Open access journal: http://periodicos.uefs.br/ojs/index.php/sociobiology ISSN: 0361-6525 DOI: 10.13102/sociobiology.v68i3.6232Sociobiology 68(3): e6232 (September, 2021) Introduction Ants are social insects of the family Formicidae in the order Hymenoptera. They account for 15% of the world’s animal biomass (Passera, 2016). More than 13,922 species are identified in the world (Bolton, 2021). They are widely distributed over different latitudes and biotopes: underground, on the soil surface, in the air, and on plants and animals. Throughout the ages, ants have been able to survive thanks to unique self-adapting and organizing mechanisms. As biological indicators of environmental quality, insects play Abstract The current study deals with the diversity of ants (Hymenoptera, Formicidae) in Kabylia of Djurdjura. It has been carried out in two forest sites from the localities of Azeffoun and Assi-Youcef, Tizi Ouzou (northern Algeria). Two sampling methods were adopted: manual capture and pitfall traps. Various community metrics were used as key elements to assess ant biodiversity within the two study sites. They included the species richness, the relative abundance, the constancy, and the Shannon-Weaver and equitability indices. Our inventory allowed identifying 24 species belonging to 12 genera and three subfamilies, which are the Myrmicinae (58%), the Formicinae (34%), and the Dolichoderinae (08%). The highest species richness was registered for the two first subfamilies, while the subfamily Dolichoderinae dominated numerically. The Site of Azeffoun, which is more submitted to human activities, recorded higher values in the number of individuals, the species richness, and the Shannon-Weaver diversity index. However, the difference between the two sites consisted mainly of the rare species, such as Crematogaster laestrygon, Goniomma sp. and Palagiolepis sp., which were present in the Azeffoun site. The local site conditions certainly have played a key role in ant species occurrence within the two study areas. Azeffoun is more disturbed than Assi-Youcef, resulting in the recruitment of much more rare and accidental species in the first site. In contrast, the rate of accessory to omnipresent species is substantially higher in Assi-Youcef, which recorded a high species evenness. To the best of our knowledge, this is the first study to report the ant genus Formica in Kabylia of Djurdjura. Sociobiology An international journal on social insects Sadou Sid-Ali1, Sadoudi Ali-hmed Djamila1, Metna Ali-Ahmed Fatiha1, Ourrad Ouiza1, Slimani Said2 Article History Edited by Evandro N. Silva, UEFS, Brazil Received 09 February 2021 Initial acceptance 27 June 2021 Final acceptance 23 July 2021 Publication date 13 September 2021 Keywords Formicidae, mediterranean, species richness, Taxonomy, Algeria. Corresponding author Sadou Sid-Ali Laboratoire Protection, Sauvegarde des Espèces Menacées et des Récoltes, influence des Variables Climatiques. Université Mouloud Mammeri de Tizi- Ouzou, Algérie. E-Mail: sidali.sadou@ummto.dz a key role in ecosystem functioning (Alonso, 2000). However, their identification remains complex, which constitutes a major problem for their use in environmental studies (New, 1996). Ants have attracted the attention of many researchers since the last century. The Formicidae have been documented in several studies all over the world, with a focus on their biology and ecology. From the 1970, many myrmecofauna inventories were carried out through project aimed at strengthening our understanding of biodiversity (Bernard, 1973, 1976; Passera, 1984; Jolivet, 1986; Longino & Colwell, 1997; Delabie et al., 1 - Laboratoire Protection, Sauvegarde des Espèces Menacées et des Récoltes, influence des Variables Climatiques. Université Mouloud Mammeri de Tizi-Ouzou, Algérie 2 - Laboratoire de Production, Amelioration et Protection des Végétaux et des Denerées Alimentaires. Université Mouloud Mammeri de Tizi-Ouzou, Algérie RESEARCH ARTICLE - ANTS Diversity of Ants (Hymenoptera, Formicidae) in Two Forest Sites from Kabylia of Djurdjura, Northern Algeria Sadou Sid-Ali, Sadoudi-Ali Ahmed Djamila, Metna-Ali-Ahmed Fatiha, Ourrad Ouiza, Slimani Said – Diversity of ants in two northern Algerian sites2 2000; Marinho et al., 2002; Vasconcelos et al., 2003; Hites et al., 2004; Lepounce et al., 2004; Lappola et al., 2006). The earliest studies on ants in North Africa were those of Emery (1914) in Tunisia, Dartigues (1988), Doumandji et Doumandji (1988), and Barech et al. (2016, 2018) in Algeria, and Cagniant (2005) and Taheri (2014) in Morocco. It is noteworthy that since the first publications dedicated to the order Hymenoptera in Algeria, few studies have been dedicated to the family Formicidae. Many authors reported that data on ants in Algeria in general and in the region of Tizi Ouzou, in particular, is scarce, old and fragmentary and that many sites remain unexplored and their fauna unknown (Bernard, 1982, 1983; Belkadi, 1990; Cagniant, 1997, 2005; Djioua & Sadoudi-Ali Ahmed, 2015). The current study reports the first findings on ants (Hymenoptera, Formicidae) diversity in two forest sites from Tizi Ouzou (Kabylia of Djurdjura, northern Algeria). These results provide relevant elements on the fauna in the study area and constitute vital information to support ongoing forest ecosystem management efforts in the region. Material and methods Study area The current study was carried out in two forest sites located at the extremities north and south of the wilaya of Tizi Ouzou (northern Algeria) (Fig 1). The two forested areas are situated some 50.5 km from one another. The site of Azeffoun is situated on the northern slope, while Assi-Youcef is situated on the southern slope of the Djurdjura mountain chain. The two study areas present important differences as regards their vegetation-soil-topography-climate association. The first site is located in the coastal zone of Azeffoun (northern Kabylia of Djurdjura), at about 56 km north-east to Tizi Ouzou, at the geographical coordinates 36° 53’ 35” N and 4° 25’ 12” E. The sampled area is situated over an altitudinal gradient ranging from 50 to 300 m. It is characterized by a maritime Mediterranean climate, wet and cool winter and a dry and warm summer. The total annual precipitation varies from 500 to 700 mm. The soil is derived from sandstone. This Mediterranean coastal site is close to the urban area of Azffoun, which makes it subjected to strong anthropic pressure, especially to grazing and forest fires. It consists of a reforested area of about 7,718 ha, dominated by a variety of introduced tree species of Eucalyptus (E. globulus, E. sideroxylon, E. gomphocephala, E. cladocalyx, E. botryoides, E. occidentalis, E. maideni) and Pinus (P. pinaster, P. pinea, P. canariensis). Furthermore, there is a notable presence of the native and spontaneous oak species Quercus suber. Main understorey vegetation consists of Pistacia lentiscus, Daphne gnidium, Erica arborea, Cistus monspenliensis, and Calycotome spinosa. The second site is located in a mountainous area belonging to the municipality of Assi-Youcef (southern Kabylia of Djurdjura), at about 50 km southwest to Tizi Ouzou, at the geographical coordinates 36° 27’ 54” N and 4° 05’ 47” E. Fig 1. Location of the study sites. Sociobiology 68(3): e6232 (September, 2021) 3 The sampled campaign was performed over an altitudinal gradient ranging from 600 to 950 m. It is characterized by a Mediterranean climate, wet and cold winter and dry and warm summer. The total annual precipitation exceeds 900 mm. The soil is derived from limestone. This site is situated within the National Park of Djurdjura. Intensive grazing and forest fires are observed, but anthropic activities are much lower than in the first site. This study area consists of a mixed Cedrus atlantica and Quercus ilex forest with a very low density of the understory, mainly represented by Juniperus oxycedrus, Calycotome spinosa, Erica arborea, Cytisus triflorus, Ampelodesma mauritanicum, and Asphodelus microcarpus. Sampling procedure Myrmecofauna sampling campaigns were carried out within the two study sites during the years 2018 and 2019. The samples were collected from March to July, every ten days, three times a month. Two sampling methods were applied in the current study: the Barber pots and the manual capture. pitfall traps The first