TCASE 15: Comparison of four ‘clean energy’ projects

How can we compare the cost, performance and value-for-money of alternative large-scale clean energy projects? Actually, it’s pretty tough to try and avoid apples-and-oranges comparisons. Still, some adjustments can be made, such as for capacity factor, to partially levelise comparisons.

Below is a simplified comparison of four recent real-world projects. All can be considered first-of-a-kind installations, except for the wind farm.

1. A large proposed wind farm in South Australia (600 MWe peak)

The wind project will use 180 of the 3.4 MWe Suzlon turbines and “generate enough electricity to power 225,000 homes“. It includes a biomass plant that could produce up to 120 MWe of backup power to cover low-wind periods, and might offset up to 2.5 million tonnes of CO2 per year. At average 8m/s winds the capacity factor is estimated to be about 35%. A 60 km undersea high voltage direct current cable will connect it with Adelaide. Cost is $1.3 billion for the generating infrastructure and $0.2 billion for the cable.

2. A large Generation III+ nuclear power plant in Finland (1600 MWe peak)

The in(famous) Olkiluoto 3 NP unit, a European Pressurised Reactor (EPR) being built by the French (AREVA). The project has seen significant delays (first electricity now expected in 2014), and a cost blowout from the original € 3.7 billion to a new figure of € 6.4 billion. Despite this, the Fins have ordered two more EPR units. Assume it runs at the average Finnish capacity factor of 86%. 

3. A large solar PV plant under construction in New South Wales (150 MWe peak)

To be built in Moree, this will cover 3.4 km squared with 645,000 multi-crystalline PV panels, and is forecast to output 404 GWh per year (enough for 45,000 households). Part of the “Solar Flagships” programme, the cost is $A 923 million. Estimated to abate 364,000 tonnes of CO2 per year (based on NSW emission factor 0f 0.9 tCO2/MWh). Estimated capacity factor is 30.7% (based on peak power and GWh forecasts) — this seems high compared to typical PV performance.
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TCASE 14: Assessment of electricity generation costs

In the previous TCASE post, I considered how various low-carbon energy technologies meet the following criteria: commercial readiness, scalability, dispatchability, fuel constraints, load access, storage requirements, capacity factor and emissions intensity. Here I consider the next issue: cost of deployment, based on expert consensus.

Emission intensity for fit-for-service baseload electricity generating technologies. Error bars represent 90% confidence intervals for the mean (bar height). NOTE: PF Coal = Pulverised fuel black coal, CCGT = Combined cycle gas turbine, IGCC = Integrated gasification combined cycle, CCS = carbon capture and storage, FOAK = first of a kind, CC = combined cycle.

The primary data again come from the work I had published in 2011 in the peer-reviewed journal Energy (with colleagues Martin Nicholson [lead author] and Tom Biegler). Cost was analysed on the basis of 15 comprehensive levelised cost of electricity studies published over the past decade. The data are as follows (see also figure above), with references given in the footnote:

(LCOE = levelised cost of electricity (in 2009 US$/MWh) — see footnotes for a more detailed explanation.)

Enthusiastic supporters of various renewable energy technologies have long made claims that all or most of the world’s electricity needs could be met with renewable energy. Our analysis point to the costs involved and hence to the reliance on future major advances on that front in order to be competitive with other, low-emission, alternatives. In our view such reliance is highly speculative and risky as part of any plan to secure future energy.

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TCASE 13: Assessment of suitability of technologies for carbon dioxide mitigation

The problem of replacing our dependence on fossil fuels is complex. In Thinking Critically About Sustainable Energy (TCASE) #12, a checklist was provided to allow assessment of energy transition plans. The sort of questions listed in TCASE 12 are critical for evaluating the feasibility of future scenarios, like the ones from the recent IPCC report on renewable energy.

However, we also need to assess the capabilities of individual technologies to mitigate CO2 emissions, effectively (and economically). The following is a list of criteria that can be used to determine the relative viability of various alternative technologies. This comes from the work I had published recently in the peer-reviewed journal Energy (with colleagues Martin Nicholson and Tom Biegler):

Proven: Has the technology been used at commercial scale?

Scalable: Can the technology be built in sufficient quantity to replace significant proportions of existing fossil-fuel generators?

