1)
India
vs Australia Carbon Management
i)
Compare
and Contract of India vs Australia Carbon Management
The
following table represents the information regarding total annual scope 1 with
and without LULUCF for India and Australia. Although, the table also includes
information regarding per capita greenhouse emission in the selected countries.
|
India
|
Australia
|
Total
Annual Scope 1 without LULUCF
|
2008.67
|
5827.7
|
Total
Annual Scope 1 with LULUCF
|
1831.65
|
6586.7
|
Per
Capita Greenhouse Gas Emissions
|
1.58
|
0.4
GT (Ucsusa.org, 2018)
|
Scope
1 Emissions by Primary sector
|
1388307
|
125000
|
Scope
1 and 2 emissions by end use sector
|
Direct
GHG emission by federal, heat, steam.
500
kt
|
1536
MtCO2e
|
The above table represents the comparative analysis of
Australia and India regarding carbon emission and GHG emissions. Although,
scope 1 and scope 2 are analyzed in detail and projected in the table.
ii)
Sectoral
Analysis using IPCCs 5th Assessment working Group
In Australia and India, the energy emission and carbon
emission are different in ratios as recorded by the previous research studies
and reports by the government of each state. Each industry, for instance, the
transportation industry and agriculture have presented details regarding the
impact of emission on GDP. The following graph further represents the annual
change in GHG emissions from 1990 to 2014.
Figure 1 Sectoral Analysis of India from 1990 to 2014.
Additionally, another graph is projected below which covers
the latest information about various sectors of India and greenhouse gas
emissions. According to this graph, the percentage of greenhouse emission by
agriculture, energy, waste, and industrial processes are 19%, 69%, 57.7, and
9%.
Figure 2 Sectoral Analysis of India
The sectoral analysis of Australia with percentage and total
greenhouse gas emission are presented here. According to the latest reports published by
the government of Australia, the greenhouse gas emission in Australia was
following (see the presented below table) in different sectors such as
manufacturing and mining.
|
WA
|
VIC
|
NSW
|
QLD
|
Total
|
Industries & Sectors of Australia
|
|
|
|
|
|
Manufacturing Sector
|
14.6
|
6.1
|
14.7
|
12
|
52.1
|
Agriculture, forestry & fishing Sector
|
-3
|
7.4
|
7.3
|
40.4
|
74.4
|
Mining Sector
|
26.7
|
2.7
|
17.2
|
27.8
|
47.4
|
Electricity gas & water Sector
|
27.2
|
60.4
|
54.5
|
54
|
196.1
|
Residential Sector
|
8
|
21.2
|
18.9
|
13.3
|
27.4
|
Commercial services and construction
|
6.5
|
7.4
|
7.5
|
6
|
29.1
|
Transport and Storage Sector
|
6.5
|
6.1
|
8.8
|
7.7
|
61.4
|
Total
|
86.4
|
111.2
|
128.9
|
161.2
|
487.7
|
The following line
chart represents the comparative analysis of sector performance and records
toward greenhouse gas emission in 2017.
Although, the presented below pie chart is representing the
percentage values for each sector calculated by the information shared in IPPC
reports and other greenhouse gas emission reports of the Australian government.
iii)
Average
Abatement cost range by Sector
The average abatement
cost range by sector for implementing the measures in the IPCC’s report is
expected to be 44 percent of total abatement potential. The following figure
represents the cumulative abatement potential by grouping in Australia by 2020 (Publications.industry.gov.au, 2020).
URL: https://www.environment.gov.au/system/files/resources/b8540c8a-8a31-4aba-a8b5-63cc46466e33/files/modelling-and-analysis-australias-2030-abatement-opportunities.pdf
According to this figure, the government is planning to
invest in and promote low carbon transport. Moreover, another most recommended mitigation
plan for greenhouse gas emission and carbon is an improvement in agriculture by
advanced emissions farming practices in the country. The abatement for each
sector would be as following:
Measures for Implementation
|
Annual Abatement Cost
|
Smart Urban Design
and Low Carbon Precincts
|
4784
|
Digital infrastructure in the industries and projecting the
requirement of transport fuel
|
2267
|
High-performance low carbon energy generation and
distribution
|
7447.36
|
Low carbon transport
|
19233
|
Advanced commercial energy-efficient equipment
|
13311
|
Intelligent industrial and building
management
systems (BMS)
|
9165.8
|
Improve land management and low emissions farming practices
|
51180
|
Advanced industrial energy-efficient equipment and process improvement
|
17443
|
Total Abatement Cost
|
124831.16
|
Total
abatement cost for each measure is projected by the following graph. According
to this graph, the improvement of land will require the highest percentage of
the total federal budget. Somehow, the least amount required by the measure is 2267
which is about digital infrastructures and intelligent systems (Environment.gov.au, 2016).
