Review Article
Austin Food Sci. 2016; 1(3): 1014.
Coffee Production Wastes: Potentials and Perspectives
Figueroa GA1, Homann T2 and Rawel HM3*
1Regional School of Sanitary Engineering of Water Resources, University of San Carlos of Guatemala, Guatemala
2Institute of Nutritional Science, University of Potsdam, Germany
3Instrumental Analysis in Nutritional Science, University of Potsdam, Germany
*Corresponding author: Harshadrai M Rawel, Instrumental Analysis in Nutritional Science, Institute of Nutritional Science, University of Potsdam, Germany
Received: May 17, 2016; Accepted: July 05, 2016; Published: July 06, 2016
Abstract
There has been a significant amount of research activity in the area of coffee by-products and coffee wastewater during the last few years. Most of the work is directed towards the potential uses of coffee residues, like utilization of pulp, husk and coffee silver skin as a starting material for production of enzymes and secondary metabolites including acquisition of bioactive compounds, antioxidants or food additives, on the other hand the pollution caused by coffee wastewater has also been a concern in many coffee producing countries due to the high content of organic matter and acid content resulting from the fermentation processes involved in the mucilage. This paper comments on the various research efforts for the management and treatment of coffee byproducts with focus on coffee wastewater. It is surely not exhaustive, but serves as a starting point for further research in this highly topical research field.
Keywords: Coffee by-products; Coffee waste water; Organic matter; Mucilage; Bioactive compounds; Phenolic compound; Proteins
Introduction
The forthcoming increase in world population demands for more efficient ways to achieve sustainable development and use of renewable sources. Rising concern on environmental issues drives ahead the improvement of sustainability by closing production cycles underlying the increased need to develop policies and solutions to solve these problems. This trend is also witnessed by a growing amount of research focused towards improving both environmental and economic benefits through efficient reuse of resources [1]. One of the key subjects has recently been reviewed and deals with the extraction of high value-added compounds from agri-food residues by means of supercritical technology [1]. Coffee is the most important food commodity worldwide and ranks second, after crude oil, among all commodities [2]. A recent compilation of the available information focuses in this context on the functional properties of coffee, coffee beans and by-products in terms of the associated potential health benefits [2]. A further review also considers different aspects of coffee by-products utilization and management giving a more detailed focus on the utilization for the purpose of value addition [3]. While trying to attain sustainability non-food applications are also providing economically viable alternatives [3,4]. The criterion for coffee by-products utilization to be industrially favorable is its costeffectiveness and eco-friendly nature, where the major determining factor is defined in the terms of the availability and quality of the substrates while considering the development for efficient processing in the food and non-food sectors [3].
Coffee waste product utilization
Coffee preparation proceeds in the first step by the elimination of the husks adhering to the beans and can be performed by a dry or a wet process. Coffee cherry husks thus obtained represents about 12% of the berry on dry-weight basis [3]. The dry process, also termed as “unwashed”, is the oldest practiced method, where the entire cherry after harvest is first cleaned and then placed in the sun to dry in thin layers or on patios. The wet method is called wet process or washed coffee and in this case the coffee cherries are immersed in water.
Unripe fruits will float and the good ripe ones will sink. The skin of the cherry and some of the pulp is removed by pressing the fruit in water through a screen by a machine, generating “coffee pulp juice”. The coffee pulp represents 29% dry-weight of the whole berry [3]. The beans are then put in a fermentation tank with a water stream and allowed to ferment to degrade a hygroscopic mucilaginous layer which is an obstacle to the drying. In addition this process generates wastewater which contains organic matter and also involves mucilage removal with high levels of environmental pollutants. Figure 1 shows exemplary a typical small scale factory where such waste water is generated. Both these approaches of coffee preparation are well described [3]. Coffee silver skin is an integument of coffee bean obtained as a by-product of the roasting process [3]. Finally, the fourth main coffee by-product results from the processing of soluble “instant” coffee preparation and is termed as “spent coffee” [5].
Figure 1: A small scale wet processing set-up (Santa Sofia) for coffee beans with the location in Aldea Ayarza, Casillas Santa Rosa, Guatemala.
