Patent Application
20140099684
The present invention relates to utilizing naturally occurring lipid-bearing microalgal mats collected from the west coast of India for the production of fatty acid methyl ester (FAME) and demonstrating the suitability of the latter for the running of a regular vehicle. The invention also relates to raising readily harvestable lipid-bearing microalgal biomass (raised from Chlorella variabilis Accession No. PTA-12198) in solar salt pans and its further conversion into FAME which too is engine worthy.
Reference may be made to the article by Daemon Fairless, Biofuel: The little shrub that could—may be. Nature (2007) 449, 652-655 and Laurent Lardon et al, Life-Cycle Assessment of Biodiesel Production from Microalgae, Environmental Science & Technology (2009) 43:17, 6475-6481 wherein, the complex issue of food versus fuel is highlighted and the need for such biomass sources which would not interfere with food production is emphasised.
Reference may also be made by D. H. Lee, Algal biodiesel economy and competition among biofuels, Bioresource Technology (2011) 102, 43-49, to the scarcity of arable land and the need for alternative locations for generating biomass useful for fuel production, in which microalgae cultivation does not require large areas of arable land. Furthermore, cultivation sites can either be in desert areas or in shallow coastal waters.
Reference may be made to Ghosh et al U.S. Pat. No. 7,666,234, wherein, the utility of marginal lands for engine worthy biodiesel production is disclosed. The biomass in question is of terrestrial origin.
Reference may be made to the paper entitled “Biodiesel production by simultaneous extraction and conversion of total lipids from microalgae, cyanobacteria, and wild mixed-cultures” (B. D. Wahlen et al. Bioresource Technol., 2011, 102, 2724-2730).
Reference may be made to the articles by Doan et al, Screening of marine microalgae for biodiesel feedstock, Biomass and Bioenergy (2011) 35:7; 2534-2544 and Matsunaga et al. Characterization of marine microalga, Scenedesmus sp. strain JPCC GA0024 toward biofuel production. Biotechnology Letters (2009) 31: 1367-1372 wherein, marine microalgal species are reported to contain lipids which could serve as a source of biodiesel.
Reference may be made to U.S. Pat. No. 7,977,076; Nasrin Moazami et al. Biomass and lipid productivities of marine microalgae isolated from the Persian Gulf and the Qeshm Island.
Reference may also be made to the article by Brennan et al, Biofuels from microalgae: A review of technologies for production, processing, and extractions of biofuels and co-products. Renewable and Sustainable Energy Reviews (2010) 14: 557-577 which, states that microalgae are normally cultured for low volume high value products requiring limited land area or where the biomass can be raised indoors in photo-bioreactors.
Reference may be made to the articles by Hankamer et al, Photosynthetic biomass and H2 production by green algae: from bioengineering to bioreactor scale-up Physiologia Plantarum (2007) 131: 10-21 and Wang et al, CO2 bio-mitigation using microalgae. Applied Microbiology and Biotechnology (2008) 79: 5; 707-718; wherein, the importance of photosynthetic production of microalgal biomass for biofuel production is emphasised.
Reference may be made to the article by Douskova et al, Simultaneous flue gas bioremediation and reduction of microalgal biomass production costs, Applied Microbiology & Biotechnology (2009), 82:179-185 wherein, it is claimed that biomass productivity of microalgae can be raised through use of flue gas as rich source of CO2.
Reference may be made to any number of articles like Griffiths et al Lipid productivity as a key characteristic for choosing algal species for biodiesel production. Journal of Applied Phycology 2009, 21:493-507 and Report prepared for Sustainable Energy Ireland by Tom Bruton et al. A Review of the Potential of Marine Algae as a Source of Biofuel in Ireland (2009) which mention the importance of marine microalgae as source of biodiesel but, do not disclose where or how such cultivation will be taken up on a scale relevant to large scale biodiesel production.
Reference may be made to a review by Pittman et al The potential of sustainable algal biofuel production using wastewater resources, Bioresource Technology (2011) 102, 17-25. However, no mention is made therein of their utility for biodiesel production, besides Microspora sp. of mix culture from agricultural waste was neither determined nor used for lipid.
Reference may be made to the work by Syed Zahir Shah & Habib-ur-Rehman Khattak (Some Green Algae from Paddy Fields of Mathra (District Peshawar), Syed Zahir Shah & Habib-ur-Rehman Khattak, Department of Botany, Islamia College, Peshawar) disclosing the presence of Microspora sp. near Sind River as part of a study on biodiversity. No mention is made therein of any utility of the biomass.
