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Research Article
Diversity of the tussock moths (Lepidoptera, Erebidae, Lymantriinae) of the wider Maputaland-Pondoland-Albany, with special reference to the fauna of Mozambique
expand article infoMichal Rindoš, Alexander Schintlmeister§, Zdeněk Faltýnek Fric
‡ The Czech Academy of Sciences, Biology Centre, Institute of Entomology, České Budějovice, Czech Republic
§ Unaffiliated, Dresden, Germany
Open Access

Abstract

Maputaland-Pondoland-Albany, one of the African biodiversity hotspots, is defined by a high diversity of its fauna and flora. Despite numerous studies published about the Lepidoptera of this region, our knowledge of diversity and distributional patterns of moths still remains inadequate. Our study evaluates the tussock moth richness and endemism of the wider Maputaland-Pondoland-Albany region. We describe for the first time the variety of the tussock moth fauna of Mozambique, with seven newly recorded genera (Euproctoides Bethune-Baker, 1911; Heteronygmia Holland, 1893; Leucoma Hübner, 1822; Ogoa Walker, 1856; Paraproctis Bethune-Baker, 1911; Polymona Walker, 1855; Tamsita Kiriakoff, 1954).

Introduction

Biodiversity hotspots are defined as highly threatened biogeographic regions with the occurrence of endemic species of animals and plants (Myers 1988). Containing approximately half of the world’s plant and a significant percentage of world’s vertebrate diversity (Myers et al. 2000), conservation and thorough investigation of these 35 remarkable regions distributed worldwide became essential for many researchers due to ongoing species mass extinction (Mittermeier et al. 2011; Eisenhauer et al. 2019). The majority of the African hotspots are located in the Afrotropics (Myers et al. 2000). Maputaland-Pondoland-Albany is one of the three recently recognized biodiversity hotspots in the region of southern Africa (Fig. 1). Diversity and endemism are focused in the three major units: Maputaland in the north, Pondoland in the south and Albany in the south-west, comprising fauna and flora of South Africa, Eswatini (Swaziland) and Mozambique (Perera et al. 2011). The dominant habitats of this region bearing the most unique diversity are tropical and subtropical moist broadleaf forests and mountain grasslands and scrublands. Despite the uniqueness of this area serving as a meeting point for six of the eight southern African biomes, only 25% of the original extent of the natural habitat remains preserved (Mittermeier et al. 2004).

Figure 1. 

Map of the studied area, modified from Weller et al. (2017). The area of the Maputaland-Pondoland-Albany is highlighted by lighter colour.

The moth subfamily Lymantriinae (Noctuoidea, Erebidae) occurs worldwide and comprises more than 2600 species in almost 360 genera (Kitching and Rawlins 1998). South Africa can be considered a well-studied part of the Maputaland-Pondoland-Albany, with several studies discussing the tussock moth fauna (Hampson 1905 – 77 spp., Janse 1917 – 109 spp., Pinhey 1975 – 57 spp., Vári et al. 2002 – 187 spp., Staude et al. 2020 – 34 spp.). However, knowledge of the Lymantriinae of the other southern African countries remains fairly insufficient. Presently, approximately 50 species of tussock moths are known to occur in Eswatini (Duke et al. 1999) and five species are reported from Lesotho (Kopij 2006). The current knowledge of the fauna of Mozambique is based mainly on past taxonomic works carried out on museum materials (e.g., Collenette 1955) counting roughly 50 species. Nonetheless, previously published works also include numerous mistakes in systematics (e.g., published synonyms, identification errors, etc.) and creates “ghost” diversity.

The purpose of this study was to provide an up-to-date overview and fill the gaps in the poor knowledge in the diversity of tussock moths of Afrotropical biodiversity hotspots. Verified distribution data also recovers potential endemic species and thus plays a significant role in the global conservation effort. In addition, we provide a first faunistic summary of the tussock moths of Mozambique, recording seven genera new to the country.

