# Bioecology of Orthopterans (Orthoptera, Insecta) in the biological reserve of Djebel Ouahch, Beni Hamidene and Grarem Gouga (Eastern Algeria)

Chahinez Derrouiche*<sup>(1)</sup>, Naima Benkenana <sup>(1)</sup>, Abir Abed <sup>(1)</sup>, Imen Guerfi <sup>(1)</sup>

*Corresponding author : Chahinez Derrouiche Email : chahinez.derrouiche@umc.edu.dz,

Une étude bioécologique sur le peuplement des orthoptères a été effectuée au niveau de trois stations dans l'est Algérien (Djebel Ouahch, Beni Hamidene et Grarem Gouga) entre Février et Juillet 2019. Les investigations ont révélé la présence de 25 espèces appartenant à cinq familles (Pamphagidae, Acrididae, Tetrigidae, Tettigoniidae et Gryllidae) dont la famille Acrididae s'est montrée quantitativement la plus abondante avec 18 espèces.

L'étude de la diversité et de la structure du peuplement d'orthoptères montre que la région d'étude est diversifiée et la majorité des espèces sont accidentelles. L'espèce *Pamphagus milevitanus* (Benkenana & Massa, 2017), récemment découverte en Algérie, a été recensée au niveau de la station de Grarem Gouga. L'étude des oothèques des femelles de cette espèce géante indique qu'elle a une forte fécondité. L'influence des variables météorologiques sur l'abondance des orthoptères révèle le rôle important de la température sur le développement de la plupart des espèces acridiennes, notamment l'espèce *Pamphagus milevitanus*.

**Mots clés** : Diversité, Acrididae, *Pamphagus milevitanus*, Fécondité, Abondance, Température.

This article presents a bioecological study on the orthoptera population at three stations in eastern Algeria (Djebel Ouahch, Beni Hamidene and Grarem Gouga) from February to July 2019. The investigation results indicate 25 species belonging to five families (Pamphagidae, Acrididae, Tetrigidae, Tettigoniidae and Gryllidae), of which the family Acrididae was quantitatively the most abundant with 18 species. The study of the diversity and structure of the orthopteran population shows that the study area is diverse, and the majority of species are accidental. The species *Pamphagus milevitanus* (Benkenana & Massa, 2017), recently discovered from Algeria, was recorded at the station Grarem Gouga. The study of oothecae of females of this giant species indicates that it has a high fecundity. The influence of meteorological variables on orthopteran abundance reveals the important role of temperature on the development of most locust species, including *Pamphagus milevitanus*.

**Keywords:** Diversity, Acrididae, *Pamphagus milevitanus*, Fecundity, Abundance, Temperature.

## INTRODUCTION

The Djebel Ouahch reserve is a natural heritage, the lung of Constantine. This massif is part of a series of small chains known as Numidian or Constantine (Boudy, 1955). It is a forest that abounds with 43 ornamental and noble forest species of Algerian, European and American origin (Hachiche, 2014), including *Quercus ilex* L., 1753 and *Pinus halepensis* Mill., 1768. It has a high diversity of forest vegetation and habitats, suggesting an equal variety of orthopterans. However, there is no in-depth faunistic study in this region, hence our interest in this topic which aims to shed some light on the orthopteran fauna in the Djebel Ouahch region. The orthopteran fauna occupies an important place in the ecosystems. They are economically significant and constitute a food resource for many vertebrates and invertebrates (Joern et al., 2006; Gandar, 1982). They are recyclers of plant material, using the remains of dead plants at one stage or another of their life cycle (Belovsky & Slade, 2002). They are

<footnote><sup>(1)</sup>Laboratoire de Biosystématique et Ecologie des Arthropodes, Université Frères Mentouri Constantine 1, 25000 Constantine, Algeria.</footnote>
also of ecological interest, representing good indicators of imbalances and climate change (Samways & Sergeev, 1997).

Orthopterans are important crop pests in different parts of the world, causing economic losses and threatening the food security of the population (Wright, 1986; Brader *et al.*, 2006; Millist & Abdalla, 2011; Latchininsky, 2013). Climatic conditions favour their proliferation (Benkenana, 2006). This work presents the list of orthopteran species recorded and some environmental factors influencing their development in Djebel Ouahch and in two others localities (Beni Hamidene in Constantine and Grarem Gouga in Mila).