Dispatchable: Can the output be allocated by the system operator to meet the anticipated load?

Fuel supply: Is the energy source reliable and plentiful, even when, as with some kinds of renewable energy, it varies with time?

Load access: Can the generator be installed close to a load centre?

Storage: Does the technology require electricity storage in order to deliver a high capacity factor?

Emission intensity: Is the emission intensity high, moderate or low (as defined in the table below)?

Capacity factor: Is the capacity factor high, moderate or low (as defined below)?

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TCASE Video – Interactive discussions about the future of nuclear power

Thinking Critically About Sustainable Energy (TCASE) is a series of posts I’ve built up over the last year on BNC (and continue to add to). This has also branched off into a live seminar series (described in detail in this post), hosted by the Royal Institution of Australia (RiAus), and has proven to be very popular (a packed house each session). So far, we’ve covered new technologies in fossil fuels (including carbon capture and storage), established renewables (e.g. wind, solar), frontier renewables (e.g. engineered geothermal, marine), and, last week, nuclear. In the next session we will cover ‘demand side management and energy storage’ (event #5 on 3 Nov, with guests Craig Oakeshott from AEMO and Glenn Platt from CSIRO), and to cap off the series, energy futures: alternative 2050 visions (event #6 on 8 Dec, with guests Ziggy Switkowski from ANSTO and Peter Seligman from Uni Melbourne). Book your seats for the last two events!

That was just a reminder, however. The main purpose of this post was to highlight the content of TCASE Seminar #4: Interactive discussions about the future of nuclear power, held last Wednesday 8 Oct 2010 at the RiAus. The moderator for this session was Prof Gus Nathan, Director of the Centre for Energy Technology (CET). There were two speakers, Dr Kim Talus from University College London’s School of Energy and Resources, and me (Barry Brook, from University of Adelaide and also a member of the CET). I have to say, I think it was the most enjoyable and worthwhile public event I’ve been engaged with over the last few years. All three speakers/panelists really clicked, the questions and answers (conducted in the style of the gentle art of interrogation) flowed naturally, and the audience was also genuinely engaged.

Now I know people tend to be reluctant to watch videos etc. online, rather than in attendance, but I’d really urge you to take the time and watch this event. It’s something I’m very proud of (and I don’t say this lightly). Moreover, I think it — between my cover talk and the subsequent Q&A sessions — covers most of the major bases of my thinking on nuclear energy as a sustainable energy source and a key solution in the effort to mitigate our current fossil fuel dependence.

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TCASE 12: A checklist for renewable energy plans

Guest post by John D. Morgan. John runs R&D programmes at a Sydney startup company. He has a PhD in physical chemistry, and research experience in chemical engineering in the US and at CSIRO. He is a regular commenter on BNC.

A 10-page printable PDF version of this post can be downloaded here.

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Beyond Zero Emissions recently launched their Zero Carbon Australia 2020 Stationary Energy Plan (read the BNC community critique here).  It joins a growing list of renewable energy plans – Desertec, Greenpeace’s Energy [R]evolution, World Wildlife Fund Australia’s Clean Energy Future, Peter Seligman’s Australian Sustainable Energy, and others around the world.

The need to cut ourselves loose from our carbon based economy is urgent, and proponents of these plans are to be applauded.  But, can they work?  Many posts and comments at Brave New Climate have focussed on the hurdles facing large scale renewable power.  Here I have tried to distill these points into a checklist to bear in mind when considering these plans.  The list is followed by some brief exposition of each item. Some of these items refer to some Australian specifics, but similar questions will arise in other countries.

These items are not a set of pass/fail criteria, rather, they are prompts to ask “Did the plan address this point, and how?” The list is not exhaustive – many other questions could be raised, and hopefully will be in the comments.  I have not really considered nuclear power in this list because I am not aware of similar comprehensive attempts to plan carbon free nuclear economies (perhaps there should be) – there would be questions, but unlike renewable energy, we have existence proofs that it can be done.

So, how does the plan check out?

0. The checklist

□     What is the emissions reduction target?

□     What is the budget for the plan?

□     How is the plan to be financed?

□     What is the cost of power if the plan is implemented?

□     What is the CO2 avoidance cost ($/tCO2 avoided)

□     Can the plan scale to 100% emissions reduction?