adopted method consisted of using pitfall traps. This technique allows capturing many walking arthropods and flying insects, which land on the surface of the trap or are driven to it by the wind (Benkhelil, 1991). The traps are vertically buried, with the opening adjusted to the ground surface. To avoid any effect due to barriers towards the traps for tiny insects, the area around the placed Barber pots was cleaned. A total of ten traps were placed in each site along a sampled transect determined by a twine (a trap every five meters). The traps were filled to 1/3 of their height with water, and a detergent is added to facilitate entrapment of attracted insects. The traps’ content was collected after 48 hours and stored in plastic tubes with a data tag. Manual capture The manual capture method was performed from late April to late July, as described by Mc Gavin (2000). During this period of the year, the capture is easy, as ants are very active and occupy the superficial chambers of their nets. Species identification The collected ants were preserved in 75% ethyl alcohol. Their identification was performed using the taxonomic keys of Bernard (1968) and Cagniant (1968, 1970, 1997, 2005, 2006, 2009). Statistical analyses A variety of statistical parameters were used to describe the biodiversity of ants in our study areas. The species richness (S) represents the total number of ant species collected at each site. The relative abundance (RA) is the percent composition of a given ant species relative to the total number of individuals collected in a given site. The species constancy (C), or the frequency of occurrence, is the number of samples in which a given species is found relative to the total number of samples. Six constancy classes were considered: the species is rare if C ≤ 17%, accidental if 17% < C ≤ 34%, accessory if 34% < C ≤ 51%, regular is 51% < C ≤ 68%, constant if 68% < C ≤ 85% and omnipresent if C > 85%. The Shannon–Weaver diversity index (H’) was applied, using the following equation: H’ = -ΣPi log2 Pi where Pi = ni / N; ni being the total number of the species i and N is the total number of individuals. The equitability or evenness index (E) was estimated according to Pielou as follows: E = H’/Hmax where H’ is the Shannon–Weaver diversity index and Hmax = log2 S, S being the species richness. In addition, sampling effort is assessed using the nonparametric species richness estimators of Chao, jackknife 1, jackknife 2 and bootstrap, which calculate the number of cumulative observed and expected species in the study sites with 100 randomizations. Fig 2. Pitfall traps. Sadou Sid-Ali, Sadoudi-Ali Ahmed Djamila, Metna-Ali-Ahmed Fatiha, Ourrad Ouiza, Slimani Said – Diversity of ants in two northern Algerian sites4 Results Our sampling campaigns allowed collecting 641 ant individuals: 454 in Azeffoun and 187 in Assi-Youcef. Ant species richness (S) within the two study sites is reported in Table 1. A total of 24 species were identified. They belong to 12 genera and three subfamilies: Myrmicinae (58%), the Formicinae (34%) and the Dolichoderinae (8%). All 24 species were present in Azeffoun, while only 13 were found in Assi-Youcef. With seven genera and 13 species, the subfamily Myrmicinae was the most diversified. Each of the genera Crematogaster, Aphaenogaster, and Messor were represented by three species. Only one species represented the other genera (Tetramorium, Pheidole, Goniomma and Temmothorax). The subfamily Formicinae registered ten species belonging to four genera. The genera Cataglyphis and Formica were represented by one single species, the genus Plagiolepis recorded two species, and the Camponotus was the richest genus, with six species. The least diversified subfamily was the Dolichoderinae, which registered only one genus (Tapinoma) and one species (Tapinoma simrothi) (Fig 3). From a quantitative perspective, the ant relative abundance (RA) varied between the two sites according to the species rank (Fig 4 and 5). In Azeffoun, Tapinoma simorthi was the most abundant species (RA = 13.22%). It was followed by Pheidole pallidula (RA = 12.56%), and Cataglyphis viaticus, and Crematogaster sticularis (RA = 11.01% for