# MATERIALS AND METHODS

## The geographical setting of the study area

The Djebel Ouahch region is located in the east of Constantine city (36°27′59″N, 6°44′13″E and altitude 994 m). It covers an area of 66.535 ha concerns seven communes, namely: Zighoud Youcef, Didouche Mourad, Constantine, El Khroub, Ibn Badis, Aïn Abid and Ouled Rahmoune. These communes are part of the Wilaya of Constantine. The ecological analyses were carried out on three localities, including Beni Hamidene located in the north-west of Constantine (36°30′20″N, 6°32′59″E, altitude 540m) and Grarem Gouga situated in the north of the Wilaya of Mila (36°30′26″N, 6°21′32″E, altitude 770 m) (Figure 1).

The climatic data used for the study period were collected from the national meteorological office completed by the database of the website (https://www.infoclimat.fr/climatologie/) (Table 1).

<figure><img src="image_1.png" /><figcaption>**Figure 1:** Presentation of the study locations</figcaption></figure>
<table><caption>**Table 1:** Climatic data in the geographical zone of the study area</caption><thead><tr><th></th><th>February</th><th>March</th><th>April</th><th>May</th><th>June</th><th>July</th></tr></thead><tbody><tr><td>Tmax (°C)</td><td>12,7</td><td>16,6</td><td>20,1</td><td>22,5</td><td>35</td><td>36,8</td></tr><tr><td>Tmin (°C)</td><td>1,6</td><td>3,7</td><td>6,9</td><td>8,5</td><td>16,3</td><td>19,1</td></tr><tr><td>Tm(°C)</td><td>7,5</td><td>10,5</td><td>13,5</td><td>15,6</td><td>25,7</td><td>28</td></tr><tr><td>P (mm)</td><td>47,6</td><td>50,4</td><td>38,2</td><td>60,4</td><td>0,2</td><td>0,2</td></tr><tr><td>W (m/s)</td><td>13.7</td><td>13.3</td><td>12.9</td><td>11.6</td><td>11.0</td><td>11.1</td></tr></tbody></table>

**Tmax:** maximum temperature, **Tmin:** minimum temperature, **Tm:** mean temperature, **P:** precipitations, **W:** wind

### Sampling and identification

The study was conducted from February to July 2019, with trips completed four times a month. Grasshoppers were captured by two sampling methods: by hand or using a sweep net for flying species. sampling took place during the day (10:00 to 17:00) under favourable weather conditions.

Specimens were placed in labelled bottles. They were pinned and pricked on polystyrene blocks. Systematic analysis of species was carried out using several identification keys; Chopard (1943), Jago (1963), Launois (1979), Massa *et al.* (2012). We used two sites ([http://orthoptera.speciesfile.org](http://orthoptera.speciesfile.org) and [https://acrinwafrica.mnhn.fr](https://acrinwafrica.mnhn.fr)) for updating the classification and nomenclature.

### Methods of analysis and data processing

The structure and diversity of orthopteran populations in the study area were assessed using ecological and statistical descriptors: frequency of occurrence, Shannon index, habitat amplitude and Pearson correlation coefficient. The analyses were performed using PAST v.1.81 on a matrix based on locust abundance (Hammer *et al.*, 2001).

### Frequency of occurrence and ecological status of inventoried species

According to Dajoz (1985), the frequency of occurrence of a species is the ratio, expressed as a percentage, between the number of samples in which this species is noted and the total number of samples collected. The formula proposed by Faurie *et al.* (2003) is defined as follows:

$$C (\%) = (P_i \times 100) / P$$

C : Constance;

Pi: Number of samples containing the species collected;

P: Total number of samples collected;

Ubiquitous species: C% = 100%;

Constant species: 75% ≤ C% < 100;

Regular species: 50% ≤ C < 75%;

Accessory species: 25% ≤ C < 50%;

Accidental species: C < 25.

### Habitat amplitude (HA) and ecological barycentre (G)

The specific distribution was examined using the habitat amplitude parameter (HA) for each species to reflect the amplitude of the spatial niche. According to Blondel (1979), this parameter has the following formula:

$$HA = e^{H'}$$

e: base of the Naperian logarithm;

H': -Σ Pi. Log2 (Pi) (Shannon and Weaver, 1949);

Pi: the proportion of individuals of the species in the environment i.

According to Blondel (1979), the barycentre measures the centre of gravity of the species' distribution along with a descriptor. It locates the average position of each species along a gradient (Ramade, 1984). It makes it possible to identify the ecological optimum of species statistically and with precision (Felzines, 1982). It depends closely on the a priori definition of the number of resource classes. The formula was defined by Lheritier *et al.* (1979) as follows:
$$g = (x1 + 2x2 + 3x3. .... nxn)/ \Sigma x$$

X1: centesimal frequency of species E in class 1 of the factor considered;

X2: centesimal frequency of species E in class 2 of the factor considered, etc.

