SPECIAL ISSUE REGULAR PAPER
Review of the cichlid genus Thysochromis (Teleostei: Ovalentaria) with the description of a
new species from the Kouilou Province in the Republic of Congo, west–central Africa
Gina Walsh 1,3,4 |Anton Lamboj 2 | Melanie L.J. Stiassny 3
1
University of the Witwatersrand, School of Animal Plant and Environmental Sciences,
Braamfontein, Johannesburg, South Africa
2
University Vienna, Faculty of Life Sciences, Department for Integrative Zoology,
Althahnstrasse 14, Vienna, Austria
3
American Museum of Natural History, Department of Ichthyology, Central Park West at 79th
Street, New York, New York, USA
4
Flora Fauna & Man Ecological Services Ltd., Road Town, Tortola, British Virgin Islands
Correspondence
Gina Walsh, University of the Witwatersrand, School of Animal Plant and Environmental
Sciences, Braamfontein, Johannesburg, South Africa, 2000
Email: g.walsh@florafaunaman.com
This article has been accepted for publication and undergone full peer review but has not been
through the copyediting, typesetting, pagination and proofreading process which may lead to
differences between this version and the Version of Record. Please cite this article as doi:
10.1111/jfb.14144
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Funding information
Initial field studies were part of an environmental impact assessment in the region. Subsequent
collection surveys were supported by the University of the Witwatersrand, University Research
Council Grant, the National Research Foundation Rated Researchers Incentive Grant 103581 and
the Axelrod Curatorship of the American Museum of Natural History.
ABSTRACT
A new species of the chromidotilapiine genus Thysochromis, is described from the Noumbi and
Kouilou River drainages in the Republic of Congo. Based on the current investigation,
Thysochromis is resolved as containing two geographically disjunct species, T. ansorgii from
localities in the upper Guinean ichthyofaunal province (Ivory Coast, Ghana, Benin and Nigeria)
and Thysochromis emili sp. nov. restricted to coastal regions of the Republic of Congo in the
lower Guinean province.
KEYWORDS
lower Guinea, morphology, mtDNA, Thysochromis emili sp. nov., taxonomy
1 | INTRODUCTION
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In a report on the fishes of the lower Kouilou River in the Republic of Congo, Teugels et al.
(1991) recorded the presence in Lake Koubambi of two specimens (MRAC 90-57-P-5288-89) of
the cichlid Thysochromis ansorgii (Boulenger 1901). They noted that this record represented a
significant range extension for a species that was otherwise known only from the upper Guinean
ichthyological province in south-eastern Ivory Coast, south-western Ghana, Benin and Nigeria
(Figure 1). Later, Lamboj & Stiassny (2007) commented on the questionable composition and
taxonomy of the genus, originally named Thysia by Loiselle & Welcomme (1972) but renamed
due to preoccupation as Thysochromis by Daget (1988). While the synonymy of Pelmatochromis
(Thysochromis) arnoldi Boulenger 1912 with T. ansorgii has generally been accepted (Loiselle
& Welcomme, 1972; Fricke et al., 2018), the status of Pelmatochromis (Thysochromis)
annectens Boulenger 1913 has remained uncertain (Lamboj, 2004; Froese & Pauly, 2019), as
Loiselle & Welcomme (1972) considered the only differences between T. annectens (type
locality, lower Niger River) and T. ansorgii (type locality, Ethiop River in Niger Basin) were
slight variants of colour patterning. Beyond these they were unable to separate the two and
concluded that it was best to accept T. annectens as a species inquirenda (Froese & Pauly, 2019).
A fourth species, Tilapia maculifer Ahl 1939 (type locality, Lagos, Nigeria) was synonymised
with T. ansorgii by Daget (1991), but unfortunately the holotype and unique specimen, originally
housed in the Zoologisches Museum Berlin, is lost and unavailable for study (Fricke et al.,
2019). Pending a more detailed review, Lamboj & Stiassny (2007) accepted the identification of
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the two Lake Koubambi specimens as T. ansorgii thereby recognising a range extension for the
species of well over 1000 km from the upper Guinean ichthyofaunal province into the southern
portion of the lower Guinean province.
Walsh et al. (2014) reported on a series of collections made throughout the lower
Kouilou, Noumbi and nearby coastal basins where numerous additional samples of
Thysochromis spp. were recovered from Lakes Youbi and Yangala. In 2017, G.W. collected
additional specimens in both black water (Bondo River, Noumbi Basin) and clear water (Tsissa
River, Kouilou Basin) rivers in the same region (Figure 1). Examination of these materials and
comparison of the available type materials of the putative West African species, indicates that
although phenetically similar, the Republic of Congo specimens are diagnostically distinct from
their West African congener and in the current paper we describe the Congolese populations of
Thysochromis as a new species.
2 | MATERIALS AND METHODS
Collection permits were issued by the National Institute for Research in Exact and Natural
Sciences (IRSEN Permit 205 and 328) and CITES permits for exportation are CG1125774 and
CG1125818.
2.1 | Field Sampling
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Various lentic (lake and swamp) and lotic (river and stream) habitats were sampled in 2012 and
2017 in the lower Kouilou and Noumbi River basins, as well as in numerous coastal lakes and
associated drainages (Figure 1). Fish sampling effort was standardised according to habitat type
and fishes collected according to AFS/AIFRB/ASIH (2003) guidelines. Specimens are deposited
in the ichthyology collections of the American Museum of Natural History (AMNH) in New
York, USA, with all data accessible online (http://sci-web-001.amnh.org/db/emuwebamnh/)..
