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MOJ
eISSN: 2573-2919

Ecology & Environmental Sciences

Review Article Volume 4 Issue 6

Product life cycle assessment (LCA) in the environmental engineering and management aspects

Jagath Kulathilaka,1 Suresh Aluvihara2

1Department of Management Sciences, Uva Wellassa University, Sri Lanka
2Department of Chemical and Process Engineering, University of Peradeniya, Sri Lanka

Correspondence: Suresh Aluvihara, Department of Management Sciences, Uva Wellassa University, Badulla, Sri Lanka

Received: November 02, 2019 | Published: November 21, 2019

Citation: Kulathilaka J, Aluvihara S. Product life cycle assessment (LCA) in the environmental engineering and management aspects. MOJ Eco Environ Sci. 2019;4(6):269-274. DOI: 10.15406/mojes.2019.04.00164

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Abstract

Environmental pollution is an ever found crux with the industrialized world although able to prevent or minimize the environmental pollution through some proper environmental management system. Product life cycle assessment (LCA) is a method of environmental assessment especially for the future plans, products and projects although it is able to assess only the environmental impacts through the product life cycle assessment (LCA). According to the methodology of the implementation of the product life cycle assessment (LCA), it is possible to continue at different stages of the relevant activities as necessary. The implementation of the assessment is done based on four key steps namely as goal and scope definition, inventory analysis, impact assessment and the interpretation. Under this assessment, basically it is expected to prevent the environmental impacts, mitigate the environmental impacts or find a solution for a future problem that relevant with the activity this is proposed.

Keywords: life cycle assessment, environmental impact, inventory analysis, impact assessment, environmental pollution control

Introduction

Regarding the most of industrial and manufacturing processes it is commonly found some problems that need to be solved in various ways. In fact that the Environmental Pollution is some sort of risky aspect that related with the industrial processes even though it is able to minimize through a proper Environmental Management system.1–3 The major Environmental Impacts found with respect to some specific industrial processes as given in the Table 1.

Pollutants

Environmental impacts

Relevant activities

CO2

Global warming (Green house gas) and Acid rain

Fossil fuel burning

NOX (X=1/2, 1, 2, 3)

Global warming (Green house gas) and acid rain

Vehicle emissions

CO

Diseases for human beings

Semi combustions

SOX (X= 2,3)

Acid rain

Coal burning

CH4

Global warming (Green house gas)

Dumping sites

Waste water

Contamination of water bodies and sources

Industrial activities and wastes

Table 1 Pollutants and their environmental impacts

Therefore, the environmental management system plays a significant role in the protection of the environment. Product life cycle assessment (LCA) is a method that it is able to identify some specific impact before the happening. The preliminaries, methodology and applications of product life cycle assessment (LCA) have been discussed in the following sections.1–5

Life Cycle Assessment (LCA)

Basically through the Life Cycle Assessment (LCA), the solutions are found for the Environmental Impacts and the Health Impacts especially in following stages with respect to some specific product.

  1. Raw material exploration and extraction stage
  2. Stage of preprocessing, collection and transportation of raw materials
  3. Production and manufacturing stage
  4. Distribution stage
  5. Uses of the product stage
  6. Disposal, recovery, reuse or recycle stage

The relevant procedure of the implementation of the Life Cycle Analysis (LCA) has been described with the appropriate example as given in the below.1–6

A, B, C and D are four same products for the similar requirements and same function although which are producing under four different processes in different factories. Therefore, those productions may have different properties. For the production of 1kg of each of following products the relevant data have been assumed as given in following Tables 2–5.

Product

Raw material extraction phase (g/kg)

Transportation phase

Production phase

Recycle phase

(g/kg)

(g/kg)

(g/kg)

Product A

2

30

20

1

Product B

1

25

35

2

Product C

3

50

15

10

Product D

8

40

45

3

Table 2 NOX emissions for 1kg of each production

Product

Raw material extraction phase (g/kg)

Transportation phase

Production phase

Recycle phase

(g/kg)

(g/kg)

(g/kg)

Product A

5

4

7

12

Product B

2

6

8

15

Product C

9

9

14

7

Product D

6

5

6

20

Table 3 SO2 emissions for 1kg of each production

Product

Raw material extraction phase (l/kg)