Lheritier *et al.* (1979) reported that the habitat amplitude and the barycentre better understand how each species is distributed along the ecological succession.

## Study of morphometric traits and oviposition characteristics of *Pamphagus milevitanus* females

Measurements of the different body parts of the female *Pamphagus milevitanus* species were taken with a precision measuring magnifier and graph paper. The following parameters were measured: overall height, head size, thorax and abdomen, length and width of the hind femur. We investigated the oothecae of three females (number and size of eggs) to study fecundity and egg-laying capacity.

## RESULTS

### Composition of the orthopterological fauna

The orthopteran fauna recorded in the study area shows 25 species belonging to nine subfamilies and five families. The Acrididae was quantitatively the most abundant, being represented by 18 species (Table 2).

<table><caption>Table 2: Orthopteran species recorded in the three study sites</caption><thead><tr><th>Sub- orders</th><th>Families</th><th>Subfamilies</th><th>Species</th><th>S1</th><th>S2</th><th>S3</th></tr></thead><tbody><tr><td rowspan="20">Caelifera</td><td rowspan="3">Pamphagidae</td><td rowspan="3">Pamphaginae</td><td>Ocneridia volxemii (Bolivar, 1878)</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Pamphagus milevitanus (Benkenana and Massa, 2017)</td><td>-</td><td>-</td><td>+</td></tr><tr><td>Pamphagus cristatus (Descamps and Mounassif, 1972)</td><td>+</td><td>-</td><td>+</td></tr><tr><td rowspan="4">Acrididae</td><td rowspan="2">Calliptaminae</td><td>Pamphagus sp</td><td>+</td><td>+</td><td>-</td></tr><tr><td>Calliptamus barbarus barbarus (Costa, 1836)</td><td>+</td><td>-</td><td>+</td></tr><tr><td rowspan="2">Oedipodinae</td><td>Calliptamus sp</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Oedipoda caerulescens sulfurescens (Saussure, 1884)</td><td>+</td><td>+</td><td>+</td></tr><tr><td rowspan="3">Pamphagidae</td><td rowspan="3">Pamphaginae</td><td>Oedipoda fuscocincta fuscocincta (Lucas, 1849)</td><td>-</td><td>-</td><td>+</td></tr><tr><td>Oedipoda sp</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Acrotylus patruelis patruelis (Herrich-Schäffer, 1838)</td><td>+</td><td>+</td><td>+</td></tr><tr><td rowspan="5">Acrididae</td><td rowspan="2">Calliptaminae</td><td>Acrotylus insubricus (Scopoli, 1786)</td><td>+</td><td>+</td><td>-</td></tr><tr><td>Aiolopus thalassinus thalassinus (Fabricius, 1781)</td><td>+</td><td>+</td><td>+</td></tr><tr><td rowspan="2">Oedipodinae</td><td>Aiolopus strepens (Lautreuille, 1804)</td><td>-</td><td>+</td><td>+</td></tr><tr><td>Thalpomena algeriana algeriana (Lucas, 1849)</td><td>+</td><td>+</td><td>+</td></tr><tr><td rowspan="2">Pamphagidae</td><td rowspan="2">Pamphaginae</td><td>Anacridium aegyptium (Linnaeus, 1764)</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Anacridium sp</td><td>-</td><td>+</td><td>+</td></tr><tr><td rowspan="5">Ensilera</td><td rowspan="2">Calliptaminae</td><td>Pezotettiginae</td><td>Dociostaurus maroccanus (Thunberg, 1815)</td><td>+</td><td>-</td><td>+</td></tr><tr><td>Tetrigidae</td><td>Dociostaurus jagoi jagoi (Soltani, 1978)</td><td>+</td><td>-</td><td>-</td></tr><tr><td rowspan="2">Calliptaminae</td><td>Tetriginae</td><td>Omocestus lucassi (Brisout de Barneville, 1850)</td><td>+</td><td>-</td><td>+</td></tr><tr><td>Tettigoniidae</td><td>Omocestus africanus (Haraz, 1970)</td><td>-</td><td>+</td><td>-</td></tr><tr><td rowspan="3">Pamphagidae</td><td rowspan="3">Pamphaginae</td><td>Ochrilidia filicornis filicornis (Krauss, 1902)</td><td>+</td><td>-</td><td>-</td></tr><tr><td>Pezotettix giornae (Rossi, 1749)</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Praephippigera pachygaster (Lucas, 1849)</td><td>+</td><td>+</td><td>+</td></tr><tr><td>Gryllidae</td><td>Gryllinae</td><td>Gryllus sp</td><td>+</td><td>-</td><td>+</td></tr></tbody><tfoot><tr><td>Total</td><td>5</td><td>9</td><td>25</td><td>20</td><td>15</td><td>20</td></tr></tfoot></table>

