Abstract
There is a frightening decline in the population pollinators around the world due to the over usage of synthetic pesticides, leading to the directly reduce of plant production. Plant extracts with insecticidal properties could be eco-friendly alternatives to synthetic pesticides in maintaining the pollinator population and the diversity of the ecosystem. The impact of aqueous extracts of Cassia occidentalis L., Eucalyptus camaldulensis Dehnh. and Hyptis suaveolens L. was investigated on the entomofauna and the seed yield of Gossypium hirsutum L. cotton. The study was carried out in RCBD, four times replicated: 3 extracts x 1 standard synthetic insecticide (TEMA) x 1 control x 4 groups of flowers (group 1: flowers free to insect visits, group 2: flowers protected from insects using gauze bags, group 3: protected flowers and opened exclusively to Amegilla sp. and group 4: protected flowers opened from time to time without any visit of insect). Gossypium hirsutum was found to be visited by the insects belonging to five orders, 10 families and 18 species. Amegilla sp.1 and Apis mellifera were the major pollinators during the rainy and dry seasons, respectively. The number and quality of seeds visited exclusively by Amegilla sp.1 were significantly improved by H. suaveolens extract. During the dry season, E. camaldulensis and H. suaveolens extracts as well as the standard insecticide improved the number of seeds and the percentage of normal seeds harvested from the flowers allowed to be visited by insects; that was probably due to their insecticidal effects which protected plants from pest damage. Therefore, aqueous extracts of E. camaldulensis and H. suaveolens are good candidates for incorporation in integrated pest management programs to minimize the risk of synthetic pesticides to pollinators, hence to increase the yield and the quality of seeds.
Keywords: Amegilla sp. 1, Gossypium hirsutum, Cassia occidentalis, Eucalyptus camaldulensis, Hyptis suaveolens, Plant extracts, Yield, Bocklé
Amegilla sp. 1; Gossypium hirsutum; Cassia occidentalis; Eucalyptus camaldulensis; Hyptis suaveolens; Plant extracts; Yield, Bocklé.
1. Introduction
In Cameroon, agriculture is the main activity in countryside and the main provider of jobs, since it employs around 60% of the working population (INS, 2017). One of the key objectives of agricultural research in Cameroon is the optimisation of agricultural yields to achieve a balanced diet (MINADER/DESA, 2010). The qualities of seeds and varieties have enabled farms to have yields of nearly 70% (MINADER, 2017). Cotton cultivation plays an important role in food self-sufficiency. In fact, the FAO estimates that nearly 100 million rural African families depend directly on cotton production, including more than 6 million rural African households (Abdoulaye et al., 2008). Cotton is the main lint crop in the world, its global production declining 3% to 25.8 million tons in 2018 (OECD/FAO, 2016). Although more than 50% of its production is intended for clothing; it also produces various derivatives, including vegetable oil and 20–30% protein (Abdoulaye et al., 2008). In Cameroon, the demand for cotton seeds and fiber (350,000 tons) is greater than its production (250,000 tons) because of pests, which represent the main cause of destruction of cotton crops (MINADER/DESA, 2010). The insect pests of cotton are grouped into four main categories, namely carpophagous caterpillars, phyllophagous caterpillars, sucker and mites. Crop losses due to attacks by these pests are greater than 30% and can reach total destruction of the production potential (SODECOTON, 2019).
Thus, in order to boost yields and meet up the ever-increasing market demand, farmers resort to the use of synthetic pesticides which has caused more damages than it has solved (Bambara and Tiemtoré, 2008). Africa uses less than 10% of global pesticide production but accounts for 75% of pesticide fatalities (Guèye et al., 2011). Indeed, they aren't just expensive, but they also acidify the soil when misuse and their residues are toxic to non-target fauna. They cause resistance in pest insects (Immaraju et al., 1992; Margni et al., 2002), and pollute surface water and groundwater (Ouédraogo, 2004). Considering the harmful effects of synthetic insecticides, it is necessary to develop and recommend alternative environmentally friendly methods to control insect pests of cotton while preserving pollinating insects. Pollinators such as bees are often involved in increasing the yield of fruits and seeds of several plants (Fluri and Frick, 2005; Djonwangwe et al., 2017).
Botanical insecticides are naturally occurring insecticides derived from plants that possess repellent, sterilant, antifeedant and toxicant properties and are environment friendly (Isman, 2000; Ayvas et al., 2009). In fact, plants through their derivatives such as powders, crude extracts, oil, essential oils and semi-purified or purified compounds provide natural insecticides for the protection of field crops and can be therefore used as a substitute for synthetic insecticides (Bambara and Tiemtoré, 2008; Cheikh et al., 2015; Barry et al., 2017, 2019). Essential oils from the leaves of C. occidentalis, E. camaldulensis and H. suaveolensis have been reported to possess insecticidal efficacy against insect pests (Conti et al., 2012; Chibuzor and Obioma, 2018; Rezaei et al., 2019). To provide farmers with quick and cheap access to crop pest control solutions, the present study was undertaken to investigate the impact of aqueous extracts of C. occidentalis, E. camaldulensis and H. suaveolens on the entomofauna and the seed yield of G. hirsutum.
2. Materials and methods
2.1. Study area and biological materials
The study was carried out over two seasons from 08 July to 17 December, 2019 and from 22 December, 2019 to 17 June, 2020 in Bocklé, 3rd district of Garoua Northern Region of Cameroon (latitude: 9°17′29.814″N; longitude: 13°25′4.38636″E; altitude: 169 masl). This area belongs to the Sudano-Sahelian zone of Cameroon characterized by unimodal rainfall. The rainy season lasts 4 months from June to September with two intermediate months of unreliable rainfall in May and October. Mean total annual rainfall is approximately 1000 mm and the mean annual temperature varied between 25.5 to 32.5 °C. Mean relative humidity varied between 42 to 83% (data recorded in 2018 by the Garoua international airport: unpublished).
The floristic species of vegetation encountered are consisting of Hyparrhemia rufa along rivers, Borassus aethiopium, Boswellia dalzielii, Commiphora africana, Lannea microcarpa, Bombax costatum, Prosopis africana, Vittellaria paradoxa and plantations of Azadirachta indica. Eucalyptus camaldulendis, Cassia occidentalis and Hyptis suaveolensis used in several traditional medicines to cure various diseases can be also found. Cassia occidentalis and H. suaveolensis are annual or short-lived perennial plants (Sharma et al., 2009; Yadav et al., 2010), while E. camaldulensis is perennial plant. There were five colonies of Apis mellifera and probably other non-inventoried colonies and, all other insects naturally present in the environment of the study area.