both). The most abundant species in Assi-Youcef was Pheidole pallidula (RA = 22.32%). It was followed by Tapinoma simorthi, Palageolipis schmitzi, and Cataglyphis viactus, with RA values of 16.04%, 11.76%, and 10.70%, respectively. All six considered constancy classes were observed while considering the two study areas (Table 2). Table 1. Ant species richness in the two study sites. Site Subfamily Species Azeffoun Assi- Youcef Camponotus toracicus + + Camponotus spissinodis + - Camponotus ruber + - Camponotus latiralis + + Formicinae Camponotus alii + + Camponotus barbarous + + Cataglyphis viaticus + + Formica sp. + - Palagiolepis schmitzi + + Palagiolepis sp. + - Myrmicinae Crematogaster sticularis + + Crematogaster auberti + - Crematogaster laestrygon + - Aphaenogaster testaceopilosa + + Aphaenogaster senilis + + Aphaenogaster sardoa + - Messor barbarous + + Messor lobicornis + - Messor capitus + - Pheidole pallidula + + Goniomma sp. + - Temnothorax sp. + - Tetramorium bisekrens + + Dolichoderinae Tapinoma simorthi + + Species Azeffoun Assi-Youcef C Category C Category Camponotus toracicus 25.00 Ac 33.33 Ac Camponotus spissinodis 04.76 Ra 00.00 Absent Camponotus ruber 04.76 Ra 00.00 Absent Camponotus latiralis 06.66 Ra 06.66 Ra Camponotus alii 28.33 Ac 16.66 Ra Camponotus barbarous 08.33 Ra 13.33 Ra Cataglyphis viaticus 66.66 Reg 60.00 Reg Formica sp. 16.66 Ra 0.00 Absent Palagiolepis schmitzi 66.66 Reg 66.66 Reg Palagiolepis sp. 03.33 Ra 00.00 Absent Crematogaster sticularis 75.00 Con 40 Acc Crematogaster auberti 30.00 Ac 00.00 Absent Crematogaster laestrygon 01.66 Ra 00.00 Absent Aphaenogaster testaceopilosa 10.00 Ra 06.66 Ra Aphaenogaster senilis 75.00 Con 50.00 Acc Aphaenogaster sardoa 08.33 Ra 00.00 Absent Messor barbarous 58.33 Reg 50.00 Acc Messor lobicornis 05.00 Ra 00.00 Absent Messor capitus 06.66 Ra 00.00 Absent Pheidole pallidula 91.66 Omn 93.33 Omn Goniomma sp. 01.66 Ra 00.00 Absent Temnothorax sp. 05.00 Ra 00.00 Absent Tetramorium bisekrens 08.33 Ra 40.00 Acc. Tapinoma simorthi 93.33 Omn 93.33 Omn. Table 2. Constancy values (C) and their corresponding categories for the two study sites. Five constancy classes were identified in Azeffoun. Accessory species were absent. A total of 14 species were rare. The rarest ones were Goniomma sp. (C = 01.66%), Crematogaster laestrygon (C = 01.66%) and Palagiolepis sp. (C = 03.33%). Three species were accidental: Crematogaster auberti (C = 30.00%), Camponotus alii (C = 28.33%) and Camponotus toracicus (C = 25.00%). Likewise the regular ones were represented by three species, which were Palagiolepis schmitzi (C = 66.66%), Cataglyphis viaticus (C = 66.66%) and Messor barbarus (C = 58.33%). Two species Sociobiology 68(3): e6232 (September, 2021) 5 were constant: Crematogaster sticularis (C = 75.00%) and Aphaenogaster senilis (C = 75.00%). Two other species were omnipresent: Tapinoma simorthi (C = 93.33%) and Pheidole pallidula (C = 93.33%). Five constancy classes were also identified in Assi- Youcef. In this site, no ant species was identified as constant. Four species were considered rare: Camponotus alii (C = 16.66%), Camponotus barbarus (C = 13.33%), Camponotus latiralis (C = 06.66%) and Aphaenogaster testaceopilosa (C = 06.66%). The class accidental was represented by only one species, Camponotus toracicus (C = 33.33%). Four accessory species were recorded: Aphaenogaster senilis (C = 50.00%), Messor barbarus (C = 50.00%), Crematogaster sticularis (C = 40.00%) and Tetramorium bisekrens (C = 40.00%). Regular and omnipresent species were both represented by two species, which are Palagiolepis schmitzi (C = 66.66%) and Cataglyphis viaticus (C = 60.00%), and Pheidole pallidula (C = 93.33%) and Tapinoma simorthi (C = 93.33%) respectively. The majority of the species identified in Azeffoun were rare (58.33%). They are followed by the accidental and the regular and species (12.50% for each category), and the least represented were the omnipresent (08.33%). In Assi-Youcef, the most present species belonged to the categories rare and accessory (30.77% for each class). They are followed by the regular and omnipresent species (15.38% for each of the classes), and the accidental ones came last (07.69%). 