□     What is the timeframe of the plan?

□     What current and future demand is assumed?

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TCASE 11: Safety, cost and regulation in nuclear electricity generation

Guest post by DV82XLHe is a Canadian chemist and materials scientist. For his previous article on the 2010 Nuclear Security Summit, see here, and on why an informed public is key to acceptance of nuclear energy, see here.

Unless you intend to design a nuclear reactor from scratch, you are going to have to accept whatever level of safety is designed into the one you buy. No original equipment manufacturer (OEM) is going to derate their product to cut costs for you. And that will go for things you will have to build yourself, like the containment, and spent fuel facilities. No one is going to risk their brand letting you install their product on a substandard site. But this is not where costs get out of control anyway.

Nor is it in operating safety protocols, which at any rate are tied into general plant integrity routines that must be done anyway. Ultimately cutting back in this area runs the risk of some failure occurring that might stop the plant from producing power, (i.e. stop making money) or causing harm to an employee. In other words most of this falls under housekeeping anyway.

The only place where costs can be controlled which is often (erroneously) referred to as safety issues, is unreasonable procedural nonsense during the initial build. Even this is not the real expense in and of itself, but it is the delays that these can cause that push cost overruns into the stratosphere. It is seeing that these do not get out of hand that is the real way to keep costs down. In any sane world too, most of these procedural issues would be properly referred to as Quality Assurance, or Quality Control (QC), as they would have little to do with real safety issues, but in the politically charged world of nuclear power plant (NPP) builds, the antinuclear forces spin these to security and safety issues their own ends.

Okay, so how to avoid this sort of pitfall? First and foremost there must be only one government agency/department/ministry/whatever, in charge of oversight, and it needs to be at the national level, and it needs to exercise eminent domain. Once the project has broken ground, it cannot be delayed by politics, or by lower levels of government. Some local water commissioner up for re-election cannot be permitted to bring the project to a halt while he grandstands demanding a second opinion on groundwater contamination, two years after the first one was done and approved. Similarly, abuses of the legal system by non-government organisations (NGO’s) have to be made impossible as well. Many of these like Greenpeace, are well aware of the financial dynamics of these builds, and are past masters at using the courts to get injunctions for the sole purpose of running up the costs, in the hope of getting a project cancelled. In fact they have been successful more than once with this tactic.

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Thinking Critically about Sustainable Energy (TCASE) – the seminar series

In the Thinking Critically About Sustainable Energy (TCASE) series — currently up to 10 parts on the BNC blog — I consider the challenges we face in scaling up renewable or nuclear energy technologies to replace fossil fuels. The blog serialisation of TCASE will continue on BNC, but the format is now also moving into a new communication medium — interactive seminars. In collaboration with the Royal Institution of Australia (RiAus), I have been planning — and will act as host and moderator — for the ‘TCASE Live’ series, launching next week on Wed 7th July 2010. The event is sponsored by the Environment Institute’s Centre for Energy Technology (of which I’m a member), and the Institute for Mineral and Energy Resources.

To book your (free) seat at the first event, click here. Do it soon, to avoid disappointment (the venue can only hold about 130 people). Each session will be held at the Science Exchange in Adelaide (Google Map link), and will also be broadcast soon after each event on the internet (tune into my Twitter feed to keep updated with the podcasts, vodcasts and slides).

Here is the context statement and sequence of events for the 6-part series, run monthly through to the end of 2010:

Thinking Critically for Sustainable Energy: the seminar series

The ability to harness natural resources and transform them into sources of useable energy has been essential in the development of modern society. As a result the supply and consumption of energy has now become central to the economies of developed nations and is vital in sustaining agriculture, construction, transportation and communications.

Since industrialisation, fossil fuels have represented a readily available and inexpensive source of energy. But as more countries become industrialised and the competition for these finite resources begins to increase exponentially, we are now facing the real threat that supply of these fuels may not be able to keep up with demand. Additionally the mining and burning of these fuels has been shown to have many adverse environmental effects. In particular the threat of anthropogenic climatic change due to the combustion of these fuels is now a major global concern.

