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Life Cycle Analysis of Wind Turbine

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Life Cycle Analysis of Wind Turbine
Chaouki Ghenai
Ocean and Mechanical Engineering Department, Florida Atlantic University
USA
1. Introduction
The development of cleaner and efficient energy technologies and the use of new and
renewable energy sources will play an important role in the sustainable development of a
future energy strategy. The promotion of renewable sources of energy and the development
of cleaner and more efficient energy systems are a high priority, for security and
diversification of energy supply, environmental protection, and social and economic
cohesion (International Energy Agency, 2006).
Sustainable energy is to provide the energy that meets the needs of the present without
compromising the ability of future generations to meet their needs. Sustainable energy has
two components: renewable energy and energy efficiency. Renewable energy uses
renewable sources such biomass, wind, sun, waves, tides and geothermal heat. Renewable
energy systems include wind power, solar power, wave power, geothermal power, tidal
power and biomass based power. Renewable energy sources, such as wind, ocean waves,
solar flux and biomass, offer emissions-free production of electricity and heat. For example,
geothermal energy is heat from within the earth. The heat can be recovered as steam or hot
water and use it to heat buildings or generate electricity. The solar energy can be converted
into other forms of energy such as heat and electricity and wind energy is mainly used to
generate electricity. Biomass is organic material made from plants and animals. Burning
biomass is not the only way to release its energy. Biomass can be converted to other useable
forms of energy, such as methane gas or transportation fuels, such as ethanol and biodiesel
(clean alternative fuels). In addition to renewable energy, sustainable energy systems also
include technologies that improve energy efficiency of systems using traditional non
renewable sources. Improving the efficiency of energy systems or developing cleaner and
efficient energy systems will slow down the energy demand growth, make deep cut in fossil
fuel use and reduce the pollutant emissions. For examples, advanced fossil-fuel technologies
could significantly reduce the amount of CO2 emitted by increasing the efficiency with
which fuels are converted to electricity. Options for coal include integrated gasification
combined cycle (IGCC) technology, ultra-supercritical steam cycles and pressurized
fluidized bed combustion. For the transportation sector, dramatic reductions in CO2
emissions from transport can be achieved by using available and emerging energy-saving
vehicle technologies and switching to alternative fuels such as biofuels (biodiesel, ethanol).
For industrial applications, making greater use of waste heat, generating electricity on-site,
and putting in place more efficient processes and equipment could minimize external
energy demands from industry. Advanced process control and greater reliance on biomass
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and biotechnologies for producing fuels, chemicals and plastics could further reduce energy
use and CO2 emissions. Energy use in residential and commercial buildings can be
substantially reduced with integrated building design. Insulation, new lighting technology
and efficient equipment are some of the measures that can be used to cut both energy losses
and heating and cooling needs. Solar technology, on-site generation of heat and power, and
computerized energy management systems within and among buildings could offer further
reductions in energy use and CO2 emissions for residential and commercial buildings.
This Chapter will focus on wind energy. Electric generation using wind turbines is growing
very fast. Wind energy is a clean and efficient energy system but during all stages (primary
materials production, manufacturing of wind turbine parts, transportation, maintenance,
and disposal) of wind turbine life cycle energy was consumed and carbon dioxide CO2 can
be emitted to the atmosphere. What is the dominant phase of the wind turbine life that is
consuming more energy and producing more emissions? What can be done during the
design process to reduce the energy consumption and carbon foot print for the wind turbine
life cycle? The first part of this chapter will include a brief history about the wind energy,
the fundamental concepts of wind turbine and wind turbine parts. The second part will
include a life cycle analysis of wind turbine to determine the dominant phase (material,
manufacturing, use, transportation, and disposal) of wind turbine life that is consuming
more energy and producing more CO2 emissions.
2. Wind energy
The use of wind as an energy source begins in antiquity. Mankind was using the wind
energy for sailing ships and grinding grain or pumping water. Windmills appear in Europe
back in 12
th
century. Between the end of nineteenth and beginning of twentieth century, first
electricity generation was carried out by windmills with 12 KW. Horizontal-axis windmills
were an integral part of the rural economy, but it fell into disuse with the advent of cheap
fossil-fuelled engines and then the wide spread of rural electrification. However, in
twentieth century there was an interest in using wind energy once electricity grids became
available. In 1941, Smith-Putnam wind turbine with power of 1.25 MW was constructed in
USA. This remarkable machine had a rotor 53 m in diameter, full-span pitch control and
flapping blades to reduce the loads. Although a blade spar failed catastrophically in 1945, it
remains the largest wind turbine constructed for some 40 years (Acker and Hand, 1999).