2.2 | Morphology
Twenty-five standard morphometric measurements and 14 meristic counts (Tables 1, 2) were
recorded following Barel et al. (1977). Vertebral and fin-ray counts were taken from
radiographed or cleared and stained (c&s) specimens. Total gill raker counts for the first arch
include the raker at the junction of ceratobranchial and epibranchial elements. Lateral line counts
exclude any small pored scales distal to the hypural plate.
For detailed anatomical investigation two specimens (T. ansorgii, AMNH 235838 and T.
emili sp. nov., AMNH 258135) were scanned using a Phoenix v/tome/x M scanner (GE
Measurements and Control; GR Digital; www.ge.com), processed using datos/x software 2.3 and
segmented and visualized using VG StudioMax 3.3 (Volume Graphics; www.heidelberg.com).
Institutional abbreviations follow Sabaj (2016), LS is standard length and LH, head length.
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The smatr package for (standardised) major axis estimation and testing routines (Warton
et al., 2012) was used in RStudio (www.rstudio.com) to calculate allometric coefficients for
morphometric data (Sidlauskas et al., 2011; Mipounga et al., 2019). Allometric analyses were
factorised using two groups to simultaneously test morphometric similarity between the upper
Guinean type materials and dissimilarity between those and lower Guinean specimens. Factor
groupings included (1) Thysochromis emili sp. nov. and (2) the type series of T. ansorgii, T.
annectens and T. arnoldi. Allometric coefficients for each factor were calculated using
standardised major axis regression of natural-log transformed morphometric traits against the
natural log of LS.
Although morphometric allometries were parallel between species, size-standardised
multivariate principal component analysis (PCA) could not be applied due to marked variation in
life stage structure amongst samples and limited among-group patterns on PC2–PC5 (Sidlauskas
et al., 2011). Bivariate plots from the regressions with parallel allometries and significant offset
intercepts (P < 0.05) were used to investigate morphological differences between the upper and
lower Guinean samples.
2.3 | Mitochondrial DNA
DNA extraction, cytochrome oxidase subunit I gene (coI) amplification and sequencing were
undertaken by Inqaba Biotechnical Industries (Pty) Ltd. ()www.inqababiotec.co.za). Contig
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assembly and sequence editing were performed using Geneious 11.1.5. (Kearse et al., 2012) and
GenBank accession numbers for the sequences generated in this study are given in Table 3.
2.4 | Habitat Association
Abiotic (landscape scale, physico-chemical and qualitative habitat) data were collected at 15
surveyed sites. Fish habitat assessment was undertaken following Kleynhans (2007) to estimate
the occurrence of broad fish-habitat cover types in various depth classes. Site slope, average
catchment slope, catchment size and stream order were modelled using Shuttle Radar
Topography Mission (SRTM) imagery at a 30 m resolution (METI & NASA, 2018) processed in
ESRI ArcMap10.5 (www.resources.esri.com).
For the purpose of illustrating habitat associations of T. emili sp. nov., abiotic and fish
community data were subjected to canonical correspondence analysis (CCA) using Canoco 4.5
(ter Braak & Smilauer, 2002). The CCA was carried out on log-transformed species and
environmental data. Forward selection with partial Monte Carlo permutation testing was used to
assess the significance of each environmental predictor variable for extending the subset of
explanatory variables used in the ordination model. The significance of axes was tested using
unrestricted Monte Carlo permutation testing (499 permutations’ P < 0.05).
3 | RESULTS
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3.1 | Group separation
Standardised major axis regressions indicated that the two geographically disjunct groups of
specimens differ significantly (P < 0.05) in allometric trajectories of caudal-peduncle length (P <
0.05) and postorbital length (pol) (P < 0.05; Figure 2). Caudal-peduncle length (cpl) showed a
weak negative allometry for upper Guinean samples (T. ansorgii group), while lower Guinean
samples (T. emili) exhibited a strong positive allometry (0.872 and 1.477, respectively). The
postorbital length was weakly positive for the upper Guinean samples (1.129) while the lower
Guinean samples showed a weak negative allometry (0.857)
Separation of upper and lower Guinean samples is further supported by the degree of
sequence divergence in the bar-code coI gene (Table 3) between exemplars from these two
regions. These data are represented here as a distance matrix (Figure 3) and divergence between
exemplars from the two geographically separated populations exceeds the standard heuristic
threshold of 3% commonly used as an indicator of species-level differentiation (Herbert et al.,
2003; Arroyave et al., 2019). While exceptions to this heuristic threshold certainly exist (Joyce et
al., 2011; van der Walt et al., 2017) these molecular data, taken in combination with the
morphometric separation highlighted above and a few qualitative anatomical differences
(discussed below), reveal a clear separation between upper and lower Guinean populations.
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Based on these combined data we describe here the lower Guinean populations of Thysochromis
as a new species.
It is worth noting that a few specimens previously identified as Thysochromis from intervening
regions are housed in museum collections. None are reported from Cameroon and the few from Gabon
have been examined in the present study. With the single exception of a juvenile collected near
Mayumba, in a coastal basin just north of the Kouilou in the Republic of Congo (MRAC A1-88-P-2497,
photograph examined), all others are misidenfications of the chromidotilapiine species Chromidotilapia
kingsleyae Boulenger 1898 and Divandu albimarginatus Lamboj & Snoeks 2000 (pers. obs).
3.2 | Thysochromis emili sp. nov.
Figures 4–5 and Table 1; urn:lsid:zoobank.org:pub:1E60CEA4-3DAE-45b7-AF1204EB6250E9D7.