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TCASE 10: Not all capacity factors are made equal

As I noted in a recent post, my new goal with TCASE posts is for them to be shorter, more targeted and more regular, with the aim being to break big problems in sustainable energy down into very focused questions (each of the new TCASE posts will be a maximum of 1,000 words — my new self-imposed editorial limit for this series!). Editorially, I like to note that if any regular BNC readers are up for submitting a short TCASE post following this format, please email me and I’ll be happy to discuss your idea. Here’s the first of the new batch.

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Capacity factor (CF) is the amount of energy a power station generates over time (usually a year) compared to what it could have produced if it had been running at full power for the whole period. (Please read TCASE 2, Energy Primer, for a fuller explanation). The CF for coal-fired and nuclear power stations averages 85-90%, wind farms ~20-35%, solar farms ~15-40% (the higher figure is for CSP with thermal storage). Gas or hydro can be high or low — depending…

Now, it’s very tempting to use these percentages as though they were directly interchangable, and indeed I’ve found that most journalists and bloggers happily do this (or else ignore CF completely and cite ‘peak’ power as though it were the same thing). It turns out, however, that this is a seriously misleading practice, as I’ll detail over the next few TCASE posts.

Consider this.

The Blowagale wind farm on Roaring Forty Peninsula has 50 of the 2.5 MWe (peak) GE 2.5xl turbines (rotor diameter = 100 m, hub height = 75 – 100 m, cut-in windspeed of 3.5 m/s, peak at 12.5 m/s, cut-out at 25 m/s). Its peak power is therefore 50 x 2.5 = 125 MWe. Over a 3-year period, it has delivered 1,115 GWh of energy to the grid. The peak expectation would have been 125 x 8760 x 3 = 3,285 GWh, so the CF is 1115/3285 = 34%.

The Trex coal-fired power station in Smogsville is a 500 MWe unit that’s been chugging away for the last 30 years. Over the last 3 years, it has produced 11,300 GWh (out of a possible 13,140), for a CF of 86%.

Okay, on an energy-for-energy basis, all we have to do is build 11300/1115 = 10 of the Blowagale-sized wind farms to replace Trex, right? Actually, that’s dead wrong — at least in the real world — for many reasons, which I’ll explore in the next few TCASE posts. Yet, that’s the impression that’s often given by ‘advocates’ (to use a euphemism).

First, let’s briefly consider what has determined these two CFs.

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TCASE 9: Ocean power II – CETO

In TCASE (thinking critically about sustainable energy) #5, I analysed a currently deployed technology for harnessing wave energy – the Pelamis device. If you haven’t read TCASE 5 then please do so now, since it explains some of the basic physical properties of wave energy, the extend of the global resource, etc. In writing the following post, I’ll consider this to be assumed knowledge.

CETO, named after a Greek sea goddess, has been developed by Carnegie Wave Energy (an Australian company), and is described in detail on their website. It is based on a submerged, underwater buoy-like device, anchored to the sea floor, which pumps water to shore at high pressure (6,400 kPa). Read more about the technology here.

The list of advantages of CETO on the website are worth citing here, as they provide a useful target for analysis. Main ones are:

  • 60% of the world live within 60km (40 miles) of a coast, removing transmission issues.
  • Waves are predictable days in advance making it easy to match supply and demand. (Wind is predictable hours in advance at best.)
  • CETO units are designed to operate in harmony with the waves rather than attempting to resist them. This means there is no need for massive steel and concrete structures to be built.
  • CETO wave farms will have no impact on popular surfing sites as breaking waves equate to areas of energy loss. CETO wave farms will operate in water deeper than 15 metres in areas where there are no breaking waves.
  • CETO is the only wave energy technology that produces fresh water directly from seawater by magnifying the pressure variations in ocean waves.
  • CETO contains no oils, lubricants, or offshore electrical components. CETO is built from components with a known subsea life of over 30 years.
  • Wave energy can be harnessed for permanent base load power and for fresh water desalination. The ratio of electrical generation to fresh water production can be quickly varied from 100% to 0% allowing for rapid variations in power demand.
  • CETO uses a great multiplicity of identical units each of which can be mass produced and containerised for shipping to anywhere in the world.

For these reasons, wave power is certainly among the most attractive of the range of possible renewable energy technologies. Unfortunately, it is also one of the most nascent in its development cycle (along with engineered geothermal systems, which is probably even further behind — I’ll cover this in a later TCASE post). Wave power is also up against one of the most hostile environments that any man-made structure has to endure — the salty (corrosive) and capricious (exposed to occasional very high energy events) marine environment.