International oil crisis in 1973 lead to re-utilization of renewable energy resources in the
large scale and wind power was among others. The sudden increase in price of oil
stimulated a number of substantial government-funded programs of research, development
and demonstration. In 1987, a wind turbine with a rotor diameter of 97.5 m with a power of
2.5MW was constructed in USA. However, it has to be noted that the problems of operating
very large wind turbines, in difficult wind climates were underestimated. With considerable
state support, many private companies were constructing much smaller wind turbines for
commercial sales. In particular, California in the mid-1980’s resulted in the installation of
very large number of quite small (less than 100 KW) wind turbines. Being smaller they were
generally easy to operate and also repair or modify. The use of wind energy was stimulated
in 1973 by the increase of price of fossil-fuel and of course, the main driver of wind turbines
was to generate electrical power with very low CO
2 emissions to help limit the climate
change. In 1997 the Commission of the European Union was calling for 12 percent of the
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Life Cycle Analysis of Wind Turbine
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gross energy demand of the European Union to be contributed from renewable by 2010. In
the last 25 years the global wind energy had been increasing drastically and at the end of
2009 total world wind capacity reached 159,213 MW. Wind power showed a growth rate of
31.7 %, the highest rate since 2001. The trend continued that wind capacity doubles every
three years. The wind sector employed 550,000 persons worldwide.
In the year 2012, the wind industry is expected for the first time to offer 1 million jobs. The
USA maintained its number one position in terms of total installed capacity and China
became number two in total capacity, only slightly ahead of Germany, both of them with
around 26,000 Megawatt of wind capacity installed. Asia accounted for the largest share of
new installations (40.4 %), followed by North America (28.4 %) and Europe fell back to the
third place (27.3 %). Latin America showed encouraging growth and more than doubled its
installations, mainly due to Brazil and Mexico. A total wind capacity of 203,000 Megawatt
will be exceeded within the year 2010. Based on accelerated development and further
improved policies, world wide energy association WWEA increases its predictions and sees
a global capacity of 1,900,000 Megawatt as possible by the year 2020 (World Wide Energy
Association report, 2009). The world’s primary energy needs are projected to grow by 56%
between 2005 and 2030, by an average annual rate of 1.8% per year (European Wind Energy
Agency, 2006)
2.1 Fundamental concept of wind turbine
A wind turbine is a rotary device that extracts the energy from the wind. The mechanical
energy from the wind turbine is converted to electricity (wind turbine generator). The wind
turbine can rotate through a horizontal (horizontal axis wind turbine – HAWT) or vertical
(VAWT) axis. Most of the modern wind turbines fall in these two basic groups: HAWT and
VAWT. For the HAWT, the position of the turbine can be either upwind or downwind. For
the horizontal upwind turbine, the wind hits the turbine blade before it hits the tower. For
the horizontal downwind turbine, the wind hits the tower first. The basic advantages of the
vertical axis wind turbine are (1) the generator and gear box can be placed on the ground
and (2) no need of a tower. The disadvantages of the VAWT are: (1) the wind speeds are
very low close to ground level, so although you may save a tower, the wind speeds will be
very low on the lower part of the rotor, and (2) the overall efficiency of the vertical axis wind
turbine is not impressive (Burton et al., 2001). The main parts of a wind turbine parts (see
Figure 1) are:
Blades: or airfoil designed to capture the energy from the strong and fast wind. The
blades are lightweight, durable and corrosion-resistant material. The best materials are
composites of fiberglass and reinforced plastic.
Rotor: designed to capture the maximum surface area of wind. The rotor rotates around
the generator through the low speed shaft and gear box.
Gear Box: A gear box magnifies or amplifies the energy output of the rotor. The gear
box is situated directly between the rotor and the generator.
Generator: The generator is used to produce electricity from the rotation of the rotor.
Generators come in various sizes, relative to the desired power output.
Nacelle: The nacelle is an enclosure that seals and protects the generator and gear box
from the other elements.
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Tower: The tower of the wind turbine carries the nacelle and the rotor. The towers for
large wind turbines may be either tubular steel towers, lattice towers, or concrete
towers. The higher the wind tower, the better the wind. Winds closer to the ground are
not only slower, they are also more turbulent. Higher winds are not corrupted by
obstructions on the ground and they are also steadier.
Fig. 1. Wind turbine parts
2.2 Wind turbine design
During the design of wind turbines, the strength, the dynamic behavior, and the fatigue
properties of the materials and the entire assembly need to be taken into consideration. The
wind turbines are built to catch the wind's kinetic energy. Modern wind turbines are not
built with a lot of rotor blades. Turbines with many blades or very wide blades will be
subject to very large forces, when the wind blows at high speed. The energy content of the
wind varies with the third power of the wind speed. The wind turbines are built to
withstand extreme winds. To limit the influence of the extreme winds and to let the turbines
rotates relatively quickly it is generally prefer to build turbines with a few, long, narrow
blades.
Fatigue Loads (forces): If the wind turbines are located in a very turbulent wind
climate, they are subject to fluctuating winds and hence fluctuating forces. The
components of the wind turbine such as rotor blades with repeated bending may
develop cracks which ultimately may make the component break. When designing a
wind turbine it is important to calculate in advance how the different components will
vibrate, both individually, and jointly. It is also important to calculate the forces
involved in each bending or stretching of a component (structural dynamics).