Reference may be made to the paper entitled Cell division and wall structure in Microspora (Picketts-Heaps. New Phytologist, (1973) 72, 347-355) wherein the cytology of Microspora sp. is discussed. It is stated therein that, such alga may occur in the form of a mat. It is further stated that the alga may or may not contain lipids. No reference is made to any attempt to utilize such mats for biodiesel preparation.
Reference may be made to the article by Mata et al, Microalgae for biodiesel production and other applications: A review. Renewable and Sustainable Energy Reviews (2010) 14: 217-232; this enumerates the various species of marine microalgae which are lipid bearing and, in that sense, of potential interest as source of biodiesel.
Reference may be also made to the article by Greenwell et al, placing microalgae on the biofuels priority list: a review of the technological challenges. Journal of the royal society interface (2010), 7: 703-726 which says that, different microalgae grow at different rates and whereas some have high oil content they are impractical to use for other reasons such as slow growth rate, difficulty of harvesting the biomass, etc.
Reference may be made to the US2009/0298159 A1 wherein a method is provided to produce biodiesel from algae using two-stage, autotrophic and heterotrophic, growth phases of Chlorella variabilis for biodiesel production which includes a sequence of procedures: cultivating photoautotrophic algae, concentrating the cells and then transferring them to a fermentor for heterotrophic cultivation. Organic carbon is added during the heterotrophic cultivation stage. It is evident that the process is conducted in closed systems and requires concentration of the cells which is energy intensive. Moreover, no mention is made of the characteristics of the biodiesel nor of any trials conducted on vehicles.
Reference may be made to the site www.treehugger.com/chevron-backs-solazyme-to-develop-algal-biodiesel-technology.html to the article entitled “Chevron Backs Solazyme to Develop Algal Biodiesel Technology” dated 2 Feb. 2008, wherein Solazyme is producing biodiesel from sugar sources through fermentation in the dark.
It will be evident from the prior art that no cost-effective process has been disclosed for production of fatty acid methyl esters from such cultured or harvested biomass obtained from naturally occurring mats of microalgae. The present invention seeks to overcome all of these basic limitations and to evolve a novel, simplified and cost-effective process for producing fatty acid methyl ester from microalgal mats along with value added by-products from the waste co-streams. The total carbon of the water at the site was found to decrease with each subsequent collection. It may be attributed to the frequent collections from the same site.
Reference may be made to the patent application PCT/IN2010/000192 by Ghosh et al which discloses the culturing of Chlorella marine microalgal species and the advantages of mixotrophic growth. No reference is made therein of biodiesel production from the biomass nor of its practical cultivation on large scale so that the biomass is perceived as a high volume, affordable feedstock.
Reference may be made to the article by Greenwell et al placing microalgae on the biofuels priority list: a review of the technological challenges. Journal of the royal society interface (2010), 7: 703-726 and Chisti, Y et al; Biotechnology Advances (2003) which, brings out the difficulties of downstream processing of microalgal biomass and the high energy penalty as a result. Foremost among these is the difficulty of harvesting the biomass from highly dilute suspensions.
Reference may be made to the articles http://www.treehugger.com/renewable-energy/chevron-backs-solazyme-to-develop-algal-biodiesel-technology.html http://www.treehugger.com/cars/solazyme-b100-algae-biodiesel-goes-on-the-road.html disclosing the running of a vehicle on B100 microalgal biodiesel. However, the article states that the biomass was raised under heterotrophic conditions using sugars as organic carbon source.
There is no report on the performance of any biodiesel obtained from naturally occurring marine microalgal mats or thermo-tolerant marine microalgal biomass raised under practical conditions of autotrophic growth in solar salt pans.
During the search for the potential micro algae along the west coast, our team came across few sites showing probability of getting some desired microalgae through images observed in Google earth software. One of the sites we came across was located at Longitude 70□ 54.959′ E. and Latitude 20□ 42.391 N. (site 1), and another site located at Longitude 68□ 59.876′ and Latitude 22□ 23.975′ (site 2), India, it showed dense micro algal mat. On microscopic examination (morphology) of the mat, it revealed that the mat contained various algal species among which Microspora sp. was found to be dominant. Available method for biodiesel from algae is much energy consuming. Hence, attempts have been made to develop cost effective process to produce biodiesel from marine micro-algae.
Reference may be made to Bligh, E. G., Dyer, W. J., A rapid method for total lipid extraction and purification, Canadian Journal of Biochemistry and Physiology (1959). 37, 911-917. Lee et al. Comparison of several methods for effective lipid extraction from microalgae, Bioresource Technology 101 (2010) S75-S7, the method of extracting lipids from marine microalgal biomass which typically entails extraction with polar solvents and yields large amounts of phospholipids besides triglycerides, the former being undesirable for biodiesel production.