CETO is certainly an innovative technology: it appears to overcome some of the shortcomings of the Pelamis device, such as a reduced bulkiness with more modular construction and deployment possible, lower vulnerability to storm damage due to anchoring at 25 m, and an added bonus of providing a neat method for reverse osmosis desalination using mechanical rather than electrical energy. The latter seems to be its biggest selling point, as I explain below.

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TCASE 8: Estimating EROEI from LCA

The concept of energy return on investment (EROI), often called energy returned on energy invested (EROEI), is a simple and familiar one. Here is the short definition, from the Encyclopedia of Earth. To cite:

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Energy return on investment (EROI) is the ratio of the energy delivered by a process to the energy used directly and indirectly in that process.

For example given a process with an EROI of 5, expending 1 unit of energy yields a net energy gain of 4 units. The break-even point happens with an EROI of 1 or a net energy gain of 0.

A common related concept is the energy payback period. Every energy system has initial investments of energy in the construction of facilities. The facility then produced an energy out for a number of years until it reaches the end of its effective lifetime. Along the way, additional energy costs are incurred in the operation and maintenance of the facility, including any self use of energy. The energy payback period is the time it takes a facility “pay back” or produce an amount of energy equivalent to that invested in its start-up.

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Wiki also has a decent article about it, and it’s a source of much discussion on websites like The Oil Drum. In short, a simple concept, but fraught with debate. It is not my intention here to wade into the arguments on EROEI of individual energy sources — that would require many TCASE posts, and even after that, I’d be unlikely to get consensus. But feel free to hammer away on the ins and outs of EROEI in the comments.

What I want to do here is propose a simple method for estimating EREOI based on a life-cycle assessment of greenhouse gas emissions. This requires some assumptions, but is useful, I think, because LCA studies are readily available and widely cited, whereas explicit EREOIs via net energy analysis are harder to find and compare in a consistent way.

There have been many well-researched peer-reviewed studies looking at the life-cycle emissions of different energy technologies, expressed in terms of kilograms of CO2-e/MWh (commonly). For non-fossil fuel energy technologies, this is a useful benchmark for calculating EROEI, because their inputs mostly come from fossil fuels, yet they produce no CO2 when generating. So, let’s consider ‘clean energy’ EROEIs on this basis.

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TCASE 7: Scaling up Andasol 1 to baseload

Andasol 1 is Europe’s first parabolic trough solar thermal power station, which went online in Nov 2008. It is located on a high desert site in Granada, Spain, which enjoys a high level of direct insolation – an average of 2,136 kWh / m2 / year. The mirror field — turbine infrastructure can yield a peak electricity generation capacity of 49.9 MWe (20 MWe average, see below). It also has a thermal storage system using molten salt.

The purpose of this post is to consider how one might scale up an Andasol 1 type plant in order to meet a rated power demand for 8,000 hours per year — thereby giving it a capacity factor of ~90%, similar to a baseload coal or nuclear power stations. This is a first attempt to improve the comparisons first given in TCASE 4.

But first, let’s look at the technology and current numbers. Here’s a good summary of its main features:

The Andasol 1 storage system absorbs part of the heat produced in the solar field during the day. A turbine produces electricity using this heat during the night, or when the sky is overcast. This process almost doubles the number of operational hours at the solar thermal power plant per year, the company said.

The heat generated in the solar field will be stored in a molten mixture of 60% sodium nitrate and 40% potassium nitrate. Both substances are used in food production as preservatives and are also used as fertilizer. The storage tank consists of two, 14-meter high tanks with a diameter of 36 meters and a capacity of 28,500 tons of molten salt. During the pumping process from the cold to the hot tank, the molten salt absorbs additional heat at an outlet temperature of approximately 280°C, reaching a temperature of 380°C.

A fully loaded storage system can keep the turbine in operation for 7.5 hours, which means almost 24-hour operation of the power plant in during high sunshine periods.

