Abstract
The biotechnological potential of microalgae has been the target of a range of research aimed at using its potential to produce macromolecules with high added value. Particular focus has been given to biofuels' production, such as biohydrogen, biodiesel, and bioethanol from lipids and carbohydrates extracted from microalgal biomass. Bioprospecting and accurate identification of microalgae from the environment are important in the search for strains with better performance. Methodologies that combine morphology and molecular techniques allow more precise knowledge of species. Thereby, this work aimed to identify the new strain LGMM0013 collected at Iraí Reservoir, located in Paraná state, Brazil, and to evaluate the production of biomass, carbohydrates, and lipids from this new microalgal strain. Based on morphology and phylogenetic tree from internal transcribed spacer (ITS), strain LGMM0013 was identified as Desmodesmus abundans. D. abundans accumulated 1500 mg L-1 of dried biomass after 22 days of cultivation in autotrophic conditions, 50% higher than Tetradesmus obliquus (LGMM0001) (Scenedesmaceae-Chlorophyceae), usually grown in photobioreactors located at NPDEAS at the Federal University of Paraná (UFPR) to produce biomass. Analysis of the D. abundans biomass from showed an accumulation of 673.39 mg L-1 of carbohydrates, 130% higher than T. obliquus (LGMM0001). Lipid production was 259.7 mg L-1, equivalent to that of T. obliquus. Nitrogen deprivation increased the production of biomass and carbohydrates in D. abundans LGMM0013, indicating this new strain greater biomass production capacity.
Keywords: bioprospection; carbohydrates; ITS sequences; lipids; nitrogen deprivation
Resumo
O potencial biotecnológico das microalgas tem sido alvo de uma série de pesquisas que visam utilizar seu potencial para produzir macromoléculas de alto valor agregado. Uma especial atenção tem sido dada à produção de biocombustíveis, como biohidrogênio, biodiesel e bioetanol, a partir de lipídios e carboidratos de microalgas. A bioprospecção e a identificação precisa de microalgas são importantes na busca de linhagens com melhor desempenho em termos de produção de biomassa e lipídios. Metodologias que combinam morfologia e técnicas moleculares permitem uma identificação mais precisa das espécies. Assim, este trabalho teve como objetivo identificar a nova cepa LGMM0013 coletada na Represa do Iraí, localizado no estado do Paraná, Brasil e avaliar a produção de biomassa, carboidratos e lipídios. Com base na morfologia e na árvore filogenética obtida com sequências ITS (“Internal Transcribed Spacer”), a cepa LGMM0013 foi identificada como Desmodesmus abundans. D. abundans acumulou 1500 mg L-1 de biomassa seca após 22 dias de crescimento em condições autotróficas, 50% superior a Tetradesmus obliquus (LGMM0001) (Scenedesmaceae-Chlorophyceae), uma cepa cultivada frequentemente em fotobiorreatores para produção de biomassa no NPDEAS, na Universidade Federal do Paraná (UFPR) para a produção de biomassa. Na análise da biomassa de D. abundans LGMM0013 constatou-se acúmulo de 673,39 mg L-1 de carboidratos, 130% maior que T. obliquus (LGMM0001). A produção de lipídios foi de 259,7 mg L-1, equivalente à de T. obliquus. A privação de nitrogênio aumentou a produção de biomassa e carboidratos em D. abundans LGMM0013, indicando uma maior capacidade de produção de biomassa desta cepa.
Palavras-chave: bioprospecção; carboidratos; sequências ITS; lipídios; privação de nitrogênio
1. Introduction
Microalgae have been the focus of numerous biotechnological researches due to their potential for producing molecules with high added value (Pang et al., 2019). The use of biomass from microalgae to produce biofuels is one of the biggest challenges in the area. Obtaining sufficient biomass for industrial-scale application and the extraction of the macromolecules of interest suffers from the process's high costs (González-Balderas et al., 2020). The search for strains with high productive potential, easy to handle and survive in a controlled environment could be the solution to this problem (Hadi et al., 2016). The production of macromolecules by microalgae may be affected by cultivation factors, such as nutrient deprivation, pH, temperature, and light incidence (Wase et al., 2018). Find the best cultivation condition is a strategy to overcome the limitations.
Microalgae cultivation has gained prominence for enhancing the production of molecules of interest while promoting wastewater decontamination. Nitrogen and phosphorous could be removed from wastewater (Wang et al., 2022), and even wastewater from swine (Caprio et al., 2019; Miyawaki et al., 2021) or cattle (Scherer et al., 2017) manure could be used for microalgae cultivation. By combining different cultivation conditions with the idea of biorefineries, a wide variety of biomass products would be obtained, eventually allowing the process to be sustainable, by becoming energetically and economically viable ('t Lam et al., 2018). Aiming to achieve such goals, the NPDEAS (http://npdeas.blogspot.com/) research group has been developing microalgae cultivation based projects, especially through an indigenous strain of Tetradesmus obliquus (LGMM0001), which has been shown to bear different environmental conditions, even when grown in 10,000 liter photobioreactors. Biomass (Silva et al., 2013; Selesu et al., 2016; Miyawaki et al., 2021), lipids (Hesse et al., 2017; Escorsim et al., 2018), and biohydrogen (Vargas et al., 2014; Corrêa et al., 2017; Dias et al., 2019) are some of the bioproducts evaluated for T. obliquus (syn. Acutodesmus obliquus, Scenedesmus obliquus) in the search for economically viable energy production. Such studies have shown that bioproducts diversification and production maximization could eventually lead to feasible and economically competitive plants.
Some Scenedesmaceae genera like Desmodesmus, Tetradesmus, and Scenedesmus have demonstrated good biomass productivity, and interest molecules accumulation, such as lipids and carbohydrates (Hess et al., 2018; Akgül et al., 2021; Najeeb et al., 2024). Changes in cultivation conditions, such as nutrient deprivation and addition of heavy metals, can affect the biomass and macromolecules’ production by Desmodesmus (Abinandan et al., 2019).
An essential step beyond the bioprospecting of new microalgae isolated from the natural habitat is the taxonomic identification approaches that combine morphological and molecular analysis (Leliaert et al., 2012). Morphologically, the genus Desmodesmus is commonly identified by the analysis of its unique cells, formation and alignment of the coenobia, in addition to the presence of a layer of sporolenin in the cell wall, which allows the formation of spines and other ornamentations, very characteristic of the genus (An et al., 1999; Hegewald, 2000).
The high degree of phenotypic variability found in different organisms leads to inconsistencies and misidentification based only on morphological characteristics. This challenge has been overcome through taxonomic reviews and the identification of new strains based on molecular analyzes (Lortou and Gkelis, 2019), such as the sequencing of the internal transcribed spacer 2 (ITS-2) rDNA region, that allowed the separation of the genus Desmodesmus, previously identified as Scenedesmus (An et al., 1999).
In this sense, the main objectives of this study were: i) to bioprospecting the isolate D. abundans LGMM0013 and quantify its biomass, carbohydrates and lipids production; ii) to identify the isolate D. abundans LGMM0013 taxonomically by morphological and molecular analysis; iii) to know its physiological response to changes in cultivation condition.
