Document Type : Research papers
Authors
1 Plant Protection Dept., Faculty of Agric. (Saba Basha) – Alex. Univ., Egypt.
2 Plant Protection Research Institute, Agriculture Research Center, Alexandria, Egypt.
Abstract
Keywords
Main Subjects
Mollusks are the second biggest phylum in the animal kingdom, accounting for a significant portion of the world's fauna. Only the Gastropoda have successfully invaded land among all classes of mollusks (Sandeep et al. 2012). Mollusks are a varied category of invertebrate animals having soft, unsegmented bodies. (O’Connor and Crowe 2005). Terrestrial gastropods are classified as agricultural pests because they damage crops and cause financial loss by eating the leaves, roots and fruits of plants, as well as numerous horticultural plants ornamental plants, wood trees, and newly sown lawn grasses. They also decrease crop quality and contaminate agricultural products with their bodies, feces, or slime (Barker, 2002; Eshra, 2004; Awad et al., 2012; Puizina et al., 2013; Awad, 2014; Ali, 2017; Hussein and Sabry, 2019). As a following result, an unpleasant odor develops, preventing both humans and animals from eating these contaminated plants (Shetaia et al., 2009).
Today's gastropods in Egypt are significantly more harmful than they were in the past (Mortada, 2002). In many Egyptian governorates, the land snails Eobania vermiculata, Theba pisana, Helicella vestalis, Monacha obstructa, and Cochlicella acuta have been observed attacking various plantations (Kassab and Daoud, 1964; El-Okda, 1979; El-Deeb et al., 1996; Abu-Bakr, 1997; Eshra, 2004). Both E. vermiculata and T. pisana are significant agricultural pests that inflict significant damage in agriculture and horticulture. They are particularly destructive in locations where they may find the right circumstances for fast growth (Puizina et al. 2013).
Methomyl and other oxime-carbamates insecticides, which are used to control snails, are moderately poisonous to land snails but extremely hazardous to mammals and beneficial insects (Hussein et al., 1994; Radwan and El-Zemity, 2007; Salama et al., 2005; Abdelgaleil, 2010). Because of the aforementioned drawbacks of conventional pesticides, the request for safe and environmentally friendly alternative molluscicides is critical in order to protect human health and the environment.
Essential oils are green insecticides that are non-toxic to mammals and other species (Ferreira et al., 2009; Stroh et al., 1998), No residue-related problems exist (Misra and Pavlostathis, 1997). Essential oils and their constituents are gaining popularity as safe alternatives to pesticides for controlling a wide range of pests, including gastropods, acting as insecticides (Isman et al., 2001; Hussein, 2005; Radwan et al., 2008; Pavela, 2015; Klein et al., 2020; Owolabi et al., 2020).
The biological management of land snails or slugs utilizing microbial agents, i.e., bacteria, is an alternative strategy that gained more attention a few years ago and offers efficient control against land snails. Bacillus thuringiensis (Bt) is a soil gram-negative bacteria that generates pest-toxic compounds. Recently, it has emerged as one of the biological control agents for a number of insect pests (Dean, 1984). Numerous studies have examined this bacterium's toxicity toward a some land snails in Egypt (Zedan et al., 1999; Azzam and Belal, 2003; Kramarz et al., 2007).
The main aim of this work is to evaluate the molluscicidal effect of A. indica, M. piperita, essential oils and a Biopesticide formulation Biotect® 9.4%W.P, a commercial formulation of B. thuringiensis, by dipping technique application and different concentrations under laboratory conditions against the most common land snails infesting various fruit orchards: E. vermiculata, and T. pisana.
2. MATERIALS AND METHODS
2.1. MATERIALS
a. Biotect 9.4%W.Pa Commercial formulation of Bacillus thuringiensis.
b. Neem oil (Azadirachta indica) and peppermint (Mentha piperita) essential oil were purchased as pure oil from National Research Center, Dokki, Cairo, Egypt.
c. Acetone (pure) was purchased from Al-Nasr Pharmaceutical Chemicals Co. (ADWIC) (Egypt).