More technical details, including some useful illustrations of the storage system, can be found here and here. In summary, the solar collectors for the existing plant add up to a total of 510,120 square metres (0.51 km2), consisting of 209,664 mirrors along 312 rows with a total length of 24 km, with 90 kilometres of absorption pipes. The total physical area occupied by the plant (after appropriate collector spacing, and allowing for the storage and turbine housing, etc.) is 1.95 km2.  The estimated energy yield is 178 GWh / year (I haven’t seen reports of actual performance data), at a capacity factor of 40.7%, and an average power yield of 10.4 W/m2. It will use 560 million litres/year of fresh water, mostly for cooling the steam circuit, drawn from local ground water (a plant using air cooling would have a lower efficiency and would have to be larger to compensate).  The lifespan of the plant is estimated to be 30 — 40 years.

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TCASE 6: Cooling water and thermal power plants

Heat engines require cooling, to turn heat energy into mechanical energy (and then, via a turbine-connected generator, to electrical energy). This is an unavoidable physical principle, and is typically exploited via the Carnot cycle. Usually, this cooling requirement uses water.

Why do I raise this point? Because it seems to be a source of much confusion (innocent and deliberate) amongst the energy illiterate, especially when mounted as an argument against nuclear energy generation (and, implicitly, as a reason for adopting renewable energy). For instance, Friends of the Earth have decried:

Nuclear power plants consume large amounts of water –35-65 million litres daily. Indeed nuclear power is the thirstiest of all energy sources. A December 2006 report by the Commonwealth Department of Parliamentary Services states: “Per megawatt existing nuclear power stations use and consume more water than power stations using other fuel sources. Depending on the cooling technology utilised, the water requirements for a nuclear power station can vary between 20 to 83 per cent more than for other power stations.” Global warming and water shortages are likely to exacerbate problems experienced by the nuclear power industry during heatwaves in recent years. Nuclear power plants in several countries, including France and the US, have had to operate at reduced capacity, or to shut down temporarily, because of reduced water supply or to avoid breaching regulations limiting the heat of expelled water.

So what’s the story? Are water limitations and discharge regulations destined to be a major limiting factor for nuclear power, especially for places that are experiences increasing water shortages, such as Australia? The short answer is no — this is classic FUD. For the longer answer, read on.

All thermal power plants, by definition, make use of heat engines with heat exchangers, and so require cooling (although this need can be reduced in various ways, as explained below). This includes coal-fired, nuclear fission, oil-fired, conventional gas-fired, solar thermal and geothermal power stations. The renewable energy sources that don’t have this cooling requirement are hydropower, wind, wave, tidal and solar photovoltaic power.

Water is used in two ways in thermal power plants: (a) Internal steam cycle: to create steam via the energy source (fossil fuel combustion, fission chain reaction, heat exchange with deep rocks [hot dry rock geothermal] or a heat transfer fluid [concentrating solar power]) and convey it to an electricity-generating turbine, and (b) Cooling cycle: to cool and condense the after-turbine steam (this condensation dramatically decreases the volume of the expanded steam,creating a suction vacuum which draws it through the turbine blades), and then to discharge surplus heat to the environment.

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TCASE 5: Ocean power I – Pelamis

The first four posts of the TCASE series were logically sequential — each post built on the conclusions of the previous one. Overall, I hope the TCASE will retain a sense of coherency, but at the same time, I don’t want to get too constrained in following a rigid structure. To be frank, I can’t plan the ‘storyline arc’ well enough at this stage to make that even half feasible, and besides, I want to the series to be responsive to topical debates (and keep each post to a digestible, bite-sized chunk of information).

So future offerings in TCASE will branch out to cover everything from examinations of different technologies/energy sources, case studies of actual real-world projects, evaluation of new policy decisions (such as Australia’s 2020 ERET), questions of build rates and constraints, cost/feasibility assessments, consideration of technology gaps and physical limitations, exposing spin and hype, limit analyses, thought experiments, etc. I certainly hope to continue to get ideas from the commenters on this blog, which collectively represent an enormous wealth of knowledge, experience and ideas. To me, this is a fine form of peer review and a great source of inspiration. Thanks BNC readers!

