Checklist of the fresh and brackish water snails (Mollusca, Gastropoda) of Bénin and adjacent West African ecoregions

Zinsou Cosme Koudenoukpo; Olaniran Hamed Odountan; Bert Van Bocxlaer; Rose Sablon; Antoine Chikou; Thierry Backeljau

doi:10.3897/zookeys.942.52722

Abstract

Currently no comprehensive checklist of fresh and brackish water gastropods from Bénin exists, and those for adjacent West African areas are outdated. Yet, such checklists provide essential biodiversity information and a consistent taxonomic and nomenclatural framework for that biodiversity. Here a first checklist of the fresh and brackish water gastropods from Bénin and adjacent West African ecoregions is presented, based on an extensive literature review and field surveys between September 2014 and June 2019 in six major fresh and brackish water ecosystems in Bénin. This inventory includes information on synonymy, species distribution in West Africa, habitats, and conservation status. The fresh and brackish water gastropod fauna includes 60 species, belonging to 28 genera and 16 families. Pachychilidae, Ampullariidae, Neritidae, and Bulinidae were the most diverse families with 9, 8, 7, and 7 species, respectively. However, literature and field data indicated that 23 species observed in West African basins that extend to Bénin do not occur in the territory of Bénin. These species were not detected in our field surveys, most likely because they are rare at collecting sites. Of the 60 species included, five are classified as “Data Deficient”, 43 as “Least Concern”, two as “Nearly Threatened”, one as “Vulnerable”, and six as “Endangered” by the IUCN, whereas the remaining three species were not evaluated. Because the taxonomy of fresh and brackish water gastropods in West Africa is still largely based on morphology, comparative molecular and taxonomic studies may result in substantial revisions of this checklist over the coming years.

Keywords

biodiversity, gastropods, inland water, species inventory, West Africa

Introduction

Mollusca are the second largest animal phylum on Earth, after Arthropoda, and comprise estimated numbers of 50,000–55,000, 25,000–30,000 and 6,000–7,000 of described and valid marine, terrestrial and freshwater species, respectively (Strong et al. 2008; MolluscaBase 2019b). The largest molluscan class, Gastropoda (83% of accepted mollusc species), has repeatedly and successfully colonized continental waters on all continents, except Antarctica (Strong et al. 2008; MolluscaBase 2019b). Despite their economic interest and ecological importance in many aquatic ecosystems (Wanninger and Wollesen 2019), our understanding of their biodiversity is far from complete, especially in developing countries, where expertise, resources and facilities for biodiversity studies are limited (Odountan et al. 2019a). A poor understanding of the biodiversity that underpins ecosystems and their functioning, hampers sustainable management. Indeed, as much legislative work depends on a validated overview of taxonomic biodiversity (Araujo and Jong 2015), biodiversity inventories are essential for the development of monitoring strategies and conservation policies. Moreover, with the growing need to understand natural resources and heritage, biodiversity checklists and databases have become essential tools facilitating communication between taxonomists, naturalist data managers, ecologists, geneticists, museum curators, conservationists, etc. Beyond consolidating taxonomic knowledge, they enable study and management at organismal and ecosystem level, making them essential for national and international conservation (Lydeard et al. 2004; Régnier et al. 2009). As result, there is an increasing demand from policy makers and managers to readily have access to datasets regarding biodiversity (Gofas et al. 2017).

Malacological investigations of fresh and brackish waters are uncommon in West Africa in general and in Bénin in particular. Adanson (1757) and Dautzenberg (1912) investigated the malacological fauna of Senegal and West Africa, respectively, but their works focussed mainly on shells of marine species. The freshwater gastropods of Bénin were studied for the first time by Germain (1917), based on collections by Henry Hubert made around the 1910s. The first identification guide of West African molluscs (from Mauritania to Angola) was published in 1950 (Nicklès 1950), but focused mainly on marine taxa. Towards the end of the 20^th century, several malacological studies have been undertaken on freshwater and brackish taxa in West Africa and in Bénin (Sellin et al. 1980; Danish Bliharziasis Laboratory 1981; Maslin and Bouvet 1986; Zabi and Le Loeuff 1992, 1993; Brown and Kristensen 1993; Le Loeuff and Zabi 1993). These regions were also covered in the first treatise on African freshwater snails (including some considerations on brackish species) on a continental scale (Brown 1980, 1994). These taxonomic papers are now becoming outdated, and in several respects inaccurate. Indeed, since the overviews by Brown (1980, 1994) much taxonomic and faunistic progress has been made (e.g., Jørgensen et al. 2008; Hayes et al. 2015), but the results of these studies have not yet been compiled in an updated overview. Moreover, most research dealing with mollusc diversity in West Africa, including Bénin, focussed on ecology (e.g., Villanueva 2004; Gnohossou 2006; Adandedjan 2012; Odountan 2017; Zinsou 2017; Koudenoukpo 2018) or the transmission of human diseases (e.g., Ibikounlé et al. 2008, 2009, 2013, 2014a, b; Agboho 2018; Onzo-Aboki et al. 2018). As a result, the taxonomic basis of many of these studies was not up to date. This also applies to the List of non-marine molluscs of Benin in Wikipedia (https://en.wikipedia.org/wiki/List_of_non-marine_molluscs_of_Benin), which is incomplete, with outdated nomenclature, it does not include synonyms, and does not provide distributional and conservation information. As such, the Wikipedia list does not inspire much confidence (Kittur et al. 2008). Hence, a new solid and comprehensive synthesis is in order. Therefore, we here provide a comprehensive taxonomic overview of the fresh and brackish water gastropods of Bénin and adjacent West African ecoregions and compile an up to date biodiversity checklist for this fauna. This checklist was developed from literature study and verified through field surveys in six major fresh and brackish ecosystems in Bénin. It provides species synonymy, distribution and habitat data for West Africa, and conservation status. As such we hope that it will act as a reference and research tool for future taxonomic and biomonitoring studies.

Materials and methods

Study region: Bénin and adjacent ecoregions

Bénin is located in West Africa between 6°15' and 12°25'N latitude and between 0°45' and 4°00'E longitude. Its neighbouring countries are Togo in the west, Burkina Faso in the north west, the Republic of Niger in the north (Niger River), and Nigeria in the east. In the south Bénin has a coastline of ~ 125 km along the Atlantic Ocean. Bénin extends from north to the south for ~ 700 km and its width varies between 125 km (along the coast) and 325 km (at the latitude of Tanguiéta). The country has a surface of 112.622 km² (Adam and Boko 1983) and a fairly large network of more or less permanent rivers and standing aquatic ecosystems. Generally, the rivers (e.g., Oueme River, Mono River) are modest in their flow regime and drain into the southern lentic system (e.g., Lake Nokoue, Lake Aheme). This aquatic network is subdivided into four basins, namely the Niger Basin (shared with Mauritania, Guinea, Algeria, Mali, Ivory Coast, Burkina Faso, Niger, Nigeria, Chad, and Cameroon), the Volta Basin (shared with Mali, Ivory Coast, Burkina Faso, Ghana, and Togo), the Oueme Basin (shared with Togo and Nigeria) and the Mono Basin (shared with Togo). Ecologically these watersheds also contain distinct natural communities, composed of different species with specific ecological dynamics, i.e., they represent distinct freshwater ecoregions (Abell et al. 2008; Graf and Cummings 2011). Sections of the same catchment system are sometimes subdivided into additional ecoregions, and matching freshwater ecoregions that have primarily been established for fish (Abell et al. 2008) with the Transboundary Freshwater dispute Database (https://tfddmgmt.github.io/tfdd/map.html). As such, Bénin and its immediate surroundings are covered by ecoregions 505–508 and 513–519 (Fig. 1; Table 1), which form the geographical scope of our study.

Table 1.

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Freshwater ecoregions of West Africa investigated and their attributes Ecoregions codes from Abell et al. (2008).

Ecoregions	Covered countries
505: Lower Niger–Benue	Mali, Burkina Faso, Niger, Bénin, Nigeria, Cameroon, Chad
506: Niger Delta	Nigeria,
507: Upper Niger	Guinea, Mali, Ivory Coast, Burkina Faso
508: Inner Niger Delta	Mali, Mauritania
513: Mount Nimba	Guinea, Ivory Coast
514: Eburneo	Ivory Coast, Burkina Faso
515: Ashanti	Ivory Coast, Ghana
516: Volta	Ivory Coast, Mali, Burkina Faso, Ghana, Togo, Bénin
517: Bight Drainage	Ghana, Togo, Bénin, Nigeria,
518: Northern Gulf of Guinea Drainages	Nigeria, Cameroon
519: Western Equatorial Crater Lakes	Cameroon

Figure 1.

Map of Bénin and surrounding ecoregions covering the major river catchment basins. Ecoregion codes and the countries each ecoregion covers are listed in Table 1.

Literature study

This checklist is based on a careful literature review to construct an up-to-date biodiversity inventory. These literature sources include peer-reviewed articles, books, reports, manuals, dissertations and other grey literature on the gastropods of Bénin, surrounding countries and their shared drainage basins. Indeed, the development of such a corpus of literature requires the collection of heterogeneous, sometimes contradictory, not to say conflictual, taxonomic opinions across a wide variety of publications.

Field surveys

We supplemented the literature-based biodiversity inventory with field sampling in Bénin. Sampling was conducted in the Sô River, the Oueme River, Lake Nokoue, the Porto-Novo Lagoon, Lake Aheme and the Coastal Lagoon of Ouidah Grand-Popo. In total, 94 field excursions (24, 22, 12, 12, 12, 12, respectively), each of two days per waterbody, were organized between September 2014 and June 2019. Eight to twelve sampling sites were defined within each waterbody to cover a wide range of sub-habitats. These field surveys were performed with an Ekman grab (0.0225 m²) and a long-handled kick net (250 µm mesh). Specifically, we inspected the littoral area, the deeper zones, within/under aquatic macrophytes and other environments suitable for molluscs. Snails were put in formalin in prelabelled plastic containers. These containers were subsequently transported to the laboratory, where the snails were washed, and identiﬁed using appropriate identification keys (Nicklès 1950; Durand and Lévêque 1981; Brown and Kristensen 1993; Brown 1994) and compared with reference specimens from Dahomey (former name of Bénin) and Bénin (if available) deposited in the collections of the Royal Belgian Institute of Natural Sciences (RBINS) and the Royal Museum for Central Africa (RMCA).