The experimental plot covered a surface area of 494 m2 (26.0 m length × 19.0 m broad). It was cleared and excavated using machetes and pickaxes, and then 4 blocks of 5 experimental units each were established. Each experimental unit consisted of one row of 3.5 m broad × 4.0 m length spaced 1.0 m apart. Five cotton Gossypium hirsutum seeds, variety QR1302 supplied by SODECOTON were sown at an intra-row and inter-row spacing of 36.36 cm and 50 cm respectively, and thinned to two per hill two weeks after sowing. The plot was manually weeded every two weeks.
2.2. Collection and processing of plant materials
Fresh leaves of C. occidentalis, E. camaldulensis and H. suaveolens were collected in the Djamboutou district at Garoua (latitude 9°310′N and longitude 13°410′E). Collection was done each two weeks on the eve of a treatment during the entire period. The aqueous plant extracts were obtained by using the method described by Sreekanth (2013): 400 g of each these leaves were weighed using a DIAMAN brand electronic balance (Capacity 3 kg, Precision 0.1 g), pounded separately using a wooden mortar and pestle before being put in a bucket containing 4L of water. Thereafter, the mixture was left to stand for 12 h. After maceration, the mixture was sifted through a 0.2mm mesh sieve into another bucket. The solutions obtained were each put into the sprayers.
2.3. Treatments
The study was carried out in a randomized complete block design (RCBD): 3 aqueous plant extracts × 1 standard synthetic insecticide (TEMA) × 1 control × 4 groups of flowers (group 1: flowers free to insect visits, group 2: flowers protected from insects using gauze bags, group 3: protected flowers and opened exclusively to Amegilla sp. and group 4: protected flowers opened from time to time without any visit of insect) × 4 replications. TEMA is a synthetic chemical insecticide containing 60 g of emamectin benzoate per kg and 75 g of teflubenzuron per kg. It is recommended at the rate of 200 g/ha to protect G. hirsutum at its different developmental stages against insect pests. In our study, 2 g was diluted in 3 L of water. Insecticide formulations were sprayed using five distinct manual gauge sprayers, each corresponding to a specific insecticidal product including the water used as control. Extracts and water at the rate of 714 L/ha and TEMA solution at the rate of 300 L/ha were applied in the evening between 5 and 6 p.m, two weeks interval, starting from the germination to the maturation of capsules. At bud stage, flowers were grouped as previously described and labelled: groups 1 and 2 = 120 flowers each, group 3 = 200 flowers and group 4 = 100 flowers.
2.4. Data collection
Flowers of group 1 were observed at the peak of flowering period and the foraging behaviour and insect species were recorded. The number of insects morphospecies visiting 120 G hirsutum flowers were counted every day between 6.00 a.m. and 5.00 p.m., with six time periods per day (6:00–7:00 a.m., 8:00–9:00 a.m., 10:00–11:00 a.m., 12:00–1:00 p.m., 2:00–3:00 p.m. and 4:00–5:00 p.m.). Since the insects were not marked, the cumulative data were expressed as the number of visits. Except A. mellifera and Amegilla sp.1, other insects visiting G. hirsutum were captured by hand/entomology forceps (larvae) or using entomological net (adults). Specimens were stored in glass vials containing 70% ethanol, except Lepidoptera that was preserved in papillotes as recommended by Borror and White (1991). Each glass vial was labelled according to the different treatments where insects were captured. At the end of the study, insects were identified by using insect keys (Delvare and Arbelenc, 1989; Borror and White, 1991; Couilloud, 1993; Eardley et al., 2010).
The number of A. mellifera and Amegilla sp.1 simultaneously foraging one and 1000 flowers was assessed according to the method described by Tchuenguem (2005). The frequency of each insect species (Fi) was determined using the following formula: Fi = (Vi/VI) ∗ 100, with Vi = number of visits of a given insect and VI the total number of visits by all insects (Tchuenguem et al., 2001).
The fruiting rate (FR), the average number of seeds (ANS) and normal seed percent (%NS) were recorded for each group as follow:
-
-
FR = (F1/F2)∗100: F1 is the number of boll formed and F2 the number of flowers initially labeled.
-
-
ANS: dried capsules were opened manually and seeds were harvested and counted.
-
-
%NS = (Number of normal seeds/Total seeds)∗100.
The mode of reproduction of G. hirsutum was determined from group 1 (not protected flowers) and group 2 (protected flowers). Ten days after the last flower wilted, the number of bolls formed in each group was counted. For each group, the fruiting index (Ifr) was calculated using the following formula: Ifr = (F1/F2), where F1 is the number of bolls formed and F2 the number of flowers initially labelled (Tchuenguem et al., 2004). The outcrossing rate (TC) was calculated using the formula: TC = {[(IfrX − IfrY)/IfrX] × 100}, where IfrX and IfrY are the mean fruiting indexes of free flowers (group 1) and protected flowers (group 2), respectively (Demarly, 1977). The rate of self-pollination in the broad sense (TA) was calculated using the formula: TA = (100 − TC).
The impact of flower insects and insecticide treatments on the fruiting rate (Fri) was evaluated using the following formula: Fri = {[(F1 − F4)/F1 + F2 − F4)] ∗ 100} where F1, F2 and F4 are the fruiting rates in groups 1 (free flowers), 2 (protected flowers) and 4 (flowers opened from time to time without any visit of insect), respectively. For a given group x, the fruiting rate is: Frx = [(number of capsules formed/number of flowers labelled)] ∗ 100 (Diguir et al., 2020).
The percentage of the number of seeds per capsule (Pg) attributable to the impact of flower insects and insecticide treatments was calculated as follow: Pg = {[(g1 − g4)/g1 + g2 − g4] ∗ 100)} where g1, g2 and g4 are the average number of seeds per capsule in groups 1, 2 and 4, respectively (Diguir et al., 2020).
The percentage of normal seeds (Pn) attributable to the impact of flower insects and insecticide treatments was calculated using the following formula: Pn = {([Pn1 − Pn4)/Pn1 + Pn2 − Pn4] ∗ 100)}; where Pn1, Pn2 and Pn4 are the percentages of normal seeds from groups 1, 2 and 4, respectively (Diguir et al., 2020).