4 7 1 10 11 1 F O R M I C I N AE M Y R M I C I N A E D O L I C H OD ER I N AE SUBFAMILLIE Number of genera Number of species Fig 3. Number of genera and species for each subfamily in the two study sites. sp 1 sp 2 sp 3 sp 4 sp 5 sp 6 sp 7 sp 8 sp 9 sp 10 sp 11 sp 12 sp 13 sp 14 sp 15 sp 16 sp 17 sp 18 sp 19 sp 20 sp 21 sp 22 sp 23 sp 24 0,1 1 10 100 0 5 10 15 20 25 30R el at iv e ab un da nc e Rank of species Fig 4. Rank-abundance curve for the relative abundance (Log10ni/N) of ant species collected in Azeffoun. sp 1 : Tapinoma simorthi; sp 2: Pheidole pallidula; sp 3: Cataglyphis viaticus; sp 4: Crematogaster sticularis; sp 5: Aphaenogaster senilis; sp 6: Palagiolepis schmitzi; sp 7: Messor barbarus; sp 8: Crematogaster auberti; sp 9: Camponotus alii; sp 10: Camponotus toracicus; sp 11: Formica sp; sp 12: Aphaenogaster testaceopilosa; sp 13: Camponotus barbarus; sp 14: Aphaenogaster sardoa; sp 15: Temnothorax sp; sp 16: Tetramorium bisekrens; sp 17: Camponotus latiralis; sp 18: Palagiolepis sp; sp 19: Messor capitus; sp 20: Messor lobicornis ; sp 21: Camponotus spissinodis ; sp 22: Camponotus ruber ; sp 23: Crematogaster laestrygon; sp 24: Goniomma sp. Sadou Sid-Ali, Sadoudi-Ali Ahmed Djamila, Metna-Ali-Ahmed Fatiha, Ourrad Ouiza, Slimani Said – Diversity of ants in two northern Algerian sites6 It is worth mentioning that the absent species in Assi- Youcef registered a low presence in Azeffoun: ten species out of 11 were rare, and one was accidental. Moreover, the rare species in Azeffoun were absent (ten species), rare (three species), or accessory (one species) in Assi-Youcef. On the contrary, the rare species in Assi-Youcef were rare (three species) or accessory (one species) in Azeffoun. In addition, the two sites registered the same omnipresent species, which are Tapinoma simorthi and Pheidole pallidula. However, we notice that the rates of the rare and the accidental species were lower and that of the omnipresent species was higher in Assi- Youcef than in Azeffoun. The results of the Shannon-Weaver (H’) and equitability (E) indices are presented in Table 3. H’ recorded a higher value in Azzefoun (2.61) than in Assi-Youcef (2.29). This also coincides with higher values in S and H’max. We notice that H’ is relatively close to H’max in Assi-Youcef, while in Azeffoun, the difference between the two parameters is huge. On the contrary, Assi-Youcef registered a slightly higher value in E. sp 1 sp 2 sp 3 sp 4 sp 5 sp 6 sp 7 sp 8 sp 9 sp 10 sp 11 sp 12 sp 13 0,1 1 10 100 0 2 4 6 8 10 12 14R el at iv e ab un da nc e Rank of spcies Fig 5. Rank-abundance curve for the relative abundance (Log10ni/N) of ant species collected in Assi-youcef. sp 1: Pheidole pallidula; sp 2: Tapinoma simorthi; sp 3: Palagiolepis schmitzi; sp 4: Cataglyphis viaticus; sp 5: Aphaenogaster senilis; sp 6: Messor barbarus; sp 7: Crematogaster sticularis; sp 8: Tetramorium bisekrens; sp 9: Camponotus toracicus; sp 10: Camponotus alii; sp 11: Camponotus barbarus; sp 12: Camponotus latiralis; sp 13: Aphaenogaster testaceopilosa. Parameter Site Azeffoun Assi-Youcef H’ 2.61 2.29 S 24 13 H’max 4.585 3.70 E 0.56 0.62 Table 3. Shannon-Weaver (H’) and equitability (E) indices for the two study sites. Sites Azeffoun Assi-Youcef Azeffoun Assi-Youcef Estimators Value Completen-ess Average completeness Completeness Average completeness Observed richness 24 13 Chao 44,63 ± 19.59 15,93 ± 3,63 53,77 % 67,09 % 81,60 % 81,60 % 81,90 % Jackknife 1 33,72 ± 4,07 15,93 ± 1,37 71,17 % Jackknife 2 40,36 16,90 59,46% 76,92 % Bootstrap 28.58 ± 2,06 14,86 ± 0,77 83,97 % 87,48 % Table 4. Estimation of the total richness of the ants. In Azeffoun, the estimated total species richness was higher than the observed value (Sobs. = 24). According to the different used estimators, the number of new species to be found in this site is 16 to 20 with the Chao 1 and jackknife 1 indices, 9 with the jackknife 2 index and four with the bootstrap index (Table 4). In contrast, in Assi-Youcef, the estimated values are close to the observed, with a minimal estimate of one to three more species to be found in this site: Sobs. = 13, Chao = 15.93 ± 3.63, jackkniefe 1 = 15.93 ± 1.37, jackknife 2 = 