energy balance and exergy analysis of large scale algal biomass production

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  • 7/27/2019 Energy Balance and Exergy Analysis of Large Scale Algal Biomass Production

    1/4

    The 2nd

    Korea - Indonesia Workshop & International Symposium on Bioenergy from Biomass

    DRN Building, Puspiptek, Serpong-BSD City, Indonesia, 13 15 June 2012

    Page 66 of 153

    ISSN: 2302-1454 (online)

    Energy Balance and Exergy analysis of large scale algal biomass production

    K. Sudhakar1, M. Premalatha2K.Sudharshan3

    1Energy department, Maulana Azad National Institute of Technology, Bhopal, India

    2 CEESAT, National Institute of Technology, Tiruchirapalli, India

    * Corresponding author; e-mail: [email protected]; tel.: +62-21-7560929; fax: +62-21-756-0549.

    Abstract:Microalgae Technology for the production of biochemical and bio fuels is emerging rapidly. Large-scale production facilities

    are necessary to fulfil the expected future demand for biodiesel and biochemical produced with algae. The present study assesses the

    sustainability of biofuel produced from microalgae and examines the environmental feasibility of a large-scale production through the

    use of energy balance and Exergy analysis adopting Life Cycle concept.Estimates of energy requirements for cultivation, harvesting, and

    oil extraction for algae biodiesel production are developed. Energy output in the form of algal biodiesel and the total energy content of

    algal biomass are compared to energy inputs required for algal cultivation & processing. Exergy analysis of algal-biodiesel cycle shows

    the overall process to be renewable. The results obtained indicate the energy content of the algae produced exceeds the energy required

    for cultivating algae.

    Keywords: Biodiesel, Large open pond, Life Cycle Analysis, Microalgae, Net energy Ratio

    1. Introduction

    Without a doubt, the world is now dependent on

    alternate sources of energy. Eukaryotic microalgae

    represent a promising alternative renewable source of

    feedstock for biofuel production. With over 40,000

    identified species; microalgae are one of the more diverse

    groups of organisms on Earth. Algae has seemed like a

    great renewable energy source because it's extremely

    efficient at creating energy from sunlight and it could

    potentially form closed loops for power plants - absorbing

    exhaust while creating new fuel. (Sheehan, 1998). hey

    naturally produce large quantities of biomass and many

    biomaterials, including lipids/oil.

    The theoretical maximum biomass and oil production

    of from microalgae has been calculated at 240 T ha-1

    yr-1

    and 57, 000 L ha-1

    yr-1

    for Indian

    Conditions.(Sudhakar.et.al .,2012),

    Algal biomass residues derived from the oil extraction

    process can be used to produce ethanol, and methane, and

    high-value biomaterials, such as biopolymers, carotenoids,

    and very long-chain polyunsaturated fatty acids.(Raja.R.et

    al.,2008)

    Microalgae naturally remove and recycle nutrients

    (such as nitrogen and phosphorous) from water and

    wastewater and carbon dioxide from flue-gases emitted

    from fossil fuel-fired power plants, providing an added

    environmental benefit (Li.Y.et al.,2008)

    The integration of wastewater bioremediation and

    carbon sequestration with biofuel production has not been

    demonstrated on Industrial scale. The micro algal research

    and development effort couples the use of microalgae for

    biofuels production with environmental bioremediation.

    However there are many challenges to be addressed which

    include refinement of the cultivation process, downstream

    processing of biomass and development of an economic

    feasibility model for commercialization of algae-basedbiofuels and biomaterials.Algae may be grown in large

    open raceway ponds or closed photo bioreactors. A

    number of closed photo bioreactors are being investigated,

    for cost-effective production of the algae. These include

    horizontal tubular, vertical tubular, thin film and

    helical/inclined systems. Productivity is higher in the case

    of algae cultivated in a photo bioreactor, but capitals and

    operating expenses are significantly higher than for open

    systems.(Chisti.Y.,2007)

    Fig. 1, Shows algae cultivation systems.

    (a)Open Pond

    (b) Tubular Photo bioreactor

    Fig 1: Algae Cultivation System

    Over the past two decades, algal-based biofuel

    research has progressed from outdoor large open pond to

    large-scale photobioreactor design and optimization, and

    downstream processing (i.e., harvesting, dewatering, and

    drying), to algal oil extraction. At the moment, algal

    biodiesels are not commercially produced and no

    economically viable production processes exist. Hence

    there exist many unknowns associated with the algae

    biodiesel production .Based on the state of the technology,there exists a need to quantify the energy and

    environmental sustainability effects of microalgae-to-

    biofuel process.

