Table 3.
Remediation Strategy | Consortial Source and Specifics | Bacterial species | Heavy Metals Adsorbed | Remediation Efficiency | Reference |
---|---|---|---|---|---|
HOMOGENOUS CONSORTIAL EPS | Methylobacterium organophilum | Copper,Lead | 21% Cu2+,18% Pb2+ removal from 0.04 ppm initial metal load | [41] | |
Herminiimonas arsenicoxydans | Arsenic | Upto 5 mmol/L metal ion uptake | [54] | ||
Activated sludge isolates | Pseudomonas sp | Copper | N.A | [48] | |
Marine bacteria | Enterobacter cloaceae | Cadmium,Copper, Chromium | 65% Cd2+,20% Cu2+; 75% Cr6+ reduction from 100 ppm initial metal load | [30], [34] | |
Shewenella oneidensis | Cadmium | 80% Cd2+ removal | [31] | ||
Cyanobacteria | Anabaena spiroides | Manganese | 8.52 mg Mn2+/g EPS | [23] | |
Gloeocapsa gelatinosa | Lead | 82.22 ± 4.82 mg Pb2+/g CPS | [80] | ||
Calothrix marchica | Lead | 65 mg Pb2+/g CPS | [82] | ||
Cyanospira capsulate (Cells + EPS) | Copper | 115 mg Cu2+/g EPS at 12.3 ppm initial metal load | [17] | ||
Nostoc PCC7936 | Copper | 85.0 ± 3.2 mg Cu2+/g EPS at 12.3 ppm initial metal load | |||
Gloeocapsa calcarea | Chromium | 36 mg Cr6+/g EPS at 20 ppm initial metal load | [87] | ||
Nostoc punctiforme | Chromium | 90.05 mg Cr6+/g EPS | |||
Lyngbya putealis | Chromium | 157 mg/g of EPS Cr6+at 30 ppm initial load |
[42] | ||
Pseudomonas putida | Cadmium | 80% Cd2+ at 10 ppm initial | [39] | ||
Rhizobium. tropici | Cadmium | 80% Cd2+ at 10 ppm initial | |||
Soil isolates | Bacillus firmus | Lead, Copper, Zinc | 1103 mg Pb2+/g EPS (98.3%,), 860 mg Cu2+/g EPS (74.9%), 722 mg Zn2+/g EPS (61.8%) |
[84] | |
Azotobacter chroococcum | Lead,Mercury | 40.48% Pb2+(33.5 mg Pb2+/g of EPS); 47.87% Hg2+ (38.9 mg of Hg/g EPS) |
[79]. | ||
Ensifer meliloti | Lead, Nickel, Zinc | 89% Pb2+, 85% Ni2+, 66% Zn2+ reduction from 50 ppm initial load |
[47] | ||
GRAS status | Paenibacillus jamilae | Lead, Cadmium | 200–300 mg Pb2+/g EPS, 21 mg Cd2+/g of EPS |
[60], [75] | |
Paenibacillus polymyxa | Copper | 1602 mg Cu2+/g EPS | [1] | ||
Lactobacillus plantarum | Lead | 276.44 mg Pb2+/g EPS, at 1000 ppm initial metal load | [21] | ||
HETEROGENUS CONSORTIAL EPS | Activated sludge mixed consortia | Zinc, Copper, Chromium Cadmium | 85 to 95% reduction from initial metal load of 10–100 ppm | [50] | |
Lead Cadmium | N.A | [29] | |||
Gram negative microbial consortia | Zinc, lead, Chromium, Nickel, Copper, Cadmium Cobalt |
75 to 78% reduction in metal load | [28] | ||
Hydrocarbon contaminated water microbial consortium | Zinc, Copper, Cadmium | 87.12% Cd2+; 19.82% of Zn2+; 37.64% of Cu2+ reduction from 1 ppm initial metal load | [56] | ||
DEAD BIOMASS EPS | Activated sludge isolate | Ochrobactrum anthropi | Chromium, Cadmium, Copper | 57.8 mg Cr6+/g EPS at initial metal load of 280 ppm, 26 mg Cu2+/g EPS at initial metal load of 91.6 ppm 29.5 mg Cd2+/g EPS at 100.6 ppm initial metal load |
[71] |
Bacillus cereus | Chromium | 89.87% reduction from initial metal load of 50 ppm | [92] | ||
Bacillus pumilus | Chromium | 89.23% reduction from initial metal load of 50 ppm | |||
Pantoea agglomerans | Chromium | 85.5% reduction from initial metal load of 50 ppm | |||
IMMOBILIZED EPS | Alginate bead immobilized | Chryseomonas luteola | Cadmium, Cobalt, Copper, Nickel |
64.10 mg Cd2+/g EPS 55.25 mg Co2+/g of EPS 1.989 mmol Cu2+/g EPS 1.224 mmol Ni2+/g EPS |
[72], [73] |
Agar Beads immobilized | Paenibacillus polymyxa | Lead | 111.11 mg Pb2+/g EPS | [32] | |
MODIFIED EPS | Phosphorylated bacterial EPS (cellulose) | Acetobacter | Lead, Copper, Manganese, Zinc, Cobalt | 90% reduction from initial metal load of 0.1 mmol/dm3 (Fe3+ > Cu2+ > Mn2+ > Zn2+; Co2+) |
[70] |