Elsevier

Renewable Energy

Volume 34, Issue 3, March 2009, Pages 667-673
Renewable Energy

Life cycle assessment of a multi-megawatt wind turbine

https://doi.org/10.1016/j.renene.2008.05.020Get rights and content

Abstract

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.

Introduction

At the present time, renewable energy, and particularly wind power energy, is becoming increasingly relevant in the world's electricity market. Over the last few years renewable sources of energy have won the legislative support of governments in several countries [2], [3], [4], [5], [6]. This support has taken the form of various legal frameworks with stable and lasting premiums. If we look at the current scene in the implementation of renewable energy, we can see the rapid advance made by wind power and its significant contribution to the electricity supply network in several countries, both at European and world level (see Fig. 1). Wind power supplies less than 1% of electricity now [7]. In the EU, 4% of the power installed originates from wind power and in Spain the figure is 9% [8]. Current forecasts predict that wind power will contribute 12% of the global demand for electricity by 2020 [9]. This huge boom in implementation and forecasts for wind power installation makes clear the need to increase people's understanding of this power source [10], [11]. Although there are several analyses about environmental impact of renewable energies [12], [13], [14], [15], not many life cycle assessment studies exist for current wind turbines with high rated power [16], [17], [18]. So an LCA model has been developed with the purpose of being able to assess the wind energy and the related emissions to produce current wind energy production technology. Furthermore, the LCA model can be used to define the energy payback time.

Section snippets

Goal, scope and background

The LCA model which has been developed seeks to identify the main types of impact on the environment throughout the life cycle of a wind turbine with doubly fed inductor generator (DFIG). The study has specifically focussed on the Gamesa onshore wind turbine model G8X with 2 MW rated power installed in the Munilla wind farm. This wind farm is located in the autonomous community of La Rioja, in northern Spain. This is a complex terrain located at 1200 m altitude. The general dimensions of this

Results of the LCA

Overall, the turbine unit has a greater environmental impact in the category corresponding to its effects on respiration, mainly due to substances of an inorganic source such as particle matter, sulphites and nitrates. Another aspect worthy of mention is the consumption of natural resources. This consumption is primarily reflected in the Fuel category.

Here are details of the main types of impact of each component in the various phases of the wind turbine's life cycle (see Fig. 3):

  • (a)

    Manufacturing

Energy payback time of the wind farm

We have established as an average production of 2000 full-load hours per year [35]. In that way for a 2 MW rated turbine, the annual output can be estimated as being 4 GWh. This output of electrical energy allows us to reduce the levels of environmental impact, since we can reduce the need for energy production from the existing conventional power stations. In the case of IR, this reduction supposes the elimination of emissions into the air, basically SO2 and NOX. Moreover, GWP basically assesses

The environmental impact of recycling end-of-life wind turbine

Another important aspect from the environmental point of view is to properly evaluate the decommissioning phase and the recycling of the turbine. In Table 4 we can see the values obtained for each of the phases of the recycling associated with the components defined in this study. Overall, the recycling processes studied allow us to significantly reduce the impact associated with the categories of Fuel, GWP, M, C and IR. Furthermore, the recycling results of the different components have been

Conclusions

From our study we can see that the foundation is the component which most affects the environment, particularly the cement, which is the main cause of the impact in the IR category. This fact points to the need to continue research into the manufacturing processes involved in preparing cement [36], [37], [38], in such a way that it would be possible to reduce its environmental impact. If we take into account that the effects on inorganic respiration as one of the main problems, it will be

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