2. Material and Methods
2.1. Isolation
Samples were collected from the Iraí Reservoir (25°25.31’S, 49°06.22’W), located in the metropolitan region of Curitiba city, Brazil. Samples were plated directly in an autotrophic CHU medium (Chu, 1942) and were incubated at 21 ºC with a photoperiod of 12:12 light/dark and light intensity of 7.4 μmol m-2 s –1. Isolated colonies were transferred to liquid cultures kept in a cultivation room at 21 ºC with continuous light and aeration of 0.4% CO2 (v/v), with 0.2 µm filters coupled to air entrance. The first pre-inoculums were prepared using stationary phase cultures (30 days) grown in 50 mL flasks (21 ºC, photoperiod 12/12 h) with 3 mL of CHU. The fastest growing and most promising strain was selected to proceed for further investigations.
The samples were fixed with the Transeau solution in a proportion of 1:1 (Bicudo and Menezes, 2006) and deposited in the Herbarium of the Botany Department of the UFPR (UPCB: 93121).
2.2. Comparison of growth, biomass, carbohydrates, and lipids production of D. abundans LGMM0013 AND T. obliquus LGMM0001
The growth, biomass, carbohydrates, and lipids production of the new isolate D. abundans LGMM0013 and T. obliquus (LGMM0001), the main strain used by NPDEAS´ researchers, at Federal University of Paraná (UFPR), were compared. The methodology used in all experiments was strictly the same for the two strains LGMM0013 and Tetradesmus obliquus LGMM0001.
2.2.1. Growth conditions
The culture medium used was liquid CHU [NaNO3 2.5 mg L-1, CaCl2.2H2O 0.25 mg L-1, MgSO4.7H2O 0.75 mg L-1, K2HPO4 0.75 mg L-1, KH2PO4 1.75 mg L-1, NaCl 0.25 mg L-1, EDTA–Na2 0.05 mg L-1, KOH 0.031 mg L-1, FeSO4.7H2O 0.00498 mg L-1, H3BO3 0.01142 mg L-1, ZnSO4.7H2O 0.0000882 mg L-1, MnCl2.4H2O 0.0000144 mg L-1, CuSO4.5H2O 0.0000157 mg L-1, Co(NO3)2.6H2O 0.0000049 mg L-1, NaMoO4. 2H2O 0.0000119 mg L-1, Chu (1942)] for autotrophic conditions. Cultures were incubated in 2 L Erlenmeyer flasks with 1.5 L of CHU medium, to provide autotrophic conditions, with aeration 0.4% CO2 (v/v). The flasks were kept in a cultivation chamber at 25ºC with continuous light of 7.4 μmol m-2 s –1. To the mixotrophic conditions, 1000 mg L-1 or 1500 mg L-1 of NaHCO3 was added to CHU.
2.2.2. Growth kinetics
Growth kinetics of D. abundans LGMM0013 and T. obliquus (LGMM0001) were evaluated considering the dry biomass (see item 2.2.3). A pre-inoculum grown for 14 days was used and inoculated in a 2 L Erlenmeyer with an initial concentration of 0.01 g L-1 of dry biomass. Growth was assessed by dry biomass every 48 hours over 22 days. At the end of the experiment, carbohydrates (see item 2.2.5) and total lipids quantification (see item 2.2.6) were extracted from biomass.
2.2.3. Biomass recovery and quantification
Biomass was recovered according to the methodology described by Selesu et al. (2016). Dry biomass quantification was obtained by filtering an aliquot of the culture through glass fiber microfilters (GF1 0.7 µm) using the gravimetric method. Filters were previously dried in an oven at 60 ºC for 24 hours and then weighed on an analytical scale model SHIMADZU AUW220D (Schimadzu Corporation, Kyoto, Japan). After filtering the culture, the filters were dried and weighed again. The data were treated by this equation (Equation 1):
Where, DB = dry biomass (mg L-1); M1 = mass of the empty microfilter (mg); M2 = microfilter mass with microalgae biomass (mg); V = filtered aliquot (L).
2.2.4. Carbohydrates quantification
The methodology used for the quantification of carbohydrates was described by Dubois et al. (1956) using phenol and sulfuric acid. In a tube, 20 mg of freeze-dried biomass was added with 1 mL of 80% H2SO4 and then rested for 20 hours. For the first 4 hours, the bottles were kept on ice and for the next hours at room temperature.
After resting, the sample was diluted in 9 mL of distilled water. A 1.5 mL aliquot was removed and centrifuged at 8,000 x g for 10 minutes. A volume of 50 μL of the supernatant was removed and placed in a test tube, then 500 μL of 5% phenol solution and 2.5 mL of concentrated H2SO4 were added. Samples were read on a spectrophotometer with 490 nm of absorbance.
2.2.5. Lipids quantification
Lipids were extracted using the Bligh and Dyer method with modifications (Bligh and Dyer, 1959; Hess et al., 2018). A sample of 50 mg of freeze-dried biomass was added in 3 mL CHCl3/CH3OH solution (1:2, v:v), mixed by ultrasound (USC 700, 55 Hz) in 3 cycles of 15 minutes and incubated overnight at 4 ºC in dark conditions. Samples were treated by ultrasound again and harvested at 2000 x g for 10 minutes. The supernatant was recovered, CHCl3/CH3OH solution was added to the remaining precipitate, and the process was repeated. The supernatant's oil content was separated by adding 2 mL of distilled water and 1 mL of CHCl3. The organic phase was recovered, and chloroform was evaporated in an exhaustion chamber. Lipid mass was weighed on an analytical scale model SHIMADZU AUW220D.
Total lipid content was calculated by the following equation (Equation 2):
Where L% = total lipids, mf = mass of flask containing lipids, m0 = mass of the empty flask, mb = microalgae biomass used for lipid quantification.
2.3. Growth under different culture medium composition
The biomass, carbohydrates, and lipids production of the isolate D. abundans LGMM0013 were evaluated after 16 days of cultivation, varying nitrogen and carbon source concentration. Three concentrations of nitrogen (2.5, 1.25 or 0.625 mg L-1 of NaNO3) in an autotrophic condition, or with 1000 mg L-1 or 1500 mg L-1 sodium bicarbonate (NaHCO3) as a carbon source to mixotrophic condition, in liquid CHU medium, were measured (as shown in Table 1), resulting in eight different culture medium composition. A pre-inoculum grown for 16 days was used and inoculated with an initial concentration of 50 mg L-1 of dry biomass at the same cultivation conditions described previously. After 16 days of culture, the dry biomass was measured, and from the total biomass recovered, the production of carbohydrates and lipids were estimated from the different media as previously described.
Growth conditions and dry biomass, lipids, and carbohydrates from Desmodesmus abundans LGMM0013 after 16 days of cultivation.
2.4. Statistical analysis
Tests were performed in triplicates. The significance of results was verified by the ANOVA test, accepting a p-value < 0.05.
2.5. Morphological and molecular analysis
Morphological and molecular identification were carried out with samples taken from the same culture. Growth was in 200 mL of liquid TAP medium (Gorman and Levine, 1965), for seven days at 21° C, without aeration in a culture chamber.
Morphological identification was conducted by light (LM) and Scanning Electron Microscopy (SEM). Desmodesmus cells were visualized and photographed under the light microscope Olympus BX40 with an attached Olympus DP71 capture camera. Samples of the D. abundans LGMM0013 culture were prepared according to Costa et al. (2018) and analyzed with a JEOL JSM6360 scanning electron microscope at the Center of Electron Microscopy from Federal University of Paraná.
