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Extended Abstract

Effect of Inorganic Coagulants on the Characteristics in Anaerobic Digested Distillery Stillage Valorization †

Department of Environment Engineering, University of Warmia and Mazury in Olsztyn, Warszawska St. 117a, 10-720 Olsztyn, Poland
*
Author to whom correspondence should be addressed.
Presented at Environment, Green Technology and Engineering International Conference (EGTEIC 2018), Caceres, Spain, 18–20 June 2018.
Proceedings 2018, 2(20), 1271; https://doi.org/10.3390/proceedings2201271
Published: 17 October 2018

Abstract

:
The aim of the study was to determine the possibility of using coagulation for treatment of anaerobically digested distillery stillage. Post-fermentation sludge from waste product of bioethanol production is usually drained. Then, condensed sediments are directed as a fertilizer for arable fields. The remaining liquid phase due to the high content of organic compounds cannot be discharged to environment. The study used inorganic salts of iron and aluminum as coagulants to treatment liquid fraction obtained after methane fermentation of distillery stillage. In valorization process, the reduction of organic compounds and suspended solids was not sufficient. The highest doses of coagulants reduced COD concentration of about 80% and lower the pH of the solution. However, the dose 10 mL/L is not economically profitable and due to concentration of aluminum or iron it is too harmful for environment.

1. Introduction

Depleting fossil fuel resources have increased interest in renewable sources of energy. The most popular among biofuels is bioethanol. In 2015, the bioethanol global production reached the level of 98 billion liters. Distillery stillage is the main waste product of bioethanol production. Inappropriate disposal of the stillage leads to pollution of soil, surface- and ground-waters. The bioethanol production sector faces noticeable challenges, as awareness regarding the environmental impacts caused by the uncontrolled disposal of stillage grows.
Approximately 13 L of stillage per every L of bioethanol is produced in the bioethanol process. [1]. Distillery stillage is characterized by complex composition, high BOD5 values and low pH value, its disposal is a serious environmental problem [2]. Depending on the raw material used to produce bioethanol, concentration of COD of stillage ranges from 10 g O2/L [3,4] to more than 100 g O2/L [5]. They also contain substances such as potassium, phosphates, nitrogen, calcium and sulphates [6,7]. The stillage has relatively low sugar content, mainly glucose, but on the other hand, it contains residues of degraded yeast cells, so it could be considered a good nitrogen source [8].
Since stillage contains many valuable ingredients, it is used as fodder, as a base for further microbiological production (for example biogas), as a fertilizer, etc. [9]. The stillage can be processed as a whole or it is screened or centrifuged to produce thin stillage and wet distillers’ grain. Separation of wastewaters to tin and concentrated fractions gives new possibilities of their uses [10].
Coagulation and flocculation are the essential processes used for the removal of particulates and organic matter from wastewaters, and are usually conducted by adding chemicals such as salts of aluminum and iron and polyelectrolytes. Coagulation is a chemical process that involves neutralization of charge whereas flocculation is a physical process and does not involve neutralization of charge. Coagulation itself results in the formation of floc but flocculation is required to help the floc further aggregate and settle.
The proposed solution for management of post-fermentation effluent from fermentation tank with distillery stillage is to use coagulation. Post-fermentation sludge from biogas plants is usually drained. Then, condensed sediments are directed as a fertilizer for arable fields. The remaining liquid phase due to the high content of organic compounds cannot be discharged to environment. The study used inorganic salts of iron and aluminum as coagulants to treatment liquid fraction obtained after methane fermentation of distillery stillage.

2. Material and Methods

The study involved the use of liquid leachate from drainage of post-fermentation sludge. The characteristic of anaerobic digested distillery stillage is presented in Table 1. Four kinds of coagulants with commercial names of PIX 111—iron (III) chloride solution ((Fe) 13.4 ± 0.6%, (Fe2+) max 0.3%), PIX 123—iron (III) sulfate solution ((Fe) 12.6 ± 0.3%, (Fe2+) max 0.7%), PAX 16—aluminum polychloride solution (Al2O3 16%) and PAX XL 19H—aluminium polychloride solution (Al2O3 23.6%) were used. The coagulant dosage ranged from 25 to 400 μL/L. Anaerobic digested distillery stillage samples were stirred with coagulants at 400 rpm for 1 min, then the mixing speed was reduced to 80 rpm for 5 min for flocculation. The sedimentation phase lasted 30 min.
COD concentrations were measured with cuvette testes (Hach Lange USA, Loveland, CO, USA) and spectrophotometer UV/VIS (DR 5000). The pH was measured with multiparameter (Hach Lange HQ 440D).