The yield was assessed for each treatment by weighting the harvested corresponding seeds.
2.5. Statistical analysis
Data on insect abundance, fruiting rate, average number of seeds per capsule, normal seeds percent, weight of seeds and seed yield were log-transformed (x + 1). The transformed data were subjected to the ANOVA procedure of SPSS 16.0. Tukey's (Honest Significant Difference) multiple range test (p = 0.05) was applied for mean separation.
3. Results
From the investigations of that study, 413 individuals of insect pollinators belonging to 18 species, 10 families and five orders (Table 1) were recorded. Insect population seize was higher during the dry season (290 individuals belonging to 18 species) than the rainy season (123 individuals belonging to 17 species). More than half of individuals recorded belonged to the order of Hymenoptera. Amegilla sp. 1 (56.10 %) and Apis mellifera (25.86 %) were the most frequent floral visitors of G. hirsutum during the rainy season and dry season, respectively. Floral products, nectar and pollen were harvested by the species belonging to the order of Hymenoptera; nectar was harvested by those belonging to Diptera and Lepidoptera orders, while pollen was harvested by Coleopteran and Orthopteran.
Table 1.
Distribution of insects depending on the species and number of visits on Gossypium hirsutum flowers during the rainy and dry seasons.
Order | Family | Genus, species, floral products | Rainy season |
Dry season |
Total |
|||
---|---|---|---|---|---|---|---|---|
n1 | P1 (%) | n2 | P2 (%) | nT | PT (%) | |||
Hymenoptera | Apidae | Amegilla sp. 1 (Ne, Po) | 69 | 56.10 | 40 | 13.79 | 109 | 26.39 |
Amegilla sp. 2 (Ne, Po) | 4 | 3.25 | 8 | 2.76 | 12 | 2.91 | ||
Apis mellifera (Ne, Po) | 5 | 4.07 | 75 | 25.86 | 80 | 19.37 | ||
Xylocopa olivacea (Ne, Po) | 1 | 0.81 | 10 | 3.45 | 11 | 2.66 | ||
Xylocopa sp. 1 (Ne, Po) | 2 | 1.63 | 11 | 3.79 | 13 | 3.15 | ||
Xylocopa sp. 2 (Ne, Po) | 0 | 0.00 | 21 | 7.24 | 21 | 5.08 | ||
Megachilidae | Megachile sp. 1 (Ne, Po) | 5 | 4.07 | 15 | 5.17 | 20 | 4.84 | |
Vespidae | (1 sp.) (Ne, Po) | 2 | 1.63 | 7 | 2.41 | 9 | 2.18 | |
3 families | 8 species | 88 | 71.54 | 187 | 64.48 | 275 | 66.59 | |
Diptera | Syrphidae | (1 sp. 1) (Ne) | 1 | 0.81 | 10 | 3.45 | 11 | 2.66 |
(1 sp. 2) (Ne) | 3 | 2.44 | 7 | 2.41 | 10 | 2.42 | ||
(1 sp. 3) (Ne) | 5 | 4.07 | 11 | 3.79 | 16 | 3.87 | ||
1 family | 3 species | 9 | 7.31 | 28 | 9.66 | 37 | 8.96 | |
Lepidoptera | Hesperiidae | (1 sp.) (Ne) | 1 | 0.81 | 11 | 3.79 | 12 | 2.91 |
Nymphalidae | Acraea acerata (Ne) | 4 | 3.25 | 10 | 3.45 | 14 | 3.39 | |
Pieridae | Eurema sp. (Ne) | 2 | 1.63 | 8 | 2.76 | 10 | 2.42 | |
3 families | 3 species | 7 | 5.69 | 29 | 10.00 | 36 | 8.72 | |
Coleoptera | Cetoniidae | Pachnoda cordata (Po) | 9 | 7.32 | 14 | 4.83 | 23 | 5.57 |
Orthoptera | Acrididae | (1 sp. 1) (Po) | 1 | 0.81 | 13 | 4.48 | 14 | 3.39 |
(1 sp. 2) (Po) | 8 | 6.50 | 12 | 4.14 | 20 | 4.84 | ||
Pyrgomorphidae | Tettigonia viridissima (Po) | 1 | 0.81 | 7 | 2.41 | 8 | 1.94 | |
2 families | 3 species | 19 | 15.45 | 46 | 15.86 | 65 | 15.74 | |
Total | 10 families | 18 species | 123 | 100% | 290 | 100% | 413 | 100 |
n1 and n2: number of visits on 120 flowers; percentage of visits: p1= (n1/123) ∗100; p2 (n1/290)∗100; Ne: collection of nectar; Po: collection of pollen; sp.: unidentified species.
The impact of aqueous extracts of C. occidentalis, E. camaldulensis and H. suaveolens on the foraging behaviour of A. mellifera and Amegilla sp. 1 was significant (F = 12.43, 16.93; p < 0.001) (Table 2). All the tested extracts were attractive to the both insect species compare to control, and standard synthetic insecticide which was very repellent. E. camaldulensis and C. occidentalis extracts were the most attractive.
Table 2.
Abundance of Amegilla sp. and Apis mellifera foragers per 1000 flowers of Gossypium hirsutum treated with insecticidal products.
Insect/season | Insecticide |
F |
||||||
---|---|---|---|---|---|---|---|---|
Control | C. occidentalis | E. camaldulensis | H. suaveolens | TEMA | ||||
Amegilla sp. 1/Rainy season | 100.24 ± 0.67bc | 122.52 ± 3.54a | 128.59 ± 4.21a | 113.79 ± 2.20ab | 93.27 ± 2.87c | 11.47∗∗∗ | ||
A. mellifera/dry season | 105.26 ± 1.21bc | 115.11 ± 1.52b | 133.86 ± 3.35a | 111.99 ± 1.21b | 101.26 ± 2.29c | 25.04∗∗∗ |
∗∗∗: p < 0.001.
Means within the same line followed by the same letter do not differ significantly (p < 0.05; Tukey's test).