The treatment of coffee by-products is generally realized by oxygen-driven biological methods, such as composting, which serves a dual purpose, i.e. valorization via manurial value and as well as decreasing the pollution potential [3,6]. Many studies have been directed towards this goal of composting coffee wastes [6-13], while implementing among others earthworms [14-16] or with the intention of modulating the mineral recycling [17-20]. The second principle treatment approach concerns realization of sustainability by application in fuel production including biogas [21-33], ethanol [34-36], biodiesel [37] or in briquetting of wastes from coffee plants with efforts also directed towards torrefied coffee residues [38-49]. Table 1 shows a compilation of recent advancements (2012-2016) and available studies featuring the utilization of coffee wastes.
Nr.
Type of coffee waste used
Method of utilization
Reference
1
Coffee by- and waste products (husks, skin, pulp, mucilage, parchment, silverskin, spent coffee, waste water)
Reviews: Different methods of utilization
[2,3,26,46,54,59,74,92,94]
2
Spent coffee grounds from different coffee making art
Source of bioactive compounds (e.g. Phenolic compounds - caffeoylquinic acids, antioxidant dietary fibers, triglycerides)
[51-54,56,57]
3
Spent coffee
Natural biosorbents for removal of heavy metals; Activatedcarbons/ Char
[69,95,96]
[64,66,97-99]
4
Spent coffee
Decolorization e.g. of real textile wastewaters
[62,63,67,68,70,100]
5
Coffee by-and waste products
Enzymes–e.g. xylanase in solid-state fermentation, beta-glucosidase.
[74,76,77]
6
Coffee silverskin, pulp /spent coffee
Bioethanol production via yeast strains
[34-36]
7
Coffee by- and waste products
Bioenergy–incl. pyrolysis and gasification of biomass residues –char, tar and gas production, biogas, bio-oil, torrefied biomass, briquetting etc.
[21,23,26,29-33,38,39,41,43-47 51,101-104]
8
Coffee husks / spent coffee
Composting / Fertilizer
[6,11,13,14,20]
9
Coffee husks / spent coffee
Polymer composites
[59,105]
10
Coffee husk ash reject material
Ceramic production
[82,83,106]
11
Coffee husks
Bacterial cellulose
[72]
12
Coffee husks
Potential utilization in food production
[107]
13
Spent coffee
Cosmetic formulations
[71,108]
14
Spent coffee
Building materials
[78,81,109,110]
15
Spent coffee
Biosynthesis of polyhydroxyalkanoates
[53]
Table 1: Recent advances on coffee waste utilization (2012-2016; for assessment of the situation before 2012 [3]).
The chemical composition of these four main coffee by-products and their utilization are well documented [3]. The potential uses in the food sector for the solid coffee wastes among others are for the production of enzymes and secondary metabolites. The use of waste streams with novel biotechnological methods have been proposed for the productions of bulk chemicals and value added products such as single cell protein, ethanol, organic acids, amino acids, secondary metabolites, mushrooms and enzymes [50]. Spent coffee grounds, coffee pulp and husks for examples have been utilized for polyphenol [51-57] or auxins recovery [58] among other bioactive compounds [3,54].
The valorization of the solid coffee by-products in the non-food sector has been directed among others towards reinforcement in polymer composites [53,59,60], in activation [3,61] / de-colorization (bio-sorbents) [3,62,63], use as electrode material [64-69], application in waste water treatment [62,64,66,69,70], for cosmetic products [71], cellulose production [72], enzyme production [12,73- 77], building materials [78-83] including crystalline nanoparticles [84,85], utilization in storage of gases [86] as well as in control of plant diseases [87].
Coffee pulp residues have been researched with various treatments [88-90] as also already mentioned above, but the characteristics and approaches to the treatment [91] and utilization [92] of coffee waste water generated during the wet processing require more concentrated efforts and attention. The wastewater generated in the cleaning and pulping contains compounds like proteins, antioxidants and secondary plant metabolites (reflecting the composition of the coffee pulp [3]) which can be used as by-products. Furthermore, the process of fermentation generates also wastewater with serious consequences for the environment because of their high Biochemical Oxygen Demand, Chemical Oxygen Demand values and acidic nature such that it is necessary to develop better methods of treatment in order to decrease their content, the envisaged result being to produce better wastewater quality and gaining new valuable products.
