Chapter-4 Isolation and screening of microalgae for carbon sequestration and its lipid content Abstract: Samples collected from Gujarat coast and from polluted habitat, were enriched for isolation and screening of potential microalgae for carbon sequestration and its lipid content. Most of the unicellular eukaryotic microalgae have higher lipid and biomass productivity. Out of the studied strains, Monoraphidium minutum and Chlorella variabilis were selected because of their higher lipid, biomass productivity and CO2 tolerance. 1. Introduction: Isolation and screening of microalgae for higher lipid productivity is important criterion for biodiesel production and CO2 sequestration (Dunahay, 1998). The tolerance of CO2 is one of the important characteristics which should be evaluated while selecting the microalgal strain in different media as well as in varied pH (Griffiths et al., 2009; Wang et al., 2008). The present chapter deals with the selection of promising microalgal strains from the coastal environment. 2. Materials and methods: 2.1. Isolation of microalgal samples: The collected microalgal samples from described assessed sites in Chapter- 3 (Table-1) were inoculated for enrichment. Each individual sample distributed and 116 poured in different autoclaved media (BG11, modified ZM, ASN-3, BBM, ACB and F2) under aseptic conditions and allowed for 7 – 10 days for enrichment. After enrichment, all the samples were taken for serial dilution (10-1, 10-2, 10-3) and, streaking were done on solid CSMCRI-agarose/ agar containing media plates under aseptic conditions. Isolated colonies which were observed after 5-20 days were picked and transferred in autoclaved fresh respective medium (10 ml.) as well as plates in sterile laminar flow chamber (Rippka, 1988; Anderson, 2005). Some of the microalgae like Monoraphidium and Navicula isolated by single cell isolation technique (Anderson, 2005). Purity of the culture was examined under optical microscope with different magnifications (10X, 40X and 100X). The media composition for BG 11 (Blue green 11; Stainer et al., 1971), modified ZM (Zarrouk’s media; Zarrouk, 1966), ACB (Algae culture broth, Himedia), F/2 media (Guillard, 1975) and BBM (Bold basal media; Kantz and Bold, 1969) were used. All media were prepared in distilled water and autoclaved. One liter of Zarrouk’s medium consists of (part A) NaHCO3 (16.80 g/l) and K2HPO4 (0.50 g/l); (part B) NaNO3 (2.50 g/l), K2SO4 (1.00 g/l), NaCl (1.00 g/l), MgSO4·7H2O (0.20 g/l), EDTA-Na2·2H2O (0.08 g/l), CaCl2·2H2O (0.04 g/l), and FeSO4·2H2O (0.01 g/l); trace elements mixture A5 (part C 10 mL/l): 1.00 ml, trace elements mixture B6 (part D 1.0 ml/l): 1.00 mL; part C (mg/L): H3BO3 2.86, MnCl2·4H2O 1.810 g, ZnSO4·7H2O 0.222 MoO3·0.015, and CuSO4·5H2O 0.074 (the used amount is 10 mL/l); part D mg/L: NH4VO3 22.9, NiSO4·7H2O 47.8, NaWO2 17.9, Ti2(SO4)3·6H2O, and 117 Co(NO3)2·6H2O 4.4 (the amount used was 1.0 mL/l). The pH of the media was maintained at 10.00.02 (Zarrouk, 1966). BG-11 media composition was having NaNO3 (1.5 g/l), K2HPO4 (0.04 g/l), MgSO4.7H2O (0.075 g/l), CaCl2.2H2O (0.036 g/l), FeC6H5O7NH4OH (0.006 g/l), C6H8O7 (0.006 g/l), C10H14N2Na2O8 (0.001 g/l), Na2CO3 (0.02 g/l). In addition to this trace metal mix (A5) was used 1ml/l. The trace metal mix solution was prepared separately with composition of H3BO3 (2.86 g/l), MnCl2.4H2O (1.81 g/l), ZnSO4.7H2O (0.222 g/l), NaMoO4.2H2O (0.39 g/l), CuSO4.5H2O (0.079 g/l), Co(NO3)2.6H2O (49.4 g/l) in distilled water. The pH of the final medium was 7.1 ± 0.2 (Stainer et al., 1971). The detailed composition of the of autoclaved F/2 media in distilled water was as follows: NaCl (29.23 g/l), KCl (1.105 