Electric Vehicles Research pdf
Electric vehicles – Scope and Future
Predictions on future of electric vehicles by sales percentage
% of EV's
➢
➢
➢
➢
Current market share of electric vehicles is 3% as of May 2020.
Electric vehicles will hit 10% of global passenger vehicle sales by 2025
Percentage of electric vehicle sales to increase to 28% by 2030
Percentage of electric vehicle sales to further increase to 58% 2040
80%
58%
60%
40%
20%
28%
3%
10%
0%
2020
2025
2040
% of EV's
Predictions on future of electric vehicles by vehicle segmentation
➢ Electric vehicles are predicted to represent 31% of all cars on road by
2040
➢ Electric vehicles are predicted to represent 67% of all municipal buses
on road by 2040
➢ Electric vehicles are predicted to represent 47% of all two-wheelers
(scooters, mopeds, motorcycles and so on) on road by 2040
➢ Electric vehicles are predicted to represent 24% of all light
commercial vehicles on road by 2040
2030
80%
70%
60%
50%
40%
30%
20%
10%
0%
69%
76%
67%
47%
31%
Cars
53%
33%
Muncipal
buses
EV's
24%
Two- Wheelers
ICE
EV- Electric Vehicle
ICE- Internal combustion engine
Light
Commercial
vehicles
Policies favoring electric vehicle adoption
✓ European Vehicle Carbon dioxide regulation
✓ China’s Electric vehicle credit system and fuel economy regulations
✓ India’s regulation to off-road all conventional internal combustion
engines by 2030
Reasons favoring electric vehicle
✓ No usage of fossil fuel, a resource which is depleting fast
✓ No requirement of internal combustion, hence no emission of carbon
dioxide and carbon mono oxide
✓ Environment friendly
✓ Economical, as there is no regular maintenance required
✓ Possibility of easy self charge with the advent of better photo voltaic cells
Do BEVs truly offer an environmental
advantage with respect to global warming
potential and secondary environmental
impacts – and if so, at what cost?
A rigorous quantitative analysis, excluding any government incentives or subsidies, to evaluate the true
cost and environmental implications of BEVs was conducted.
From R&D and manufacture, including raw material procurement, to ownership and end-of-life
disposal, our study covers every aspect of the vehicle's lifecycle.
For BEVs (Battery Electric Vehicle/s) and ICEVs (Internal Combustion Engine Vehicle/s), we developed models
to assess 2015 Total Cost of Ownership (TCO), Global Warming Potential (GWP), and Secondary Environmental
Impacts (e.g., Human Toxicity Potential described as Disability Adjusted Life Years lost).
To begin with, the electricity cost of operating a BEV over a one-mile trip is much lower than the gasoline cost
of operating a comparable ICEV over the same distance.
Second, due to the relative elegance and simplicity of a battery-electric motor system vs the periodic
maintenance necessary for functioning of an internal combustion engine, BEVs are less expensive to operate.
Third, automobile battery technology has advanced fast since the current generation of BEVs hit the market,
with lithium-ion battery packs dropping in price per kilowatt-hour (kWh) from $1,126 in 2010 to just $300 in
2015.
While most of the environmental impacts generated by ICEV’s are localized to combustion of gasoline in the vehicle
engine. Manufacturing process for BEV’s generate a much more dispersed and damaging set of environmental
impacts. In particular, the usage of heavy metals in the manufacture of lithium-ion battery pack. Compounded with
the pollution generated by the coal power plant for charging the batteries is approximately 3 times the amount of
human toxicity.
Green house gases emission comparison over a
20-year life cycle
Days of life impact (Death or disability for a ICEV
versus BEV over a 20-year ownership lifecycle
Total cost of ownership comparison between ICEV and an equivalent BEV
Total of Ownership for a BEV is significantly higher that of an equivalent ICEV. Ultimately the cost barrier has impacted
wider adoption of the BEV’s
Total cost of ownership over a 20-year
lifetime of ICEV v/s an equivalent BEV
In Thousands of Dollars
Total cost of ownership over a 20-year
lifetime of compact ICEV v/s an
equivalent BEV
In Thousands of Dollars
Total cost of ownership over a 20-year
lifetime of mid size ICEV v/s an
equivalent BEV
In Thousands of Dollars
Environmental Assessment: Global Warming Potential
Tailpipes emissions from gasoline combustion in an internal combustion engine combined with upstream emissions
associated with gasoline production and distribution contribute the majority of greenhouse gas emission from ICEV.