The main object of the present invention is to utilize naturally occurring mats of marine micro algal consortium and auto-settling marine microalgae raised in solar salt pans as sources of engine worthy fatty acid methyl ester (biodiesel).
Another object is to identify Cladophora sp. (ATCC Accession No. PTA-12199) and Microspora sp. (ATCC viability testing under progress) as the dominant species in the mats of the marine microalgal consortium referred to above.
Another object is to artificially cultivate such floating mats in solar salt pans and/or to raise lipid content through application of stress conditions.
Another object is to utilize Chlorella variabilis (ATCC Accession No. PTA-12198) isolated from the west coast of India as the auto-settling and thermo-tolerant marine microalgal strain ideal for raising in solar salt pans under summer conditions in Gujarat, India.
Another object is to minimize the energy penalty associated with lipid isolation from the biomass.
Another object is to utilize readily harvestable biomass as a means to reduce the energy penalty.
Another object is to create the opportunity to raise marine microalgal biomass on large scale utilizing ca.0.1 million acres of surplus land available for solar salt production.
Another object is to minimise the input costs for cultivation by using seawater, cheap inorganic nutrients, and avoiding mechanical gadgets for agitation of the culture medium while still achieving a maximum daily growth rate 45 g (dry basis)/m2/day during summer months.
Another object is to draw on basic practices followed in solar salt production such as gravity feeding and shifting of liquids from pan to pan.
Another object is to sundry the harvested biomass.
Another object is to extract lipid from sundried biomass using volatile non-polar solvents such as hexane to minimise the proportion of undesired lipids in the overall extracted lipid mass.
Another object is to optionally utilize fossil diesel for the extraction process where blended biodiesel is used.
Another object is to utilise solar thermal energy for the extraction and lipid isolation processes to maximise the energy output to input ratio.
Another object is to derive maximum value from the spent biomass.
Another object is to refine the raw oil through simple and cost effective means.
Another object is thereafter to draw on the known process of FAME production as disclosed in U.S. Pat. No. 7,666,234.
Another object is to demonstrate production of marine microalgal FAME with desired specifications of basic parameters such as viscosity, free fatty acid content, oxidation stability, free and total glycerol, phosphorous content, moisture content etc.
Another object is to demonstrate the running of a standard vehicle with B20 biodiesel produced from the marine microalgal mats and B100 biodiesel produced from Chlorella variabilis (ATCC Accession No. PTA-12198)
Another object is to utilise the by-product crude glycerol stream for accelerated growth and higher lipid content of the cultured microalgae as disclosed in the prior art.
The present invention provide Fatty acid methyl ester (FAME) for use as biodiesel, the esters being produced from naturally floating marine microalgal mats or thick layers of settled marine microalgae being formed during cultivation in solar salt pans or mixture thereof.
In an embodiment of the present invention is disclosed Fatty Acid methyl esters (FAME) 1 wherein the mats used for preparation of the biodiesel comprise lipid-bearing Microspora sp. (ATCC accession number awaited) or Cladophora sp. (ATCC Accession Number PTA 12199) as the dominant strains and the thick layer of marine microalgae cultivated in solar salt pan comprises thermo-tolerant Chlorella variabilis (ATCC Accession Number PTA 12198).
In yet another embodiment of the present invention is disclosed FAME wherein the lipid is extracted from marine microalgal mat comprising Microspora sp. (ATCC accession number awaited) through extraction with hexane, the lipid having composition as analyzed by GC-MS 0.6% of 14:0 fatty acid, 9.4% of 16:0 fatty acid, 0.7% of 16:1 fatty acid, 3.7% of 18:0 fatty acid, 33.2% of 18:1 fatty acid, 50.4% of 18:2 fatty acid, 0.7% of 20:0 fatty acid, 1.3% of 22:0 fatty acid.
In another embodiment of the present invention is disclosed FAME wherein lipid is extracted from marine microalgae from Chlorella variabilis (ATCC Accession Number PTA 12198), through extraction with hexane, the lipid having composition as analyzed by GC-MS 0.4% of 14:0 fatty acid, 12.1% of 16:0 fatty acid, 1.0% of 16:1, 1.0% of 16:2 fatty acid, 4.2% of 18:0 fatty acid, 29.4% of 18:1, 45.7% of 18:2 fatty acid, 4.8% of 18:3 fatty acid, 1.4% of 22:0.