Data compilation

All taxa included in this study were cross-checked for their original name combination, synonymies, type locality data, habitats and dubious records against MolluscaBase (accessed at http://www.molluscabase.org during October 2019), and the Worldwide mollusc species Data Base (WMSD accessed at http://www.bagniliggia.it/ during October 2019) when MolluscaBase did not provide the required data. In addition, the conservation status of each species was determined from the IUCN red list (accessed at https://www.iucnredlist.org/ during October 2019). The discussion of the occurrence and conservation status of species whose geographical distribution extends beyond the targeted ecoregions, is mainly limited to the ecoregions covered here. We based our systematic arrangement of subclasses and orders on Bouchet et al. (2017), whereas families, genera and species are listed in alphabetical order.

Results

Our final checklist includes 60 species belonging to 28 genera and 16 families. Information on each of these species is provided below.

Systematic Catalogue

Class GASTROPODA Cuvier, 1795

Subclass Neritimorpha Golikov & Starobogatov, 1975

Order Cycloneritida Frýda, 1998

Family NERITIDAE Rafinesque, 1815

Genus Clypeolum Récluz, 1842

Clypeolum owenianum (W. Wood, 1828)

Original combination. Nerita oweniana W. Wood, 1828.

Synonyms. Neritina tiassalensis Binder, 1956.

Type locality. Africa (Brown 1994).

Habitat. Fresh and Brackish water.

Distribution. Ivory Coast to Cameroon, including Volta River (up to Bator) (Binder 1968; Brown and Kristensen 1993; Le Loeuff and Zabi 1993; Brown 1994; Le Loeuff 1999; Bony 2007; Kouadio et al. 2008, 2011; Edokpayi and Ikharo 2011; Diomandé et al. 2013).

Evidence in Bénin. Along the coast of the Atlantic Ocean (Kristensen and Stensgaard 2010e).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/40087/10303057

Remarks. The last whorl encloses earlier whorls almost completely and the lip is commonly expanded in two wing-like projections which appear to be most fully developed in freshwater (Pilsbry and Bequaert 1927). The species is widely distributed and observed beyond our region of interest in countries such as Liberia, the DR Congo and Angola (Brown 1994).

Genus Nereina de Cristofori & Jan, 1832

Nereina afra (G. B. Sowerby I, 1836)

Original combination. Neritina afra G. B. Sowerby I, 1836.

Synonyms. Nerita africana Récluz, 1844; Neritina aequinoxialis Morelet, 1848.

Type locality. Fernando Po (= Bioko, Equatorial Guinea).

Habitat. Fresh and Brackish water.

Distribution. From Ivory Coast to Cameroon (Brown and Kristensen 1993; Brown 1994; Bandel and Kowalke 1999; Kouadio et al. 2008, 2011).

Evidence in Bénin. Coastal Lagoon of Bénin (Adandedjan 2012).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165778/6119044

Remarks. Observed in our field data in ecoregion 517.

Genus Vitta Adams & Adams, 1854

Vitta adansoniana (Récluz, 1841)

Original combination. Nerita adansoniana Récluz, 1841.

Synonyms. Neritina adansoniana (Récluz, 1841); Neritina sangara Morelet, 1848.

Type locality. Senegal River estuary.

Habitat. Fresh and Brackish water.

Distribution. Ivory Coast to Cameroon (Binder 1968; Brown and Kristensen 1993; Le Loeuff and Zabi 1993; Brown 1994; Guiral et al. 1999; Finlayson et al. 2000).

Evidence in Bénin. Presence uncertain (Kristensen and Stensgaard 2010d) and it was not found in the field surveys.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165788/6126163

Vitta cristata (Morelet, 1864)

Original combination. Neritina cristata Morelet, 1864.

Synonyms. -.

Type locality. Como River, Gabon.

Habitat. Fresh and Brackish water.

Distribution. Sierra-Leone, Ivory Coast, Cameroon and Gabon (Binder 1968; Brown and Kristensen 1993; Le Loeuff and Zabi 1993; Brown 1994; Guiral et al. 1999; Le Loeuff 1999; Kouadio et al. 2008, 2011).

Evidence in Bénin. Porto-Novo Lagoon, Coastal lagoon of Ouidah Grand-Popo (Adandedjan 2012; Odountan 2017).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/14627/4450516

Remarks. Observed in our field data in ecoregion 517.

Vitta glabrata (G. B. Sowerby II, 1849)

Original combination. Neritina glabrata G. B. Sowerby II, 1849.

Synonyms. Clithon glabrata (G. B. Sowerby II, 1849); Clithon glabratum (G. B. Sowerby II, 1849).

Type locality. Unknown.

Habitat. Fresh and Brackish water.

Distribution. Ivory Coast to Angola (Binder 1968; Sankaré and Etien 1991; Brown and Kristensen 1993; Le Loeuff and Zabi 1993; Guiral et al. 1999; Le Loeuff 1999; Kouadio et al. 2008, 2011; Olomukoro and Azubuike 2009).

Evidence in Bénin. Lake Nokoue, Porto-Novo lagoon, Coastal lagoon (Adandedjan 2012; Odountan 2017; Koudenoukpo 2018).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165780/6120407

Remarks. Observed in our field data in ecoregion 517. Very common in Porto-Novo lagoon.

Vitta kuramoensis (Yoloye & Adegoke, 1977)

Original combination. Neritina kuramoensis Yoloye & Adegoke, 1977.

Synonyms. -.

Type locality. Kuramo Water (a branch of Lagos Lagoon), Nigeria.

Habitat. Brackish and marine water.

Distribution. Ivory Coast, Ghana, Bénin, Nigeria and Gabon (Le Loeuff and Zabi 1993; Brown 1994; Guiral et al. 1999; Le Loeuff 1999; Kouadio et al. 2008, 2011; MolluscaBase 2019d).

Evidence in Bénin. Coastal lagoon (Adandedjan 2012).

IUCN status. Not Evaluated.

Remarks. Observed in our field data in ecoregion 517. Sometimes confused with V. adansoniana and some specimens identified as V. adansoniana may refer to V. kuramoensis (Brown 1994).

Vitta rubricata (Morelet, 1858)

Original combination. Neritina rubricata Morelet, 1858.

Synonyms. -.

Type locality. Senegambia (= Senegal).

Habitat. Fresh and Brackish water.

Distribution. Ivory Coast to Cameroon and Gabon (Binder 1968; Brown and Kristensen 1993; Le Loeuff and Zabi 1993; Brown 1994; Bandel and Kowalke 1999; Guiral et al. 1999; Le Loeuff 1999; Kouadio et al. 2008).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/40090/10304117

Remarks. According to Brown (1994) syntypes from Morelet’s collection (Natural History Museum, London) are labelled from Calabar, Gabon and Congo. The confusion about the type locality and the possible syntypes is well-documented in Breure et al. (2018).

Subclass Caenogastropoda Cox, 1960

Grade Architaenioglossa Haller, 1890

Family AMPULLARIIDAE Gray, 1824

Genus Afropomus Pilsbry & Bequaert, 1927

Afropomus balanoideus (Gould, 1850)

Original combination. Ampullaria balanoidea Gould, 1850.

Synonyms. Afropomus balanoidea (Gould, 1850).

Type locality. Grand Cape Mount, Liberia, Liberia (Cowie 2015).

Habitat. Freshwater.

Distribution. Sierra Leone, Liberia, Ivory Coast, Nigeria (Hubendick 1977; Brown and Kristensen 1993; Brown 1994; Asor et al. 2003; Daget 2003).

Evidence in Bénin. Not reported.

IUCN status. Near Threatened.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165386A6011118.en

Remarks. Present in neighbouring countries of Bénin (Binder 1963:13), it may occur in Bénin, where its preferred habitats such as ditches, creeks, and small rivers have been surveyed to limited extent only (Brown 1994). As an intermediate host of pulmonary paragonimiasis, the taxon may be of interest to human disease investigators. Afropomus balanoides is a misspelling.

Genus Lanistes Montfort, 1810

Lanistes chaperi (Kobelt, 1912)

Original combination. Meladomus libycus chaperi Kobelt, 1912.

Synonyms. -.

Type locality. Dahomey, Africae occidentalis (=Bénin).

Habitat. Freshwater.

Distribution. Reported from Bénin only (Cowie 2015).

Evidence in Bénin. Original description.

IUCN status. Not Evaluated.

Remarks. Two syntypes of this species exist in the Senckenberg Museum (Frankfurt am Main, Germany): SMF 7451 and 7452. The species has been described as a subspecies of L. libycus, and because of that reason it is neither specifically mentioned by Brown and Kristensen (1993), nor by Brown (1994). However, it was considered to be a valid species by Pilsbry and Bequaert (1927), which is maintained by Cowie (2015). Therefore, its ecology should be investigated further.

Lanistes libycus (Morelet, 1848)

Original combination. Ampullaria libyca Morelet, 1848.

Synonyms. Meladomus libycus (Morelet, 1848); Meladomus (Lanistes) libycus var. albersi Kobelt, 1912; Meladomus boettgeri Kobelt, 1912.

Type locality. Gabon.

Habitat. Freshwater.

Distribution. Coastal countries of West Africa, i.e., Ivory Coast, Ghana, Togo, Bénin, Nigeria, Cameroon, Equatorial Guinea and Gabon (Brown 1994; Diomandé et al. 2009; Jørgensen et al. 2010a; Salawu and Odaibo 2014; Diakité et al. 2017; Danladi et al. 2019).

