Agricultural Science Digest

  • Chief EditorArvind kumar

  • Print ISSN 0253-150X

  • Online ISSN 0976-0547

  • NAAS Rating 5.52

  • SJR 0.156

Frequency :
Bi-monthly (February, April, June, August, October and December)
Indexing Services :
BIOSIS Preview, Biological Abstracts, Elsevier (Scopus and Embase), AGRICOLA, Google Scholar, CrossRef, CAB Abstracting Journals, Chemical Abstracts, Indian Science Abstracts, EBSCO Indexing Services, Index Copernicus

Barn Owls (Tyto alba Scopoli, 1769) in the Saharan Region of Algeria (Souf): Valuable Predators for Rodent Control in Agriculture

Zeid Alia1,2, El Amine Khechekhouche1,3, Djilani Ghemam Amara1,3, Mohammed Messaoudi1,3, Makhlouf Sekour 4
1Laboratory of Biology, Environment and Health, Department of Biology, Faculty of Life and Natural Sciences, University of El Oued, Algeria.
2Department of Agronomy, Faculty of Life and Natural Sciences, University of El Oued, Algeria.
3Department of Biology, Faculty of Life and Natural Sciences, University of El Oued, Algeria.
4Department of Agronomic Sciences, Faculty of Life and Nature Sciences, University of Kasdi Merbah, Ouargla.

Background: Barn Owls (Tyto alba Scopoli, 1769), which are nocturnal birds of prey, play a crucial role in controlling rodent populations that damage crops. They are valuable allies for farmers because they can effectively hunt small rodents. In Algeria, the Barn Owl is represented by two subspecies, Tyto alba alba and Tyto alba guttata

Methods: This study focuses on the Barn Owls' diet in the Saharan region, specifically in the Souf region, characterized by a dry climate. The research examines the contents of the Barn Owl's reject balls, which are regurgitated, to determine their diet. 

Result: The study reveals that each reject ball contains 1 to 9 prey items. The researchers identified 23 prey species, with rodents being the most abundant, making up 88.3% of the diet. The most commonly found prey species in Barn Owl balls are G. gerbillus, G. campestris, M. musculus, G. nanus and G. tarabuli. Overall, the Barn Owl's diet in the Saharan region is crucial for maintaining ecosystem balance by controlling rodent populations.

Nocturnal birds of prey are considered predators par excellence; This puts them at the top of the food chain pyramid (Ramade, 2012; Dulsat-Masvidal et al., 2021; Dhakal et al., 2023). Given the nature of the selected prey, including rats and mice, which cause damage to crops in open fields and grain storage places, they are considered valuable assistants to the farmer (Giban and Haltebourg, 1965; Viteri et al., 2022; Choudhary et al., 2020; Sobhana et al., 2022). These predators help limit the size of prey populations, even when the harvest may seem small (Ramade, 2012; Martínez-Ruiz et al., 2020; Montoya et al., 2021). Several studies have been carried out to clarify the diet of birds of prey around the world, including the Barn Owl in Spain (Delibes et al., 1984; Sridevi et al., 2020), Switzerland (Roulin, 1996), Italy (Natalini et al., 1997) and Morocco (Rihane, 2005). In Algeria, on the other hand, some works are carried out in different districts of Algeria (Baziz et al., 1999), in the suburbs of Algiers (Baziz et al., 1999), in the Mergueb Nature Reserve (Sekour, 2010; Sekour et al., 2010) and (Alia et al., 2012; Alia et al., 2015; Hadjoudj et al., 2020) about the Barn Owl.
       
The family Tytonidae is represented in Algeria by a single species that includes two subspecies Tyto alba alba (Scopoli, 1759) and Tyto alba guttata (Brehm, 1831) (Heim de Balsac and Mayaud 1962; Isenmann and Moali 2000). Also known as the Barn Owl or the White Lady, it is a nocturnal bird of prey that often feeds on small mammals (Bourlière 1984; Leonardi and Dell'Arte 2006). These are generally Muridae such as Mus musculus (Linnaeus 1758), Mus spretus (Lataste 1883) and Gerbillus gerbillus (Olivier 1801) (Boukhemza, 1989; Boukhamza et al., 1994). Furthermore, the trophic diet of this species is largely unknown in the Saharan regions, particularly in the Souf region. To compensate for this deficiency, this study was published to complement the North Saharan (Souf) rodent database and highlight the importance of rodents-prey items in the trophic diet of this predator. For these studies, we applied the analysis of Effraie balls to make the necessary observations for a possible study of this species in the Saharan region.
Area Study
 