In yet another embodiment of the present invention is disclosed FAME wherein the lipid is extracted from marine microalgal mat comprising Cladophora sp. (ATCC Accession Number PTA 12199) through extraction with hexane, the lipid having composition as analyzed by GC-MS 0.9% of 14:0 fatty acid, 0.4% of 15:0 fatty acid, 21.5% of 16:0 fatty acid, 1% of 16:1 fatty acid, 2.9% of 18:0 fatty acid, 21.2% of 18:1 fatty acid, 22.3% of 18:2 fatty acid, 0.5% of 20:0 fatty acid, 16.3% of 20:1 fatty acid, 0.4% of 22:0 fatty acid, 11.4% of 22:1 fatty acid, 0.7% of 24:0 fatty acid, 0.6% of 24:1 fatty acid.
In another embodiment of the present invention is disclosed FAME wherein the lipid fraction obtained from Microspora sp. is refined and transesterified to obtain FAME having composition as analyzed by GC-MS comprising 9.92% of 16:0 fatty acid, 2.44% of 18:0 fatty acid, 28.27% of 18:1 fatty acid, 59.37% of 18:2 fatty acid, and 5-30 ppm of BHT antioxidant.
In yet another embodiment of the present invention is disclosed FAME from Micorspora sp which is a clear yellow liquid having 0.872 gm/ml density, 4.5 cSt (at 40° C.) viscosity, 0.1014% total glycerol and 0.0086% free glycerol.
In another embodiment of the present invention is disclosed FAME for use in a regular unmodified diesel vehicle as B20 blend under full load condition and complying with emission requirements.
In yet another embodiment of the present invention is disclosed FAME, wherein the lipid fraction obtained from Chlorella variabilis (ATCC Accession Number PTA 12198) is refined and transesterified to obtain FAME having composition as analyzed by GC-MS comprising 6.9% of 16:0 fatty acid, 3.1% of 18:0 fatty acid; 32.6% of 18:1 fatty acid, and 57.3% of 18:2 fatty acid, and 5-30 ppm of BHT antioxidant.
In another embodiment of the present invention is disclosed FAME from Chlorella variabilis (ATCC Accession Number PTA 12198) which is a clear mustard yellow liquid having density at 25° C. and 40° C., 0.8704 and 0.8591 g/cm3, respectively; viscosity at 40° C., 4.8 cST; total glycerin, 0.15%; free glycerin, 0.02%; CFPP, moisture content, 0.029%; −5° C.; Phosphorous, 5.1 ppm; oxidation stability, 0.43 years (25° C.) and 0.12 year (40° C.) and calorific value as measured by Standard calorimetric test is 9842 kcal/kg
In another embodiment of the present invention is disclosed FAME for use in the same unmodified diesel vehicle of claim 8 as B100 biodiesel under full load condition and complying with the emission requirement.
In yet another embodiment of the present invention is disclosed FAME wherein the marine macroalgal mat dominant in Microspora sp. was harvested during July-December from 70° 54.959′ E., 20° 42.391 N.
In another further embodiment of the present invention is disclosed FAME wherein the Chlorella variabilis (ATCC Accession Number PTA 12198) is cultivated in salt pans located at: 72° 07.316′ E. 21° 47.4888′ N.; elevation, 28 feet, under autotrophic conditions during January-June.
In another embodiment of the present invention is disclosed FAME wherein the growth rate of Chlorella variabilis (ATCC Accession Number PTA 12198) in solar salt pans was in the range 11.67-45.56 g/m2/day.
In another further embodiment of the present invention is disclosed FAME wherein the lipid yield with hexane extraction for mats of Microspora sp. was in the range 5.22-16.32%.
In yet another embodiment of the present invention is disclosed FAME wherein the lipid yield with hexane extraction for the cultivated Chlorella variabilis (ATCC Accession Number PTA 12198) was in the range of 11.11-11.21%
In another further embodiment of the present invention is disclosed FAME wherein growth rate and lipid yield of Chlorella variabilis was influenced by addition of 3-6 kg of sodium bicarbonate, 1-2 kg sodium nitrate, and 0.01-0.02 kg ferrous sulphate per 1000 L of the seawater culture medium.
In another further embodiment of the present invention is disclosed FAME wherein crude glycerol by-product streams of the FAME process is optionally added to enhance biomass productivity by 50-200%.
In yet another embodiment of the present invention is disclosed FAME wherein solar reflectors were found to enhance the growth rate and lipid productivity of Chlorella variabilis during off summer period in open cultivation.