Evidence in Bénin. RMCA nos. 37061 and 37066 (Dahomey; ex. coll. Putzeys 1935).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T175137A7110785.en

Remarks. This species was not recorded during our sampling in Bénin, although it should occur in the eastern regions of Bénin, around Ketou, Pobè and Sakété. These localities are in close vicinity to Yewa North in Nigeria, where the species is abundant (Salawu and Odaibo 2014).

Lanistes ovum Troschel, 1845

Original combination. Lanistes (Meladomus) ovum Troschel, 1845.

Synonyms. Lanistes (Meladomus) procerus von Martens, 1866; Lanistes procerus von Martens, 1866-; Lanistes ovum var. elatior von Martens, 1866; Lanistes olivaceus var. procerus von Martens, 1866; Lanistes ellipticus var. luapulensis Furtado, 1886; Lanistes affinis var. manyarana Sturany, 1894; Lanistes ovum var. plicosus von Martens, 1897; Lanistes ovum var. lacoini Germain, 1907; Lanistes ovum var.major Germain, 1907; Lanistes procerus var. minor Germain, 1907; Lanistes (Meladomus) procerus langi Pilsbry & Bequaert, 1927; Lanistes (Meladomus) connollyi Pain, 1954; Lanistes (Meladomus) ovum mweruensis Pain, 1954.

Type locality. Tete, Mozambique, but paralectotypes also come from Sena, Mozambique (Köhler and Glaubrecht 2006).

Habitat. Freshwater.

Distribution. Scattered localities over a large area in Africa including all West African countries (Brown 1994; Albrecht et al. 2018; Ouedraogo et al. 2018).

Evidence in Bénin. Alibori River (Agblonon Houelome et al. 2017).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165799A6134027.en

Remarks. Specimens of L. ovum have been included in molecular studies (Jørgensen et al. 2008; Schultheiß et al. 2009), which suggested that multiple evolutionary lineages have been lumped into this taxon. Given that the type locality of L. ovum is in Mozambique, it is likely that the West African specimens resembling L. ovum belong to a distinct taxon. Molecular work is required to resolve the issue.

Lanistes varicus (O. F. Müller, 1774)

Original combination. Helix varica O. F. Müller, 1774.

Synonyms. Ampullaria olivacea Lamarck, 1816; Lanistes olivaceus (Lamarck, 1816); Ampullaria guinaica Lamarck, 1822; Meladomus adansoni Kobelt, 1911; Lanistes adansoni (Kobelt, 1911); Lanistes millestriatus Pilsbry & Bequaert, 1927.

Type locality. Unknown.

Habitat. Freshwater (permanent and temporary).

Distribution. Senegal, Gambia, Mali, Ivory Coast, Ghana, Burkina Faso, Niger and Nigeria (Brown 1994).

Evidence in Bénin. Widespread especially at Cotonou garden ASECNA, Toho-Todougba lake, Sèhouè Hlan lake and Acron (Ibikounlé et al. 2009), Cocotomey (Agboho 2018), Oueme River (Zinsou 2017), Sô River (Koudenoukpo 2018), Alibori River (Agblonon Houelome et al. 2017), Porto Novo Lagoon and Coastal lagoon of Ouidah Grand-Popo (Adandedjan 2012).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T175132A7107425.en

Remarks. Observed in our field data in ecoregion 517. Lanistes varicus is an intermediate host for non-human schistosomes and is often investigated by parasitologists (Ibikounlé et al. 2009). It is an edible species consumed by humans in Bénin (Koudenoukpo 2018). It usually is abundant in natural permanent water bodies. Lanistes guinaicus mutation depressa Germain, 1917 (513–514) from Région des Tchis, cercle de Mono and Tchaourou (misspelled as Ichaourou)] is an unavailable name because of its infrasubspecific nature (Code, Art. 45.6, Glossary) (Cowie 2015). This taxon seems to be referable to L. varicus, but specimens of L. varicus from the localities mentioned by Germain (1917) should be further studied to elucidate the status of L. guinaicus mutation depressa. L. varicus as in Adandedjan (2012) is a misspelling.

Genus Pila Röding, 1798

Pila africana (von Martens, 1886)

Original combination. Ampullaria africana von Martens, 1886.

Synonyms. -

Type locality. Goldküste, Abetifi (= Ghana).

Habitat. Freshwater.

Distribution. Ivory Coast and Ghana (Brown and Kristensen 1993)

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165375A6007169.en

Remarks. Pila africana is the most common species of Pila in countries to the west of Bénin. A lectotype and paralectotypes at the Natural History Museum, Berlin (ZMB) have been assigned by Köhler and Glaubrecht (2006).

Pila ovata (Olivier, 1804)

Original combination. Ampullaria ovata Olivier, 1804.

Synonyms. Lanistes ovatus (Olivier, 1804); Ampullaria gradata Smith, 1881; Ampullaria erythrostoma var. stuhlmanni von Martens, 1897; Ampullaria gordoni var. bukobae von Martens, 1897; Ampullaria ovata var. conglobata von Martens, 1874; Ampullaria ovata var. deckeni von Martens, 1897; Ampullaria ovata var. emini von Martens, 1897.

Type locality. Lac Maréotis (Egypt).

Habitat. Freshwater.

Distribution. In West Africa only known from Nigeria and Chad. Common in East Africa from Egypt to northern Mozambique (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165765/6110071

Remarks. The Nigerian specimens identified as Pila ampullacea (Linnaeus, 1758) by (Gadzama 2012) seem to belong to Pila ovata (Olivier, 1804). Molecular work is required to examine whether P. ovata indeed has a very wide geographical distribution, or whether it consists of several cryptic species that have been lumped together.

Pila wernei (Philippi, 1851)

Original combination. Ampullaria wernei Philippi, 1851.

Synonyms. -.

Type locality. White Nile.

Habitat. Freshwater.

Distribution. In West Africa, present in Mali, Nigeria, Cameroon, Chad and doubtfully in Guinea, Ivory Coast, Burkina Faso, Ghana, Togo, Bénin and Niger (Jørgensen et al. 2010b).

Evidence in Bénin. Presence uncertain (Jørgensen et al. 2010b).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T175127A7104032.en

Remarks. This species is common in the Niger River from Mali to Nigeria and therefore could be present in Niger tributaries in Bénin, namely the Mékrou, Alibori and Sota. It seems that reports from coastal environments in West Africa are misidentifications. Köhler and Glaubrecht (2006) designated a lectotype (Museum für Naturkunde, Berlin: ZMB 1335), a paralectotype exists apparently at the Museo Nacional de Historia Natural, Santiago, Chile (MNHNCL). This species has, like P. ovata, a wide geographical distribution, which, however, needs to be examined with molecular data.

Family VIVIPARIDAE Gray, 1847

Genus Bellamya Jousseaume, 1886

Bellamya unicolor (Olivier, 1804)

Original combination. Cyclostoma unicolor Olivier, 1804.

Synonyms. Vivipara duponti De Rochebrune, 1881; Bellamya bellamya Jousseaume, 1886; Viviparus unicolor (Olivier, 1904).

Type locality. Alexandria, Egypt.

Habitat. Freshwater.

Distribution. The species is widely distributed in the northern hemisphere part of sub-Saharan Africa, and along the Nile (Brown 1994). In West Africa it occurs in Burkina Faso and Nigeria (Gadzama 2012; Gadzama et al. 2015; Ouedraogo et al. 2015, 2018).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2016-3.RLTS.T98275044A84313812.en

Remarks. This species has been considered to be a bucket taxon that requires taxonomic revision (Schultheiß et al. 2014). The type of the genus is B. bellamya Jousseaume, 1886, by original designation, which is considered a synonym of Vivipara duponti De Rochebrune, 1881, which represents a West African form of Bellamya unicolor (Olivier, 1804). The type locality of B. bellamya is Kora, Haut-Senegal, and of V. duponti the Bakoy River [= Bakoye River] at Pangalla. It is possible that one or both species would prove to be genetically distinct from B. unicolor upon molecular examination.

Order Littorinimorpha Golikov & Starobogatov, 1975

Family ASSIMINEIDAE H. Adams & A. Adams, 1856

Genus Assiminea Fleming, 1828

Assiminea hessei Boettger, 1887

Original combination. Assiminea hessei Boettger, 1887.

Synonyms. -.

Type locality. swamp behind the English trade house at Banana, West Zaire (= Democratic Republic of Congo).

Habitat. Brackish water.

Distribution. Nigeria, DR Congo (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Endangered.

https://www.iucnredlist.org/species/175138/7111055

Remarks. This salt-tolerant species is associated with mangrove habitats, and easily overlooked because of its small size (length of ~3 mm). As such, it may potentially occur elsewhere, including in mangroves in Bénin.

Family BITHYNIIDAE Gray, 1857

Genus Gabbiella Mandahl-Barth, 1968

Gabbiella africana (Frauenfeld, 1862)

Original combination. Bithynia africana Frauenfeld, 1862.

Synonyms. Bithynia tournieri Binder, 1955.

Type locality. West Africa (without further detail).

Habitat. Fresh and brackish water.

Distribution. Mali, Ivory Coast, Togo, and doubtfully in Ghana (Kristensen and Stensgaard 2010b; Camara et al. 2012; Bony et al. 2013).

Evidence in Bénin. Coastal lagoon of Ouidah Grand-Popo at many sites including Alongo, and Agonnékanmè (Adandedjan 2012).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165403A6017400.en

Remarks. Observed in our field data in ecoregion 517. Previous records of this species were all in freshwater habitats, whereas the specimens reported in Bénin occurred in brackish water. Brown (1994) suggested that Bithynia tournieri Binder, 1955 may be conspecific, which is followed here, but in the absence of molecular studies the systematics of Gabbiella are very poorly known. The contrast in habitat between previously recorded specimens and those from Bénin could be indicative for specific differences, but until compelling evidence indicates otherwise, we consider the Bénin specimens conspecific.

