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This data book is a revision to the Material Flow
Data Book: World Resource Flows around Japan (CGER-D022-'99), published in
March 1999. The main changes from the 1999 edition are the addition of trade
data from 1998, the inclusion of this English translation of the main text, and
the inclusion of trade-flow maps and trade matrices on electronic media
(CD-ROM).
This
data book consists of Chapter I – Introduction; Chapter II – Method for Creating
Trade-flow Map/Trade Matrix; Chapter III – Trade-flow Maps; and the included CD-ROM.
Due to limitations of space, most of the trade-flow maps and trade matrices are
contained on the CD-ROM; a portion of the trade-flow maps are printed in
Chapter III.
The figures
contained in Chapter III and the CD-ROM are the core of the data book. These
figures contain data on the trade of major resources, extracted and tabulated
from UN Trade Statistics, and presented in map and table form. Chapter II gives
an overview of the method used to create the trade-flow maps and trade matrices
contained in this publication. This data book presents data on material flows
in terms of weight. In the UN Trade Statistics, however, sometimes only
monetary amounts are reported, and some countries use different units of
quantity measurement. Chapter II describes the statistical method used to
covert these values into units of weight. Chapter III contains a collection of
maps, and is put together in such a way as to allow an overview of the trade
flows of major resources between worldwide regional blocks. For some
commodities, a trade-flow map for trade among the Asian countries was added. In
addition to the trade-flow maps, the included CD-ROM also contains trade matrices.
This
chapter (Chapter I) contains some brief explanatory notes for interpreting the
figures in this data book. Section1.1 describes the purpose of this publication,
including the background of and need for the preparation of data on material
flows, as well as the involvement of the National Institute for Environmental
Studies in this issue. Section1.2 defines the significance of the import and
export of resources for Japan, and contains a figure and some brief explanatory
notes in order to get an overview of material flows in Japan. Section1.3
describes the characteristics of the resource trade-flow data contained in
Chapter III and the CD-ROM, focusing on the role of Japanese imports and
exports in the world and the recent changes in Asia.
Japan and the other industrialized nations take large
quantities of resources from the natural environment, and process them into a
wide variety of products. By consuming these products, our lives are made
richer and more convenient. Meanwhile, however, pollutants produced at the
production and consumption stages, and waste produced by consumed products,
returns to the environment. The scale of this cycle of material between people
and the environment far exceeds the environment’s capacity to regenerate its resources and
clean up our waste. Accumulation of carbon dioxide, CFCs, and other greenhouse
gases in the atmosphere is changing the global climate. Forested area is
shrinking as trees are harvested for fuel, building materials, paper and the
like. These are prime examples of how huge human-induced flows of materials are
changing the environment on the
global scale. At a local level, we are running out of space for landfills, and
the incinerators for reducing the quantity of waste encounter the environmental
pollution with dioxins. In other words, the majority of today’s environmental
issues are linked to our socio-economic system of mass production, mass
consumption, and mass disposal.
Perspectives are widening from the traditional focus
on pollution, toward more global environmental issues and sustainable
development. It has thus come to be realized how important it is to have a
quantitative measure of natural resources and the environment. The realization
that the quantity of available resources and the environment’s carrying capacity
are limited is one of the fundamental awarenesses for discussing sustainable development.
Chapter 4, “Changing Consumption Patterns” of Agenda 21, which was adopted at
the 1992 Earth Summit, points out that the current pattern of production and
consumption of the industrialized nations is not sustainable. More recently,
the Johannesburg Declaration made at the 2002 World Summit on Sustainable
Development (WSSD) stated the need to change our patterns of production and
consumption, and protect and manage our natural resources. In Japan, a Basic Environmental
Plan was formulated in 1994, based on the Basic Environment Law. This plan
calls into question the socio-economic activities and lifestyles of mass
production, mass consumption, and mass disposal, and declares the need to
change to sustainable production and consumption patterns, advocating a
heightened awareness of the dangers of pursuing material wealth alone.
Additionally, in 2000 the Basic Law for Establishing a Recycling-based Society
was established, with the goal of changing from the current economy fueled by
mass production, mass consumption, and mass disposal to a closed-loop economy.
Thus, today’s society and economy are characterized by
huge quantities of materials. In order to analyze the relationship between
society/the economy and environmental issues, it is necessary to systematically
track the flow of materials and energy between the natural environment and
economic activities, and among the various major economic sectors. Environmental
resource accounting, and Material Flow Accounting/Analysis (MFA) in particular,
is a powerful tool for accomplishing this goal. For more than 10 years, the National
Institute for Environmental Studies has researched environmental resource
accounting via the Global Environmental Research Fund. Japan depends on large
amounts of imports of natural resources, and is the world’s fourth-largest
emitter of greenhouse gases. For this reason, it is particularly vital for
Japan to reflect global issues in its environmental resource accounting, and we
have thus focused our efforts on preparing data to enable this. The data on the
trade of natural resources contained in this data book was created in this process.