Apis mellifera and Amegilla sp. 1 were found to visit G. hirsutum flowers from 6 a.m. to 5 p.m (Figure 1). Foraging activities fluctuated from the morning to the evening. Frequency of appearance was noted more between 10 a.m. to 1 p.m. for A. mellifera (dry season) and between 12 to 3 p.m. for Amegilla sp. 1 (rainy season). The peaks of activities were 12–1 p.m. and 2–3 p.m., respectively for A. mellifera and Amegilla sp. 1. Insecticidal products were either repulsive or attractive to pollinators depending on the periods of foraging activities. Overall, extracts were more moderately attractive to Amegilla sp. 1 than the control treatment, early in the morning (6–7 a.m.) and in the evening (4–5 p.m.). At 8–9 a.m. and 10–11 a.m., H. suaveolens and E. camaldulensis were also respectively more attractive to Amegilla sp. 1 compare to the control treatment. Furthermore, all the extracts were more attractive to Amegilla sp. 1 than the standard synthetic insecticide TEMA, before noon and in the evening at 4–5 p.m. However, TEMA was very attractive to Amegilla sp. 1 compared to the extracts at 12–3 p.m. At 8–9 a.m., extracts were most attractive to A. mellifera than control and synthetic insecticide. In fact, the standard synthetic insecticide was repellent to A. mellifera compare to extracts, except at 12–1 p.m.
Figure 1.
Frequency of Amegilla sp. 1 and Apis mellifera visits on Gossypium hirsutum flowers according to daily periods and insecticide treatments during the rainy (A) and dry (B) seasons.
The number of insect pest species (Figure 2) recorded on G. hirsutum plants varied between treatments. Six, seven and eight species were recorded from C. occidentalis, H. suaveolens and E. Camaldulensis treatments, respectively. The same species were recorded on plants treated with E. Camaldulensis and on those without treatment. Treatment with the standard synthetic insecticide TEMA recorded the highest number of species (nine). Overall, insect abundance between treatments including the control was not significant (Table 3).
Figure 2.
Insect pest species recorded on Gossypium hirsutum plants treated with botanical insecticides. A: Aphis gossypii, B: Dysdercus delauneyi, C: Cheilomenes propinqua, D: Pachnoda cordata, E: Anthonomus sp., F: Halitarodes derogata, G: Diparopsis wateri, H: Lacusta migratoria, I: Zonocerus variegatus.
Table 3.
Abundance of insect pest species on Gossypium hirsutum plants treated with insecticidal products.
Insect pest species | Insecticide |
F4,15 |
||||
---|---|---|---|---|---|---|
Control | Cassia occidentalis | Eucalyptus camaldulensis | Hyptis suaveolens | TEMA | ||
Aphis gossypii | 4.75 ± 1.70 | 4.25 ± 0.25 | 2.50 ± 0.50 | 3.75 ± 0.85 | 4.75 ± 1.55 | 0.69ns |
Dysdercus delauneyi | 2.00 ± 2.00 | 0.75 ± 0.47 | 0.25 ± 0.25 | 0.00 ± 0.00 | 0.25 ± 0.25 | 0.74ns |
Cheilomenes propinqua | 2.25 ± 1.03 | 0.00 ± 0.00 | 0.75 ± 0.47 | 2.00 ± 0.81 | 2.25 ± 1.60 | 1.15ns |
Pachnoda cordata | 6.00 ± 4.06 | 3.50 ± 1.50 | 3.50 ± 1.04 | 4.25 ± 1.43 | 3.00 ± 0.91 | 0.31ns |
Anthonomus sp. | 0.50 ± 0.28 | 2.25 ± 1.03 | 2.75 ± 0.95 | 2.00 ± 1.08 | 1.25 ± 0.25 | 1.19ns |
Halitarodes derogata | 0.00 ± 0.00 | 0.50 ± 0.29 | 0.00 ± 0.00 | 0.50 ± 0.29 | 0.25 ± 0.25 | 1.36ns |
Diparopsis wateri | 0.25 ± 0.25 | 0.00 ± 0.00 | 1.25 ± 1.25 | 2.25 ± 2.25 | 1.00 ± 0.57 | 0.57ns |
Lacusta migratoria | 4.25 ± 1.60 | 3.25 ± 1.10 | 0.75 ± 0.25 | 1.00 ± 0.71 | 1.75 ± 0.85 | 2.23ns |
Zonocerus variegatus | 2.50 ± 1.44 | 0.00 ± 0.00 | 0.50 ± 0.50 | 0.00 ± 0.00 | 0.25 ± 0.25 | 0.66ns |
Total | 22.50 ± 8.00 | 14.50 ± 2.40 | 25.25 ± 2.87 | 15.75 ± 3.77 | 14.75 ± 4.71 | 0.76ns |
ns: p > 0.05.
The comparison of fruiting rate (Fr), average number of seeds per capsule (ANSPC) and normal seeds percent (NSP) under diverse reproduction system (Tables 4 and 5) showed that observed differences were significant between some treatments. Eucalyptus camaldulensis extract significantly (F4,115 = 3.13–10.83, p ≈ 0.05–0.001) improved Fr, ANSPC and NSP when the flowers were exclusively allowed for self-pollination during the rainy and dry seasons. During the dry season (Table 5), E. camaldulensis and H. suaveolens treatments as well as the standard insecticide improved ANSPC and NSP harvested from the flowers visited exclusively by Amegilla sp.1. The contributions of Amegilla sp. 1 to increase ANSPC and NSP during the rainy and dry seasons was significant for control (F3,8 = 6.96, 7.78, p = 0.01, 0.05) and treatment with aqueous extract of H. suaveolens (F3,8 = 10.21, 18.42, p = 0.01, 0.001). During the dry season, C. occidentalis improved the Fr and ANS of G. hirsutum pollinated by Amegilla sp.1.
Table 4.
Fruiting rate, average number of seeds per capsule and normal seeds percent of Gossypium hirsutum treated with insecticidal products under diverse reproduction system during the rainy season.
