Research Article |
Corresponding author: Boris Dodji Kasseney ( borisdodji@gmail.com ) Academic editor: James S. Pryke
© 2021 Toblie Quashie Effowe, Boris Dodji Kasseney, Abdoulaye Baïla Ndiaye, Bassan Banibea Sanbena, Komina Amevoin, Isabelle Adolé Glitho.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Effowe TQ, Kasseney BD, Ndiaye AB, Sanbena BB, Amevoin K, Glitho IA (2021) Termites’ diversity in a protected park of the northern Sudanian savanna of Togo (West Africa). Nature Conservation 43: 79-91. https://doi.org/10.3897/natureconservation.43.59474
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Termites occur in many ecosystems throughout tropical and subtropical areas. Their distribution is driven by several factors, including landscape and some soil characteristics. This study aims to determine soil organic matter’s role on termites’ diversity in a shrubby savanna park. Termites were sampled across transects in 3 sites of Galangashi park (northern part of Togo). The soil in which termites were harvested was analyzed to check organic matter’s influence on termites’ species richness. A total of 28 termite species belonging to 14 genera and 6 subfamilies were identified. Feeding group II (all fungus-growing termites, grass feeders, and wood feeders) was the most important among the three identified groups. Nine species (with two potentially new species for sciences: Amitermes sp and Eremotermes sp) were recorded for the first time in the country. A strong correlation was found between species richness, total organic matter, and total organic carbon, suggesting the influence of soil richness on termite distribution. The occurrence of the unique member of the feeding group I, Coptotermes intermedius Silvestri, 1912, as well as the occurrence of Fulleritermes tenebricus Silvestri, 1914 (both wood-dwelling termites), was certainly due to the vegetation. The relatively higher species richness as well as the correlation between the species richness and the organic matter of shrub savanna, suggest a better conservation of this landscape.
Organic carbon, shrub savanna, species richness, systematic
Termites are ecosystem engineers (
In comparison to these primary forests, agro-systems hosted fewer species because termites are very sensitive to any disturbance of their environment and are thus used as bioindicators (
Several authors (
This study was carried out at Galangashie protected park located in the savanna region (Fig.
Termites were sampled within the frame of belt transects. Three sets of three belt transects were laid at three sites: site 1 (10°26'42.6"–10°26'43.4"N; 000°23'52.4"–000°26'56.9"E) site 2 (10°27'30.8"–10°27'31.9"N; 000°23'39.5"–000°23'42.0"E) and site 3 (10°28'11.2"–10°28'10.8"N; 000°23'16.4"–000°23'16.6"E). The sets of three transects were at a distance of at least 2 km from each other, and two consecutive transects were separated by at least 15 m (Fig.
Termite specimens were sorted and grouped into morpho-species. The identification was based on morphological characters (antenna, mandible, head, labrum, pronotum, gula) and morphometric parameters (head length and width, mandible length, pronotum width, gula width, and hind tibia length). Measurements were made using a stereomicroscope (Leica EZ4) with an integrated camera connected to a computer. Las EZ software application was used for image acquisition and mensuration. The reference works of
The voucher specimens are conserved in the entomological collection of “Laboratoire d’Entomologie Appliquée” of the University of Lomé (Togo).
The obtained species list of this study was compared to previous studies (
The identified species were classified within their corresponding feeding groups, according to
Soil samples were collected in transects in which termites were harvested. An amount of 500 g of soil was taken from each sampling site and kept in plastic bags. They were brought to the Laboratory of Chemistry of the University of Lomé for chemical analysis. Five grams of each soil sample (previously dried at 220 °C) were burned at 450 °C for 3 hours. After cooling, the percentage of mass loss generated by the calcinations constitutes the soil samples’ total organic material content. The total organic carbon content was derived from the total organic matter. It was estimated to be 58% of the content of the total organic material.
For analysis smoothness, each set of three transects was considered as a replica. Data from each set of three transects were then pooled, and three replicates were obtained. We used the occurrence (presence or absence) and the relative abundance (the percentage of the occurrence of each single species in a sampling site) of specimen instead of a number of collected individuals because the occurrence of a single individual indicates the presence of a whole colony of termites around.
Alpha diversity indices, including the total observed richness (Sobs), Simpson index of diversity (1-D), and Shannon index, were calculated using Past 3.2 software (
The test of Kendalls τ was run to examine the correlation between species richness, total organic material, and total organic carbon of the soils from each set of three transects. Because there were three sets of three transects, the sample size was 3: each set of three transects was combined to get one sample size. This test was carried out in SPPS 20 at the level of 0.01. The coefficient of Kendalls τ test ranges from -1 (a strong negative correlation) to +1 (a strong positive correlation) with 0 value indicating no link between the examined factors.
A total of 28 species belonging to 14 genera and 6 subfamilies were identified (Table
List of termites’ species collected, feeding group and habits, and relative abundance (RA).