g/l), MgSO4·7H2O (11.09 g/l), Tris-base (1.21 g/l) , CaCl2 2H2O (1.83 g/l), NaHCO3 (0.25 g/l), and a 3.0 mL trace metal solution that was composed of 281.3 mg NaNO3, 21.2 mg NaH2PO4·H2O, 16.35 mg Na2·EDTA, 11.8 mg FeCl3·6H2O, 675 MnCl2·4H2O, 37.5 CoCl2·6H2O, 37.5 ZnSO4·7H2O, 22.5 Na2MoO4, 0.375 mg vitamin B1, and 0.188 of biotin (Guillard, 1975). The algae culture broth was prepared in sterile distilled water and, final composition of the media consist of NH4Cl (0.05 g/L), CaCl2 (0.058 g/L), K2HPO4 (0.25 g/L), FeCl3 (0.003g/L),, MgSO4 (0.513 g/L), NaNO3 (1g/L). The final pH of the medium was adjusted up to 7.00.02. 2.2. Mass propagation and culture maintenance: 118 Culture volume of each isolated monoalgal culture successively increased by adding fresh autoclaved medium under laminar flow conditions. Isolated colonies of microalgae identified morphologically by using standard monographs (Desikachary, 1959) under 40X and 100X magnification of Carl Zeiss Microscope. The isolated cultures were also maintained as mother culture as well as on solid agar containing media plates and slant test tubes. 2.3. Screening of microalgal strains: Isolated microalgal strains were checked for their growth in different media (BG11, ZM, ACB, BBM) with some selective range of pH 3.0-10) to know their optimum growth. Growth was monitored at OD540, dry weight (oven dry weight at 80ºC) and pH. All the cultures were harvested in stationary phase by centrifugation at 8000 rpm. The promising microalgae of higher biomass productivity were grown at 1000 ml volumetric scale. After harvesting and drying of microalgal biomass, total lipid extracted, separated and weighed gravimetrically. Microalgae having higher biomass productivity and lipid content (lipid productivity) were selected for further experiments. The total lipid was extracted from freeze-dried biomass using Chloroform: Methanol in 2:1 ratio (Bligh and Dyer, 1959). The extracted total lipid for each sample was weighed gravimetrically after removal of solvent and, %lipid calculated (Bligh and Dyer, 1959). All sample analyzed in triplicates. The resistance of microalgal strains towards CO2 was checked by inhibition of growth in sterile CO2 incubator under different CO2%. The 100 ml of each selected microalgal culture having OD540 of 0.25 was inoculated in 250 ml flask containing favorable media. All culture flasks transferred 119 in CO2 incubator at 50µM photons/m2/sec. light and 30ºC temp. for incubation wherein mouth of the flasks kept open for direct exposure of CO2. The light source was provided externally and light transmitted through glass door of CO2 incubator. The OD540 and pH were checked daily. 3. Results and discussions: The Oscillatoria spp., Phormidium spp., Lyngbya sp. Chlorella spp., Monoraphidium sp., Navicula sp., Chroococcus sp., Spirulina sp., Synechococcus sp., Synechocystis sp. and Scenedesmus sp. were isolated and identified as shown in Table 1. Out of total 17 strains, unicellular microalgae were chosen for the study. The most of the strains were alkalophilic but some of them were able to tolerate acidic conditions eg. Chlorcoccum sp., Synechoccoccus sp., and Synechocystis sp. showed growth even when pH was acidic (6.80, 4.0 and 3.0) in BBM and BG11, which showed the resistance of these strains. The highest OD540 was observed in Monoraphidium minutm and Chlorella variabilis in ZM as shown in Table 2. The Monoraphidum minutum, Synechococcus sp., Chlorococcum sp. and Chlorella sp. had higher biomass productivity (Table 3). Monoaraphidium minutum showed maximum biomass productivity (24.75 mg/L/day) at pH 8.0 in ZM. Monoraphidium minutum also showed comparable biomass productivity (23.83 mg/L/day) at pH 10.0 in the same ZM. The second most promising strain was Chlorella variabilis with 23.57 mg/L/day and 24.75 mg/L/day at pH 10.0 and pH 8.0 in ZM, respectively. Both M. minutum and C. variabilis were also having good growth in ACB after ZM as shown in Table 2 & Table 3. These both strains had CO2 tolerance of 2%. The total lipid% of the 120 four promising microalgae was estimated. The lipid% of Monoraphidum minutum, Synechococcus sp, Chlorococcum sp. and Chlorella sp. were 20.93±1.12, 14.60±0.43, 14.07±0.58 and 15.3±0.55, respectively. 