |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
28 |
Araneidae |
Zygiella x-notata (Clerck, 1757) |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
1 |
Cheiracanthiidae |
Cheiracanthium albidulum (Blackwall, 1859) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
218 |
Clubionidae |
Porrhoclubiona decora (Blackwall, 1859) |
10 |
7 |
3 |
3 |
3 |
0 |
0 |
9 |
52 |
Dictynidae |
Lathys affinis (Blackwall, 1862) |
0 |
0 |
0 |
16 |
18 |
2 |
0 |
0 |
70 |
Dictynidae |
Nigma puella (Simon, 1870) |
0 |
0 |
15 |
0 |
0 |
0 |
0 |
0 |
15 |
Dysderidae |
Dysdera coiffaiti Denis, 1962 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
8 |
Dysderidae |
Dysdera crocata C.L.Koch, 1838 |
5 |
8 |
18 |
2 |
0 |
3 |
0 |
0 |
43 |
Gnaphosidae |
Drassodes lutescens (C.L.Koch, 1839) |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
1 |
Gnaphosidae |
Haplodrassus sp. 158 |
0 |
0 |
0 |
18 |
7 |
0 |
25 |
18 |
68 |
Gnaphosidae |
Haplodrassus sp. 164 |
0 |
0 |
0 |
6 |
5 |
0 |
5 |
2 |
18 |
Gnaphosidae |
Haplodrassus omissus (O. Pickard-Cambridge, 1872) |
6 |
0 |
0 |
0 |
1 |
0 |
13 |
1 |
35 |
Gnaphosidae |
Heser hispanus Senglet, 2012 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
59 |
Gnaphosidae |
Macarophaeus cultior (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Gnaphosidae |
Micaria pallipes (Lucas, 1846) |
1 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
3 |
Gnaphosidae |
Setaphis carmeli (O.P.-Cambridge, 1872) |
0 |
0 |
0 |
1 |
1 |
6 |
0 |
0 |
8 |
Gnaphosidae |
Trachyzelotes holosericeus (Simon, 1878) |
1 |
0 |
0 |
7 |
4 |
1 |
0 |
0 |
13 |
Gnaphosidae |
Trachyzelotes lyonneti (Audouin, 1826) |
0 |
7 |
1 |
4 |
0 |
17 |
0 |
2 |
37 |
Gnaphosidae |
Zelotes aeneus (Simon, 1878) |
0 |
0 |
0 |
4 |
0 |
0 |
2 |
1 |
7 |
Gnaphosidae |
Zelotes tenuis (L.Koch, 1866) |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Gnaphosidae |
Zimirina lepida (Blackwall, 1859) |
0 |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
5 |
Linyphiidae |
Agyneta canariensis Wunderlich, 1987 |
3 |
0 |
0 |
28 |
7 |
3 |
0 |
5 |
46 |
Linyphiidae |
Agyneta fuscipalpa (C.L.Koch, 1836) |
2 |
66 |
15 |
8 |
1 |
23 |
10 |
13 |
150 |
Linyphiidae |
Canariellanum sp. 21 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
10 |
Linyphiidae |
Centromerus variegatus Denis, 1962 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Linyphiidae |
Ceratinopsis sp. 111 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Linyphiidae |
Ceratinopsis acripes (Denis, 1962) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
29 |
Linyphiidae |
Ceratinopsis infuscata (Denis, 1962) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
14 |
Linyphiidae |
Ceratinopsis sp. 233 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Linyphiidae |
Ceratinopsis sp. 58 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Linyphiidae |
Diplocephalus graecus (O.P.-Cambridge, 1873) |
33 |
2 |
6 |
12 |
3 |
76 |
1 |
9 |
620 |
Linyphiidae |
Entelecara schmitzi Kulczyński, 1905 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
34 |
Linyphiidae |
Frontinellina dearmata (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
177 |
Linyphiidae |
Frontiphantes fulgurenotatus (Schenkel, 1938) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
26 |
Linyphiidae |
Lepthyphantes mauli Wunderlich, 1992 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Linyphiidae |
Microctenonyx subitaneus (O.P.-Cambridge, 1875) |
3 |
0 |
0 |
2 |
3 |
8 |
0 |
4 |
26 |
Linyphiidae |
Microlinyphia johnsoni (Blackwall, 1859) |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
110 |
Linyphiidae |
Ostearius melanopygius (O.P.-Cambridge, 1880) |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
0 |
2 |
Linyphiidae |
Palliduphantes schmitzi (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
45 |
Linyphiidae |