Material and methods

For the compilation of the list of Lymantriinae of the wider Maputaland-Pondoland-Albany we used presence/absence datasets covering the fauna of South Africa, Lesotho, Eswatini and Mozambique (Table 1). The data were mined from literature (e.g., Vári et al. 2002), corrected and supplemented by data obtained by the revision of the following museum collections: African Natural History Research Trust (Leominster, United Kingdom), Natural History Museum (London, United Kingdom), Museum Witt (Munich, Germany), Bavarian State Collection of Zoology (Munich, Germany), and Naturalis Biodiversity Centre (Leiden, Netherlands). In total 2352 specimens from South Africa, 2079 specimens from Mozambique, 18 specimens from Lesotho and 61 specimens from Eswatini were revised. The specimens were photographed using a Nikon D90 camera with Nikkor AF Micro 60 mm lens and assembled for our plates using the Corel DRAW X7 computer program.

Table 1.

The presence, or absence of tussock moth species of the wider Maputaland-Pondoland-Albany. New genus records are marked with symbol (*) and endemic species highlighted with bold.

Species Mozambique Lesotho South Africa Eswatini
Aroa anthora (Felder R., 1874) 0 0 1 0
Aroa difficilis Walker, 1865 0 0 1 1
Aroa discalis Walker, 1855 1 0 1 1
Aroa melanoleuca Hampson, 1905 1 0 1 0
Bracharoa dregei (Herrich-Schäffer, 1854) 0 1 1 0
Bracharoa mixta (Snellen, 1872) 1 0 1 0
Bracharoa quadripunctata (Wallengren, 1875) 1 1 1 1
Bracharoa tricolor (Herrich-Schäffer, 1856) 0 1 1 0
Cataphractes arenacea (Linnaeus, 1767) 0 0 1 0
Cataphractes fasciata (Walker, 1855) 0 0 1 1
Cimola opalina Walker, 1855 1 0 1 1
Conigephyra rikatia Collenette, 1956 1 0 0 0
Creagra liturata (Guérin-Méneville, 1844) 1 0 1 1
Cropera phlebitis (Hampson, 1905) 1 0 1 0
Cropera sericea (Hampson, 1910) 0 0 1 1
Cropera stilpnaroma Hering, 1926 0 1 1 0
Cropera testacea Walker, 1855 1 0 1 1
Crorema adspersa (Herrich-Schäffer, 1854) 0 0 1 1
Crorema fulvinotata (Butler, 1893) 1 0 1 0
Crorema setinoides (Holland, 1893) 0 0 1 0
Dasychira albimaculata Hering, 1926 0 0 1 1
Dasychira amata Hering, 1926 0 0 1 0
Dasychira aurivillii Hering, 1926 0 0 1 0
Dasychira batoides (Plötz, 1880) 0 0 1 0
Dasychira bryophilina Hampson, 1910 0 0 1 0
Dasychira confinis Distant, 1899 0 0 1 0
Dasychira curvivirgata Karsch, 1895 0 0 1 1
Dasychira didyma Collenette, 1956 0 0 1 0
Dasychira diplogramma Hering, 1927 0 0 1 0
Dasychira eclipes Collenette, 1939 0 0 1 0
Dasychira esthlopis Collenette, 1953 0 0 1 0
Dasychira extatura Distant, 1897 1 0 1 1
Dasychira extorta Distant, 1897 1 0 1 1
Dasychira fusca (Walker, 1855) 0 0 1 0
Dasychira gephyra Hering, 1926 0 0 1 0
Dasychira hampsoni Hering, 1926 1 0 1 0