    PAPER CODE: OP-027

  • 7/27/2019 Energy Balance and Exergy Analysis of Large Scale Algal Biomass Production

    2/4

    The 2nd

    Korea - Indonesia Workshop & International Symposium on Bioenergy from Biomass

    DRN Building, Puspiptek, Serpong-BSD City, Indonesia, 13 15 June 2012

    Page 67 of 153

    ISSN: 2302-1454 (online)

    Hence the key objective of this study is to perform a LCA

    of the large scale microalgae biodiesel process and to

    identify the specific research efforts to make this process

    environmentally sustainable. This consequential life cycle

    analysis of algae biodiesel is based on estimated

    production potential of large scale algae biomass

    cultivation, process thermodynamics, and academicliterature data. This LCA follows algal biodiesel

    production through five stages: cultivation, harvesting,

    lipid extraction, transesterification, and reuse of the

    leftover biomass. The carbon and energy balance for each

    stage of production considering energy required, the

    energy produced, and the environmental impact are

    quantified.

    2. Materials and Method

    Large Scale open raceway pond cultivation system is

    considered in this study. For this energy input at each stage

    of the cycle during cultivation, harvesting, dewatering, oilextraction, transesterification is estimated. Total of energy

    input in all the process gives the total energy demand of

    the algae biodiesel cycle, which is energy input to the

    system. This energy input is called as indirect energy. The

    energy contained in the micro-algal bio-diesel (Eout) is

    compared with the total energy input (Ein).

    Fig.2. Flow diagram of Algal Biodiesel production process.

    Fig. 2 shows a flowchart listing main stages and inputs

    of microalgae biodiesel production process.Fig.3 shows

    step involved in LCA process.

    1. Goal Definition

    2. Life Cycle Inventory

    3. Impact Assessment

    4. Interpretation

    1. Goal Definition

    2. Life Cycle Inventory

    3. Impact Assessment

    4. Interpretation

    Fig.3. Life Cycle Assessment framework.

    Life cycle assessment (LCA) is a decision making tool

    to identify environmental burdens and evaluate the

    environmental consequences of a product, process or

    service over its life cycle from cradle to grave .The

    functional unit for the LCA analysis is 1 hectare of land.

    To evaluate the energy consumption during the life cycle

    of the micro-algae bio-diesel, a cradle to grave analysis is

    carried out. The data were organised in a MS-Excel

    spreadsheet, for transparency and easier calculations.

    Considered in the interaction during the lifecycle is

    indirect energy given to the system and not the materials,

    direct energy inputs like solar energy taken by the plant

    (micro-algae).

    2.1 Exergy Analysis and Energy balance

    When converting energy from one form to another

    more useful form the second law of thermodynamics

    dictates that some energy will be lost. Net energy gain

    (NEG), the difference between the total energy outputs and

    total energy inputs, is one of the accepted indices for

    analysing biofuels.

    Net Energy Gain = Energy output Energy Input.

    2.2. Carbon balance

    CO2 Reduction = CO2 Sequestered by microalgae

    CO2 produced during each Input stage.

    2.3 Net Energy ratio (NER)

    The energy efficiency of bio fuels can be analyzed by

    finding Net Energy ratio (NER). Net energy ratio is

    defined as the ratio of total energy outputs to total energy

    inputs.

    Ein =Egrowth+Eharvest+Edewatering +Edrying

    +Eoilextraction+Etransesterification (MJ ha-1

    )

    Eout = CV *T*1000*Where, CV= Calorific value of Micro algal biodiesel (MJ

    Kg-1

    ) = 41 (MJ Kg-1

    ) (Q.Wu.et al., 2006)

    T= Quantity of biodiesel (tonne)

    =brake-thermal efficiency of a CI Engine (20%)

    Water

    Water

    Water CO2 AlgaeLight

    Cultivation

    Harvesting/

    Drying

    Transesterification

    Extraction

    Liquid Algae

    Algae Cake

    Green Crude Biomass

    Glycerol Bio-Diesel

  • 7/27/2019 Energy Balance and Exergy Analysis of Large Scale Algal Biomass Production

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    The 2nd

    Korea - Indonesia Workshop & International Symposium on Bioenergy from Biomass

    DRN Building, Puspiptek, Serpong-BSD City, Indonesia, 13 15 June 2012

    Page 68 of 153

    ISSN: 2302-1454 (online)

    2.4 Assumptions:

    The various parameters and values used for this study are

    listed in Table 1.

