TABLE 1.
Selected recent literature on algal bioremediation of PW.
Strain | Wastewater type | Cultivation conditions | Highest biomass yield (g·L−1) | Pollutants removed | Highest removal efficiency (%) | Reference | |
---|---|---|---|---|---|---|---|
1 | Chlorella sp | produced water from a Qatari local petroleum company | In a temperature-controlled room, a glass bottle was agitated with compressed air and illuminated with an light intensity of 600 µmol photons·m−2·s−1 | 1.72 | TOC | 73 | Das et al. (2019) |
total Nitrogen | 92 | ||||||
2 | Chlorella vulgaris | Produced water from an oil and gas facility in United States. | Tissue Culture Roller Drum Apparatus inside an incubator with a constant level of CO2 of 2%–3% (v/v), a temperature of 28°C with 16:8 h light:dark cycle and an illumination of ∼4000 lux | 3.1 ± 0.5 | total Nitrogen | 100 | Rahman et al. (2021) |
phosphorus | ≈74.2 | ||||||
3 | Chlorella vulgaris | PW from dumping site generated by oil wells in Colombia | fluorescent light at an irradiance of 36.8 ± 4.2 μmol photons m−2 s−1 at the surface of the culture medium, temperature at 20 °C and permanent aeration supplied by a blower | — | Total hydrocarbons | ≈100 | Calderón-delgado et al. (2019) |
4 | Chlorella pyrenoidosa | PW from oilfield in Algeria | outdoor, under sunlight radiation, using an open system sited in the desert area in the winter season. The temperatures fluctuated from 26 to 31°C during the day | 1.15 | COD | 89.67% | Rahmani et al. (2022) |
Ammonium nitrogen | 100% | ||||||
total Nitrogen | 57.14%, | ||||||
total Phosphorus | 75.51% | ||||||
Copper | 73.39 | ||||||
Lead | 72.80 | ||||||
Cadmium | 48.42 | ||||||
5 | Nannochloropsis oculata | Produced water from oil field in Iraq | Florescence light (2000 lux) at and a light photoperiod of 18:6 h light:dark, 25°C±1°C, continuous filtered air at a constant flow rate via two aquarium air pumps | 1.13 | Oil | 66.5 | Ammar et al. (2018) |
COD | 54 | ||||||
6 | Nannochloropsis oculata | Produced water from a TOTAL operating site in France | 14/10 h light/dark periods, by LED lamps, temperature at (21 ± 1°C), autotrophic conditions with air. CO2 was added in pulse, 5 s each 20–40 min and pH between 7.5 and 9 | — | Ammonium nitrogen | ≈100 | Parsy et al. (2020) |
COD | 70 | ||||||
Iron | 100 | ||||||
7 | Nannochloropsis oculata | Produced water from an oil field in Brazil | Aerated photobioreactors (3 L min−1), cold white LED lamps with light intensity of 57 μmol m−2·s−1, photoperiod of 12:12 h. Temperature controlled at 21°C±.9°C. The pH was fixed at 7 | — | PAHs | 94 | Marques et al. (2021) |
NAP | 96 | ||||||
APT | 95 | ||||||
FLU | 91 | ||||||
PHE | 83 | ||||||
BbF | 95 | ||||||
DA | 90 | ||||||
BaP | 95 | ||||||
Iron | 96.80 | ||||||
8 | Galdieria sulphuraria | Produced water from an oil and gas facility in United States. | Tissue Culture Roller Drum Apparatus inside an incubator CO2 level was kept constant at 2%–3% (v/v), temperature 42°C with 24 h of continuous illumination (∼4000 lux) | 5.12 ± .28 | total Nitrogen | ≈100 | Rahman et al. (2021) |
9 | Isochrysis galbana | Produced water from oil field in Iraq | Florescence light (2000 lux), and a photoperiod of 18:6 h light: dark, 25°C±1°C, continuous filtered air at a constant flow rate via two aquarium air pumps | 1.01 | Oil | 68 | Ammar et al. (2018) |
COD | 56 | ||||||
10 | Dunaliella tertiolecta | Produced water from an oil production facility in the Permian Basin of southeast New Mexico | Temperature controlled at 24°C in a growth chamber with fluorescent illumination of 100 μmol photons m−2 s−1. agitation was set at at 140 rpm with a 16-h light/8-h dark cycle | ≈0.3 | nitrate | ≈99.6 | Hopkins et al. (2019) |
Phosphate | ≈99.6 |
PAHs, polycyclic aromatic hydrocarbons; NAP, naphthalene; AP, acenaphthylene; FLU, fluorene; PHE, phenanthrene; BbF, benzo(b)fluoranthene; DA, dibenzo (a, h) anthracene; BaP, benzo(a)pyrene.