| Biotechnological application . | Organisms . | Degradation/production potential . | References . |
|---|---|---|---|
| Phenol degradation | A. calcoaceticus | 91.6% of 0.8 g/l phenol in 48 h | Irankhah et al. (2019) |
| A. radioresistens | 99% of 450 mg/kg of phenol-contaminated soil | Liu et al. (2020) | |
| A. lwoffii | 41.67 mg/l per hour | Irankhah et al. (2019) | |
| A. tandoii | 100% degradation at the concentration of 280 mg/l | Van et al. (2019) | |
| Nitrogen assimilation and removal | A. boisseri | Not mentioned | Alvarez-Perez et al. () |
| A. calcoaceticus | Capable of nitrogen removal under low temperature conditions | Wu et al. (2022) | |
| A. nectaris | Not mentioned | Alvarez-Perez et al. () | |
| Chromium reduction | A. bouvetii | Able to reduce 40% chromium absorbed by plant roots | Qadir et al. (2021) |
| Bioremediation of heavy metals | A. imdicus | Can reduce chromium(IV) and mercury(II) | Hu et al. (2021) |
| Hydrocarbon degradation | A. lwoffii | Can degrade C13- C35 n-alkanes in crude oil | Liu et al. (2020) |
| A. pitti | Can degrade 88% of crude oil | Chettri et al. (2019) | |
| A. baumannii | Can degrade 76% diesel and 90% paraffins | Kumar and De (2023) | |
| Dye discoloration and degradation | A. pittii | Can degrade 84% methylene blue in 24 h | Ogunlaja et al. (2020) |
| A. calcoaceticus | Azo dye amaranth degradation with 90% efficiency | Ameenudeen et al. (2021) | |
| A. haemolyticus | Can degrade methylene green, basic violet, and acid blue dyes | Hossain et al. (2022) | |
| A. baumannii | Decolourized 90% of 500 mg/l of azo dye | Shreedharan et al. (2021) | |
| Toulene | A. junnii | Can degrade 80% of 50 ppm toluene within 72 h | Singh et al. (2018) |
| Diesel degradation | A. vivani | Can use diesel as the sole source of carbon | Zhang et al. (2022) |
| A. haemolyticus | Diesel degradation facilitated by kurstakin molecules | Diallo et al. (2021) | |
| A. baumannii | Can degrade 99% diesel at pH 7 | Imron et al. (2018) | |
| A. lwoffii | Bioremediation in marine environment | Imron et al. (2020) | |
| A. calcoaceticus | Presence of diesel degrading genes alkM and xcpR | Ho et al. (2020) | |
| Polyurethane degradation | A. baumannii | Grows on polyurethane | Espinosa et al. (2020) |
| Crude oil degradation | A. venetianus | Can degrade upto 60.6% waxy crude oil | Liu et al. (2021), Wang et al. (2019) |
| A. pitti | Can degrade 36% percent crude oil in 21 days at 10 g/l | Wang et al. (2019) | |
| Insecticide degradation | A. schindleri | Can degrade insecticides α-endosulfan and α-cypermethrin with more than 60% efficiency | Gur and Algur (2022) |
| Furfural degradation | A. baylyi | Can degrade 1 g furfural in 1 h | Arteaga et al. (2021) |
| Fipronil degradation | A. calcoaceticus | 86.6% degradation after 45 days | Uniyal et al. (2016) |
| A. oleivorans | 89.7% degradation after 45 days | Uniyal et al. (2016) | |
| NAP, ANT, and other polyaromatic hydrocarbon degradation | A. johnsonii | Can degrade 200 mg/l NAP and 1950 mg/l ANT | Jiang et al. (2018) |
| A. baumannii | Efficient at 300 mg/l concentration of pyrene | Gupta et al. (2020) | |
| Catechol production | A. bouveti | Produces novel biscatechol siderophores namely propanochelin, butanochelin, and pentanochelin | Reitz and Butler (2020) |
| N-acetyl-β-D-glucosamine production | A. parvus | Can convert chitin to N-acetyl-β-D-glucosamine | Kim et al. (2017) |
| Cellulase production | A. junnii | Capable of producing cellulase at 112.38 U/ml | Banerjee et al. (2020) |
| Mevalonate production |
| Produces mevalonate from lignin derived compounds by β-keto adipose pathway | Arvay et al. (2021) |