The Souf region is located in southeast Algeria, roughly 600 kilometers from Algiers, the country’s capital. It is located in the Eastern Erg’s northern region (33° to 34° N; 6° to 8° E). The large Tunisian Chott El-Djérid is to the east and the Merouane, Melrhir and Rharsa Chotts are to the north. The Chott trail of Oued Righ and the Oued M’Ya forms the western and southern boundaries, respectively (Voisin 2004; Côte, 2006). Based on meteorological data from 1980 to 2022, this study area belongs to the Saharan bioclimatic stage and experiences moderate winters. The same facts point to a dry season all year long. Tyto alba ball samples were gathered in Elarfji, which is 25 kilometers northwest of El-Oued, in 2021. The Barn Owl repellent balls were gathered beneath the mosque’s (Soumaa) minaret in the community. 200 Phoenix dactylefera (L. 1753) variation palm trees and 300 Olea europaea (L. 1753) type olive trees are among the famous crops grown in Elarfji. The primary food source for L’Effraie, which hunts in open areas, is tiny rodents (Bourlière, 1974; Sekour, 2010). It differs from other nocturnal birds of prey by consuming insectivores, such as bats, frogs, and birds trapped in midair.
 
Study of Tyto alba reject balls
 
These digestive byproducts of birds, which in some species do not follow the typical route of excretion when agglomerated, are called reject balls, according to (Taberlet 1983; Montoya et al., 2021). The patient tries to escape through the mouth opening and not through the oesophagus and moves in the opposite direction. For this study, this strategy included examining the materials of scarecrow rejection balls. L’Effraie prefers to hunt in open areas. Its diet is more varied than that of other nocturnal birds of prey, which these insectivores tend to despise (Bourlière, 1974; Sekour et al., 2010); It consists of 90 to 95 percent small rodents, the rest are flight-caught bats, frogs and birds (Hadjoudj et al., 2020).
       
Tyto alba’s nutritional research is divided into four parts. The first will be completed outside. This is the study station’s collection of raptor-repellent balls. The second, third and fourth processes are completed in the laboratory. This includes analyzing the aqueous wet rejection balls and identifying and counting the prey species discovered in the barn owl’s shelled balls.
 
Ball collection and experimental analysis institute
 
The balls of rejection were collected in the mosque’s minaret at the Elarfgi station in 2021. Each ball is housed in its small paper cone, containing information about the bird of prey’s name, date and collection location.
       
The laboratory and analytical work for this project was conducted at the Biology, Environment and Health Laboratory at the University of El Oued. The results, especially species identification, were then passed to Professor Sekour Makhlouf of the University of Ouargla to confirm and verify their scientific names. This work took place from January 2019 to March 2022.
 
Analysis of the rejection balls
 
According to (Boireau, 2009), this technique aims to extract from the ball the essential parts that provide most of the data necessary to identify the target. These parts include vertebral bones of vertebrates and sclerotinized fragments of arthropods. The ball is measured, macerated in a glass Petri dish with some water, then transported to the trituration step to remove the bone fragments, bug fragments, hair and feathers using two pliers (Libois et al., 1983). Following separation, the fragments are put in a new Petri dish with the date, the location of the collection and the paddle number on it. A binocular magnifying glass and graph paper gauge the size of arthropods and bones found in the paddle to identify the prey species (Fig 1). The later parts are compared with identification keys, reference collections and keys.
 

Fig 1: Stages of analysis of Barn Worm rejection balls (Original).