3. Results and Discussion

Usually higher COD removal was achieved with aluminum-contained coagulants. However, the highest COD reduction was achieved with the use of the coagulant PIX 111 in a dose of 300 μL/L (Figure 1). The COD concentration in valorized solution reached 5527 ± 106.82 mg O2/L. As valorization process ensured only 34% reduction in COD, in the subsequent studies higher coagulant doses were used, ranged from 0.8 mL/L to 10 mL/L of digestate.
Using PIX 111 with a dose of 10 mL/L, COD concentration in coagulated liquid fraction of digestate of 1480 ± 132.14 mg O2/L was achieved. In turn, the same dose of PIX 123 and PAX 16 ensured COD reduction to the level of 2000 mg O2/L (Figure 2.). The lowest COD removal was noted during the coagulation with PAX XL 19H. Despite high efficiency of COD removal with a dose of coagulat of 10 mL/L, the process is economically unprofitable. This dose of coagulant also introduce high amount of aluminum/iron in the obtained sludge.
The coagulation of liquid fraction from methane fermentation of distillery stillage influenced on the pH values in the obtained solution. The use of high doses of inorganic coagulants resulted in a significant decrease in pH of the valorized digestate (Figure 3).
The use of the coagulation process appears to be ineffective for treatment of liquid fraction from methane fermentation of distillery stillage. Organic matter removal was low, even at high dosages of coagulants it was not sufficient. Moreover, coagulation generated large amounts of solids difficult to remove via gravity sedimentation. The color of the anaerobic digested distillery stillage was removed slightly.

Author Contributions

M.Z. and M.D. conceived and designed the experiments; M.D. and P.R. performed the experiments; M.D. and M.Z. analyzed the data; M.D. and P.R. contributed reagents/materials/analysis tools; M.D. wrote the paper.

Acknowledgments

The study was carried out in the framework of the project under a program BIOSTRATEG funded by the National Centre for Research and Development “Processing of waste biomass in the associated biological and chemical processes “BIOSTRATEG2/296369/5/NCBR/2016.

Conflicts of Interest

The authors declare no conflict of interest. The founding sponsors had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript, and in the decision to publish the results.