Parapelecopsis nemoralioides (O. Pickard-Cambridge, 1884) |
4 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
9 |
Linyphiidae |
Pelecopsis inedita (O.P.-Cambridge, 1875) |
3 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
28 |
Linyphiidae |
Tenuiphantes sp. 259 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
1 |
Linyphiidae |
Tenuiphantes tenebricoloides (Schenkel, 1938) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
Linyphiidae |
Tenuiphantes tenuis (Blackwall, 1852) |
5 |
0 |
14 |
0 |
1 |
2 |
0 |
1 |
540 |
Linyphiidae |
Turinyphia maderiana (Schenkel, 1938) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
13 |
Liocranidae |
Mesiotelus cf. grancanariensis Wunderlich, 1992 |
0 |
0 |
0 |
20 |
5 |
0 |
1 |
2 |
29 |
Lycosidae |
Hogna insularum (Kulczyński, 1899) |
54 |
0 |
1 |
6 |
4 |
32 |
34 |
32 |
272 |
Lycosidae |
Hogna schmitzi Wunderlich, 1992 |
0 |
0 |
0 |
7 |
2 |
0 |
0 |
5 |
14 |
Lycosidae |
Pardosa proxima (C.L.Koch, 1847) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
Mimetidae |
Ero aphana (Walckenaer, 1802) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
Mysmenidae |
Trogloneta madeirensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
25 |
Nesticidae |
Eidmannella pallida (Emerton, 1875) |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
3 |
Oecobiidae |
Oecobius similis Kulczyński, 1909 |
82 |
0 |
152 |
5 |
8 |
28 |
1 |
0 |
294 |
Oonopidae |
Gamasomorpha insularis Simon, 1907 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
Oonopidae |
Oonops cf. pulcher Templeton, 1835 |
2 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
3 |
Oonopidae |
Opopaea concolor (Blackwall, 1859) |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
Oonopidae |
Orchestina sp. 160 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
2 |
Oxyopidae |
Oxyopes sp. 80 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
0 |
2 |
Philodromidae |
Philodromus insulanus Kulczyński, 1905 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Philodromidae |
Philodromus MAD266 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
2 |
Philodromidae |
Thanatus vulgaris Simon, 1870 |
10 |
5 |
0 |
2 |
8 |
0 |
8 |
4 |
49 |
Pholcidae |
Pholcus madeirensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
11 |
Salticidae |
Chalcoscirtus sublestus (Blackwall, 1867) |
2 |
1 |
20 |
3 |
3 |
1 |
1 |
1 |
34 |
Salticidae |
Macaroeris cf. desertensis Wunderlich, 1992 |
0 |
0 |
0 |
7 |
1 |
0 |
2 |
7 |
17 |
Salticidae |
Macaroeris cf. diligens (Blackwall, 1867) |
0 |
0 |
0 |
3 |
7 |
5 |
1 |
26 |
42 |
Salticidae |
Macaroeris diligens (Blackwall, 1867) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
26 |
Salticidae |
Macaroeris sp. 8 |
8 |
4 |
4 |
1 |
0 |
0 |
0 |
0 |
27 |
Salticidae |
Pellenes maderianus Kulczyński, 1905 |
2 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
Scytodidae |
Scytodes velutina Heineken & Lowe, 1832 |
0 |
0 |
3 |
0 |
0 |
0 |
0 |
0 |
3 |
Segestriidae |
Ariadna maderiana Warburton, 1892 |
0 |
0 |
0 |
1 |
1 |
0 |
0 |
0 |
2 |
Segestriidae |
Segestria florentina (Rossi, 1790) |
0 |
3 |
6 |
0 |
0 |
1 |
0 |
0 |
10 |
Tetragnathidae |
Meta stridulans Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
62 |
Theridiidae |
Cryptachaea blattea (Urquhart, 1886) |
0 |
1 |
0 |
0 |
1 |
0 |
0 |
0 |
53 |
Theridiidae |
Dipoenata longitarsis (Denis, 1962) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Theridiidae |
Echinotheridion gibberosum (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
316 |
Theridiidae |
Enoplognatha diversa (Blackwall, 1859) |
1 |
0 |
0 |
0 |
1 |
1 |
1 |
0 |
4 |
Theridiidae |
Enoplognatha sattleri Bösenberg, 1895 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Theridiidae |
Episinus maderianus Kulczyński, 1905 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
746 |
Theridiidae |
