Soil samples were collected from various farm sites (where multiple plants were planted) in the Samarkand region of the Republic of Uzbekistan—where pesticides (chlorpyrifos and cypermethrin) have been used for many years. Soil samples were taken from depths of 0–20 cm using the envelope method and placed in sterile bags. Under laboratory conditions, the soil was cleared of all additional parts (large stones, plant debris, etc.) and filtered through a stainless-steel sieve with a diameter of 2 mm.

The cypermethrin standard (purity 97), acetone, and all other substances and reagents were chemically pure and commercially available. Stock solutions (40 $\pm$ 0.05 mg/kg, 80 $\pm$ 0.02 mg/kg) were prepared using acetone. A Mettler Toledo AG pH meter (8603, Mettler Toledo, Schwerzenbach, Switzerland) was used. The following nutrient media were used to grow the microorganisms: MPA, MPB (HiMedia Laboratories Private Limited, Maharashtra, India), mineral salt medium (MSM) (pH 6.8–7.0), containing (g/L) K${}_2$HPO${}_4$: 1.5, KH${}_2$PO${}_4$: 0.5, NaCl: 0.5, (NH${}_4$) ${}_2$SO${}_4$: 0.5, MgSO${}_4$ • 7H${}_2$O: 0.2, and 1 mL of trace element solution. The microelements solution consisted of (g/L) H${}_3$BO${}_3$: 5.0, Na${}_2$MoO${}_4$ • 2H${}_2$O: 5.0, MnSO${}_4$ • 4H${}_2$O: 3.0, KI: 0.5, NaBr: 0.5, ZnSO${}_4$ • 7H${}_2$O: 0.2, and Al${}_2$(SO${}_4$)3 • 18H${}_2$O: 0.3.

The collected soil samples were mixed and additionally contaminated with cypermethrin, then kept in a thermostat at 30 °C for 2 months. After a month, 10 g of soil was added to Erlenmeyer flasks containing nutrient broth with cypermethrin and incubated on a rotary shaker at 30 °C with a rotation speed of 150 rpm for 48 hours. On day 5, appropriate dilutions were prepared from the enrichment culture and added to agar + cypermethrin plates. The grown individual colonies were subcultured on MSM plates supplemented with higher concentrations of cypermethrin.

Identification of bacteria was carried out by studying morphological and cultural properties, Gram-staining, and Matrix-Assisted Laser Desorption/Ionzation Time of Flight Mass Spectrometry (MALDI-TOF MS) analysis. The 16S rRNA method determined the nucleotide sequences to ensure a more accurate identification.

First, a nutrient broth was prepared, and a bacterial culture was added. Then, the broth was grown at 30 °C for 12 hours. Next, bacterial DNA was isolated from the bacterial culture grown in 10 mL nutrient broth using the RIBO-prep (InterLabServis, Moscow, Russia) reagent kit. DNA extraction was performed according to the protocol provided in the kit. Extracted DNA samples were analyzed on 0.9% agarose and a spectrophotometer before storing at –20 °C. PCR was used to amplify the 16S rRNA gene, which had been selected for molecular genetic identification of bacterial cultures. The following primers were used to amplify the 16S gene: 5${}^{\prime }$-AGAGTTTGATCCTGGCTCAG-3${}^{\prime }$ and 5${}^{\prime }$-GGTTACCTTGTTACGACTT-3${}^{\prime }$ [23]. The total volume of the amplification reaction was 20 µL, and a ready-made lyophilized kit of PCR core (Isogene, Russia) was used. Primers (2 µL at 5 pmol/µL) were added alongside 2.5 µL free nucleotides and 2 µL of DNA at 20 ng/µL. Enzymes and free nucleotides were acquired in a ready-made kit and placed separately in each test tube in a lyophilized form. Then, 10 µL of buffer and up to 20 µL of deionized water were added. The reaction program was performed using the following conditions: initial denaturation at 95 °C for 5 minutes, then 35 cycles of 95 °C for 20 seconds, 57 °C for 20 seconds, and 72 °C for 40 seconds before a final denaturation step of 72 °C for 3 minutes. The PCR product was analyzed using electrophoresis on a 2% agarose gel. The PCR product was purified using the GFX™ PCR DNA and Gel Band Purification kit (Thermo Fisher, Waltham, MA, USA) and its concentration was measured on a Qubit 2.0 (Invitrogen, Carlsbad, CA, USA) apparatus. The purified PCR product was subjected to a sequencing reaction using the BigDye Terminator v3.1 Cycle Sequencing kit (Thermo Fisher). The sequencing product was purified using the BigDye XTerminator Purification kit and loaded into the sequencer. Sequencing reactions and sequencing product purification procedures were performed according to kit instructions. The resulting sequence product was processed in the Codon Code Aligner software and compared (BLAST) to the National Center for Biotechnology Information (NCBI) database. The resulting sequence was deposited in the international NCBI database and registered with the corresponding number (GenBank: OL587509.1).