3.2.1 | Holotype
AMNH 271740, male, 69.4 mm LS, Republic of Congo, Kouilou Province, Lake Youbi, 04o 11’
30.4” S, 11o 40’ 12.8” E, M.N. Jonker, V. Mamonekene, V. Boukaka Mikembi, 17 July 2012.
3.2.2 | Paratypes
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AMNH 271741, 6 specimens, 1 c&s, 55.4–66.7 mm LS, same data as holotype. MRAC 2018027-P-0003-0004, 2 specimens, 60.7–61.2 mm LS., same data as holotype. NMW 99244, 2
specimens, 58.2–62.4 mm LS, same data as holotype. AMNH 271742, 3 specimens, 63.1–67.2
mm LS, Republic of Congo, Kouilou Province, Lake Yangala, 04 o 07’ 26.1” S, 11o 35’ 48.9” E,
M.N. Jonker, V. Mamonekene, V. Boukaka Mikembi, 19 July 2012. ZSM 47495, 2 specimens,
63.4–65.0 mm LS, same data as AMNH 271742. AMNH 271747, 2 specimens. 36.0–54.0 mm
LS, Republic of Congo, Kouilou Province, Bondo River, 04o 4’ 7.04” S, 11o 38’ 3.08” E, G.
Walsh, V. Boukaka Mikembi, J. Mountou, 6 September 2017. AMNH 271748, 1 specimen, 61.0
mm LS, Republic of Congo, Kouilou Province, Tsissa River, 04o 0’ 57.63” S, 11o 42’ 4.09” E, G.
Walsh, V. Boukaka Mikembi, J. Mountou, 7 September 2017.
3.2.3 | Differential Diagnosis
While no unambiguous morphological autapomorphies have been located to diagnose T. emili sp.
nov., it is distinguished from its West African congener, T. ansorgii, by the following
combination of characters (Tables 1, 2). Fewer scale rows between the pectoral and pelvic-fin
origins (3–4 v. 5–6), jaw teeth closely spaced and evenly implanted over entire length of both
upper and lower jaws (v. widely space and unevenly implanted along distal portions) and a
supraoccipital crest that is continuous with the frontal ridge (v. terminating posterior to frontal
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ridge). Shorter postorbital length (38.2–41.9% v. 42.8–46.7% LH) and a shorter caudal peduncle
length (7.7–11.3% v. 11.4–12.7% LS).
3.2.4 | Description
Medium-sized cichlid, maximum recorded LS 91.3 mm (mature male, MRAC 90-57-P-5288;
Figure 4). Counts and proportional measurements for holotype and 18 paratypes given in Table
1. Deep-bodied (body depth, DB 38.4–47.8% LS), greatest depth at level of 4th or 5th dorsal-fin
spine. Head small (LH 34.2–38.9% LS, depth 65.0–76.8% LH), short postorbital length (38.2–
41.9% LH), snout short, mouth small with well-developed, fleshy lips. Dorsal head profile 40–
50° to mid-orbit, rising steeply to nape. Dorsal and ventral body profiles convex to short (7.7–
11.3% LS), deep (15.6–18.5% LS) caudal peduncle.
Dorsal fin XV–XVII (mode XVI) 9–11 (mode 10). Anal fin III 7–9 (mode 8). Dorsal spines
increase in length posteriorly. Soft dorsal and anal fins extending over caudal-fin base. Caudal
fin large, sub-truncate to rounded, with 14 branched rays. Pectoral fins short and rounded,
extending to mid-body, not reaching anus. Pelvic fins reaching just short of, or to anus in
females, extending beyond anal-fin origin in mature males. First branched ray of pelvic fin
longest in both sexes.
Jaws short and isognathus. Outer row teeth in both jaws, somewhat recurved unicuspids, with
distally flattened, bilaterally shouldered crowns (Figure 5a). Outer row premaxillary and dentary
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teeth evenly implanted, closely spaced over entire length of dentigerous arms (Figure 5a) v.
widely spaced and unevenly implanted along distal portions in T. ansorgii (Figure 5b). Two to
four inner rows of small, similarly shaped, unicuspid teeth restricted to anterior third of both
jaws. Infraorbital series with broad, plate-like first infraorbital (lachrymal) bearing 4 small,
sensory-canal pores. Second to fifth infraorbital elements narrow and tubular, forming complete
suborbital ring.
Lower pharyngeal jaw wider than long, with slightly convoluted ventral suture. Twenty-four
to 28 teeth along posterior row, symphysial teeth moderately robust, becoming slender laterally.
Eight to ten tuberculate ceratobranchial rakers along first arch, often short raker in angle of arch,
4–7 simple epibranchial rakers. Microbranchiospines lacking on inner faces of second to fourth
arches. Pharyngeal hanging pad moderately developed, extending just anterior to first
epibranchial.
Scales cycloid. Flank scales large, uniformly sized onto chest, 3–4 between pectoral and
pelvic-fin origins. Cheek with 3 scale rows, 4 horizontal scale rows on opercle. Prominent dark
opercular blotch unscaled. Pored lateral-line scales 26–28, upper and lower lateral lines not
overlapping. Upper line separated from dorsal-fin base at highest point (8th pored scale) by 2-2.5
scales, last pored scale separated by 1-1.5. Proximal third of caudal fin covered with small
interradial scales. Sixteen (rarely 15) circumpeduncular scales.
Total number of vertebrae: 24– 26, comprising 13 abdominal and 11–13 caudal centra.
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Supraoccipital crest contiguous with frontal ridge (Fig 5a) v. crest terminating posterior to frontal
ridge (Figure 5b).
