Biomethane Potential of Selected Organic Waste and Sewage Sludge at Different Temperature Regimes
Abstract
:1. Introduction
2. Materials and Methods
2.1. Materials
- GTS, which was obtained from the grease traps that are installed at the facility of a meat processing plant in the Silesian region of Poland. The content of VS. for this type of substrate was determined as 57.80%. The C/N ratio was 12.8.
2.2. Experimental Procedure
2.2.1. BMP Assay
2.2.2. Physicochemical Analysis of Mixtures
2.3. Kinetic Study and Statistical Analysis
3. Results and Discussion
3.1. Physicochemical Analysis
3.2. BMP Assay
3.3. Kinetic Study
3.4. Statistical Analysis
4. Conclusions
- Application of GTS and AB substrates for SS co-digestion with feed composition 60/30/10% (SS/GTS/AB) improved both YB and Ym parameters for 35.13% and 88.37%, respectively, at mesophilic temperature and 35.42% and 71.09% at thermophilic one in comparison to standalone SS; however, its λ was the second highest one compared to other mixtures. This mixture also had the highest potential methane yield, particularly at thermophilic temperature.
- Application of OFMSW and AB for SS co-digestion shows rapid adaptation as proved by the kinetic study (its λ was the lowest one at both temperatures among other studied mixtures).
- Thermophilic temperature significantly increased N-NH4+ and FAN concentration.
- All the applied models proved that they can be used for efficient evaluation of three component AcD; however, the best fitting was obtained for the MG model (9 of 10 cases) and the worst fitting for the LF (9 of 10 cases).
- VS removal was much slower at thermophilic temperature, and the values were lower for 64% (as an average for all mixtures) at the first thermophilic digestion week in comparison to the mesophilic one. As confirmed by the statistical analysis, temperature influenced this parameter the most.
- Statistical analysis confirmed that the YB results depended highly on the choice of substrates (factor “mixture”) for mixture preparation and operational temperature of the digestion as was also proved with the Tukey HSD test.
Supplementary Materials
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Substrate | TS (%) | VS (%) | VS/TS (–) | C/N (–) |
---|---|---|---|---|
AB | 88.70 | 60.08 | 0.67 | 9.36 |
OFMSW | 20.20 | 19.70 | 0.96 | 29.3 ± 0.7 |
GTS | 58.40 | 57.80 | 0.99 | 12.8 |
Digested sludge (inoculum) | 2.61 (1)–2.84 (2) | 1.38 (1)–1.59 (2) | 0.53 (1)–0.56 (2) | 8.65 (2)–8.85 (1) |
Mixture | Percentage Composition of Each Mixture Based on VS. of Each Substrate | Mesophilic Digestion | Thermophilic Digestion | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
AB | SS | GTS | OFMSW | |||||||||
TS (%) | VS (%) | VS/TS (−) | C/N (−) | TS (%) | VS (%) | VS/TS (−) | C/N (−) | |||||
M-I | – | 100 | – | – | 3.84 | 3.08 | 0.80 | 10 | 3.22 | 2.42 | 0.75 | 10.3 |
M-II | 100 | – | – | – | 4.76 | 3.20 | 0.67 | 8.3 | 4.72 | 3.03 | 0.64 | 8.2 |
M-III | 10 | 90 | – | – | 4.02 | 3.15 | 0.78 | 11.6 | 3.46 | 2.56 | 0.74 | 10 |
M-IV | 10 | 60 | 30 | – | 5.54 | 4.51 | 0.81 | 9.9 | 4.99 | 3.99 | 0.79 | 11.7 |
M-V | 10 | 60 | – | 30 | 5.26 | 4.25 | 0.80 | 10.5 | 4.83 | 3.82 | 0.79 | 10.8 |
Mixture | YB (N mL/g-VSadd) | Ym (N mL-CH4/g-VSadd) | ||
---|---|---|---|---|
M | T | M | T | |
M-I | 474.61 ± 11.94 bc | 497.23 ± 33.31 bcd | 138.47 ± 4.70 bcd | 161.13 ± 13.11 de |
M-II | 456.61 ± 13.60 bc | 397.64 ± 36.06 b | 97.50 ± 2.85 b | 108.79 ± 5.73 bc |
M-III | 451.30 ± 9.98 bc | 452.11 ± 8.97 bc | 138.04 ± 2.94 bcd | 138.57 ± 5.38 bcd |
M-IV | 641.34 ± 33.84 e | 673.36 ± 8.97 e | 260.83 ± 15.02 f | 275.66 ± 4.11 f |
M-V | 512.55 ± 30.05 cd | 592.74 ± 98.36 de | 147.18 ± 7.88 cd | 203.07 ± 47.49 e |
IN | 78.74 ± 0.00 a | 36.84 ± 1.08 a | 4.22 ± 0.00 a | 0.49 ± 0.01 a |
Mixture | Model | Pm (N mL-CH4/g-VSadd) | Rm (N mL-CH4 × g-VSadd−1 × d−1) | λ (d) | R2 (−) | ||||