Meanwhile, there is an active commitment to Material
Flow Accounting in Europe and other countries, and communication and joint
research is taking place on the international level. In November 1995, SCOPE
(Scientific Committee on Problems of the Environment), which was leading a
research project to develop indicators for measuring the achievement level of
sustainable development, held an expert workshop in Wuppertal, Germany. At the
workshop, it was concluded that Material Flow Analysis was one of the most
important fields of indicator development. The workshop spurred four of the
attending institutions to launch an international comparative research project
on material flows. These four institutions were Japan’s National Institute
for Environmental Studies, Germany’s Wuppertal Institute, the United States’ World Resources
Institute, and the Netherlands’ Ministry of Housing, Spatial Planning and
the Environment. 1996 was spent creating a common framework for analysis and
gathering data, and in April 1997, the four institutions jointly published
their results1). Then in the fall of 2000, the results of the second
period of research were published by 5 countries (Austria joined the group)2).
This international joint research project is based on
the Material Flow Accounting framework developed by the Wuppertal Institute.
The initial stage of the project focused on tracking the flow of resources from
the natural environment (the Ecosphere) to the sphere of human activity (the Anthroposphere),
by cross-sectioning the flow of resources at the boundary of these two spheres.
This was due to a focus on the issues of resource depletion and allocation, and
the consideration for the fact that all collected resources are potential
waste, and the association between resource flows in general and a host of
types of environmental impact.
The biggest feature of this framework is the focus on
“hidden
flows.” This refers to flows of materials that are not caught by conventional
means of tracking material flows, because although they are harvested by
people, they are not considered to be commodities. Taking mining as an example,
the quantity of soil and stone removed during the mining process, and
impurities removed when the ore is processed, is much larger than the quantity
of refined ore that actually enters the economy. For countries like Japan
depending on imports for the majority of their mineral resources, this type of
waste produced by the countries supplying the resources does not show up on any
table. This is a typical case of a “hidden flow.” It should be understood that more
resources are being consumed than the imports we actually see. Other examples
are the additional lumber
harvested for wood products, and the feed given to livestock. Note that the
term “hidden flow” is the English translation of the Wuppertal Institute’s (German) term “Ecological Rucksack”, which was accepted
by the international joint research project.
A similar concept has been incorporated into the
framework of the ecological footprint analysis3) advocated by
Wackernagel et al. An “ecological footprint” signifies the
imprint left on the earth by human activity, and is calculated as the area
required to supply resources and clean up pollution. This concept is an attempt
at measuring the size of the impact of human activities on the environment.
Large areas of land in the United States and other countries around the world
are used to produce the agricultural products that Japan imports, and the
ecological footprint is suited to expressing this situation.
The considerations used to select resource-trade data to incorporate in this data book include these hidden flows and the concept of the ecological footprint, as well as absolute quantities imported by Japan (e.g. fossil fuels and iron ore). This criteria applies to meats, grains, non-ferrous metals and the like.
The goal of this data book is to provide a reference
for thinking about resource-related environmental issues, recognizing Japan’s place in worldwide
resource trade. It therefore includes a large number of color maps based on the
collected data, in order to facilitate an intuitive understanding.
Additionally, the numerical data used to create these figures is also included,
in order to enable its use in model analysis incorporating trade data and other
research studies. Meanwhile, companies are starting to trace material
procurement as part of their Life-Cycle Assessments and other environmental
evaluations, and one issue in this is grasping the environmental impact of
natural resources procured abroad. We believe that this data book will be a
useful reference in this field as well.
Although the main focus of this data book is
facilitating the understanding of the place of Japanese imports in the world,
it is also essential to get an overall understanding of material flows inside
Japan, and the place of imported resources within these flows. Thus, we will
here summarize the data relating to material flows in Japan, and compare it
internationally.
Over the
past decade, there has been a call in Japan for the need to get a grasp of
material flows in the country as a whole, mainly from the point of view of
promoting recycling. Since the fiscal 1993 edition, the Japanese Environment
Agency’s Environmental White Paper has included calculations of the material
balance. The information in this publication is based on the data that the
authors prepared as part of the above-mentioned international joint research
project, and the Environmental White Paper has used the same calculation
methods since the fiscal 1997 version.