Gabbiella tchadiensis Mandahl-Barth, 1968

Original combination. Gabbiella tchadiensis Mandahl-Barth, 1968.

Synonyms. -.

Type locality. South East shore at Bol in Lake Chad, Chad.

Habitat. Freshwater.

Distribution. Tchad and Nigeria (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Endangered.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165387A6011471.en

Remarks. This species occurs in the catchment of Lake Chad, including the Komadugu Yobe River. This catchment falls beyond the ecoregions under study here, but the taxon is considered to have had a more extensive Late Pleistocene-Holocene distribution in the Chad Basin (Van Damme 1984). Additionally, recent specimens have been reported also from Lake Léré on the border between Cameroon and Chad (Brown 1994), which is part of the Niger Basin and the reason for inclusion here.

Family HYDROBIIDAE Stimpson, 1865

Genus Hydrobia Hartmann, 1821

Hydrobia accrensis Connolly, 1929

Original combination. Hydrobia accrensis Connolly, 1929.

Synonyms. -.

Type locality. Quarry near Accra, Ghana.

Habitat. Freshwater.

Distribution. Ghana and Togo (Kristensen and Stensgaard 2010c).

Evidence in Bénin. Not reported.

IUCN status. Near Threatened.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165400A6016291.en

Remarks. As for Bithyniidae, the lack of knowledge on the anatomy of hydrobiid species combined with a lack of molecular studies currently hampers confident systematic placement of African Hydrobiidae (see e.g., Seddon et al. 2011).

Hydrobia guyenoti Binder, 1955

Original combination. Hydrobia guyenoti Binder, 1955.

Synonyms. -.

Type locality. Toupah Bay in Lagune Ebrié, Ivory Coast.

Habitat. Fresh and brackish water.

Distribution. Ivory Coast in Lagune Ebrié (Brown 1994).

Evidence in Bénin. Coastal lagoon (Adandedjan 2012).

IUCN status. Endangered.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165381A6009233.en

Remarks. This species endemic to West Africa is not mentioned by MolluscaBase but is included in WMSDB and regional reports (Smith et al. 2009; Adandedjan 2012). It may be more widespread than previously assumed. It is one the smallest species of the genus: 2.7×1.8 mm. The whorls are strongly convex with a deep suture. The central radular tooth has a single basal denticle on each side and long lateral lobes (Brown 1994).

Hydrobia lineata Jekelius, 1944

Original combination. Hydrobia lineata Jekelius, 1944.

Synonyms. -.

Type locality. Bingerville Bay, in fresh water, Ivory Coast.

Habitat. Freshwater.

Distribution. Ivory Coast, Togo and Bénin (Brown 1994).

Evidence in Bénin. Reported in Lac Toho Todougba (Brown 1994).

IUCN status. Data Deficient.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165380A6008870.en

Remarks. Observed in our field data in ecoregion 517. Only one specimen was observed and that was empty shells, not a living specimen. The species is known from fossils only according to MolluscaBase (2019c), but some authors reported extant specimens (Smith et al. 2009; Badahoui et al. 2010). The species requires taxonomical study (Seddon et al. 2011).

Family LITTORINIDAE Children, 1834

Genus Littoraria Gray, 1833

Littoraria angulifera (Lamarck, 1822)

Original combination. Phasianella angulifera Lamarck, 1822.

Synonyms. Littorina angulifera (Lamarck, 1822).

Type locality. Unknown.

Habitat. Brackish and marine and water.

Distribution. Senegal, Sierra Leone, Liberia, Ghana and Nigeria (Rosewater 1981).

Evidence in Bénin. Cotonou (Rosewater 1981).

IUCN status. Not Evaluated.

Remarks. Observed in our field data in ecoregion 517. Specimens from mangroves of the Coastal lagoon of Ouidah, Grand-Popo that have been assigned to Littoraria scabra (Linnaeus, 1758) by Adandedjan et al. (2012) seem to be referable to Littoraria angulifera (Lamarck, 1822). Littoraria scabra is very polymorphic, but endemic to the Indo-West Pacific region (Reid et al. 2010).

Subcohort Cerithiimorpha Golikov & Starobogatov, 1975

Remarks. A temporary order named Caenogastropoda has been established (MolluscaBase 2019a) to group a number of superfamilies that belong to the Subclass Caenogastropoda but not to the Order Littorinimorpha. This group has previously been referred to as the subcohort Cerithiimorpha (Bouchet et al. 2017), which is followed here. We do not use the temporary Order [unassigned] Caenogastropoda to avoid confusion with the Subclass Caenogastropoda.

Family PACHYCHILIDAE Fischer & Crosse, 1892

Genus Potadoma Swainson, 1840

Potadoma angulata Thiele, 1928

Original combination. Potadoma angulata Thiele, 1928.

Synonyms. -

Type locality. Samanga (known as Sanaga River), Cameroon.

Habitat. Freshwater.

Distribution. Currently, this species has only been recorded from Cameroon (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Endangered.

https://www.iucnredlist.org/species/184556/8292306

Remarks. This endemic species of Cameroon is known only from the southernmost parts of ecoregion 505.

Potadoma bicarinata Mandahl-Barth, 1967

Original combination. Potadoma bicarinata Mandahl-Barth, 1967.

Synonyms. -.

Type locality. Volta River at Asikoko village near Frankadua, Ghana.

Habitat. Freshwater.

Distribution. Currently, this species has only been recorded from Ghana (Mandahl-Barth 1967).

Evidence in Bénin. Unconfirmed, may be reported by Adandedjan (2012) under Potadoma sp.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165383A6009945.en

Remarks. The distribution of Potadoma is disjunct, most taxa occur in West Africa, whereas some others in Central Africa (Brown 1994). The phylogenetic affinities of taxa from both regions are currently unknown. Especially the West African taxa, several of which occur in the ecoregions under study here, display high morphological disparity. Many of the endemic Potadoma species from Cameroon fall just beyond the boundaries of the ecoregions considered here, such as P. zenkeri (von Martens, 1901). Late Cenozoic fossils suggest that the genus was more widespread before, including in the Albertine Rift (e.g., Van Damme and Pickford 2003; Salzburger et al. 2014), the Turkana Basin (Van Bocxlaer et al. 2008) and even in Botswana (Riedel et al. 2009).

Potadoma freethi (Gray, 1831)

Original combination. Melania freethi Gray, 1831.

Synonyms. Melania foenaria Reeve, 1860; Melania guineensis Reeve, 1860; Potadoma freethi dykei Spence, 1925; Melania nigrita Morelet, 1851; Melania nigritina Morelet, 1848; Potadoma freethii guineensis Pilsbry & Bequaert, 1927.

Type locality. Fernando Po (= Bioko, Equatorial Guinea).

Habitat. Freshwater.

Distribution. From Ivory Coast to Nigeria (Brown 1994; Owojori et al. 2006; Kouadio et al. 2008).

Evidence in Bénin. Reported by Kristensen and Stensgaard (2010e).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/175120/7099504

Remarks. P. freethi is the type species of the genus, by original designation (Gray 1847). Observed in our field data in ecoregion 517. Several subspecies, such as P. f. dykei Spence, 1925 and P. f. guineensis Reeve, 1860 have been described and these are included here. Two other subspecies have been described from Central Africa (DR Congo), i.e., P. f. tigrina Connolly, 1938 and P. f. graptoconus Pilsbry & Bequaert, 1927, but it seems doubtful these would belong to P. freethi given the disjunct distribution of the genus Potadoma. Melania conulus Lea & Lea, 1851, is another species described from Fernando Po of which the original description is similar to P. freethi, but more research is required before we can confirm it to be a synonym. Therefore, M. conulus is considered to be a “taxon inquirendum” (MolluscaBase 2019a: taxon 1115355).

Potadoma liberiensis (Schepman, 1888)

Original combination. Melania liberiensis Schepman, 1888.

Synonyms. Melania sancti-pauli Schepman, 1888; Potadoma bequaerti Binder, 1963.

Type locality. St Paul’s River near Bavia, Liberia.

Habitat. Freshwater.

Distribution. Guinea, Liberia and Ivory Coast (Mandahl-Barth 1967; Diomandé et al. 2009).

Evidence in Bénin. Perhaps included in Potadoma sp. reported by Adandedjan (2012).

IUCN status. Data Deficient.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165385A6010770.en

Remarks. The synonyms concern variants in which spiral ridges are developed to variable extent.

Potadoma moerchi (Reeve, 1859)

Original combination. Melania moerchi Reeve, 1859.

Synonyms. -.

Type locality. ‘Guinea danica’ according to Brot (1874), confirmed as Ghana by Pilsbry and Bequaert 1927.

Habitat. Freshwater.

Distribution. Ghana, Togo, Bénin and South-West Nigeria (Mandahl-Barth 1967; Salawu and Odaibo 2014).

Evidence in Bénin. Reported by Brown (1994).

IUCN status. Least concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165382A6009591.en

Remarks. Observed in our field data in ecoregion 517.

Potadoma nyongensis Spence, 1928

Original combination. Potadoma nyongensis Spence, 1928.

Synonyms. -.

Type locality. Nyong River at 3°35'N, 10°10'E, Cameroon.

Habitat. Freshwater.

Distribution. Currently, the species is only recorded from its type locality and the Man River at Sakbayeme Cameroon (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Endangered.

https://www.iucnredlist.org/species/184695/8315726

Remarks. Potadoma nyongoensis, as in MolluscaBase, is probably a misspelling. The type locality of this endemic species of Cameroon falls beyond the boundaries of the ecoregions considered here, but Man River at Sakbayeme is part of our study area.

Potadoma togoensis Thiele, 1928

Original combination. Potadoma togoensis Thiele, 1928.

Synonyms. -.

Type locality. White Volta River at Apaso, Ghana.

Habitat. Freshwater.

Distribution. Ghana and Togo (Brown 1994).

Evidence in Bénin. Perhaps included in Potadoma sp. reported by Adandedjan (2012).