| Lipase production | A. indicus | Efficient lipase producer from industrial waste | Patel et al. (2021) |
| A. radioresistens | Can produce 4.16 U/ml (at pH 9) of enzyme after 72 h | Gupta et al. (2018) | |
| A. haemolyticus | Produces lipase which is highly stable at 4°C displaying 90% activity even after 2 months | Sarac et al. (2016) | |
| A. calcoaceticus | A. calcoaceticus Rag-1 produces the most widely studied Emulsan (1000 kDa) | Mujumdar et al. (2019) | |
| Bioemulsion and biosurfactant production | A. pittii | Can produce 0.57 g/l lipopeptide biosurfactant when incubated with 1% (v/v) crude oil | Mujumdar et al. (2019) |
| A. beijerinckii | Produces the only bioemulsion that contains lipoprotein while others contain polysaccharides | Mujumdar et al. (2019) | |
| A. baumannii | Produces lipoglycan, using edible oil as carbon source | Mujumdar et al. (2019) | |
| A. radioresistens | Produces alsan, utilizing carbon source as ethanol | Mujumdar et al. (2019) | |
| A. bouvetii | Produces the highest molecular weight lipo-hetero-polysaccharide bioemulsifier | Mujumdar et al. (2019) | |
| A. lwoffii | Produces proteoglycan in presence of castor oil as carbon source | Mujumdar et al. (2019) | |
| Phenanthrene degradation | A. venetianus | Phenanthrene degradation ability facilitated by ball-milled biochar (2.4 times increase) | Guo et al. (2022) |
| Proteases production | A. pittii | Yields as high as 11–12 U/ml with de-oiled neem seed cake | Reddy et al. (2022) |
| Biohydrogen production | A. junii | Can produce up to 566 ml/l of H2 from wastewaters at pH 7.5 | Murugan et al. (2021) |
| Biodiesel degradation | A. oleivorans | Uses biodiesel as a sole source of carbon at 30°C | Deems et al. (2021) |
| Polyhydroxybutyrate (PHB) production | A. nosocomialis | Can yield up to 5.88 g/l of PHB under optimal conditions | Ranganadha et al. (2020) |
| Biotechnological application . | Organisms . | Degradation/production potential . | References . |
|---|---|---|---|
| Phenol degradation | A. calcoaceticus | 91.6% of 0.8 g/l phenol in 48 h | Irankhah et al. (2019) |
| A. radioresistens | 99% of 450 mg/kg of phenol-contaminated soil | Liu et al. (2020) | |
| A. lwoffii | 41.67 mg/l per hour | Irankhah et al. (2019) | |
| A. tandoii | 100% degradation at the concentration of 280 mg/l | Van et al. (2019) | |
| Nitrogen assimilation and removal | A. boisseri | Not mentioned | Alvarez-Perez et al. () |
| A. calcoaceticus | Capable of nitrogen removal under low temperature conditions | Wu et al. (2022) | |
| A. nectaris | Not mentioned | Alvarez-Perez et al. () | |
| Chromium reduction | A. bouvetii | Able to reduce 40% chromium absorbed by plant roots | Qadir et al. (2021) |
| Bioremediation of heavy metals | A. imdicus | Can reduce chromium(IV) and mercury(II) | Hu et al. (2021) |
| Hydrocarbon degradation | A. lwoffii | Can degrade C13- C35 n-alkanes in crude oil | Liu et al. (2020) |
| A. pitti | Can degrade 88% of crude oil | Chettri et al. (2019) | |
| A. baumannii | Can degrade 76% diesel and 90% paraffins | Kumar and De (2023) | |
| Dye discoloration and degradation | A. pittii | Can degrade 84% methylene blue in 24 h | Ogunlaja et al. (2020) |
| A. calcoaceticus | Azo dye amaranth degradation with 90% efficiency | Ameenudeen et al. (2021) | |
| A. haemolyticus | Can degrade methylene green, basic violet, and acid blue dyes | Hossain et al. (2022) | |
| A. baumannii | Decolourized 90% of 500 mg/l of azo dye | Shreedharan et al. (2021) | |
| Toulene | A. junnii | Can degrade 80% of 50 ppm toluene within 72 h | Singh et al. (2018) |
| Diesel degradation | A. vivani | Can use diesel as the sole source of carbon | Zhang et al. (2022) |