Kochiura aulica (C.L.Koch, 1838) |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Theridiidae |
Laseola sp. 268 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
Theridiidae |
Macaridion barreti (Kulczyński, 1899) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
494 |
Theridiidae |
Paidiscura orotavensis (Schmidt, 1968) |
0 |
0 |
0 |
1 |
2 |
19 |
0 |
17 |
77 |
Theridiidae |
Rhomphaea nasica (Simon, 1873) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
Theridiidae |
Rugathodes madeirensis Wunderlich, 1987 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
325 |
Theridiidae |
Steatoda grossa (C.L.Koch, 1838) |
1 |
2 |
4 |
0 |
0 |
0 |
0 |
0 |
13 |
Theridiidae |
Steatoda nobilis (Thorell, 1875) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
24 |
Theridiidae |
Theridion hannoniae Denis, 1945 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
1 |
Theridiidae |
Theridion musivivum Schmidt, 1956 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Theridiidae |
Theridion sp. 89 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
28 |
Thomisidae |
Misumena cf. nigromaculata Denis, 1963 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Thomisidae |
Misumena spinifera (Blackwall, 1862) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
12 |
Thomisidae |
Thomisus onustus Walckenaer, 1805 |
0 |
0 |
0 |
0 |
1 |
1 |
0 |
0 |
2 |
Thomisidae |
Xysticus nubilus Simon, 1875 |
16 |
38 |
4 |
12 |
10 |
7 |
0 |
3 |
101 |
Uloboridae |
Hyptiotes flavidus (Blackwall, 1862) |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
111 |
Uloboridae |
Uloborus walckenaerius Latreille, 1806 |
1 |
4 |
7 |
0 |
0 |
0 |
0 |
0 |
13 |
Zodariidae |
Zodarion styliferum (Simon, 1870) |
16 |
13 |
810 |
0 |
0 |
0 |
2 |
9 |
850 |
Species richness |
30 |
21 |
24 |
31 |
27 |
22 |
19 |
26 |
7462 |
The most widespread (morpho)species were Tenuiphantes tenuis (Blackwall, 1852) (introduced), Porrhoclubiona decora (Blackwall, 1859) (native non-endemic), Neoscona crucifera (Lucas, 1838) (introduced), Microlinyphia johnsoni (Blackwall, 1859) (native non-endemic), Cryptachaea blattea (Urquhart, 1886) (introduced), Cheiracanthium albidulum (Blackwall, 1859) (endemic), Ceratinopsis acripes (Denis, 1962) (native non-endemic), Meta stridulans Wunderlich, 1987 (endemic), Echinotheridion gibberosum (Kulczyński, 1899) (native non-endemic), Episinus maderianus Kulczyński, 1905, (native non-endemic) and Paidiscura orotavensis (Schmidt, 1968) (native non-endemic). The five most abundant species were Zodarion styliferum (Simon, 1870) (11%, unknown origin), Episinus maderianus Kulczyński, 1905 (9%, native non-endemic), Diplocephalus graecus (O.P.-Cambridge, 1873) (8%, introduced), Tenuiphantes tenuis (Blackwall, 1852) (7%, introduced) and Macaridion barreti (Kulczyński, 1899) (7%, native non-endemic).
In this section, we point out, explain and discuss the identification of some of the species and morphospecies found – the ones for which information is limited and ordered as in Tables 2, 3 and 4 – and their classification as endemic, native non-endemic, introduced and unknown.
Synaphris saphrynis
This species is known from Spain and Selvagens Islands. It is also present on Bugio island (Desertas), as one of the authors (L. Crespo) identified a specimen collected by M. Boieiro et al. in 2011/12 (unpublished record). The limited number of available records does not allow us to infer its total distribution with certainty.
Haplodrassus omissus
Although Haplodrassus omissus had not been recorded previously in Madeira, it does not come as a surprise to be present there, given its known distribution across the Mediterranean basin and the Canary Islands.
Haplodrassus sp. 164
This morphospecies is present in Porto Santo and, possibly, in other locations of the Madeira archipelago. Haplodrassus MS 164 belongs to the dalmatensis group.