According to the fiscal 2002 edition of the Environmental
White Paper, a total of about 1,120 million tons of resources taken from the
natural environment in Japan that year. Adding to this the approximately 710 million
tons of imported resources, and the 70 million tons of imported products, a
total of about 1,900 million tons of new materials entered the Japanese economy
that year. By weight, about 40% of these new sources are imports. Adding to
these materials the flow of recycled resources, approximately 2,100 million
tons of materials passed through the Japanese economy.
Fig. I-1 shows the balance between materials input
into the Anthroposphere from the environment, and the materials output from the
Anthroposphere into the environment. On the output side, what is generally
tracked as “waste” includes about 50 million tons of municipal solid waste, and about 400
million tons of industrial waste. As industrial sludge, livestock manure, and
the like contain considerable amounts of water, the dry weight of this waste is
considerably lower. The input resources outweighs the output wastes. Some of
this remainder is returned to the environment in a form not normally considered
waste, and some remains stockpiled in the Anthroposphere.
Of the material flows that return to the Ecosphere
from the Anthroposphere in a form other than waste, the largest is the emission
of carbon dioxide into the atmosphere resulting from the combustion of fossil
fuels. Because carbon dioxide is emitted into the air in a gas state, it is
hard to get an intuitive sense of how much is being released. Performing this
type of calculation, however, shows that carbon dioxide, currently the focus of
much attention for its contribution to global warming, is actually humankind’s most weighty waste
product. In addition, the food that we eat, and the agricultural products fed
to livestock, are emitted into the Ecosphere by human and animal respiratory
and excretory systems, mainly as carbon dioxide and water. There are also
materials produced by humans whose use presupposes that they will be emitted
into the environment. These include fertilizers, agricultural chemicals, and
solvents for paints.
Thus, about 700 million tons of resources flow from
the Anthroposphere to the Ecosphere in a number of forms. Further, 110 million
tons enter the Anthropospheres of other countries as exports. Correcting the
balance of resource flows for water, the remaining approximately 1,200 million
tons remains in the Anthroposphere, adding to human stockpiles. Most of these
stockpiled resources take the form of buildings and other structures, i.e.
roads, bridges, dams, river embankments, waterworks, sewage systems, and other
public works (infrastructure), office buildings, houses, factories, and the
like. These stockpiles also include increased ownership of cars, appliances,
furniture and other durable consumer goods, stocks of plant equipment, and the
like. Most of these durable goods are disassembled and discarded after their
lifetime has ended, and so these increased stockpiles are actually latent
waste.
Fig.I-1 Material Balance in Japan (1995,
in millions of tons)
1.3 Overview of Global Resource
Trade Flows
This section provides an overview of the
characteristics of the trade of natural resources between the various regions
of the world, based on the worldwide trade-flow maps in Chapter III of this
publication and the included CD-ROM. Particular focus is placed on the role of
Japanese imports and exports in this flow. As this overview focuses on the flow
of resources between the world’s regional blocks, intra-block trade (e.g. trade
between European nations) does not appear on the maps. Information about
intra-block trade can be obtained from the trade matrices contained on the
CD-ROM. Additionally, the arrows from one regional block to another represent
the balance of trade; in most cases, resources are actually being traded in
both directions. This can also be confirmed in the trade matrices on the
CD-ROM. Note that the printing of historical trends was minimized, in order to
reduce the number of color-print pages. Trade-flow maps showing historical
trends of major commodities can also be found on the CD-ROM.
Note that this data book focuses on trade-flows of
resources taken from the Ecosphere, and materials with low levels of
processing. Data on machinery, chemicals, and other commodities with high
levels of processing have been excluded. Resources are exported from resource
producers to resource consumers with little or no processing, but are also
exported as highly processed products. Recently, exports of products have been
trending upward. Home appliances in particular were once mostly domestically
manufactured, but in recent years, an increasing number of them are being
imported.
For this
reason, it is necessary to take note of the hidden resource consumption behind
trade of highly processed products, in order to accurately ascertain resource
consumption. This topic, however, will be left for a future opportunity.
Figs. 1-A to 1-D show trends in worldwide trade of
the following three main types of resource from 1983 to 1998: fossil fuels,
biomass (agricultural, forestry, and marine resources), and base metals. Of
these, the largest flow in terms of quantity is fossil fuels. The flow of
exports from the oil-producing countries of western Asia to Japan and Europe is
particularly notable. Other noticeable trends are the increase of imports to
other Asian countries besides Japan (fossil fuels and metals), and the increase
of exports (metals) from South America.