16.90 and bootstrap = 14.86 ± 0.77). In addition, the inventory completeness rate reached a value of 67.09% in Azeffoun and 81.90 in Assi-Youcef. Moreover, the inadequacy of the sampling effort within the two sites is confirmed by the difference between the species accumulation curves (Sobs.) and those obtained using the adopted estimators (Fig 6 and 7). Sociobiology 68(3): e6232 (September, 2021) 7 Sample Chao Jackknife1 Jackknife2 Bootstrap3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 size 10 15 20 25 30 35 40 45 50 sp ec ifi c ric hn es s Sample Chao Jackknife1 Jackknife2 Bootstrap 3 5 7 9 11 13 15 17 19 21 23 25 27 29 31 33 size 6 8 10 12 14 16 18 S pe ci fic r ic hn es s Fig 6.Curves of accumulation of the species, estimators of the richness in Azeffoun. Fig 7.Curves of accumulation of the species, estimators of the richness in Assi-Youcef. Sadou Sid-Ali, Sadoudi-Ali Ahmed Djamila, Metna-Ali-Ahmed Fatiha, Ourrad Ouiza, Slimani Said – Diversity of ants in two northern Algerian sites8 Discussion The current investigation on the myrmecological fauna allowed identifying 24 species in the two studied sites. They belong to three subfamilies, which are: the Myrmicinae, the Formicinae, and the Dolichoderinae. Our findings showed that the species richness was much higher in Azeffoun (24 species) than in Assi-Youcef (13 species). This difference may be due to the differences in ecological conditions within the two studied areas. The close relationship between ants and the type of habitats has been reported by Agosti et al. (2000). Indeed, the site of Azeffoun is coastal and is located on the northern slope of the Djurdjura mountain chain. On the contrary, Assi-Youcef is mountainous and is situated on the southern slope of the Djurdjura massif. Moreover, even if the two studied sites are forested areas, the site of Azeffoun is a reforested one. It is close to the urban area, so it is more or less artificial and submitted to high anthropogenic pressure (overgrazing, forest fires, illegal loggers), while the site of Assi-Youcef consists of a spontaneous forest located in a protected area, which is the Djurdjura National Park. These differences suggest that the site of Azeffoun is much more disturbed and open, which may play a key role in recruiting much more species than in Assi-Youcef. The soil type could also be a determining factor: in Azeffoun, the soil is siliceous, while in Assi- Youcef, it is calcareous. A larger-scale study, carried out by Djioua and Sadoudi Ali-Ahmed (2015) in the region of Tizi Ouzou, involving four different sites (Aghrib, Azazga, Ain El Hammam, and Tizi Ouzou), allowed identifying 15 species. This richness is close to the one we found for Assi-Youcef. This result confirms the particular influence of the ecological conditions that prevail in our site of Azeffoun, which recorded much higher species richness (24 species). The majority of the identified ant species in the two studied sites have already been reported by Cagniant (1968, 1969, 1972, and 1973) and Bouzekri et al. (2013) in their works on Algerian ant populations. However, to the best of our knowledge, the current study is the first to report the genus Formica in Kabylia of Djurdjura, occuring in the richest site, Azeffoun. For both sites, the most abundant species were Tapinoma simorthi and Pheidole pallidula. Similar results have been reported by Belkadi (1990), Djioua, and Sadoudi Ali-Ahmed (2015) in the region of Tizi Ouzou and Dehina (2009) in two stations in the Algiers region. Crematogaster scutellaris was also abundant. Many authors have reported this species in the Mediterranean forests; these results corroborate with those of Janine (1972). Our results are consistent with those reported by Cagniant (2005) in Morocco, who mentioned the genus Crematogaster as one of the most abundant among the Formicidae and corroborate those noted by Djioua & Sadoudi Ali-Ahmed (2015) in the region of Tizi Ouzou. The constancy index, reflecting the frequencies of occurrence, varies considerably among the identified ant species and confirms the difference mentioned between the two sites regarding their species richness. As mentioned above, the site of