The morphological identification was achieved by analyzing coenobia morphology, cell number, marginal cell morphology, median cell morphology, length (μm), width (μm), and presence or absence of thorns and tubes. Characteristics were compared with relevant literature, such as Chodat (1926), Komarek and Fott (1983), and González (1996).
The molecular identification of LGMM0013 using the internal transcribed sequence (ITS) of ribosomal DNA was performed. The genomic DNA was extracted using NucleoSpin® Plant II kit (Macherey-Nagel), according to fabricant instructions. ITS region (ITS 1, 5.8S, and ITS2) was amplified using the primers V9 (5'-TGCGTTGATTACGTCCCTGC-3') (Hoog and van den Ende, 1998) and LS266 (5'-GCATTCCCAAACAACTCGACTC-3') (Masclaux et al., 1995). Amplification was performed as suggested for Platinum Taq DNA Polymerase (Thermo Fisher Scientific) with an annealing temperature of 55 ºC. Sequencing was performed after EXO-SAP purification in ACTGene Biotechnology (RS/Brazil).
The sequence qualities were checked by BioEdit 7.1 (Hall, 1999) and edited using MEGA 10.1 software (Kumar and Gopal, 2015).
For phylogenetic analyzes, only the most reliable sequences from ITS-1 and ITS-2 regions available at Genbank for the genus Desmodesmus were selected, prioritizing sequences mainly used in identification articles (An et al., 1999; Hegewald, 2000; Vanormelingen et al., 2007; Fawley et al., 2011; Fawley et al., 2013; Kaplan-Levy et al., 2016; Hegewald and Braband, 2017). Among them, sequences from identified strains collections such as Culture Collection of Algae and Protozoa (CCAP), Culture Collection of Algae (SAG), and Culture Collection of Algae at the University of Texas at Austin (UTEX) were used. Alignments were inferred with MUSCLE default parameters (Edgar, 2004). Bayesian inference tree was generated in CIPRES (Miller et al., 2010), evolutionary model of Kimura 2 parameters with distribution in range five categories. A maximum-likelihood tree was created using GARLI 2.01 software through the CIPRES platform (Miller et al., 2010). The resulting trees were plotted and edited in Figtree v1.4.3 (http://tree.bio.ed.ac.uk/software/figtree/).
3. Results
3.1. Performance of D. abundans LGMM0013 versus T. obliquus LGMM0001
Cultivation started with 10 mg L-1 of dry biomass from both species of microalgae. From the 8th day, strain D. abundans LGMM0013 began to have higher dry biomass than T. obliquus (LGMM0001).The exponential phase started on the 10th day for both isolates (see Figure 1). Dry biomass on the 22nd day was 1500 mg L-1 for D. abundans LGMM0013, whereas for T. obliquus LGMM0001 it was 980 mg L-1. Therefore, D. abundans LGMM0013 produces a higher amount of dry biomass compared to T. obliquus LGMM0001.
Growth comparison in autotrophic conditions between D. abundans LGMM0013 and T. obliquus LGMM0001 by dry biomass production. Bars indicate standard deviation.
Values of carbohydrates and lipids were obtained by freeze-dried biomass from the 22nd day (see Figure 2). Accumulation of carbohydrates in D. abundans LGMM0013 was 673.39 mg L-1, 130% higher than T. obliquus (LGMM0001) that was 292.16 mg L1.
Lipids and carbohydrate production of D. abundans LGMM0013 and T. obliquus LGMM0001 under autotrophic conditions after 22 days. Bars indicate standard deviation.
For lipids, D. abundans LGMM0013 shared similar results to T. obliquus (LGMM0001) (see Figure 2). D. abundans LGMM0013 manages to match lipid content (259.7 mg L-1) due to its high biomass production (see Figure 2).
3.2. Growth under different culture medium composition
Treatments with the addition of NaHCO3 as a carbon source showed high accumulation of lipids along with the treatment 1 (control). Treatment 8 using a combination of nitrogen deprivation and addition of NaHCO3 accumulated 207.48 mg L-1 of lipids in its biomass, closer to the treatment 1 that was 194.04 mg L-1. Treatments with the addition of NaHCO3 as a carbon source did not show a higher accumulation of biomass than autotrophic cultures, without a carbon source (see Table 1).
Highest accumulation of total carbohydrates occurred in two scenarios, using 50% nitrogen deprivation in the culture medium (treatment 2) and with the addition of 1000 mg L-1 of NaHCO3 in the medium without nitrogen deprivation (treatment 4), 688.44 mg L-1 and 641.79 mg L-1 respectively.
Treatment with a reduction of 50% of nitrogen source and no addition of NaHCO3 (treatment 2) had the most significant biomass recovery by the 16th day with 1034 mg L-1. The same treatment resulted in one of the highest percentages of carbohydrates in dry biomass (688.44 mg L-1/ 66.58%), alongside treatment 4 (641.79 mg L-1).
3.3. LGMM0013 identification and species description
Through optical and Scanning Electron Microscopy (SEM) (see Figure 3), LGMM0013 was characterized as Desmodesmus abundans (Kirchner) E.H.Hegewald. The Desmodesmus abundans description is given below (Hegewald, 2000).
Morphology of D. abundans LGMM0013 by optical microscopy (A-C) and scanning electron microscopy (D-F). From A to C scale bar (black) equivalent to 10 μm. A: single cell. B: Coenobium with two cells. C: Coenobium with four cells. From D to F scale bar equivalent to 5 μm. D: Single-cell, presence of spines and tubes. E: Coenobium with two cells, presence of thorns. F: Coenobium with four cells, presence of spines and tubes. Black arrow: chimney-like rosettes; white arrow: longitudinal ridges.
Desmodesmus abundans (Kirchner) E.H.Hegewald
Algological Studies, v. 96, p. 1, 2000.
Solitary cells elliptical. Coenobia with 2 to 4 cells arranged linearly. Cells elliptical, rounded poles, 5.2–6.2 µm long and 1.5–4 µm wide. Coenobia and solitary cells with one spine at each pole (see Figure 3A, 3C, 3D, 3F) and few short spines. Two celled colonies with 4 to 6 short spines irregularly distributed on the cell surface (see Figure 3B, 3E). Cell walls smooth with longitudinal ridges and one or two chimney-like rosettes per cell (see Figure 3D). Chloroplast parietal, with single pyrenoid.
The population studied here is morphologically similar to D. abundans morphotype IIIa presented by Hegewald and Schnepf (1991), differing by the shorter cell length of our specimens (5.2–6.2 µm), compared to D. abundans morphotype IIIa (7–9.2 µm). However, according to Hegewald and Schnepf (1991), D. abundans morphotypes include cells with smaller length (4.5–38 µm), thus admitting our population in the species.
Desmodesmus abundans morphologically resembles D. spinosus and D. subspicatus. However, D. abundans differs by having a longitudinal ridge, one or two chimney-like rosettes per cell, and smaller measures of cell length and width. D. spinosus has a median spine on the outer cells of the coenobia, beyond the apical ones. In addition, on the internal cells lateral spines are arranged in series and may or may not have apical spines on the coenobia. D. subspicatus, a species very similar to D. spinosus, is distinguished by one or two simple rosettes decorating each cell (Hindak, 1990).
