Based on the findings from scientific experiments conducted in laboratory settings in 2021, it was confirmed that the insecticidal crystal-forming bacterial culture fluids Bt
EM-54 and Bt
EM-82, which were microbiologically isolated from deceased larvae of the brown-tail moth and mountain tent caterpillar in (2020) under natural conditions, exhibited high biological efficiency ranging from 95.0% to 98.3% against brown-tail moth larvae at various stages (I-II (early), III-IV (middle), V-VII (adult)) within 10 days after spraying. The notable levels of biological effectiveness observed in laboratory conditions warranted further evaluation of these bacterial culture fluids against brown-tail moth larvae at different stages in apple orchards located in the Ujan village, through both small-scale and production experiments (Table 1 and 2). In the orchards selected for our study, the average number of brown-tail moth larvae in the I-II stages (with larval head capsule sizes of 0.4 and 0.5 mm, respectively), III-IV stages (0.7 and 0.9 mm) and V-VII stages (1.3 - 2.5 mm) per linear meter of branch reached the economic damage threshold. Overall, the average number of larvae per linear meter of branch ranged between 2.8 and 3.4. Spraying against larvae in the I-II, III-IV and V-VII stages was conducted in forests on 07.25.2021, 05.12.2022 and 05.26.2022, respectively. Results from small-scale scientific experiments (Fig 1) confirmed that local culture fluids Bt
EM-54 and Bt
EM-82 exhibited high biological efficiency of 95.2% and 96.4%, 93.5% and 95.2%, 92.8% and 93.1% against the larvae in the I-II, III-IV and V-VII stages, respectively, within 10 days after spraying. The biological efficiency indicators of standard lepidocide variants used against the same stages of these phytophagous larvae (I-II, III-IV and V-VII) during the same observation period were 95.4%, 94.2% and 93.5%, respectively. As shown in the table (Table 1), the biological efficiency indicators recorded in both experimental (Bt
EM-54, Bt
EM-82) and standard (lepidocide) treatments, measured at 3 and 7 days after spraying (ranging from 41.0% to 69.7% and 82.0% to 90.6%, respectively), were lower compared to those observed on the 10
th day after spraying. This difference can be attributed to the specific mechanism of action of Bt-type bacterial insecticides. It is noteworthy, that the indicators of biological efficiency recorded on the 10
th day in both experimental (Bt
EM-54, Bt
EM-82) and standard (lepidocide) versions, were constant until the larva reached the pupal stage.
In the days following the spray, larvae in the experimental groups treated with bacterial culture fluids gradually ceased feeding, became unresponsive to mechanical stimuli, gradually reduced in size, softened, discolored and exhibited other negative symptoms, ultimately resulting in mortality.
Microbiological examination of the deceased larvae from the experimental groups sprayed with bacterial insecticides confirmed the presence of insecticidal spore-crystal components within the partially decomposed tissues and intestinal cavities of the larvae. In some cases, bacterial vegetative cells were also detected. These findings validate that the mortality of phytophagous larvae resulted from exposure to Bt-type bacterial insecticides.
The promising results obtained from small-scale experiments paved the way for large-scale testing of local bacterial culture fluids of Bt type against brown-tail moth larvae at different stages under production conditions through large-scale spraying. Each bacterial insecticide was tested on a separate experimental site, covering an area of 2000 m
2 (0.2 hectares).
The results obtained from scientific experiments conducted under production conditions are summarized in Table 2. and that revealed the highest levels of biological efficiency for Bt-type bacterial culture fluids against brown-tail moth larvae in stages I-II, III-IV and V-VII were observed 10 days after spraying with rates of 94.1% and 95.0%, 92.4% and 94.5%, 92.1% and 93.4%, respectively. In the case of standard lepidocide, the indicators for the same groups and observation period were 95.7%, 93.1% and 92.9%, respectively.
