Input-Output LCA Flashcards

1
Q

What kind of method is Input-Output-Method?

A

A quantitative economic technique that represents the interdependencies between different sectors of a national economy or different regional economies.

–> purely economic analysis

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2
Q

Could you explain the Leontief inverse?

A

x=(I-A)^-1 *y => (I-A)^-1 is the leontief inverse

I: Identity matrix -> a sector produces 1 unit of its output
A: Input-Output Matrix -> a sector needs these amounts of input

=> describes interrerlations of economic sectors in economy -> in LCA it describes the upstream chain

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3
Q

Input-Output Table

A

Show in monetary units how production and consumption activities are interrelated in an economy

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4
Q

Input-Output Matrix

A

What is needed to produce what?

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5
Q

Production level

A

𝑋=(𝐼−𝐴)^−1∙𝑌

```
I: Identity Matrix
A: Input Output Matrix
Efficiency Matrix
X: Production level
Y: Demand
~~~

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6
Q

What is the output level x of industry sectors for a given final demand y?

A

x=(I-A)^->*y

I: Identity matrix: a sector produces 1 unit of its output
A: Input-Output matrix: a sector needs these amounts of input

(I-A)^-1= Leontief inverse

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7
Q

Leontief inverse

A

describes the interrelations of economics sectors in the economy

in LCA language: it describes the upstream chain

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8
Q

IO Tables - examples

A

•Multiregional Input Output table (MRIO) covering a number of nations or
regions with a certain geographic resolution

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9
Q

What is the pollution level m for a given output level x of industry sectors?

A

m = B*x

m: total emissions
B: IO-Emission-Matrix

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10
Q

What is the pollution level m for a given final demand y?

A

m = B*(I − A)^-1 *y

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11
Q

Environmentally

extended IO Tables

A

•Databases using a country as a system boundary: e.g. simapro, which includes IO LCA based data, in addition to process based databases such as
Ecoinvent

•Databases using multiple countries as system boundary (MRIO): e.g. Global Trade Analysis Project (GTAP) and Externality Data and Input Output Tools for Policy Analysis (EXIOPOL, EXIOBASE)

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12
Q

Global Trade Analysis Project (GTAP)

A

• Developed by the Center for Global Trade Analysis, Purdue University
• Containing tables for 2004, 2007 and 2011 with complete bilateral trade
information, transport and protection linkages
• Comprising 140 countries and regions, including the ROW, each of which
consists of 57 endogenous sectors
•nThese tables are supplemented by satellite data on such issues as
– Energy consumption
– CO 2 emissions
– Land use

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13
Q

EXIOPOL ( Externality Data and Input Output Tools for Policy Analysis)

A

– EU research project during 2007 2011
– Consisting of 44 countries including the “rest of the world (ROW)“
– Sample data are provided free of charge, while the entire database is available on
purchase of a license.
– Extensive satellite data on environmental loads and resource use were used to
estimate
• 30 types of environmental load and
• 80 types of resource use for each sector

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14
Q

Limitations of IO-Tables

A

• Resolution of IO Tables:
– Environmentally Extended Input Output Tables show environmental impact per € in
a particular sector
• Problem:
– If e.g. sand and cement are mixed in the sector “construction materials” they will
have the same impact/€ –> difference in impact/kg only reflected via price

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15
Q

Hybrid LCA

A

• Combination of “normal” process LCA and IO LCA
• Start with process LCA; whenever no upstream data is available, use IO LCA to
fill the data gap

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16
Q

Differences between EE-IOA and LCA - time horizon

A

EE-IOA: one year of consumption and production

LCA: Life cycle of a product with possible inputs produced in former years and services needed in the future

17
Q

Differences between EE-IOA and LCA - reference units

A

EE-IOA: Monetary value of products

LCA: phsysical flows

18
Q

Differences between EE-IOA and LCA - investment goods

A

EE-IOA: Production only covered for reference year and not for past provision or future use. Provision of investment goods kept separately and not assigned to the production pattems.

LCA: Investment goods are depreciated over their full life cycle to the production volume in this time.

19
Q

Differences between EE-IOA and LCA - disposal services

A

EE-IOA: Only included in the reference years. Thus, falsification if stocks of goods are built up.

LCA: Included as far as possible, but future or past disposal assumed to be the same as today and thus possible developments are not considered.

20
Q

Differences between EE-IOA and LCA - system boundaries

A

EE-IOA: In principle all inputs and outputs are considered.

LCA: Cut-off criteria allow truncaton of inputs or outputs, wich are considered to have a minor contribution in the life cycle.

21
Q

Differences between EE-IOA and LCA - allocation principle

A

EE-IOA: Environmental impacts are allocated by the value of products provided by a certain sector. No subdivision giong deepeer than the sectors distinguished. –> economic allocation!

LCA: Different principles might be applied. Where possible, joint production processes are subdivided in order to allocate environmental impacts to single products.

22
Q

Differences between EE-IOA and LCA - sectors and products covered

A

EE-IOA: All economic sectors and thus all products are in principle investigated. …

LCA: Focus on products and services with environmental relevance and large production volumes. …

23
Q

Differences between EE-IOA and LCA - stock of goods

A

EE-IOA: Production of stocks of goods not sold in the particular time horizon is considered separately.

LCA: Change of stocks is not included in the assessment. It is assumed that products produced by a company enter the market immediately.