Cheese Whey for Producing Renewable Biofuels: History
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Agro-industrial residues such as bagasse, pomace, municipal residues, vinasse and cheese whey are an environmental problem around the world, mainly due to the huge volumes that are generated because of the food production to satisfy the nutritional needs of the growing world population. Among the above residues, cheese whey has gained special attention because of its high production with a worldwide production of 160 million tons per year. Most of it is discarded in water bodies and land causing damage to the environment due to the high biological oxygen demand caused by its organic matter load. The environmental regulations in developing countries have motivated the development of new processes to treat transform cheese whey into added-value products such as food supplements, cattle feed and food additives. 

  • bioenergy
  • cheese whey
  • bioethanol
  • biohydrogen
  • biomethane
  • biodiesel

1. Introduction

Dairy is a worldwide industry and the main waste generated by the milk transformation is whey. The world production of this waste in 2020 was 183 million tons [1]. Since governments in various jurisdictions around the world acted, except for some developing countries, it is currently illegal to dispose of untreated cheese whey in water bodies [2]. In the second half of the 20th century, community action groups, environmental agencies and processors equally recognized and highlighted the environmental damage caused by the release of untreated cheese whey. Essentially, when cheese whey is released into water bodies or directly into the soil, contributes to eutrophication in the water body and increases the acidity (depending on the discarded cheese whey type) in the soil [3]. The principal compound of cheese whey is lactose (44–46%), leading to a high biological and chemical oxygen demand (30 to 50 mg/L, and 60 to 80 mg/L, respectively) that contributes to the eutrophication [4]. The increase in acidity in the soil is highly dependent on cheese making process due to factors such as type of cheese (fresh, mozzarella, cottage), curd process and milk source have an effect. For instance, cheese whey obtained from the curding process utilizing organic acids (acid cheese whey) hold pH values between 3.5 to 4.5, and higher than 5.6 when curt-enzymes processes are used. Likewise, it has been reported that secondary cheese whey holds pH values ≤ 3 [1]. The high untreated amounts that are discarded and the pollution caused by this dairy residue have led governments from all around the world to demand industries focus on the clean production of goods and services. Likewise, secondary cheese whey resulting mainly from cottage cheese production has been used directly as feedstock to produce biofuels. However, it has been reported that the substrate has some limitations to be used in the microbial process. Some of these limitations is the increase in acidity (≥3), high dissolved oxygen (80 gL−1), high biological demand (30 gL−1) and low solid content (8 gL−1). The above nutrient limitations and the relatively small production in comparison with the other cheese whey sources are the main barriers to complete exploitation and better approach to this residue [5][6]. This situation has obligated cheese companies to create solutions to decrease their cheese whey loads by re-designing their processes and/or valorizing their by-products [7].
The exploitation of cheese whey to produce different goods has increased in recent decades. Some of the conventional goods and products are lactose, organic acids and protein fractions. During the past years, the research on the use of this residue has been intensified to produce chemical compounds for industrial sectors such as pharmaceutical, cosmetic and bioenergy [8][9][10]Figure 1 shows some of the products as well as the sectors in which cheese whey is currently used as feedstock to produce added-value compounds.
Figure 1. Biorefinery concept of cheese whey.

2. Cheese whey-based biofuels

2.1 Bioethanol

Bioethanol production through fermentation has emerged as a potential alternative to replace fossil fuels such as gasoline. This renewable biofuel not only has application in the energy industry but is widely used as a replacement for chemical or grain-based ethanol in the cosmetic, pharmaceutical, food and beverage industries [11]. It has been reported that bioethanol production from corn and sugarcane has been produced extensively by the United States and Brazil, respectively. Nevertheless, the use of the above two feedstocks increases the total production cost and compromises food security due to the high land use for these crops [12]. In this sense, different feedstocks such as different lignocellulosic biomass, starches, food wastes and agri-food residues have been used for bioethanol production. The use of cheese whey as a substrate to produce bioethanol through fermentation is economically competitive in comparison with substrates such as sugarcane, corn and lignocellulosic biomass. In addition, it is a residue, and its valorization represents several advantages in terms of sustainable development, such as a decrease in waste, and organic carbon recycling [13].

2.1 Biomethane

Methane is the one of most abundant biogas fractions produced by anaerobic di-gestion of organic residues, including cheese whey. As mentioned above, anaerobic di-gestion is a well know technology to produce methane. However, several challenges come with each specific feedstock that is used as a carbon source. These challenges can be classified into three main categories, microbiological, chemical, and operational, making anaerobic digestion one of the most complicated biological processes. Moreover, this technology is highly recommended to treat wastewater and residues with high biological oxygen demand, such as cheese whey [14]. Additionally, requirements related to the installation and operation of anaerobic biodigesters such as technology, energy consumption and space are relatively low. Nevertheless, depending on the re-actor type and feedstock the total cost can vary considerably. Likewise, the reactor type plays a key role during biogas production and classified the anaerobic digestion process into two different systems: low-rate system and high-rate system.