Feeding group | Feeding habit | Subfamilies | Termites species | RA (%) |
---|---|---|---|---|
Group IV | S | Apicotermitinae | Adaiphrotermes sp. | 2.91 |
Aderitotermes sp. | 2.66 | |||
Group I | W | Coptotermitinae | Coptotermes intermedius Silvestri, 1912 | 0.48 |
Group IV | S | Cubitermitinae | Cubitermes sp.* | 0.24 |
Noditermes cristifrons* Wasmann, 1911 | 0.73 | |||
Noditermes sp. | 0.24 | |||
Group II | W/L (F) | Macrotermitinae | Ancistrotermes cavithorax Sjöstedt, 1899 | 0.73 |
Ancistrotermes crucifer Sjöstedt, 1897 | 0.24 | |||
Macrotermes bellicosus Smeathman, 1781 | 1.21 | |||
Microtermes grassei Ghidini, 1955 | 25.42 | |||
Microtermes hollandei* Grassé, 1937 | 1.69 | |||
Microtermes Lepidus Sjöstedt, 1924 | 3.15 | |||
Microtermes toumodiensis* Grassé, 1937 | 11.62 | |||
Odontotermes erraticus Grassé, 1947 | 0.73 | |||
Odontotermes sp. | 0.48 | |||
Group II | W | Termitinae | Amitermes evuncifer Silvestri, 1912 | 3.15 |
Amitermes guineensis Sands, 1992 | 0.97 | |||
Amitermes sp.* | 0.48 | |||
Amitermes spinifer* Silvestri, 1914 | 0.24 | |||
Amitermes truncatidens* Sands, 1959 | 1.21 | |||
Group IV | S | Eremotermes sp.* | 2.91 | |
Group II | W | Microcerotermes parvulus Sjöstedt, 1911 | 5.33 | |
Microcerotermes solidus* Silvestri, 1912 | 4.12 | |||
Microcerotermes sp. | 6.78 | |||
Group II | W | Nasutitermitinae | Fulleritermes tenebricus Silvestri, 1914 | 5.33 |
Trinervitermes occidentalis Sjöstedt, 1904 | 4.84 | |||
Trinervitermes oeconomus Trägårdh, 1904 | 11.62 | |||
Trinervitermes togoensis Sjöstedt, 1899 | 0.48 |
Microtermes grassei Ghidini, 1955 was the most sampled species with 25.42% of occurrence (Table
Among the sampled specimens, 9 species to our knowledge were identified for the first time in Togo (showed in Table
The sampled termite species (from both landscapes) belong to 3 out of 4 feeding groups: feeding group I (FG I), feeding group II (FG II), and feeding group IV (FG IV) (Table
The Simpson index (1-D) for sampled termites was 0.89 (Suppl. material
The total organic material of soil was positively correlated with the species richness found in this landscape (Fig.
The distribution of termites (like many other terrestrial arthropods) is driven by several factors, including soil richness (
The high percentage of Macrotermitinae species occurrences is certainly due to their feeding habit and, therefore, to their feeding group. Indeed, these species could feed on diverse sources of celluloses from dry herbs to dry wood as well as dry leaves, twigs, litter, and even animal dung (
Coptotermes intermedius, feed essentially on wood (dry or still alive). The presence of many kinds of wood has facilitated its occurrence in the shrub savanna. Indeed, wood feeders were reported to be very sensitive to disturbance and therefore were less abundant in habitats with few and small trees (
Microtermes grassei was the most sampled species indicating its ubiquitous state and its ability to dwell on large food sources. This species was also sampled in the forest ecosystem (
A positive correlation was found between termite species richness and soil organic matter. Indeed, this landscape, as mentioned above, was a protected area since its creation. Fallen leaves, dry twigs, and branches from sampled trees are food for many termite species that recycle these plant parts (
The occurrences of newly recorded species underlined the importance and the contribution of this study to the knowledge of termite species in the country, in keeping with previous studies (
It is the first recent study carried out on termites in the area mentioned above. The study area was quite well diversified. Twenty-eight (28) termite species were identified from the three sets of three transects. Macrotermitinae was the most important subfamily and Microtermes grassei was the most sampled species among them all. This study was a modest contribution to the list of termites in Togo as 9 new species (among the 28 identified) were added to the list of termites’ species that occur in the country. Two of these newly recorded species (Amitermes sp and Eremotermes sp) seemed to have been hitherto undescribed to the best of our knowledge. Termites’ species richness was correlated with soil organic matter.
The authors are grateful to Danpanpkergou and Mango’s local villagers for their assistance and help in the field sampling. We also thank the authorities of the “Direction regional de l’Environnement de la Region des Savannes” for the logistics and other facilities. This study was part of a project financed by UEMOA (Union Economique et Monétaire Ouest Africaine).
Tables S1, S2
Data type: diversity data
Explanation note: Table S1. Termites diversity index in the two habitats. Table S2. Correlation with Kendall τ test.