2)
Sugar
Mills and Short-Run average marginal abatement Cost
To produce power a sugar mill burns 75kt of bagasse per year derived
from 250kt of sugar case input. The mill can choose from three sugar cane
varieties which have different costs and emission contribution. Using variety A
as a base case, the following histogram is plotted with the short-run average
marginal abatement cost and marginal abatement cost curve for the sugar mill. See
the following graph for sugar mills case.
Part: 2
3)
GHG
emissions reduction
iv)
NPV
and Long-run average Abatement Cost
The shire of
fabricated is a local government area in the north of Queensland. As a part of
the sustainability strategy, it is looking to reduce the greenhouse gas
emission from its activities. The table represents the NPV and long-run average
abatement cost.
NPV of Project 1
|
Year
|
Cash Inflows
|
Cash Outflows
|
Net Cash flow
|
Discount Factor
|
PV
|
Cumulative PV
|
1
|
750000
|
$10,000
|
$740,000
|
0.714286
|
$528,571.43
|
$528,571.43
|
2
|
750000
|
$10,000
|
$740,000
|
0.510204
|
$377,551.02
|
$906,122.45
|
3
|
750000
|
$10,000
|
$740,000
|
0.364431
|
$269,679.30
|
$1,175,801.75
|
4
|
750000
|
$10,000
|
$740,000
|
0.260308
|
$192,628.07
|
$1,368,429.82
|
5
|
750000
|
$10,000
|
$740,000
|
0.185934
|
$137,591.48
|
$1,506,021.30
|
6
|
750000
|
$10,000
|
$740,000
|
0.13281
|
$98,279.63
|
$1,604,300.93
|
7
|
750000
|
$10,000
|
$740,000
|
0.094865
|
$70,199.73
|
$1,674,500.66
|
The NPV analysis for the second project
NPV of Project 2
|
|
|
|
|
|
|
Year
|
Cash Inflows
|
Cash Outflows
|
Net Cash flow
|
Discount Factor
|
PV
|
Cumulative PV
|
1
|
152306
|
$10,000
|
$142,306
|
0.714286
|
$101,647.14
|
$101,647.14
|
2
|
152306
|
$10,000
|
$142,306
|
0.510204
|
$72,605.10
|
$174,252.24
|
3
|
152306
|
$10,000
|
$142,306
|
0.364431
|
$51,860.79
|
$226,113.03
|
4
|
152306
|
$10,000
|
$142,306
|
0.260308
|
$37,043.42
|
$263,156.45
|
5
|
152306
|
$10,000
|
$142,306
|
0.185934
|
$26,459.59
|
$289,616.04
|
6
|
152306
|
$10,000
|
$142,306
|
0.13281
|
$18,899.70
|
$308,515.74
|
7
|
152306
|
$10,000
|
$142,306
|
0.094865
|
$13,499.79
|
$322,015.53
|
Project: 3 option
NPV of Project 3
|
|
|
|
|
|
|
Year
|
Cash Inflows
|
Cash Outflows
|
Net Cash flow
|
Discount Factor
|
PV
|
Cumulative PV
|
1
|
2235000
|
$10,000
|
$2,225,000
|
0.714286
|
$1,589,285.71
|
$1,589,285.71
|
2
|
2235000
|
$10,000
|
$2,225,000
|
0.510204
|
$1,135,204.08
|
$2,724,489.80
|
3
|
2235000
|
$10,000
|
$2,225,000
|
0.364431
|
$810,860.06
|
$3,535,349.85
|
4
|
2235000
|
$10,000
|
$2,225,000
|
0.260308
|
$579,185.76
|
$4,114,535.61
|
5
|
2235000
|
$10,000
|
$2,225,000
|
0.185934
|
$413,704.11
|
$4,528,239.72
|
6
|
2235000
|
$10,000
|
$2,225,000
|
0.13281
|
$295,502.94
|
$4,823,742.66
|
7
|
2235000
|
$10,000
|
$2,225,000
|
0.094865
|
$211,073.53
|
$5,034,816.18
|
Project: 4 option
NPV of Project 4
|
|
|
|
|
|
|
Year
|
Cash Inflows
|
Cash Outflows
|
Net Cash flow
|
Discount Factor
|
PV
|
Cumulative PV
|
1
|
11500
|
$10,000
|
$1,500
|
0.714286
|
$1,071.43
|
$1,071.43
|
2
|
11500
|
$10,000
|
$1,500
|
0.510204
|
$765.31
|
$1,836.73
|
3
|
11500
|
$10,000
|
$1,500
|
0.364431
|
$546.65
|
$2,383.38
|
4
|
11500
|
$10,000
|
$1,500
|
0.260308
|
$390.46
|
$2,773.84
|
5
|
11500
|
$10,000