Morphological comparison between Desmodesmus abundans-like species was presented in Table 2.
The obtained ITS sequence of D. abundans LGMM0013 (GenBank accession number: ON191015) was used for phylogenetic analysis. Based on the phylogenetic tree, using sequences of ITS region of Desmodesmus species (see Figure 4), the D. abundans LGMM0013 strain is closely related to D. abundans, D. spinosus and D. asymetricus species, corroborating with the morphological data.
Phylogenetic analysis of Desmodesmus species by Bayesian inference using ITS sequences. Posteriori probability values are left from nodes.
4. Discussion
In this work, we isolated a new strain of the genus Desmodesmus from the Iraí Reservoir, Brazil. Autotrophic conditions allowed D. abundans LGMM0013 a recovery of biomass 50% larger than T. obliquus LGMM0001. The mixotrophic cultivation resulted in a biomass production up to 5 times greater than autotrophic cultivation since this condition support an overcome of possible limitations imposed by photosynthesis (Patel et al., 2021). Mixotrophic cultivation reduces the energy source's dependence, allowing improvement of growth and macromolecules production by microalgae, using both the photosynthesis and oxidative phosphorylation mechanisms (Pandey et al., 2018).
Another widely explored point is the induction of stressors to the cultivation of microalgae, a factor that enhances the production of macromolecules, especially lipids. One of the main forms of stress is caused by nitrogen limitation in growth conditions (Converti et al., 2009). This response may be related to the great adaptive capacity found in several species belonging to the Scenedesmacea (Ismagulova et al., 2018).
Here, we explore the adaptability and response of D. abundans LGMM0013 in culture using sodium bicarbonate as a carbon source along with changes in concentrations of nitrogen, inducing stress by nutrient limitation. D. abundans LGMM0013 showed higher production of carbohydrates (688.44 mg L-1) and biomass (1034 mg L-1) in treatment with a 50% reduction in nitrogen concentration. The 50% reduction in NaNO3 was associated with accumulating carbohydrates in the cell (González-Fernández and Ballesteros, 2012). A similar result was observed with the addition of 1.5 g L-1 of sodium bicarbonate without altering the nitrogen concentration, a condition in which 641.79 mg L-1 of carbohydrates and 930 mg L-1 of biomass were recovered.
Our results revealed that D. abundans LGMM0013 responds positively to different growth conditions. In addition, it shows its ability to modulate this response. The accumulation of lipids was similar to that observed for T. obliquus LGMM0001 (see Figure 2), reaching 207.48 mg L-1 of this metabolite in the dry biomass, with 1.5 g L-1 of sodium bicarbonate coupled with reduction (50% less) of nitrogen. Sipaúba-Tavares et al. (2020) compared photoautotrophic and mixotrophic cultivation of Messastrum gracile (Chlorophyceae), and observed more than a twofold increase in the dry biomass lipid content (19%), under mixotrophic cultivation.
Rizza et al. (2017) explores the ability of Desmodesmus for carbohydrate production and its application in biohydrogen production, besides addressing the importance of selecting strains with high productivity of macromolecules to reduce the costs of applying microalgae in the biofuel industry. The same authors managed to convert 81.4% of sugars to bioethanol from biomass of a Desmodesmus strain, showing this genus can produce this biofuel. Microalgae with superior biomass production capacity and adaptation to different environments can be an alternative to enable a process that, until now, faces the challenge of imposing high economic costs.
The isolation of new strains from the environment also involves the process of identification, which allows for a deeper understanding of their physiology (Li et al., 2015). For a long time, the identification of microalgae was based only on morphological analysis. However, due to microalgae morphological plasticity, the application of molecular identification techniques is essential (Zou et al., 2016). For the molecular identification of microalgae, ITS region sequencing is often used (An et al., 1999), and was used to elucidate many doubts regarding the identification at the level of species in genera such as Desmodesmus and Tetradesmus, for example (Hegewald, 2000; Hegewald and Wolf, 2003).
Morphological analysis showed that LGMM0013 was identified as D. abundans (as shown in Figure 3 and Table 2). The molecular analysis confirmed this result, where LGMM0013 is closer to D. abundans, D. spinosus and D. asymmetricus (see Figure 4). It is important to note that there are two D. abundans sequences in the phylogenetic tree, a CCAP 258/211 sequence that was close to the strain studied in this work and another UTEX LB 1358 that appeared on a distant branch. Both come from important microalgae collections, however the UTEX strain was identified only by molecular analysis and no morphological description was found by us (Lara-Gil et al., 2014). The CCAP strain (originally Hegewald 1977-222) was isolated and identified morphologically by Hegewald (Hegewald and Schnepf, 1991). The use of only one technique for the identification of microalgae is not enough and can lead to inaccurate results and this is still a common practice in microalgae identification. Therefore, it is important that future works include cross-analysis of molecular and morphological characteristics to obtain more accurate results.
Tests carried out in this study shown that D. abundans LGMM0013 has the potential for the production of molecules with applicability in the biotechnology industry of biofuels, denoting its potential to produce bioethanol. The results observed in this work provide a basis for future studies and substantial knowledge of D. abundans LGMM0013 physiology.
5. Conclusion
In this work, a new strain of the species Desmodesmus abundans LGMM0013 was isolated from the Iraí Reservoir, Brazil. Through morphological and DNA sequences analysis it was possible to identify this strain at the species level. Laboratory analyzes were performed to better understand the physiology of this strain and quantify molecules of biotechnological interest. The comparison of D. abundans LGMM0013 with the T. obliquus LGMM0001 allows denoting the high potential of D. abundans LGMM0013 for biomass production for different purposes, like biofuels. The main conclusions of this study are: i) it was confirmed through morphological and DNA sequences analysis that the microalgae LGMM0013 belongs to the species Desmodesmus abundans; ii) autotrophic conditions allowed D. abundans LGMM0013 a recovery of biomass 50% larger than T. obliquus LGMM0001; iii) D. abundans LGMM0013 showed an accumulation of carbohydrates 130% larger than T. obliquus LGMM0001; iv) nitrogen deprivation was correlated with an increase in the production of biomass and carbohydrates in D. abundans LGMM0013, denoting its potential to produce bioethanol, and v) preliminary tests carried out in this study shown that D. abundans LGMM0013 has the potential for the production of molecules with applicability in the biotechnology industry of biofuels.
Acknowledgements
This work was supported by the Brazilian National Council for Scientific and Technological Development (CNPq) (project 430986/2016-5 and 312516/2019-3), and the Araucaria Foundation (agreement 115/2018, protocol 50.579-PRONEX) for financial support. TAVL (311876/2019-6), JVCV (313646/2020-1), LVGT (312502/2019-2), and VMK (312516/2019-3) acknowledge Brazilian National Council of Scientific and Technological Development (CNPq) for their research productivity grant. We thank the CME (Electron Microscopy Center – BL/UFPR) for the scanning electron microscope availability and SANEPAR (Paraná Sanitation Company) for allowing the access to the Iraí Reservoir.
References
-
AKGÜL, R., AKGÜL, F. and KIZILKAYA, I.T., 2021. Effects of different phosphorus concentrations on growth and biochemical composition of Desmodesmus communis (E.Hegewald) E.Hegewald. Preparative Biochemistry & Biotechnology, vol. 51, no. 7, pp. 705-713. http://dx.doi.org/10.1080/10826068.2020.1853156 PMid:33280505.