S1: Djebel Ouahch, S2: Beni Hamidene, S3: Grarem Gouga
## Frequency of occurrence and ecological status of inventoried species

**Table 3** lists the frequencies of occurrence of orthopteran fauna. The environment of the Djebel Ouahch site has, out of a total of 20 species, 12 accidental species, five accessory species, two regular species and one constant species. At the Beni Hamidene site, out of 15 species, there are seven accidental species, four accessory species, three regular species and one constant species. At the Grarem Gouga site, out of 20 species, accidental species are predominant (14); there are also three accessory species, two regular species and one constant species.

<table><caption>**Table 3:** Assessment of the ecological status of orthopteran species in the study areas</caption><thead><tr><th rowspan="2">Species</th><th colspan="3">Jebel El Ouahch</th><th colspan="3">Beni Hamidene</th><th colspan="3">Grarem Gouga</th></tr><tr><th>ni</th><th>F%</th><th>C%</th><th>Econo mic stat.</th><th>ni</th><th>F%</th><th>C%</th><th>Econo mic stat.</th><th>ni</th><th>F%</th><th>C%</th><th>Stat. Eco</th></tr></thead><tbody><tr><td>Calliptamus b. barbarus</td><td>6</td><td>3,82</td><td>11,11</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>2</td><td>1,10</td><td>10</td><td>AC</td></tr><tr><td>Calliptamus sp</td><td>14</td><td>8,92</td><td>33,33</td><td>ACC</td><td>1</td><td>0,93</td><td>12,5</td><td>AC</td><td>3</td><td>1,66</td><td>10</td><td>AC</td></tr><tr><td>Oedipoda f. fuscocincta</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>17</td><td>9,39</td><td>20</td><td>AC</td></tr><tr><td>Oedipoda sp</td><td>8</td><td>5,10</td><td>11,11</td><td>AC</td><td>1</td><td>0,93</td><td>12,5</td><td>AC</td><td>20</td><td>11,05</td><td>40</td><td>ACC</td></tr><tr><td>Oedipoda caerulescens sulfurescens</td><td>2</td><td>1,27</td><td>11,11</td><td>AC</td><td>2</td><td>1,87</td><td>12,5</td><td>AC</td><td>11</td><td>6,08</td><td>50</td><td>R</td></tr><tr><td>Acrotylus insubricus</td><td>6</td><td>3,82</td><td>11,11</td><td>AC</td><td>4</td><td>3,74</td><td>25</td><td>ACC</td><td>0</td><td>0,00</td><td>0</td><td>/</td></tr><tr><td>Acrotylus patruelis patruelis</td><td>20</td><td>12,74</td><td>44,44</td><td>ACC</td><td>18</td><td>16,82</td><td>62,5</td><td>R</td><td>32</td><td>17,68</td><td>60</td><td>R</td></tr><tr><td>Aiolopus thalassinus thalassinus</td><td>1</td><td>0,64</td><td>11,11</td><td>AC</td><td>9</td><td>8,41</td><td>25</td><td>ACC</td><td>4</td><td>2,21</td><td>10</td><td>AC</td></tr><tr><td>Aiolopus strepens</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>5</td><td>4,67</td><td>37,5</td><td>ACC</td><td>10</td><td>5,52</td><td>30</td><td>ACC</td></tr><tr><td>Thalpomena