Page 86 - Implementation of ITU-T international standards for sustainable management of waste electrical and electronic equipment: The path to a circular economy in Costa Rica
P. 86
Implementation of ITU-T international standards for sustainable management of waste
electrical and electronic equipment: The path to a circular economy in Costa Rica
Table 5 – Proposed sub-indicator estimate for each tracer considered in the study for
2020 (continued)
Managed Generated Managed WEEE
WEEE WEEE (Sub indicator)
Category Tracer
2020 2020 2020
(tonnes) (tonnes) (%)
Television sets Flat televisions 38.95 6623 0.6 %
CRT televisions 1.15 75 1.5 %
Telecom equipment Cell phones 3.93 692 0.6 %
Computers Laptops 32.34 1532 2.1 %
PC 23.36 1122 2.1 %
Small IT 357.68 573 62.5 %
Flat monitors 21.28 124 17.1 %
CRT monitors - 27 0.0 %
Printers 150.85 1532 9.8 %
The grouping of tracers into categories is as explained in Figure 15 - Selected tracers for the
Case Study of Costa Rica and their relations with EEE EU-6 and UNU-KEY categories.
Table 6 – Proposed sub-indicator estimate for EEE categories considered in the study
for 2020
Generated Managed WEEE
Managed WEEE
Categories 2020 WEEE (Sub-indicator)
2020
2020
(tons)
(tons) (%)
Large household appliances 422.65 9467 4.5
Televisions 40.10 6698 0.6
Telecom equipment 3.93 692 0.6
Computers 585.51 4911 11.9
3 6 4 Evaluation of consequences and hotspots
Recommendation ITU-T L.1031 points out that assessing the consequences of inappropriate
WEEE management at any point in the value chain provides insights into socio-economic and
environmental impacts, known as “hotspots”. For this purpose, the flow diagram presented in
3.6.2.1 Current material flows is used as a basis, and the results of the mass flows and balances
are analysed in terms of potential socio-economic and environmental impacts, as well as
shortcomings of the management system that do not allow the generation of information for
the material flows. Figure 59 shows the hotspots identified.
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