In another further embodiment of the present invention is disclosed FAME wherein residual biomass after solvent extraction of lipid is utilized in production of biofertilizer, aqua feed, source of carotenoids, and source of energy.
In yet another embodiment of the present invention is disclosed FAME, wherein co-product streams of crude glycerol is utilized for algal productivity through mixotrophic growth and/or for biodegradable biopolymer
Another aspect of the the present invention provides an integrated process for the preparation of engine worthy fatty acid methyl ester (biodiesel) from naturally harvested floating mats with consortium of Microspora and Cladophora ATCC Accession no. PTA-12199 and cultured microalgal mat along with the mass cultivated selected thermo-tolerant strain (Chlorella variabilis ATCC Accession No. PTA-12198) of microalgae and utilization of the by-products from the microalgal mass as well as the by-products from the fatty acid methyl esters and the said process comprising the steps of:
In an embodiment of the present invention is disclosed a process for the production of engine worthy fatty acid methyl ester for use as biodiesel, the process comprises the steps of:
In another embodiment of the present invention is disclosed a process for preparing FAME, wherein FAME obtained from Microspora sp.is. having composition as analyzed by GC-MS comprising 9.92% of 16:0 fatty acid, 2.44% of 18:0 fatty acid, 28.27% of 18:1 fatty acid, 59.37% of 18:2 fatty acid, and 5-30 ppm of BHT antioxidant.
In yet another embodiment of the present invention is disclosed a process, wherein FAME obtained from Chlorella variabilis is having composition as analyzed by GC-MS comprising 6.9% of 16:0 fatty acid, 3.1% of 18:0 fatty acid; 32.6% of 18:1 fatty acid, and 57.3% of 18:2 fatty acid, and 5-30 ppm of BHT antioxidant
In one embodiment of the present invention, the present invention provides an integrated process for the preparation of engine worthy fatty acid methyl ester (biodiesel) from nature and cultured microalgal mat along with the mass cultivated selected strain of microalgae and utilization of the by-products from the microalgal mass as well as the by-products from the fatty acid methyl esters.
In another embodiment of the present invention, the microalgal mat is a consortium of different microalgal species with Microspora and Cladophora spp. ATCC Accession No. PTA-12199 as the dominant species.
In yet another embodiment of the present invention, sea water with essential micronutrients/CSMCRI-ESF salt is used for the outdoor mass cultivation of the microalgae.
In yet other embodiment of the present invention, the oil extraction was done using solvents selected from the group consisting of hexane, chloroform, methanol, acetone, tetrahydrofuran, diethyl ether; preferably hexane, chloroform and methanol.
In a yet another embodiment of the present invention, the biodiesel co-product streams are used for production of PHA-biopolymers, biogas, gasification, fertilizer, aqua feed, carotenoids and for the preparation of briquettes.
A few sites showing the probability of getting some desired microalgae were selected through images observed in Google Earth software. One of the sites was located at Longitude 70° 54.959′ E. and Latitude 20° 42.391 N. (site 1), and another site located at Longitude 68° 59.876′ and Latitude 22° 23.975′ (site 2), India. It showed dense floating microalgal mat. On microscopic examination (morphology) of the mat, it revealed that the mat contained various microalgal species among which Microspora sp. and Cladophora sp. ATCC Accession No. PTA-12199 was found to be dominant. Available methods for biodiesel from algae is much energy consuming. Hence, attempts have been made to develop a cost effective process to produce biodiesel from a consortium in marine micro-algal mat as well as the isolated and mass cultivated strain of Chlorella variabilis ATCC Accession no. PTA-12198.
Utilization of the microalgal mats containing Microspora and Cladophora spp. ATCC Accession No. PTA-12199 (dominant from site 1 and 2 respectively) for biodiesel production with an integrated process is unique. The natural mat is widely spread and found to regenerate within a few weeks after it has been harvested. Besides, it was observed to regenerate at other experimental sites too. Mat of consortium with dominant Microspora and Cladophora spp. ATCC Accession No. PTA-12199 was found to survive and grow in a variable range of environmental parameters.
The main inventive steps are the following:
With the help of Google Maps™ a search was undertaken of green patches in coastal waters which may help us to identify possible floating microalgal mats. Some of the prominent green patches found were in the coastal regions of Goa (Madkai; 15° 41.0616′ N., 73° 95.6227′ E.), Kerala (Vellanathuruthu Road; 9° 01.6659′ N., 76° 52.5022′ E.), West Bengal (Port Canning, 22° 31.5577′ N., 88° 67.3307′ E.; Dongajora, 22° 13.2696′ N., 88° 60.2676′ E.; Haldia refinery, 22° 04.9408′ N., 88° 07.308′ E.), Diu (Nagoa road side, 70□ 54.959′ E., 20□ 42.391 N.) and Gujarat (Okha, 68□ 59.876′, 22□ 23.975′). Ground truthing was undertaken of the sites identified in Diu and Gujarat and indeed green coloured floating mats of microalgae were found.