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Life Cycle Analysis of Wind Turbine
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Upwind/Downwind wind turbines designs: The upwind wind turbines have the rotor
facing the wind. The basic advantage of upwind designs is that one avoids the wind
shade behind the tower. By far the vast majority of wind turbines have this design. The
downwind wind turbines have the rotor placed on the lee side of the tower.
Number of blades: Most modern wind turbines are three-bladed designs with the rotor
position maintained upwind using electrical motors in their yaw mechanism. The vast
majority of the turbines sold in world markets have this design. The two-bladed wind
turbine designs have the advantage of saving the cost of one rotor blade and its weight.
However, they tend to have difficulty in penetrating the market, partly because they
require higher rotational speed to yield the same energy output.
Mechanical and aerodynamics noise: sound emissions from wind turbines may have
two different origins: Mechanical noise and aerodynamic noise. The mechanical noise
originates from metal components moving or knocking against each other may
originate in the gearbox, in the drive train (the shafts), and in the generator of a wind
turbine. Sound insulation can be useful to minimise some medium- and high-frequency
noise. In general, it is important to reduce the noise problems at the source, in the
structure of the machine itself. The source of the aerodynamic sound emission is when
the wind hits different objects at a certain speed, it will generally start making a sound.
For example, rotor blades make a slight swishing sound at relatively low wind speeds.
Careful design of trailing edges and very careful handling of rotor blades while they are
mounted, have become routine practice in the industry.
2.3 Wind farm
Commercial wind farms are constructed to generate electricity for sale through the electric
power grid. The number of wind turbines on a wind farm can vary greatly, ranging from a
single turbine to thousands. Large wind farms typically consist of multiple large turbines
located in flat, open land. Small wind farms, such as those with one or two turbines, are
often located on a crest or hill. The size of the turbines can vary as well, but generally they
are in the range of 500 Kilowatts to several Megawatts, with 4.5 Megawatts being about the
largest. Physically, they can be quite large as well, with rotor diameters ranging from 30 m
to 120 m and tower heights ranging from 50 m to 100 m. The top ten wind turbine
manufacturers, as measured by global market share in 2007 are listed in Table 1. Due to
advances in manufacturing and design, the larger turbines are becoming more common. In
general, a one Megawatt unit can produce enough electricity to meet the needs of about 100-
200 average homes. A large wind farm with many turbines can produce many times that
amount. However, with all commercial wind farms, the power that is generated first flows
into the local electric transmission grid and does not flow directly to specific homes.
2.4 Wind turbine power
The Wind turbines work by converting the kinetic energy in the wind first into rotational
kinetic energy in the turbine and then electrical energy. The wind power available for
conversion mainly depends on the wind speed and the swept area of the turbine:
(1)
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Table 1. Top ten wind commercial wind turbines manufactures in 2007
Where is the air density (Kg/m3), A is the swept area (m2) and V the wind speed (m/s).
Albert Betz (German physicist) concluded in 1919 that no wind turbine can convert more
than 16/27 (59.3%) of the kinetic energy of the wind into mechanical energy turning a rotor
(Betz Limit or Betz). The theoretical maximum power efficiency of any design of wind
turbine is 0.59 (Hau, 2000 and Hartwanger and Horvat, 2008). No more than 59% of the
energy carried by the wind can be extracted by a wind turbine. The wind turbines cannot
operate at this maximum limit. The power coefficient C
p needs to be factored in equation (1)
and the extractable power from the wind is given by:
(2)
The Cp value is unique to each turbine type and is a function of wind speed that the turbine
is operating in. In real world, the value of C
p is well below the Betz limit (0.59) with values
of 0.35 - 0.45 for the best designed wind turbines. If we take into account the other factors in
a complete wind turbine system (gearbox, bearings, generator), only 10-30% of the power of
the wind is actually converted into usable electricity. The power coefficient C
p, defined as
that the power extracted by rotor to power available in the wind is given by:
(3)
3. Life cycle analysis and selections strategies for guiding design
The material life cycle is shown in Figure 2. Ore and feedstock, drawn from the earth’s
resources, are processed to give materials. These materials are manufactured into products
that are used, and, at the end of their lives, discarded, a fraction perhaps entering a recycling
loop, the rest committed to incineration or land-fill. Energy and materials are consumed at
each point in this cycle (phases), with an associated penalty of CO2 , SOx, NOx and other
emissions, heat, and gaseous, liquid and solid waste. These are assessed by the technique of
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life-cycle analysis (Ashby, 2005, Ashby et al., 207, Granta Design, 20090). The steps for life
cycale analysis are:
1. Define the goal and scope of the assessment: Why do the assessment? What is the
subject and which bit (s) of its life are assessed?
2. Compile an inventory of relevant inputs and outputs: What resources are consumed?
(bill of materials) What are the emissions generated?
3. Evaluate the potential impacts associated with those inputs and outputs
4. Interpretation of the results of the inventory analysis and impact assessment phases in
relation of the objectives of the study: What the result means? What is to be done about
them?
The life cycle analysis studies examine energy and material flows in raw material
acquisition; processing and manufacturing; distribution and storage (transport,
refrigeration…); use; maintenance and repair; and recycling options (Gabi, 2008, Graedel,
1998, and Fiksel, 2009).