The PDB-3 strain was introduced into soil containing 80 $\pm$ 0.02 mg/L cypermethrin at various temperatures (25, 30, 35, 40 °C) and PDB-3 optical densities (optical densitys (ODs) = 0.05 $\pm$ 0.02; 0.1 $\pm$ 0.04; 0.15 $\pm$ 0.05; 0.2 $\pm$ 0.05). To study the effect of the initial pesticide concentration, cypermethrin was added in the following concentrations: 80 $\pm$ 0.02, 120 $\pm$ 0.4, 160 $\pm$ 0.01, and 200 $\pm$ 0.05 mg/L. The residual cypermethrin concentration was determined by Gas chromatograohy-mass spectrometry (GC–MS).

A test culture was grown for 24 hours at a ratio of 50:1 and added to sterile soil contaminated with cypermethrin. The cell titer of the culture fluid was 10${}^8$ cells/mL. Every 3 days, the soil was rinsed with sterile distilled water.

Studies on the biodegradation of cypermethrin by the isolated culture were conducted using sterile soils. An initial cypermethrin concentration of 80 $\pm$ 0.02 mg/kg was added to soil samples (100 g) using an acetone-based cypermethrin solution. Initially, the prepared solution was added to a small part (15–20 g) of the soil, which was then mixed with the remaining soil after the solvent had evaporated. Soil samples were inoculated and incubated in a thermostat at 30 °C. The tests were carried out in triplicate. The control was uninoculated sterile soil with cypermethrin. The duration of the experiment was 20 days.

Cypermethrin concentrations were determined using an Agilent 8890B gas chromatograph mass spectrometry with split and splitless evaporators, which was used in conjunction with an Agilent 5977B series GC/MS in SIM, SCAN, and electron impact ionization (EI) modes. Analysis conditions: Gas chromatography analysis parameters. Analytical column HP: 5 ms; Ultra Inert: 30 m • 250 µm • 0.25 µm. Injection volume of 1 µL; Splitless injection mode. Evaporator temperature 280 °C UI liner, splitless, single throat, fiberglass Sputtered Gasket Gold plated, The evaporator temperature was 280 °C. Hydrogen was used as the Ccarrier gas Hydrogen, and a constant flow, of 1.2 mL/min. The thermostat program was 60 °C for 1 minute, then 40 °C/min to 170 °C, then 10 °C/min to 310 °C, then hold for 2 minutes. The temperature in the transport line was 280 °C. Data collection mode: SIM, SCAN. Gain factor 1.00. Source temperature: 250 °C. Quadrupole temperature: 150 °C.

Statistical analysis and exponential curve fitting were performed using Origin 8.6 software (Microcal Software Inc., Northampton, MA, USA). Results were expressed as the mean $\pm$ SE. One-way ANOVA was performed to determine the statistical significance of the results.