» http://dx.doi.org/10.1080/10826068.2020.1853156 -
AN, S.S., FRIEDL, T. and HEGEWALD, E., 1999. Phylogenetic relationships of Scenedesmus and Scenedesmus-like coccoid green algae as inferred from ITS-2 rDNA sequence comparison. Plant Biology, vol. 1, no. 4, pp. 418-428. http://dx.doi.org/10.1111/j.1438-8677.1999.tb00724.x
» http://dx.doi.org/10.1111/j.1438-8677.1999.tb00724.x - BICUDO, C.D.M. and MENEZES, M., 2006. Gêneros de algas de águas continentais do Brasil São Carlos: Rima. 552 p.
-
BLIGH, E.G. and DYER, W.J., 1959. A rapid method of total lipid extraction and purification. Canadian Journal of Biochemistry and Physiology, vol. 37, no. 8, pp. 911-917. http://dx.doi.org/10.1139/o59-099 PMid:13671378.
» http://dx.doi.org/10.1139/o59-099 -
CAPRIO, F., ALTIMARI, P., IAQUANIELLO, G., TORO, L. and PAGNANELLI, F., 2019. Heterotrophic cultivation of T. obliquus under non-axenic conditions by uncoupled supply of nitrogen and glucose. Biochemical Engineering Journal, vol. 145, pp. 127-136. http://dx.doi.org/10.1016/j.bej.2019.02.020
» http://dx.doi.org/10.1016/j.bej.2019.02.020 -
CHODAT, R., 1926. Scenedesmus. Étude de génétique de systématique expérimentale et d’hydrobiologie. Schweizerische Zeitschrift für Hydrologie, vol. 3, no. 3-4, pp. 71-258. http://dx.doi.org/10.1007/BF02485756
» http://dx.doi.org/10.1007/BF02485756 -
CHU, S.P., 1942. The influence of the mineral composition of the medium on the growth of planktonic algae: part I. Methods and culture media. Journal of Ecology, vol. 30, no. 2, pp. 284-325. http://dx.doi.org/10.2307/2256574
» http://dx.doi.org/10.2307/2256574 -
CONVERTI, A., CASAZZA, A.A., ORTIZ, E.Y., PEREGO, P. and BORGHI, M., 2009. Effect of temperature and nitrogen concentration on the growth and lipid content of Nannochloropsis oculata and Chlorella vulgaris for biodiesel production. Chemical Engineering and Processing: Process Intensification, vol. 48, no. 6, pp. 1146-1151. http://dx.doi.org/10.1016/j.cep.2009.03.006
» http://dx.doi.org/10.1016/j.cep.2009.03.006 -
CORRÊA, D.O., DUARTE, M.E.R. and NOSEDA, M.D., 2019. Biomass production and harvesting of Desmodesmus subspicatus cultivated in flat plate photobioreactor using chitosanas flocculant agent. Journal of Applied Phycology, vol. 31, no. 2, pp. 857-866. http://dx.doi.org/10.1007/s10811-018-1586-z
» http://dx.doi.org/10.1007/s10811-018-1586-z -
CORRÊA, D.O., SANTOS, B., DIAS, F.G., VARGAS, J.V.C., MARIANO, A.B., BALMANT, W., ROSA, M.P., SAVI, D.C., KAVA, V., GLIENKE, C. and ORDONEZ, J.C., 2017. Enhanced biohydrogen production from microalgae by diesel engine hazardous emissions fixation. International Journal of Hydrogen Energy, vol. 42, no. 33, pp. 1-13. http://dx.doi.org/10.1016/j.ijhydene.2017.05.176
» http://dx.doi.org/10.1016/j.ijhydene.2017.05.176 -
COSTA, F.D.M., RAMOS, G.J.P., OLIVEIRA, I.B., BICUDO, C.E.D.M. and MOURA, C.W.D.N., 2018. Five new taxa and a new record of Euastrum (Desmidiaceae) from the Chapada Diamantina region, Bahia State, Brazil. Phytotaxa, vol. 372, no. 3, pp. 193-202. http://dx.doi.org/10.11646/phytotaxa.372.3.2
» http://dx.doi.org/10.11646/phytotaxa.372.3.2 -
DIAS, F.G., VARGAS, J.V.C., YANG, S., ROSA, M.P., SANTOS, B., KAVA, V.M., BALMANT, W., MARIANO, A.B. and ORDONEZ, J.C., 2019. Experimental calibration of a biohydrogen production estimation model. Journal of Verification, Validation and Uncertainty Quantification, vol. 4, no. 2, p. 021002. http://dx.doi.org/10.1115/1.4044664
» http://dx.doi.org/10.1115/1.4044664 - DOMINGUES, C.D. and TORGAN, L.C., 2012. Chlorophyta de um lago artificial hipereutrófico no sul do Brasil. Iheringia. Série Botânica, vol. 67, no. 1, pp. 75-91.
-
DUBOIS, M., GILLES, K., HAMILTON, J., REBERS, P. and SMITH, F., 1956. Colorimetric method for determination of sugars and related substances. Analytical Chemistry, vol. 28, no. 3, pp. 350-356. http://dx.doi.org/10.1021/ac60111a017
» http://dx.doi.org/10.1021/ac60111a017 -
EDGAR, R.C., 2004. MUSCLE: multiple sequence alignment with high accuracy and high throughput. Nucleic Acids Research, vol. 32, no. 5, pp. 1792-1797. http://dx.doi.org/10.1093/nar/gkh340 PMid:15034147.
» http://dx.doi.org/10.1093/nar/gkh340 -
ESCORSIM, A.M., ROCHA, G., VARGAS, J.V.C., MARIANO, A.B., RAMOS, L.P., CORAZZA, M.L. and CORDEIRO, C.S., 2018. Extraction of Acutodesmus obliquus lipids using a mixture of ethanol and hexane as solvent. Biomass and Bioenergy, vol. 108, pp. 470-478. http://dx.doi.org/10.1016/j.biombioe.2017.10.035
» http://dx.doi.org/10.1016/j.biombioe.2017.10.035 -
FAWLEY, M.W., FAWLEY, K.P. and HEGEWALD, E., 2011. Taxonomy of Desmodesmus serratus (Chlorophyceae, Chlorophyta) and related taxa on the basis of morphological and DNA sequence data. Phycologia, vol. 50, no. 1, pp. 23-56. http://dx.doi.org/10.2216/10-16.1
» http://dx.doi.org/10.2216/10-16.1 -
FAWLEY, M.W., FAWLEY, K.P. and HEGEWALD, E., 2013. Desmodesmus baconii (Chlorophyta), a new species with double rows of arcuate spines. Phycologia, vol. 52, no. 6, pp. 565-572. http://dx.doi.org/10.2216/12-116.1
» http://dx.doi.org/10.2216/12-116.1 -
GODINHO, L.R., GONZÁLEZ, A.A.C. and BICUDO, C.E.M., 2010. Criptógamos do Parque Estadual das Fontes do Ipiranga, São Paulo, SP. Algas, 30: Chlorophyceae (família Scenedesmaceae). Hoehnea, vol. 37, no. 3, pp. 513-553. http://dx.doi.org/10.1590/S2236-89062010000300005
» http://dx.doi.org/10.1590/S2236-89062010000300005 - GONZÁLEZ, A.C., 1996. Las Chlorococcales dulciacuícolas de Cuba Berlin: J. Cramer. 265 p. Biblioteca Phycologica, no. 99.