2.2. Experimental snails:
Adults of the brown garden snail, E. vermeculata (Müller), and the white garden snail, T. pisana (Müller), having approximately the same age and size were collected for laboratory experiments from El-Maamoura locality, Alexandria. These snails were transferred to plastic cups covered with cloth netting and maintained under laboratory conditions of 27 °C and 65% R.H. The snails were fed on lettuce leaves daily up to the initiation of tests. The snails were allowed to acclimatize to these conditions for two weeks. Dead snails were excluded as soon as possible, whenever needed.
2.3. Laboratory bioassay (Dipping leaves method)
The essential oils of each of A. indica and M. piperita, as well as the biopesticide formulation of B. thuringiensis, were tested for toxicity against E. vermiculata and T. pisana. Homogenous disks of lettuce leaves were dipped in a series of each of A. indica, M. piperita, and B. thuringiensis prepared concentrations for 5 min and left for dryness. The treated lettuce disks were transferred into plastic cups, and 10 adult snails were placed in each cup. Each treatment concentration had three replicates; results were detected along three different periods; after 24, 48, and 72 h., untreated lettuce disks were used as a check treatment. Mortality percentages were recorded after 24, 48, and 72 h post-treatment.
3. Statistical analysis.
Lethal effect was evaluated as percentages of cumulative daily mortality, corrected for mortality in the control variant according to Abbott's formula (Abbott, 1925) as follows:
Corrected Mortality =
The statistical toxicity indices, LC50 and LC95, were estimated as described by Finney (1952), via the LdP line program (Ehab Soft, Cairo, Egypt).
3. RESULTS AND DISCUSSION
3.1. Efficiency of neem; peppermint essential oilsand Biotect® (commercial formulation B. thuringiensis)against T. pisana and E. vermiculata snails.
The toxicity of (neem oil) against T. pisana and E. vermiculata was evaluated. The calculated LC50 values for T. pisana were 2.66, 1.29, and 0.87% after 24, 48, and 72hrs post treatment, respectively (Table, 1). Also, the extracted LC50 values for E. vermiculata were 5.35, 4.02, and 2.26% after 24, 48, and 72 h post treatment, respectively. Noticeably, the toxicity of neem oil increased as the time of exposure increased for both snails T. pisana and E. vermiculata. The obtained results indicated that neem oil was the high toxic against T. pisana than E. vermiculata snails.
The exhibited data in Table (2) show that tested peppermint oil was more toxic upon adults of T. pisana than E. vermiculata snails, with LC50 values of 6.24, 3.19, and 2.37 % after 24, 48, and 72 hours, respectively. While, its deduced LC50 values against E. vermiculata were 15.29, 11.07, and 9.523% after 24, 48, and 72hrs respectively. These results elucidate that the extracted LC50 values of peppermint oil decreased with increasing the exposure time and indicated its higher toxicity against T. pisana than E. vermiculata snails.
Table (1): The calculated LC50 values of neem oil on adults of T. pisana and E. vermiculata snails under laboratory conditions.
Land snails species |
Exposure Time (hr)
|
LC50 %
|
Confidence Limits at 50% of probability |
LC95 %
|
Confidence Limits at 95% of probability |
Slope ±Variance |
X2
|
||
Lower |
Upper |
Lower |
Upper |
||||||
T. pisana |
24 |
2.66 |
2.18 |
3.80 |
11.6 |
6.80 |
32.4 |
2.58±0.42 |
1.03 |
48 |
1.29 |
1.07 |
1.63 |
16.7 |
9.05 |
45.7 |
1.48±0.19 |
0.91 |
|
72 |
0.87 |
0.73 |
1.04 |
9.69 |
5.98 |
20.7 |
1.57±0.19 |
7.41 |
|
E.vermiculata |
24 |
5.35 |
3.25 |
6.45 |
52.2 |
49.3 |
55.1 |
1.66±0.71 |
0.37 |
48 |
4.02 |
2.57 |
9.30 |
102.9 |
30.25 |
105.3 |
1.17±0.20 |
5.15 |
|
72 |
2.26 |
1.60 |
4.16 |
51.5 |
17.7 |
60.4 |
1.21±0.20 |
0.63 |
Table (2): The estimated LC50 values of peppermint oilon adults of T. pisana and E. vermiculata under laboratory conditions.