| A. haemolyticus | Diesel degradation facilitated by kurstakin molecules | Diallo et al. (2021) | |
| A. baumannii | Can degrade 99% diesel at pH 7 | Imron et al. (2018) | |
| A. lwoffii | Bioremediation in marine environment | Imron et al. (2020) | |
| A. calcoaceticus | Presence of diesel degrading genes alkM and xcpR | Ho et al. (2020) | |
| Polyurethane degradation | A. baumannii | Grows on polyurethane | Espinosa et al. (2020) |
| Crude oil degradation | A. venetianus | Can degrade upto 60.6% waxy crude oil | Liu et al. (2021), Wang et al. (2019) |
| A. pitti | Can degrade 36% percent crude oil in 21 days at 10 g/l | Wang et al. (2019) | |
| Insecticide degradation | A. schindleri | Can degrade insecticides α-endosulfan and α-cypermethrin with more than 60% efficiency | Gur and Algur (2022) |
| Furfural degradation | A. baylyi | Can degrade 1 g furfural in 1 h | Arteaga et al. (2021) |
| Fipronil degradation | A. calcoaceticus | 86.6% degradation after 45 days | Uniyal et al. (2016) |
| A. oleivorans | 89.7% degradation after 45 days | Uniyal et al. (2016) | |
| NAP, ANT, and other polyaromatic hydrocarbon degradation | A. johnsonii | Can degrade 200 mg/l NAP and 1950 mg/l ANT | Jiang et al. (2018) |
| A. baumannii | Efficient at 300 mg/l concentration of pyrene | Gupta et al. (2020) | |
| Catechol production | A. bouveti | Produces novel biscatechol siderophores namely propanochelin, butanochelin, and pentanochelin | Reitz and Butler (2020) |
| N-acetyl-β-D-glucosamine production | A. parvus | Can convert chitin to N-acetyl-β-D-glucosamine | Kim et al. (2017) |
| Cellulase production | A. junnii | Capable of producing cellulase at 112.38 U/ml | Banerjee et al. (2020) |
| Mevalonate production |
| Produces mevalonate from lignin derived compounds by β-keto adipose pathway | Arvay et al. (2021) |
| Lipase production | A. indicus | Efficient lipase producer from industrial waste | Patel et al. (2021) |
| A. radioresistens | Can produce 4.16 U/ml (at pH 9) of enzyme after 72 h | Gupta et al. (2018) | |
| A. haemolyticus | Produces lipase which is highly stable at 4°C displaying 90% activity even after 2 months | Sarac et al. (2016) | |
| A. calcoaceticus | A. calcoaceticus Rag-1 produces the most widely studied Emulsan (1000 kDa) | Mujumdar et al. (2019) | |
| Bioemulsion and biosurfactant production | A. pittii | Can produce 0.57 g/l lipopeptide biosurfactant when incubated with 1% (v/v) crude oil | Mujumdar et al. (2019) |
| A. beijerinckii | Produces the only bioemulsion that contains lipoprotein while others contain polysaccharides | Mujumdar et al. (2019) | |
| A. baumannii | Produces lipoglycan, using edible oil as carbon source | Mujumdar et al. (2019) | |
| A. radioresistens | Produces alsan, utilizing carbon source as ethanol | Mujumdar et al. (2019) | |
| A. bouvetii | Produces the highest molecular weight lipo-hetero-polysaccharide bioemulsifier | Mujumdar et al. (2019) | |
| A. lwoffii | Produces proteoglycan in presence of castor oil as carbon source | Mujumdar et al. (2019) | |
| Phenanthrene degradation | A. venetianus | Phenanthrene degradation ability facilitated by ball-milled biochar (2.4 times increase) | Guo et al. (2022) |
| Proteases production | A. pittii | Yields as high as 11–12 U/ml with de-oiled neem seed cake | Reddy et al. (2022) |
| Biohydrogen production | A. junii | Can produce up to 566 ml/l of H2 from wastewaters at pH 7.5 | Murugan et al. (2021) |
| Biodiesel degradation | A. oleivorans | Uses biodiesel as a sole source of carbon at 30°C | Deems et al. (2021) |
| Polyhydroxybutyrate (PHB) production | A. nosocomialis | Can yield up to 5.88 g/l of PHB under optimal conditions | Ranganadha et al. (2020) |
