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Solar power tops the list of renewable
energies in the world, both in installed capacity and rate of growth. Solar
photovoltaic – generating electricity from sunlight – has been growing the
fastest, driven by technological advances that bring prices down, as much as by
government policies such as feed-in tariffs  (World Reached
25 % Renewable Energy Capacity, SiS 49). But
how green is solar energy? A particular worry is the toxicities of metals such
as cadmium that goes into the new thin film PVs.
The Silicon Valley Toxics
Coalition based in San Jose California in the United States carried out a survey
early in 2010 comparing environmental health and safety practices, recycling
policies and sustainability among 14 major solar panel manufacturers that
represent about a quarter of the global solar panels market share [2, 3].
German companies scored the highest overall: Calyxo, Solarworld and Sovello;
Yingli in China came fourth. US-based First Solar and Abound Solar followed. There
was no response from several major manufacturers including Sharp, Miasolé, Best
Solar and Solyndra.
The survey also found that:
Half the companies surveyed supported mandatory
take-back and recycling at the end of the solar panels; life, but many need to
start setting aside money for the programmes
About two-thirds of the companies surveyed
failed to perform life-cycle analysis of their products
The risk of chemicals used during solar panel
manufacture is not assessed by the majority of responding manufacturers
It is important
to perform life-cycle analysis as well as environmental and health impacts of
renewable energy options, and end of life recycling should be mandatory,
especially for toxic components, such as cadmium or cadmium telluride.
Life cycle analysis
Researchers led by Vasilis Fthenakis at
Columbia University, New York, in the United States, have been carrying out
life-cycle analysis of solar panels ( Solar Power
Getting Cleaner Fast, SiS 39). In the most recent comprehensive
update, the analysis start from raw material
acquisition, through material processing, manufacturing, use, decommissioning,
treatment/disposal and recycling, if any, accounting for the material and
energy inputs, and waste effluents to air, water or ground .
material and energy inputs and outputs during life cycles of silicon photovoltaics
(Si PVs) and thin-film cadmium telluride (CdTe) PVs were investigated in detail
based on actual measurements from PV production plants between 2004 and 2006.
They used the most up-to-date data from researchers on life-cycle
inventory (LCI) for producing crystalline silicon modules in Western Europe
under the framework of the Crystal Clear, a large
European Integrated Project focusing on crystalline
silicon technology, co-funded by the European Commission and the participating
countries. The LCI data for CdTe thin-film technology were taken from the
production data of First Solar’s plant in Perrysburg, Ohio, United States.
The typical thickness of multi- and mono-Si PV is 270–300 mm, and that of
ribbon-Si is 300–330 mm; 72 individual cells of 156 cm2 (125 cm x 125 cm)
comprise a module of
for all Si-PV types. The conversion efficiency of ribbon-, multi-, and mono-Si
module is 11.5, 13.2, and 14.0 percent, respectively. As of 2006, First Solar’s
25-MWp plant manufactures frameless, double-glass, CdTe modules of 1.2 m by 0.6
m rated at 9 percent efficiency with ~3mm thick active layer, a
hundredth the thickness of the silicon PVs.
important part of the solar panel installation that has not been considered in
previous life-cycle analysis is the ‘balance of system’ (BOS), all components
other than the PV panels needed for supporting the panels and for their
modules require an aluminium frame of 3.8 kg/m2 for mounting, while
a glass backing performs the same functions for the CdTe PV. For rooftop PV,
the BOS typically includes inverters, mounting structures, cable and
connectors. Large-scale ground-mounted PVs require
additional equipment and facilities, such as grid connections, office
facilities, and concrete. The mass of this was 9 to 10 times the panels for a
3.5 MW installation in Springville, AZ.
payback time and greenhouse emissions
The most frequently
measured life-cycle metrics of PV system environmental analyses are the energy
payback time (EPBT) and the greenhouse-gas (GHG) emissions. EPBT is the period
required for a renewable energy system to generate the same amount of energy
that we used to produce the system itself. Calculating the primary energy
equivalent requires knowledge of the country-specific fuels, feedstock and
technologies used to generate energy.
The EPBTs are shown in Figure 1. As can be seen, CdTe PVs have the
lowest values by far, one year in Europe and slightly over one year in the US.