The eco audit or life cycle analyis and selection strategies for guiding the design are:
The first step is to develop a tool that is approximate but retains sufficient discrimination to
differentiate between alternative choices. A spectrum of levels of analysis exist, ranging
from a simple eco-screening against a list of banned or undesirable materials and processes
to a full LCA, with overheads of time and cost.
The second step is to select a single measure of eco-stress. On one point there is some
international agreement: the Kyoto Protocol committed the developed nations that signed it
to progressively reduce carbon emissions, meaning CO2 (Kyoto Protocol, 1997). At the
national level the focus is more on reducing energy consumption, but since this and CO2
production are closely related, they are nearly equivalent. Thus there is certain logic in
basing design decisions on energy consumption or CO2 generation; they carry more
conviction than the use of a more obscure indicator. We shall follow this route, using
energy as our measure. The third step is to separate the contributions of the phases of life
because subsequent action depends on which is the dominant one. If it is that a material
production, then choosing a material with low “embodied energy” is the way forward. But
if it is the use phase, then choosing a material to make use less energy-intensive is the right
approach, even if it has a higher embodied energy.
For selection to minimize eco-impact we must first ask: which phase of the life cycle of the
product under consideration makes the largest impact on the environment? The answer
guides material selection. To carry out an eco-audit we need the bill of material, shaping or
manufacturing process, transportation used of the parts of the final product, the duty cycle
during the use of the product, and also the eco data for the energy and CO2 footprints of
materials and manufacturing process.
The Life-Cycle Analysis has now become a vital sustainable development tool. It enables the
major aspects of a product’s environmental impact to be targeted, prioritization of any
improvements to be made to processes, and a comparison of two products with the same
function on the basis of their environmental profiles.
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Fig. 2. Material Life cycle analysis
4. Results: Life cycle analysis of 2.0 MW wind turbine
Life cycle analysis (LCA) of 2.0 MW wind turbine is presented in this chapter. The LCA
addresses the energy use and carbon foot print for the five phases (materials,
manufacturing, transportation, use and disposal) through the product life cycle (Martinnez
et al., 2009 and Nalukowe et al., 2006). Power generation from wind turbine is a renewable
and sustainable energy but in a life cycle perspective wind turbines consumes energy
resources and causes emissions during the production of raw materials, manufacturing
process, its use, transportation and disposal. In order to determine the impacts of power
generation using wind turbine, all components needed for the production of electricity
should be include in the analysis including the tower, nacelle, rotor, foundation and
transmission.
The bill of materials for a 2 MW land-based turbine (Elsam Engineering, 2004, Nordex, 2004,
and Visat, 2005) is listed in Table 2. Some energy is consumed during the turbine’s life
(expected to be 25 years), mostly in primary materials production, manufacturing processes,
and transport associated with maintenance. The energy for the transportation of small and
large parts of the wind turbine and the nergy used for maintenace was calculated from
information on inspection and service visits in the Vestas report (Elsam Engineering, 2004,
Nordex, 2004, and Visat, 2005) and estimates of distances travelled (entered under “Static”
use mode as 200 hp used for 2 hours 3 days per year). The manufacturing process for the
wind turbine parst are summarized in Table 3.
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Table 2. Bill of Materials for the 2 MW Wind Turbines
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Component
Manufacturing Process
Tower structure
Forging, rolling
Tower, Cathodic Protection
Casting
Nacelle, gears
Forging, rolling
Nacelle, generator core
Forging, rolling
Nacelle, generator conductors
Forging, rolling
Nacelle, transformer core
Forging, rolling
Nacelle, transformer conductors – Copper
Forging, rolling
Nacelle, transformer conductors – Aluminum
Forging, rolling
Nacelle, cover
Composite forming
Nacelle, main shaft
Casting
Nacelle, other forged components
Forging, rolling
Nacelle, other cast components
Casting
Rotor, blades
Composite forming
Rotor, iron components
Casting
Rotor, spinner
Composite forming
Rotor, spinner
Casting
Foundations, pile & platform
Construction
Foundations, steel
Forging, rolling
Transmission, conductors – Copper
Forging, rolling
Transmission, conductors – Aluminum
Forging, rolling
Transmission, insulation
Polymer extrusion
Table 3. Manufacturing Processes
The net energy demands of each phase of life are summarized in Figure 3. The life cycle
analysis was performed first without recycled wind turbine materials sent to landfill). The
second analysis was performed with recycled wind turbine materials (the wind turbine
materials that can be recycled were sent to recycling at the end life of the wind turbine). Figure
3 and Table 4 show clearly that the dominant phase that is consuming more energy and
produccing more CO2 emisions is the material phase. More energy is consumed and high
amount of CO2 is released in the atmosphere during the primary material production of the
wind turbine parts. The second dominant phase is the manufacuring process when the parts of
turbine are sent to landfill at the end life of the turbine. The results also show the benefits of
recycling the materials at the end life of the wind turbine. If all the materials are sent to landfill
at the end of life of the wind turbine, 2.18 E+011 J of energy (1.1 % of the total energy) is
needed to process these materials and 13095.71 Kg of CO2 (0.9% increase of the total CO2) are
released to the atmosphere at the end of life of the turbine. If the material of the wind turbine
are recycled, a total energy of 6.85E+012 J representing 54.8% of the total energy is recovered at
the end life of the material. A net reduction of C02 emissions by 495917.28 Kg (55.4% of the
total CO2 emission) is obtained by recycling the wind turbine material (see Table 4).