algeriana</td><td>1</td><td>0,64</td><td>11,11</td><td>AC</td><td>6</td><td>5,61</td><td>37,5</td><td>ACC</td><td>3</td><td>1,66</td><td>10</td><td>AC</td></tr><tr><td>Anacridium aegyptium</td><td>2</td><td>1,27</td><td>11,11</td><td>AC</td><td>2</td><td>1,87</td><td>12,5</td><td>AC</td><td>4</td><td>2,21</td><td>20</td><td>AC</td></tr><tr><td>Anacridium sp</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>1</td><td>0,93</td><td>12,5</td><td>AC</td><td>1</td><td>0,55</td><td>10</td><td>AC</td></tr><tr><td>Dociostaurus maroccanus</td><td>9</td><td>5,73</td><td>55,56</td><td>R</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>1</td><td>0,55</td><td>10</td><td>AC</td></tr><tr><td>Dociostaurus jagoi jagoi</td><td>3</td><td>1,91</td><td>22,22</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>0</td><td>0,00</td><td>0</td><td>/</td></tr><tr><td>Omocestus africanus</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>1</td><td>0,93</td><td>12,5</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td></tr><tr><td>Omocestus lucassi</td><td>1</td><td>0,64</td><td>11,11</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>1</td><td>0,55</td><td>10</td><td>AC</td></tr><tr><td>Ochrilidia filicornis filicornis</td><td>3</td><td>1,91</td><td>33,33</td><td>ACC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>0</td><td>0,00</td><td>0</td><td>/</td></tr><tr><td>Pezotettix giornae</td><td>54</td><td>34,39</td><td>88,89</td><td>CO</td><td>1</td><td>0,93</td><td>12,5</td><td>AC</td><td>14</td><td>7,73</td><td>40</td><td>ACC</td></tr><tr><td>Ocneridia volxemii</td><td>4</td><td>2,55</td><td>44,44</td><td>ACC</td><td>45</td><td>42,06</td><td>75</td><td>CO</td><td>42</td><td>23,20</td><td>80</td><td>CO</td></tr><tr><td>Pamphagus milevitanus</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>4</td><td>2,21</td><td>10</td><td>AC</td></tr><tr><td>Pamphagus cristatus</td><td>8</td><td>5,10</td><td>55,56</td><td>R</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>2</td><td>1,10</td><td>20</td><td>AC</td></tr><tr><td>Pamphagus sp</td><td>3</td><td>1,91</td><td>22,22</td><td>AC</td><td>4</td><td>3,74</td><td>50</td><td>R</td><td>0</td><td>0,00</td><td>0</td><td>/</td></tr><tr><td>Paratettix meridionalis</td><td>10</td><td>6,37</td><td>33,33</td><td>ACC</td><td>7</td><td>6,54</td><td>50</td><td>R</td><td>4</td><td>2,21</td><td>20</td><td>AC</td></tr><tr><td>Praephippigera pachygaster</td><td>2</td><td>1,27</td><td>11,11</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>6</td><td>3,31</td><td>30</td><td>AC</td></tr><tr><td>Grillus sp</td><td>6</td><td>3,82</td><td>11,11</td><td>AC</td><td>0</td><td>0,00</td><td>0</td><td>/</td><td>2</td><td>1,10</td><td>10</td><td>AC</td></tr></tbody></table>