BEV’s on the other hand do not produce any tailpipe emission, however the BEV’s rely on the powerplants and grid.
Furthermore, BEV’s batteries require different inputs such as heavy metal mining and purification, battery cell
manufacture which involves organic solvents and various chemical processes.
GWP Emissions from Battery Manufacturing
In Kg of CO2 emissions per Kg of Battery Weight
Emissions over a 20-year lifetime for a
ICEV versus an equivalent BEV
In pounds of CO2 emissions
GWP emissions from a compact ICEV v/s
equivalent BEV at different stages of
vehicle life
GWP emissions from a mid size ICEV
v/s equivalent BEV at different stages
of vehicle life
In pounds of CO2 emission
In pounds of CO2 emission
Environmental Assessment: Secondary Environmental Impact
In addition to global warming potential, there are other multiple environmental
impacts which arise out of ICEV and BEV operations. There is direct impact on
human, terrestrial, aquatic life and depletion of natural resources.
❖ Human toxicity potential (HTP) is a calculated index that reflects the potential
harm to humans from a unit of chemical released into the environment
❖ Fresh water toxicity potential (FTP) is a calculated index that reflects the
potential harm to freshwater organisms from a unit of chemical released into
the environment.
❖ Terrestrial toxicity potential (TTP) is calculated index that reflects the
potential harm to terrestrial organism from a unit of chemical released into
the environment
❖ Mineral depletion potential (MDP) is a measure of consumption of natural
resources especially those which are mined (expressed in grams of ironequivalent)
❖ Fossil fuel depletion potential (FFDP) is a measure of consumption of fossil
fuel (expressed in grams of oil equivalent)
We have found that over a 20-year vehicle lifetime of BEV generated enough
toxicity potential to impact human health by 20 days loss of life or disability.
Days of life impact (death or disability) for
a compact passenger ICEV v/s an
equivalent BEV over 20 years of
ownership
Technology forecast: BEVs and ICEV’s for 2025
Given that BEV technology is still in the nascent stage, many of the factors presented above are going to change over a
period of time.
❑ If the cost per Kwh and environmental impacts of lithium-ion batteries decline, that would radically alter the
scenario for BEV’s
❑ Since the launch of BEV’s cost of batteries have declined by 70%
❑ Projections are that cost per Kwh of lithium-ion battery packs would be further reduced by 60% until 2025.
❑ Range of BEV’s would improve over a period of time further reducing the requirement of ICEV’s
❑ Despite the significant technological advancements in BEV’s, total cost of ownership advantage would be still
retained by ICEV’s for compact vehicles by 12% and for mid-sized vehicle ICEV’s would still hold advantage of 20%
❑ However, regarding GWP the advantage would be in favor of BEV’s by 27% for a compact vehicle and by 23% for a
mid-sized vehicle, over an ICEV
❑ Compact BEV would generate approximately 1700 more pounds of CO2 equivalents than the comparable ICEV by
2025, whereas a mid-sized BEV would generate approximately 4600 more pounds of CO2 equivalents than the
comparable ICEV
Total cost of ownership (TCO) over a 20year lifetime for a compact ICEV and an
equivalent BEV (2015 v/s 2025)
Total cost of ownership (TCO) in
thousands of dollars over a 20-year
lifetime for a 2025 Compact passenger
ICEV v/s and equivalent BEV
Emissions of CO2 from a compact
passenger ICEV compared to an
equivalent BEV (2015 v/s 2025)
GWP emissions from a 2025 compact
passenger v/s and equivalent BEV at
different stages of Vehicle life
Conclusion
Ultimately, improvements in technology come with a cost – and whether it is paid in dollars, green house gas
emission or human health impacts, BEV’s and ICEV’s both present a complex set of economic and environmental
trade-offs.
Advancement in one of the areas are unavoidably connected to impact others.
As the technologies for BEV’s and ICEV’s continue to evolve – TCO, GWP, and secondary environmental impacts will
all shift to some degree. While the 44% TCO differential favors compact ICEV’s over BEV’s in the current scenario,
that variance declines to only 10% in 2025.
23% GWP variance favors the compact BEV’s over ICEV’s currently, will increase to 27% by 2025
HTP generated by BEV’s will increase by more than half in 2025, representing the trade-off between greenhouse gas
emissions and human health impacts.
Impact
Vehicle type
Currently
2025
2025 v/s
current
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