Parameter | TREATMENTS |
|||||
---|---|---|---|---|---|---|
Control | Cassia occidentalis | Eucalyptus camaldulensis | Hyptis suaveolens | TEMA | F4,115 | |
Fruiting rate (%) | ||||||
FF | 100 ± 0.00 | 95.83 ± 4.17ab | 100 ± 0.00 | 100 ± 0.00 | 100 ± 0.00 | 1.00ns |
BF | 83.33 ± 8.33 | 100 ± 0.00a | 100 ± 0.00 | 91.66 ± 8.33 | 100 ± 0.00 | 2.00ns |
FvA | 88.09 ± 8.58 | 84.92 ± 4.76ab | 100 ± 0.00 | 100 ± 0.00 | 100 ± 0.00 | 1.41ns |
FOWV | 74.60 ± 9.91B | 84.92 ± 0.79ABb | 100 ± 0.00A | 100 ± 0.00A | 95.24 ± 4.76A | 10.83∗∗∗ |
F3,8 | 2.55ns | 4.04∗ | - | 1.00ns | 1.00ns | |
Average number of seeds | ||||||
FF | 16.92 ± 2.18b | 18.25 ± 6.18 | 22.09 ± 1.17 | 26.71 ± 0.25a | 29.17 ± 0.93 | 3.07ns |
BF | 18.33 ± 0.73BCb | 25.42 ± 1.16AB | 21.88 ± 1.96ABC | 16.67 ± 2.96Cb | 28.79 ± 1.00A | 8.03∗∗ |
FvA | 27.53 ± 2.56a | 24.66 ± 0.88 | 28.03 ± 0.76 | 29.33 ± 0.35a | 28.61 ± 1.32 | 1.63ns |
FOWV | 19.92 ± 0.94ABb | 10.42 ± 2.09B | 27.34 ± 1.81A | 24.96 ± 2.66Aa | 22.63 ± 3.88A | 6.99∗∗ |
F3,8 | 6.96∗ | 4.35ns | 4.81ns | 7.47∗ | 2.09ns | |
Normal seeds (%) | ||||||
FF | 59.03 ± 4.87 | 62.83 ± 19.36 | 81.54 ± 1.93 | 84.13 ± 2.47ab | 95.85 ± 0.24 | 2.90ns |
BF | 49.01 ± 5.62B | 72.85 ± 1.75AB | 68.61 ± 9.73 AB | 46.06 ± 9.17Bc | 82.90 ± 5.29A | 5.19∗ |
FvA | 68.14 ± 10.48AB | 68.63 ± 6.09B | 84.14 ± 3.93 AB | 94.40 ± 0.34 Aa | 86.33 ± 8.16 AB | 2.91ns |
FOWV | 48.77 ± 8.49C | 56.38 ± 4.94BC | 84.67 ± 3.13A | 64.32 ± 3.10ABCbc | 75.79 ± 6.10AB | 7.17∗∗ |
F3,8 | 1.44ns | 0.46ns | 1.84ns | 18.42∗∗∗ | 1.76ns |
ns: p > 0.05; ∗: p < 0.05; ∗∗: p < 0.001; ∗∗∗: p < 0.001.
Means within the same column and line followed respectively by the same small and capital letter do not differ significantly (p < 0.05; Tukey's test).
–: estimation of the F value is not possible due to equal variance; FF: free flowers; BF: bagged flower; FvA: flowers visited exclusively by Amegilla sp. 1; FOWV: flowers opened without any visit of insect.
Table 5.
Fruiting rate, average number of seeds per capsule and normal seeds percent of Gossypium hirsutum treated with insecticidal products under diverse reproduction system during the dry season.
Parameter | Treatments |
|||||
---|---|---|---|---|---|---|
Control | Cassia occidentalis | Eucalyptus camaldulensis | Hyptis suaveolens | TEMA | F4,115 | |
Fruiting rate (%) | ||||||
FF | 100 ± 0.00 | 94.00 ± 6.00a | 100 ± 0.00 | 100 ± 0.00 | 100 ± 0.00 | 1.00ns |
BF | 73.33 ± 13.64 | 100 ± 0.00a | 78.67 ± 12.72 | 66.67 ± 20.27 | 95.00 ± 5.00 | 1.29ns |
FvA | 100 ± 0.00 | 100 ± 0.00a | 100 ± 0.00 | 95.00 ± 5.00 | 100 ± 0.00 | 1.00ns |
FOWV | 76.00 ± 14.80AB | 49.67 ± 7.80Bb | 100 ± 0.00A | 77.33 ± 13.92AB | 90.04 ± 9.96AB | 3.13∗ |
F3,8 | 2.12ns | 24.47∗∗∗ | 2.81ns | 1.52ns | 0.73ns | |
Average number of seeds | ||||||
FF | 15.42 ± 2.20BCb | 10.75 ± 1.76Cab | 20.59 ± 1.17ABab | 22.21 ± 0.25Aab | 24.27 ± 0.93A | 15.29∗∗∗ |
BF | 16.53 ± 0.73BCb | 11.28 ± 0.30Cab | 20.08 ± 1.96Bb | 14.87 ± 2.95BCb | 20.79 ± 1.00A | 12.49∗∗∗ |
FvA | 26.3 ± 2.57Aa | 13.56 ± 0.88Ba | 26.93 ± 0.76Aa | 28.23 ± 0.35Aa | 25.71 ± 1.32A | 19.41∗∗∗ |
FOWV | 18.02 ± 0.94Ab | 08.18 ± 0.44Bb | 25.44 ± 1.81Aab | 19.06 ± 2.66Ab | 17.73 ± 3.88AB | 7.21∗∗ |
F3,8 | 7.78∗∗ | 4.68∗ | 5.21∗ | 7.92∗∗ | 2.75ns | |
Normal seeds (%) | ||||||
FF | 39.03 ± 4.87Bab | 46.16 ± 16.13ABab | 61.54 ± 1.92AB | 57.43 ± 0.92ABab | 75.65 ± 0.77A | 3.47∗ |
BF | 29.01 ± 5.62b | 52.82 ± 1.75a | 45.28 ± 11.99 | 29.28 ± 7.16c | 61.71 ± 8.64 | 3.42ns |
FvA | 49.56 ± 3.88Ba | 60.26 ± 3.92ABa | 66.28 ± 5.64A | 71.88 ± 0.93Aa | 69.62 ± 3.00A | 5.55∗∗ |
FOWV | 36.49 ± 1.06ABab | 14.92 ± 3.57Bb | 54.61 ± 8.5A | 42.80 ± 8.92ABbc | 52.92 ± 8.11A | 5.55∗∗ |
F3,8 | 4.04∗ | 5.46∗ | 1.32ns | 10.21∗∗ | 2.58 ns |
ns: p > 0.05; ∗: p < 0.05; ∗∗: p < 0.001; ∗∗∗: p < 0.001.
Means within the same column and line followed respectively by the same small and capital letter do not differ significantly (p < 0.05; Tukey's test).
-: estimation of the F value is not possible due to equal variance; FF: free flowers; BF: bagged flower; FvA: flowers visited exclusively by Amegilla sp. 1; FOWV: flowers opened without any visit of insect.