The waste water generally has a pH of 4.0 to 4.5. pH stabilization is therefore necessary and is performed by adding an alkali to obtain a pH range close to 7, which allows the proper subsequent processing of such waste. The coffee industry often recommends the use of calcium hydroxide to stabilize the pH of the wastewater although the use of bicarbonate seems to be more appropriate due to sufficient buffering capacity. If wet processing of coffee beans is being performed in big style, the untreated effluents produced will greatly exceed the self-purification capacity of the natural waterways. In order to overcome the pollution potential of processing such waste waters, a clear understanding of its constitution is inevitable to design a feasible treatment system [93].
Finally, to guarantee an efficient valorization, the by-products need to have a certain quality in order to maintain economic viable processing options. The chemical composition will vary from plant to plant from different geographic locations, depending also on their age, climate, and soil conditions [3]. Knowledge of the physical and chemical properties will lead to a better understanding of application of coffee-by products [3].
Conclusion
We have been seen a significant amount of studies regarding valorization of coffee by-products and wastewater. Some potential utilization possibilities are available, but further work in this area will definitely be more helpful for the maintaining of environment and waterways. Coffee consumption is a global issue and many countries with rich economies import these to primarily roast these according to the individual consumer demand, correspondingly the utilization of spent coffee residues appears to be much more advanced. But those countries producing and primarily processing the raw beans are burdened with low economical incomes to fight against the severe contamination posing serious environmental problems caused by wet processing resulting in coffee pulp and waste water. It is in this direction that more research has to be initiated to develop simple methods of controlling the waste by-product quality and simple solutions to not only increase the pollution awareness but to make re-processing economically more attractive. Finally, a citation in this context from [3] “… applications utilize only a fraction of available quantity as they are not technically very efficient. However, considering the high amounts of waste generated, there is still a need to find other alternative uses for this solid residue (coffee pulp) …” very appropriately underlines the present situation, if we add to it the waste water generated.
References
- Vardanega R, Prado JM, Meireles MAA. Adding value to agri-food residues by means of supercritical technology. J Supercrit Fluid. 2015; 96: 217-227.
- Esquivel P, Jimenez VM. Functional properties of coffee and coffee by-products. Food Res Int. 2012; 46: 488-495.
- Murthy PS, Naidu MM. Sustainable management of coffee industry by-products and value addition-A review. Resour Conserv Recy. 2012; 66: 45-58.
- Rathinavelu R, Graziosi G. Potential alternative use of coffee wastes and by-products ICS-UNIDO: Science Park, Padriciano, Trieste, Italy; Department of Biology, University of Trieste, Italy. 2005.
- Ramalakshmi K, Rao LJM, Takano-Ishikawa Y, Goto M. Bioactivities of low-grade green coffee and spent coffee in different in vitro model systems. Food Chem. 2009; 115: 79-85.
- Shemekite F, Gomez-Brandon M, Franke-Whittle IH, Praehauser B, Insam H, Assefa F. Coffee husk composting: an investigation of the process using molecular and non-molecular tools. Waste Manag. 2014; 34: 642-652.
- Velmourougane K, Bhat R, Gopinandhan TN. Composting coffee wastes, a potential source of ochratoxigenic fungi and ochratoxin A contamination. World Mycotoxin J. 2012; 5: 373-376.
- Salakinkop SR, Shivaprasad P, Raghuramulu Y. Manurial value and economics of composting of coffee (Coffea canephora) wastes. Indian J Agr Sci. 2005; 75: 814-816.
- Raphael K, Velmourougane K. Chemical and microbiological changes during vermicomposting of coffee pulp using exotic (Eudrilus eugeniae) and native earthworm (Perionyx ceylanesis) species. Biodegradation. 2011; 22: 497-507
- Nogueira WA, Nogueira FN, Devens DC. Temperature and pH control in composting of coffee and agricultural wastes. Water Sci Technol. 1999; 40: 113-119.
- Nascimento AF, Pires FR, Czepak MP, Fernandes AA, Rodrigues JD. Characterization of Vermicompost Produced with Straw Coffee and Cattle Manure. Rev Caatinga. 2015; 28: 1-9.
- Fujii K, Takeshi K. Penicillium strains as dominant degraders in soil for coffee residue, a biological waste unsuitable for fertilization. J Appl Microbiol. 2007; 103: 2713-2720.
- Dzung NA, Dzung TT, Khanh VTP. Evaluation of Coffee Husk Compost for Improving Soil Fertility and Sustainable Coffee Production in Rural Central Highland of Vietnam. Resources and Environment. 2013; 3: 77-82.