The mats of Example 1 were collected and observed under the Microscope (Carl Zeiss Axio Imager at 40×) for taxonomic identification. Both mats revealed a consortium of microalgae which were dominated by the Chlorophycae family. The one collected from 70□ 54.959′ E., 20□ 42.391 N. had Microspora as the dominant form whereas the one collected from 68□ 59.876′, 22□ 23.975′ was dominated by Cladophora. Isolation of associated species of the consortium was carried out by using serial dilution method. The algal mat was washed with distilled water to remove the adhering dirt and impurities and was further subjected to centrifugation. The supernatant was collected and inoculated in 24 well tissue culture plates with different culture media (BG-11, BBM, Zarrouk's, ASN-III, etc). The serial dilution was carried out using 1:10 dilution. The tissue culture plates were kept in artificial light (300 lux) in 12 hr light and dark cycle at 25° C. After visible growth, the enriched culture were streaked on solid 1% Agarose plates. The Petri plates were incubated under artificial light (300 lux) in 12 hr light and dark cycle at 25° C. The isolated culture was inoculated aseptically in liquid medium and kept in artificial light (300 lux) in 12 hr light and dark cycle at 25° C. The mats from the above two locations were lyophilized and sent to American Type Culture Collection Centre (ATCC) for viability testing prior to allotment of accession numbers. One of the mats having Cladophora as the dominant lipid-bearing strain has been given ATCC Accession No. PTA-12199 while the viability testing of the other mat having Microspora as the dominant lipid-bearing strain is underway.
Naturally occurring marine microalgal mats were skimmed off from the microalgal dominated site Longitude 70° 54.959′ E. and Latitude 20° 42.391 N. The site was visited after 3-4 weeks on regular basis to study re-growth of the mats. During Summer season, the biomass productivity was 22.22 g/m2/day and total lipid content was 10%; during monsoon, the biomass productivity was 6.03 g/m2/day and total lipid content was 9.61% and during winter biomass productivity of 16 g/m2/day and total lipid content of 12.85% was achieved. This example teaches us that it is feasible to harvest microalgal mats from nature in sustainable manner.
The effect of elevated solar radiation on biomass productivity of ATCC-Chlorella variabilis was studied during winter (Air temp. 25-30 ° C.) in open tanks. Two tanks having 1.51 m2 area and depth of 0.3 m containing 200 L sea' water medium were inoculated with 10% inoculum of Chlorella culture (OD540 nm=1.65) The dry biomass yield after 14 days was 5.03 g/l with reflectors whereas the yield was 4.07 g/l in the control tank. This example teaches us the beneficial effect that solar reflectors can have on the cultivation process, especially when the ambient temperature is less than optimum.
Mass cultivation of Chlorella variabilis ATCC Accession No. PTA-12198 was carried out at the Institute's experimental salt farm (21° 47.488′ N. 72° 07.316′ E. Elevation: 28 ft.). The cultivation was carried out during the months of March-June. The outdoor temperature during the cultivation was 45±3° C. The culture needed for this purpose was first grown in two tanks with an area of 18 m2 each which were first used as inoculum tanks. The tanks were monitored regularly by measuring the pH, OD at 540 nm and biomass yield. After a cell concentration of 5 g/l (wet basis) was reached, the culture was used to inoculate 7 more tanks with an area of 18 m2 each and 3 tanks with an area of 90 m2 each. pH, OD at 540 nm, biomass yield and environmental parameters were regularly monitored. The tanks were agitated manually (thrice a day) using a hollow pipe tied with strings at its ends up to 18 days. After 20 days of cultivation, it was observed that the biomass settled automatically forming a thick layer at the bottom of the tanks. Data on biomass productivity is given in the table below.
The supernatant from each tank was transferred into an empty tank and the settled biomass was collected and sun dried. This example teaches us the feasibility of cultivating Chlorella variabilis (ATCC Accession No. PTA-12198) in solar salt pans
The experiments of Example 5 were repeated in two additional pans. 25 kg sodium bicarbonate, 6 kg sodium nitrate and 62.5 g of ferrous sulphate were added into 5000 L of the seawater culture medium. The biomass productivity was found to increase as can be seen from the table below.
