Integrating Environmental Considerations into the Economic Decision-Making Process
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Volume 3East and Southeast AsiaMalaysia (agriculture) Index
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IV. MEASURES FOR INTEGRATING ENVIRONMENTAL CONSIDERATIONS INTO AGRICULTURE

[ IV | IV-A | IV-B | IV-C | IV-D | IV-E ]

E. Environmental management systems: possible effects of the ISO 14001 standard on Malaysian exports

Increased use of standards regarding environmental management systems, and in particular the development of international standards under the ISO 14000 series, have generated both interest and concern in Malaysia. The principal concern is that to the extent that the ISO 14000 (in particular the ISO 14001 certification standard) becomes a de facto condition for doing business, at least in certain sectors, Malaysian producers will face additional costs. Such additional costs, it is argued, may be higher for Malaysian firms, in particular small and medium-sized firms, than for their competitors in developed countries, which are already implementing environmental strategies and are using more environment-friendly production processes. On the other hand, the continuous environmental improvements encouraged by ISO 14000 may induce cost savings, e.g., through reduced input costs resulting from a more efficient use of materials and energy. Also, participation in ISO 14001 provides a basis for the certification of a firm’s environmental management system, which may give it greater credibility with overseas clients and the government. The government itself may benefit from ISO 14000 to the extent that environmental management systems put greater emphasis on self-regulation on the part of industry, providing enforcement officers with more time to spend on controlling the most polluting industries. A National Committee on Environmental Standards has been established in Malaysia to study the impacts of the ISO 14000 series.

The potential effects of ISO 14001 on exports from Malaysia are difficult to project. Any such effects are expected to occur principally in relation to firm-to-firm operations, in particular with overseas customers. The closest analogue to environmental management systems can perhaps be found in the ISO 9000 series on quality control, and experience with ISO 9000 may shed some light on the possible impact of ISO 14001. It should be noted, however, that the impact of ISO 14001 relative to that of ISO 9000 may be reduced by the fact that, whereas quality concerns are of direct importance to all companies, environmental concerns may be of relevance mainly to industries in certain environmentally sensitive sectors. Thus, ISO 14001 may have relatively little effect on certain sectors.

As to the costs of participation, two elements are important: (a) the additional costs involved in meeting the environmental objectives of environmental management systems; and (b) the costs involved in registration.

With regard to element (a), the main requirement of ISO 14001 is for producers to establish and maintain an environmental management system based on self-determined environmental policy and goals. Compliance with all applicable environmental regulations is a minimum requirement. It should be noted that in the case of Malaysian producers, that requirement refers to domestic environmental legislation in Malaysia. Statistics from the Department of Environment show that the rate of compliance with domestic environmental regulations varies from sector to sector. It may also vary according to farm size. It should also be noted, however, that ISO 14001 also expects participating companies to go beyond the levels of the environmental requirements established by law, by committing themselves to the continuous improvement of environmental management systems. That aspect may imply additional costs for many producers in all sectors. At the same time, environmental management systems themselves may contribute to environmental improvements and economic benefits, e.g., through savings on input costs or improved business opportunities.

With regard to (b), obtaining and maintaining certification is expensive. In general, companies in developing countries may have to rely on the services of expensive consultancy firms when setting up environmental management systems. In addition, registration fees may be an important cost factor. In the case of Malaysia, it is likely that MAC will become responsible for accrediting registrars.

Table 6. Trends in pollution from crude palm oil mills

Year

BOD load

Population
equivalent

(‘000)
Licence fees collected by the Department of Environment
  Generated

(tons/day)
Emitted

(tons/day)
  (xM$ 1,000a)

1960

1965

1970

1971

1972

1973

1974

1975

1976

1977

1978

1979

1980

1981

1982

1983

1984

1985

1986

1987

1988

1989

1990

1991

30

48

138

186

230

256

329

396

436

508

563

690

850

1,000

1,100

1,200

1,640

1,640

1,573

1,627

1,647

1,693

30

48

138

186

230

256

329

396

436

508

563

222

130

58

35

19

4

4

5

5

5

5

7

6

600

960

2,760

3,720

4,600

5,120

8,000

10,150

12,000

14,150

15,890

4,440

2,600

1,160

700

380

80

80

110

110

110

110

140

120

 

 

 

 

 

 

 

 

 

 

2,768

714

714

40

219

271

254

258

281

310

335

362

391

376

Sources: Environmental Quality Reports, Department of Environment; Aiken and others, op. cit.; additional calculations.

aM$ 1.00 = US$ 0.40 (1992 rate).

Table 7. Regulatory standards for palm oil mill effluent

Parameter

Effective date:

1 July of relevant year
A

1978
B

1979
C

1980
D

1981
E

1982
F

1984
Biochemical oxygen demand (BOD)a 5,000 2,000 1,000 500 250 100
Chemical oxygen demand 10,000 4,000 2,000 1,000 - -
Total solids 4,000 2,500 2,000 1,500 - -
Suspended solids 1,200 800 600 400 400 400
Oil and grease 150 100 75 50 50 50
Ammoniacal nitrogen 25 15 15 10 150b 100b
Organic nitrogen 200 100 75 50 - -
Total nitrogen - - - - 300b 200b
pH 5.0 - 9.0 5.0 - 9.0 5.0 - 9.0 5.0 - 9.0 5.0 - 9.0 5.0 - 9.0
Temperature, oC 45 45 45 45 45 45

Source: Department of Environment, 1983.

All parameters in mg/l except pH and temperature.

aSample for BOD analysis incubated at 30 oC for three days.

bValue of filtered sample.

Table 8. Status of compliance by palm oil mills, 1991

Parameter Percentage

pH

Ammoniacal nitrogen

Total nitrogen

Suspended solids

BOD

Oil and grease

100

98

98

82

75

0

Source: Environmental Quality Report, 1991, Department of Environment.

Table 9. Palm oil industry response to effluent-related fees, 1978-1982

BOD standard applicable (mg/l) 1978 1979 1980 1981 1982
5 000 2 000 1 000 500 250
Range of fees (M$) Percentage of mills

0 - 1 000

1 000 - 10 000

10 000 - 50 000

50 000 - 100 000

Above 100 000

Total

19

35

24

15

7

100

63

37

-

-

-

100

73

24

3

-

-

100

68

31

1

-

-

100

75

25

-

-

-

100

Source: Ong, Maheswaran and Ma Ah Ngan, 1987.

Table 10. BOD Load reduction in the crude palm oil industry, 1978-1989

BOD standard applicable (mg/l) 1978

5 000
1979

2 000
1980

1 000
1981

500
1982

250
1984

100
1989

100
Number of mills 131 140 147 157 167 186 254
Crude palm oil production (1,000 tons) 1,786 2,188 2,573 2,822 3,511 3,715 6,057
BOD load generated (tons/day) 563 690 850 1,000 1,100 1,640 1,693
BOD load discharged (tons/day) 563 222 130 58 5 4 5
Percentage reduction in BOD load discharged 0 67.8 84.7 94.2 96.8 99.8 99.7

Sources: Ong, Maheswaran and Ma Ah Ngan, 1987; Environmental Quality Reports, Department of Environment; additional calculations.

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