Research Article |
Corresponding author: Michal Rindoš ( michal.rindos@gmail.com ) Academic editor: Alberto Zilli
© 2022 Michal Rindoš, Alexander Schintlmeister, Zdeněk Faltýnek Fric.
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:
Rindoš M, Schintlmeister A, Fric ZF (2022) Diversity of the tussock moths (Lepidoptera, Erebidae, Lymantriinae) of the wider Maputaland-Pondoland-Albany, with special reference to the fauna of Mozambique. Nota Lepidopterologica 45: 87-99. https://doi.org/10.3897/nl.45.61588
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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).
Biodiversity hotspots are defined as highly threatened biogeographic regions with the occurrence of endemic species of animals and plants (
The moth subfamily Lymantriinae (Noctuoidea, Erebidae) occurs worldwide and comprises more than 2600 species in almost 360 genera (
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.
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
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. (
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
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.
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.
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.
Angola (
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.
Kenya (
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.
Cameroon (
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.
Kenya (
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.
DR Congo (Afromoths, N. Voaden), South Africa (
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.
Botswana (
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.
Kenya (
The highest species richness of tussock moths was recognised in the Republic of South Africa (N = 157) representing 93% of all recorded species (Table
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
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 |
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 (
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.
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.