Dasychira herbida (Walker, 1856) 0 0 1 0
Dasychira hughesi Collenette, 1933 0 0 1 0
Dasychira lunensis Hampson, 1905 0 0 1 0
Dasychira mediofasciata Hering, 1926 0 0 1 0
Dasychira nubifuga (Holland, 1893) 0 0 1 1
Dasychira octophora (Hampson, 1905) 1 0 1 1
Dasychira phenax Collenette, 1932 0 0 1 0
Dasychira pheosia Hampson, 1910 0 0 1 1
Dasychira pluto Hering, 1926 0 0 1 0
Dasychira polia Hering, 1926 0 0 1 0
Dasychira postpura Hampson, 1905 0 0 1 1
Dasychira pulcherrima Hering, 1926 0 0 1 0
Dasychira pyrosoma Hampson, 1910 0 0 1 1
Dasychira rocana Swinhoe, 1906 1 0 1 1
Dasychira thanatos Hering, 1926 0 0 1 0
Dasychira vilis (Felder R., 1874) 0 0 1 0
Eudasychira amata (Hering, 1926) 0 0 1 0
Eudasychira georgiana (Fawcett, 1901) 1 0 1 0
Eudasychira metathermes (Hampson, 1905) 1 0 1 1
Eudasychira poliotis (Hampson, 1910) 0 0 1 0
Eudasychira proleprota (Hampson, 1905) 0 0 1 0
Euproctis aethiopica Snellen, 1872 0 0 1 1
Euproctis aspersum (Felder R., 1874) 0 0 1 0
Euproctis beato Bryk, 1934 0 0 1 0
Euproctis bicolor Walker, 1855 1 1 1 1
Euproctis chionea Collenette, 1956 0 0 1 0
Euproctis crocata (Boisduval, 1847) 0 0 1 0
Euproctis flavicincta Janse, 1915 0 0 1 0
Euproctis haemodetes Hampson, 1905 0 0 1 1
Euproctis hardenbergia (Janse, 1915) 0 0 1 0
Euproctis iridescens Janse, 1915 0 0 1 0
Euproctis kettlewelli Collenette, 1956 0 0 1 0
Euproctis mayottensis Collenette, 1956 0 0 1 0
Euproctis melanura (Wallengren, 1860) 0 0 1 0
Euproctis nigripuncta Janse, 1915 0 0 1 0
Euproctis pallida (Kirby, 1896) 1 0 1 1
Euproctis petavia (Stoll, 1782) 0 0 1 0
Euproctis producta (Walker, 1863) 0 1 0 0
Euproctis punctifera (Walker, 1855) 1 0 1 0
Euproctis rufopunctata (Walker, 1862) 1 0 1 0
Euproctis sanguigutta Hampson, 1905 0 0 1 1
Euproctis stellata Distant, 1897 0 0 1 0
Euproctis straminicolor Janse, 1915 0 0 1 0
Euproctis subalba (Janse, 1915) 0 0 1 0
Euproctis terminalis (Walker, 1855) 0 1 1 1
Euproctoides ertli (Wichgraf, 1922) * 1 0 1 0
Griveaudyria cangia (Druce, 1887) 1 0 1 0
Hemerophanes libyra (Druce, 1896) 1 0 1 1
Heteronygmia dissimilis (Aurivillius, 1910) * 1 0 1 0
Homochira poecilosticta Collenette, 1938 1 0 0 0
Homochira rendalli (Distant, 1897) 1 0 1 1
Homoeomeria flavicapilla (Wallengren, 1860) 0 0 1 0
Homoeomeria nivea Aurivillius, 1909 0 0 1 1
Lacipa bizonoides Butler, 1893 1 0 1 0
Lacipa exetastes Collenette, 1952 1 0 0 0
Lacipa florida (Swinhoe, 1903) 0 0 1 0
Lacipa gracilis Hopffer, 1857 1 0 1 0
Lacipa nobilis (Herrich-Schäffer, 1855) 1 1 1 0
Lacipa ostra (Swinhoe, 1903) 1 0 0 0
Lacipa picta (Boisduval, 1847) 0 0 1 0
Lacipa pulverea Distant, 1898 0 0 1 0
Lacipa quadripunctata Dewitz, 1881 1 1 1 1
Lacipa sarcistis Hampson, 1905 0 0 1 0
Lacipa sexpunctata Distant, 1897 0 0 1 0