4. Conclusion: Out of the studied strains, Monoraphidium minutum and Chlorella variabilis were selected because of their higher lipid, biomass productivity and CO2 tolerance. Chlorella variabilis was also selected because of its ongoing successful trial of mass cultivation in open ponds by CSIR-CSMCRI team. 121 Table 1. Isolated microalgal strains from different sites. Major region Vasad Ankleshwar Sub-site Code MAHI A-DP A-CP2 A-AML2 Isolated strains Chlorella, Lyngbya Chlorella Scenedesmus Chlorella A-AML Oscillatoria, Phormidium Su- IE Chroococcus, Scenedesmus, Monoraphidium Surat- Hazira Su-CS Somanath Madhavpur Bet-Dwarka Som-CS M-CS D-CS Navicula Synechococcus, Spirulina Phormidium Synechocystis, Chlorococcum, Phormidium 122 Table 2. OD540 of the selected microalgal strains on 18th day in different media and pH. Name of the strain/genus BG11 ZM ACB BBM Initial pH 7.1 6.0 3.0 10.0 8.0 6.0 3.0 8.0 6.0 3.0 6.8 4.0 Chlorococcum sp. Mean 0.82 0.51 0.40 0.46 0.55 0.65 0.29 0.71 0.99 NG 1.52 0.75 SD 0.00 0.02 0.01 0.06 0.00 0.04 0.00 0.10 0.05 0.00 0.01 0.43 Synechococcus sp. Mean 0.95 0.84 0.43 0.68 1.71 0.42 0.41 0.65 0.44 NG 0.40 NG SD 0.03 0.03 0.00 0.06 0.03 0.01 0.01 0.00 0.00 0.00 0.00 Synechocysits sp. Mean 0.88 0.79 0.68 0.45 0.30 0.50 0.00 0.48 0.57 NG SD 0.03 0.02 0.00 0.01 0.00 0.01 0.00 0.03 0.01 0.00 Chlorella Variabilis Mean 0.44 0.30 NG 1.79 1.88 0.63 0.00 0.92 1.21 SD 0.02 0.00 0.00 0.05 0.08 0.01 0.00 0.03 0.01 0.00 0.01 0.01 Monoraphidium minutum Mean 0.92 0.43 NG 1.81 1.89 0.70 0.00 1.74 1.22 NG 0.72 NG SD 0.01 0.04 0.00 0.02 0.05 0.00 0.00 0.01 0.03 0.00 0.00 0.00 Chroococccus sp. Mean 0.42 0.44 NG 1.08 1.37 0.95 0.31 1.22 0.42 NG 0.45 NG SD Mean 0.01 0.99 0.04 0.64 0.00 0.29 0.02 0.71 0.05 0.69 0.00 0.53 0.02 NG 0.01 0.89 0.01 0.96 0.00 NG 0.00 0.73 0.00 NG SD 0.01 0.00 0.00 0.02 0.01 0.01 0.00 0.01 0.02 0.01 0.03 0.00 Scenedesmus sp. 0.00 NG 0.30 0.00 1.10 NG 0.00 NG Italic value in the table shows optimum growth. NG shows that no growth was observed. 123 Table 3. Biomass productivity (mg/L/day) of some of the selected microalgal strains. BG11 ZM ACB BBM Name of the strain/genus Initial pH 7.1 6 3 10 8 6 3 8 6 3 6.8 4 Mean 10.80 6.72 5.27 6.06 7.24 8.56 3.82 9.35 13.04 NG 20.01 9.88 SD 0.01 0.26 0.13 0.79 0.01 0.53 0.09 1.32 0.66 - 0.13 0.66 Mean 12.51 11.06 5.66 8.95 22.52 5.53 5.40 8.56 5.79 NG 5.27 NG SD 0.40 0.40 0.04 0.79 0.40 0.13 0.13 0.04 0.03 - 0.03 - Mean 11.59 10.40 8.95 5.93 3.95 6.58 0.01 6.32 7.51 NG 3.95 NG SD 0.40 0.26 0.01 0.13 0.05 0.13 NG 0.40 0.13 - 0.01 - Mean 5.79 3.95 NG 23.57 24.75 8.30 NG 12.11 15.93 NG 14.48 NG SD 0.26 0.01 0.01 0.66 1.05 0.13 0.01 0.40 0.13 - 0.20 - Mean 12.11 5.66 NG 23.83 24.89 9.22 NG 22.91 16.06 NG 9.48 NG SD 0.13 0.53 0.00 0.26 0.66 0.00 NG 0.13 0.40 - 0.00 - Mean 5.53 5.79 NG 14.22 18.04 12.51 4.08 16.06 5.53 NG 5.93 NG SD 0.13 0.53 0.00 0.26 0.66 0.00 0.26 0.13 0.04 - 0.10 - Mean 13.04 8.43 3.82 9.37 9.16 7.03 NG 11.31 12.64 NG 9.66 NG SD 0.13 0.00 0.00 0.26 0.13 0.13 0.00 0.13 0.26 - 0.40 - Growth inhibition by minimum CO2 (%) 2 Chlorococcum sp. 1 Synechococcus sp. 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