3.2.5 | Coloration in life
Head and body yellowish or yellowish-brown, paler ventrally (Figure 6). Scaleless, dark
opercular spot often extending posteriorly over one or two scale rows. Three short dark bars
along mid-flank, not extending to ventrum. Single dark bar or rounded spot in midline or over
dorsal half of caudal peduncle. Flank scales ringed with dark-brown pigment contrasting with
paler central field, more strongly marked in males (Figure 6a) than females (Figure 6b). Ventral
portions of cheek, operculum and chest silvery with a greenish or turquoise flush. Cluster of
silvery scales located lateroventrally around vent, reduced in number and less clearly marked in
males (Figure 6a), prominent in mature females (Figure 6b). Belly flushed pale rosy pink in
mature females. Leading edge of pelvic fin darkly pigmented. Soft dorsal and anal fins with
alternating pale and dark maculae variously evident, but always present. Caudal-fin membranes
with conspicuous rows of maculae, strongest proximally. All fin spotting more prominent in
mature males than in females and juveniles. In preservation (Figure 4), ground coloration of
body brownish yellow, darker dorsally. Opercular spot and bars on flank and caudal peduncle
clearly visible, fin maculae variously evident.
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3.2.6 | Distribution
Despite extensive collections made during a number of surveys throughout the region, T. emili
sp. nov.is known from only five localities (Figure 1). Currently it has been recorded in the
Noumbi and Kouilou River drainages in the Republic of Congo and appears to be restricted to
larger systems in the coastal plain of the Republic of Congo. The species has been recorded from
Lakes Youbi, Yangala and Koubambi and in the Bondo and Tsissa Rivers. The record of T. emili
in Lake Koubambi is based on specimens collected by Teugels et al. (1991), but despite
extensive sampling of suitable habitat in that lake during the 2012 and 2017 expeditions, the
species was not re-collected there. Vreven et al. (2007) recorded multiple introductions of the
Nilo-Sudanic species, Heterotis niloticus (Cuvier 1829), throughout the region and Walsh et al.
(2014) reported on the dominance of H. niloticus in catches from Lake Koubambi. We suggest
that the current absence, or rarity, of T. emili sp. nov. in Lake Koubambi may be the result of
competition with introduced H. niloticus for habitat and resource partitions.
As noted above, examination of a photograph of a single juvenile Thysochromis specimen
(MRAC A1-88-P-2497, specimen lost) from a coastal basin just north of the Kouilou, in Gabon,
suggests that the distribution of T. emili sp. nov. probably extends into suitable habitats in
southern coastal Gabon.
3.2.7 | Habitat Preferences
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The species–environment correlations showed a cumulative percentage variance of species data
of 49.1% explained on the first two axes. Environmental variables significantly (P ≤ 0.05)
contributing towards the measured variance in the data include catchment size (P < 0.01)
conductivity (P < 0.01), turbidity (P < 0.01), stream order (P < 0.01) and aquatic macrophytes
(P < 0.05; Figure 7).
Thysochromis emili sp. nov. were collected exclusively in well oxygenated lakes and rivers
situated in higher order systems (> 4th order) of the Kouilou and Noumbi River basins. The
species was sampled over sandy substrate in shallow (< 0.5 m), clear, shoreline waters fringed by
abundant overhanging vegetation, deeply undercut banks and root wads. It was not found in
other coastal lake or river basins despite efforts to collect it in these localities. The new species
showed a positive correlation and co-occurrence with the distichodontid Nannocharax
parvus Pellegrin 1906 and two other omnivorous or herbivorous substrate-brooding cichlids
Coptodon guineensis (Günther 1862) and Coptodon tholloni (Sauvage 1884).
3.2.8 | Breeding Behaviour
Not known, but as compared with its west African congener and its preferred habitat, it is
probably a pair-bonding, cave brooder.
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3.2.9 | Etymology
The species is named for Emil Woolf Kentridge-Young, grandson of William Kentridge and
Anne Stanwix, in recognition of their support of research in Africa.
3.3 | Additional Material Examined
AMNH 258106, 12 specimens, Republic of Congo, Kouilou Province, Lake Youbi, 04o 11’
30.4” S, 11 o 40’ 12.8” E, M.N. Jonker, V. Mamonekene, V. Boukaka Mikembi, 17 July 2012.
AMNH 258135, 8 specimens, 1 c&s, Republic of Congo, Kouilou Province, Lake Yangala, 04 o
07’ 26.1” S, 11o 35’ 48.9” E, M.N. Jonker, V. Mamonekene, V. Boukaka Mikembi, 19 July
2012. AMNH 261035, 2 specimens, Republic of Congo, Kouilou Province, Lake Yangala, 04 o
07’ 26.1” S, 11o 35’ 48.9”, Mamonekene and Walsh, 19 July 2012. MRAC 90-57-P-5288-89, 2
specimens, Republic of Congo, Kouilou Province, Lake Koubambi, G. Teugels et al., 1990.
MRAC A1-088-P-2497, 1 specimen (photograph examined), Gabon, Petit ruisseau sur route
forestière aprés Doumvou, Mamonekene, 24 July 2001.
3.4 | Comparative material examined
3.4.1 | Thysochromis annectens
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BMNH 1913.7.15:8–9, syntypes, 2 specimens, 52.8–83.4 mm LS, Nigeria, Lower Niger River,
J.P. Arnold.
3.4.2 | Thysochromis arnoldi
BMNH 1912.2.2:10–12, syntypes of T. arnoldi, 3 specimens, 56.1–65.4 mm LS, Nigeria, lower
Niger River, J.P. Arnold.