 
Identification of prey species
 
The vertebrate prey species discovered in rejection balls fall into the following taxonomic groups: Insectivora, Rodentia and Chiroptera. (Barreau et al., 1991; Chaval, 2014) state that rodent identification is based on three criteria. The first is based on the shape of the back of the lower jaw. The second concerns the calvaria’s zygomatic plate and tympanic bubbles and their properties. The third method is based on the molars’ wear surface layout and the quantity of dental roots’ alveoli. According to Bourlière (1974; Tavernier et al., 2022), the upper first molar in Mus musculus is roughly equivalent to the second and third molar’s combined length. Mus spretus, however, has a tetra-lobed first lamella of the lower first molar and a consistently shaped zygomatic plate (Benamane et al., 2019; Merabet et al., 2022). The upper incisors of the Gerbillinae are hollow with a median groove, according to (Boukhamza et al., 1994; Hamdine 1998; Rihane, 2018). Tympanic bubbles in this family’s species are highly developed and have a broad skull (Le Louarn and Quéré, 2011; Masudi et al., 2016).
 
Count of prey species
 
The existence of the forehead and jaws is the main factor used to count rodents. The long bones are considered in the latter’s absence, particularly the femurs, pelvic bones, tibias, humerus and others.
 
Exploitation of results by statistical methods
 
The deferential indexes, which include generic, specific and average wealth, take advantage of the outcomes. Relative abundance (A.R. per cent) is the ratio of the number of individuals of a prey species (Ni) to the sum of all the individuals of all the species (N) as determined by all surveys (Zaime and Gautier, 1989; Fethia et al., 2021). Occurrence frequency (FO) is the proportion of surveys (Pi) with the species I present to all surveys (P), expressed as a percentage (Dajoz, 2000; Faurie, 2011; Serge and Figuié, 2016). The link between the natural diversity (H’) and the maximal theoretical diversity is known as equitability (E), which is also employed (H max).
Rodent inventory by random trapping is a separate study from the Tyto alba rejection balls analysis. The findings on the Barn Owl’s feeding system are presented in this section. The primary aim of the rodent study is to analyze 133 balls of rejects from the later raptor found in the mosque’s minaret in Elarfgi.
 
Characteristics of the balls of the Barn Owl
 
As for the peculiarities of the regurgitates of this raptor, it is helpful to focus on the dimensions of the balls and their weights. Then, variations in the number of preys per paddle are considered.
 
Dimensions of Barn Owl reject balls
 
The average measurements of the length, large diameter and weight of the Tyto alba balls analyzed are grouped in Table 1. Tyto alba rejected 133 balls, 23 of which were fractured. The remnants (110 balls) have a length of 24 to 97 mm (average: 39.7±8.61 mm; Table 1). The large paddle sizes of this raptor range from 12 to 40 mm (average: 24.8±3.76 mm). These paddles have weights ranging from 1 to 22.5 g (average: 4.16±2.06 g) (Table 1). They come in 39.7 mm and 8.61 mm average lengths. According to ALIA et al., (2012), the average size of the gathered pellets is 38.75 mm and 11.68 mm. In contrast, SEKOUR et al., (2010) claim that the M’Sila region has high mean length values. These writers noted 48.10 mm as the average length. This raptor’s huge balls have a diameter of 24.8 mm and 3.76 mm. Additionally, these balls weigh an average of 4.16 mm and 2.06 g each. According to alia et al., (2012), this raptor’s huge balls have a diameter of 24.7 mm and 2.9 mm. Similarly, SHEHAB (2005) records readings in Syria ranging from 18 to 32 mm. Barn Owl rejection balls with huge diameters of 26 mm were reported by Switzerland MEBS in 1994.
 

Table 1: Dimensions (mm) and weight (g) of Barn Owl balls harvested in the Souf region.


 
Variation of the number of preys per ball in Tyto alba
 
Fig 2 depicts variations in the number of preys per paddle in the investigated Barn in the Souf region. In this piece, there are somewhere between 1 and 9 preys on each paddle (Fig 2). The most common type of ball, with a rate of 27.8%, has two preys in it. They are followed by those that have three preys (25.6%) and those that have one prey (18.0%). (Fig 2). Similarly, Alia et al., (2015b) report an even number of preys per paddle, ranging from 1 to 9. Balls with two preys are the most prevalent, accounting for 31.7% of all balls. Presents balls of the barn in Cote d’Or (France), distinguished by a variety of prey, ranging from 1 to 13 prey (Baudvin, 1986). However, Sekour et al., (2010) report that there are only 1 to 4 prey per skein in the highlands of Mergueb. The same scientists report that balls with only one prey are most frequently observed (69.1 per cent), followed by balls with two prey (25.5%). Therefore, it can be claimed that the Barn Owl often only feeds on one to three preys, which suggests that its prey is significant in size and biomass, as is the case for rodents.
 