AC: Accidental, ACC: Accessory, R: Regular, Co: Constant, OMN: Omnipresent

## Habitat amplitude (HA) and ecological barycentre (G)

The results summarised in **Table 4** indicate that each environment has preferential species. Nevertheless, of the 25 species inventoried, almost half are found in the locality of Djebel Ouahch (g>2), followed by the locality of Beni Hamidene (g>1). These two environments attract almost all the species (23 species). Taking into account all the species (25) confirms these observations. Furthermore, **Table 4** shows that the species whose HA=1 are species restricted to the locality of Grarem Gouga. On the other hand, species with 1<HA≤2 are species whose spatial niche (ecological plasticity) encompasses two localities, Grarem Gouga and Beni Hamidene. On the other hand, species with 2<AH≤3 are species whose spatial niche (ecological plasticity) encompasses two localities: Beni Hamidene and Djebel Ouahch. It can be noted that the most significant habitat amplitude belongs to the species *Acrotylus patruelis patruelis*, with a value of 2.90.
<table><caption>**Table 4:** Distribution of Orthoptera species along the altitudinal gradient of the study areas</caption><thead><tr><th>Species</th><th>Code</th><th>ni</th><th>g</th><th>H'</th><th>HA</th></tr></thead><tbody><tr><td>Calliptamus barbarus barbarus</td><td>Calba</td><td>8</td><td>2,50</td><td>0,562</td><td>1,75</td></tr><tr><td>Calliptamus sp</td><td>Callsp</td><td>18</td><td>2,61</td><td>0,655</td><td>1,92</td></tr><tr><td>Oedipoda fuscocincta fuscocincta</td><td>Oefu</td><td>17</td><td>1,00</td><td>0,000</td><td>1,00</td></tr><tr><td>Oedipoda sp</td><td>Oesp</td><td>29</td><td>1,59</td><td>0,728</td><td>2,07</td></tr><tr><td>Oedipoda caerulescens sulfurescens</td><td>Oeca</td><td>15</td><td>1,40</td><td>0,765</td><td>2,15</td></tr><tr><td>Acrotylus insubricus</td><td>Acin</td><td>10</td><td>2,60</td><td>0,673</td><td>1,96</td></tr><tr><td>Acrotylus patruelis patruelis</td><td>Acpa</td><td>70</td><td>1,83</td><td>1,065</td><td>2,90</td></tr><tr><td>Aiolopus thalassinus thalassinus</td><td>Aisth</td><td>14</td><td>1,79</td><td>0,831</td><td>2,29</td></tr><tr><td>Aiolopus strepens</td><td>Aistr</td><td>15</td><td>1,33</td><td>0,637</td><td>1,89</td></tr><tr><td>Thalpomena algeriana algeriana</td><td>Thal</td><td>10</td><td>1,80</td><td>0,898</td><td>2,45</td></tr><tr><td>Anacridium aegyptium</td><td>Anae</td><td>8</td><td>1,75</td><td>1,040</td><td>2,83</td></tr><tr><td>Anacridium sp</td><td>Anms</td><td>2</td><td>1,50</td><td>0,693</td><td>2,00</td></tr><tr><td>Dociostaurus maroccanus</td><td>Doma</td><td>10</td><td>2,80</td><td>0,325</td><td>1,38</td></tr><tr><td>Dociostaurus jagoi jagoi</td><td>Doja</td><td>3</td><td>3,00</td><td>0,000</td><td>1,00</td></tr><tr><td>Omocestus africanus</td><td>Omaf</td><td>1</td><td>2,00</td><td>0,000</td><td>1,00</td></tr><tr><td>Omocestus lucassi</td><td>Omlu</td><td>2</td><td>2,00</td><td>0,693</td><td>2,00</td></tr><tr><td>Ochrilidia filicornis filicornis</td><td>Ocfi</td><td>3</td><td>3,00</td><td>0,000</td><td>1,00</td></tr><tr><td>Pezotettix giornae</td><td>Pegi</td><td>69</td><td>2,58</td><td>0,577</td><td>1,78</td></tr><tr><td>Ocneridia volxemii</td><td>Ocvo</td><td>91</td><td>1,58</td><td>0,842</td><td>2,32</td></tr><tr><td>Pamphagus milevitanus</td><td>Pamil</td><td>4</td><td>1,00</td><td>0,000</td><td>1,00</td></tr><tr><td>Pamphagus cristatus</td><td>Pasc</td><td>10</td><td>2,60</td><td>0,500</td><td>1,65</td></tr><tr><td>Pamphagus sp</td><td>Pasp</td><td>7</td><td>2,43</td><td>0,683</td><td>1,98</td></tr><tr><td>Paratettix meridionalis</td><td>Parma</td><td>21</td><td>2,29</td><td>1,035</td><td>2,82</td></tr><tr><td>Praephippigera pachygaster</td><td>Parrp</td><td>8</td><td>1,50</td><td>0,562</td><td>1,75</td></tr><tr><td>Grillus sp</td><td>Grisp</td><td>8</td><td>2,50</td><td>0,562</td><td>1,75</td></tr></tbody></table>

ni: number of individuals, g: ecological barycentre, H': Shannon's index, HA: Habitat amplitude

**Figure 2** indicates an almost complete turnover of the population between the second and third biotope. The lowest HA values are for *Pamphagus milevitanus* (*Pamil*) and *Oedipoda f. fuscocinta* (*Oefu*). While the highest values are for the species *Dociostaurus jagoi jagoi* (*Doja*) and *Ochrilidia filicornis filicornis* (*Ocfi*), which have the highest values, they characterise the locality of Djebel Ouahch.

<figure><img src="image_2.png" /><figcaption>**Figure 2:** Relationship between maximum abundance (g) and species dispersal (HA)</figcaption></figure>
## Study of morphometric traits and oviposition characteristics of *Pamphagus milevitanus* females

The coefficient of variation (CV) was calculated to express better the morphometric measurements of the female and her litter (oothecae) (Figure 3). A CV below 15% indicates the true values of the measurements. For each measurement, the CVs were checked at 15%. Measurements that exceeded the norms were processed by reducing the outliers (*). Table 5 shows the final measurements of the different morphometric traits and oviposition characteristics of *Pamphagus milevitanus* females.