3.4.3 | Thysochromis ansorgii
BMNH 1901.1.28:9–12, syntypes, 4 specimens, 40.7–67.5 mm LS, Nigeria, Niger River system,
Ethiop River at Sapele station, W.J. Ansorge.–MRAC 91-10-P-661–671, 11 specimens, 35.8–
54.0 mm LS, Nigeria, Niger River system, New Calabar River, Akpor, C.B. Powell, December
1990.–AMNH 225991, 2 specimens, 1 c&s, 54.5–61.5 mm LS, Nigeria, New Calabar River
system, stream 3 km southeast of Emuhoa, C.B. Powell, 5 January 1991.–AMNH 235838, 2
specimens, 1 c&s, 62.9–71.6 mm LS, Benin, Oueme River, small stream near game village, R.
Schelly et al., 13 November 2003.
4 | DISCUSSION
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Lamboj & Stiassny (2007) accepted the identification of Teugels et al. (1991) for two specimens
from Lake Koubambi in the Republic of Congo as T. ansorgii thereby recognizing a 1000+ km
range extension spanning two ichthyofaunal regions. However, based on the current study,
Thysochromis is resolved as containing two geographically disjunct species: T. ansorgii
(including T. annectens and T. arnoldi as synonyms) from the upper Guinean ichthyofaunal
province and T. emili sp. nov. restricted to the lower Guinean province, specifically the Kouilou
Department of the Republic of Congo. The Kouilou Department is located along the Atlantic
coastal plain in the southern portion of the lower Guinean ichthyofaunal province. The region
consists of low-altitude savanna and forest ranging between Gabon to the north and Cabinda to
the south (van Rooyen et al., 2016; FEOW, 2019). The lowland coastal area has a continuum of
beaches and dunes in the west, transitioning into undulating hills on the coastal plains and the
Mayumbe Escarpment in the east. The landscape is crossed by a dense network of drainage
channels flowing into larger rivers and natural lakes, resulting in a high freshwater habitat
heterogeneity (Vande Weghe, 2004; Walsh et al., 2014; van Rooyen et al., 2016). The high
richness in freshwater fish in the lower Guinean province (Stiassny et al., 2007) was probably
driven by the aquatic refugium offered by the forested west coast equatorial region during
climatic fluctuations during the Pleistocene (Lévêque, 1997; Brooks et al., 2011). It appears that
the lower and upper Guinean ichthyological provinces have more recently experienced recurrent
isolation during dry phases of the climatic cycle that reduced the rainforest between the Late
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Pleistocene and present day and which created optimal conditions for allopatric speciation
(Teugels et al., 1991; Lévêque, 1997).
The current study highlights the importance of including multiple data sources when
considering geographically widespread and taxonomically under-studied species where failure to
recognize divergent lineages has often resulted in the underestimation of diversity (Arroyave et
al., 2019).
ACKNOWLEDGEMENTS
Our thanks to J. Snoeks and M. Parrent (MRAC), J. Maclaine (BMNH) and M. Hakansson
(Gothenburg, Sweden) for the donation or loan of materials. We thank J.Y. Gaugris (Flora Fauna
and Man Ecological Services), V. Mamonekene and V.N. Boukaka Mikembi (University of
Marien Ngouabi, Republic of Congo) and M.N Jonker (Ecotone Freshwater Consultants) for
facilitation and participation of expeditions in the region. L. Kirtley, L. Passy and K. Wheeler
(Elemental Minerals) for logistical support in the field. We gratefully acknowledge B. Sidlauskas
(Oregon State University) and anonymous reviewers who gave input that improved the quality of
this paper. Finally, we thank Jean de Dieu Mountou, Frédéric Avoukou and Gislain Nakoundzi
Taty of Koutou Village for their invaluable assistance during our field collections.
Author Contributions
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G.W. designed field surveys, collected fish specimens and environmental data and performed
statistical computations. A..L performed morphometric and meristic analyses and M.L.J.S. was
responsible for CT scanning, qualitative morphological analysis and DNA analysis. All authors
contributed to the writing of the manuscript.
ORCID
Gina Walsh https://orcid.org/0000-0002-6859-4568
Melanie Stiassny https://orcid.org/0000-0001-8220-4768
REFERENCES
AFS/AIFRB/ASIH. (2003). Guidelines for the use of fishes in research. The American Fisheries
Society American Institute of Fisheries Research Biologists American Society of
Ichthyologists and Herpetologists, Bethesda, Maryland. Available at
http://www.asih.org/sites/default/files/documents/resources/guidelinesfishresearch2003draft.pdf. (last accessed 10 October 2018).
Arroyave, A., Martinez, C.M. & Stiassny, M.L.J. (2019). DNA barcoding uncovers extensive
cryptic diversity in the African long-fin tetra Bryconalestes longipinnis (Alestidae:
Characiformes). Journal of Fish Biology, DOI: 10.1111/jfb.13987.
This article is protected by copyright. All rights reserved.
Barel, C.D.N., Oijen, M.J.P., Witte, F. & Witte-Maas, E.L.M. (1977). An introduction to the
taxonomy of the Haplochromine Cichlidae from Lake Victoria. Netherlands Journal of
Zoology, 27(4), 333-389.
Braak, C.J.F. ter & Smilauer, P. (2002). CANOCO reference manual and Canodraw for
Windows user's guide: Software for canonical community ordination (version 4.5).
Microcomputer Power, New York, 500 pp.
Brooks, E.G.E., Allen, D.J. & Darwall, W.R.T. (2011). The Status and Distribution of
Freshwater Biodiversity in Central Africa. Gland, Switzerland and Cambridge, United
Kingdom: IUCN.