Figs. 2-A to 2-D show flows of biomass broken down
into food and wood resources, and flows of base metals broken down into ferrous
and non-ferrous metals, excluding fossil fuels, which dominate the figures
above. These figures show that North America is a major source of non-fossil
fuel resources. Additionally, the southern hemisphere – e.g. Australia, South
America, and Africa – is a major supplier of base metals. Japan, along with
Europe, is shown to be a clear net importer of resources. The figures also
point to an increase of imports of base metals into Asia in recent years. This
is to be discussed in (4), below.
Figs. 3 to 8 show the flow of food resources. Figs. 3
and 4 show trade in meats, classified into beef, chicken, pork, mutton, and
other. Although Japan’s imports make up a rather small
proportion of worldwide trade in food commodities, this amount has been growing
in recent years. Trade on a worldwide level is on the rise. Although Europe and
North America do import some foods, they stand out as overall suppliers. Figs.
5 and 6 show trade in fish and shellfish. Japan’s imports make up a large part of total
trade, and the levels of imports are growing rapidly. Additionally, other Asian
countries besides Japan are also becoming more involved in trade in this area. Figs.
7 and 8 show trade in grains, classified into wheat, maze, rice, barley, and
other. It is clear from the data that North America is a major exporter to
other regions worldwide. Although Japan is also an importer, since the flow to
other regions is also large, its relative contribution to total trade in this
area is small.
Fig. 9 shows trade of wood resources, classified into
roundwood, sawnwood, wood manufactures, pulpwood (e.g. woodchips), pulp, and
paper. Japan imports wood in many forms from North America, Southeast Asia,
Australia, the former Soviet Union, and other countries. Thus, its wood imports
make up a fairly large proportion of total world trade. In addition to Japan,
Europe is also a major importer of wood resources, and although not shown in
the figure, there is also a great deal of trade within Western Europe. In
recent years, Asian countries other than Japan have been increasing their
imports of pulp and paper from North America.
Figs. 10A-D show historical trends in the Asian
region. In Southeast Asia, Malaysia and Indonesia stand out for their export
levels. Additionally, while in the past most exports were in the form of
roundwood, recently levels of such processed products as sawnwood and plywood,
pulp, and paper have been rising, and this also applies to imports to Japan
from these countries. In addition to Japan, the growth of imports to Korea and
China has been striking.
Figs. 11 to 16 show the flow of metal resources. Firstly,
Fig. 11 shows trade of iron ore, steel, and scrap iron. Australia and South
America are major exporters of iron ore, while Japan and Western Europe are
major importers. In recent years, imports to Asian countries other than Japan
have also been rising. Japan and Western Europe are major exporters of steel;
imports of iron ore to these regions are being exported as steel. Another
notable trend has been the increase of steel exports to countries in the Asian
region other than Japan, and this region also imports scrap iron from North
America and Western Europe.
Fig. 12 shows a detailed view of the Asian region. As
can be seen in the figure, India and the Philippines are also producers of iron
ore, and export to Japan and Korea. Steel exports from Japan reach many Asian
nations. In recent years, imports of iron ore and scrap iron to Korea have been
on the rise, and as a result, Korea has begun to export steel to Japan and
China. Additionally, imports of iron ore and steel to China are surging, and
its trading partners are numerous. As mentioned at the beginning of this
section, it must also be noted that steel travels the world in many processed
forms, i.e. as industrial machinery, automobiles, ships, and other
transportation machines, and other products.
Fig. 13 shows trade of aluminum ore (bauxite),
alumina, and aluminum (including refined aluminum). Australia, South America,
and Africa are major producers of bauxite, and export bauxite and alumina to
consumption/processing centers in Japan, Western Europe, North America, and the
like. As typified by exports from Australia to Japan, however, in recent years
more exports have been in the form of refined metal aluminum from the producing
country. In the case of Japan, the large amount of electric power required to
refine aluminum is prohibitively expensive in Japan, leading to this shift in
trade pattern.
Fig. 14 shows trade in base metals other than iron
and aluminum. Trade is classified and tabulated in terms of ore, and refined
metal. As with iron and aluminum, Australia, South America, and Africa are
producers of this category, and are major exporters as well. Additionally,
Japan and Western Europe are net importers? in this case as well.
Fig. 15 shows trade in base-metal ore, classified as
copper, nickel, zinc, lead, and others. Imports of copper and nickel ore to
Japan make up a large proportion of worldwide trade. Europe is also a major
importer of zinc and other ores. Although Asian countries besides Japan export
copper and nickel ore to Japan, in recent years their imports from other
regions have been on the rise.
