TABLE 3.
Biochemical properties of food processing wastewater.
| Wastewater | Biochemical properties | References | ||||
|---|---|---|---|---|---|---|
| TOC (mg L-1) | COD (mg L-1) | TN (mg L-1) | TAN (mg L-1) | TP (mg L-1) | ||
| Soybean fermentation effluent | 2042.20 | 6749.33 | 394.44 | 372.44 | 46.78 | Deng et al. (2021) |
| Soybean processing wastewater | NA a | 13,215 | 267.1 | 52.1 | 56.3 | Hongyang et al. (2011) |
| Molasses | 1870 | 6500 | 420 | ∼18 | NA | Avcioglu et al. (2011) |
| Meat processing wastewater | NA | 19,580 | 137.5 | NA | 10.8 | Hu et al. (2019) |
| Meat processing wastewater | NA | 8,470 | 219.8 | NA | 108.3 | Hu et al. (2019) |
| Fruits and vegetables processing wastewater | NA | 10,913–22300 | 220–252 | NA | 20.8–512.4 | Asgharnejad et al. (2021) |
| Coffee processing wastewater | NA | 15,040–18080 | 22.4–40.32 | NA | 4–7.3 | Asgharnejad et al. (2021) |
| Meat processing wastewater | NA | 3,560 | 327.6 | 193.0 | 46.8 | Lu et al. (2015) |
| Edible oil wastewater | NA | 15,000–100000 | 180–1,400 | NA | 180 | Lee et al. (2019b), Asgharnejad et al. (2021) |
| Sugarcane spent wash | 205 | 21,698 | 182 | NA | 2.15 | Vasistha et al. (2023) |
| Dairy wastewater | NA | 191,000 | 3,570 | 429 | 22,350 | Lu et al. (2016) |
| Molasses wastewater | NA | 4,150 | 864.7 (NO3-N: 44.7 mg L-1) | 820 | NA | Tsioptsias et al. (2015) |
| Alcohol wastewater | NA | 65,000 | 618.68 | 279.72 | 47.16 | Yang et al. (2015b) |
| TAP medium (artificial medium) | NA | 3,870 | 364.4 | 132.0 | 28.6 | Yang et al. (2006) |
a
NA means not available.