Transportation phase

Production phase

Recycle phase

(l/kg)

(l/kg)

(l/kg)

Product A

2

-

4

7

Product B

1

-

6

10

Product C

4

-

5

3

Product D

5

-

3

4

Table 4 Water consumptions for 1kg of each production

Product

Raw material extraction phase (g/kg)

Transportation phase

Production phase

Recycle phase

(g/kg)

(g/kg)

(g/kg)

Product A

6

4

3

9

Product B

23

5

2

7

Product C

15

6

9

12

Product D

10

8

12

18

Table 5 Solid waste generations for 1kg of each production

The above data were used in the following steps of the product life cycle analysis (LCA) accordingly as the purposes.

Goal and scope definition

This is the initial step of the product life cycles assessment (LCA) and in this stage mainly it is considered about the relevant product, activity, project or plan by defining the relevant purposes of existing study and defining some appropriate system boundaries for such activities.1–9

Goal: Determination of the overall environmental impact from some specific amounts of product A, product B, product C and product D.

Defining of a functional unit: The functional unit should be descriptively common for each type of product to be compared with the other product. In addition this is called as the basis for the product life cycle assessment (LCA).

According to the above example the basis was assumed as the production of 100kg of each production. Therefore, in the following steps there were expected to determine the amounts of emissions, water consumptions and solid waste generations with respect to 100kg of each product.

Defining of system boundaries: The common process flow diagram (PFD) for each product has been given in the Figure 1.

Figure 1 The process flow diagram (PFD).

According to the process flow diagram (PFD) the environmental impacts of different phases of each product were determined and finally the total environmental impact with respect to each product was determined.

Inventory Analysis

This is the second major step of product life cycle assessment (LCA). At this stage basically it was identified some relevant inputs and outputs of the each stages of the each product.

The total emissions of NOX throughout the manufacturing of 100kg of each production have been determined in the Table 6.

Product

Raw material extraction phase (g)

Transportation Phase

Production Phase

Recycle Phase

Total (g)

(g)

(g)

(g)

Product A

200

3000

2000

100

5300

Product B

100

2500

3500

200

6300

Product C

300

5000

1500

1000

7800

Product D

800

4000

4500

300

9600

Table 6 Total emissions of NOX of 100kg of each production

The total emissions of SO2 throughout the manufacturing of 100kg of each production have been determined in the Table 7.

Product

Raw material extraction phase (g)

Transportation phase (g)

Production phase

Recycle phase

Total

 (g)

(g)

(g)

Product A

500

400

700

1200

2800

Product B

200

600

800

1500

3100

Product C

900

900

1400

700

3900

Product D

600

500

600

2000

3700

Table 7 Total emissions of SO2 of 100kg of each production

The total water consumptions throughout the manufacturing of 100kg of each production have been determined in the Table 8.

Product

Raw material extraction phase (l)

Transportation phase

Production phase

Recycle phase

Total

(l)

(l)

(l)

(l)

Product A

200

-

400

700

1300

Product B

100

-

600

1000

1700

Product C

400

-

500

300

1200

Product D

500

-

300

400

1200

Table 8 Total water consumptions of 100kg of each production

The total solid waste generations throughout the manufacturing of 100kg of each production have been determined in the Table 9.

Product

Raw material extraction phase (g)

Transportation phase

Production phase

Recycle phase

Total

(g)

(g)

(g)

(g)

Product A

600

400

300

900

2200

Product B

2300

500

200

700

3700

Product C

1500

600

900

1200

4200

Product D

1000

800

1200

1800

4800

Table 9 Total solid waste generations of 100kg of each production

Impact assessment

In this stage mainly it was considered the estimation and determination of the environmental impacts from the identified pollutants such as the emissions and wastes. In this stage the basically analyzed the potential impact of such pollutant and the significance relevant with that. The factor may have much validity in the determination of the magnitude of such impacts. The values for the factors might be varied according to different standards and scales. There were assumed some numerical values for such factors as examples for the existing analysis and these are not standard values. The factor may have different units purposely such as the eco-points.1–5

The impacts from NOX of such products have been given in the Table 10.