Daget, J. (1988). Thysochromis nom. nov. en remplacement de Thysia (Pisces, Cichlidae).
Cybium, 12(1), 97.
Daget, J. (1991). Thysochromis. In J. Daget, J.-P. Gosse, G.G. Teugels and D.F.E. Thys van den
Audenaerde (eds.) Check-list of the freshwater fishes of Africa (CLOFFA). ISNB,
Brussels; MRAC, Tervuren; and ORSTOM, Paris. Vol. 4. p. 480-481.
Fricke, R., Eschmeyer, W. N. & van der Laan, R. (eds) (2018). Catalog of Fishes: Genera,
Species, References. Available at
This article is protected by copyright. All rights reserved.
http://researcharchive.calacademy.org/research/ichthyology/catalog/fishcatmain.asp. Elec
tronic (last accessed 12 September 2018).
Freshwater Ecoregions of the World (FEOW). (2019). Freshwater Ecoregions of the World.
Available at www.feow.org/globalmap. (last accessed 19th June 2019).
Froese, R. & Pauly, D. (eds). (2019). FishBase: World Wide Web electronic publication.
Available at www.fishbase.org. (last accessed 12 July 2019).
Herbert, P.D.N, Ratnasingham, S. & de Waard, J. R. (2003). Barcoding animal life: cytochrome
oxidase subunit 1 divergences among closely related species. Proceedings of the Royal
Society B, 270, 313-322.
Joyce, D.A., Lunt, D.H., Genner, M.J., Turner, G.F., Bills, R. & Seehausen, O. (2011). Repeated
colonization and hybridization in Lake Malawi cichlids. Current Biology, 21, R108R109.
Kearse, M., Moir, R., Wilson, A., Stone-Havas, S., Cheung, M., Sturrock, S. & Thierer, T.
(2012). Geneious basic: An integrated and extendable desktop software platform for the
organization and analysis of sequence data. Bioinformatics, 28(12), 1647-1649.
This article is protected by copyright. All rights reserved.
Kleynhans, C.J. (2007). Module D: Fish Response Assessment Index in River EcoClassification:
Manual for EcoStatus Determination (version 2) Joint Water Research Commission and
Department of Water Affairs and Forestry report, Pretoria, South Africa. Available at
http://www.dwa.gov.za/iwqs/rhp/eco/EcoStatus/ModuleD_FRAI/Module%20D_FRAI.pd
f. (last accessed 11 October 2018)
Lamboj, A. (2004). The Cichlid Fishes of Western Africa. Birgit-Schmettkamp-Verlag,
Bornheim, Germany, 255 p.
Lamboj, A. & M.L.J. Stiassny (2007). Genus Thysochromis Daget, 1988. In The Fresh and
Brackish water fishes of Lower Guinea West-Central Africa. Volume II (Stiassny, M.L.J.,
Teugels, G.G & Hopkins. C.D, eds), pp. 320-322. Paris, IRD Éditions.
Leveque, C. (1997). Biodiversity dynamics and conservation: the freshwater fish of tropical
Africa. Cambridge University Press, United Kingdom. 435 pp.
Mipounga H.K, Cutler J., Mve Beh, J.H., Adam, B. & Sidlauskas B.L. (2019). Enteromius
pinnimaculatus sp. nov.(Cypriniformes: Cyprinidae) from southern Gabon. Journal of
Fish Biology, 1–16.
This article is protected by copyright. All rights reserved.
Loiselle P.V. & Welcomme, R.L. (1972). Description of a new genus of Cichlid fish from West
Africa. Revue de Zoologie et de Botaniques Africaines, 85, 37-58.
METI & NASA. (2018). ASTER GDEM is a product of METI and NASA. Available at
https://lpdaac.usgs.gov/data_access. (last accessed 11 October 2018).
Rooyen, M. van, Rooyen, N. van, Orban, B., Nsongola, G., Miabangana, E.S. & Gaugris, J.Y.
(2016). Floristic composition, diversity and structure of the forest communities in the
Kouilou département, Republic of Congo. Tropical Ecology, 57(4), 805–824.
Sabaj, M.H. (2016. Standard symbolic codes for institutional resource collections in herpetology
and ichthyology: an online reference. Version 6.5. Washington, D.C.: American Society
of Ichthyologists and Herpetologists. Available at http://www.asih.org (last accessed 16th
August 2016).
Sidlauskas, B.L., Mol, J.H. &Vari, R.P. (2011). Dealing with allometry in linear and geometric
morphometrics: a taxonomic case study in the Leporinus cylindriformis group
(Characiformes: Anostomidae) with description of a new species from Suriname.
Zoological Journal of the Linnean Society, 162, 103–130.
This article is protected by copyright. All rights reserved.
Stiassny, M.L.J., G.G. Teugels, & Hopkins, C.D. (2007). Poissons d’eaux douces et saumâtres de
basseGuinée, ouest de l’Afrique centrale. The fresh and brackish water fishes of lower
Guinea, west-centralAfrica, vol. 1. Paris: IRD Éditions, 800 pp.
Teugels, G. G., Snoeks, J., De Vos, L. & Diakanou-Matongo, J.C. (1991). Les poissons du bassin
inferieur du Kouilou (Congo). Tauraco Research Report 4, 109-139.
Walt, K. van der, Mäkinen, T., Swartz, E.R., & Weyl, O.L.F. ( 2017). DNA barcoding of South
Africa’s ornamental freshwater fish–are the names reliable? African Journal of Aquatic
Sciences, 42, 155-160.