Fig 2: Prey rate per ball for T. alba in the Souf region.


 
Study of the diet of the Tyto alba by ecological indices of composition
 
The study of the data on Tyto alba’s food by ecological composition indices is covered in the following section.
 
Generic, specific richness of the prey identified in the reject balls of the Barn Owl
 
Table 2 lists the general and specific prey richness of Tyto alba regurgitations.
 

Table 2: Generic, prey-specific richness of Tyto alba reject balls and importance of rodents.


       
Tyto alba rejections from 133 balls were analyzed, and the results revealed 23 prey species (Sm = 1.9±0.63 species) in 17 genera (all taxa combined, Table 2). When it comes to rodents, there are 7 genera, 13 species (Sm = 1.65±0.67 species) and 341 individuals (Table 2). According to Alia et al., (2015b), 170 individuals were found after analyzing the rejection balls and they were grouped into 17 genera and 23 prey species (Sm=1.83±0.93 species). In Bouclans (France), Michelat and Giraudoux (1993) found a total species richness of 13 species. Roulin (1996) noted the same amount in the Swiss canton of Broye. The total richness (39 species) Baziz et al., (2002) mentioned is higher than ours. In the balls of Tyto alba, Aulanginer et al., (1999) recorded 32 prey species in Morocco.
 
Relative abundance applied to prey categories
 
Fig 3 displays the relative quantity of prey categories discovered in Tyto alba reject balls. There seem to be 5 categories listed (Fig 3). Rodentia (88.3%%) has the highest population density, followed by Aves (20%, 5.2%), Insects (15 individuals, 3.4%), Reptilia (1.8%) and Chiroptera (1.3 %, Fig 3). In the exact study location, Alia et al., (2012) discovered that rodents are the tiny trophic Tyto alba’s most prevalent prey type (88.2%). Similarly, Sekour et al., (2005) in the M’Sila region report that rodents predominate all prey by examining rejection balls with 89.6% and even for the remnants at the nest of this raptor (62.6%). Even though rats make up 63.8 per cent of the trophic menu of the Barn et al., (2000) emphasize the significance of microorganisms (68.4%). After analyzing barn pellets, Staouéli et al., (2002) confirmed the dominance of rodents (67.0%). Rihane (2005) reveals the significance of rodents in Tyto alba rejection balls with a rate of 50.8 per cent in the semi-arid plains of Morocco. Similarly, Leonardi and Dell’arte (2006) demonstrate the predominance of rodents in the diet of the Barn Owl in a steppe setting in Tunisia. According to Amat and Soriguer (1981), mammals make up 72.7% of the land area in western Spain. According to Sorgo (1992), micro-mammals are the source of 96.5 per cent of Tyto alba’s prey in Slovenia.
 

Fig 3: Relative abundance of prey categories noted in Tyto alba balls.


 
Relative abundance of prey species sampled in Barn Owl regurgitates
 
The importance of all prey species ingested by Barn Owls is shown in Fig 4.
 

Fig 4: Relative abundance of prey species noted in Tyto alba balls.


       
G. gerbillus is the prey species found in Barn Owl balls at a rate of 36.8%. M. musculus (10.6 per cent), G. nanus (9.8 percent), G. tarabuli (11.1 per cent) and G. campestris were the following most common species (8.3 %). With rates that don’t go above 3.5 per cent, other species, including insects, reptiles, birds and bats are only marginally represented (Fig 4). The two species that souf encounters the Barn Owl the most frequently are G. gerbillus (44.0%) and G. compestris (13.3%). (Alia et al., 2015b). While in the highlands, Meriones shawii is the most consumed prey by the barn in Ain El-Hadjel (87%) (Sekour et al., 2010).
 
Occurrence frequency of prey species noted in Barn Owl reject balls
 
Results for the frequency of occurrence of all prey species ingested by the Barn Owl are shown in Fig 5. Based on the frequency of occurrence values, G. gerbillus (OF = 54.1%) is a regular prey item in the Barn Owl trophic menu (Fig 5). By contrast, the species that are considered accidental prey in the diet of this raptor are G.nanus (OF = 23.1%), G. campestris (OF = 20.3%), G. tarabuli (OF = 19.5%), M. musculus (OF = 17.3%), D. simoni (OF = 7.5%), J. jaculus (FO = 7.3%), Passer sp. (OF = 6.0%) and Lacertidae sp. ind (FO = 5.3%, Fig 5).
 