- Zibetti VK, Nachtigal GD, de Lima DL, Schiedeck G. Growth and Reproduction of Earthworm in Organic Waste Mixtures and Effects on Chemical and Microbial Properties of Vermicompost. Interciencia. 2015; 40: 57-62.
- Prakongkep N, Gilkes RJ, Wiriyakitnateekul W. Forms and solubility of plant nutrient elements in tropical plant waste biochars. J Plant Nutr Soil Sc. 2015; 178: 732-740.
- Orozco FH, Cegarra J, Trujillo LM, Roig A. Vermicomposting of coffee pulp using the earthworm Eisenia fetida: Effects on C and N contents and the availability of nutrients. Biol Fert Soils. 1996; 22: 162-166.
- Morikawa CK, Saigusa M. Recycling coffee grounds and tea leaf wastes to improve the yield and mineral content of grains of paddy rice. J Sci Food Agric. 2011; 91: 2108-2111.
- Morikawa CK, Saigusa M. Recycling coffee and tea wastes to increase plant available Fe in alkaline soils. Plant Soil. 2008; 304: 249-255.
- Escudero C, Gabaldon C, Marzal P, Villaescusa I. Effect of EDTA on divalent metal adsorption onto grape stalk and exhausted coffee wastes. J Hazard Mater. 2008; 152: 476-485.
- Ciesielczuk T, Rosik-Dulewska C, Wisniewska E. Possibilities of Coffee Spent Ground Use as a Slow Action Organo-mineral Fertilizer. Rocz Ochr Sr. 2015; 17: 422-437.
- Valero D, Montes JA, Rico JL, Rico C. Influence of headspace pressure on methane production in Biochemical Methane Potential (BMP) tests. Waste Manag. 2016; 48: 193-198.
- Neves L, Oliveira R, Alves MM. Anaerobic co-digestion of coffee waste and sewage sludge. Waste Manag. 2006; 26: 176-181.
- Malave' ACL, Bernardi M, Fino D, Ruggeri B. Multistep Anaerobic Digestion (MAD) as a tool to increase energy production via H2 + CH4. Int J Hydrogen Energ. 2015; 40: 5050-5061.
- Kostenberg D, Marchaim U. Anaerobic-Digestion and Horticultural Value of Solid-Waste from Manufacture of Instant Coffee. Environ Technol. 1993; 14: 973-980.
- Kostenberg D, Marchaim U. Solid-Waste from the Instant Coffee Industry as a Substrate for Anaerobic Thermophilic Digestion. Water Sci Technol. 1993; 27: 97-107.
- Hughes SR, Lopez-Nunez JC, Jones MA, Moser BR, Cox EJ, Lindquist M, et al. Sustainable conversion of coffee and other crop wastes to biofuels and bioproducts using coupled biochemical and thermochemical processes in a multi-stage biorefinery concept. Appl Microbiol Biot. 2014; 98: 8413-8431.
- Houbron E, Larrinaga A, Rustrian E. Liquefaction and methanization of solid and liquid coffee wastes by two phase anaerobic digestion process. Water Sci Technol. 2003; 48: 255-262.
- Houbron E, Gonzalez-Lopez GI, Cano-Lozano V, Rustrian E. Hydraulic retention time impact of treated recirculated leachate on the hydrolytic kinetic rate of coffee pulp in an acidogenic reactor. Water Sci Technol. 2008; 58: 1415-1421.
- Hernandez MA, Rodriguez Susa M, Andres Y. Use of coffee mucilage as a new substrate for hydrogen production in anaerobic co-digestion with swine manure. Bioresour Technol. 2014; 168: 112-118.
- de Oliveira JL, da Silva JN, Pereira EG, Oliveira D, Carvalho DR. Characterization and mapping of waste from coffee and eucalyptus production in Brazil for thermochemical conversion of energy via gasification. Renew Sust Energ Rev. 2013; 21: 52-58.
- Corro G, Paniagua L, Pal U, Banuelos F, Rosas M. Generation of biogas from coffee-pulp and cow-dung co-digestion: Infrared studies of postcombustion emissions. Energ Convers Manage. 2013; 74: 471-481.
- Chaiklangmuang S, Kurosawa K, Li LY, Morishita K, Takarada T. Thermal degradation behavior of coffee residue in comparison with biomasses and its product yields from gasification. J Energy Inst. 2015; 88: 323-331.