Laelia amaura Hering, 1926 0 0 1 0
Laelia angustipennis (Walker, 1855) 0 0 1 0
Laelia aureus Janse, 1915 0 0 1 1
Laelia bifascia Hampson, 1905 0 0 1 0
Laelia bonaberiensis (Strand, 1915) 0 0 1 0
Laelia clarki Janse, 1915 0 0 1 1
Laelia figlina Distant, 1899 0 0 1 1
Laelia fracta Schaus & Clements, 1893 1 0 1 1
Laelia gwelila (Swinhoe, 1903) 0 0 1 0
Laelia haematica Hampson, 1905 0 0 1 0
Laelia janenschi Hering, 1926 0 0 1 0
Laelia lavia Swinhoe, 1903 0 0 1 0
Laelia melaxantha (Walker, 1865) 0 0 1 0
Laelia municipalis Distant, 1897 1 0 1 0
Laelia nigripulverea Janse, 1915 0 0 1 0
Laelia punctulata (Butler, 1875) 0 0 1 0
Laelia robusta Janse, 1915 0 0 1 1
Laelia rosea Schaus & Clements, 1893 0 0 1 0
Laelia subrosea (Walker, 1855) 1 0 1 1
Laelia subviridis Janse, 1915 0 0 1 0
Laelia swinnyi Janse, 1915 0 0 1 0
Laelioproctis leucosphena Collenette, 1939 0 0 1 0
Lepidopalpus hyalina Janse, 1915 0 0 1 1
Leptaroa sp. 1 0 0 0
Leptaroa paupera Hering, 1926 0 0 1 0
Leucoma ogovensis (Holland, 1893) * 0 0 1 0
Leucoma parva Plötz, 1880 * 1 0 1 0
Leucoma sevastopuloi Collenette, 1955 * 1 0 0 0
Lymantria kettlewelli Collenette, 1953 0 0 1 0
Lymantria lutea (Boisduval, 1847) 0 0 1 0
Lymantria subfusca (Boisduval, 1847) 0 0 1 0
Marblepsis flabellaria (Fabricius, 1787) 1 0 1 1
Marblepsis melanocraspis (Hampson, 1905) 1 0 1 0
Micraroa minima Janse, 1915 0 0 1 0
Micraroa rufescens Hampson, 1905 0 0 1 0
Morasa modesta Walker, 1855 1 0 1 1
Naroma varipes (Walker, 1865) 1 0 1 1
Ogoa simplex Walker, 1856 * 1 0 1 1
Olapa fulviceps Hampson, 1910 1 0 1 0
Olapa nigribasis Janse, 1917 0 0 1 1
Olapa nigricosta Hampson, 1905 0 0 1 0
Olapa tavetensis (Holland, 1892) 1 0 1 0
Olene basalis (Walker, 1855) 1 0 1 0
Palasea albimacula Wallengren, 1863 1 0 1 1
Paraproctis chionopeza Collenette, 1954 * 1 0 1 0
Pirga pellucida Wichgraf, 1922 1 0 1 0
Pirga transvalensis Janse, 1915 0 0 1 0
Pirgula atrinotata (Butler, 1897) 1 0 1 0
Polymona rufifemur Walker, 1855 * 1 1 1 1
Porthesaroa maculata Collenette, 1938 1 0 1 0
Psalis securis Hübner, 1823 1 0 1 1
Pseudobazisa perculta (Distant, 1897) 0 0 1 1
Pteredoa monosticta (Butler, 1898) 1 0 1 1
Pteredoa subapicalis Hering, 1926 1 0 1 0
Pteredoa usebia (Swinhoe, 1903) 0 0 1 0
Rhypopteryx hemichrysa Collenette, 1960 0 0 1 0
Rhypopteryx lugardi (Swinhoe, 1903) 0 0 1 0
Rhypopteryx rhodalipha (Felder R., 1874) 1 0 1 1
Rhypopteryx rhodea (Hampson, 1905) 1 0 1 0
Rhypopteryx rubripunctata (Weymer, 1892) 0 0 1 0
Rhypopteryx tacita (Hering, 1927) 0 0 1 1
Rhypopteryx triangulifera (Hampson, 1910) 0 0 1 0
Ruanda eleuteriopsis Hering, 1926 1 0 0 0
Ruanda furva (Hampson, 1905) 1 0 1 0
Ruanda nuda (Holland, 1897) 0 0 1 0
Stracena bananae (Butler, 1897) 1 0 1 0
Tamsita habrotima (Tams, 1930) * 1 0 0 0