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Life Cycle Analysis of Wind Turbine
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Fig. 3. Life Cycle Analysis of Wind Turbine - With and Without Wind Turbine Material
Recycling
Table 4. Energy and CO2 Footprint Summary – Wind Turbine
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Table 5. Construction Energy, Wind Turbine Energy Output and Energy Pay Back Time
The turbine is rated at 2 MW but it produces this power only with the right wind conditions.
In a best case scenario the turbine runs at an average capacity factor of 40% giving an annual
energy output of 7.0 x 10
6
kWhr /year. The total energy generated by the turbine over a 25
year life is 175 x 10
6
kWhr (see Table 5). The total energy generated by the turbine over 25
year life time is about 32.32 times the energy required to build and service it (5.41 10
6
kWhr)
if the turbine materials are sent to landfill at the end of life of the turbine. If the materials are
recycled, the total energy generated by the turbine over 25 year life time is about 50.43 times
the energy required to build and service it (3.47 10
6
kWhr). With a wind turbine capacity
factor of 40 %, the energy payback time is about 9.27 months if the wind turbine materials
are sent to landfill at the end life of the turbine and is only 5.94 months if the materials are
recycled. The results show clearly the benefits of recycling parts of the wind turbine at the
end life of the turbine.
5. Conclusions
The development of cleaner and efficient energy technologies and the use of new and
renewable energy sources will play an important role in the sustainable development of a
future energy strategy. Power generation from wind turbine is a renewable and sustainable
energy but in a life cycle perspective wind turbines consumes energy resources and causes
emissions during the production of raw materials, manufacturing process, transportation of
small and large parts of the wind turbines, maintenance, and disposal of the parts at the end
life of the turbines. To determine the impacts of power generation using wind turbine, all
components needed for the production of electricity should be include in the analysis
including the tower, nacelle, rotor, foundation and transmission.
In eco aware wind turbine design, the materials are energy intensive with high embodies
energy and carbon foot print, the material choice impacts the energy and CO2 for the
manufacturing process, the material impacts the weight of the product and its thermal and
electric characteristics and the energy it consumes during the use; and the material choice
also impacts the potential for recycling or energy recovery at the end of life. The eco aware
wind turbine design has two-part strategy: (1) Eco Audit: quick and approximate
assessment of the distribution of energy demand and carbon emission over a product’s life;
and (2) material selection to minimize the energy and carbon over the full life, balancing the
influence of the choice over each phase of the life (selection strategies and eco informed
material selection).
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Life Cycle Analysis of Wind Turbine
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The results of life cycle analysis of the 2.0 MW wind turbine show the problem with the
energy consumed and carbon foot print was for the material phase. More energy and more
emissions are produced during the primary material production of the wind turbine parts.
The manufacturing process is the second dominant phase. The energy consumption and
carbon foot print are negligible for the transportation and the use phases. The results also
show clearly the benefits of recycling the wind turbine parts at the end of life. The life cycle
analysis of the 2.0 MW wind turbine show that 54.8% of the total energy is recovered and a
net reduction of C02 emissions by 55.4% is obtained by recycling the wind turbine materials
at the end of life of the wind turbine.
6. References
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Aerodynamics Experiment (Phase IV) Twisted Rotor”, AIAA-99-0045, Prepared for
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Ashby, M.F., (2005) “Materials Selection in Mechanical Design”, 3rd edition, Butterworth-
Heinemann, Oxford, UK, Chapter 16
Ashby, M.F. Shercliff, H. and Cebon, D., (2007), “Materials: engineering, science, processing
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Burton T., Sharpe D., Jenkins N. and Bossanyi E, (2001), Wind Energy Handbook, John
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European Wind Energy Agency, VV.AA. Annual report. Technical report, EWEA, European
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Fiksel, J., Design for Envirnment, (2009), A guide to sustianble product development,
McGraw Hill, ISBN 978-0-07-160556-4
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Granta Design Limited, Cambridge, (2009) (www.grantadesign.com), CES EduPack User
Guide
Hartwanger, D. and Horvat, (2008), A., 3D Modeling of a wind turbine using CFD,
NAFEMS UK Conference, Cheltenham, United of Kingdom, June 10-11, 2008
Hau E, (2000), Wind turbines. Springer: Berlin.
Elsam Engineering A/S, (2004) “Life Cycle Assessment of Offshore and Onshore Sited Wind
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International Energy Agency, VV.AA, (2006), Wind energy annual report, Technical report,
IEA, International Energy Agency.