- Abouelenien F, Namba Y, Kosseva MR, Nishio N, Nakashimada Y. Enhancement of methane production from co-digestion of chicken manure with agricultural wastes. Bioresour Technol. 2014; 159: 80-87.
- Mussatto SI, Machado EMS, Carneiro LM, Teixeira JA. Sugars metabolism and ethanol production by different yeast strains from coffee industry wastes hydrolysates. Appl Energ. 2012; 92: 763-768.
- Menezes EG, do Carmo JR, Alves JG, Menezes AG, Guimares IC, Queiroz F, et al. Optimization of alkaline pretreatment of coffee pulp for production of bioethanol. Biotechnol Prog. 2014; 30: 451-462.
- Gurram R, Al-Shannag M, Knapp S, Das T, Singsaas E, Alkasrawi M. Technical possibilities of bioethanol production from coffee pulp: a renewable feedstock. Clean Technol Envir. 2016; 18: 269-278.
- Kondamudi N, Mohapatra SK, Misra M. Spent coffee grounds as a versatile source of green energy. J Agric Food Chem. 2008; 56: 11757-11760.
- Zanella E, Della Zassa M, Navarini L, Canu P. Low-Temperature Co-pyrolysis of Polypropylene and Coffee Wastes to Fuels. Energ Fuel. 2013; 27: 1357-1364.
- Tsai WT, Liu SC. Effect of temperature on thermochemical property and true density of torrefied coffee residue. J Anal Appl Pyrol. 2013; 102: 47-52.
- Soares LD, Moris VAD, Yamaji FM, de Paiva JMF. Use of Waste Coffee Grounds and Sawdust in Briquettes Molding and Evaluation of Properties. Materia-Brazil. 2015; 20: 550-560.
- Zerbinatti OE, da Silva AB, Pereira AJ, Miranda JM. Briquetting of wastes from coffee plants conducted in zero harvest system. Semin-Cienc Agrar. 2014; 35: 1143-1152.
- Saenger M, Hartge EU, Werther J, Ogada T, Siagi Z. Combustion of coffee husks. Renew Energ. 2001; 23: 103-121.
- Rincon SL, Gomez A. Comparative Behaviour of Agricultural Biomass Residues during Thermochemical Processing. Global Nest J. 2012; 14: 111-117.
- Protasio TD, de Melo ICNA, Guimaraes M, Mendes RF, Trugilho PF. Thermal Decomposition of Torrefied and Carbonized Briquettes of Residues from Coffee Grain Processing. Cienc Agrotec. 2013; 37: 221-228.
- Protasio TD, Bufalino L, Tonoli GHD, Guimaraes M, Trugilho PF, Mendes LM. Brazilian Lignocellulosic Wastes for Bioenergy Production: Characterization and Comparison with Fossil Fuels. Bioresources. 2013; 8: 1166-1185.
- Mokhtar NM, Omar R, Idris A. Microwave Pyrolysis for Conversion of Materials to Energy: A Brief Review. Energ Source Part A. 2012; 34: 2104-2122.
- Jeguirim M, Bikai J, Elmay Y, Limousy L, Njeugna E. Thermal characterization and pyrolysis kinetics of tropical biomass feedstocks for energy recovery. Energy Sustain Dev. 2014; 23:188-193.
- Fernandez Y, Menendez JA. Influence of feed characteristics on the microwave-assisted pyrolysis used to produce syngas from biomass wastes. J Anal Appl Pyrol. 2011; 91: 316-322.
- Becidan M, Varhegyi G, Hustad JE, Skreiberg O. Thermal decomposition of biomass wastes. A kinetic study. Ind Eng Chem Res. 2007; 46: 2428-2437.
- van Dam JEG, Harmsen P. Coffee residues utilization. Wageningen: Wageningen UR Food & Biobased Research. 2010; 75.
- Zuorro A, Lavecchia R. Spent coffee grounds as a valuable source of phenolic compounds and bioenergy. J Clean Prod. 2012; 34: 49-56.
- Zuorro A. Optimization of polyphenol recovery from espresso coffee residues using factorial design and response surface methodology. Sep Purif Technol. 2015; 152: 64-69.
- Obruca S, Benesova P, Petrik S, Oborna J, Prikryl R, Marova I. Production of polyhydroxyalkanoates using hydrolysate of spent coffee grounds. Process Biochem. 2014; 49: 1409-1414.