We compared the faunal diversity of the regions using number of species, and similarity or uniqueness of the species composition expressed as a nestedness of the species and species turnover expressed as binary presence/absence data. We calculated the data in R v. 4.0.3. (R Core Team 2018), by a command “nestedbetajac” (package vegan – Oksanen et al. 2019). Species endemicity was evaluated based on the data of species occurrence available from online database (De Prins and De Prins 2021) and from literature (e.g., Swinhoe 1903).

Results

We reported altogether 168 species of tussock moths belonging to 43 genera currently occurring in the Maputaland-Pondoland-Albany biodiversity hotspot. We are listing 158 species from South Africa, 62 species from Mozambique, 48 species from Eswatini and 10 species from Lesotho. The faunal comparison analysis also revealed 44 potentially endemic species from South Africa and six potentially endemic species from Mozambique (Table 1). By the term “potential endemic species” we mean a species reported so far from only one country, but we cannot rule out its distribution in surrounding countries.

The following genera are recorded for the first time from Mozambique: Euproctoides Bethune-Baker, 1911; Heteronygmia Holland, 1893; Leucoma Hübner, 1822; Ogoa Walker, 1856; Paraproctis Bethune-Baker, 1911; Polymona Walker, 1855; Tamsita Kiriakoff, 1954 (Fig. 2).

Figure 2. 

Seven representatives of newly recorded genera of tussock moths in Mozambique. A. Euproctoides ertli (Wichgraf, 1922); B. Heteronygmia dissimilis (Aurivillius, 1910); C. Leucoma ogovensis (Holland, 1893); D. Ogoa simplex Walker, 1856; E. Paraproctis chionopeza Collenette, 1954; F. Polymona rufifemur Walker, 1855; G. Tamsita habrotima (Tams, 1930). Scale bars: 1 cm.

Euproctoides Bethune-Baker, 1911

Euproctoides ertli (Wichgraf, 1922)

Fig. 2A

Material

Mozambique • 1♂; Zambezia Province, Mt. Namuli, SW slopes near Mucunha village (forest remnant); 15°22'33"S, 37°05'05.7"E; 15–16 Aug. 2018; 1245 m; MV Light Trap; G. László, W. Miles, A. Vetina leg.; ANHRT: 2018.30, ANHRTUK 00094093.

Distribution

Angola (Wichgraf 1922), South Africa (Vári et al. 2002).

Heteronygmia Holland, 1893

Heteronygmia dissimilis (Aurivillius, 1910)

Fig. 2B

Material

Mozambique • 1♂; Manica Province, Chimanimani National Reserve, Moribane Forest, Ndzou Camp (Moist Forest); 19°44'01.4"S, 33°20'15.1"E; 3–5 Aug. 2018; 630 m; Actinic Light Trap; G. László, W. Miles, A. Vetina leg.; ANHRT: 2018.30, ANHRTUK 00046725.

Distribution

Kenya (Hering 1926), Malawi (Murphy and Chipeta 2018), Tanzania (Aurivillius 1910), Zimbabwe (Hering 1929).