Fig 5: Occurrence frequency of species prey in Barn Owl rejection balls.


 
Study of the diet of the Barn Owl by ecological indices of structure
 
The Shannon-Weaver Diversity Index uses the Barn Owl regurgitation ball analysis results, the Maximum Diversity Index and equitability. They are set out in Table 3.
 

Table 3: Shannon-Weaver diversity index, maximum diversity and equitability applied to prey species from Tyto alba to Souf.


       
The H’ value is 3.25 bits for all prey species compared to 2.68 bits for rodents exclusively (Table 3). Therefore, the rodent category is particularly diversified compared to the other animal types stated in the balls of the Barn. H’ max values 4.52 bits for all prey species, compared to 3.70 bits for rodents only (Table 3). At the same time, the obtained equitability values for both groups tend to be equal to 1, whether it is for all prey species (E = 0.72) or simply for rodent prey species (E = 0.73) (Table 3). This indicates that the quantity of prey species included in this raptor’s rejection balls tends to be balanced.
 
Study of the age categories of rodents-prey found in the Barn Owl balls in the Souf region
 
The age categories of rodent-prey species noted in the regurgitations of Tyto alba are given in Table 4.
 

Table 4: Age variation of rodents-prey found in barn owl rejection balls.


       
Most of the prey rodent species, as shown in Table 4, are adults and sub adults. The four age groups correspond to the species G. gerbillus, G. nanus, G. tarabuli and G. campestris, as well as D. simoni, M. musculus and J. jacullus. R. rattus and P. duprasi, however, each have three age groups (subadult, adult and elderly). G. gerbillus (62.7%), G. nanus (60.5%), G. tarabuli (53.1%), G. campestris (55.8%), M. musculus (46.3%) and J. jacullus all have high populations in the subadult age class (53.8 %, Table 4). However, Mus spretus (subadult and elderly) and P. obesus are two species that have two age categories (sub adult and adult).
The analysis of the waste pellets, used as a complementary method alongside rodent trapping, revealed important information. The rodent prey found in the pellets of Tyto alba are classified into two families: Muridae and Dipodidae. The species identified include G. gerbillus, G. nanus, G. tarabuli, G. campestris, D. simoni, P. duprasi, P. obesus, M. musculus, M. spretus, R. rattus and J. jaculus. Among these, gerbils are the preferred prey for the Barn Owl, particularly G. gerbillus and G. campestris. In terms of prey diversity, the Barn Owl's regurgitated pellets exhibit a notable variety of environments utilized by this raptor, indicating a balanced distribution in prey numbers. Furthermore, the age categories most frequently chosen by the Barn Owl in the Souf region are subadults and adults, suggesting these age groups are the most actively hunted.
On behalf of all the authors of the aforementioned manuscript, I am writing to confirm that we have no conflicts of interest related to the research, authorship and publication of this article. None of the authors have any financial, personal or institutional interests that could be perceived as influencing the outcomes or interpretations presented in the manuscript.
               
The findings and conclusions in our study are based solely on objective scientific data and analysis. We assure you that this work was conducted without any bias or external influence that could compromise its integrity.

  1. Alia, Z. and M. Sekour, et al. (2012). Importance of the rodents in the diet of Tyto alba (Scopoli, 1759) in the Souf region (Algeria). Revue des BioRessources. 2(2): 11.

  2. Alia, Z. and M. Sekour, et al. (2015). Régime alimentaire de Tyto alba (Scopoli, 1759) que des rongeurs dans la région de Souf (Algérie). 3 Colloque International sur l» Ornithologie Algérienne à l’aube du 3ême millénaire (les oiseaux et leurs milieux). Uni. Guelma.

  3. Amat, J. and S. RC (1981). Analyse comparative des régimes alimentaires de l’Effraie Tyto alba et du Moyen-duc Asio otus dans l’Ouest de l’Espagne.

  4. Aulagnier, S., M. Thevenot, et al. (1999). Régime alimentaire de la Chouette effraie, Tyto alba, dans les plaines et reliefs du Maroc Nord-Atlantique. Alauda (Dijon). 67(4): 323-336.