    Table 1. Parameters used for the study (Liaw.et al,2010)

    Stage Inputs Unit value

    Growth Diesel fuel

    consumption

    L/ha 10

    Electricity

    Consumption

    KWh/ha 41404

    Algae

    dewatering

    Electricity

    use

    KWh/ha 30788

    Lipid

    extraction

    Natural

    gas

    Consumption

    MJ/ha 141994

    Electricity

    consumption

    KWh/ha 12706

    3. ResultsNet Energy balance, GHG Balance and NER for algal

    biodiesel production based on current technology, has been

    determined.

    3.1 Net Energy Balance Assessment of large scale raceway

    ponds.

    (i)Algal Cultivation:

    Diesel Use in growing microalgae = 10 L/hectare/year.

    Calorific Value of Conventional Diesel = 44,800 KJ/kg

    Density of Diesel = 0.832 kg/L.

    Therefore, Mass of diesel in 10 L = 8.32 kg

    Energy consumption of Diesel = 372.74 MJ/hectare/year.

    Electricity Use in growing microalgae = 41,404 KWh =

    149054.4 MJ/hectare/year.Total energy consumption in cultivation = 149427.14

    MJ/hectare/year

    (ii)Biomass Processing:

    Biomass processing (dewatering, drying) electricity use

    = 30,788 KWh/hectare/year.

    = 110836.8 MJ/hectare/year.

    Energy consumption in biomass processing is 110836.8

    MJ/hectare/year .

    (iii)Extraction and Esterification :

    Electricity Consumption in expeller = 12,706 KWh =

    45741.6 MJ/hectare/year

    Natural gas required = 1, 41,994 MJ/hectare/year

    Total power consumption in extraction and esterificationis 187735.6 MJ/hectare/year.

    (iv)Energy Available in Biodiesel Produced:

    Total quantity of biodiesel produced = 40,000

    kg/hectare/year.

    Calorific Value of Biodiesel = 37,800 KJ/kg

    Total energy available = 1512000 MJ.

    (v)Net Energy Assessment:

    Net Energy generated = 1512000 - 149427.14 -

    110836.8 - 187735.6 = 1064000.46 MJ/hectare/year.

    Net energy generated is 1064000.46 MJ/hectare/year

    from Microalgae Biodiesel.

    A cumulative energy analysis of algae biodiesel process

    is shown in Fig.4

    Fig 4: Energy assessment of Microalgae biodiesel.

    3. 2 Carbon balance of large scale raceway ponds

    (i)Algae Cultivation:

    Diesel Use in growing microalgae = 10 L/hectare/year.

    Electricity Use in growing microalgae = 41,404

    KWh/hectare/year.

    Carbon dioxide emission for diesel = 22.2 gallons/pound.

    I.e. Carbon dioxide emissions = 22.2 x 8.34 L/kg =

    185.15 L/kg

    Density of Diesel = 0.832 kg/L.

    Therefore, Mass of diesel in 10 L = 8.32 kg

    So, carbon dioxide emission = 8.32 x 185.15 L =

    1540.45 L of CO2

    = 0.154 m3

    of CO2

    Density of CO2 = 1.842 kg/m3.

    Therefore, weight of CO2 = 1.842 x 0.154 = 0.28

    kg/hectare/year.

    From electricity usage = 41,404 x 0.8 = 33,123.2

    kg/hectare/year of CO2

    Therefore, CO2 emission in growth stage = 33123.5

    kg/hectare/year.

    Total Carbon Dioxide emissions = 33123.78

    kg/hectare/year.

    (ii)Carbon Dioxide Sequestration by Microalgae:

    1 gram of algal biomass consumes 1.8 grams of CO2

    So, 91,000 kg/hectare of algae consumes (91,000 x 1.8)

    = 1, 63,800 kg/hectare/year.

    Total Carbon Dioxide sequestered during growth of

    microalgae is 1, 63,800 kg/hectare/year.

    (iii)Biomass Processing:

    Dewatering electricity use = 30,788 KWh/hectare/year.Carbon Dioxide emissions = 30,788 x 0.8 = 24,630

    kg/hectare/year.

    Carbon Dioxide emissions in Biomass Processing are

    24,630 kg/hectare/year.

    (iv)Extraction and Esterification:

    Electricity Consumption in expeller = 12,706

    KWh/hectare/year

    Carbon Dioxide emission = 12,706 x 0.8 = 10,164.8

    kg/hectare/year.

    Natural gas required = 1, 41,994 MJ/hectare/year

    Total power consumption = 1, 41,994 x (33/1000)

    = 4685.80 kg of CO2

    Total Carbon dioxide emission during extraction is10164.8 + 4685.80 = 14, 850.60 kg.

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