- Murthy PS, Naidu MM. Recovery of Phenolic Antioxidants and Functional Compounds from Coffee Industry By-Products. Food Bioprocess Tech. 2012; 5: 897-903.
- Marchaim U, Kostenberg D, Epstein E. Auxins and phenols in anaerobic thermophilic digestion of coffee wastes and their synergistic effect in horticulture. Microbiologiya. 1997; 66: 693-698.
- Manna L, Bugnone CA, Banchero M. Valorization of hazelnut, coffee and grape wastes through supercritical fluid extraction of triglycerides and polyphenols. J Supercrit Fluid. 2015; 104: 204-211.
- Bravo J, Juaniz I, Monente C, Caemmerer B, Kroh LW, De Pena MP, et al. Evaluation of spent coffee obtained from the most common coffeemakers as a source of hydrophilic bioactive compounds. J Agric Food Chem. 2012; 60: 12565-12573.
- Machado CM, Soccol CR, de Oliveira BH, Pandey A. Gibberellic acid production by solid-state fermentation in coffee husk. Appl Biochem Biotechnol. 2002; 102-103: 179-191.
- Yusriah L, Sapuan SM, Zainudin ES, Mariatti M. Underutilized Malaysian Agro-wastes Fiber as Reinforcement in Polymer Composites: Potential and Challenges. J Polym Mater. 2012; 29: 201-216.
- Reis KC, Pereira L, Melo ICNA, Marconcini JM, Trugilho PF, Tonoli GHD. Particles of Coffee Wastes as Reinforcement in Polyhydroxybutyrate (PHB) Based Composites. Mater Res-Ibero-Am J. 2015; 18: 546-552.
- Goncalves M, Souza VC, Galhardo TS, Mantovani M, Figueiredo FCA, Mandelli D, et al. Glycerol Conversion Catalyzed by Carbons Prepared from Agroindustrial Wastes. Ind Eng Chem Res. 2013; 52: 2832-2839.
- dos Santos DC, Adebayo MA, Pereira SDP, Prola LDT, Cataluna R, Lima EC, et al. New carbon composite adsorbents for the removal of textile dyes from aqueous solutions: Kinetic, equilibrium, and thermodynamic studies. Korean J Chem Eng. 2014; 31: 1470-1479.
- Chinmai K, Hamsa BC, Dsouza KD, Mahesh Chandra BR, Shilpa BS. Feasibility Studies on Spent Coffee Grounds Biochar as an Adsorbent for Color Removal. International Journal of Application or Innovation in Engineering & Management (IJAIEM). 2014; 3: 9-13.
- Yang CY, Liu YY, Ma CY, Norton M, Qiao JL. Preparing Desirable Activated Carbons from Agricultural Residues for Potential Uses in Water Treatment. Waste Biomass Valori. 2015; 6: 1029-1036.
- Rufford TE, Hulicova-Jurcakova D, Zhu ZH, Lu GQ. Nanoporous carbon electrode from waste coffee beans for high performance super capacitors. Electrochem Commun. 2008; 10: 1594-1597.
- Nowicki P, Skibiszewska P, Pietrzak R. NO2 removal on adsorbents prepared from coffee industry waste materials. Adsorption. 2013; 19: 521-528.
- Kyzas GZ, Lazaridis NK, Mitropoulos AC. Removal of dyes from aqueous solutions with untreated coffee residues as potential low-cost adsorbents: Equilibrium, reuse and thermodynamic approach. Chem Eng J. 2012; 189: 148-159.
- Kyzas GZ. A Decolorization Technique with Spent "Greek Coffee" Grounds as Zero-Cost Adsorbents for Industrial Textile Wastewaters. Materials. 2012; 5: 2069-2087.
- Kyzas GZ. Commercial Coffee Wastes as Materials for Adsorption of Heavy Metals from Aqueous Solutions. Materials. 2012; 5: 1826-1840.
- Nitayaphat W, Jintakosol T, Engkaseth K, Wanrakakit Y. Removal of Methylene Blue from Aqueous Solution by Coffee Residues. Chiang Mai J Sci. 2015; 42: 407-416.
- Ribeiro H, Marto J, Raposo S, Agapito M, Isaac V, Chiari BG, et al. From coffee industry waste materials to skin-friendly products with improved skin fat levels. Eur J Lipid Sci Tech. 2013; 115: 330-336.