<figure><img src="image_3.png" /><figcaption>Figure 3: Ootheca of the species *Pamphagus milevitanus* (x40)</figcaption></figure>

a: Oothecae, b: Egg, c: Size of eggs

<table><caption>Table 5: Morphometric analyses of female individuals of the species *Pamphagus milevitanus*</caption><thead><tr><th></th><th>Size general (cm)</th><th>Number eggs</th><th>The size eggs (cm)</th><th>weight of an egg (g)</th><th>Total weight of the Ootheca (g)</th><th>Head (cm)</th><th>Thorax (cm)</th><th>Abd (cm)</th><th>l. femur (cm)</th><th>L. femur (cm)</th></tr></thead><tbody><tr><td>1</td><td>8,8</td><td>236*</td><td>0,8</td><td>0,008</td><td>1,88</td><td>0,9</td><td>1,8</td><td>6,3</td><td>2,8</td><td>0,6</td></tr><tr><td>2</td><td>8,4</td><td>176</td><td>0,75</td><td>0,0075</td><td>1,32</td><td>0,8</td><td>1,8</td><td>6,1</td><td>2,6</td><td>0,6</td></tr><tr><td>3</td><td>7,6</td><td>109</td><td>0,69</td><td>0,0065</td><td>0,7*</td><td>0,6</td><td>1,6</td><td>5,9</td><td>2,9</td><td>0,6</td></tr><tr><td>Means.</td><td>8,267</td><td>173,667</td><td>0,747</td><td>0,007</td><td>1,300</td><td>0,767</td><td>1,733</td><td>6,100</td><td>2,767</td><td>0,600</td></tr><tr><td>SE</td><td>0,353</td><td>36,680</td><td>0,032</td><td>0,000</td><td>0,341</td><td>0,088</td><td>0,067</td><td>0,115</td><td>0,088</td><td>0,000</td></tr><tr><td>C.V. (&lt;15%)</td><td>0,043</td><td>0,211</td><td>0,043</td><td>0,060</td><td>0,262</td><td>0,115</td><td>0,038</td><td>0,019</td><td>0,032</td><td>0,000</td></tr><tr><td>Means.</td><td>8,267</td><td>142,5</td><td>0,747</td><td>0,007</td><td>1,600</td><td>0,767</td><td>1,733</td><td>6,100</td><td>2,767</td><td>0,600</td></tr><tr><td>SE</td><td>0,353</td><td>18,87</td><td>0,032</td><td>0,000</td><td>0,056</td><td>0,088</td><td>0,067</td><td>0,115</td><td>0,088</td><td>0,000</td></tr><tr><td>C.V. (&lt;15%)</td><td>0,043</td><td>0,1324</td><td>0,043</td><td>0,060</td><td>0,035</td><td>0,115</td><td>0,038</td><td>0,019</td><td>0,032</td><td>0,000</td></tr></tbody></table>

l: width, L: length, Abd: Abdomen

## Influence of environmental parameters on orthopteran settlement

The impact of the variation of certain climatic parameters on the availability of orthopterans was studied, including temperature, precipitation and wind. Furthermore, the relationship between orthopteran availability and climatic factors was verified by drawing a regression graph. The R² value indicates whether the climate variable explains the orthopteran abundance variable. The Pearson correlation
coefficient (r) calculation showed the influence of temperature, precipitation, and wind on orthopteran
abundance (Figure 4a-b-c). Figure 4a shows that higher temperature favours a higher abundance of the
whole orthopteran community, while Figure 4b shows that the precipitation factor negatively impacts
the abundance of orthopterans. Figure 4c shows that wind does not influence the abundance of the
orthopteran fauna.

<figure><img src="image_4.png" /><figcaption>**Figure 4:** Impact of some environmental parameters on orthopteran abundance</figcaption></figure>
DISCUSSION

This study shows that the study area is very diverse, with 25 species of orthopterans recorded belonging to five families and nine subfamilies. In general, the Acrididae shows clear dominance in terms of taxonomic richness. It is represented by 18 species divided into five subfamilies, which its adaptation can explain the environmental conditions of the area and the diversified vegetation. The subfamily Oedipodinae is the most widespread with eight species. These results are similar to those made by many researchers in Eastern Algeria, namely Benkenana (2006), Benkenana & Harrat (2009) and Benkenana et al. (2019), where the dominance of the family Acrididae is reported. Betina et al. (2017) reported 21 species in Batna, while Mahloul et al. (2016) inventoried 17 species in Oum El Bouaghi. The distribution of species between the three study sites indicates a high diversity in the two sites; Djebel Ouahch Park and Beni Hamidene. In contrast, the Grarem Gouga site has low diversity. This difference is linked to the environment and climatic conditions.