IUCN status. Data Deficient.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165394A6014033.en

Remarks. Observed in our field data in ecoregion 517.

Potadoma trochiformis (Clench, 1929)

Original combination. Goodrichia trochiformis Clench, 1929.

Synonyms. -.

Type locality. Man River near Sakbayeme (NE of Edea), Cameroon.

Habitat. Freshwater.

Distribution. Currently, the species is reported only from its type locality (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Endangered.

https://www.iucnredlist.org/species/184704/8318057

Remarks. Possibly synonymous with P. nyongensis (see Mandahl-Barth 1967; Brown 1994).

Potadoma vogeli Binder, 1955

Original combination. Potadoma vogeli Binder, 1955.

Synonyms. -.

Type locality. Agnéby (river or stream) at Abgoville, Ivory Coast.

Habitat. Freshwater.

Distribution. Ivory Coast (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Vulnerable.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165393A6013707.en

Family PALUDOMIDAE Stoliczka, 1868

Genus Cleopatra Troschel, 1856

Cleopatra bulimoides (Olivier, 1804)

Original combination. Cyclostoma bulimoides Olivier, 1804.

Synonyms. Paludina senegalensis Morelet, 1860; Cleopatra pirothi Jickeli, 1881; Cleopatra bulimoides var. richardi Germain, 1911; Cleopatra bulimoides var. welwitschi von Martens, 1897.

Type locality. Kalidje Canal near Alexandria, Egypt.

Habitat. Freshwater.

Distribution. In West Africa this species occurs in Senegal, Guinea, Mali, Ivory Coast, Burkina Faso, Ghana, Togo, Bénin, Niger, Nigeria, and Chad (Brown 1994; Kristensen and Stensgaard 2010a), it also occurs in Northeast Africa, including the northern part of the East African Rift.

Evidence in Bénin. Observed during our field data in ecoregion 517.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/175131/7106773

Remarks. Observed in our field data in ecoregion 517. Cleopatra bulimoides is conchologically a highly polytypic species, with many nominal species in possible synonymy, such as C. cyclostomoides (Küster, 1852) and C. congener Preston, 1913. The species boundaries of C. bulimoides need to be explored by molecular methods.

Genus Pseudocleopatra Thiele, 1928

Pseudocleopatra togoensis Thiele, 1928

Original combination. Pseudocleopatra togoensis Thiele, 1928.

Synonyms. -.

Type locality. Volta River near Apaso, Ghana (in Togo according to Thiele, but apparently in SE Ghana near Akwamu).

Habitat. Freshwater.

Distribution. Ghana (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165404A6017727.en

Remarks. Pseudocleopatra togoensis is the type species of the genus.

Pseudocleopatra voltana Mandahl-Barth, 1973

Original combination. Pseudocleopatra voltana Mandahl-Barth, 1973.

Synonyms. -.

Type locality. Volta River at Daboya, Ghana.

Habitat. Freshwater.

Distribution. Ghana (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Data Deficient.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165376A6007457.en

Family POTAMIDIDAE H. Adams & A. Adams, 1854

Genus Tympanotonos Schumacher, 1817

Tympanotonos fuscatus (Linnaeus, 1758)

Original combination. Murex fuscatus Linnaeus, 1758.

Synonyms. Murex radula Linnaeus, 1758; Murex fuscatus radula Linnaeus, 1758 ; Nerita aculeata O. F. Müller, 1774; Tympanotonos radula (Linnaeus, 1758); Murex terebella Gmelin, 1791; Potamides granulatus (Lamarck, 1816).

Type locality. ‘M. Mediterraneo’, an incorrect reference to the Mediterranean Sea (Brown 1994).

Habitat. Brackish water.

Distribution. Senegal to Angola (Brown and Kristensen 1993; Brown 1994)

Evidence in Bénin. Sô River, Coastal lagoon of Ouidah Grand-Popo, Lake Aheme, Lake Nokoue, Porto-Novo Lagoon (Gnohossou 2006; Adandedjan 2012; Odountan 2017; Koudenoukpo 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165803A6137267.en

Remarks. Observed in our field data in ecoregion 517. Tympanotonus and Tympanotomus are very common misspellings and ill-founded emendations of the genus name Tympanotonos (Pilsbry & Bequaert, 1927).

Family THIARIDAE Gill, 1871(1823)

Genus Melanoides Olivier, 1804

Melanoides manguensis (Thiele, 1928)

Original combination. Melania manguensis Thiele, 1928.

Synonyms. -.

Type locality. Oti River at Mangu, East Ghana (located by Thiele in Togo).

Habitat. Freshwater.

Distribution. Ghana and Ivory Coast (Brown 1994)

Evidence in Bénin. Not reported.

IUCN status. Data Deficient.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165379A6008515.en

Remarks. Presence of this species in Togo is uncertain (Brown 1994).

Melanoides tuberculata (O. F. Müller, 1774)

Original combination. Nerita tuberculata O. F. Müller, 1774.

Synonyms. Melania (Melanoides) tuberculata (O. F. Müller, 1774); Melania tuberculata (O. F. Müller, 1774); Melanoides tuberculata tuberculata (O. F. Müller, 1774); Melanoides (Melanoides) tuberculata (O. F. Müller, 1774); Melanoides (Melanoides) tuberculata tuberculata (O. F. Müller, 1774); Melanoides tuberculatus (O. F. Müller, 1774); Striatella tuberculata (O. F. Müller, 1774); Melanoides fasciolata Olivier, 1804; Turritella tuberculata Link, 1807; Turritella turricula Link, 1807; Melania cancellata Say, 1829; Melania mauriciae Lesson, 1831; Melania terebra Lesson, 1831; Melania trunculata Lamarck, 1822; Melania virgulata Quoy & Gaimard, 1834; Melania ornata von dem Busch, 1842; Melania flammigera Dunker, 1844; Melania rivularis Philippi, 1847; Melania suturalis Philippi, 1847; Melania rustica Mousson, 1857; Melania commersoni Morelet, 1860; Melania inhambanica von Martens, 1860; Melania zengana Morelet, 1860; Melania dominula Tapparone Canefri, 1883; Melania flyensis Tapparone Canefri, 1883; Melania pellicens Tapparone Canefri, 1883; Melania singularis Tapparone Canefri, 1883; Melania baldwini Ancey, 1899; Thiara baldwini (Ancey, 1899); Melania tuberculata var. victoriae Dautzenberg, 1908; Melania carica Oppenheim, 1919; Melania dadiana Oppenheim, 1919; Melanoides (Melanoides) carica (Oppenheim, 1919); Melanoides (Melanoides) dadiana (Oppenheim, 1919); Melanoides tuberculata dadiana (Oppenheim, 1919); Melanoides tuberculata var. dautzenbergi Pilsbry & Bequaert, 1927.

Type locality. Coromandel coast, India.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Ivory Coast, Burkina Faso, Ghana, Niger, Bénin and Nigeria (Brown 1994; Gadzama 2012; Gadzama et al. 2015; Diakité et al. 2017).

Evidence in Bénin. Widespread in Bénin at freshwater sites including in Coastal lagoon of Ouidah Grand-Popo around Aho Channel (Adandedjan 2012), Nokoue lake and Porto-Novo Lagoon around Totchè Channel (Gnohossou 2006; Adandedjan 2012; Odountan et al. 2019b), Acron and Djidja (Agboho 2018), Pehunco town (Ibikounlé et al. 2014b), Alibori River (Agblonon Houelome et al. 2017), Oueme River (Zinsou 2017), Lake Ahémé around Tohonou (Odountan 2017).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T155675A120117210.en

Remarks. Observed in our field data in ecoregion 517. The taxonomic status of the parthenogenetic M. tuberculata is problematic, first because it contains African and Oriental strains, and the species has invaded many tropical freshwater habitats around the globe. Native and invasive strains both occur in West Africa (Van Bocxlaer et al. 2015).

Melanoides voltae (Thiele, 1928)

Original combination. Melania voltae Thiele, 1928.

Synonyms. -.

Type locality. Volta River at Apaso, Ghana.

Habitat. Freshwater.

Distribution. Ghana and Nigeria (Brown 1994; Mafiana and Beyioku 1998).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165406A6018396.en.

Genus Pachymelania E. A. Smith, 1893

Pachymelania aurita (O. F. Müller, 1774)

Original combination. Nerita aurita O. F. Müller, 1774

Synonyms. Strombus tympanorum africanus Chemnitz, 1786; Melania zonata Philippi, 1848; Melania balteata Philippi, 1851; Melania aurita Reeve, 1860; Melania histrionica Reeve, 1860; Io rota Reeve, 1860; Melania subaurita Brot, 1868; Melania soriculata Morelet, 1864; Claviger auritus Brot, 1874; Clavigerina aurita von Martens, 1903.

Type locality. Unknown.

Habitat. Brackish water.

Distribution. Senegal to Angola including Ivory Coast, Togo, and Nigeria (Binder 1968; Brown 1994; Imoobe 2008; Tampo 2015).

Evidence in Bénin. At coastal area of the Coastal lagoon of Ouidah Grand-Popo (Adandedjan 2012); Oueme River (Zinsou 2017); Sô River (Koudenoukpo 2018); Lake Nokoue and Lake Aheme (Odountan 2017).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165769A6112482.en

Remarks. Observed in our field data in ecoregion 517. The species is morphologically variable with respect to the number of spiral cords, threads and tubercles. A molecular systematic study of Pachymelania is required to assess species boundaries and morphological variation.

Pachymelania byronensis (W. Wood, 1828)

Original combination. Strombus byronensis W. Wood, 1828.

Synonyms. Melania owenii Gray, 1831; Melania tuberculosa Rang, 1832; Melania rangii Deshayes, 1838; Pachymelania bryoni Smith, 1893.

Type locality. Coast of Upper Guinea.

Habitat. Freshwater.

Distribution. Ivory Coast to Nigeria (Brown and Kristensen 1993; Brown 1994).