| Biotechnological application . | Organisms . | Degradation/production potential . | References . |
|---|---|---|---|
| Phenol degradation | A. calcoaceticus | 91.6% of 0.8 g/l phenol in 48 h | Irankhah et al. (2019) |
| A. radioresistens | 99% of 450 mg/kg of phenol-contaminated soil | Liu et al. (2020) | |
| A. lwoffii | 41.67 mg/l per hour | Irankhah et al. (2019) | |
| A. tandoii | 100% degradation at the concentration of 280 mg/l | Van et al. (2019) | |
| Nitrogen assimilation and removal | A. boisseri | Not mentioned | Alvarez-Perez et al. () |
| A. calcoaceticus | Capable of nitrogen removal under low temperature conditions | Wu et al. (2022) | |
| A. nectaris | Not mentioned | Alvarez-Perez et al. () | |
| Chromium reduction | A. bouvetii | Able to reduce 40% chromium absorbed by plant roots | Qadir et al. (2021) |
| Bioremediation of heavy metals | A. imdicus | Can reduce chromium(IV) and mercury(II) | Hu et al. (2021) |
| Hydrocarbon degradation | A. lwoffii | Can degrade C13- C35 n-alkanes in crude oil | Liu et al. (2020) |
| A. pitti | Can degrade 88% of crude oil | Chettri et al. (2019) | |
| A. baumannii | Can degrade 76% diesel and 90% paraffins | Kumar and De (2023) | |
| Dye discoloration and degradation | A. pittii | Can degrade 84% methylene blue in 24 h | Ogunlaja et al. (2020) |
| A. calcoaceticus | Azo dye amaranth degradation with 90% efficiency | Ameenudeen et al. (2021) | |
| A. haemolyticus | Can degrade methylene green, basic violet, and acid blue dyes | Hossain et al. (2022) | |
| A. baumannii | Decolourized 90% of 500 mg/l of azo dye | Shreedharan et al. (2021) | |
| Toulene | A. junnii | Can degrade 80% of 50 ppm toluene within 72 h | Singh et al. (2018) |
| Diesel degradation | A. vivani | Can use diesel as the sole source of carbon | Zhang et al. (2022) |
| A. haemolyticus | Diesel degradation facilitated by kurstakin molecules | Diallo et al. (2021) | |
| A. baumannii | Can degrade 99% diesel at pH 7 | Imron et al. (2018) | |
| A. lwoffii | Bioremediation in marine environment | Imron et al. (2020) | |
| A. calcoaceticus | Presence of diesel degrading genes alkM and xcpR | Ho et al. (2020) | |
| Polyurethane degradation | A. baumannii | Grows on polyurethane | Espinosa et al. (2020) |
| Crude oil degradation | A. venetianus | Can degrade upto 60.6% waxy crude oil | Liu et al. (2021), Wang et al. (2019) |
| A. pitti | Can degrade 36% percent crude oil in 21 days at 10 g/l | Wang et al. (2019) | |
| Insecticide degradation | A. schindleri | Can degrade insecticides α-endosulfan and α-cypermethrin with more than 60% efficiency | Gur and Algur (2022) |
| Furfural degradation | A. baylyi | Can degrade 1 g furfural in 1 h | Arteaga et al. (2021) |
| Fipronil degradation | A. calcoaceticus | 86.6% degradation after 45 days | Uniyal et al. (2016) |
| A. oleivorans | 89.7% degradation after 45 days | Uniyal et al. (2016) | |
| NAP, ANT, and other polyaromatic hydrocarbon degradation | A. johnsonii | Can degrade 200 mg/l NAP and 1950 mg/l ANT | Jiang et al. (2018) |
| A. baumannii | Efficient at 300 mg/l concentration of pyrene | Gupta et al. (2020) | |
| Catechol production | A. bouveti | Produces novel biscatechol siderophores namely propanochelin, butanochelin, and pentanochelin | Reitz and Butler (2020) |
| N-acetyl-β-D-glucosamine production | A. parvus | Can convert chitin to N-acetyl-β-D-glucosamine | Kim et al. (2017) |
| Cellulase production | A. junnii | Capable of producing cellulase at 112.38 U/ml | Banerjee et al. (2020) |
| Mevalonate production |
| Produces mevalonate from lignin derived compounds by β-keto adipose pathway | Arvay et al. (2021) |
| Lipase production | A. indicus | Efficient lipase producer from industrial waste | Patel et al. (2021) |