- Rani MU, Appaiah KA. Production of bacterial cellulose by Gluconacetobacter hansenii UAC09 using coffee cherry husk. J Food Sci Technol. 2013; 50: 755-762.
- Murthy PS, Naidu MM, Srinivas P. Production of alpha-amylase under solid-state fermentation utilizing coffee waste. J Chem Technol Biot. 2009; 84: 1246-1249.
- Murthy PS, Naidu MM. Production and Application of Xylanase from Penicillium sp Utilizing Coffee By-products. Food Bioprocess Tech. 2012; 5: 657-664.
- Macedo GA, Matsuda LK, Battestin V. Screening of tanase producing fungi present in rich tannin vegetable residues. Cienc Agrotec. 2005; 29: 833-838.
- Knob A, Fortkamp D, Prolo T, Izidoro SC, Almeida JM. Agro-residues as Alternative for Xylanase Production by Filamentous Fungi. Bioresources. 2014; 9: 5738-5773.
- Dias M, Melo MM, Schwan RF, Silva CF. A new alternative use for coffee pulp from semi-dry process to β-glucosidase production by Bacillus subtilis. 2015; 61: 588-595.
- Gama NV, Soares B, Freire CSR, Silva R, Neto CP, Barros-Timmons A, et al. Bio-based polyurethane foams toward applications beyond thermal insulation. Mater Design. 2015; 76: 77-85.
- Eliche-Quesada D, Martinez-Garcia C, Martinez-Cartas ML, Cotes-Palomino MT, Perez-Villarejo L, Cruz-Perez N, et al. The use of different forms of waste in the manufacture of ceramic bricks. Appl Clay Sci. 2011; 52: 270-276.
- Eliche-Quesada D, Perez-Villarejo L, Iglesias-Godino FJ, Martinez-Garcia C, Corpas-Iglesias FA. Incorporation of coffee grounds into clay brick production. Adv Appl Ceram. 2011; 110: 225-232.
- Arulrajah A, Maghoolpilehrood F, Disfani MM, Horpihulsuk S. Spent coffee grounds as a non-structural embankment fill material: engineering and environmental considerations. J Clean Prod. 2014; 72: 181-186.
- Acchar W, Dultra EJV, Segadaes AM. Untreated coffee husk ashes used as flux in ceramic tiles. Appl Clay Sci. 2013; 75-76: 141-147.
- Acchar W, Dultra EJV. Thermal analysis and X-ray diffraction of untreated coffee's husk ash reject and its potential use in ceramics. J Therm Anal Calorim. 2013; 111: 1331-1334.
- Espindola-Gonzalez A, Martinez-Hernandez AL, Angeles-Chavez C, Castano VM, Velasco-Santos C. Novel Crystalline SiO2 Nanoparticles via Annelids Bioprocessing of Agro-Industrial Wastes. Nanoscale Res Lett. 2010; 5: 1408-1417.
- Alfaro ME, Barrantes MFC, Villalta GAJ, Amador KR. Coffee wastes as potential source of nanocellulose. Abstr Pap Am Chem S. 2014; 247.
- Akasaka H, Takahata T, Toda I, Ono H, Ohshio S, Himeno S, et al. Hydrogen storage ability of porous carbon material fabricated from coffee bean wastes. Int J Hydrogen Energ. 2011; 36: 580-585.
- Alstrom S. Antibacterial Activity of Tea and Coffee Wastes against Some Plant Pathogenic Pseudomonas-Syringae Strains. J Phytopathol. 1992; 136: 329-334.
- Ulloa Rojas JB, Verreth JA, Amato S, Huisman EA. Biological treatments affect the chemical composition of coffee pulp. Bioresour Technol. 2003; 89: 267-274.
- Rojas JBU, Verreth JAJ. Growth of Oreochromis aureus fed with diets containing graded levels of coffee pulp and reared in two culture systems. Aquaculture. 2003; 217: 275-283.
- Bello Mendoza R, Sanchez JE. Anaerobic filter treatment of wastewater from mushroom cultivation on coffee pulp. World J Microb Biot. 1997; 13: 51-55.
- Ramya PM, Jayasravanthi M, Dulla BJ, Venkata NR. Chemical Oxygen Demand Reduction from Coffee Processing Waste Water - a Comparative Study on Usage of Biosorbents Prepared from Agricultural Wastes. Global Nest J. 2015; 17: 291-300.