  5. Barreau, D., A. Rocher, et al. (1991). Eléments d’identification des crânes des rongeurs du Maroc, SFEPM [Société française pour l’étude et la protection des mammifères].

  6. Baudvin, H. (1986). La reproduction de la chouette effraie (Tyto alba). Le Jean-le-Blanc. 25: 1-125.

  7. Baziz, B., S. Doumandji, et al. (1999). Adaptations trophiques de la Chouette effraie Tyto alba (Aves, Tytonidae) dans divers milieux en Algérie. Proceedings of International Union of Game Biologists. pp 217-227.

  8. Baziz, B., S. Doumandji, et al. (1999). Prédation de la Chouette effraie Tyto alba (Aves, Tytonidae) dans la banlieue d’Alger. Proceedings of International Union of Game Biologists. pp 267-276.

  9. Baziz, B., Hamani A. Doumandji S. (2000). Données sur le régime alimentaire de la Chouette Effraie T. alba (Scopoli, 1759) (Aves, Tytonidae) au niveau du barrage de Boughzoul: le point sur plusieurs années des travaux. 1989–1999. 5eme Journée Ornith., 18 avril 2000, Dép. Zool. agri. for. Inst. Nat. Agro., El Harrach, Alger. 21 p. 

  10. Baziz, B. and S. Doumandji, et al. (2002). Adaptations trophiques de la Chouette effraie Tyto alba (Aves, Tytonidae) dans diverses zones humides dans le Nord-Ouest de l’Afrique. Ornithologia algirica 2(1): 56-64.

  11. Benamane, A. H. and S. Bissati-Bouafia, et al. (2019). Diet of Barn Own (Tyto alba) determination from regurgitated pellets in southeastern Algeria, coupling the classical approach with the eDNA analysis. International Journal. 75(2/1). doi: 10.21506/j.ponte.2019.2.5. 

  12. Boireau, J. (2009). Problèmes posés par l’Effraie des clochers Tyto alba dans cinq colonies de reproduction de grand rhinolophe Rhinolophus ferrumequinum (Schreber, 1774) en Bretagne occidentale. Le Rhinolophe. 18: 43-49.

  13. Boukhamza, M., Hamdine, W. et al. (1994). Données sur le régime alimentaire du Grand-duc ascalaphe Bubo bubo ascalaphus en milieu steppique (Ain Ouessera, Algérie). Alauda (Dijon) 62(2): 150-152.

  14. Boukhemza, M. (1989). Données sur le régime alimentaire de la Chouette effraie (Tyto alba) dans la banlieue suburbaine d’Alger. Aves. 26(3-4): 234-236.

  15. Bourlière, F. (1974). Chaline, J.; Baudvin, H.; Jammot, D. et Saint Girons, MC-Les proies des Rapaces (Petits Mammifères et leur environnement). Paris, Doin, 1974. Revue d’Écologie (La Terre et La Vie). 28(3): 477-478.

  16. Bourlière, F. (1984). Etchecopar, RD et Hue, F.—Les oiseaux de Chine, de Mongolie et de Corée. Volume 2. Passereaux. Paris, Société Nouvelle des Editions Boubée, 1983. Revue d’Écologie (La Terre et La Vie). 39(1): 120-121.

  17. Chaval, Y. (2014). Taxonomie intégrative de la tribu des Rattini (Rodentia, Muridae) en Asie du Sud-Est.

  18. Choudhary O.P., Priyanka, Kalita P.C., Arya R.S., Rajkhowa T.K., Kalita A., Doley P.J., Keneisenuo (2020). Morphometric and radiographic characteristics of the skull in crested serpent eagle (Spilornis cheela) and brown wood owl (Strix leptogrammica). Indian Journal of Animal Research. 55(4): 426-432. doi: 10.18805/ijar.B-3968.

  19. Côte, M. (2006). Si le Souf m’était conté. Comment se fait et se défait un paysage.

  20. Dajoz, R. (2000). Précis d’Écologie. 7ème éd. Paris, Éditions Dunod.

  21. Delibes, M., P. Brunet-Lecomte, et al. (1984). Datos sobre la alimentacion de la lechuza comun (Tyto alba), el buho chico (Asio otus) y el mochuelo (Athene noctua) en una misma localidad de Castilla la Vieja. Ardeola. 30: 57-63.