|
$1,500
|
0.185934
|
$278.90
|
$3,052.75
|
6
|
11500
|
$10,000
|
$1,500
|
0.13281
|
$199.22
|
$3,251.96
|
7
|
11500
|
$10,000
|
$1,500
|
0.094865
|
$142.30
|
$3,394.26
|
Project: 5 Option
NPV of Project 5
|
|
|
|
|
|
|
Year
|
Cash Inflows
|
Cash Outflows
|
Net Cash flow
|
Discount Factor
|
PV
|
Cumulative PV
|
1
|
10200
|
$10,000
|
$200
|
0.714286
|
$142.86
|
$142.86
|
2
|
10200
|
$10,000
|
$200
|
0.510204
|
$102.04
|
$244.90
|
3
|
10200
|
$10,000
|
$200
|
0.364431
|
$72.89
|
$317.78
|
4
|
10200
|
$10,000
|
$200
|
0.260308
|
$52.06
|
$369.85
|
5
|
10200
|
$10,000
|
$200
|
0.185934
|
$37.19
|
$407.03
|
6
|
10200
|
$10,000
|
$200
|
0.13281
|
$26.56
|
$433.59
|
7
|
10200
|
$10,000
|
$200
|
0.094865
|
$18.97
|
$452.57
|
Now calculating the abatement cost and
emission abated for the projects.
|
Emission Abatement
|
Long Run cost
|
Project 1
|
950000
|
6650000
|
Project 5
|
530250
|
3711750
|
v)
The
Marginal Abatement Cost and Curves
The marginal cost can
be calculated by finding the difference in the total cost of two or more than
two projects. Then, calculating the total difference in the output or revenue
generated by these projects. Now the next step is to divide the difference of cost
by the difference of output or revenue. Considering this the marginal cost
cannot be calculated if all projects have the same revenue amounts. Thus, the
marginal cost is calculated by changing the revenue stream.
|
Revenue
|
Cost
|
Project 1
|
100000
|
750000
|
Project 5
|
10000
|
10200
|
|
|
|
Marginal cost
|
8.22
|
|
4)
Potential
role of Carbon Capture and Storage
a)
Appropriate
Scale of Technology
b)
The
carbon capture and storage can generate a negative impact on our environment if
proper storage and inventory control measures are not taken by the responsible
authorities. According to the recent research studies and reports, carbon is
creating threats for our environmental safety and goals of zero pollution.
Carbon not only promote an unhealthy lifestyle but also increases pollution.
The technology has been trying to control these issues carbon-related issues in
our society. Following the research, it is already succeeded to reduce carbon
by spreading awareness in the society and industrial sectors to control the
generation of carbon after machine processing.
c)
Incentives
of India vs Australia Carbon Management
Carbon prices for each
activity are different. Somehow, at least millions of dollars are required to
pay for the carbon prices in our society.
In 2017, India set a budget of 1.4 billion for three charging infrastructures.
d)
Barriers
of India vs Australia Carbon Management
Some technical,
regulatory, environmental, and social barriers are drawing impact on carbon
control strategies and developmental plans (Carbonbrief.org, 2019).
Technical
|
Some
machines and equipment generating carbon cannot be replaced because of the
excessive cost of replacement.
|
Environmental
|
Some
companies are taking advantages of their environmental position therefore
they do not take interest in carbon control strategies.
|
Regulatory
|
Poor
implementation of laws and regulations.
|
Social
Barriers
|
In
many countries, illiterate people are not well aware of possible strategies
to control such issues.
|