Weghe, J.P. van de (2004). Forests of Central Africa. Nature and Man. Lanoo Publishers, Tielt,
Belgium, 365 pp.
Vreven, E.J., Musschoot, T., Boden, G. & Stiassny, M.L.J. (2007). Introduced or alien species of
Lower Guinea. In The Fresh and Brackish water fishes of Lower Guinea, West-Central
Africa. Volume I (Stiassny, M.L.J., Teugels, G.G & Hopkins. C.D, eds), pp. 59-101.
Paris: IRD Éditions.
This article is protected by copyright. All rights reserved.
Walsh, G., Jonker, M.N & Mamonekene, V. (2014). A collection of fishes from tributaries of the
lower Kouilou, Noumbi and smaller coastal basin systems, Republic of the Congo, Lower
Guinea, west-central Africa. Check List, 10(4), 900-912.
Warton, D. I., Duursma, R. A., Falster, D. S., & Taskinen, S. (2012) SMATR 3– an R package
for estimation and inference about allometric lines. Methods in Ecology and Evolution, 3,
257–259.
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SIGNIFICANCE STATEMENT
The composition and taxonomy of the genus Thysochromis Daget 1988 has long been considered
problematical and in need of revision. This study clarifies the composition of the genus,
synonymizing three described Upper Guinean species, and includes a description of a new species
of the chromidotilapiine cichlid genus from the lower Kouilou and Noumbi basins of southern
Republic of Congo in the Lower Guinean ichthyofaunal province.
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Accepted Article
CAPTIONS TO FIGURES
FIGURE 1 (a) Distribution of Thysochromis ansorgii (■→) and Thysochromis emili sp. nov.
(■→★). (b) Typical habitat in Lake Youbi and (c) in Tsissa River where T. emili were collected
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FIGURE 2 Standardised major axis regressions of the natural log of (a) caudal peduncle length
(cpl), and (b) postorbital length (pol) against the natural log of standard length (LS) for: ●,
Thysochromis emili sp. nov.; ▲, T. ansorgii; ♦, T. arnoldi; ■, T. annectens. █, Area of 95% CI
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FIGURE 3 Matrix of cytochrome oxidase subunit I gene (coI) distance between Thysochromis
emili sp. nov. and T. ansorgii from different locations. Inset images are of voucher specimens
photographed immediately post mortem
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FIGURE 4 (a) Lateral view of preserved male Thysochromis emili sp. nov. general habitus
(holotype, AMNH 271740) and (b) female (paratype, AMNH 271742). Scale bar = 1 cm
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FIGURE 5 Whole specimen and microCT scanned lateral views of neurocranium and
premaxilla, of (a) Thysochromis emili sp. nov. (AMNH 258135) and (b) Thysochromis ansorgii
(AMNH 235838). Scale bar = 3 mm
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FIGURE 6 Immediately post mortem coloration of Thysochromis emili sp. nov.. (a) male from
Lake Youbi and (b) female from Lake Yangala
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2
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FIGURE 7 Canonical correspondence analysis of the fish community data in relation to various
environmental attributes. ← and bold text, abiotic variables; ▼, position of Thysochromis emili
sp. nov.
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Accepted Article
TABLE 1 Morphometric measurements and meristic data for the holotype and 18 paratypes of
Thysochromis emili sp. nov.
Morphometric measurements
Standard length (LS; mm)
% LS
Head length (LH)
Body depth
Caudal-peduncle length
Caudal-peduncle depth
Dorsal-fin base
Anal-fin base
Predorsal length
Pre-anal length
Prepectoral length
Prepelvic length
Longest dorsal-fin ray
Longest anal-fin ray
Longest pectoral-fin ray
Longest pelvic-fin ray
% LH
Head depth
Snout length
Eye diameter
Postorbital length
Interorbital distance
Cheek depth
Premaxillary length
Lower jaw length
Preorbital length
Meristic counts
Lateral line scales (upper row)
Lateral line scales (lower row)
Lateral line scales (total)
Circumpeduncular scales
Dorsal-fin spine
Dorsal-fin rays
Anal-fin spine
Anal-fin rays
Pectoral-fin rays
Gill rakers (lower limb)
Holotype
69.4
Paratypes
min max
36.0 69.4
n mean SD
18
35.9
38.4
10.9
15.8
61.7
21.2
30.1
69.0
37.0
40.7
19.4
23.2
23.1
35.7