Figure 1 Energy payback time for different
The greenhouse-gas (GHG) emissions during the
lifecycle of a PV system are estimated as an equivalent of CO2 using
an integrated time period of 100 years; the major emissions included as GHG
emissions are CO2 (global warming potential, GWP =
1), CH4 (GWP = 23), N2O (GWP = 296), and chlorofluorocarbons
(GWP = 4600–10 600).
Figure 2 Greenhouse gas emissions for solar
PVs compared with some non-renewable sources
Again, CdTe PVs emissions at 24 g per kWH come
out ahead of silicon PVs at 37 gm per kWh. These are way below those of coal
natural gas and petroleum. I have omitted the GHG emissions of nuclear given in
the authors’ graph at 24 g, the same as CdTe PVs. This value was way below that
resulting from a detailed realistic analysis, which put nuclear GHG emissions
at between a minimum of 85 g and a maximum of 130 g per kWh ( The
Nuclear Black Hole, SiS 40).
Electricity and fuel use during the
PV materials and module production are the main sources of the GHG emissions
for PV lifecycles. Upstream
electricity-generation methods also play an important
role in determining the total GHG emissions. For
instance, the GHG emission factor of the average US electricity grid is 40 percent higher than that of the average Western European (UCTE), resulting
in higher GHG estimates for the US – produced modules. It is clear that improvements in material
and energy use and recycling will enhance the environmental profiles.
A recent, major improvement is a recycling
process for the sawing slurry, the cutting fluid that is used in the wafer
cutting. This recycling process recovers 80–90 percent of the silicon carbide
and polyethylene glycol that was previously wasted, and decreases the EPBTs of
these technologies by 10 percent.
Other waste gases were compared. Emissions of
NOx and SOx from CdTe PVs at 42 mg/kWh and 79 mg/kWh are about half of those of
the silicon modules.
Heavy metal emissions
metal emissions are a major concern during the extraction, manufacturing
process and during use.
Cadmium is a byproduct of zinc and lead, and is collected from
emissions and waste streams during the production of these major metals. The
largest fraction of cadmium, ~99.5 percent pure, is in the form of a sponge from
the electrolytic recovery of zinc. This sponge is transferred to
a cadmium-recovery facility, and further processed through oxidation and
leaching to generate a new electrolytic solution. After selectively precipitating
the major impurities, cadmium 99.99 percent pure is recovered by electro-winning.
It is further purified by vacuum distillation for CdTe PV manufacture.
While cadmium emissions can take place throughout the extraction
process, emissions during the lifespan of a finished CdTe module are negligible,
as it is encased in glass. The only way it could be released is if a fire broke
out. Experiments at Brookhaven National Laboratory that simulated real fire
conditions revealed that CdTe is effectively contained within the glass-to-glass
encapsulation during the fire, and only minute amounts (0.4–0.6 percent) of Cd
are released. The dissolution of Cd into the molten glass was confirmed by high-energy
synchrotron X-ray microscopy studies.
Coal and oil-fired power plants routinely
generate Cd during their operation, as it is a trace element in both fuels. According
to the US Electric Power Research Institute’s data, under the best/optimized operational and maintenance
conditions, burning coal for electricity releases between 2 and 7 g of Cd/GWh.
In addition, 140 g/GWh of Cd inevitably collects as fine dust in boilers,
baghouses, and electrostatic precipitators (ESPs).
The emissions of Cd from heavy-oil burning power
plants are 12–14 times higher than those from coal plants, even though heavy
oil contains much less Cd than coal (~0.1 ppm), because these plants do not
have particulate-control equipment. Cadmium emissions are also associated with
natural gas and nuclear-fuel life cycles because of the
energy used in fuel processing and material productions. Thus, displacing the conventional
energy sources with CdTe PV markedly lowers the amount of Cd released
into the air. Every GWh of electricity generated by CdTe PV modules saves
around 5 g of Cd air emissions if used instead of, or as a supplement to, the Western
Europe UCTE electricity grid.
The direct emissions of Cd during the life cycle of CdTe PV are 10
times lower than the indirect ones due to electricity and fuel use in the same
life cycle, and about 30 times less than those indirect emissions from
crystalline photovoltaics. The results are given in Figure 3.