Product

Amount /quantity (g)

Factor (units/g)

Impact (units)

Product A

5300

1.5

7950

Product B

6300

1.5

9450

Product C

7800

1.5

11700

Product D

9600

1.5

14400

Table 10 Impacts from NOX of such products

The impacts from SO2 of such products have been given in the Table 11.

Product

Amount /quantity (g)

Factor (units/g)

Impact (units)

Product A

2800

1

2800

Product B

3100

1

3100

Product C

3900

1

3900

Product D

3700

1

3700

Table 11 Impacts from SO2 of such products

The impacts of water consumptions of such products have been given in the Table 12.

Product

Amount /quantity (l)

Factor (units/g)

Impact (units)

Product A

1300

0.5

650

Product B

1700

0.5

850

Product C

1200

0.5

600

Product D

1200

0.5

600

Table 12 Impacts from water consumption of such products

The impacts from solid waste generation of such products have been given in the Table 13.

Product

Amount /Quantity (g)

Factor (units/g)

Impact (units)

Product A

2200

0.25

550

Product B

3700

0.25

925

Product C

4200

0.25

1050

Product D

4800

0.25

1200

Table 13 Impacts from solid waste generation of such products

Interpretation

At this stage especially it is expected to interpret the results or outcomes of above analysis. The total impacts of each product throughout the entire manufacturing process have been determined in the Table 14.

Product

Impact of NOX (units)

Impact of SO2 (units)

Impact of water consumption (units)

Impact of solid waste generation (units)

Total impact (units)

Product A

7950

2800

650

550

11950

Product B

9450

3100

850

925

14325

Product C

11700

3900

600

1050

17250

Product D

14400

3700

600

1200

19900

Table 14 Total impacts of each production

According to the overall impact analysis results that it is possible to emphasize the least environmental impact from product A and the highest environmental impact from product D throughout the manufacturing of such products. Therefore these results are important in the making of some decision to choose the most eco-friendly product among a list of product. Due to such analysis and decision there were expected to minimize or preventions of the environmental impact of some pollutants as given in the below.

  1. Reduction of NOX emission–Mitigation of acid rains
  2. Reduction of SO2 emission–Prevention of smog and acid rain
  3. Reduction of water consumption–Mitigation of waste water generations and fresh water pollution
  4. Reduction of solid waste generation–Mitigation of water pollution and air pollution

In addition to the overall environmental impact analysis of each product, it is possible to analyze the impact of some specifically identified pollutant at some necessary phase of some selected production and the results should be important in the selection of mitigation options against such environmental impact. The obtained results should be compared with some reference values, norms or standard limits and it should be identified whether the specific activity is an environmental impact or not.

Applications in the life cycle assessment

  1. Selection of some eco-friendly product or project among a list of such items.
  2. Make some appropriate mitigation options in risky phases in the product life cycle.
  3. Identification of pollutants and relevant activities.
  4. Improve the quality of the product, process or project. 

Merits of life cycle assessment for the environmental management

  1. Identification or eliminate the impact of the pollution.
  2. Identification and confirmation of renewable and non- renewable resources.
  3. Improve and well adaptation for reduce, reuse, recycle and recovery (4R concept) and minimize the waste.
  4. Suggest most appropriate pollution prevention methods with respect to each pollutant.
  5. Minimize the impacts of pollutants on the ecosystems

Importance of life cycle assessment

  1. Assessment of the risky activities of relevant product or project.
  2. Important in the product development and improvement.
  3. Environmental protection

Conclusion

As the major outcomes of the product life cycle assessment are the impact assessments regarding some process of manufacturing and product development. It is suitable for future plans and through that it will be analyzed the environmental impact of entire process or product development. The analysis is much important in the making of decisions to choose some eco friendly product or project while identifying some important phases of some products to be improved to mitigate the relent environmental impact from that phase. In the analysis of the environmental impact that related with some activity it is an essential step to consider about the impact factor for each harmful or adversely considered component.

Acknowledgments

None.

Funding

None.

Conflicts of interest

The authors declared that there no conflicts of interest.

References

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©2019 Kulathilaka, et al. This is an open access article distributed under the terms of the, which permits unrestricted use, distribution, and build upon your work non-commercially.