The study of the frequency of occurrence aims to define the structuring species of the procession. At the Djebel Ouahch station level, the study of the frequency of occurrence shows that the species: *Pezotettix giornae* is the most abundant, with a value of 34.39. This means that this species is less disadvantaged than the others by the ecological conditions of the station. It is a species that occurs during most of the year in dry places, grasses, and low bushes (Chopard, 1943). Overall, the species belonging to the family Acrididae dominate the park's population. This family is the most represented in all the work carried out in Algeria (Chopard, 1943; Ould El Hadj, 2004; Moussi et al., 2011). The regularity of the surveys allowed us to distinguish four groups of species: only one constant species; *Pezotettix giornae*, two regular species; *Dociostaurus maroccanus* and *Pamphagus cristatus*, five accessory species; *Calliptamus sp*, *Acrotylus patruelis patruelis*, *Ochrilidia filicornis filicornis*, *Ocneridia volxemii* and *Paratettix meridionalis*, and ten accidental species.

For the Beni Hamidene station, the study of the frequency of each species made it possible to point out that certain species have high frequencies compared to others. It follows that this station contains one constant species; *Ocneridia volxemii*, which is the most frequent species. According to Benkenana (2013), *Ocneridia volxemii* has been recorded in 24 stations in eastern Algeria, and has been found in the semi-arid, subhumid and humid bioclimatic stages, when the temperature is lower than 6°C. It also holds three regular species; *Acrotylus patruelis patruelis*, *Pamphagus sp* and *Paratettix meridionalis*, four accessory species and seven accidental species.

At the Grarem Gouga station, it appears that it contains only one constant species *Ocneridia volxemii*, two regular species; *Oedipoda caerulescens sulfurescens* and *Acrotylus patruelis patruelis*, three accessory species and 14 accidental species.

The habitat amplitude (HA) was used to estimate each species' spatial niche and thus see their distribution. The species *Acrotylus patruelis patruelis is the most observed orthopteran in the study area*. It is an essentially Mediterranean species (Bellmann & Luquet 1995). According to Defaut (1999), it is present throughout Africa. However, the species: *Pamphagus milevitanus*, *Ochrilidia filicornis filicornis*, *Omocestus africanus*, *Dociostaurus jagoi jagoi* and *Oedipoda fuscocincta fuscocincta* have a reduced spatial niche (HA=1), they are the most vulnerable, and this may be since they are influenced by the less favourable ecological conditions prevailing in the geographical area studied.

*Pamphagus milevitanus*, an endemic species of the family Pamphagidae, described by Benkenana & Massa in 2017. It was reported for the first time in north-eastern Algeria in Mila. The study of morphometric and oothecae analyses of females shows that this species is giant with high fecundity. The number of eggs per ootheca exceeds 173. According to Bounechada (2007), the species *Ocneridia volxemii* of the same family as *P. milevitanus*, the number per ootheca varies between 30 and 35. This difference may be related to size, as *Ocneridia volxemii* is small in size; the diet is also different. Bounechada (2007) found that environmental conditions, including the quantity and quality of food consumed, influence the number of eggs in the oothecae. According to Benkenana (2013), *Ocneridia volxemii* is graminivorous, feeding mainly on Poaceae. On the other hand, species of the genus *Pamphagus* have a preference for Fabaceae.
Climatic factors have a significant influence on the availability and distribution of orthopterofauna. According to Dusoulier (2002), orthopterans show a high sensitivity to environmental conditions. The Pearson correlation coefficient (r) calculation allowed us to deduce that the temperature variable positively affects orthopteran abundances (r = 6.09×10⁻⁴). This correlation indicates that the variable precipitation negatively influences Orthopteran abundance (r = -0.465). Wind speed's climatic variable does not seem to affect orthopteran availability (r-value is very low (r = -0.340). Temperature is a key factor for many orthopteran species (Bellmann & Luquet, 1995; Boitier, 2003).

## CONCLUSION

This study highlighted an important richness of orthopterans in the study area. The number of species recorded in the three stations surveyed indicates a considerable diversity (25 species). The results reveal a clear difference in biodiversity between the three study stations. The family Acrididae is the richest in terms of number of species and individuals in the three surveyed stations. *Pezotettix giornae* is a constant and very abundant species in the park of Djebel Ouahch. The species *Pamphagus milevitanus* shows a high fecundity. This giant species, prey to various predators (birds, reptiles, etc.), has established itself in several sites. The sampling procedure and the ecological and statistical analyses proposed in this article allow an estimate of the spatial distribution of species, the structure and diversity of orthopteran populations in the study area. It is recommended to extend and deepen the research in the entire Eastern Algeria region to complete the results.

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