No larval mortality was observed in the control groups of both small-scale and production experiments. The biological efficiency indicators remained consistent until the larva reached the pupal stage on the 10
th day in both experimental and standard groups. Furthermore, the biological efficiency indicators recorded on the 3
rd and 7
th days of spraying were also relatively low compared to those on the 10
th day, as outlined in the table (Table 2). In the literature, there is conflicting data regarding the viability of Bt bacterial insecticides in the soil after spraying. Some researchers stated that depending on the type of bacterial insecticide and soil composition, the crystal-forming bacteria can persist in the soil for 2 days (
Akiba, 1986). Conversely, others stated that these bacteria remain active for 1-5 months
(Ghazaryan et al., 2006; Tetreau et al., 2021) or even 1-10 years
(Li et al., 2022; Metze et al., 2023). Given these varying reports, our objective was to assess the viability of Bt
EM-54 and Bt
EM-82 isolated from the individual elements of the biocenosis, as well as Bt var.
kurstaki bacterial insecticide, which is the basis for the release of the commercial lepidocide bacterial preparation.
The results of the experiments (Fig 1) confirm that the quantities of Bt
EM-54, Bt
EM-82 and Bt var.
kurstaki bacterial insecticides that fell into the light-brown soil of the apple orchard as a result of spraying in May (initial amounts were 21.68, 18.96 and 17.48 million/g, respectively), has decreased during the following months of vegetation (June, July, August). Furthermore, the viability of these insecticides in this soil subtype was found to be 5 months after a single spraying during the vegetation period. Findings of the present work also suggest that soil-dwelling antagonists such as
Bacillus mesentericus,
Bacillus sp., Sarcina sp. and Penicillium puberulum (
Chapanyan and Sargsyan, 2018b) contribute to the reduction in the quantity of Bt-type bacterial insecticides. This phenomenon appears to influence our scientific experiment as well. Notably, the amounts of Bt
EM-54 and Bt
EM-82 insecticides recorded in September increased by 20.0% and 25.4%, respectively, compared to August.
This phenomenon can likely be attributed to the gradual adaptation of Bt
EM-54 and Bt
EM-82 insecticides to the environment, alongside the autumnal replenishment of soil nutrients from decomposing plant matter. In the case of Bt var
. kurstaki, the quantitative reduction continued in September. Ammonification, a crucial process shaping nitrogen balance in biocenosis, involves ammonia-producing microbes such as bacteria, actinomycetes and microscopic fungi. This process converts organic nitrogen into NH
3 or NH
4, which is readily absorbed by plants (
Harutyunyan, 2010). Karyagina, Kazaryan and Wang have highlighted that ammonification is a key determinant of soil fertility, with a strong positive correlation (r=0.89) observed between humus levels and soil-dwelling ammonifiers in the soil (
Karyagina, 1983;
Kazaryan, 2007;
Wang, 2017). Along with the dynamics of change in the quantity of Bt-type bacterial insecticides that fell into the soil as a result of spraying during the vegetation period, we have studied the dynamics of change in the quantity of ammonifying bacteria in the light-brown soil of apple orchards, which were either sprayed with Bt
EM-54 and Bt
EM-82 and Bt var.
kurstaki bacterial insecticides separately or not sprayed at all (control sample)
, based on which the impact of Bt bacterial insecticides on soil fertility has been assessed. Microbiological analyses (Fig 2) demonstrated fluctuations in the total quantity of ammonifying bacteria during the vegetation period both in the experimental and control plots, with peak levels in June (22.6-26.2 million/g of soil) and a decline level in September (typically 8.2-10.2 million/g of soil). The intensity of ammonification has been correlated with soil moisture, temperature, air saturation and the composition of decomposing organic matter
(Beeckman et al., 2018) as observed in our experiments. Statistical analysis of larval quantities affected by Bt insecticides, along with those found in soil due to spraying and soil-dwelling ammonifiers, revealed a consistent range of statistical error (2.7 to 5.5) and coefficient of variation (4.75% to 12.41%). These findings validate the accuracy of our scientific experiments.
The calculated values of the Student’s i test when P < 0.95 and n=5 generally ranged from 0.513 to 1.461. These values were smaller than the tabulated value of 2.571, indicating no significant statistical difference between the quantitative indices of soil-dwelling ammonifiers observed in soil samples treated with Bt bacterial insecticides compared to untreated samples.
Similarly, for all larval stages, the calculated values of Student’s i test when P0.95 and n=3 generally ranged from 0.513 to 1.461 (Fig 2) and were smaller than its tabulated value of 3.182, This confirms no significant statistical difference between the biological efficiency indicators calculated for samples treated with BtEM-54 and BtEM-82 culture fluids compared to those treated with an aqueous suspension of lepidocide (standard).