Leucoma Hübner, 1822

Leucoma ogovensis (Holland, 1893)

Fig. 2C

Material

Mozambique • 1♂; Maputo Special Reserve, West Gate (Sand Forest); 26°30'14.2"S, 32°42'59.6"E; 21–22 Feb. 2018; 22 m; MV Light Trap; G. László, J. Mulvaney, L. Smith leg.; ANHRT: 2018.2, ANHRT 00027695.

Distribution

Cameroon (Aurivillius 1904), Congo (Holland 1920), Gabon (Holland 1893), Ghana (Swinhoe 1903), Kenya (Le Cerf 1922), Nigeria (Swinhoe 1903), South Africa (Hering 1926).

Ogoa Walker, 1856

Ogoa simplex Walker, 1856

Fig. 2D

Material

Mozambique • 1♂; Maputo Special Reserve, West Gate (Sand Forest); 26°30'14.2"S, 32°42'59.6"E, 13–15 Feb. 2018; 22 m; MV Light Trap; G. László, J. Mulvaney, L. Smith leg.; ANHRT: 2018.2, ANHRTUK 00038737.

Distribution

Kenya (Butler 1898), South Africa (Walker, 1856), Tanzania (Grünberg 1907).

Paraproctis Bethune-Baker, 1911

Paraproctis chionopeza Collenette, 1954

Fig. 2E

Material

Mozambique • 1♂; Maputo Special Reserve, Mangrove Camp (Mangrove-Woodland Mosaic); 26°19'35.9"S, 32°42'35.7"E; 7–9 Dec. 2016; 9 m; MV Light Trap; M. Aristophanous, J. Cristóvão, G. László, W. Miles leg.; ANHRT: 2017.22, ANHRTUK 00053987.

Distribution

DR Congo (Afromoths, N. Voaden), South Africa (Vári et al. 2002), Zambia (Collenette 1954), Zimbabwe (Afromoths, R. Butler).

Polymona Walker, 1855

Polymona rufifemur Walker, 1855

Fig. 2F

Material

Mozambique • 1♂; Maputo Special Reserve, Ponta Milibangalala (Dune Grassland – Dune-Forest Ecotone); 26°26'58.6"S, 32°55'29.8"E; 30 Nov.-3 Dec. 2016; 15 m; Light Trap; M. Aristophanous, J. Cristóvão, G. László, W. Miles leg.; ANHRT: 2017.22, ANHRTUK 00055859.

Distribution

Botswana (Pinhey 1975), Djibouti (Dall’Asta 1977), Eritrea (Berio 1939), Ethiopia (Collenette 1938), Gambia (Druce 1887), Kenya (Le Cerf 1922), Lesotho (Kopij 2006), Malawi (Swinhoe 1903), Namibia (Dall’Asta 2004), South Africa (Janse 1915), Tanzania (Pinhey 1975), Zambia (Pinhey 1975), Zimbabwe (Swinhoe 1903).

Tamsita Kiriakoff, 1954

Tamsita habrotima (Tams, 1930)

Fig. 2G

Material

Mozambique • 1♂; Zambezia Province, Mt. Namuli, SW slopes near Mucunha village (forest remnant); 15°22'33"S, 37°05'05.7"E; 15–16 Aug. 2018; 1245 m; MV Light Trap; G. László, W. Miles, A. Vetina leg.; ANHRT: 2018.30, ANHRTUK 00050678.

Distribution

Kenya (Tams 1930), Uganda (Tams 1930).

Lymantriinae diversity patterns

The highest species richness of tussock moths was recognised in the Republic of South Africa (N = 157) representing 93% of all recorded species (Table 2). The highest turnover among studied countries was found in Lesotho (37.8%).

Table 2.