Azeffoun recorded a higher number of identified species. However, the difference between the two sites was mainly represented by the category of rare species. Consequently, more submitted to anthropogenic disturbances, the site of Azeffoun tends to recruit more non-characteristic species. In contrast, located in a protected area, Assi-Youcef showed a higher rate of omnipresent species, which are characteristic of the forest environment. The values reported in Table 2 were recorded from May to June. Similar results have been reported in Algeria by Bakiri (2001) in the suburban environment near Algiers and Dehina (2009), who also listed Tapinoma simrothi as an omnipresent species. However, different results have been reported concerning the omnipresent species, Pheidole pallidula. Hacini (1995) listed it among omnipresent species in Staouali (northern Algeria), while Djioua & Sadoudi-Ali Ahmed (2015) mentioned it as regular within four sites in the region of Tizi Ouzou. Table 3 revealed that the Shannon-Weaver and equitability indices were high in both sites. However, the most disturbed site (Azeffoun) recorded higher values of S, H’, and H’max. In contrast, the most stable one (Assi-Youcef) registered a higher value of E. In addition, this site showed close values of H’ and H’max, which suggests that many species have more or less the same abundance. On the contrary, the higher diversity in species of Azeffoun is characterized by a high range of abundances among species. Our findings stem from a sampling procedure associating manual capture and pitfall trap methods. Other authors adopted this combined technique to assess ant biodiversity in Algeria. Their results showed lower H’ values: Barech et al. (2016) noted values ranging from 1.35 bits in Medbah to 1.47 bits in Biskra. Barech et al. (2018) reported an H’ value of 1.10 bits at the edges of the dam of El Ksob (M’sila). This difference could be because our study areas are located in different climatic zones: our sites are situated in a humid area, facing the Mediterranean Sea, while the studies of Barech et al. (2016, 2018) were carried out within sub-arid and arid zones, which are characterized by lower fauna biodiversity compared to the northern part of the country. According to the estimated total specifies richness, the adopted sampling methods allowed capturing two thirds (67.09%) of the ant species that would be present in Azeffoun and over than three quarters (81.90%) of those expected to be found in Assi-Youcef. This justifies the differences exhibited between the accumulation curves of the captured and expected species within the two sites. The accumulation curve did not reach an asymptote for all samples. This suggests that the sampling effort is incomplete. Hence, additional samples would be required in order to capture new species. Sociobiology 68(3): e6232 (September, 2021) 9 Conclusion A total of 641 ant individuals were collected. They belong to 24 species, 12 genera and three subfamilies, which are: the Myrmicinae, the Formicinae and the Dolichoderinae. The local site conditions could have played a key role in ant species occurrence within the two study areas. The site of Azeffoun is more submitted to human activities than Assi- Youcef, which is located in a protected area, the Djurdjura National Park. This promoted recruitment of much more rare and accidental species in that disturbed site, while the rate of accessory to omnipresent species is substantially higher in Assi-Youcef. To the best of our knowledge, the current study is the first to identify the genus Formica in the region of Tizi Ouzou. Compared to other works realized on ants since years. Scientific research on this group of bio-indicator insects should be continued in order to better understand the biodiversity levels of these hotspots. Acknowledgements The authors acknowledge the Department of Biology and the PSEMRVC laboratory, Mouloud Mammeri University of Tizi-Ouzou, for valuable support. We also thank doctor Djaffer Dib, Slimani Said and Chafika Ali-Ahmed for their contribution. References Alonso, L.E. (2000). Ants as indicators of diversity. 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