Haplodrassus sp. 158
The morphospecies Haplodrassus MS158 belongs to a different group from that of Haplodrassus MS164, as its genitalia is more similar to species such as H. deserticola, which is present in the Canary Islands or H. minor, which has been recorded from Europe to Turkey, according to the World Spider Catalogue. It is possible that more species of this group are present in the Madeira archipelago.
Macarophaeus cultior
Macarophaeus cultior may be a single-island endemic from Madeira. Although the World Spider Catalog and the Banco de Datos de Biodiversidad de Canarias (based on
Zelotes aeneus
We classified this species as introduced, because of its distribution throughout Europe up to Azerbaijan.
Agyneta canariensis
We have considered this species as native non-endemic, because it is present in the Canary Islands, Selvagens and Madeira.
Canariellanum sp. 21
We considered this species as a new endemic species of a genus so far restricted to the Canary Islands.
Ceratinopsis spp.
Given the morphological mismatch of this morphospecies with other described species from the region, we have considered it as endemic to the island of Madeira.
Tenuiphantes sp. 259
This morphospecies is probably a new Tenuiphantes from the archipelago of Madeira and we, therefore, considered it endemic.
Tenuiphantes tenebricoloides
This species has been found and cited several times from the forests of Madeira island. There is a citation from the Canary Islands by Denis (
Mesiotelus cf. grancanariensis
The species Mesiotelus grancanariensis has been cited from the south west coast of Portugal and across the entire archipelago of Madeira – in treeless dry habitats and along the central mountain chain of Madeira. Hence the classification of this species as a native species.
Oonops cf. pulcher
Although it is possible that this species is an undescribed cryptic species native to Madeira, based on morphological characters, it is very likely to be Oonops pulcher and, therefore, introduced.
Orchestina sp. 160
We classified this morphospecies as archipelago-endemic, based on previous findings by L. Crespo in areas with dry habitats of Porto Santo and Desertas.
Oxyopes sp. 80
Since this morphospecies has not been described or cited before, it is very likely endemic to the Madeiran archipelago.
Philodromus sp. 266
This morphospecies has not been described or cited before, hence our classification as endemic.
Macaroeris cf. desertensis , Macaroeris cf. diligens and Macaroeris sp. 8
We considered Macaroeris cf. desertensis , Macaroeris cf. diligens and Macaroeris sp. 8 as most likely new undescribed species and, therefore, endemic to the Madeiran archipelago.
Lasaeola sp. 268
Based on the morphological features of this morphospecies, we considered it as a new species and, therefore, an archipelago endemic.
Rhomphaea nasica
Rhomphaea nasica is known to be present in Africa and on the remote island of St. Helena. Specimens of this species have also been identified in modified habitats such as the Funchal Botanical Garden (Madeira Island). Therefore, we considered this species as introduced.
Theridion hannoniae
This species has a Mediterranean distribution and, in the Madeiran archipelago, it is usually found in dry, relatively disturbed areas. We classified this species as of unknown biogeographic category, given the impossibility of knowing whether it arrived at the Madeiran archipelago naturally or with human intervention.
Theridion sp. 89
This morphospecies is most likely a new species, so we considered it to be single-island endemic, probably from laurel forest.
Misumena cf. nigromaculata
Here we considered this morphospecies to be a new endemic species given the little information on Misumena nigromaculata, whose female has been described only once and whose male is unknown.
Xysticus nubilus
Xysticus nubilus has a Mediterranean distribution and is usually found in dry habitats in the Madeiran archipelago. Therefore, as with Theridion hannoniae, we classified it as of unknown biogeographic category in Madeira.
Hyptiotes flavidus
Although the distribution of this species is largely Mediterranean, given that it is usually found in laurel forests, we classified it as native to Madeira.
This research was supported by the project FCT MACDIV financed by Fundação para a Ciência e a Tecnologia – ref. FCT-PTDC/BIABIC/0054/2014, that also supported the Open Access of the manuscript. We are grateful to the Madeira Natural Park for the logistic support as well as permission for the collection of specimens.
PAVB, PC and FR conceived the study design and sampling programme. JM-O, PAVB, PC, LCFC, RG, FP, RC, CR, MB, and FR performed spider sampling. PAVB and LCFC performed spider identification. JM-O analysed the data and JM-O and PAVB led the writing. All authors commented on the final version of the manuscript.