- Rattan S, Parande AK, Nagaraju VD, Ghiwari GK. A comprehensive review on utilization of wastewater from coffee processing. Environ Sci Pollut Res Int. 2015; 22: 6461-6472.
- von Enden JC, Calvert KC. Review of coffee waste water characteristics and approaches to treatment. PPP Project, Improvement of Coffee Quality and Sustainability of Coffee Production in Vietnam”. German Technical Cooperation Agency (GTZ) Khe Sanh, Huong Hoa, Quang Tri, SR Vietnam / CEO Renertech Consulting. 159 St. Andrew Street, Invercargill, 9501. New Zealand. 2002.
- Ravindran R, Jaiswal AK. Exploitation of Food Industry Waste for High-Value Products. Trends Biotechnol. 2016; 34: 58-69.
- Imessaoudene D, Hanini S, Bouzidi A, Ararem A. Kinetic and thermodynamic study of cobalt adsorption by spent coffee. Desalin Water Treat. 2016; 57: 6116-6123.
- Wu CH, Kuo CY, Guan SS. Adsorption of heavy metals from aqueous solutions by waste coffee residues: kinetics, equilibrium, and thermodynamics. Desalin Water Treat. 2016; 57: 5056-5064.
- Jutakridsada P, Prajaksud C, Kuboonya-Aruk L, Theerakulpisut S, Kamwilaisak K. Adsorption characteristics of activated carbon prepared from spent ground coffee. Clean Technol Envir. 2016; 18: 639-645.
- Nowicki P, Kazmierczak-Razna J, Skibiszewska P, Wisniewska M, Nosal-Wiercinska A, Pietrzak R. Production of activated carbons from biodegradable waste materials as an alternative way of their utilisation. Adsorption. 2016; 22: 489-502.
- Popovici D, Dusescu C, Neagu M. Removal of Phenol from Aqueous Solutions on Activated Carbon Obtained from Coffee Grounds. Rev Chim-Bucharest. 2016; 67: 751-756.
- Lafi R, Hafiane A. Removal of Methyl Orange (MO) from aqueous solution using cationic surfactants Modified Coffee Waste (MCWs). J Taiwan Inst Chem E. 2016; 58: 424-433.
- Battista F, Fino D, Mancini G. Optimization of biogas production from coffee production waste. Bioresour Technol. 2016; 200: 884-890.
- Dohlert P, Weidauer M, Enthaler S. Spent coffee ground as source for hydrocarbon fuels. J Energy Chem. 2016; 25: 146-152.
- Sakuragi K, Li P, Otaka M, Makino H. Recovery of Bio-Oil from Industrial Food Waste by Liquefied Dimethyl Ether for Biodiesel Production. Energies. 2016; 9: 106.
- Yang LX, Nazari L, Yuan ZS, Corscadden K, Xu CB, He Q. Hydrothermal liquefaction of spent coffee grounds in water medium for bio-oil production. Biomass Bioenerg. 2016; 86: 191-198.
- Iyer KA, Zhang LH, Torkelson JM. Direct Use of Natural Antioxidant-rich Agro-wastes as Thermal Stabilizer for Polymer: Processing and Recycling. Acs Sustain Chem Eng. 2016; 4: 881-889.
- Acchar W, Avelino KA, Segadaes AM. Granite waste and coffee husk ash synergistic effect on clay-based ceramics. Adv Appl Ceram. 2016; 135: 236-242.
- Bondesson E. A nutritional analysis on the by-product coffee husk and its potential utilization in food production. Swedish University of Agricultural Sciences. Uppsala: Swedish University of Agricultural Sciences. 2015.
- Marto J, Gouveia LF, Chiari BG, Paiva A, Isaac V, Pinto P, et al. The green generation of sunscreens: Using coffee industrial sub-products. Ind Crop Prod. 2016; 80: 93-100.
- Arulrajah A, Kua TA, Phetchuay C, Horpibulsuk S, Mahghoolpilehrood F, Disfani MM. Spent Coffee Grounds-Fly Ash Geopolymer Used as an Embankment Structural Fill Material. J Mater Civil Eng. 2016; 28.
- Velasco PM, Mendivil MA, Morales MP, Munoz L. Eco-fired clay bricks made by adding spent coffee grounds: a sustainable way to improve buildings insulation. Mater Struct. 2016; 49: 641-650.