Today’s post offers a first look at ocean power — the mighty fist of Poseidon (mythologically and in reality) — harnessing the energy in waves (I’ll look at tidal energy separately). Wave power is a form of indirect solar energy — driven by fairly consistent oceanic winds, which whip up waves over hundreds or thousands of km of open ocean. This energy may be harnessed with the use of buoys, oscillating air columns, barrages and so on, with a conversion efficiency of ~30%. Waves are a linear energy resource — once you’ve tapped its energy, you need thousands more km of ocean to regenerate new waves, so the resource is measured in kW per linear metre (not metre-squared, like direct solar). Average annual wave power density range from 10-40 kW per metre in inshore regions to as much as 70 kW/m in highly energetic regions. Although it is somewhat more regular (‘available’) than wind (and with a higher power density), wave energy is not constant and will still require substantial back-up and/or energy storage. More technical documents here.

Carnegie corporation, an Australian wave power company, state that their CETO technology (which I will look at in detail in another post — it has some fascinating prospects) can generate 100 MW peak using an a 500 buoy system; so, 200 kW peak per undersea buoy. To date, however, the only commercially operating wave farm in the world is in Aguçadoura, Portugal, about a year ago — so let’s focus first on the energy potential of this technology.

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TCASE 4: Energy system build rates and material inputs

In TCASE 3 – The energy demand equation to 2050, I concluded the following:

The world in 2050 will demand ~700 EJ of thermal energy, or roughly 300 EJ of electrical energy. This will require ~10,000 GWe (10 TWe) of generating capacity, which is a 5-fold increase in electricity generating capacity, or 680 MWe, every day, for the next 40 years (2010 to 2050).

Given the large uncertainties associated with this forecast, the actual value could easily be as high as 15 TWe, which would up the daily built-out rate to a little over 1 GWe per day. But let’s stick with 680 MWe rate for this post.

What would that mean in terms of today’s zero-carbon (when generating) energy sources? Consider three technologies that are potentially (i.e., theoretically) able to be scaled up sufficiently to do this job (wind, solar thermal and nuclear fission), and then look at the limit analysis (what would be needed for any one technology to do the whole job — accepting that in reality, there will always be some diversity of energy technologies that are deployed worldwide). I will, for simplicity, use US capacity factors for these energy sources (solar thermal from Spain), based on the latest (2008) data. We can assume the US situation would be reflective of global conditions if the technologies are properly deployed worldwide (with due expertise and siting considerations).

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1. Wind turbines. Wind power collects ~2 W/m2 (or 2 MWe per km2), and this figure is not really dependent on the turbine size. (If you have larger turbines, you need to space them further apart. If you build large turbines with tall towers, the increased hub height does access stronger winds, increasing the yield by ~30%). The 2008 US capacity factor for wind was 23.5%. For our unit, let’s choose a widely deployed turbine, the 2.5 MWe (peak), the GE 2.5xl (rotor diameter = 100 m, hub height = 75 – 100 m, cut-in windspeed of 3.5 m/s, peak at 12.5 m/s, cut-out at 25 m/s).

To get 680 MWe average power, 680/0.235  = 2900/2.5 =  1,160 GE 2.5xl turbines per day, worldwide, spread over 340 km2 of land area (a square 18.4 x 18.4 km). Based on the University of Sydney ISA report (p145), which also agrees with Prof Per Peterson’s figures, this will consume ~1,250,000 tonnes of concrete and 335,000 tonnes of steel per day. Every day, from 2010 to 2050. Adding 1 day’s energy storage using NaS batteries (to make it equivalent to the solar thermal example below), increases the mass of steel required to 455,000 tonnes per day (see chart at bottom of the post).

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TCASE 3: The energy demand equation to 2050

Updated 13/10/2009, based on post comments. Bottom line: 2050 power demand will be ~10 TWe of electrical generating power — a 5-fold increase on today’s levels, requiring the construction of ~680 MWe per day from 2010 to 2050.

Before we look in detail at the various low-carbon energy technologies that may provide the means to move away from fossil fuels, it is worthwhile considering what our future energy targets are likely to be. That is, what are plausible energy demand scenarios?

In the developed world (US, Europe, Japan, Australia and so on), we’ve enjoyed a high standard of living, linked to a readily available supply of cheap energy, based mostly on fossil fuels. Indeed, it can be argued that this has encouraged energy profligacy, and we really could be more efficient in the mileage we get out of our cars, the power usage of our fridges, lights and electrical appliances, and in the design of our buildings to reduce demands for heating and cooling. There is clearly room for improvement, and sensible energy efficiency measures should be actively pursued. More on that in later posts.