Evaluation of tussock moth richness patterns in the wider Maputaland-Pondoland-Albany.

species nestedness turnover
Mozambique 62 0.315 0.295
Lesotho 10 0.265 0.379
South Africa 157 0.532 0.103
Eswatini 12 0.380 0.238

The neighbouring countries Mozambique, Lesotho and Eswatini yielded approximately the same values (60%) of species exchange between each other (Table 3). Surprisingly, neither Lesotho nor Eswatini show any faunal exchange with South Africa. All three countries also displayed high species richness differences towards South Africa (Table 4). Due to its geography, the fauna of Lesotho is, not surprisingly, deeply nested in the fauna of South Africa. However, South Africa showed the lowest value in nestedness towards Mozambique (44.6%).

Table 3.

Faunal exchange (turnover) among studied countries of the Maputaland-Pondoland-Albany.

Mozambique Lesotho South Africa Eswatini
Mozambique 0.000 0.667 0.229 0.648
Lesotho 0.667 0.000 0.182 0.667
South Africa 0.229 0.182 0.000 0.000
Eswatini 0.648 0.667 0.000 0.000
Table 4.

Faunal nestedness among the countries of the Maputaland-Pondoland-Albany.

Mozambique Lesotho South Africa Eswatini
Mozambique 0.000 0.259 0.446 0.058
Lesotho 0.259 0.000 0.762 0.239
South Africa 0.446 0.762 0.000 0.696
Eswatini 0.058 0.239 0.696 0.000

Discussion

Our study has reviewed the tussock moth fauna hitherto recorded from the wider Maputaland-Pondoland-Albany and analysed the faunal diversity between those four southern African countries abutting the area of the hotspot. We also have presented a first summary of the tussock moths occurring in Mozambique along with seven genera newly recorded in the country. All these were expected to occur in Mozambique because of their presence in neighbouring countries and these records connect their disjunctive distribution ranges with South Africa. The only exception is the genus Tamsita Kiriakoff, 1954, the presence of which in Mozambique represents the southernmost occurrence of the genus.

The diversity of the tussock moths in Maputaland-Pondoland-Albany displayed several peculiar distributional trends. In spite of the large amount of faunistic studies published about the South African fauna and flora, only very few of them discussed their distributional or biogeographic patterns with regards to the studied countries. We found that the fauna of Lesotho is deeply nested in the South African fauna, but otherwise it has a high turnover among all other countries. This result outlined the potential origin scenario. Lesotho is a country with the high average altitude and the occurrence of specific alti-montane ecoregions (e.g., Drakensberg grasslands and woodlands) with difficult accessibility and hard conditions. Therefore, it was colonized by tussock moth species from neighbouring countries (Sayre et al. 2013). On the other hand, the South African fauna can be considered very similar to the fauna of Mozambique based on the values of nestedness, and simultaneously does not exhibit any faunal exchange towards Eswatini and Lesotho. Thus it forms a gradient of almost the same fauna along the Indian Ocean coast. Our results also highlighted that approximately 27.8% of the South African fauna and 9.6% of the species of Mozambique are potentially endemic to the Maputaland-Pondoland-Albany.

In conclusion, we reviewed and extended the current knowledge of the diversity and distribution patterns of tussock moths in southern Africa. What is more, we also provided a pilot snapshot of species endemicity of Lymantriinae in this region, which contributes to future conservation efforts of this remarkable biodiversity hotspot.

Acknowledgements

We are greatly indebted to Gyula M. László (The African Natural History Research Trust, United Kingdom) for his help with photographing of specimens and draft reading. We would also like to thank Richard Smith (The African Natural History Research Trust, United Kingdom), Alberto Zilli, Geoff Martin (Natural History Museum London, United Kingdom), Thomas Witt (†) (Museum Witt/Witt Foundation, Germany), Axel Hausmann (Bavarian State Collection of Zoology, Germany) and Rob de Vos (Naturalis Biodiversity Centre, Netherlands) for providing us access to the collections under their care. Work of MR was supported by grant GA JU 038/2019/P provided by the University of South Bohemia.

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