This example teaches us that biomass productivity can be enhanced through addition of certain critical nutrients into the seawater medium.
Hexane extraction of lipid was conducted on the microalgal mats harvested from nature. Hexane was used as solvent. The data are provided in the table below. As can be seen, the lipid content varied from 5-16%.
Oil yield on
and-free bas
indicates data missing or illegible when filed
The study of Example 7 was repeated with Chlorella variabilis biomass of Examples 5 and 6. The data are provided in the table below. This example teaches us that cultivated biomass gives a more consistent oil yield.
The Table below gives relevant data pertaining to the fatty acid composition of the raw oils of Examples 7 and 8 as analysed by GC-MS above.
18.738 kg of, oil obtained in batch 1 of Example 8 was taken in a stainless steel vessel and was heated to 90° C. 1.8 kg of Fullers earth was added to it. The oil was filtered to obtain 15.916 kg of clarified oil. The clarified oil was analysed for its FFA content and was found to contain 0.6% FFA. 13 gm of NaOH was taken and dissolved in 65 ml of water. The alkali solution so prepared was added into the clarified oil and stirred for 15 minutes. It was filtered to remove soap. The filtrate clear oil weighed 15.210 kg. The refined oil was tranesterified using 2.92 kg (3.756 L) of methanol and 399.24 gm of KOH. The contents were stirred for 90 minutes at ambient temperature and allowed to stand for 60 minutes. The glycerol layer containing excess alcohol and KOH was separated; the weight of the glycerol layer was 4 kg. The biodiesel layer was washed with 682 gm of glycerol and allowed to settle for 60 minutes. The glycerol wash weighed 687 gm. The biodiesel layer was then washed with 1 L of water till pH reached 7. It was dried by heating the content at 110° C. 13.35 kg of Biodiesel so obtained was analysed for free glycerol, total glycerol, moisture, viscosity and density. The data are provided in the table below.
The study of Example 10 was also conducted with oil obtained from Batch 2 in Example 7. The data are provided in Table 6 below.
The table below provides the fatty acid composition of the fatty acid methyl esters of Examples 10 and 11, respectively as analysed by GC-MS. It will be evident that the compositions are very clean.
The data of Example 12 provided confidence that the marine microalgal biodiesels of Examples 10 and 11 may be engine worthy. B20 biodiesel prepared from the fatty acid methyl ester of Example 11 and B100 biodiesel of Example 10 were used directly in a regular TAVERA car without any modification whatsoever. No difficulty of any kind was seen in running of the vehicle and mileage similar to that of fossil diesel was estimated. A journalist had this to say about the running of the car on the B100 biodiesel of Example 11: “This correspondent took a test ride in the Tavera that was flagged off by the minister. The experience was equivalent to that of any other diesel vehicle, accompanied by a monotonous hum by a diesel engine. The two-km drive around the Central Secretariat area was smooth and without any hiccups.” (Dinsa Sachan, “Biodiesel from microalgae becomes a reality”, Down to Earth, Mar. 30, 2012; www.downtoearth.org.in).
Steam at 121° C. 15-psi pressure passed through the bed of 30 g of Chlorella biomass of calorific value 4590 kCal/Kg for 15 minutes. 10.1 g of this steam treated sample was taken in cellulosic thimble for lipid extraction in Automated Soxhlet of solvent capacity 150 ml for 4 hours with 100 ml of hexane at 80° C. The studies indicated that hexane extraction becomes more efficient after steam pretreatment and complete extraction required 10 hours compared to the 16 hours taken normally.
The extraction of carotenoids was done in a closed reaction vessel of 1 L capacity from 50 g deoiled microalgal biomass of Example 8. Extraction was conducted with 500 ml of 80% (v/v) acetone and kept in a dark room at constant magnetic stirring of 200 rpm. After continuous magnetic stirring for 3 hours, the solution was evaporated and the acetone free extract was filtered via filter paper to obtain carotenoids as the retentate. The carotenoids obtained ranged from 2-4%.
The residual biomass from Examples 7 and 8 were used for biogas production. After the biogas generation, the biomass slurry, which has a lot of micronutrients, carbon and nitrogen, can be used as a biofertilizer. The residual biomass can also be used as an aqua feed; it has proteins, carbohydrates and essential micronutrients. Briquettes of the residual biomass can be prepared.
