Source: UNIVERSITY OF ARIZONA submitted to NRP
BIODIESEL PRODUCTION FROM ALGAE
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
ACTIVE
Funding Source
Reporting Frequency
Annual
Accession No.
0207917
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Jul 1, 2006
Project End Date
Sep 30, 2010
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
UNIVERSITY OF ARIZONA
888 N EUCLID AVE
TUCSON,AZ 85719-4824
Performing Department
AGRI & BIOSYSTEMS ENGINEERING
Non Technical Summary
The rising cost of fuels necessitates the development of alternative fuels such as biofuels. The rationale for the development of clean-alterative fuels, specifically "biofuels" such as biodiesel, is threefold - economic development, energy security and environment-friendliness. This study aims to produce biodiesel fuel using algae cultures grown in bioreactors.
Animal Health Component
40%
Research Effort Categories
Basic
20%
Applied
40%
Developmental
40%
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
4032150100010%
4032150202010%
4042150100010%
4042150202010%
5112150100020%
5112150202040%
Goals / Objectives
The objectives of the study are as follows: Phase 1: Bench-Top Microalgal Culture Optimization 1. To determine the effects of critical environmental factors, such as light intensity, culture density, and CO2 supply rate on the growth rate and hydrocarbon productivity of the algal culture; 2. To determine the effects of tertiary-treated wastewater (100%, 50%, 0%) on the growth rate and hydrocarbon productivity of the algal culture using the optimal settings for the environmental factors determined in the previous objective; and, 3. To determine reduction rates in N and P in the tertiary-treated wastewater used for algal culture. Phase 2: Bench-Top Microalgal Photobioreactor System 4. To determine the effects of various reactor parameters, such as height to diameter (H/D) ratio, ratio of cross-sectional riser and downcomer areas (Ar/Ad), number of internal optical cables, etc., on the growth rate and hydrocarbon productivity of the algal culture using the optimal settings for the environmental factors determined in Phase 1, and as a function of liquid flow rate; 5. To determine the performance of the photobioreactor in terms of growth rate, hydrocarbon productivity and reduction rates in N and P when the optimal level of tertiary-treated wastewater is used at the optimal settings for the reactor parameters and for the environmental factors previously determined; and, 6. To evaluate the economic feasibility of the photobioreactor.
Project Methods
Employing algal cultures grown in 125-mL flasks, a full-factorial experiment will be conducted with the following specifications: Factors (independent variables): Light intensity (100, 200, 250 micromol m-2 s-1) Culture density (0.05, 0.10 g/L), CO2 level (ambient, 5%) CO2 supply rate (0.002 l gas l-1 medium min-1, 0.0104 l gas l-1 medium min-1) Response Variables (Dependent Variables): growth rate, CO2 fixation rate, and hydrocarbon productivity Experimental Design: Thus, there will be a total of 3 x 2 x 2 x 2 = 24 experimental treatments. Each treatment will have three sample flasks. Also, a second time replication will be conducted. Experimental Set Up: The flasks containing the cultures will be in water baths (MW-1130A-1, Blue M, Blue island, IL, USA) to keep their temperature constant at 25 C. The treatments will be illuminated using 1.22-m (48-in) long, 40-W fluorescent lamps. The photoperiod will be set at 16 h per day. The average room ambient CO2 concentration over 24 hours is within the range of 370-405 ppm (micromol/mol) and will be verified during the course of the study. For elevated CO2 conditions, pre-configured 5% CO2 in cylinders will be used. The pre-configured 5% CO2 will be supplied to the batch cultures contained in flasks via a 1/8-OD tubing system. The CO2 concentration within ppm level will be measured using an IRGA, LCA-4 (Analytical Development Company Limited, Hertfordshire, England). Also employing flask experiments -- using the optimal settings for the environmental factors determined in the previous objective -- two treatments that use tertiary-treated wastewater (50%, 100%) will be evaluated with reference to a control (0% tertiary-treated wastewater). With the tertiary-treated wastewater being rich in nitrogen (N) and phosphorus (P), the aim is for the algae to further treat the water by assimilating the N and P, which the algae need for growth, while the algae is producing hydrocarbons. With the treatments and the control each having three sample flasks, there will be a total of 3 x 3 x 3 = 9 flasks. A second time replication will be conducted. The algal growth rates and hydrocarbon productivity will be measured in the same way as in the previous objective. Six 5-L bioreactors will be used for experimental treatments and three 5-L bioreactors will be used for the controls. The three treatments will have three combinations of H/D and Ar/Ad. The three controls will have the same three combinations of H/D and Ar/Ad, but will not be equipped with polymer cables for internal lighting. Each treatment will be tested with two levels (high and low) each of # fiberoptic cables and gas supply rate. Thus, there will be 2 x 2 = 4 runs for each of the three experimental treatments representing three combinations of H/D and Ar/Ad. Thus, there will be a total of 3 x 4 = 12 treatment runs and 3 x 4 = 12 control runs. A time replication will be performed.

Progress 01/01/06 to 12/31/06

Outputs
A factorial study on the growth of the oil-producing Botryococcus braunii cultured in 150-mL flasks was conducted by investigating the following factors: light (150, 200 micromoles per squared meter per second); mixing (0, 100 rpm); and carbon dioxide (0.035%, 5%). The algae cultures on average reached growth saturation on day 5. The results showed that algal growth with enrichment by carbon dioxide was at least double that under ambient conditions. Indeed, the treatments without enrichment of carbon dioxide and which did not receive mixing barely grew at all. The treatments without enrichment of carbon dioxide, but which received mixing, grew to an average of 12 gFW/L by the end of the growing period (day 8). By contrast, the treatments that were enriched with carbon dioxide grew to at least 30 gFW/L by the end of the growing period (day 8). The best treatment was obtained when provided with both enrichment of carbon dioxide and mixing. Bench-top tubular photobioreactors have been set up to investigate how the hydrodynamic properties in the photobioreactors correleate with the growth and oil production of the algae.

Impacts
Algae, such as B. braunii, possess major advantages as sources of biofuels including the following: (1) they constitute a renewable energy production system, using sunlight as energy source via photosynthesis; (2) they can contribute to the reduction of CO2 emissions by electric power plants by channeling the emitted CO2 into algae photobioreactors for biofuel production; (3) their energy productivity is 2 to 5 fold higher than traditional agricultural crops such as corn and soybeans and fast-growing "energy crops" such as willow and Miscanthus; (4) they require significantly smaller land area than agricultural crops when the algae are grown in scaled-up photobioreactors; (5) unlike agricultural crops, algal production in photobioreactors prevents the introduction of fertilizers and pesticides into the soil and groundwater as well as the disturbance and potential compaction and erosion of the soil; (6) lower quality water can be used for growing algae, such as the effluent of biological waste water treatment, aquaculture or hydroponic facilities; and (7) algae are not used traditionally as food and animal feed, unlike corn and soybeans whose use as feedstocks for biofuel production has already significantly raised their market prices.

Publications

  • No publications reported this period