Land snails species |
Exposure Time (hr) |
LC50 % |
Confidence Limits at 50% of probability |
LC95 % |
Confidence Limits at 95% of probability |
Slope ±Variance |
X2
|
||
Lower |
Upper |
Lower |
Upper |
||||||
T. pisana |
24 |
6.24 |
5.62 |
7.8 |
56.23 |
33.33 |
139.9 |
1.76±0.25 |
1.38 |
48 |
3.19 |
2.55 |
3.76 |
24.99 |
17.48 |
45.01 |
1.84±0.24 |
7.64 |
|
72 |
2.37 |
1.81 |
2.85 |
15.27 |
11.69 |
23.22 |
2.03±0.25 |
4.00 |
|
E.vermiculata |
24 |
15.29 |
12.01 |
26.27 |
62.91 |
33.29 |
285.1 |
2.68±0.56 |
0.73 |
48 |
11.07 |
9.32 |
14.45 |
61.92 |
37.23 |
149.6 |
2.2±0.31 |
1.55 |
|
72 |
9.523 |
7.994 |
12.41 |
75.24 |
41.78 |
215.5 |
1.83±0.27 |
2.37 |
The included data in Table (3) represents the extracted LC50 values for the tested commercial formulation of B. thuringiensis (Biotect®) against E. vermiculata and T. pisana snails; their confidence limits, slope, and X2 values. The estimated LC50 values of Biotect® against T. pisana were 9.59, 15.7, and 8.81% after 24, 48, and 72hrs post treatment; while for E. vermiculata these values comprised 9.98, 16.3 and 2.16% after 24, 48, and 72hrs post treatment. The lower LC50 values were obtained with increasing exposure. The toxic efficiency of Biotect® was higher against E. vermiculata than T. pisana snails.
Table (3): The calculated LC50 values of experimental commercial formulation of B. thuringiensis (Biotect®) on adults of T. pisana and E. vermiculata snails under laboratory conditions.
Land snails species |
Exposure Time (hr)
|
LC50 %
|
Confidence Limits at 50% of probability |
LC95 %
|
Confidence Limits at 95% of probability |
Slope ±Variance |
X2
|
||
Lower |
Upper |
Lower |
Upper |
||||||
T. pisana |
24 |
9.59 |
6.77 |
25.7 |
53.5 |
21.7 |
80.5 |
2.20±0.56 |
0.00 |
48 |
15.7 |
8.08 |
20.8 |
926.5 |
113.9 |
982.0 |
0.93±0.27 |
0.45 |
|
72 |
8.81 |
5.99 |
21.2 |
189.5 |
53.6 |
200.5 |
1.23±0.27 |
0.50 |
|
E.vermiculata |
24 |
9.98 |
6.89 |
21.9 |
115.2 |
41.3 |
145.3 |
1.54±0.30 |
0.23 |
48 |
16.3 |
10.5 |
20.8 |
9584 |
5214 |
9863 |
0.59±0.24 |
8.45 |
|
72 |
2.16 |
1.74 |
2.57 |
28.2 |
15.6 |
86.4 |
1.47±0.24 |
1.81 |
The aforementioned results agree with those recorded by Abobakr et al. (2022) whoinvestigated the fumigant toxicity and feeding deterrent effect of extracted essential oils from Lavandula dentata, Juniperus procera, and Mentha longifolia against the land snail M. obstructa. It was found that the three tested EOs exhibited a strong feeding deterrent effect at sublethal concentrations. Also, Gabr et al. (2006) found that several neem formulations (Neemix4.5®) had molluscicidal action against M. obstructa and E. vermiculata snails in the laboratory and in the field. Also, Eshra et al. (2016) discovered that lavandula dentata oil derived from the leaves and flowers was fumigantly poisonous to T. pisana snails, with an LC50 value of 16.3 µl/L air. Boufatoum and Abu Bakri (2013) proved that the oil extract of Citrullus coloeynhis with a concentration of 100 g had the greatest efficacy against T. pisana. Furthermore, the present results are in accordance with those reported by El-Zemity and Radwan (2001), who used peppermint, caraway, thyme, and chenopodium oils topically on adults of T. pisana and discovered that the oils had strong molluscicidal activity against the snails after a contact toxicity assay for 48 h .