-
GONZÁLEZ-BALDERAS, R.M., VELÁSQUEZ-ORTA, S.B., VALDEZ-VAZQUEZ, I. and LEDESMA, M.T.O., 2020. Intensified recovery of lipids, proteins, and carbohydrates from wastewater-grown microalgae Desmodesmus sp. by using ultrasoundor ozone. Ultrasonics Sonochemistry, vol. 62, p. 104852. http://dx.doi.org/10.1016/j.ultsonch.2019.104852 PMid:31806557.
» http://dx.doi.org/10.1016/j.ultsonch.2019.104852 -
GONZÁLEZ-FERNÁNDEZ, C. and BALLESTEROS, M., 2012. Linking microalgae and cyanobacteria culture conditions and key-enzymes for carbohydrate accumulation. Biotechnology Advances, vol. 30, no. 6, pp. 1655-1661. http://dx.doi.org/10.1016/j.biotechadv.2012.07.003 PMid:22820270.
» http://dx.doi.org/10.1016/j.biotechadv.2012.07.003 -
GORMAN, D.S. and LEVINE, R.P., 1965. Cytochrome f and plastocyanin: their sequence in the photosynthetic electron transport chain of Chlamydomonas reinhardi. Proceedings of the National Academy of Sciences of the United States of America, vol. 54, no. 6, pp. 1665-1669. http://dx.doi.org/10.1073/pnas.54.6.1665 PMid:4379719.
» http://dx.doi.org/10.1073/pnas.54.6.1665 -
HADI, S.I., SANTANA, H., BRUNALE, P.P.M., GOMES, T.G., OLIVEIRA, M.D., MATTHIENSEN, A., OLIVEIRA, M.E.C., SILVA, F.C.P. and BRASIL, B.S.A.F., 2016. DNA barcoding green microalgae isolated from neotropical Inland waters. PLoS One, vol. 11, no. 2, p. e0149284. http://dx.doi.org/10.1371/journal.pone.0149284 PMid:26900844.
» http://dx.doi.org/10.1371/journal.pone.0149284 - HALL, T.A., 1999. BioEdit: a user-friendly biological sequence alignment editor and analysis program for Windows 95/98/NT. Nucleic Acids Symposium Series, vol. 41, no. 41, pp. 95-98.
- HANSGIRG, A., 1888. Ueber die süsswasserangen-gattungen Trochisia Kütz. (Acanthococcus Lagerh., Glochiococcus De Toni) und Tetraëdron Kütz. (Astericium Corda, Polyedrium Nag., Ceraterias Reinsch). Hediwigia, vol. 27, pp. 126-132.
-
HEGEWALD, E. and BRABAND, A.A., 2017. Taxonomic revision of Desmodesmus serie Desmodesmus (Sphaeropleales, Scenedesmaceae). Journal of the Czech Phycological Society, vol. 17, no. 2, pp. 191-208. http://dx.doi.org/10.5507/fot.2017.001
» http://dx.doi.org/10.5507/fot.2017.001 -
HEGEWALD, E. and SCHNEPF, E., 1991. Scenedesmus abundans (KIRCHN.) Chod., an older name for Chlorella fusca Shih. et Kraus. Archiv fur Protistenkunde, vol. 139, no. 1-4, pp. 133-176. http://dx.doi.org/10.1016/S0003-9365(11)80015-1
» http://dx.doi.org/10.1016/S0003-9365(11)80015-1 -
HEGEWALD, E. and WOLF, M., 2003. Phylogenetic relationships of Scenedesmus and Acutodesmus (Chlorophyta, Chlorophyceae) as inferred from 18S rDNA and ITS-2 sequence comparisons. Plant Systematics and Evolution, vol. 241, no. 3-4, pp. 185-191. http://dx.doi.org/10.1007/s00606-003-0061-7
» http://dx.doi.org/10.1007/s00606-003-0061-7 -
HEGEWALD, E., 2000. New combinations in the genus Desmodesmus (Chlorophyceae, Scenedesmaceae). Algological Studies, vol. 96, pp. 1-18. http://dx.doi.org/10.1127/algol_stud/96/2000/1
» http://dx.doi.org/10.1127/algol_stud/96/2000/1 -
HENTSCHKE, G.S. and TORGAN, L.C., 2010. Desmodesmus e Scenedesmus (Scenedesmaceae, Sphaeropleales, Chlorophyceae) em ambientes aquáticos na planície costeira do Rio Grande do Sul, Brasil. Rodriguésia, vol. 61, no. 4, pp. 585-601. http://dx.doi.org/10.1590/2175-7860201061403
» http://dx.doi.org/10.1590/2175-7860201061403 -
HESS, S.K., LEPETIT, B., KROTH, P.G. and MECKING, S., 2018. Production of chemicals from microalgae lipids – status and perspectives. European Journal of Lipid Science and Technology, vol. 120, no. 1, p. 1700152. http://dx.doi.org/10.1002/ejlt.201700152
» http://dx.doi.org/10.1002/ejlt.201700152 -
HESSE, M.C.S., SANTOS, B., SELESU, N.F.H., CORRÊA, D.O., MARIANO, A.B., VARGAS, J.V.C. and VIEIRA, R.B., 2017. Optimization of flocculation with tannin-based flocculant in the water reuse and lipidic production for the cultivation of Acutodesmus obliquus. Separation Science and Technology, vol. 52, no. 5, pp. 936-942. http://dx.doi.org/10.1080/01496395.2016.1269130
» http://dx.doi.org/10.1080/01496395.2016.1269130 - HINDÁK, F., 1990. Studies on the chlorococcal algae (Chlorophyceae), 5 Bratislava: Veda. 225 p. Biologické Prace, no. 36.
-
HOOG, G.S. and VAN DEN ENDE, A.H.G., 1998. Molecular diagnostics of clinical strains of filamentous Basidiomycetes. Mycoses, vol. 41, no. 5-6, pp. 183-189. http://dx.doi.org/10.1111/j.1439-0507.1998.tb00321.x PMid:9715630.
» http://dx.doi.org/10.1111/j.1439-0507.1998.tb00321.x -
ISMAGULOVA, T., CHEKANOV, K., GORELOVA, O., BAULINA, O., SEMENOVA, L., SELYAKH, I., CHIVKUNOVA, O., LOBAKOVA, E., KARPOVA, O. and SOLOVCHENKO, A., 2018. A new subarctic strain of Tetradesmus obliquus - part I: identification and fatty acid profiling. Journal of Applied Phycology, vol. 30, no. 5, pp. 2737-2750. http://dx.doi.org/10.1007/s10811-017-1313-1
» http://dx.doi.org/10.1007/s10811-017-1313-1 -
KAPLAN-LEVY, R.N., ALSTER-GLOUKHOVSKI, A., BENYAMINI, Y. and ZOHARY, T., 2016. Lake Kinneret phytoplankton: integrating classical and molecular taxonomy. Hydrobiologia, vol. 764, no. 1, pp. 283-302. http://dx.doi.org/10.1007/s10750-015-2517-5
» http://dx.doi.org/10.1007/s10750-015-2517-5 - KIM, Y., 2015. Algal Flora of Korea Incheon: National Institute of Biological Resources, vol. 6, no. 8, 134 p.
