Table 3.

Microbial degradation of dichlorvos.

No.	Strain or Community	Sample Sources	Detected Metabolites	Comments	Reference
1	Cunninghamella elegans	Surroundings of sewage disposing outlet from agro-pesticide manufacturing in Owo, Nigeria	O,O-dimethyl phosphonic ester, desmethyl dichlorvos, also known as 2,2-dichlorovinyl O-methylphosphate, and O,O,O-trimethyl phosphoric ester, also known as dichlorvos (2,2-dichlorovinyl-O,O-dimethyl phosphate)	Cunninghamella elegans strain was the most dominant fungal strain in pesticide-polluted soil samples with 37 appearances in 50 samples (74% incidence), Talaromycesatro roseus had 33 appearances (66% incidence), Aspergillus oryzae had 32 appearances (64% incidence), Fusarium solani and Penicillium sp. both had 26 appearances (52% incidence).	[56]
2	Fusarium solani
3	Talaromycesatro roseus
4	Aspergillus oryzae
5	Penicillium sp.
6	Ochrobactrum intermedium DV-B31	Farmland annually sprayed with organophosphorus pesticides	No data	96.38% dichlorvos was degraded by DV-B31 in 8 days	[61]
7	Pseudomonas aeruginosa	Agricultural field inPunjab, India	No data	90% of dichlorvos was degraded in around 20 days	[58]
8	Bacillus amyloliquefaciens YP6	Phosphate mine in Guizhou Province, China	No data	53% of dichlorvos was degraded in 1 h	[62]
9	Trichoderma atroviride T23	No data	Dichloroethane and trichloroethylene	300 μg/mL dichlorvos was degraded in 120 h	[60]
10	Trichoderma atroviride mutant AMT-28	Vegetable field in Shenyang, China	No data	Dichlorvos was completely removed when treated with mycelia of AMT-28 for 7 d	[64]
11	Consortium of Pseudomonas, Xanthomonas, Sphingomonas, Acidovorax, Agrobacterium, and Chryseobacterium	Greenhouse within Xisanqi Ecological Garden, Beijing, China	No data	Dichlorvos degradation efficiency of these bacteria was 11.5%,70.0%, 78.7%, 52.6%, 66.4%, and 25.2%, respectively	[66]
12	Pseudomonas stutzeri smk	India	Free methyl and phosphate	80% of dichlorvos was degraded on 7th day of incubation	[65]