  22. Dhakal H.R., AhsanKabir A.K.M., Gulshan Z., Amin M.R., Rahman M.M., Khan M.R.I. (2023). Effect of deep bedded pack system in manure management for reducing heat stress of cattle in Bangladesh . Asian Journal of Dairy and Food Research. 42(2): 174-178. doi: 10.18805/ajdfr.DRF-289.

  23. Dulsat-Masvidal, M., R. Lourenço, et al. (2021). A review of constraints and solutions for collecting raptor samples and contextual data for a European raptor biomonitoring facility. Science of the Total Environment. 793: 148-599.

  24. Faurie, C. (2011). Écologie Approche scientifique et pratique (6e ed.), Lavoisier.

  25. Fethia, L., Faiza, M. et al. (2021). Preliminary data on the feeding regime of the juvenile pharaoh eagle owl (Bubo bubo ascalaphus Savigny, 1809) in the semi-arid region of Oum el Bouaghi (east Algeria). Oltenia, Studii si Comunicari Seria Stiintele Naturii. 37(1).

  26. Giban, J. and H. Haltebourg (1965).“The problem of the Meriones of Shaw in Morocco.” French, Congr. Protect. Cultures Tropic, Chambre de Commerce et d’Industrie, Marseilles, France 587.

  27. Hadjoudj, M., M. L. Benhaddya, et al. (2020). Diet of the Barn Owl (Tyto alba)(Strigiformes: Tytonidae) in the Saharan Touggourt Area (Algeria). Acta Zoológica Lilloana: 30-42.

  28. Hamdine, W. (1998). Eléments d’identification des crânes des Gerbillidés d’Algérie. Trav. EPHE, Labo. BEV, Montpellier.

  29. Heim de Balsac, H. and N. Mayaud (1962). Les oiseaux du Nord- Ouest de l’Afrique [The Birds of North-West Africa]. Paris, Paul Lechevalier.

  30. Isenmann, P. and A. Moali (2000). Birds of Algeria. Paris, SEOF. Khemici M., Baziz B. et Doumandji S., 2002.- Partage des ressources alimentaires entre la Chouette effraie Tyto alba et l’Hibou moyen-duc Asio otus dans un agro-écosystème à Staoueli. 6ème Journée d’Ornithologie, 11 mars 2002, Dép. zool. agri. for., Inst. Nati. Agro., El Harrach, Alger, 24 p.

  31. Le Louarn, H. and J.P. Quéré (2011). Les rongeurs de France: faunistique et biologie. Les rongeurs de France: 1-312.

  32. Leonardi, G. and G. Dell’Arte (2006). Food habits of the Barn Owl (Tyto alba) in a steppe area of Tunisia. Journal of Arid Environments. 65(4): 677-681.

  33. Libois, R. M., R. Fons, et al. (1983). Le régime alimentaire de la chouette effraie, Tyto alba, dans les Pyrénées-Orientales. Etude des variations écogéographiques. Revue d’Ecologie, Terre et Vie. 37(2): 187-217.

  34. Martínez-Ruiz, M., V. Arroyo-Rodríguez, et al. (2020). Patterns and drivers of the scale of effect of landscape structure on diurnal raptors in a fragmented tropical dry forest. Landscape Ecology. 35(6): 1309-1322.

  35. Masudi, F. M., A. Dudu, et al. (2016). Biodiversité des rongeurs et Soricomorphes de champs de cultures mixtes de la région de Kisangani, République Démocratique du Congo. International Journal of Innovation and Applied Studies. 14(2): 327-339.

  36. Merabet, S., N. Khammes-El Homsi, et al. (2022). Seasonal reproduction shift among three murine rodents in a mediterranean area of north-western Africa. Pakistan Journal of Zoology 54(5): 2309-2314.

  37. Michelat D. et Giraudoux P., 1993.- Relation proies-prédateur-paysage chez la Chouette effraie Tyto alba pendant l’élevage des jeunes. Alauda. 61(2): 65-72.

  38. Montoya, A., X. Cabodevilla, et al. (2021). Vertebrate diet of the common kestrel (Falco tinnunculus) and barn owl (Tyto alba) in rain-fed crops: implications to the pest control programs. European Journal of Wildlife Research 67(5): 1-8.