- KIRCHNER, O., 1878. Algen. In: F. COHN, ed. Kryptogamen-Flora von Schlesien. Part 1 Breslau: J.U. Kern's Verlag, vol. 2, 284 p.
- KOMÁREK, J. and FOTT, B. 1983. Chlorophyceae (grünalgen) Ordnung: Chlorococcales. In: G. HUBER-PESTALOZZI, org. Das Phytoplankton des Süsswassers: systematic und biologie Nägele: Schweizerbart’sche Verlagsbuchhandling, vol. 7, no. 1, pp. 799-941.
- KORSHIKOV, O.A., 1953. Pidklas Protokokovi (Protococcineae). Viznačnik prisnovodnich vodorostej Ukrainskoj RSR Vol. 5. Kiev: Akad, 439 p.
-
KUMAR, B.L. and GOPAL, D.V.R., 2015. Effective role of indigenous microorganisms for sustainable environment. 3 Biotech, vol. 5, no. 6, pp. 867-876. http://dx.doi.org/10.1007/s13205-015-0293-6 PMid:28324402.
» http://dx.doi.org/10.1007/s13205-015-0293-6 -
KÜTZING, F.T. 1849. Species algarum. Leipzig: F.A. Brockhaus, 922 p. https://doi.org/10.5962/bhl.title.60464.
» https://doi.org/10.5962/bhl.title.60464 -
LARA-GIL, J.A., ÁLVAREZ, M.M. and PACHECO, A., 2014. Toxicity of flue gas components from cement plants in microalgae CO2 mitigation systems. Journal of Applied Phycology, vol. 26, no. 1, pp. 357-368. http://dx.doi.org/10.1007/s10811-013-0136-y
» http://dx.doi.org/10.1007/s10811-013-0136-y -
LELIAERT, F., SMITH, D.R., MOREAU, H., HERRON, M.D., VERBRUGGEN, H., DELWICHE, C.F. and DE CLERCK, O., 2012. Phylogeny and molecular evolution of the green algae. Critical Reviews in Plant Sciences, vol. 31, no. 1, pp. 1-46. http://dx.doi.org/10.1080/07352689.2011.615705
» http://dx.doi.org/10.1080/07352689.2011.615705 -
LI, L., CUI, J., LIU, Q., DING, Y. and LIU, J., 2015. Screening and phylogenetic analysis of lipid-rich microalgae. Algal Research, vol. 11, pp. 381-386. http://dx.doi.org/10.1016/j.algal.2015.02.028
» http://dx.doi.org/10.1016/j.algal.2015.02.028 -
LORTOU, U. and GKELIS, S., 2019. Polyphasic taxonomy of green algae strains isolated from Mediterranean freshwaters. Journal of Biological Research (Thessaloniki), vol. 26, no. 1, p. 11. http://dx.doi.org/10.1186/s40709-019-0105-y PMid:31696064.
» http://dx.doi.org/10.1186/s40709-019-0105-y -
MASCLAUX, F., GUÉHO, E., DE HOOG, G.S. and CHRISTEN, R., 1995. Phylogenetic relationships of human-pathogenic Cladosporium (Xylohypha) species inferred from partial LS rRNA sequences. Journal of Medical and Veterinary Mycology, vol. 33, no. 5, pp. 327-338. http://dx.doi.org/10.1080/02681219580000651 PMid:8544086.
» http://dx.doi.org/10.1080/02681219580000651 -
MILLER, M.A., PFEIFFER, W. and SCHWARTZ, T., 2010. Creating the CIPRES science gateway for inference of large phylogenetic trees. In: Gateway Computing Environments Workshop, 14 November 2010, New Orleans, USA. New York, USA: IEEE, pp. 1-8. http://dx.doi.org/10.1109/GCE.2010.5676129
» http://dx.doi.org/10.1109/GCE.2010.5676129 -
MIYAWAKI, B., MARIANO, A.B., VARGAS, J.V.C., BALMANT, W., DEFRANCHESCHI, A.C., CORREA, D.O., SANTOS, B., SELESU, N.H., ORDONEZ, J.C. and KAVA, V.M., 2021. Microalgae derived biomass and bioenergy production enhancement through biogas purification and wastewater treatment. Renewable Energy, vol. 163, pp. 1153-1165. http://dx.doi.org/10.1016/j.renene.2020.09.045
» http://dx.doi.org/10.1016/j.renene.2020.09.045 -
MORESCO, C. and BUENO, N.C., 2007. Scenedesmaceae (Chlorophyceae - Chlorococcales) de um lago artificial urbano: Desmodesmus e Scenedesmus. Acta Scientiarum. Biological Sciences, vol. 29, no. 3, pp. 289-296. http://dx.doi.org/10.4025/actascibiolsci.v29i3.483
» http://dx.doi.org/10.4025/actascibiolsci.v29i3.483 -
NAJEEB, M.I., AHMAD, M.D., ANJUM, A.A., MAQBOOL, A., ALI, M.A., NAWAZ, M., ALI, T. and MANZOOR, R., 2024. Distribution, screening and biochemical characterization of indigenous microalgae for bio-mass and bio-energy production potential from three districts of Pakistan. Brazilian Journal of Biology = Revista Brasileira de Biologia, vol. 84, p. e261698. http://dx.doi.org/10.1590/1519-6984.261698 PMid:35792736.
» http://dx.doi.org/10.1590/1519-6984.261698 - OLIVEIRA, R.S., 2015. Família Scenedesmaceae (Chlorophyceae, Sphaeropleales) no estado de Goiás: biodiversidade e distribuição geográfica Goiânia: Universidade Federal de Goiás, 105 p. Dissertação de mestrado em Biodiversidade Vegetal.
- PANDEY, A., LEE, D.J., CHANG, J.S., CHISTI, Y. and SOCCOL, C.R., 2018. Biomass, biofuels, biochemicals: biofuels from algae 2nd ed. Amsterdam: Elsevier. 603 p.
-
PANG, N., GU, X., CHEN, S., KIRCHHOFF, H., LEI, H. and ROJE, S., 2019. Exploiting mixotrophy for improving productivities of biomass and co-products of microalgae. Renewable & Sustainable Energy Reviews, vol. 112, pp. 450-460. http://dx.doi.org/10.1016/j.rser.2019.06.001
» http://dx.doi.org/10.1016/j.rser.2019.06.001 -
PATEL, A.K., SINGHANIA, R.R., SIM, S.J. and DONG, C., 2021. Recent advancements in mixotrophic bioprocessing for production of high value microalgal products. Bioresource Technology, vol. 320, no. Pt B, p. 124421. http://dx.doi.org/10.1016/j.biortech.2020.124421 PMid:33246239.
» http://dx.doi.org/10.1016/j.biortech.2020.124421 - PATIL, S.A., 2013. Genus Scenedesmus Meyen from Mangrul Dam Dist Jalgaon, Maharashtra. Indian Journal of Fundamental and Applied Life Sciences, vol. 3, no. 2, pp. 204-210.
- PRINTZ, H., 1914. Kristianiatraktens Protococcoideer Christiania: I kommission hos J. Dybwad, vol. 6, 121 p.
