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14 декабря, 2021
It is nowadays widely recognized that successful implementation of industrial PHA production will only be achieved through satisfaction of sustainability aspects coupled with production of biodegradable polymers with desirable properties. Sustainability aspects include cost-competitiveness, environmental benignness and production of biodegradable polymers that serve certain market and societal needs. Additional advantages will be provided through the ability to produce PHAs with adjustable properties that could be used in different end-uses by simple modification of fermentation conditions. For instance, the production of different types of PHAs that could be used for both commodity
(e. g. food packaging) and specialty (e. g. scaffolds for tissue engineering applications) end-uses by simple modification of fermentation parameters could provide process flexibility.
An important innovation on future PHA-based processes will be the creation of cascade processing schemes in order to increase resource efficiency (Anonymous, 2012b). Cascade processing is based on the reutilization of packaging material after its use (also called postconsumer plastics) for other commercial purposes. For instance, hydrolysis into monomers could create value — added platform molecules for the chemical industry. In addition, bioplastics could be used as replacements for coal and heating fuel due to their high calorific value (Anonymous, 2012b). Reutilization of PHA-based packaging materials is strongly dependent on the development of suitable recycling technologies.
Despite their significant advantages, industrial production of PHAs is hindered by high production cost.
Previous attempts to produce PHAs in large scale had to rely on conventional fermentation technologies that cannot compete with low-cost petroleum-derived plastics. As mentioned earlier, raw material supply is one of the most important factors that should be optimized in order to reduce processing costs. For this reason, recent research focuses on the utilization of low-cost feedstock for PHA production (e. g. molasses, crude glycerol, whey, animal fats, and waste cooking oils among others) aiming to substitute for conventional and expensive carbon sources. Table 24.2 presents the results regarding PHA production from various waste and by-product streams. However, even if waste or byproduct streams are used as fermentation feedstocks, aerobic cultivation for PHA production in industrial scale operations is still an expensive unit operation. For this reason, integration of PHA production into existing industrial plants or the development of new industrial plants for PHA production should be combined
By-Product or Waste Stream |
Strain |
Type of PHA |
Maximum CellWeight |
Max PHA Concentration (g/l) |
PHA Content (%) |
Productivity (g/l h) |
References |
Waste glycerol |
Cupriavidus necator DSM 545 |
PHB |
68.8 |
26.1 |
38 |
0.84 |
Cavalheiro et al. (2009) |
Bagasse hydrolysates |
Ralstonia eutropha |
PHA |
11.1 |
6.3 |
56.5 |
— |
Yu and Stahl (2008) |
Crude glycerol and rapeseed hydrolysates |
Cupriavidus necator DSM 545 |
P(3HB-co-3HV) |
19.6 |
10.9 |
55.6 |
0.12 |
Garcia et al. (2013) |
Wheat-derived media (shake flask cultures) |
Cupriavidus necator NCIMB 11599 |
PHB |
73.2 |
51.1 |
70 |
0.3 |
Koutinas et al. (2007b) |
Wheat-derived media (bioreactor cultures) |
Wautersia eutropha NCIMB 11599 |
PHB |
175.2 |
162.8 |
93 |
0.89 |
Xu et al. (2010) |
Soybean oil |
Ralstonia eutropha H16 |
PHB |
126 |
95.8 |
76 |
0.99 |
Kahar et al. (2004) |
Ralstonia eutropha PHB-4 (DSM 541) |
P(3HB-co-3HHx) |
138 |
102.1 |
74 |
1.06 |
||
Oleic acid |
Pseudomonas putida PGA1 |
PHAs-mcl |
30.2 |
13.52 |
44.8 |
0.19 |
Marsudi et al. (2007) |
Hydrolyzed whey |
Haloferax mediterranei DSM 1411 |
PHA |
11 |
5.5 |
50 |
0.05 |
Koller et al. (2007b) |
Pseudomonas hydrogenovora DSM 1749 |
10.83 |
1.3 |
12 |
0.03 |
|||
Hydrogenophaga pseudoflava DSM 1034 |
6.75 |
2.7 |
40 |
0.05 |
|||
Hydrolyzed whey permeate |
Pseudomonas hydrogenovora |
PHB |
10.58 |
1.27 |
12 |
0.03 |
Koller et al. (2008) |
Hydrolyzed whey permeate and valerate |
DSM 1749 |
P(3HB-co-3HV) |
12 |
1.44 |
12 |
0.05 |
|
Cheese whey |
Methylobacterium sp. ZP24 |
PHB |
5.53 |
3.54 |
64 |
0.09 |
Nath et al. (2008) |
Saccharified waste potato starch |
Ralstonia eutropha NCIMB 11599 |
PHB |
179 |
94 |
55 |
1.47 |
Haas et al. (2008) |
Extruded rice bran and extruded corn starch |
Haloferax mediterranei ATCC 33500 |
PHB |
140 |
77.8 |
55.6 |
0.65 |
Huang et al. (2006) |
Sugarcane molasses and corn steep liquor |
Bacillus megaterium |
PHB |
3.6 |
2.2 |
59.4 |
— |
Gouda et al. 2001 |
Sugarcane molasses and urea |
Bacillus megaterium BA-019 |
PHB |
72.6 |
30.5 |
42 |
1.27 |
Kulpreecha et al. 2009 |
TABLE 24.2 PHA Production from Various Crude Renewable Resources, Waste and By-Product Streams |
PHA PRODUCTION INTEGRATED IN BIOREFINERY CONCEPTS 423 |
with the production of value-added co-products. This can be achieved through fractionation of agricultural resources or by-product and waste streams from existing industrial processes.
PHA production cost increases further due to downstream separation and purification of PHAs from residual microbial mass. Several methods have been reported for the recovery of PHAs based on the utilization of organic solvents such as acetone, chloroform or dichlo — roethane. However, these methods are unfavorable for large-scale production since solvents increase operational cost and additional equipment for solvent recovery is often needed. Alternative extraction methods have been also proposed including enzymatic lysis of residual microbial mass (Kapritchkoff et al., 2006; Verlin — den et al., 2007), supercritical fluid extraction (Hejazi et al., 2003), mechanical disruption of bacterial cells coupled with chemical treatment, autolysis of bacterial cells, and chemical treatment under acidic or alkaline conditions (Yu and Chen, 2006; Verlinden et al., 2007).
Several studies have also focused on the estimation of PHA production costs from different feedstocks (Choi and Lee, 1997; van Wegen et al., 1998; Posada et al.,
2011) . However, there are limited studies on the evaluation of integrated biorefineries focusing on the fractionation of the initial raw material combining the production of PHAs with the extraction or production of value-added co-products. In addition, future costing studies should also focus on the evaluation of the potential to integrate PHA production in existing industries.
In recent years, several studies focused on the production of PHAs from low-cost renewable resources (Akaraonye et al., 2010; Koller et al., 2010; Du et al.,
2012) . This study focuses on the presentation of representative biorefinery concepts targeting the production of PHAs and other value-added products. In particular, PHA production could be combined with biofuel and bioenergy production.