Biogas production from waste microalgae biomass, after oil extraction, is potentially feasible and can considerably increase the energy yield from biomass. Therefore, it has been regarded as a necessary step in order to make biodiesel production from microalgae sustainable. (Torres and Jeison, 2010)
Residual deoiled biomass having calorific values of 1884.52 kcal/kg for deoiled cake of Example 7 and 1679.00, Kcal/kg for deoiled cake of Example 8 were taken. The digested slurry from the biogas plant was used as an inoculum for biogas production. The set was divided into three parts (1) Digester (5.0 L), (2) Glass holder bottle (1.0 L) and (3) Liquid displacement bottle (1.0 L). The digester was marked at 4.0 L capacity and its joints were made air tight by applying silicon tape and vacuum grease. Gas holder bottle of 1.0 L capacity was filled up to its mark with 1.0 L of a colour reagent. A graduated scale was pasted on it to measure the gas production accurately. The biogas experiment was conducted in continuous and batch mode for each Test (residual biomass) and one control digester each for the continuous and batch processes. The Hydraulic Retention time (HRT) for this experiment was 30 days and the feeding substrate was 5%; for continuous digester 134 ml (4.0 L/30 days=0.1333 or 134 ml) sample was replaced with 134 ml test [as 5% (6.7 g) biomass+67 ml slurry+67 ml t/w] daily through feeding tube while in batch digester 200 g biomass was added directly (5% for 4.0 L). A diluted activation solution at a ratio of 1:10 (multivitamin tablet and cysteine hydrochloride) was used to induce the growth of micro flora for biogas production and maintaining the anaerobic conditions. The resulting effluent slurry was analysed every day for parameters like total solids, total volatile solids, pH, electrical conductivity, total organic carbon, available nitrogen and available phosphorus. The total biogas production was also measured every day. The average daily biogas production in digester of deoiled biomass of Example 7 and 8 were 426.26 and 446.02 ml d−1, respectively, for the batch process and 270.51 and 473.15 ml d−1 for the continuous process.
The microalgal biodiesel by-product containing crude glycerol was utilized as a nutrient source for Mixotrophic, and heterotrophic growth of Chlorella variabilis, where all flasks containing 100 ml. sea water medium with variation of Algal Biodiesel waste residue (ABWR) for Mixotrophic growth at room temperature. After inoculation the OD is 0.5 at 540 nm. After 8 days biomass productivity was observed to be maximum in 5 g/L of ABWR (Mixotrophic). This example teaches us the utility of the crude glycerol stream in raising the biomass productivity.
The spent microalgal biomass is used as biofertilizer to promote growth and can substitute chemical fertilizers. The NPK content is 1.2:0.03:0.6 (%) for Cladophora, 1.4:0.01:1.1 (%) for Microspora and 2.19:0.01:1.0 (%) for Chlorella. Experiments were conducted in two plots for Maize crop with 6 lanes for control (K2O) and 4 lanes each for Cladophora, Microspora and Chlorella on equivalent nutrient (K2O) basis. The plant height, number of leaves per plant, numbers of cobs per plant, length and width of cobs and chlorophyll index were measured after eight weeks of growth. The results show that Chlorella gave the best results with an average plant height of 167.8±7.34 cm, 14.8±0.583 leaves per plant, 2 cobs per plant, 32.0±0.84 cm cob length, 7.24±0.24 cm cob width and 49.31±0.03 chlorophyll index (Opti-Sciences CCM-200, USA) as compared to control (chemical fertilizer K2O) 158.4±2.79 cm plant height, 13.6±0.4 leaves per plant, 1.6±0.25 cobs per plant, 28.6±0.75 cm cob length, 7.24±0.24 cm cob width and 40.25±1.97 chlorophyll index. An increase of 16.43% in yield was observed when Chlorella was used as a biofertilizer instead of K2O (control). This example teaches us a further utility of the deoiled cake.
The deoiled cake of Example 8 had calorific value of 1765.91 kcal/kg. The algae was mixed with 10% by weight of wet cow dung, converted to hand-made briquettes of diameter 4 cm and depth 2 cm and were subjected to open sun drying. 30 kg of such dried biomass was then charged into the biomass gasifier of 15 Kg/hr installed at the Institute's ESF premises. After about 10 minutes of gasifier operation, the combustible component of the producer gas was noted using an online gas analyser. The gas burnt with a yellow flame. This example teaches us that the deoiled cake can also be used in biomass gassifier.
Advantages of the present invention are:
| Number | Date | Country | Kind |
|---|---|---|---|
| 1507/DEL/2011 | May 2011 | IN | national |
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/IN2012/000372 | 5/22/2012 | WO | 00 | 11/20/2013 |
