Plastics - Environmental aspects
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The main problem is, that parts of the plastics production can be counted
as crude oil use, partly they are not. And there are also important
differences between different types of plastics.
The parts which are oil related are the amount of directly oil related raw
materials, and the energy use directly involved in distilling the fractions
of crude oil or used for cracking of these fractions into plastics raw
materials, like ethylene and propylene. In most (but not all!) cases this
energy is based on crude oil wastes.
Also for the manufacturing of petrol, the energy used to distill crude oil
and for reformers/crackers to make high grade petrol is mainly based on
crude oil/cracking wastes, and should be added to the total crude oil
consumption of petrol.
The same applies for electricity used inside the refineries and - if
integrated - the heat/electricity use of polymerisation units for the
plastics involved.
The parts which are not directly oil related are parts of the raw
materials: chlorine from salt for PVC and oxygen from air for PET and PC.
Other energy related sources CAN be oil products, but also electricity,
natural gas and (brown)coal for heating and gas-, (brown)coal-, nuclear-,
solar-, hydro- or windenergy for electricity generation. That makes a lot
of difference.
We have tried to give an impression of the minimum and maximum directly oil
related energy use for different plastics. "Oil" being the used oil
derivatives as raw materials and the minimal direct oil related energy use
to derive these raw materials.
energy use in MJ/kg
material Total "oil" "others"
PVC 53 24 29
PE 70 55 15
PP 73 58 15
PS 80 55 25
PET 84 31 53
PC 107 36 71
Source for total energy use: Environmentaly friendly packaging in the
future, 1991, Stichting Milieudefensie (Environmental Defense Group) of The
Netherlands.
Source of "oil"/"others" partition: own interpretation, based on oil
related material content and direct oil related energy use.
These figures inlude the average energy efficiency of mixed electricity
generation in Europe (ca. 40%). If more low-efficiency electricity is used
(e.g. nuclear - 31%), the "others" figures will be higher, if
high-efficiency electricity is used (e.g. cogeneration - appr. 90%,
hydropower - 87%), they will be lower.
With a 90% efficiency at the source and 8% energy use, 1 l of petrol (0.76
kg) needs appr. 0.9 kg of crude oil, with 1 kg crude oil counted for 44
MJ/kg. This gives a plastics to petrol ratio in kg/l:
material min max
PVC 0.75 1.65
PE 0.57 0.72
PP 0.54 0.68
PS 0.50 0.72
PET 0.47 1.28
PC 0.37 1.10
Minimum is when all "others" are counted as oil based. Maximum when all
"others" are not oil based.
PVC and PC in reality will be more to the maximum side, because of
relatively high electricity consumption, mainly not produced from oil, and
low oil base as feedstock. For PE, PP and PS the balance is more toward the
minimum, because they are more oil dependent. PET is somewhere in between.
But this depends very strongly on the (inter) national or local and
sometimes on site electricity production.
In the literature, the amount of "crude oil" used to make PE varies between
1.55 and 1.95 kg/kg. That is comparable with the preceding
estimates.
We have no energy figures for other plastics, but if known and if the
balance of oil/non-oil components is known, the ratio can be calculated in
the same way.
Some remarks to end:
Plastics manufacturing in the world counts for appr. 4% of crude oil use.
If crude oil was only used to make plastics, it would be an abundant
material.
At the end of their usefull life, plastics can be burned and can give a
part of the energy back, mainly depending on their carbon content.
Glossary:
PVC: Polyvinylchloride
PE: Polyethylene
PP: Polypropylene
PS: Polystyrene
PET: Polyethyleneterephtalate
PC: Polycarbonate
Ferdinand Engelbeen
Chairman Chlorophiles
Ferdinand.Engelbeen@ping.be
http://www.ping.be/~ping5859/
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