Fig. 16 shows a breakdown of trade in the refined
versions of these metals. In terms of producers, South America and Africa are
major exporters of copper, while Australia is a major exporter of lead and
zinc. In recent years, exports from the former Soviet Union are also being
seen. Although Japan imports refined copper from a number of regions, it is an
exporter of copper to the Asian region. Aside from copper, imports of the
refined versions of these metals to Japan are small, showing that unlike the
example of aluminum, above, these metals are being refined domestically. There
is a similar trend between Western Europe and Japan, in that Western Europe is
a large importer of these metals, and also an exporter to the Asian region. The
Asian region other than Japan is characterized by importing from around the
world.
Fig. 17
shows trade in fossil fuels, broken down into coal, petroleum (both crude oil
and petroleum products), and natural gas. As is well known, Western Asia is a
major exporter of petroleum. Other exporters include the former Soviet Union,
South America, and Africa. Coal exporters include Australia, North America, and
Eastern Europe, while Japan and Western Europe are importers. As natural gas
cannot be transported without a pipeline or liquefaction plant, trade is limited
to countries with these facilities. Japan imports liquid natural gas from
Indonesia and other countries.
1)
Adriaanse,
A., Bringezu, S., Hammond, A., Moriguchi, Y., Rodenburg, E., Rogich, D., &
Schuetz, H. (1997): Resource Flows - Material Basis for Industrial Economies -,
joint publication by World Resources Institute, Wuppertal Institute, Dutch
Ministry of Housing, Spatial Planning and Environment, and National Institute
for Environmental Studies, World Resources Institute, 66pp.
2)
Matthews E.,
Amann, C., Bringezu, S., Fischer-Kowalski, M., Huettler, W., Kleijn, R.,
Moriguchi, Y., Ottke, C., Rodenburg, E., Rogich, D., Shandl, H., Schuetz, H.,
van der Voet, E., and Weisz, H. (2000), The Weight of Nations –Material
outflows from industrial Economies-, World Resources Institute, Washington
D.C., 125pp
3)
Wackernagel, M. & Rees, W. (1995): Our Ecological Footprint, New Society
Publishers, 160pp.
Global Environmental Research Fund
Fiscal 1991 Feasibility
study on establishing environmental accounting system
Fiscal 1992 – 1994 Establishment
of environmental and natural resource accounting system
Fiscal 1998 – 2000 Studies
on integrated environmental economic analysis towards a sustainable global
society
[Publications and
presentations in English]
Adriaanse, A., Bringezu, S., Hammond, A.,
Moriguchi, Y., Rodenburg, E., Rogich, D., and Schuetz, H.(1997), Resource
Flows: The Material Basis of Industrial Economies, World Resources Institute,
Washington D.C., 66pp.
Moriguchi, Y. (1997) Environmental
Accounting in Physical Term in Japan –Preliminary Material Flow Accounts and
Trade-Related Issues, Proc. ConAccount workshop, 21-23 January 1997, Wuppertal
Special 4, 166-172.
Moriguchi, Y. (1997) Material Flow
Indicators for the Japanese Basic Environmental Plan, Proc. ConAccount
Conference, 11-12 Sempember 1997, Wuppertal Special 6, 108-114.
Moriguchi, Y. (1999) Recycling and waste
management from the viewpoint of material flow accounting, Journal of Material
Cycles and Waste Management, 1(1), 2-9.
Matthews
E., Amann, C., Bringezu, S., Fischer-Kowalski, M., Huettler, W., Kleijn, R.,
Moriguchi, Y., Ottke, C., Rodenburg, E., Rogich, D., Shandl, H., Schuetz, H.,
van der Voet, E., and Weisz, H. (2000) The weight of nations –Material outflows
from industrial Economies-, World Resources Institute, Washington D.C., 125pp
Moriguchi,Y. (2001) Rapid Socio-Economic
Transition and Material Flows in Japan, Population and Environment, 23(1),
105-115.
Moriguchi, Y. (2001), Lessons from
Japanese MFA, Inaugural meeting of International Society for Industrial
Ecology, Nordwijkerhout.
Moriguchi, Y. (2001) Material Flow Accounting as a Tool for
Industrial Ecology, EcoDesign 2001: Second International Symposium on
Environmentally Conscious Design and Inverse Manufacturing, Tokyo, 880-885.
Moriguchi, Y.(2002) Material flow analysis
and industrial ecology studies in Japan, in A Handbook of Industrial Ecology
(R..Ayres and L. Ayres ed.), Edward Elgar, 680pp., 301-310.
Bringezu, S. & Moriguchi, Y. (2002)
Material flow analysis, in A Handbook of Industrial Ecology (R..Ayres and L.
Ayres ed.), Edward Elgar, 680pp. 79-90.
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