Kyoto protocol, United Nations, Framework Convention on Climate Change, (1997),
Document FCCC/CP 1997/7/ADD.1
Martinnez E., Sanz, F., Pellegrini, s., Jimenez e., Blanco, j., (2009), Life cycle assessment of a
multi-megawatt wind turbine, Renewable Energy 34 (2009) 667–673
Nalukowe B.B., Liu, J., Damien, W., and Lukawski, T., (2006), Life Cycle Assessment of a
Wind Turbine, Report 1N1800
Nordex N90 Technical Description, Nordex Energy (2004)
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Energy, Engineering and Technologies – Manufacturing and Environment
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Vestas (2005) “Life cycle assessment of offshore and onshore sited wind turbines” Vestas
Wind Systems A/S, Alsvij 21, 8900 Randus, Denmark (www.vestas.com)
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Sustainable Development - Energy, Engineering and Technologies
- Manufacturing and Environment
Edited by Prof. Chaouki Ghenai
ISBN 978-953-51-0165-9
Hard cover, 264 pages
Publisher InTech
Published online 29, February, 2012
Published in print edition February, 2012
InTech Europe
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The technological advancement of our civilization has created a consumer society expanding faster than the
planet's resources allow, with our resource and energy needs rising exponentially in the past century. Securing
the future of the human race will require an improved understanding of the environment as well as of
technological solutions, mindsets and behaviors in line with modes of development that the ecosphere of our
planet can support. Some experts see the only solution in a global deflation of the currently unsustainable
exploitation of resources. However, sustainable development offers an approach that would be practical to
fuse with the managerial strategies and assessment tools for policy and decision makers at the regional
planning level. Environmentalists, architects, engineers, policy makers and economists will have to work
together in order to ensure that planning and development can meet our society's present needs without
compromising the security of future generations.
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and Technologies - Manufacturing and Environment, Prof. Chaouki Ghenai (Ed.), ISBN: 978-953-51-0165-9,
InTech, Available from: http://www.intechopen.com/books/sustainable-development-energy-engineering-and-
technologies-manufacturing-and-environment/life-cycle-analysis-of-wind-turbine-
... kilograms of CO 2 (representing a 0.9% increase in total CO 2 emissions) into the atmosphere. In contrast, recycling wind turbine materials allows for the recovery of a total energy amounting to 6.85 × 10 12 J, which constitutes 54.8% of the total energy, at the end of the material's lifespan [116]. ...
... As a result, 3D printing technology can reduce the waste generated from wind turbine systems by reusing the system components to build new wind turbines [118]. Furthermore, recycling of wind turbines results in a net decrease of 495,917.28 kilograms of CO 2 emissions, which accounts for 55.4% of the total CO2 emissions reduction [116]. Bassett et al. [124] discussed the possibility of utilizing 3D printing to create small wind turbines. ...
... This is primarily due to the high energy consumption and significant CO 2 emissions during the material phase. The production of wind turbine components using conventional manufacturing technologies consumes a substantial amount of energy and results in the release of a large volume of CO 2 into the atmosphere [116]. ...
... The main parts of a wind turbine are: the blades, rotor, gear box, generator, nacelle, and tower [16]. The blades are the biggest problem for utilization. ...
... The fragmented material was obtained from ANMET (Szprotawa, Poland). The material Materials 2023, 16, 4774 3 of 12 was sieved using a sieve with a mesh size of 0.5 × 0.5 mm to remove very fine and dusty fractions. Hereinafter, the material is referred to as polymer chips or windmill blade chips. ...
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Nowadays, a significant increase in interest in renewable energy sources can be observed. Wind farms have been one of the solutions representing this trend for many years. One of the important elements of windmills is the blades. The data indicate that what to do with the blades after their use is a global problem, and so it is important to find a way to recycle them. Hence, this work aimed to use these blades in the production of wood-based materials. Two fractions of a fragmented blade were used for the tests: a small one and large one. Boards characterized by densities of 650 kg/m3 and 700 kg/m3 were produced, in which the assumed substitution of the wood material with a polymer was 20% or 40%. Mechanical properties such as bending strength (MOR), modulus of elasticity (MOE), and internal bond strength (IB) were investigated. The 2S65 variant achieved the highest static bending strength and a modulus of elasticity of 2625 N/mm2. The second best result was noted for the 4S65 variant, which was significantly different from the 2S65 variant. In the case of the variants with a density of 700 kg/m3, no significant differences were found and their results were significantly lower. Moreover, research on thickness swelling (TS) after 24 h of immersion and water absorption (WA) were also conducted. The obtained results indicate that the manufactured boards are characterized by good physical and mechanical properties.
... During the production phase, the recycling of materials can result in a reduction of emissions by up to 90% [39,40]. Moreover, the energy payback time is reduced from 0.75 years to 0.5 years [40,41]. In addition to recycling, remanufacturing and reuse offer alternative ways to extend the lifespan of wind turbines and reduce material consumption [42][43][44]. ...