| A. radioresistens | Can produce 4.16 U/ml (at pH 9) of enzyme after 72 h | Gupta et al. (2018) | |
| A. haemolyticus | Produces lipase which is highly stable at 4°C displaying 90% activity even after 2 months | Sarac et al. (2016) | |
| A. calcoaceticus | A. calcoaceticus Rag-1 produces the most widely studied Emulsan (1000 kDa) | Mujumdar et al. (2019) | |
| Bioemulsion and biosurfactant production | A. pittii | Can produce 0.57 g/l lipopeptide biosurfactant when incubated with 1% (v/v) crude oil | Mujumdar et al. (2019) |
| A. beijerinckii | Produces the only bioemulsion that contains lipoprotein while others contain polysaccharides | Mujumdar et al. (2019) | |
| A. baumannii | Produces lipoglycan, using edible oil as carbon source | Mujumdar et al. (2019) | |
| A. radioresistens | Produces alsan, utilizing carbon source as ethanol | Mujumdar et al. (2019) | |
| A. bouvetii | Produces the highest molecular weight lipo-hetero-polysaccharide bioemulsifier | Mujumdar et al. (2019) | |
| A. lwoffii | Produces proteoglycan in presence of castor oil as carbon source | Mujumdar et al. (2019) | |
| Phenanthrene degradation | A. venetianus | Phenanthrene degradation ability facilitated by ball-milled biochar (2.4 times increase) | Guo et al. (2022) |
| Proteases production | A. pittii | Yields as high as 11–12 U/ml with de-oiled neem seed cake | Reddy et al. (2022) |
| Biohydrogen production | A. junii | Can produce up to 566 ml/l of H2 from wastewaters at pH 7.5 | Murugan et al. (2021) |
| Biodiesel degradation | A. oleivorans | Uses biodiesel as a sole source of carbon at 30°C | Deems et al. (2021) |
| Polyhydroxybutyrate (PHB) production | A. nosocomialis | Can yield up to 5.88 g/l of PHB under optimal conditions | Ranganadha et al. (2020) |
| Biotechnological application . | Organisms . | Degradation/production potential . | References . |
|---|---|---|---|
| Phenol degradation | A. calcoaceticus | 91.6% of 0.8 g/l phenol in 48 h | Irankhah et al. (2019) |
| A. radioresistens | 99% of 450 mg/kg of phenol-contaminated soil | Liu et al. (2020) | |
| A. lwoffii | 41.67 mg/l per hour | Irankhah et al. (2019) | |
| A. tandoii | 100% degradation at the concentration of 280 mg/l | Van et al. (2019) | |
| Nitrogen assimilation and removal | A. boisseri | Not mentioned | Alvarez-Perez et al. () |
| A. calcoaceticus | Capable of nitrogen removal under low temperature conditions | Wu et al. (2022) | |
| A. nectaris | Not mentioned | Alvarez-Perez et al. () | |
| Chromium reduction | A. bouvetii | Able to reduce 40% chromium absorbed by plant roots | Qadir et al. (2021) |
| Bioremediation of heavy metals | A. imdicus | Can reduce chromium(IV) and mercury(II) | Hu et al. (2021) |
| Hydrocarbon degradation | A. lwoffii | Can degrade C13- C35 n-alkanes in crude oil | Liu et al. (2020) |
| A. pitti | Can degrade 88% of crude oil | Chettri et al. (2019) | |
| A. baumannii | Can degrade 76% diesel and 90% paraffins | Kumar and De (2023) | |
| Dye discoloration and degradation | A. pittii | Can degrade 84% methylene blue in 24 h | Ogunlaja et al. (2020) |
| A. calcoaceticus | Azo dye amaranth degradation with 90% efficiency | Ameenudeen et al. (2021) | |
| A. haemolyticus | Can degrade methylene green, basic violet, and acid blue dyes | Hossain et al. (2022) | |
| A. baumannii | Decolourized 90% of 500 mg/l of azo dye | Shreedharan et al. (2021) | |
| Toulene | A. junnii | Can degrade 80% of 50 ppm toluene within 72 h | Singh et al. (2018) |
| Diesel degradation | A. vivani | Can use diesel as the sole source of carbon | Zhang et al. (2022) |
| A. haemolyticus | Diesel degradation facilitated by kurstakin molecules | Diallo et al. (2021) | |