Evidence in Bénin. Coastal lagoon of Ouidah Grand-Popo (Adandedjan 2012), Oueme River (Zinsou 2017), Sô River (Koudenoukpo 2018), Lake Nokoue and Lake Aheme (Odountan 2017).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T175140A7112397.en

Remarks. Observed in our field data in ecoregion 517.

Pachymelania fusca (Gmelin, 1791)

Original combination. Murex fuscus Gmelin, 1791.

Synonyms. Murex fuscatus Maton, 1804; Pirena granulosa Lamarck, 1822; Melania quadriseriata Gray, 1831; Melania matoni Gray 1831; Melania mutans Gould, 1843; Melania tessellata Lea, 1850; Melania fuscaia Hanley, 1854–1858; Melania fusca Reeve, 1860; Melania loricata Reeve, 1860; Melania matoni var. loricata Boettger, 1885; Melania quadriseriata var. carinata Brot, 1868; Claviger matoni Brot, 1874; Clavigerina fusca quadriseriata von Martens, 1903.

Type locality. Unknown.

Habitat. Fresh and brackish water.

Distribution. Senegal to Angola (Brown and Kristensen 1993; Brown 1994).

Evidence in Bénin. Mainly at sites close to the Atlantic Ocean in Lake Nokoue and Lake Aheme (Odountan 2017), Coastal lagoon of Ouidah Grand-Popo (Adandedjan 2012), Oueme River (Zinsou 2017), Sô River (Koudenoukpo 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165779A6119724.en

Remarks. Observed in our field data in ecoregion 517. Like P. aurita this species has a very variable morphology.

Subclass Heterobranchia Burmeister, 1837

Order Ellobiida Van Mol, 1867 [see Bouchet et al. (2017) for this emendation]

Family ELLOBIIDAE L. Pfeiffer, 1854(1822)

Remarks. The family name was first introduced in synonymy, but is now available under art. 11.6 with the authorship determined by art. 50.7 (see Bouchet et al. 2017)

Genus Melampus Monfort, 1810

Melampus liberianus H. Adams & A. Adams, 1854

Original combination. Melampus liberianus H. Adams & A. Adams, 1854.

Synonyms. Melampus obovatus H. Adams & A. Adams, 1854.

Type locality. Liberia.

Habitat. Brackish (mangrove) and marine water.

Distribution. River estuaries from Liberia to DR Congo, including in Ghana, Cameroon and São Thomé (Pilsbry and Bequaert 1927; Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/175139/7111601

Remarks. Melampus obovatus represents a subadult stage of M. liberianus (Dohrn 1878).

Superorder Hygrophila Férussac, 1822

Remarks. Hydrophila was originally spelled as “hygrophiles” (vernacular), subsequently latinized by Herrmannsen (1847 [in 1846–1852]: 547) and established as a suborder. Later, it was treated by Thiele (1926 [in 1925–1926]: 136) as a “Sippe” [= superfamily] but it is now considered a- Superorder (see Bouchet et al. 2017)

Family BULINIDAE Fischer & Crosse, 1880

Genus Bulinus O. F. Müller, 1781

Bulinus globosus (Morelet, 1866)

Original combination. Physa globosa Morelet, 1866.

Synonyms. Bulinus (Physopsis) globosus (Morelet, 1866); Isidora (Physopsis) globosa (Morelet, 1866); Physa masakaensis Preston, 1913; Physopsis choziensis Preston, 1913.

Type locality. Dande River (Luanda Province), Angola.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Mali, Ivory Coast, Burkina Faso, Ghana, Togo, Bénin, Niger, Nigeria, Cameroon, Chad, Equatorial Guinea and Gabon (Ntonifor and Ajayi 2007; Okafor and Ngang 2008; Salawu and Odaibo 2014; Diakité et al. 2017; Abe et al. 2018; Ouedraogo et al. 2018)

Evidence in Bénin. Widespread, especially at Djèffa and Ganhatin (Assogba and Youssao 2002); Acron, Cotonou garden ASECNA, Djidja, Nikki, Péhunco and Pèrèrè towns, Sô Ava, Pahou, Sand quarries, and Sô Tchanhoué (Ibikounlé et al. 2009, 2013, 2014a; Agboho 2018); Alibori River (Agblonon Houelome et al. 2017); Sô River (Koudenoukpo 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T99504682A120114163.en

Remarks. Observed in our field data in ecoregion 517. Bulinus globosus and Bulinus spp. in general are important intermediate hosts for trematode parasites. Especially parasites of the genus Schistosoma cause debilitating tropical diseases in humans and livestock. Bulinus globosus is part of the B. africanus species complex (Jørgensen et al. 2011). Beyond the recognition of several species complexes, our general understanding of taxonomic diversity and species relationships within Bulinus is still limited (see Jelnes 1986), especially within the B. truncatus/tropicus complex where several polyploidisation events have taken place (Jørgensen et al. 2011). Bulinus globosus is diploid (2n = 36) (see Jelnes 1986).

Bulinus forskalii (Ehrenberg, 1831)

Original combination. Isidora forskalii Ehrenberg, 1831.

Synonyms. Bulinus (Pyrgophysa) forskalii (Ehrenberg, 1831); Bulinus (Pyrgophysa) mariei (Crosse, 1879); Physa apiculata Morelet, 1867; Physa capillacea Morelet, 1867; Physa clavulata Morelet, 1867; Physa gradata Melvill & Ponsonby, 1898; Physa semiplicata Morelet, 1867; Physa turriculata Morelet, 1867; Physa wahlbergi Krauss, 1848; Pyrgophysa mariei Crosse, 1879.

Type locality. Damietta, Egypt.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Mali, Ivory Coast, Burkina Faso, Ghana, Togo, Bénin, Niger, Nigeria, Cameroon, Chad, Equatorial Guinea and Gabon (Ntonifor and Ajayi 2007; Okafor and Ngang 2008; Salawu and Odaibo 2014; Diakité et al. 2017; Abe et al. 2018; Ouedraogo et al. 2018).

Evidence in Bénin. Widespread especially at Djèffa and Ganhatin (Assogba and Youssao 2002); Cotonou garden ASECNA, Nikki, Péhunco and Pèrèrè towns, Sô Ava, Pahou’s sand quarries, Cocotomey, Djidja, and Sô Tchanhoué (Ibikounlé et al. 2009, 2013, 2014a; Agboho 2018), Alibori River (Agblonon Houelome et al. 2017), Sô River (Koudenoukpo 2018).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165794/6130451

Remarks. Observed in our field data in ecoregion 517. Bulinus forskali as in Agboho (2018), is a misspelling. The B. forskalii species complex appears to be the most deeply split Bulinus species complex (Jørgensen et al. 2011). Species of this complex have a much higher spire than species of other Bulinus complexes (Brown 1994). Further investigation did not clarify the issue: study of its shell morphology suggests B. jousseaumei to be distinct (Kristensen and Christensen 1991), whereas enzyme analyses support synonymization (Jelnes 1986).

Bulinus jousseaumei (Dautzenberg, 1890)

Original combination. Isidora jousseaumei Dautzenberg, 1890.

Synonyms. -.

Type locality. Senegal River near Medine, Mali.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Mali, Burkina Faso, Togo, Niger, and Nigeria (Brown 1994, Salawu and Odaibo 2014).

Evidence in Bénin. Reported (Salawu and Odaibo 2014)

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165388A6011857.en

Remarks. Two specimens observed in our field data in ecoregion 517 seem to be referable to B. jousseaumei (Dautzenberg, 1890). The species is not native in Bénin (Salawu and Odaibo 2012), but seems to be introduced. Bulinus jousseaumei belongs to the B. africana species complex, and is either a distinct species (Mandahl-Barth 1965) or a form of B. globosus (Wright 1961).

Bulinus senegalensis O. F. Müller, 1781

Original combination. Bulinus senegalensis O. F. Müller, 1781.

Synonyms. -.

Type locality. Podor, Senegal.

Habitat. Freshwater.

Distribution. Mainly Sahelian, from Guinea through the middle Niger Basin to Nigeria (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165398A6015514.en

Remarks. Being first introduced as ‘Le Bulin’ by Adanson (1757), Bulinus senegalensis is the type species of the genus. The species belongs to the B. forskalii species complex (Brown 1994), is diploid (2n = 36) and enzyme analyses indicated that it is distinct from B. forskalii (Jelnes 1986). The species occurs mainly in seasonal rain pools and aestivates during drought (Brown 1994). It was not observed in our survey of perennial waterbodies in Bénin. The species is an important host of Schistosoma haematobium in various regions of West Africa.

Bulinus truncatus (Audouin, 1827)

Original combination. Physa truncata Audouin, 1827.

Synonyms. Bulinus (Bulinus) truncatus (Audouin, 1827); Bulinus (Bulinus) truncatus truncatus (Audouin, 1827); Bulinus (Isidora) truncatus (Audouin, 1827); Bulinus (Isidora) truncatus truncatus (Audouin, 1827); Physa rohlfsi Clessin, 1886; Bulinus (Bulinus) truncatus rohlfsi (Clessin, 1886); Bulinus rohlfsi (Clessin, 1886); Physa mutandaensis Preston, 1913.

Type locality. Egypt.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Mali, Ivory Coast, Burkina Faso, Ghana, Togo, Bénin, Niger, Nigeria, Cameroon, Chad, Equatorial Guinea, and Gabon (Ntonifor and Ajayi 2007; Okafor and Ngang 2008; Salawu and Odaibo 2014; Diakité et al. 2017; Abe et al. 2018; Ouedraogo et al. 2018).