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This study explores the integration of sustainability considerations into quality management (QM) within wind turbine design, focusing on the framework provided by DIN EN ISO 9000ff. Quality management, which aims to prevent future failures and enhance economic efficiency, is traditionally tied to economic sustainability. However, this paper examines how QM can be expanded to address broader sustainability aspects, such as environmental and social impacts. This study’s primary objective is to assess the current state of sustainable wind turbine design using a literature review. Then the concept of Planetary Boundaries is introduced as a method for measuring sustainability in the early stages of product development. Additionally, it explores the potential of integrating quality management methodologies to guarantee adherence to sustainability standards and examines the effectiveness of preventive measures in the design phase.
... According to Invernizzi et al. (2019), decommissioning projects and megaprojects are the new, emerging, global, and unavoidable challenges that policymakers will face more and more severely in (Ghenai, 2012), in a decade or two, there will be plenty of decommissioning megaprojects in the wind power sector (Purnell et al., 2018). A similar consideration can be given considering about 500 GWe of solar power installed 1 . ...
... Согласно исследованиям [368,397], реализация вторичной переработки крайне важна с позиций показателей анализа жизненного цикла ВЭУ: показатель выбросов парниковых газов, срок компенсации энергии улучшаются на десятки процентов. Однако организация переработки и сжигания некоторых материалов требует развития технологий. ...
... Greenhouse gases emissions are calculated for onshore and offshore wind farms throughout their life cycle, considering a wind farm lifespan of 20 years [41]. Emissions are computed using the life-cycle assessment methodology [115],which accounts for all the phases of the product lifecycle: materials extraction, product manufacturing, transport, operation and disposal [116]. The life-cycle assessment methodology is internationally standardized and has been used to evaluate the environmental impacts of numerous energy systems [117,118]. ...
Article
Installed wind-generation capacity has been rapidly expanding globally and in France. In this article, we conduct a structured literature review on resources related, technical, economic, environmental and social aspects regarding onshore and offshore wind, with a focus on France. On the technical side, we cover the whole energy conversion chain. For economic aspects, we review different costs of wind energy systems. On the environmental side, we cover impacts on the fauna and flora and on greenhouse gases. Finally, on the social part, we consider local acceptance, visual and noise disturbance, and the potential of wind energy for creating jobs and improving farmers revenues. Compared to existing review articles, we gather, discuss and combine information on all of the above mentioned aspects. This is important as the combined consideration of these aspects is necessary for the sustainable implementation of wind energy projects. Additionally, we detail aspects that were insufficiently covered in the existing reviews such as generators technologies and the impact on farmers. This review can orientate policy makers and companies in their project development not only in France but also abroad, as several of the covered aspects (e.g. technical ones, several environmental ones) are also valid for other countries.
... During the optimization procedure, the ANN based model provide the maximum wind speed values over specified time intervals, taking into account the wind turbine lifetime, Ghenai [18], and the corresponding location's coordinates. The obtained results, computed for few time intervals are presented into Table 3. ...
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In order to obtain the most efficient solution in harvesting offshore wind energy, the converting devices must be located in places where the wind provides enough power, according to the used device specifications and, as possible, with constant value during turbine lifetime. On the other hand, the device must be chosen for a specific place-imposed by other reasons, like water depth, shore distance etc. The paper presents an analysis and prediction methodology for the wind speed based on the artificial neural networks modeling. The proposed approach uses as input data the previous recorded and forecasted wind speed values and the GPS coordinates for several places in Black Sea allowing the identification of the location with less wind speed modification during analyzed period of time. Also, the model provides useful information about inputs importance on output evolution. The obtained results are used for the identification of optimal placement of wind energy converting devices, leading to an improved efficiency.
Article
The global shift toward low-carbon growth policies has significantly expanded wind energy projects worldwide. South Korea plans to increase its wind energy capacity to 37 GW, up from the existing 1.97 GW as of 2024. However, wind turbine blades have an average lifespan of 20–25 years and the growth of the wind turbine market has raised issues regarding their recycling. Traditionally, discarded blades have been landfilled or incinerated, contradicting global carbon neutrality policies. To address these issues, developing and using recyclable materials in the design and manufacturing of blades is essential. In Korea, efforts have begun to develop technologies for recycling wind turbine blade materials, which are expected to reduce environmental impacts. To assess these reduction effects, this study conducted a life cycle assessment (LCA) of the recyclable materials of wind turbine blades. To understand the environmental reduction impact intuitively, the application of recyclable blade materials to an offshore wind farm (60 MW) in South Korea was simulated. The environmental impact of the wind farm was quantitatively analyzed by comparing the effects between cases of using conventional (non-recyclable) and recyclable materials. The environmental reduction effects of several single impacts and impact categories were analyzed for whole life cycle of the wind farm under the life cycle using recycled (scenario I) and non-recycled (scenario II) epoxy resins. Carbon dioxide emissions will be reduced by 15,140 Mt if the epoxy resin is recycled. Carbon monoxide and sulfuric acid have a difference of 85 Mt and 211 kg between two scenarios, respectively. The environmental mitigation effects for global warming potential(climate change), ozone depletion, and acidification show 18,816 Mt∙CO2-Eq, 519 kg∙CFC-11-Eq and 127,331,681 mol H + -Eq respectively. In conclusion, the LCA revealed that the environmental impact of wind turbine blades can be reduced by using a recyclable blade epoxy resin. Specifically, the result of this research shows a significant mitigation effect for carbon dioxide emission, monoxide emission, global warming potential and acidification impacts. Even though current recyclable wind turbine blade materials do not have a remarkable advantage compared to conventional ones, the results from this study will support to justify development of the technology and commercialization of recyclable blade resins.