In addition, the foregoing results of the biocide, B. thuringiensis, are in agreement with the findings of Zedan et al. (1999) who investigated the effectiveness of B. thuringiensis var israelensis against the land snail M. obstructa. They determined that the bacterial formulation was superior to methomyl. On the contrary, Genena et al. (2008) found that when E. vermiculata and Monacha cantiana snails were treated with eight strains of B. thuringiensis, none of the strains had any detrimental effect or caused death in each snail species. Also, Kramarz et al. (2007) conducted study on the Bt toxin (Cry1Ab's) impact upon the land snail Helix aspersa under laboratory environment, the toxin had no detrimental effects on the snail throughout the following stages of life.
CONCLUSION
The aforementioned study of the molluscicidal activity using neemand peppermintessential oils and the commercial formulation of Bacillus thuringiensis as biopesticide, were tested for their molluscicidal activity against two terrestrial snails: E. vermiculata and T. pisana. The bioassay technique was performed using the dipping leaves method against both terrestrial snails under laboratory conditions. The obtained results indicated that neem and peppermint oils were more toxic against T. pisana than E. vermiculata snails. On the other hand, the toxicity of B. thuringiensis was more effective against E. vermiculata than T. pisana snails. Essential oils and Bt bioprepation as biopesticide constituents are gaining increasing interest for use as safe alternatives to pesticides for controlling various pests, including gastropods.
الملخص العربي
فعالية مركبين كيميائيين نباتيين ومستحضر حيوي على القواقع الأرضية السائدة في محافظة الإسكندرية ، مصر.
حسن على عبدالحميد مصباح 1 أحمد كمال خليل مراد 1 السيد حسن عشره 2 و مسعودة رمضان الزروق1
1- قسم وقاية النبات – كلية الزراعة (سابا باشا) – جامعة الإسكندرية – مصر.
2- معهد بحوث وقاية النباتات - مركز البحوث الزراعية - الأسكندرية – مصر
أصبحت مبيدات الرخويات النباتية مثيرة للإهتمام بسبب كونها صديقة للبيئة وسهولة الوصول إليها وسهولة استخدامها. تم تقييم النشاط الابادى لزيت النيم و زيت النعناع الفلفلى العطرى و المستحضر التجارى لبكتيريا الباسيلس ثورينجينسيس كمبيد حيوي ضد قوقع الحدائق البني و قوقع الحدائق الابيض و تم عمل التقييم الحيوي باستخدام طريقة غمس الاوراق لحساب قيم التركيز المميت لـ50 % من العشيرة و 95% للقواقع ، تحت الظروف المعملية. و أشارت النتائج المتحصل عليها أن كل من زيت النيم وزيت النعناع كان اكثر فعالية ضد قوقع الحدائق الابيض عن قوقع الحدائق البنى حيث بلغ قيم التركيز المميت لـ50 % لزيت النيم بلغ 0.87 % بينما كان لزيت النعناع 2.37 % ضد قوقع الحدائق الابيض فى حين ان، بلغت قيمة التركيز المميت لـ50 % لزيت النيم بلغ 2.26% و لزيت النعناع 9.52 % بعد المعاملة ب 72 ساعة ضد قوقع الحدائق البنى ومن ناحية أخرى ، كانت بكتيريا باسيلس ثورينجينسيس أكثر فاعلية ضد قوقع الحدائق البنى عن قوقع الحدائق الابيض فبلغت قيمة التركيز المميت النصفي للقواقع المعاملة لها هو 2.16% و 8.81 % على الترتيب بعد المعاملة بـ 72 ساعة. أظهرت هذه الدراسة أنها تدعم الاستخدام الواعد للزيوت العطرية كمبيدات حيوية ضد الرخويات الضارة.