| 000 | 02812nab|a22003857a|4500 | ||
|---|---|---|---|
| 001 | 64470 | ||
| 003 | MX-TxCIM | ||
| 005 | 20211101203959.0 | ||
| 008 | 190822s2018||||sz |||p|op||||00||0|eng|d | ||
| 022 | _a1996-1073 | ||
| 024 | 8 | _ahttps://doi.org/10.3390/en11082101 | |
| 040 | _aMX-TxCIM | ||
| 041 | _aeng | ||
| 100 | 1 |
_924512 _aValero, D. |
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| 245 | 1 | 0 | _aEnhancing biochemical methane potential and enrichment of specific electroactive communities from nixtamalization wastewater using granular activated carbon as a conductive material |
| 260 |
_aBasel (Switzerland) : _bMDPI, _c2018. |
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| 500 | _aPeer review | ||
| 500 | _aOpen Access | ||
| 520 | _aNejayote (corn step liquor) production in Mexico is approximately 1.4 × 1010 m3 per year and anaerobic digestion is an effective process to transform this waste into green energy. The biochemical methane potential (BMP) test is one of the most important tests for evaluating the biodegradability and methane production capacity of any organic waste. Previous research confirms that the addition of conductive materials significantly enhances the methane production yield. This study concludes that the addition of granular activated carbon (GAC) increases methane yield by 34% in the first instance. Furthermore, results show that methane production is increased by 54% when a GAC biofilm is developed 10 days before undertaking the BMP test. In addition, the electroactive population was 30% higher when attached to the GAC than in control reactors. Moreover, results show that electroactive communities attached to the GAC increased by 38% when a GAC biofilm is developed 10 days before undertaking the BMP test, additionally only in these reactors Geobacter was identified. GAC has two main effects in anaerobic digestion; it promotes direct interspecies electron transfer (DIET) by developing an electro-active biofilm and simultaneously it reduces redox potential from −223 mV to −470 mV. These results suggest that the addition of GAC to biodigesters, improves the anaerobic digestion performance in industrial processed food waste. | ||
| 546 | _aText in English | ||
| 650 | 7 |
_2AGROVOC _912258 _aMethane |
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| 650 | 7 |
_2AGROVOC _924513 _aRedox potential |
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| 650 | 7 |
_2AGROVOC _924514 _aOxidoreductions |
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| 650 | 7 |
_2AGROVOC _924515 _aBioreactors |
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| 650 | 7 |
_2AGROVOC _924516 _aActivated carbon |
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| 700 | 1 |
_aRico, C. _924517 |
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| 700 | 1 |
_aCanto-Canché, B. _924518 |
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| 700 | 1 |
_aDomínguez-Maldonado, J.A. _924519 |
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| 700 | 1 |
_aTapia-Tussell, R. _924520 |
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| 700 | 1 |
_aCortes-Velazquez, A. _924521 |
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| 700 | 1 |
_aAlzate-Gaviria, L. _924522 |
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| 773 | 0 |
_tEnergies _gv. 11, no. 8, art. 2101 _dBasel (Switzerland) : MDPI, 2018. _x1996-1073 |
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| 856 | 4 |
_yClick here to access online _uhttps://doi.org/10.3390/en11082101 |
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| 942 |
_cJA _n0 _2ddc |
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| 999 |
_c64470 _d64462 |
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