| A. baumannii | Can degrade 99% diesel at pH 7 | Imron et al. (2018) | |
| A. lwoffii | Bioremediation in marine environment | Imron et al. (2020) | |
| A. calcoaceticus | Presence of diesel degrading genes alkM and xcpR | Ho et al. (2020) | |
| Polyurethane degradation | A. baumannii | Grows on polyurethane | Espinosa et al. (2020) |
| Crude oil degradation | A. venetianus | Can degrade upto 60.6% waxy crude oil | Liu et al. (2021), Wang et al. (2019) |
| A. pitti | Can degrade 36% percent crude oil in 21 days at 10 g/l | Wang et al. (2019) | |
| Insecticide degradation | A. schindleri | Can degrade insecticides α-endosulfan and α-cypermethrin with more than 60% efficiency | Gur and Algur (2022) |
| Furfural degradation | A. baylyi | Can degrade 1 g furfural in 1 h | Arteaga et al. (2021) |
| Fipronil degradation | A. calcoaceticus | 86.6% degradation after 45 days | Uniyal et al. (2016) |
| A. oleivorans | 89.7% degradation after 45 days | Uniyal et al. (2016) | |
| NAP, ANT, and other polyaromatic hydrocarbon degradation | A. johnsonii | Can degrade 200 mg/l NAP and 1950 mg/l ANT | Jiang et al. (2018) |
| A. baumannii | Efficient at 300 mg/l concentration of pyrene | Gupta et al. (2020) | |
| Catechol production | A. bouveti | Produces novel biscatechol siderophores namely propanochelin, butanochelin, and pentanochelin | Reitz and Butler (2020) |
| N-acetyl-β-D-glucosamine production | A. parvus | Can convert chitin to N-acetyl-β-D-glucosamine | Kim et al. (2017) |
| Cellulase production | A. junnii | Capable of producing cellulase at 112.38 U/ml | Banerjee et al. (2020) |
| Mevalonate production |
| Produces mevalonate from lignin derived compounds by β-keto adipose pathway | Arvay et al. (2021) |
| Lipase production | A. indicus | Efficient lipase producer from industrial waste | Patel et al. (2021) |
| A. radioresistens | Can produce 4.16 U/ml (at pH 9) of enzyme after 72 h | Gupta et al. (2018) | |
| A. haemolyticus | Produces lipase which is highly stable at 4°C displaying 90% activity even after 2 months | Sarac et al. (2016) | |
| A. calcoaceticus | A. calcoaceticus Rag-1 produces the most widely studied Emulsan (1000 kDa) | Mujumdar et al. (2019) | |
| Bioemulsion and biosurfactant production | A. pittii | Can produce 0.57 g/l lipopeptide biosurfactant when incubated with 1% (v/v) crude oil | Mujumdar et al. (2019) |
| A. beijerinckii | Produces the only bioemulsion that contains lipoprotein while others contain polysaccharides | Mujumdar et al. (2019) | |
| A. baumannii | Produces lipoglycan, using edible oil as carbon source | Mujumdar et al. (2019) | |
| A. radioresistens | Produces alsan, utilizing carbon source as ethanol | Mujumdar et al. (2019) | |
| A. bouvetii | Produces the highest molecular weight lipo-hetero-polysaccharide bioemulsifier | Mujumdar et al. (2019) | |
| A. lwoffii | Produces proteoglycan in presence of castor oil as carbon source | Mujumdar et al. (2019) | |
| Phenanthrene degradation | A. venetianus | Phenanthrene degradation ability facilitated by ball-milled biochar (2.4 times increase) | Guo et al. (2022) |
| Proteases production | A. pittii | Yields as high as 11–12 U/ml with de-oiled neem seed cake | Reddy et al. (2022) |
| Biohydrogen production | A. junii | Can produce up to 566 ml/l of H2 from wastewaters at pH 7.5 | Murugan et al. (2021) |
| Biodiesel degradation | A. oleivorans | Uses biodiesel as a sole source of carbon at 30°C | Deems et al. (2021) |
| Polyhydroxybutyrate (PHB) production | A. nosocomialis | Can yield up to 5.88 g/l of PHB under optimal conditions | Ranganadha et al. (2020) |
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