ENERGY CONSIDERATIONS & BUILDING
MATERIALS - A Case Study For India
In India a very high component of energy is invested in the
manufacture of building materials and building components. While engineering
design efficiency in industrial products has been widely researched, work in
the area of energy utilization and life cycle accounting of energy costs in
building materials and buildings has been largely ignored. The worsening
energy crisis makes it imperative to analyze the energy content of the
material against parameters of renewability, efficiency of use and local
availability, as also its aggregated energy value.
Table
1: Demand, and energy demand in the building material sector |
Building Material |
Total Demand |
Total energy demand (billion kWh) |
Percentage |
|
|
|
Electrical |
Thermal |
Embodied |
Bricks
(million)
Cement (mt)
Lime (mt)
Timber (mt)
Aggregate (mt)
Sand (mt)
Boards
Particle board (msf)
Fibre board (msf) |
70,000
39.37
7.00
5.50
258
140
94.6
83.8
|
76.3
55.2
15.4
-
10.6
-
0.50
0.97 |
0
30
10
-
100
-
3
16 |
100
70
90
-
-
-
25
24 |
-
-
-
-
-
-
72
60 |
Total |
|
158.02 |
|
|
|
mt - million tonnes; msf=million
sqft |
Table (1) summarizes the building material demand and the
energy demand in India at current levels of technology. The total electricity
generated in 1990-91 was 264.6 billion k Who including thermal, hydro and
nuclear power. Coal alone provides 60 percent of the total energy consumption
in the building materials sector. (The aluminium industry relying heavily on
electricity, is excluded from this analysis). In the last one year rising
coal costs have resulted in a 14 percent price increase in the brick sector,
25 percent in the cement and 39 percent in fireclay products. The
construction sector in India, the single largest consumer of energy intensive
materials, like steel and cement accounts for a large share of the total
emissions. This results from inefficient combustion technology and very high
emission coefficient for coal. Improved technology is urgently needed in
areas related to basic raw material manufacture, conversion of fuel into
energy and in the utilization of energy.
Bricks are produced extensively in India in batches ranging
from 50,000 bricks in country clamps to 800,000 bricks in kilns. The fuel is
used in varying combinations: cow-dung cakes, agro-residues, coal and wood.
There are constant efforts at fuel substitution by business enterprises
through the use of non-wood based biomass like rice-husk, bagasse and mustard
stocks in place of wood. But these innovations focus only on direct cost
reductions, especially because conventional brickmaking thrives on low
operating costs and maximum return on investment. The Bulls-trench kiln with
a movable chimney consumes 17-18t of coal/100,000 bricks as against 13t for
the fixed chimney and only 12t for the high draught kiln. The use of high
draught kiln producing only 55 percent good quality bricks, is limited. The
movable chimney kiln offering low initial investments continues to be most
popular choice inspite of excessive fuel consumption. This widespread
indifference has lead to a stagnation of technology and wasteful use of fuel
leading to increased CO2 emissions.
Lime is another traditional material whose use as a
building material is being marginalised. Building lime, which forms 20
percent of the total lime output is the contaminated accounts for the other 80
percent catering primarily to the paper, textile and sugar industry. The
continuous vertical shaft kiln is the most commonly used technology which
offers a marginal improvement over the traditional rectangular batch process
kilns. The fuel consumption in the lime industry has remained static at 2.5t
of coal/t of lime fore the last decade. Moreover lime which is a highly
polluting industry due to the CO2 evolved during the calcination of
limestone, adopts almost on pollution control measures.
Both the above materials have to compete with industrial
materials like cement and concrete blocks, because of rapid strides in
technology development and improved energy efficiencies in the cement
industry. These industries, mainly in the large scale sector, can afford
environment control measure even at high initial costs, because of assured
returns over a period of time. With obvious economic benefits, there has been
a marked downward trend in the energy content of cement. As a result,
concrete block walls are today at least 30 percent more efficient in their
material energy content, when compared with brick walls. There are entire
belts in India, areas with vast reserves of stone, where concrete blocks are
replacing bricks. The coarse aggregate manufacturing units generate huge
quantities of stone dust, otherwise a waste, but which is a major constituent
of concrete blocks. This has lead to a symbiotic relationship between the two
technologies. In areas, where stone aggregates are not easily available and
soil for bricks is not suitable, fly ash substitution is common. Flyash acts
as a filler and assists the burning process due to its residual calorific
value.
An interesting backlash of the imposed ban on the use of
primary wood in government construction is the promotion of aluminium and
steel structurals. It has also promoted the introduction of new materials
like medium density fibreboard and cement based boards. All these materials
are regrettably more energy intensive compared to wood or even plywood.
Through a comparison of the equivalent energy in medium density fibreboard and
cement based boards (fig.1) it is evident that the energy used in their
manufacture is much greater than the respective energies for plywood. Plywood
manufacture involves the use of primary wood; implying depletion of forest
reserves. As a positive step towards sustainable enterprises, many of the
plywood industries are investing in captive plantations of fast growing wood
species. This move ensures income and fuel wood to the local farmers, and
these plantations are also a valuable sinks for CO2.
Fig. 1:
Energy in Wood-based Board |
Medium
density
fibre (MDF) |
 |
Ply Board
(PB) |
Cement-Wood
(CW) |
|
Energy in
kWh*/sqft |
|
Eembodied
|
Eproduction
|
Etransport
|
|
|
|
raw
|
Finished
|
MDF |
7.4 |
4.5 |
0.1 |
0.1 |
PB |
3.8 |
1.6 |
0.1 |
0.1 |
CW |
4.9 |
1.3 |
0.3 |
0.1 |
|
* kWh = kWh (thermal)=860
kcal |
With emphasis on the social imperatives like employment
generation and local production, the key determinants of a sustainable
building economy are demonstrated by the example of plywood manufacture.
Development Alternatives, in the course of its research programme on “Energy
Content of Building Materials” focuses on the identification of technology
gaps in the existing building materials sectors. This will enable decision
makers to assess energy requirements for different growth scenarios as well
as provide insights for influencing material development, fuel substitution
and energy pricing issues.
A unique opportunity for NGOs to have their say: We would
be delighted to create space in our newsletter for NGOs working on issues
related to environment and development. We especially welcome those who often
have no medium or vehicle to place their points of view and achievements and
problems in the larger public arena. We hope this would help strengthen the
NGO network. Send your views, previews, reviews, interviews ... whatever. |
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