The mean fruiting indexes were 0.99 and 0.87 in treatments 1 and 2, respectively. During rainy season, the allogamy rate was 12.12 % and the autogamy rate was 87.88%. During the dry season, the rates of 28.72% and 71.28% were recorded in the same order. It appears that G. hirsutum has a mixed mating system, autogamous-allogamous, with the predominance of allogamy.
Seed yields were not significantly different (F4,15 = 0.64, p > 0.05) between the treatments during the rainy season and significantly different (F4,15 = 3.37, p < 0.05) during the dry season (Table 6). Seed yields were higher during the dry season. The impact of insecticidal products on seed yield during the rainy season was not significant. During the dry season, aqueous extracts and the standard synthetic insecticide recorded significant higher seed yields compare to the control; C. occidentalis being recording the highest value.
Table 6.
Seed yield of Gossypium hirsutum treated with aqueous extracts of local botanicals at Bocklé during the rainy and dry seasons.
Treatment | Seed yield (kg.ha−1) |
---|---|
Rainy season | |
Control | 318.08 ± 155.02 |
Cassia occidentalis, | 192.33 ± 83.69 |
Eucalyptus camaldulensis | 135.28 ± 48.35 |
Hyptis suaveolens | 202.09 ± 38.27 |
TEMA | 234.27 ± 18.44 |
F(4, 15) | 0.64ns |
Dry season | |
Control | 492.19 ± 150.47b |
Cassia occidentalis | 1627.20 ± 447.50a |
Eucalyptus camaldulensis | 1128.30 ± 118.20ab |
Hyptis suaveolens | 1352.70 ± 134.93ab |
TEMA | 1466.50 ± 186.98ab |
F4, 15 | 3.37∗ |
ns: p > 0.05; ∗: p < 0.05; ∗∗: p < 0.001; ∗∗∗: p < 0.001.
Means within the same column followed by the same letter do not differ significantly (p < 0.05; Tukey’s test).
4. Discussion
According to this study, insects pollinate G. hirsutum in exchange of nectar and/or pollen, thus both are mutually benefitted. Insects are important pollinators for G. hirsutum. However, the specific type of insect varies across the globe (Bozbek et al., 2008; Parys et al., 2020). From that investigation, Amegilla sp. 1 was found as constant species visiting G. hirsutum during the rainy season, A. mellifera was accessory during the dry season and all other species were sporadic either during the rainy or dry seasons according to the classification of Bigot and Bodot (1973). Relative abundance of A. mellifera found in the present study as the major insect pollinators of G. hirsutum during the dry season might be partially explained by the presence of five colonies of that Apidae identified around the study area, and optimum environmental conditions for their foraging activities. The absence during the dry season or the presence during the rainy season of others flowering plants around the site of study might be another plausible reason of that seasonal abundance of A. mellifera. Amegilla sp. 1 was found to be the major insect pollinator of G. hirsutum during the rainy season in contrast to the finding reported by Mazi et al. (2020), where A. mellifera was found to be more abundant. The contrast between the results of these studies might be due to the impact of environmental conditions on the population size of each species. According to Ghosh et al. (2020), the temperature around 20–28 °C is optimum for A. mellifera to forage and foragers rarely work below 13 °C and above 38 °C (Abou-Shaara, 2018). Since the temperature of environmental area of the study was above 30 °C during the dry season and lower during the rainy season, temperature is less important factor to explain that seasonal variation of the abundance of A. mellifera visiting G. hirsutum. The plausible reason should be the availability of diverse resources more attractive than G. Hirsutum to honey bees during the rainy season. However, further study is required to assess the attractiveness of floristic plants surrounding cotton plantation to honey bees. The relative humidity, rainfall and wind speed might be also other factors which had significant negative effect on the foraging activity of A. mellifera during the rainy season. In a simple legitimate way, each bee pollinator has specific ecological threshold for foraging activity which might differ inter specifically depending upon the level of adaptation of a given species in an environment as reported by previous researchers (Burill and Dietz, 1981; Abrol and Kapil, 1986).
The peak of activity of A. mellifera at 12–1 p.m. and that of Amegilla sp. 1 at 2–3 p.m. was probably linked to the daily periods of greater availability of the floral products of G. hirsutum, at optimum environmental conditions which might be not the same for the both insect species. Ghosh et al. (2020) demonstrated that the honey bees were more active in the afternoon than in the morning and found the highest foraging activity at 1 p.m. because the highest amount of pollen foraged during this period of the day. These finding including ours did not corroborate with that of Adamou et al. (2020) who reported the peak of activity of Amegilla sp. 1 before noon at 10–11 a.m. The peak of the pollinator activity would depend on the daily flower blooming rate which may also depend on several abiotic factors. More details concerning the assessment of available resources, flower blooming rate and abiotic factors should be considered in the further study to more elucidate these contrasts.
Eucalyptus camaldulensis extract improved Fr, ANSPC and NSP of G. hirsutum allowed for self-pollination and this suggest that the use of botanicals to control the pests at vegetative stage of a plant might improve some plant yield parameters. This may be attributed to insecticidal activities of that plant. Abdelkhalek et al. (2020) reported the bark extract of that plant to be effective against Tribolium castaneum and Sitophilus oryzae. According to Dwibedi et al. (2017), the grain yield is highly correlated with the vegetative parameters and this relationship may be influenced by pests (Chastain and Young, 1998). In fact, insect pests have a direct impact on agricultural food production by chewing the leaves and stamen of crop plants, sucking out plant juices, boring within the roots, stems or leaves, and spreading plant pathogens. Eucalyptus camaldulensis and H. suaveolens aqueous extracts might be not toxic to non-target insects such as Amegilla sp, but toxic to insect pests, hence the improvement of ANSPC and NSP harvested from non-protected flowers. The pesticidal activities of these botanicals were reported by the previous researchers (Appiah et al., 2018; Sabo and Knezevic, 2019). The high seed yield recorded from C. occidentalis treatment during the dry season may be explained by the combined impact of that plant extract and pollination done by Amegilla sp.1.