Evidence in Bénin. Widespread especially at Djèffa and Ganhatin (Assogba and Youssao 2002), Accron, Cotonou garden ASECNA, Djidja, Nikki, Péhunco and Pèrèrè towns, Sô Ava, Pahou, Sand quarries, and Sô Tchanhoué (Ibikounlé et al. 2009, 2013, 2014a; Agboho 2018), Alibori River (Agblonon Houelome et al. 2017), Sô River (Koudenoukpo 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T99507883A120114540.en

Remarks. Observed in our field data in ecoregion 517. Bulinus truncatus is tetraploid (2n = 72) (Jelnes 1986) and morphologically very variable (Brown 1994). Detailed studies with high-throughput sequencing are required to address many of the outstanding questions related to the biology of this species, for example, on heterozygosity and potential interspecies molecular variation across the wide geographic range of B. truncatus. Species such as B. guernei (Dautzenberg, 1890), B. contortus Michaud, 1829, B. coulboisi (Bourguignat, 1888), B. mutandaensis (Preston, 1913), and B. sericinus (Jickeli, 1874) are regularly considered to be synonyms of B. truncatus (Brown, 1994).

Bulinus umbilicatus Mandahl-Barth, 1973

Original combination. Bulinus umbilicatus Mandahl-Barth, 1973.

Synonyms. -.

Type locality. Zalingei in Darfur Province, West Sudan.

Habitat. Freshwater.

Distribution. Widespread in West Africa mainly in Mali, Niger, Nigeria, and Chad (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/175134/7109049

Remarks. Bulinus umbilicatus is diploid (2n = 36), belongs to the B. africanus species complex (Jelnes 1986; Brown 1994), and displays intergradation with B. globosus both at the level of allozymes and shell morphology (Jelnes 1986; Kristensen and Christensen 1991). Like B. senegalensis, the taxon frequently occurs in seasonal aquatic habitats and aestivates during dry periods (Brown 1994).

Genus Indoplanorbis Annandale & Prashad, 1921

Indoplanorbis exustus (Deshayes, 1833)

Original combination. Planorbis exustus Deshayes, 1833.

Synonyms. Planorbis indicus Benson, 1836; Planorbis coromandelicus Dunker, 1856; Planorbis zebrinus Dunker, 1856; Planorbis hindu Clessin, 1886; Planorbis indicus var. zonatus Clessin, 1886.

Type locality. marshes on the coast of Malabar, South West India.

Habitat. Freshwater.

Distribution. Ivory Coast and Nigeria (Brown 1994; Koné et al. 2013).

Evidence in Bénin. Freshwater habitats of Parakou city, Pahou, Sand quarry, Acron, Djassin, Djeffa, Tchivié, Cotonou, ASECNA garden, and Sô Ava (Ibikounlé et al. 2009, 2013; Agboho 2018).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165594/17211568

Remarks. Observed in our field data in ecoregion 517. Some authors have erroneously used “1834” as the year of publication. The species is native to Asia, and has been introduced into West Africa by man (Kristensen and Ogunnowof 1987). Originally, these introductions were to Ivory Coast and Nigeria, but our data suggest that the taxon is spreading in West Africa. Although Indoplanorbis hosts Schistosoma species that parasitise domestic livestock in Asia, no evidence exists to our knowledge that it transmits schistosomes in Africa.

Family LYMNAEIDAE Rafinesque, 1815

Genus Radix Montfort, 1810

Radix natalensis (Krauss, 1848)

Original combination. Linnaeus natalensis Krauss, 1848.

Synonyms. Lymnaea (Radix) natalensis Krauss, 1848; Lymnaea natalensis Krauss, 1848; Radix (Exsertiana) natalensis (Krauss, 1848); Radix hovarum (Tristram, 1863); Limnaea hovarum Tristram, 1863; Limnaeus natalensis var. exsertus von Martens, 1866; Limnaea orophila Morelet, 1867; Limnaea electa Smith, 1882; Limnaea caillaudi Bourguignat, 1883; Limnaea acroxa Bourguignat, 1883; Lymnaea caillaudi (Bourguignat, 1883); Limnaea gravieri Bourguignat, 1885; Limnaea nyansae von Martens, 1892; Limnaea arabica Smith, 1894; Limnaea arabica Smith, 1894; Lymnaea arabica Smith, 1894; Limnaea elmeteitensis. Smith, 1894; Limnaea humerosa von Martens, 1897; Limnaea undussumae von Martens, 1897; Limnaeus dakaensis Sturany, 1898.

Type locality. Natal, South Africa.

Habitat. Freshwater.

Distribution. Widespread in West Africa including Senegal, Burkina Faso, Ivory Coast, Nigeria (Gadzama 2012; Koné et al. 2013; Salawu and Odaibo 2014; Diakité et al. 2017).

Evidence in Bénin. Djèffa and Ganhatin (Assogba and Youssao 2002), Acron, Baaka, Cotonou ASECNA garden, Cotonou beach temporary ponds, Lake Nokoue, Lake Toho-Todougba, and Sèhouè bridge (Ibikounlé et al. 2009; Agboho 2018), Nikki, Pehunco and Pèrèrè towns (Ibikounlé et al. 2014a, b)

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T165761A120112796.en.

Remarks. Observed in our field data in ecoregion 517. Some authors have erroneously used “1948” (Agboho 2018) as year of the publication of the name. The species occurs throughout most of Africa, including Madagascar, several islands in the Indian Ocean and Arabia. It usually lives in permanent waters and it is rare in seasonal habitats, unless they are directly connected to permanent waters. Molecular work is required to examine whether R. natalensis indeed has a very wide geographical distribution or whether it consists of several cryptic species that have been lumped together.

Family PLANORBIDAE Rafinesque, 1815

Genus Biomphalaria Preston, 1910

Biomphalaria pfeifferi (Krauss, 1848)

Original combination. Planorbis pfeifferi Krauss, 1848.

Synonyms. Planorbis (Coretus) pfeifferi Krauss, 1848; Planorbis (Planorbula) pfeifferi Krauss, 1848; Biomphalaria madagascariensis (Smith, 1882); Planorbis hildebrandti von Martens, 1882; Planorbis madagascariensis Smith, 1882; Planorbis bowkeri Melvill & Ponsonby, 1893; Planorbis nairobiensis Dautzenberg, 1908; Planorbis hermanni Boettger, 1910.

Type locality. Natal in Umgeni Valley, South Africa.

Habitat. Freshwater.

Distribution. Widespread especially in Ivory Coast, Burkina Faso Niger, Nigeria (Okafor and Ngang 2008; Salawu and Odaibo 2014; Diakité et al. 2017; Abe et al. 2018; Ouedraogo et al. 2018).

Evidence in Bénin. Widespread especially at Djèffa and Ganhatin (Assogba and Youssao 2002), Toho Todougba Lake, Kpinnou Lake, Sonon, Nikki, Péhunco and Pèrèrè towns, Sô Ava (Ibikounlé et al. 2009, 2013, 2014a; Agboho 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2015.RLTS.T165782A85689765.en

Remarks. Observed in our field data in ecoregion 517. Enzyme studies on populations of B. pfeifferi from Cameroon and Senegal have found consistent biological differences (Mimpfoundi and Greer 1990), suggesting that multiple West African species of Biomphalaria may have been lumped in B. pfeifferi.

Biomphalaria camerunensis (Boettger, 1941)

Original combination. Australorbis camerunensis Boettger, 1941.

Synonyms. Biomphalaria alexandrina wansoni Mandahl-Barth, 1957.

Type locality. Mongongo, NW of Mount Cameroon, Cameroon.

Habitat. Freshwater.

Distribution. From Ghana eastwards to Central African Republic (Brown 1994).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/175130/7105918

Remarks. In Cameroon B. camerunensis is confined to the southern equatorial climatic zone (Greer et al. 1990), and it was never found in the same site as B. pfeifferi (Brown, 1994).

Genus Gyraulus Charpentier, 1837

Gyraulus costulatus (Krauss, 1848)

Original combination. Planorbis costulatus Krauss, 1848.

Synonyms. Planorbis (Gyraulus) costulatus Krauss, 1848; Caillaudia angulata Bourguignat, 1883.

Type locality. Natal in Umgeni Valley, South Africa.

Habitat. Freshwater.

Distribution. From Senegal to Angola including Ivory Coast, Bénin and Nigeria (Brown 1994; Salawu and Odaibo 2014).

Evidence in Bénin. Alibori River (Agblon Houelome et al. 2017).

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165767/6111409

Remarks. Observed in our field data in ecoregion 517. The taxonomy of African Gyraulus is poorly known, but Meier-Brook (1983) found the African species G. costulatus and G. connollyi to have distinct anatomical characteristics that warranted him to place them in the subgenus Caillaudia Bourguignat, 1883. So far, this alternate representation has not been formally accepted.

Genus Hovorbis Brown & Mandahl-Barth, 1973

The genus was formerly known as Afrogyrus Brown and Mandahl-Barth, 1973, which however is an invalid junior homonym of the coleopteran genus Afrogyrus Brinck, 1955. Özdikmen and Darilmaz (2007) altered the name to Africanogyrus, however, the available name Hovorbis Brown and Mandahl-Barth, 1973 has priority.

Hovorbis coretus (de Blainville, 1826)

Original combination. Planorbis coretus de Blainville, 1826.

Synonyms. Planorbis coretus de Blainville, 1826; Africanogyrus coretus (de Blainville, 1826); Afrogyrus coretus (de Blainville, 1826); Planorbis misellus Morelet, 1867; Planorbis (Spiralina) anderssoni Ancey, 1890; Planorbis anderssoni Ancey, 1890.

Type locality. Podor, Senegal.

Habitat. Freshwater.

Distribution. Bénin, Burkina Faso, Cameroon, Chad, Ivory Coast, Equatorial Guinea, Ghana, Guinea, Guinea-Bissau, Niger, Nigeria, Sierra Leone, Togo. (see www.iucnredlist.org/species/165775/120113348).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T165775A120113348.en

Remarks. Two specimens observed in our field data in ecoregion 517 seem to be referable to H. coretus. This species was first introduced as ‘Le Coret’ by Adanson (1757). Several potential synonyms are mentioned in Brown (1994), but more study of these taxa is required to verify their status.