Figure 3 Cadmium emissions of PVs and other conventional sources
The authors also examined the indirect heavy metal emissions in the
life cycle of the Si PVs and found that CdTe PVs has the fewest heavy metal
emissions among PVs; the emissions of arsenic, chromium, lead, mercury and
nickel are much less than the silicon modules.
PV system, the ‘Amonix high-concentrator PV’ (HCPV) consists of units called
MegaModules mounted on two-axis trackers. Each MegaModule is made up of 48
blocks of sub-module units rated at 3.8 kWp-AC each under 850 W/m2
of direct normal irradiance. A refractive concentration technology based on
acrylic Fresnel lenses achieves an effective concentration ratio of 250. A
piece of thin acrylic plate with 24 lenses 4 mm thick and antireflection
coated, is mounted on each submodule. A total of 1 152 single-junction,
single-crystal silicon cells, each 1.2 cm2 are mounted at the focal
points of a MegaModule (see Fig. 4). This AM-10TM single-crystal
solar cell operates at 26.5 percent efficiency. Arizona Public Service has
installed and tested several Amonix HCPV systems with capacities of around 500
kWp, the largest being the 168 kWp installed at their PV plant near Prescott, Arizona. The data for analysis were obtained from the 24 kW system in APS STAR
center in Phoenix.
Figure 4 The Amonix MegaModule and complete 24 kW systems in APS
STAR center in Phoenix, www.Ammonix.com
major components of the 5-MegaModule 24 kWp system includes frames, optics,
singlecrystal Si cells, heat sinks, tracker, foundation, hydraulic drive,
motor, controller, inverter, sensor, power meter, and anemometer (a gauge for
recording wind velocity). While the aperture area is 182 m2, the
total area of the concentrator is 230 m2 including the frame areas.
The trackers consist of a 5.5 m high pedestal, a torque tube and a hydraulic
drive with a controller. The concrete foundation used in the STAR test facility
in Phoenix, is 5.5 m deep and 1.2 m in diameter. Each 24 kWp MegaModule system
has a 30 kW Xantrex inverter and multiple MegaModules share one transformer.
The direct beam solar radiation is on average 2480 kWh/m2/year
in Phoenix, AZ. Performing with a 16 percent rated AC conversion efficiency, the
installation should ideally produce 72 MWh (2480 x 0.16 x 182 m2) a year under standard conditions of 25 ˚C ambient temperature 1 m/s wind
speed). However, it generated only 49.2 MWh in 2005, 30 percent less. Losses
were put down to soiling, alignment, shadows between units and other objects,
temperature, equipment failure.
1 gives the life cycle parameters of the concentrator utility compared with
ordinary PVs. As can be seen, the ordinary PVs, especially CdTe PVs outperform
the concentrator facility, the latter in both EPBT and CHG emissions. The CdTe
thin film PVs looks like the clear winner for now. It shows that distributed
small scale installations can work better than large utilities. And there is
certainly more room for improvement, such as recycling toxic materials and
better yet, finding non-toxic alternatives.
Life cycle parameters of concentrator PV and ordinary PVs
Todd Millions Comment left 23rd January 2011 11:11:45 I do like these system/lifecycle overveiws.While extracting alumium(for the frame),from ore for example-is very energy intense.Recycling scrap alumium is a very low power operation.
One choke point on these efforts in any solar power system is the durability of glass-Last I checked,the insurance industry half life for the worlds structural glass was-10years.Rather close to the payback period for PV and thermal instalations,when half of them will break in a decade on even odds.Since normal low iron glass can be anealled with molten salt too be almost as tough as normal grades of pesplex(nearly as flexible too boot),and since there are quantities of waste heat from the glass melt furnaces and the tin float of any modern glass plant too melt the salt-this can only be as the glass companies like it.A problem that goes back to the empour Tiberius,according too some sources.
Given that the proliferation of small arms and idiots has accelerated so much in recent times(now blimps and other airships,can't be operated over populated areas anywhere,because of the expense of patching and repurifing/ replacing the heliun-due too pin heads with guns perishing too see if they can blow them up.),These durability issues sould be addressed.
As they are solved already techincally,impimentation efforts should perhaps be directed elsewhere.Politically-spare me.Perhaps it would best further too bring the uncost/benifit ratio of better glass to the attention of Swiss Re.By ajusting their rates,both cosumers and the factories that produce the glass could be encouraged too do what they should have found out and demanded themselves-30 years ago.