5. Conclusion
From the present findings, it could be concluded that the preservation of nesting sites of A. mellifera during the rainy season and those of Amegilla sp. 1 all year round near cotton plantations increased fruit and seed yield. Overall, all the tested extracts were attractive to the both insect species compare to control, and standard synthetic insecticide, TEMA which was very repellent. E. camaldulensis and C. occidentalis extracts were the most attractive. Eucalyptus camaldulensis and H. suaveolens aqueous extracts improved ANSPC and NSP harvested from non-protected flowers by gauze bags and may be therefore recommended as good candidates for incorporation in the management of insect pollinators at flowering period of G. hirsutum. Aqueous extract of C. occidentalis improved Fr, ANS and seed yield, especially during the dry season. Hence, C. occidentalis extract may be also recommended to control field insect pests at different stages of the development of G. hirsutum.
Declarations
Author contribution statement
Moïse Adamou, Ph.D; Elias N. Nukenine, Ph.D; Daniel Kosini, Ph.D; A. Tchoubou-Salé, Ms: Conceived and designed the experiments; Analyzed and interpreted the data; Contributed reagents, materials, analysis tools or data; Wrote the paper.
Odette D. Massah, Ms: Performed the experiments; Analyzed and interpreted the data; Contributed reagents, materials, analysis tools or data.
T. F.C. Tchocgnia, Ms; M. Mohammadou, Ms; O. Youssoufa, Ms: Performed the experiments.
Funding statement
This research did not receive any specific grant from funding agencies in the public, commercial, or not-for-profit sectors.
Data availability statement
Data included in article/supp. material/referenced in article.
Declaration of interest’s statement
The authors declare no conflict of interest.
Additional information
No additional information is available for this paper.
References
- Abdelkhalek A., Salem M.Z.M., Kordy A.M., Salem A.Z.M., Behiry S.I. Antiviral, antifungal, and insecticidal activities of Eucalyptus bark extract: HPLC analysis of polyphenolic compounds. Microb. Pathog. 2020;147:1–11. doi: 10.1016/j.micpath.2020.104383. [DOI] [PubMed] [Google Scholar]
- Abdoulaye O., Lazare Y., Siaka D., Frank E., Raphael D. Helvetas; 2008. Guide de production du coton biologique et équitable; p. 47. [Google Scholar]
- Abou-Shaara H. The foraging behaviour of honey bees, Apis mellifera: a review. Vet. Med. 2018;59:1–10. [Google Scholar]
- Abrol D.P., Kapil R.P. Factors affecting pollination activity of Megachile lanata. Proc. Indian Acad. Sci. 1986;95:757–769. [Google Scholar]
- Adamou M., Nepide N.C., Mazi S., Yatahaï C.M. Impact of the pollinating activity of Apis mellifera (Hymenoptera: Apidae) on pod and seed yields of Vigna unguiculata (Fabaceae) variety BR1 in Djoumassi (North Cameroon) CJBBS. 2020;28:146–159. [Google Scholar]
- Appiah S.P., Chi M.V., Adom D., Asiedu F.A. Pesticidal effects of extracts from Hyptis suaveolens and Hyptis spicigera on cowpea Weevils. Int. J. Environ. Agric. Biotech. 2018;3:1691–1699. [Google Scholar]
- Bambara D., Tiemtoré J. Efficacité biopesticide de Hyptis spicigera Lam., Azadirachta indica A. Juss. et Euphorbia balsamifera Ait. sur le niébé Vigna unguculata L. Walp. Tropicultura. 2008;26:53–55. [Google Scholar]
- Barry B.R., Ngakou A., Nukenine N.E. Pesticidal activity of plant extracts and mycoinsecticide (Matarhizium anisopliae) on crowpea flowers Thrips and Leaves Damages in the Field. J. Exp. Agric. Int. 2017;18:1–15. [Google Scholar]
- Barry B.R., Ngakou A., Tamo M., Nukenine E.N. The incidence of aqueous neem leaves (Azadirachtaindica A. Juss) extrat and Metarhrizium anisoplia Metch. On cowpea thrips (Megolurothips sjotedtitrybom) and yield in Ngaoundéré (Adamaoua – Cameroun) J. Entomol. Zool. Stud. 2019;7:333–338. [Google Scholar]
- Bigot L., Bodot P. Contribution à l’étude biocénotique de la garrigue à Quecus coccifera – Composition biotique du peuplement des invertébrés. Vie Milieu. 1973;23:229–249. [Google Scholar]
- Borror D.J., White R.E. Laprairie; 1991. Les insectes de l’Amérique du Nord (au nord du Mexique). Broquet (éd.) p. 408. [Google Scholar]
- Bozbek T., Ozbek N., Sezener V., Erdogan O., Yavas I., Unay A. Natural crossing and isolation distance between cotton genotypes in Turkey. Sci. Agric. 2008;65:314–317. [Google Scholar]
- Burill R.M., Dietz A. The response of honey bees to variations in solar radiation and temperature. Apidologie. 1981;12:319–328. [Google Scholar]
- Chastain T., Young W. Vegetative plant development and seed production in cool-season perennial grasses. Seed Sci. Res. 1998;8:295–301. [Google Scholar]
- Cheikh T., Emile V.C., Saliou D., Mbaye D., Ousmane N., Ndiaga C., Mbacké S. Senna occidentalis L., une plante prometteuse dans la lutte contre Caryedon serratus Ol. (Coleoptera, Bruchidae), insecte ravageur des stocks d’arachide au Sénégal. Int. J. Biol. Chem. Sci. 2015;9:1399–1418. [Google Scholar]
- Chibuzor O.O., Obioma C.O. Mechanism of insecticidal action of oil extracted from the leaves of Cassia occidentalis. Asian J. Agric. Res. 2018;12:19–24. [Google Scholar]
- Conti B., Benelli G., Flamini G., Cioni P.L., Profeti R., Ceccarini L., Macchia M., Canale A. Larvicidal and repellent activity of Hyptis suaveolens (Lamiaceae) essential oil against the mosquito Aedes albopictus Skuse (Diptera: Culicidae) Parasitol. Res. 2012;110:2013–2021. doi: 10.1007/s00436-011-2730-8. [DOI] [PubMed] [Google Scholar]
- Delvare G., Arbelenc H.P. 1989. Les insectes d’Afrique et d’Amérique tropicale : clés pour la reconnaissance des familles. CIRAD (ed.), Montpellier; p. 297. [Google Scholar]