Genus Segmentorbis Mandahl-Barth, 1954

Segmentorbis angustus (Jickeli, 1874)

Original combination. Segmentina angusta Jickeli, 1874.

Synonyms. Planorbis (Segmentina) emicans Melvill & Ponsonby, 1892; Segmentina (Hippeutis) emicans (Melvill & Ponsonby, 1892); Segmentina kempi Preston, 1912.

Type locality. Toquor River at Mekerka (west of Asmara) in Hamasen Province, Ethiopia.

Habitat. Freshwater.

Distribution. Ivory Coast (Diakité et al. 2017); Nigeria and Cameroon (Kristensen and Stensgaard 2010; Salawu and Odaibo 2012; Salawu and Odaibo 2014).

Evidence in Bénin. Not reported.

IUCN status. Least Concern.

https://www.iucnredlist.org/species/165771/6114438

Remarks. Segmentorbis angustus is the type species of the genus. The small body size of Segmentorbis species (<6 mm) implies that it may be sometimes be overlooked in freshwater snail surveys. Segmentorbis angustus occurs in permanent waterbodies, often within the vegetation.

Segmentorbis kanisaensis (Preston, 1914)

Original combination. Segmentina kanisaensis Preston, 1914.

Synonyms. Segmentorbis formosa Connolly, 1928.

Type locality. Nile at Kanisa, South Sudan.

Habitat. Freshwater.

Distribution. Widely distributed in West Africa from Gambia to Chad (Albrecht et al. 2008)

Evidence in Bénin. Not Reported.

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2010-3.RLTS.T165763A6107847.en

Remarks. This species can be readily distinguished from S. angustus by its depressed shell with strongly carinated periphery. It is sometimes found together with S. angustus, but also occurs in temporary waters (Brown 1994).

Family PHYSIDAE Fitzinger, 1833

Genus Afrophysa Starobogatov, 1967

Afrophysa brasiliensis (Küster, 1844)

Original combination. Physa brasiliensis Küster, 1844.

Synonyms. Physa mosambiquensis Clessin, 1886; Physa (Aplecta) waterloti Germain, 1911; Aplexa waterloti Brown, 1994.

Type locality. “Brasil” but Taylor (2003) restricted it to Porto Alegre, Rio Grande do Sul.

Habitat. Freshwater.

Distribution. Ghana, Togo and Nigeria (MolluscaBase 2018).

Evidence in Bénin. Porto-Novo (Germain 1911), Sô River (Odountan 2017; Koudenoukpo 2018).

IUCN status. Least Concern (evaluated under Aplexa waterloti).

https://www.iucnredlist.org/species/165396/6014756

Remarks. Observed in our field data in ecoregion 517. Physa (Aplecta) waterloti Germain, 1911 was established by Taylor (2003) as junior synonym of Afrophysa brasiliensis based on type specimens (from Bénin) which were morphologically degraded and very bad. Molecular work on specimens from the type locality in Brazil and West Africa is required to resolve relationships within Afrophysa.

Genus Physella Haldeman, 1842

Physella acuta (Draparnaud, 1805)

Original combination. Physa acuta Draparnaud, 1805.

Synonyms. Haitia acuta (Draparnaud, 1805); Lymnaea heterostropha Say, 1817; Physa fontana Haldeman, 1841; Physa inflata Lea, 1841; Physa charpentieri Küster, 1850; Physa heterostropha nigricans var. callosa Rigacci, 1866; Physa heterostropha var. gibbosa Rigacci, 1866; Physa heterostropha var. minor Rigacci, 1866; Physa lata Tryon, 1865; Physa plicata De Kay, 1843; Physa philippii Küster, 1844; Physa primeana Tryon, 1865; Physa say de Blainville, 1826; Physa striata Menke, 1828; Physa tenuissima Lea, 1864.

Type locality. River Garonne, France.

Habitat. Freshwater.

Distribution. Widely distributed in West Africa from Senegal to Angola (Van Damme et al. 2017)

Evidence in Bénin. Acron, Cocotomey, Djeffa, and Djidja (Agboho 2018).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2017-3.RLTS.T155538A91354457.en

Remarks. Observed in our field data in ecoregion 517. The taxon is native to America and has been introduced in many other regions around the world including Europe, Asia and Africa. The African Physella fauna likely consists of a composite from multiple introductions. Nominal species such as Physa borbonica Férussac, 1827, P. cubensis Pfeiffer, 1839, P. canariensis Bourguignat, 1856, P. tenerifae Mousson, 1872, P. mamoi Benoit, 1875, and Aplecta orbignyi Mazé, 1883, considered as synonyms of P. acuta (e.g Brown 1994), are not mentioned in MolluscaBase.

Genus Stenophysa von Martens, 1898

Stenophysa marmorata (Guilding, 1828)

Original combination. Physa marmorata Guilding, 1828.

Synonyms. Limnea (Physa) rivalis Sowerby, 1822; Aplexa marmorata (Guilding, 1828); Physa acuminata Villa & Villa, 1841; Aplecta sowerbyana d’Orbigny, 1841.

Type locality. St. Vincent, Lesser Antilles.

Habitat. Freshwater.

Distribution. Ivory Coast (Bony et al. 2008), Nigeria (Oloyede et al. 2017).

Evidence in Bénin. Djèffa and Ganhatin (Assogba and Youssao 2002), Sô Ava (Ibikounlé et al. 2013).

IUCN status. Least Concern.

http://dx.doi.org/10.2305/IUCN.UK.2011-2.RLTS.T189786A8768994.en

Remarks. Observed in our field data in ecoregion 517.

Discussion

This study provides the first checklist of fresh and brackish water gastropods in Bénin and adjacent ecoregions, i.e., ecoregions 505–508 and 513–519 of Abell et al. (2008). It comprises a total of 60 species, classified in 28 genera. More specifically, Architaenioglossa, Cerithiimorpha, Cycloneritida, Ellobiida, Hygrophila, and Littorinimorpha comprise 9, 19, 7, 1, 17, and 7 species, respectively. From the 16 families listed, Pachychilidae, Ampullariidae, Neritidae, Bulinidae, and Thiaridae were the most diverse with 9, 8, 7, 7, and 6 species, respectively. Of the 60 species listed, 37 are recorded (sometimes uncertain) in Bénin (~ 62 %), indicating a considerable species richness. The high richness in Pachychilidae relates to the diversity within the genus Potadoma, whereas the high richness in Ampullariidae relates to the diversity within the genera Pila and Lanistes throughout (sub-)tropical Africa (Cowie 2015). However, almost half of the Pachychilidae and one third of the ampullariids that are recorded in this study have not been recorded directly from Bénin. The fact that only a small part of Bénin’s aquatic environments, especially around the Niger River, the largest river in West Africa, have been sampled might explain why some species that are broadly distributed in West Africa such as Pila wernei (endemic to the Niger River basin) and Bulinus senegalensis O. F. Müller, 1781 have not been detected in our sampling.

Our findings with literature-based data also provoked some taxonomic concerns, because several papers on the fresh and brackish water malacofauna of Bénin or West-Africa, contained several (nomenclatural) errors. A case in point is the erroneous listing of Codakia orbicularis (Linnaeus, 1758), Cardita calyculata (Linnaeus, 1758), Thais coronata califera (Lamarck, 1822), Thais nodosa (Linnaeus, 1758), Turritella Lamarck, 1799, Polinices Montfort, 1810, Patella Linnaeus, 1758 as non-marine gastropod species in Bénin (e.g., Adandedjan 2012). These taxa were excluded in this study. In addition, we were unable to find information on Melanoides anomala (Smith, 1877) reported from Bénin (Adandedjan et al. 2012), and this taxon was consequently omitted. This identification seems to refer to Melanoides anomala (Dautzenberg & Germain, 1914), which has its type locality in the DR Congo and is endemic to the Congo Basin (Brown 1994). The difference in authorship and the report of the species outside its known region is suspect and calls for verification. Similarly, records that cannot be checked, e.g., Lanistes ovum (Agblonon Houelome et al. 2017) because specimens have not been illustrated and nor deposited in publicly accessible institutions, should be treated with caution. Hence, until compelling evidence indicates otherwise, we regard such doubtful species records in the literature as misidentifications.

Although only four species are threatened (Endangered/Vulnerable), a significant number of species has been assessed as Data Deficient, Not assessed or Not applicable. One of the main reasons for Data Deficiency in molluscs is taxonomic uncertainty and poor geographic knowledge (Seddon et al. 2011). Moreover, in West Africa, there are only few, reliable, recent survey data available, so that more species were marked as Data Deficient (Seddon et al. 2011). Therefore, a large field inventory is required that should focus on diverse habitats of fresh and brackish water from North to South with the possibility of molecular analyses. Moreover, species such as Afrophysa brasiliensis (Küster, 1844), Lanistes guinaicus mutation depressa Germain, 1917, Lanistes chaperi (Kobelt, 1912), Lanistes ovum Troschel, 1845, Physa (Aplecta) waterloti Germain, 1911, Pila ovata (Olivier, 1804), and Radix natalensis (Krauss, 1848) need further taxonomic study.

Bénin and its transboundary basins present a diversified fresh and brackish water gastropod fauna. The current checklist contains information on 60 species. However, many of these species require more detailed taxonomic and phylogenetic scrutiny, our current knowledge remains in its infancy. This checklist is hence an updated baseline for further taxonomic and ecological studies of the fresh and brackish water gastropods of Bénin and adjacent West African ecoregions.

Acknowledgements

CZK and OHO thank the Belgian National Focal Point to the Global Taxonomy Initiative of the CEBioS programme, financed by the Belgian cooperation for development (DGD) for granting the taxonomy capacity building Internships at RBINS, Brussels. OHO gratefully acknowledges the International Foundation for Science (Grant I2_A_6057-1) and the Rufford Foundation (26531-1) for their financial support. BVB was supported by ANR-JCJC-EVOLINK. We thank the anonymous reviewer for providing helpful comments that improved the manuscript substantially.

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1 Contributed equally as the first authors.