In the bigger, global picture, however, there is no realistic prospect that we can use less energy in the future. There are three obvious reasons for this.

1) Most of the world’s population – collectively, the developing world – is extremely energy poor. Over a third of all humanity, some 2.5 billion people, have no access to electricity whatsoever. For those that do, their long-term aspirations for energy growth, to achieve something equating that used today by the developed world, is a powerful motivation for development. For a nation like India, with over 1 billion people, that would mean a twenty-fold increase in per capita energy use.

2) As the oil runs out, we need to replace it if we are to keep our vehicles going. Oil is both a convenient energy carrier, and an energy source (we ‘mine’ it). In the future, we’ll have to create our new energy carriers, be they chemical batteries or oil-substitutes like methanol or hydrogen. On a grand scale, that’s going to take a lot of extra electrical energy! This counts for all countries.

3) With a growing human population (which we hope will stabilise by mid-century at less than 10 billion) and the burgeoning impacts of climate change and other forms of environmental damage, there will be escalating future demands for clean water (at least in part supplied artificially, through desalination and waste water treatment), more intensive agriculture which is not based on ongoing displacement of natural landscapes like rainforests, and perhaps, direct geo-engineering to cool the planet, which might be needed if global warming proceeds at the upper end of current forecasts.

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TCASE 2: Energy primer

Before getting entangled in the thorny bramble of sustainable energy options, I thought it helpful to arm you with a set of terminological secateurs. So TCASE #2 (recalling that TCASE = the Thinking Critically About Sustainable Energy series) is a brief primer and glossary on energy terms. This is not meant to be anything comprehensive, but it’s enough to get your technical feet wet and to understand some of the units and concepts that are liberally thrown around by those who are used to talking in the energy jargon. (If readers feel I have missed something important [no doubt], please feel free to add this to the comments, and I will also update this post to reflect the important suggestions.)

Anyway, first up, we need to understand the difference between power and energy. Let’s say you have a jug of water. It has some volume, which is the amount of water the jug holds. Now, let’s say you gradually tip out the water — the flow of water (the amount of water being poured per unit time) is a rate. Well, in caricature, the volume of water is like energy, and the flow of water is like power. Not a perfect analogy, but they never are…

Now, when measuring anything, you could use any manner of units. I’m going to consistently stick to SI (Système Internationale) units. If you want to translate back and forth (imperial, metric, nonsensic, etc.), look up the tables here. The basic SI unit of energy is the Joule. The basic unit of power is the Watt (W), which has units of Joules per second (J/s). So, a 60 W incandescent light globe uses up energy at a rate of 60 J/s, or 216,000 J per hour (60 x 3,600 = 216 kilojoules, kJ). Or, to express it another way, in one hour (h) that light would use up 60 Wh worth of energy, and in a day, it’d use 60 x 24 = 1,440 Wh, or 1.44 kWh. So, kWh are a unit of energy.

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Thinking critically about sustainable energy (TCASE) 1: Prologue

This is the first post in what is planned to be an extended series, ‘Thinking critically about sustainable energy‘ (henceforth TCASE #). As explained in my previous blog entry, A necessary interlude, this series will look in detail at the issues confronting renewable and nuclear energy, with an aim to break down the often complex and multifaceted critiques and promotions being made about various energy generation technologies into simpler, single-issue chunks, which can be more readily pinned down and understood.

I will also profile some of the less well-developed low-carbon technologies, such as tidal, wave, microalgae, and geothermal, as well as nuclear fusion, fusion-fission hybrids, travelling wave reactors etc. and speculate on their possible future roles. I hope in this way that I’ll be able to reinforce people’s understanding of why I no longer hold renewable energy to be a primary solution — and yet, by the same yardstick of maintaining intellectual honesty, acknowledging that I’ll also keep an open mind to unconsidered possibilities and caveats that are raised by commenters (be these against nuclear energy, and/or for renewables). Indeed, I’ll also discuss critically the social and technical impediments facing nuclear power adoption and the Generation III/IV synergy.

First up, a little history of the evolution of my thought on this topic, as documented my professional research and in the archives of this blog.

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