  39. Natalini, R., A. Manganaro, et al. (1997). Spettro trofico del Barbagianni Tyto alba (Scopoli, 1759) e della Civetta Athene noctua (Scopoli, 1769) nella tenuta di Castelporziano (Roma). Alula. 6(1-2): 20-28.

  40. Ramade, F. (2012). Éléments d’écologie-7e éd.-Écologie appliquée, Dunod.

  41. Rihane, A. (2005). Contribution à l’étude du régime alimentaire de la chouette effraie Tyto alba dans les plaines semi-arides du Maroc (compléments). Go-South Bull. 2: 37-43.

  42. Rihane, A. (2018). Prédation de la Chouette effraie Tyto alba sur deux espèces sympatriques de rongeurs Gerbillidae: Gerbillus campestris et Dipodillus maghrebi dans les plaines de Chaouia et Doukkala.

  43. Roulin, A. (1996). Alimentation hivernale de la chouette effraie (Tyto alba), du hibou moyen-duc (Asio otus), du busard Saint- Martin (Circus cyaneus) et du faucon crécerelle (Falco tinnunculus). Bulletin de la Société Vaudoise des Sciences Naturelles. 84(1): 19-32.

  44. Sekour M. and Baziz B,et al., (2005). Comportement trophique des rapaces nocturne dans la réserve naturelle de Mergueb. 9eme Journée d’Ornith., 7 mars 2005, Dép. zool. agri. for. Inst. Nat. Agro., El Harrach, Alger. Pp: 64. 

  45. Sekour, M. (2010). Insectes, oiseaux et rongeurs, proies des rapaces nocturnes dans quelques locali-tés en Algérie. Thèse Doctorat, École Nati. sup. agro., El Harrach.

  46. Sekour, M. and B. Baziz, et al. (2010). Régime alimentaire de la Chevêche d’Athena Athene noctua, de l’Effraie des clochers Tyto alba, du Hibou moyen-duc Asio otus et du Grand-duc ascalaphe Bubo ascalaphus: réserve naturelle de Mergueb (Algérie). Alauda 78(2): 103-117.

  47. Serge, M. M. and Figuié (2016). Biogéographie et écologie de l’émergence.

  48. Shehab, A. H. (2005). Food of the Barn owl Tyto alba in Southern Syria. Acta Zoologica Cracoviensia 48(1-2): 35-42.

  49. Sobhana E., Swaminathan C., Kannan P., Gurusamy A. (2022). Conservation agriculture practices: Impact on productivity, energy utilisation and profitability of legume-based cropping system . Legume Research. 45(3): 334-340. doi: 10.18805/LR-4627.

  50. Šorgo, Andrej (1992). Prehrana pegaste sove Tyto alba na Dravskem polju. Acrocephalus.13(55): 166-173.

  51. Sridevi P., Rajalakshmi K., Sivakumar M., Karthikeyan A. (2020). Gross morphological studies on the vertebral column of Indian eagle owl (Bubo bengalensis). Indian Journal of Animal Research. 55(7): 801-805. doi: 10.18805/IJAR.B-4132.

  52. Taberlet, P. (1983). Evaluation du rayon d’action moyen de la chouette effaie, Tyto alba (Scopoli, 1769), à partir de ses pelotes de réjection. Revue d’Ecologie, Terre et Vie. 38(2): 171-177.

  53. Tavernier, G. and R. Pena, et al. (2022). Le régime alimentaire du Grand-duc d’Europe Bubo bubo dans le sud du département du Tarn, de 2009 à 2019. Nos oiseaux. 1(547): 69.

  54. Viteri, M. C. and M. A. Stegner, et al. (2022). Assessing the reliability of raptor pellets in recording local small mammal diversity. Quaternary Research. 106: 1-10.

  55. Voisin, J. (2004). Le Souf. Ed. El Walid, El-oued. 319. 

  56. Zaime, A. and J.Y. Gautier. (1989). Comparaison des régimes alimentaires de trois espèces sympatriques de Gerbillidae en milieu saharien,au Maroc. Revue d’Ecologie, Terre et Vie. 44(2): 153-163.

Editorial Board

View all (0)