34.2
38.4
7.7
15.6
58.0
18.6
29.7
69.0
36.7
40.7
15.6
15.6
22.6
29.7
38.9
47.8
11.3
18.5
62.7
21.3
34.3
75.8
41.0
47.0
26.6
23.8
26.3
37.8
18
18
18
18
18
18
18
18
18
18
18
18
18
18
36.8
43.4
9.9
17.4
60.4
19.4
31.9
73.6
38.8
43.6
19.2
24.4
24.2
31.5
1.4
2.4
1
1
1.4
0.8
1.5
1.8
1.2
1.7
1.8
2.2
2.1
2
69.4
31.0
31.0
40.0
27.6
28.5
28.2
33.9
19.2
Holotype
65
76.8
28.8 34.6
27.0 30.1
38.2 41.9
25.4 33.2
26.2 31.2
23.1 28.2
30.2 38.1
17.2 24
Paratypes
18
18
18
18
18
18
18
18
18
68.7
31.2
28.6
40.2
29.1
29.4
26.1
32.3
20.3
3.2
1.6
1.1
1.1
2.3
1.8
1.9
2.2
1.7
19
7
28
16
XVI
10
III
9
13
9
17(2), 18(2), 19(9), 20(1)
6(1), 7(9), 8(2), 9(1)
26(2), 27(10), 28(2)
15(1), 16(13)
XV(6), XVI(7), XVII(1)
9(2), 10(10), 11(3)
III(14)
7(1), 8(12), 9(1)
13(14)
8(2), 9(8), 10(4)
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Accepted Article
Total gill rakers
Abdominal vertebrae
Caudal vertebrae
Total vertebrae
14
13
13
26
14(3), 15(8), 16(2), 17(1)
13(14)
11(1), 12(110), 13(3)
24(1), 25(9), 26(4)
TABLE 2 Morphometric measurements and meristic data for the syntypes Thysochromis
ansorgii, T. annectens and T. arnoldi
T. ansorgii
BMNH
1901.1.28:9–12
Morphometric
measurements
Standard length (LS; mm)
% LS
Head length (LH)
Body depth
Caudal peduncle length
Caudal peduncle depth
Dorsal-fin base
Anal-fin base
Predorsal length
Preanal length
Prepectoral length
Prepelvic length
Longest dorsal fin-ray
Longest anal fin-ray
Longest pectoral fin-ray
Longest pelvic fin-ray
% LH
Head depth
Snout length
Eye diameter
Postorbital length
Interorbital width
min max
mean
40.7 67.5
Syntypes
T. annectens
BMNH
1913.7.15:8–9
min
max
63.6
52.8
mean
T. arnoldi
BMNH
1912.2.2:10–12
min
max
56.1
65.4
mean
31.7
43.1
11.4
16.8
60.5
18.6
26.5
69
33.8
37.9
17.8
22.1
22.9
29.4
33.3
46.0
12.7
17.4
64.5
20.1
29.3
72.1
38.2
40.7
25.9
23.8
39.1
33.3
33.1
44.1
12.3
17.2
62.0
18.9
28.7
69.4
35.9
40.2
21.1
22.7
29.7
31.4
35.1
38.2
11.6
16.1
60.2
19.4
30.7
69.4
36.8
42.4
23.1
24.4
27.0
38.8
37.7
37.1
13.8
17.5
60.1
19.2
31.6
68.2
38
42.4
18.6
20.2
25.6
26.7
36.4
37.7
12.7
16.8
60.2
19.3
31.2
68.8
37.4
42.4
20.9
22.3
26.3
32.8
34.0
35.8
12.5
16.1
58.4
19.9
26.2
65.4
34.6
38.5
26.1
31.4
24.6
25.0
35.6
39.9
13.3
17.5
63.9
21.3
31.0
68.6
38.3
40.6
26.6
28.4
30.7
44.5
34.9
37.9
12.8
15.5
60.9
20.5
28.7
66.8
35.9
39.5
24.1
29.8
27.7
33.3
63.1
24.2
25.8
42.8
28.5
71.6
30.6
33.0
46.7
32.6
64.0
27.1
29.5
43.5
30.7
60.9
26.5
27.4
43.5
27.6
65.0
29.2
29.3
44.2
29.4
63.0
27.9
28.4
43.9
28.5
70.7
25.4
24.5
41.3
27.1
78.7
30.1
28.9
47.2
30.1
75.5
28.5
27.0
44.6
28.8
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Cheek depth
Premaxillary length
Lower jaw length
Preorbital length
Meristic counts
31.0
25.3
28.5
18.4
33.2
29.2
34.1
19.6
31.8
27.0
30.7
18.9
Lateral line scales (upper row)
Lateral line scales (lower row)
18(1), 19(2)
6(1), 7(3)
26(1), 27(1), 28
Lateral line scales (total)
(1)
Circumpeduncular scales
16(4)
Dorsal-fin spines
XV(2), XVI(2)
Dorsal-fin rays
10(3), 11(1)
Anal-fin spines
III(4)
Anal-fin rays
7(1), 8(3)
Pectoral-fin rays
12 (2), 13(2)
Gill rakers (lower limb)
9(3), 10(1)
Total gill rakers
13(3), 14(1)
BMNH, British Museum (Natural History)
27.7
27.2
29.9
16.9
30.0
29.2
31.3
17.2
28.6
28.2
30.6
17.1
25.7
28.9
33.1
17.0
33.8
33.4
34.4
18.8
31.0
30.8
33.8
17.8
18(1), 19(1)
7(1), 8(1)
19(3)
7(2), 8(1)
26(1), 27(1)
27(1), 28(2)
16(2)
XV(2)
9(1), 10(1)
III(2)
7(1), 8(1)
13(2)
10(2)
15(1), 16(1)
16(3)
XV(1), XVI(2)
9(1), 10(2)
III(3)
8(1), 9(2)
13(3)
9(3)
12(1), 13(2)
TABLE 3 Taxa, voucher catalog numbers and GenBank accession numbers for coI sequences
obtained in this study
Taxon
AMNH catalogue
Tissue
code
GenBa
nk
Locality
Thysochromis emili
sp. nov.
AMNH 258106
AMCC
211381
MN160
147
Lake Youbi, Republic of
Congo
Thysochromis emili
sp. nov.
AMNH 258135
AMCC
211386
MN160
148
Lake Yangala, Republic
of Congo
Thysochromis
ansorgii
ZCUV 2018/003
NIG-001
MN160
149
Niger River, Nigeria
Thysochromis
ansorgii
Uncatalogued photo
voucher
NIG-002
MN160
150
Niger River, Nigeria
AMNH, American Museum of Natural History
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Figure 1
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Figure 2A
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Figure 2B
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