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The island of Sark, located in the English Channel, has endured an electricity distribution crisis for the past few years, resulting in high electricity costs almost six times higher than UK mainland energy prices. This article is focused on a methodology for finding the best renewable energy system with the lowest levelized cost of energy (LCOE) in comparison to the current energy rate of 66 p/kWh. Three different main cases of study have been compared in performance for different levels of renewable energy integration and energy storage, evaluating the estimated size of the system, installation cost and CO2 emissions. The results, which depend on the assumptions outlined, show that Case 2 renewable energy generation system is the most suitable in terms of reduction of CO2 emissions and expected earnings from a lower LCOE. Uncertainty in the results could be minimized if actual data from the island is made available by following the same methodology to find the best solution to the island’s current energy generation problem. Due to non-available data for the load profiles and wind velocity a set of assumption were required to be implemented. As such, two different load profiles were selected—one with a peak of energy consumption in winter and the other with a summer peak.
Chapter
In the past, wind data were measured and evaluated almost exclusively from a meteorological point of view. However, these data are not sufficient when one is considering the commercial exploitation of wind resources by means of wind turbines. The earlier meteorological data do not provide much detailed information about the inner case in wind speed with height up to 150 m or the local wind conditions of a particular terrain. It is only in the past three decades that extensive wind measurements have been carried out with consideration of the particular aspects relating to the use of wind turbines. In the meantime, full-coverage wind data are available in the countries in which wind energy utilisation is widespread. A reliable database is provided mainly by the long-term evaluation of the energy supply from existing wind turbines.
Article
A novel materials-selection procedure has been developed and implemented in software. The procedure makes use of Materials Selection Charts: a new way of displaying material property data; and performance indices: combinations of material properties which govern performance. Optimisation methods are employed for simultaneous selection of both material and shape.
Chapter
Project development. Initial site selection, project feasibility assessment including the measure-correlate-predict technique for estimating energy yields from wind farm sites, micro-siting of turbines, the importance of public consultation and an overview of the preparation of environmental impact assessments.Visual and landscape assessment. Wind farm design and mitigation measures, assessment of visual impact and the use of Zones of Visual Impact (ZVI), wire-frame representations and photomontages.Noise. Terminology and basic concepts, sources of noise from a wind turbine, measurement and prediction of wind farm noise.Electro-magnetic interference. Impact of wind farms on various types of communication signals, modelling and prediction of electro-magnetic interference from wind turbines.Ecological assessment. Impact on birds.Financing wind farm developments. Project appraisal using discounted cash flow techniques, project finance and support mechanisms for wind energy development.
Article
At the present moment in time, renewable energy sources have achieved great significance for modern day society. The main reason for this boom is the need to use alternative sources of energy to fossil fuels which are free of CO2 emissions and contamination. Among the current renewable energy sources, the growth of wind farms has been spectacular. Wind power uses the kinetic energy of the wind to produce a clean form of energy without producing contamination or emissions. The problem it raises is that of quantifying to what extent it is a totally clean form of energy. In this sense we have to consider not only the emissions produced while they are in operation, but also the contamination and environmental impact resulting from their manufacture and the future dismantling of the turbines when they come to the end of their working life. The aim of this study is to analyse the real impact that this technology has if we consider the whole life cycle. The application of the ISO 14040 standard [ISO. ISO 14040. Environmental management – life cycle assessment – principles and framework. Geneva, Switzerland: International Standard Organization; 1998.] allows us to make an LCA study quantifying the overall impact of a wind turbine and each of its components.Applying this methodology, the wind turbine is analysed during all the phases of its life cycle, from cradle to grave, with regard to the manufacture of its key components (through the incorporation of cut-off criteria), transport to the wind farm, subsequent installation, start-up, maintenance and final dismantling and stripping down into waste materials and their treatment.
Article
A novel materials selection procedure containing a database of quantitative and qualitative data for a wide range of engineering materials was implemented in software. The management system provided an interactive graphical selection environment appropriate for mechanical engineering design using performance indices in the selection of materials with optimum properties and section shape.
Life Cycle Assessment of Offshore and Onshore Sited Wind Farms Report by Vestas Wind Systems A/S of the Danish Elsam Engineering International Energy Agency
  • Elsam Engineering
Elsam Engineering A/S, (2004) "Life Cycle Assessment of Offshore and Onshore Sited Wind Farms", Report by Vestas Wind Systems A/S of the Danish Elsam Engineering International Energy Agency, VV.AA, (2006), Wind energy annual report, Technical report, IEA, International Energy Agency.