References

  1. Kim, J.S.; Kim, B.G.; Lee, C.H.; Kim, S.W.; Jee, H.S.; Koh, J.H.; Fane, A.G. Development of clean technology in alcohol fermentation industry. J. Clean. Prod. 1997, 5, 263–267. [Google Scholar] [CrossRef]
  2. Mojovi’c, L.; Pejin, D.; Rakin, M.; Pejin, J.; Nikoli’c, S.; Djuki’c-Vukovi’c, A. How to improve the economy of bioethanol production in Serbia. Renew. Sustain. Energy Rev. 2012, 16, 6040–6047. [Google Scholar] [CrossRef]
  3. España-Gamboa, E.; Mijangos-Cortes, J.; Barahona-Perez, L.; Dominguez-Maldonado, J.; Hernandez-Zarate, G.; Alzate-Gaviria, L. Vinasses: Characterization and treatments. Waste Manag. Res. 2011, 29, 1–16. [Google Scholar] [CrossRef]
  4. Kharayat, Y. Distillery wastewater: Bioremediation approaches. J. Integr. Environ. Sci. 2012, 9, 69–91. [Google Scholar] [CrossRef]
  5. Robles-González, V.; Galíndez-Mayer, J.; Rinderknecht-Seijas, N.; Poggi-Varaldo, H.M. Treatment of mezcal vinasses: A review. J. Biotechnol. 2012, 157, 524–546. [Google Scholar] [CrossRef]
  6. Mutton, M.A.; Rossetto, R.; Mutton, M.J.R. Agricultural Use of Stillage. In Sugarcane Bioethanol—R&D for Productivity and Sustainability; Cortez, L.A.B., Ed.; Edgard Blücher: São Paulo, Brazil, 2014; pp. 423–440. [Google Scholar]
  7. Wilkie, A.C.; Riedesel, K.J.; Owens, J.M. Stillage Characterization and Anaerobic Treatment of Ethanol Stillage from Conventional and Cellulosic Feedstocks. Biomass Bioenergy 2000, 19, 63–102. [Google Scholar] [CrossRef]
  8. Kosseva, M. Sources, characterization and composition of food industry wastes. In Food Industry Wastes: Assessment and Recuperation of Commodities; Kosseva, M., Webb, C., Eds.; Academic Press: London, UK, 2013; pp. 44–48. [Google Scholar]
  9. Qian, P.; Schoenau, J.; Urton, R. Effect of Soil Amendment with Thin Stillage and Glycerol on Plant Growth and Soil Properties. J. Plant Nutr. 2011, 34, 2206–2221. [Google Scholar] [CrossRef]
  10. de Sena, R.F.; Claudino, A.; Moretti, K.; Bonfanti, I.C.P.; Moreira, R.F.P.M. ; José, HJ Biofuel Application of Biomass Obtained from a Meat Industry Wastewater Plant through the Flotation Process—A Case Study. Resour. Conserv. Recycl. 2008, 52, 557–569. [Google Scholar] [CrossRef]
Figure 1. Efficiency of COD removal by coagulation with PIX 111, PIX 123, PAX 16, PAX 19H in the dose ranged from 25–400 μL/L.
Figure 1. Efficiency of COD removal by coagulation with PIX 111, PIX 123, PAX 16, PAX 19H in the dose ranged from 25–400 μL/L.
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Figure 2. Efficiency of COD removal by coagulation with PIX 111, PIX 123, PAX 16, PAX 19H in the dose ranged from 0.8 to 10 mL/L.
Figure 2. Efficiency of COD removal by coagulation with PIX 111, PIX 123, PAX 16, PAX 19H in the dose ranged from 0.8 to 10 mL/L.
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Figure 3. pH during coagulation in the doses of coagulants from 25 to 400 μL/L.
Figure 3. pH during coagulation in the doses of coagulants from 25 to 400 μL/L.
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Table 1. Characteristic of anaerobically digested distillery stillage.
Table 1. Characteristic of anaerobically digested distillery stillage.
IndicatorUnitValue
pH 7.8
CODmg O2/L8365 ± 23
Total nitrogenmg Ntot/L1688 ± 88
Total phosporusmg P-PO4/L192 ± 13
Total solidsmg/L7115 ± 102
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MDPI and ACS Style

Dudek, M.; Rusanowska, P.; Zieliński, M.; Dębowski, M. Effect of Inorganic Coagulants on the Characteristics in Anaerobic Digested Distillery Stillage Valorization. Proceedings 2018, 2, 1271. https://doi.org/10.3390/proceedings2201271

AMA Style

Dudek M, Rusanowska P, Zieliński M, Dębowski M. Effect of Inorganic Coagulants on the Characteristics in Anaerobic Digested Distillery Stillage Valorization. Proceedings. 2018; 2(20):1271. https://doi.org/10.3390/proceedings2201271

Chicago/Turabian Style

Dudek, Magda, Paulina Rusanowska, Marcin Zieliński, and Marcin Dębowski. 2018. "Effect of Inorganic Coagulants on the Characteristics in Anaerobic Digested Distillery Stillage Valorization" Proceedings 2, no. 20: 1271. https://doi.org/10.3390/proceedings2201271

APA Style

Dudek, M., Rusanowska, P., Zieliński, M., & Dębowski, M. (2018). Effect of Inorganic Coagulants on the Characteristics in Anaerobic Digested Distillery Stillage Valorization. Proceedings, 2(20), 1271. https://doi.org/10.3390/proceedings2201271

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