To isolate microorganisms resistant to the insecticide cypermethrin, we used soil from various agricultural plots in the Samarkand region, which had been treated with pesticides chlorpyrifos, cypermethrin, and others for many years. Under laboratory conditions, soil samples were also contaminated with cypermethrin at 40 $\pm$ 0.05 mg/kg of soil. The treated samples were kept in a thermostat for 2 months at 30 °C to allow the microorganisms to adapt to the pesticide. Then, the samples (10 g of soil) were added to Erlenmeyer flasks containing nutrient broth with cypermethrin and incubated on a rotary shaker at 150 rpm at 30 °C for 48 hours. As a result of such passages, microorganisms resistant to these pesticide concentrations were isolated. Nine isolated microorganisms could grow and multiply on a medium containing cypermethrin. Next, microorganisms were selected among the isolated microorganisms to determine the decomposition of cypermethrin in the soil.

The results showed that isolate 3 was the most effective at degrading cypermethrin. This microorganism was isolated from soil brought from an orchard. In further studies, this isolate was selected to determine the effective degradation of high concentrations of cypermethrin.

Under laboratory conditions, morphological and cultural properties, some physiological and biochemical properties, and the movements of living cells were studied under a microscope. The cells are rod-shaped, size 1.2–2.0 µm, solitary, and on MPA, they form smooth convex, shiny colonies, are white–gray in color, 2–2.5 mm in diameter, do not form spores, and have a pH of 6.9–7.2. Gram-staining indicated that this strain is a Gram-negative bacterium (Fig. 1). MALDI–TOF MS analysis was also performed.

Fig. 1.

Gram-staining.

The obtained results tentatively suggest that this strain is Ochrobactrum intermedium. To ensure a more accurate identification, the 16S rRNA nucleotide sequence was determined. The results show 100% similarity to the species Ochrobactrum intermedium (Fig. 2).

Fig. 2.

Phylogenetic tree of Ochrobactrum intermedium strain PDB-3.

The 16S rRNA gene sequence data of Ochrobactrum intermedium strain PDB-3 were processed using UniGene Ver35 and Chromas software, and the low-confidence peaks were removed. Then, the DNA sequences were analyzed against the NCBI nucleotide database using BLAST. Highly similar DNA sequences were aligned using the MegaX program and the ClustalW algorithm. A phylogenetic tree was constructed using the Neighbor-Joining algorithm in the MegaX program.

Thus, strain PDB-3 Ochrobactrum intermedium showed very close similarity (100%) to strains of Ochrobactrum intermedium. This indicates that the strain under study belongs to the phylum Ochrobactrum intermedium. The strain was registered in the NCBI database: GenBank: OL587509.1.

The influence of external factors on cypermethrin decomposition was studied under laboratory conditions. Strain PDB-3 was added to soil containing 80 $\pm$ 0.02 mg/kg cypermethrin. The influence of temperatures of 25 °C, 30 °C, 35 °C, and 40 °C was studied. Each option was kept in a thermostat. The optimal temperature was identified as 30 °C, in which the cypermethrin degradation reached 100%. A decrease or increase in temperature negatively affected the decomposition process (Fig. 3A). Subsequently, studies were performed to determine the effect of the optical density of the PDB-3 strain on the decomposition of cypermethrin. Strain PDB-3 was added to sterile soil in the following optical densities: (OD = 0.05 $\pm$ 0.02; 0.1 $\pm$ 0.04; 0.15 $\pm$ 0.05; 0.2 $\pm$ 0.05) (Fig. 3B). OD was measured using a spectrophotometer [24, 25, 26]. Decomposition proceeded slower at the lower OD values. The results obtained confirm that an increase in microbial mass has a positive effect on the decomposition process. All studies were carried out in triplicate. At the end of the experiment, the residual concentration of cypermethrin was determined by GC–MS. Our next step was to determine the effect of the initial concentration of cypermethrin on the biodegradation process. Strain PDB-3 was actively multiplied in a medium supplemented with cypermethrin at a concentration of up to 80 mg/kg and was completely degraded. Based on this, the concentration was increased to the following values: 80 $\pm$ 0.02, 120 $\pm$ 0.4, 160 $\pm$ 0.01, and 200 $\pm$ 0.05 mg/L (Fig. 3C). It has been established that as the concentration increased, the speed of degradation process reduced.