2.2 Biohydrogen

Methane is the one of most abundant biogas fractions produced by anaerobic di-gestion of organic residues, including cheese whey. As mentioned above, anaerobic di-gestion is a well know technology to produce methane. However, several challenges come with each specific feedstock that is used as a carbon source. These challenges can be classified into three main categories, microbiological, chemical and operational, making anaerobic digestion one of the most complicated biological processes. Moreover, this technology is highly recommended to treat wastewater and residues with high biological oxygen demand, such as cheese whey [14]. Additionally, requirements related to the installation and operation of anaerobic biodigesters such as technology, energy consumption and space are relatively low. Nevertheless, depending on the re-actor type and feedstock the total cost can vary considerably. Likewise, the reactor type plays a key role during biogas production and classified the anaerobic digestion process into two different systems: low-rate system and high-rate system.

2.3 Microbial lipids for Biodiesel

Biodiesel is one of the most popular biofuels produced due to is environmentally friendly and its net greenhouse emissions are lower in comparison with the produced from fossil fuels. Microbial lipid-base biodiesel production is one of the most promising biofuels due to its advantages (non-toxic, biodegradable, renewable, no sulfur content, high lubricity) in comparison with fossil diesel [15]. Microbial lipid-base biodiesel production is a potential alternative using low-cost residues such as cheese whey with high carbon content as a feedstock [16]. Table 1 shows a some of the research in biofuel production using cheese whey as a substrate.

Table 1. Produced biofuels using cheese whey as substrate.

Substrate

Strain

Ethanol

Concentration (g/L−1)

Volumetric

Productivity

(g L−1 h−1)

Reference

Cheese whey

(permeate)

K. marxianus URM 7404

8.90

0.66

[17]

Cheese whey

(powder)

S. cerevisiae

23.80

nd

[18]

Fresh cheese whey

K. marxianus URM 7404

25.81

2.57

[17]

 

 

 

 

 

Substrate

Inoculum

Bioreactor

Methane Yield

Reference

Cheese whey powder + vinasse

Sludge from a poultry slaughterhouse

AnSBBR

11.5 molCH4 kg COD−1

[19]

Fresh cheese whey

Sludge from the wastewater treatment plant

SBR

340.4 L CH4 kg−1 CODfeed

[20]

Cheese whey powder

Sludge from the wastewater treatment plant

Anaerobic batch

reactors

0.266 L CH4 g CODconsumed

[21]

 

 

 

 

 

Substrate

Strain

Biohydrogen

yield

Biohydrogen

productivity

Reference

Cheese whey

(permeate)

Microbial consortium

3.60 mol H2/mol of lactose

140.02 mmol H2/L day

[22]

Fresh cheese whey

Clostridium sp.

6.35 mol H2/mol lactose

139 mL/g/h

[23]

Hydrolysed cheese whey

Microbial consortium

1.93

mol H2 mol−1 of sugars

5.07

L H2 L−1 day−1

[15]

 

 

 

 

 

Substrate

Strain

Total lipid

(g/L−1)

Lipid

Accumulation (%)

Reference

Fresh cheese whey

M. circinelloides

URM 4182

1.06

22.5

[24]

Deproteinized

cheese whey

C. oligophagum JRC1

5.64

44.12

[25]

Ricotta cheese whey

M. isabelline

1757

4.49

37

[26]

 

This entry is adapted from the peer-reviewed paper 10.3390/en15186828

References

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  11. Das, B.K.; Kalita, P.; Chakrabortty, M. Integrated Biorefinery for Food, Feed, and Platform Chemicals. In Platform Chemical Biorefinery; Elsevier: Amsterdam, The Netherlands, 2016; pp. 393–416, ISBN 978-0-12-802980-0.
  12. Saini, P.; Beniwal, A.; Kokkiligadda, A.; Vij, S. Evolutionary adaptation of Kluyveromyces marxianus strain for efficient conversion of whey lactose to bioethanol. Process Biochem. 2017, 62, 69–79. https://doi.org/10.1016/j.procbio.2017.07.013.
  13. Ky, I.; Le Floch, A.; Zeng, L.; Pechamat, L.; Jourdes, M.; Teissedre, P.L. Tannins. In Encyclopedia of Food and Health; Elsevier: New York, NY, USA, 2016; pp. 486–492, ISBN 9780123849533.
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  21. Novais, R.M.; Gameiro, T.; Carvalheiras, J.; Seabra, M.P.; Tarelho, L.A.; Labrincha, J.A.; Capela, I. High pH buffer capacity biomass fly ash-based geopolymer spheres to boost methane yield in anaerobic digestion. J. Clean. Prod. 2018, 178, 258–267. https://doi.org/10.1016/j.jclepro.2018.01.033.
  22. Romão, B.B.; Silva, F.T.M.; Costa, H.C.D.B.; Carmo, T.S.D.; Cardoso, S.L.; Ferreira, J.D.S.; Batista, F.R.X.; Cardoso, V.L. Alternative techniques to improve hydrogen production by dark fermentation. 3 Biotech 2019, 9, 18. https://doi.org/10.1007/s13205-018-1538-y.
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  24. Braz, C.A.; Carvalho, A.K.F.; Bento, H.B.S.; Reis, C.E.R.; De Castro, H.F. Production of Value-Added Microbial Metabolites: Oleaginous Fungus as a Tool for Valorization of Dairy By-products. BioEnergy Res. 2020, 13, 963–973. https://doi.org/10.1007/s12155-020-10121-y.
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