---|---|---|---|---|---|---|---|---|---|
M | T | M | T | M | T | M | T | ||
M-I | MG | 135.80 | 157.11 | 32.33 | 47.42 | 1.074 | 1.099 | 0.9985 | 0.9986 |
LF | 141.52 | 168.14 | 36.21 | 50.46 | 0.409 | 0.388 | 0.9825 | 0.9775 | |
TF | 134.53 | 155.30 | 32.64 | 47.78 | 1.229 | 1.212 | 0.9958 | 0.9957 | |
M-II | MG | 96.70 | 70.33 | 29.77 | −6.18 | 1.433 | 93.036 | 0.9995 | 0 |
LF | 100.70 | 122.99 | 28.40 | 24.77 | 0.464 | 0.866 | 0.9685 | 0.9374 | |
TF | 95.93 | 107.52 | 29.65 | 39.49 | 1.544 | 2.975 | 0.9983 | 0.9997 | |
M-III | MG | 136.17 | 138.08 | 36.23 | 51.85 | 0.921 | 0.856 | 0.9985 | 0.9995 |
LF | 141.29 | 144.29 | 41.93 | 56.41 | 0.356 | 0.258 | 0.9822 | 0.9777 | |
TF | 134.77 | 137.05 | 36.08 | 51.45 | 1.033 | 0.934 | 0.9943 | 0.997 | |
M-IV | MG | 260.56 | 275.93 | 37.54 | 74.34 | 1.234 | 1.507 | 0.9995 | 0.9994 |
LF | 277.23 | 298.17 | 43.91 | 75.72 | 0.606 | 0.532 | 0.9882 | 0.969 | |
TF | 256.36 | 272.79 | 40.84 | 74.01 | 1.624 | 1.633 | 0.9968 | 0.999 | |
M-V | MG | 146.71 | 191.69 | 42.78 | 49.69 | 0.808 | 0.853 | 0.9995 | 0.9952 |
LF | 151.12 | 206.25 | 51.28 | 58.03 | 0.289 | 0.349 | 0.9811 | 0.984 | |
TF | 145.45 | 188.83 | 42.19 | 50.18 | 0.907 | 0.979 | 0.997 | 0.9904 |
Parameter | Factor | |||||||
---|---|---|---|---|---|---|---|---|
Time | Mixt. | Temp. | Time/Mixt. | Time/Temp. | Mixt./Temp. | Time/Mixt./Temp. | ||
VS removal | F | 218.39 | 57.66 | 602.79 | 9.34 | 41.55 | 113.57 | 8.37 |
p | 0.000000 | 0.000000 | 0.000000 | 0.000000 | 0.000000 | 0.000000 | 0.000000 | |
YB | F | 0.693 | 13.953 | 0.630 | 0.072 | 0.250 | 3.345 | 0.073 |
p | 0.558967 | 0.000000 | 0.429667 | 0.999992 | 0.860842 | 0.013855 | 0.999990 | |
Ym | F | 57.537 | 1.118 | 10.650 | 0.293 | 3.391 | 0.475 | 0.311 |
p | 0.000000 | 0.346796 | 0.001620 | 0.988921 | 0.012927 | 0.700691 | 0.985666 | |
Variation of methane in biogas | F | 25.262 | 19.073 | 59.791 | 3.209 | 14.373 | 7.360 | 3.261 |
p | 0.000000 | 0.000000 | 0.000000 | 0.000866 | 0.000000 | 0.000042 | 0.000738 |
Parameter | Factor | Mixture | |||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
VS removal | Mixt. | M-V | M-IV | M-II | M-II | M-I | M-III | M-I | M-IV | M-V | M-III |
Temp. | T | T | T | M | M | M | T | M | M | T | |
Mean | 18.32 | 21.24 | 23.90 | 27.21 | 31.93 | 33.53 | 34.16 | 36.28 | 39.96 | 45.93 | |
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YB | Mixt. | MV | MIV | MII | MII | MI | MIII | MI | MIV | MV | MIII |
Temp. | T | T | T | M | M | M | T | M | M | T | |
Mean | 316.40 | 388.01 | 396.35 | 443.99 | 444.63 | 449.70 | 457.21 | 502.33 | 614.21 | 660.51 | |
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Ym | Mixt. | MV | MIV | MII | MII | MI | MIII | MI | MIV | MV | MIII |
Temp. | T | T | T | M | M | M | T | M | M | T | |
Mean | 92.31 | 97.50 | 103.72 | 122.06 | 135.04 | 143.24 | 147.51 | 156.68 | 247.83 | 275.66 | |
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Variation of methane in biogas | Mixt. | MV | MIV | MII | MII | MI | MIII | MI | MIV | MV | MIII |
Temp. | T | T | T | M | M | M | T | M | M | T | |
Mean | 5.00 | 17.00 | 25.70 | 27.00 | 28.42 | 30.00 | 33.40 | 36.58 | 41.00 | 41.40 | |
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Smetana, G.; Neczaj, E.; Grosser, A. Biomethane Potential of Selected Organic Waste and Sewage Sludge at Different Temperature Regimes. Energies 2021, 14, 4217. https://doi.org/10.3390/en14144217
Smetana G, Neczaj E, Grosser A. Biomethane Potential of Selected Organic Waste and Sewage Sludge at Different Temperature Regimes. Energies. 2021; 14(14):4217. https://doi.org/10.3390/en14144217
Chicago/Turabian StyleSmetana, German, Ewa Neczaj, and Anna Grosser. 2021. "Biomethane Potential of Selected Organic Waste and Sewage Sludge at Different Temperature Regimes" Energies 14, no. 14: 4217. https://doi.org/10.3390/en14144217