-
RIZZA, L.S., SMACHETTI, M.E.S., NASCIMENTO, M., SALERNO, G.L. and CURATTI, L., 2017. Bioprospecting for native microalgae as an alternative source of sugars for the production of bioethanol. Algal Research, vol. 22, pp. 140-147. http://dx.doi.org/10.1016/j.algal.2016.12.021
» http://dx.doi.org/10.1016/j.algal.2016.12.021 -
ROSINI, E.F., SANT’ANNA, C.L. and TUCCI, A., 2013. Scenedesmaceae (Chlotococcales, Chlorophyceae) de pesqueiros da Região Metropolitana de São Paulo, SP, Brasil: levantamento florístico. Hoehnea, vol. 40, no. 4, pp. 661-678. http://dx.doi.org/10.1590/S2236-89062013000400008
» http://dx.doi.org/10.1590/S2236-89062013000400008 -
SCHERER, M.D., DE OLIVEIRA, A.C., FILHO, F.J.C.M., UGAYA, C.M.L., MARIANO, A.B. and VARGAS, J.V.C., 2017. Environmental study of producing microalgal biomass and bioremediation of cattle manure effluents by microalgae cultivation. Clean Technologies and Environmental Policy, vol. 19, no. 6, pp. 1745-1759. http://dx.doi.org/10.1007/s10098-017-1361-x
» http://dx.doi.org/10.1007/s10098-017-1361-x -
SELESU, N.F.H.V., DE OLIVEIRA, T., CORRÊA, D.O., MIYAWAKI, B., MARIANO, A.B., VARGAS, J.V.C. and VIEIRA, R.B., 2016. Maximum microalgae biomass harvesting via flocculation in large scale photobioreactor cultivation. Canadian Journal of Chemical Engineering, vol. 94, pp. 304-309. http://dx.doi.org/10.1002/cjce.22391
» http://dx.doi.org/10.1002/cjce.22391 - SHIHIRA, I. and KRAUSS, R.W. 1965. Chlorella Physiology and Taxonomy of Forty-one Isolates. University of Maryland, College Park, vol. 97, pp. 1-97.
-
SHUBERT, E., WILK-WOŹNIAK, E. and LIGĘZA, S., 2014. An autecological investigation of Desmodesmus: implications for ecology and taxonomy. Plant Ecology and Evolution, vol. 147, no. 2, pp. 202-212. http://dx.doi.org/10.5091/plecevo.2014.902
» http://dx.doi.org/10.5091/plecevo.2014.902 -
SILVA, A.G., CARTER, R., MERSS, F.L.M., CORRÊA, D.O., VARGAS, J.V.C., MARIANO, A.B., ORDONEZ, J.C. and SCHERER, M.D., 2013. Life cycle assessment of biomass production in microalgae compact photobioreactors. Global Change Biology. Bioenergy, vol. 7, no. 2, pp. 184-194. http://dx.doi.org/10.1111/gcbb.12120
» http://dx.doi.org/10.1111/gcbb.12120 -
SIPAÚBA-TAVARES, L.H., SCARDOELI-TRUZZI, B., FENERICK, D.C. and TEDESQUE, M.G., 2020. Comparison of photoautotrophic and mixotrophic cultivation of microalgae Messastrum gracile (Chlorophyceae) in alternative culture media. Brazilian Journal of Biology = Revista Brasileira de Biologia, vol. 80, no. 4, pp. 914-920. http://dx.doi.org/10.1590/1519-6984.226548 PMid:31800772.
» http://dx.doi.org/10.1590/1519-6984.226548 - SMITH, G.M., 1916. A monograph of the algal genus Scenedesmus based upon culture studies. Transactions of the Wisconsin Academy of Sciences, Arts, and Letters, no. 18, pp. 422-530.
-
'T LAM, G.P., VERMUE, M.H., EPPINK, M.H.M., WIJFFELS, R.H. and VAN DEN BERG, C., 2018. Multi-product microalgae biorefineries: from concept towards reality. Trends in Biotechnology, vol. 36, no. 2, pp. 216-227. http://dx.doi.org/10.1016/j.tibtech.2017.10.011 PMid:29132753.
» http://dx.doi.org/10.1016/j.tibtech.2017.10.011 -
TSARENKO, P.M., HEGEWALD, E. and BRABAND, A., 2005. Scenedesmus-like algae of Ukraine. 1. Diversity of taxa from water bodies in Volyn Poissia. Algological Studies, vol. 118, pp. 1-45. http://dx.doi.org/10.1127/1864-1318/2006/0118-0001
» http://dx.doi.org/10.1127/1864-1318/2006/0118-0001 -
VANORMELINGEN, P., HEGEWALD, E., BRABAND, A., KITSCHKE, M., FRIEDL, T., SABBE, K. and VYVERMAN, W., 2007. The systematics of a small spineless Desmodesmus species, D-Costato-granulatus (sphaeropleales, chlorophyceae), based on ITS2 rDNA sequence analyses and cellwall morphology. Journal of Phycology, vol. 43, no. 2, pp. 378-396. http://dx.doi.org/10.1111/j.1529-8817.2007.00325.x
» http://dx.doi.org/10.1111/j.1529-8817.2007.00325.x -
VARGAS, J.V.C., MARIANO, A.B., CORRÊA, D.O. and ORDONEZ, J.C., 2014. The microalgae derived hydrogen process in compact photobioreactors. International Journal of Hydrogen Energy, vol. 39, no. 18, pp. 9588-9598. http://dx.doi.org/10.1016/j.ijhydene.2014.04.093
» http://dx.doi.org/10.1016/j.ijhydene.2014.04.093 -
WANG, L., WANG, L., MANZI, H.P., YANG, Q., GUO, Z., ZHENG, Y., LIU, X. and SALAMA, E., 2022. Isolation and screening of Tetradesmus dimorphus and Desmodesmus asymmetricus from natural habitats in Northwestern China for clean fuel production and N, P removal. Biomass Conversion and Biorefinery, vol. 12, no. 5, pp. 1503-1512. http://dx.doi.org/10.1007/s13399-020-01034-z
» http://dx.doi.org/10.1007/s13399-020-01034-z -
WASE, N., BLACK, P. and DIRUSSO, C., 2018. Innovations in improving lipid production: algal chemical genetics. Progress in Lipid Research, vol. 71, pp. 101-123. http://dx.doi.org/10.1016/j.plipres.2018.07.001 PMid:30017715.
» http://dx.doi.org/10.1016/j.plipres.2018.07.001 - WOLLE, F., 1887. Fresh-water algae of the United States (exclusive of the Diatomaceae) complemental to desmids of the United States Bethlehem: The Comenius Press. 364 p.
-
ZOU, S., FEI, C., WANG, C., GAO, Z., BAO, Y., HE, M. and WANG, C., 2016. How DNA barcoding can be more effective in microalgae identification: a case of cryptic diversity revelation in Scenedesmus (Chlorophyceae). Scientific Reports, vol. 6, no. 1, p. 36822. http://dx.doi.org/10.1038/srep36822 PMid:27827440.
» http://dx.doi.org/10.1038/srep36822
Publication Dates
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Publication in this collection
21 Nov 2022 -
Date of issue
2022
History
-
Received
22 June 2022 -
Accepted
01 Nov 2022