Fig. 3.

Determination of the influence of some external factors on the degradation of cypermethrin. (A) Temperature. (B) Cypermethrin concentration. (C) Optical density.

The potential for maximum microbial degradation of pesticides depends entirely on optimal environmental conditions, such as initial concentration [27], pH, temperature, additional energy sources, and inoculum concentration [28]. Biotechnological processes based on microorganisms are usually influenced by environmental factors [29, 30]. Lysinibacillus cresolivuorans strain HIS7 was isolated from contaminated soil. Thus, the degradation process of cypermethrin was studied using this strain under the influence of various environmental factors. The optimal parameters for the biodegradation of cypermethrin were previously established as an incubation period of 8 days, inoculation volume of 3 mL, temperature of 35 °C, pH 7, and an additional source of carbon and nitrogen, which increased decomposition from 57.7% to 86.9%. In soil, the HIS7 strain degraded cypermethrin to 93.1% within 42 days [31].

Studies on the biodegradation of cypermethrin were carried out in sterile soils. The soil was dried in laboratory conditions, and all unnecessary parts were removed, e.g., large stones, plant debris, etc. Then, it was sterilized in an autoclave at 121 °C for 45 minutes. Cypermethrin solutions were prepared using acetone and added to a small part of the soil (approximately 15–20% of the total soil mass); the soil was thoroughly mixed with the cypermethrin solution (80 $\pm$ 0.02 mg/kg) and then mixed with the remaining soil. Subsequently, the cultural liquid of the PDB-3 strain (OD = 0.2 $\pm$ 0.05) was added to the soil. The studies were carried out in triplicate. The experiments lasted 20 days. Humidity plays an important role in the reproduction and development of microorganisms because when humidity decreases, the growth and reproduction of microorganisms decrease, negatively affecting the biodegradation process. Therefore, to maintain humidity (about 60–70%), the test soil samples were rinsed with sterile distilled water every 3 days. Soil samples were collected every 4 days for chromatographic analysis. The GC–MS results show the presence of cypermethrin as a peak appeared in the soil samples at a retention time of 19.357 min (Fig. 4).

Fig. 4.

Initial Gas chromatograohy-mass spectrometry (GC–MS) chromatogram of cypermethrin.

Thereafter, this peak gradually decreased and was undetectable in the soil samples on day 20. In the control sample, virtually no changes were observed during the experiment. Based on the chromatographical analyses, the decrease in the initial concentration of cypermethrin (Fig. 5A) and the percentage of degradation (Fig. 5B) were calculated.

Fig. 5.

Cypermethrin degradation using PDB-3. (A) Decrease in initial concentration. (B) Degradation percentage.

Fig. 5 shows that strain PDB-3 successfully decomposes 80 $\pm$ 0.02 mg/kg of cypermethrin in the soil compared to the control sample. Initially, the decomposition rate was somewhat slower, although an increase in microbial biomass in the soil environment, starting from day 8, accelerated the degradation of cypermethrin. The percentage of cypermethrin degradation on day 4 was 11.25 $\pm$ 0.03%; on day 8: 27.5 $\pm$ 0.05%; on day 12: 62.5 $\pm$ 0.05%; on day 16: 90 $\pm$ 0.02%. Cypermethrin residues were not detected in our soil samples on day 20, which confirms that the initial concentration was completely degraded. Comparatively, the degradation percentage was 12.3 $\pm$ 0.05% in the non-inoculated control soil.