- Demarly Y. Masson; Paris: 1977. Génétique et amélioration des plantes; p. 577. [Google Scholar]
- Diguir B.B., Pando J.B., Fameni T.S., Tchuenguem F.-N. Pollination efficiency of Dactylurinas taudingeri (hymenoptera: Apidae) on Vernonia amygdalina (Asteraceae) Florets at Dang (Ngaoundéré, Cameroon) IJRSAS. 2020;6:22–31. [Google Scholar]
- Djonwangwe D., Pando J.B., Kameni B.A.S., Bella M.M.A., Tchuenguem F.F.-N., Messi J. Impact des activités de butinage de Xylocopa inconstans Smith F. 1874 (Hymenoptera : Apidae) et Megachile eurymera Smith 1864 (Hymenoptera : Megachilidae) sur la pollinisation et les rendements fruiter et grainier de Vigna unguiculata (L.) Walp.1843 (Fabaceae) à Maroua, Extrême - Nord, Cameroun. Afr. Sci. 2017;13:1–17. [Google Scholar]
- Dwibedi S.K., De G.C., Dhua S.R. Correlation between vegetative parameters and yield with weed biomass of kharif rice genotypes at varying dates of sowing and systems of cultivation in Coastal Odisha. Environ. Ecol. 2017;35:35–39. [Google Scholar]
- Eardley C.D., Kuhlmann M., Pauly A. Vol. 9. ABC Taxa; 2010. Les genres et sous-genres d’abeilles de l’Afrique subsaharienne; p. 152. [Google Scholar]
- Fluri P., Frick R. Apiculture in Sweden: state and perspectives. Rev. Suisse Agric. 2005;37:81–86. [Google Scholar]
- Ghosh S., Jeon H., Jung C. Foraging behaviour and preference of pollen sources by honey bee (Apis mellifera) relative to protein contents. J. Ecol. Environ. 2020;44:1–7. [Google Scholar]
- Guèye M.T., Seck D., Wathelet J.P., Lognay G. Lutte contre les ravageurs des stocks de céréales et de légumineuses au Sénégal et en Afrique occidentale : synthèse bibliographique. Biotechnol. Agron. Soc. Environ. 2011;15:183–194. [Google Scholar]
- Immaraju J., Paine T., Bethke J., Robb K., Newman J. Western flower thrips (Thysanoptera: Thripidae) resistance to insecticides in coastal California Greenhouses. J. Econ. Entomol. 1992;85:9–14. [Google Scholar]
- INS (Institut National de Statistiques) Agriculture; 2017. Annulaire statistique du Cameroun, chapitre 13; p. 24. [Google Scholar]
- Margni M., Rossier D., Crettag P., Jolliet O. Life cycle impact assessment of pesticides on human health and ecosystem. Agric. Ecosyst. Environ. 2002;93:279–392. [Google Scholar]
- Mazi S., Adamou M., Issaya K., Jean M., Esaïe F. Impact of Amegilla calens and Apis mellifera pollination on Gossypium hirsutum var. QR1302 flowers at Tchabbal-Mounguel (Ngaoundéré, Cameroon) Open J. Ecol. 2020;10:445–459. [Google Scholar]
- MINADER . Cameroon tribune; 2017. «Campagne agricole 2017: c’est parti dans le Septentrion». N° 11355/7554. [Google Scholar]
- MINADER/DESA . 2010. Annuaire des statistiques du secteur agricole, campagnes 2007 & 2008. AGRI-STAT N°16; p. 98. [Google Scholar]
- OECD/FAO . OECD Publishing; Paris: 2016. OECD-FAO Agricultural Outlook 2016-2025. [Google Scholar]
- Ouédraogo E. Ouagadougou CEAS; 2004. L’utilisation des insecticides naturels dans la protection des cultures au Burkina Faso. Communication faite au CTR de l’INERA; p. 56. [Google Scholar]
- Parys K.A., Esquivel I.L., Wright K.W., Griswold T., Brewer M.J. Native pollinators (hymenoptera: anthophila) in cotton grown in the gulf south, United States. Agronomy. 2020;10:698. 1– 4. [Google Scholar]
- Rezaei M., Khaghani R., Moharramipour S. Insecticidal activity of Artemisia sieberi, Eucalyptus camaldulensis, Thymus persicus and Eruca sativa oils against German cockroach, Blattella germanica (L.) J. Asia Pac. Entomol. 2019;22:1090–1097. [Google Scholar]
- Sabo A.V., Knezevic P. Antimicrobial activity of Eucalyptus camaldulensis Dehn. plant extracts and essential oils: a review. Ind. Crop. Prod. 2019;132:413–429. doi: 10.1016/j.indcrop.2019.02.051. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Sharma G.P., Purnima R., Raghubanshi A.S. Hyptis suaveolens: an emerging invader of Vindhyan plateau, India. Weed Biol. Manag. 2009;9:185–191. [Google Scholar]
- SODECOTON . 2019. Direction de la production agricole. Fiche portant organisation des traitements insecticides. Garoua, Cameroun 2019/2020; p. 14p. [Google Scholar]
- Sreekanth Field evaluation of certain leaf extracts for the control of mussel scale (Lepidosaphes piperis Gr.) in Black pepper (Piper nigrum L.) J. Biopestic. 2013;6:1–5. [Google Scholar]
- Tchuenguem F.F.-N. Université de Yaoundé I; 2005. Activité de butinage et de pollinisation d’Apis mellifera adansonii Latreille (Hymenoptera: Apidae, Apinae) sur les fleurs de trois plantes à Ngaoundéré (Cameroun): Callistemon rigidus (Myrtaceae), Syzygium guineense var. macrocarpum (Myrtaceae) et Voacanga africana (Apocynaceae) p. 103. Thèse de Doctorat d’Etat. [Google Scholar]
- Tchuenguem F.F.-N., Messi J., Pauly A. Activité de Meliponula erythra sur les fleurs de Dacryodes edulis et son impact sur la fructification. Fruits. 2001;56:179–188. [Google Scholar]
- Tchuenguem F.F.-N., Messi J., Brückner D., Bouba B., Mbofung G. Foraging and pollination behaviour of the African honey bee (Apis mellifera adansonii) on Callistemon rigidus flowers at Ngaoundéré (Cameroon) J. Cameroon Acad. Sci. 2004;4:133–140. [Google Scholar]
- Yadav J.P., Arya V., Yadav S., Panghal M., Kumar S., Dhankhar S. Cassia occidentalis L.: a review on its ethnobotany, phytochemical and pharmacological profile. Fitoterapia. 2010;81:223–230. doi: 10.1016/j.fitote.2009.09.008. [DOI] [PubMed] [Google Scholar]
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Data Availability Statement
Data included in article/supp. material/referenced in article.