WEEE/E-waste Business Model - International Environmental ...
WEEE/E-waste Business Model - International Environmental ...
WEEE/E-waste Business Model - International Environmental ...
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2.3 SWOT Analysis<br />
The analysis of the above three models indicates that there are three mechanisms for E-<strong>waste</strong><br />
management out of which two mechanisms are at extreme levels i.e. conventional E-<strong>waste</strong><br />
recycling model and EPR based business model. Strength, Weakness, Opportunities and<br />
Threat (SWOT) analysis of these two extreme mechanisms has been carried out to understand<br />
the applicability under the current business environment. This analysis has been summarized in<br />
table 2.3. The common points, which can be inferred from this analysis, are given below.<br />
4. Regulatory intervention is required in implementation of both the models.<br />
5. Government participation will boost the implementation of both the models.<br />
6. Potential of leakage exists in both the systems i.e. they are not foolproof system.<br />
Though EPR system offers the potential of reduction of leakage of <strong>waste</strong> to informal<br />
sector, it is also not 100% foolproof. The recent EU report on the implementation of<br />
<strong>WEEE</strong> directive in member countries clearly states the gap in <strong>WEEE</strong> collection<br />
efficiency.<br />
The major point of difference in the implementation of the two models is the “money flow” i.e.<br />
“who” pays ‘whom”. In Combodian context, the EPR system will lead to a complete shift in<br />
“consumer behavior”. The existing consumer, which is used to receive the “best salvage value”<br />
of their E-<strong>waste</strong>, will start giving it “free of cost” and start paying “Recycling Fee” at the same<br />
time. The major barriers, which are expected to implement this system, are given below.<br />
7. Is the consumer ready at the moment to adopt the system or ‘shift’ in attitude?<br />
8. If yes, then what is the time line for implementation?<br />
9. Does the regulatory monitoring system have capacity to monitor this system?<br />
10. Who will be responsible for leakages and implementation of penal provisions?<br />
11. Who will be responsible for ownership of imported E-<strong>waste</strong> seized at the point of<br />
entry in the country?<br />
12. How many E-<strong>waste</strong> recycling facilities will be viable under this system and how the<br />
E-<strong>waste</strong> collection and transportation system will be organized considering intra<br />
province or province state issues?<br />
A summary mapping of the “sensitivity analysis” versus the three models is given in table 2.4.<br />
The following inferences can be drawn from this mapping.<br />
1. A clear “trade off” exists between the government participation in terms of land/<br />
subsidy/ customs duty & octroi waiver/ income tax rebate/ interest rate rebate on one<br />
hand and input raw material cost, rights to sell recovered material and recycling fee<br />
on the other hand.<br />
2. The timing of this trade off can be linked to time taken to shift ‘consumer behavior”.<br />
This provides the basis for either supporting the recyclers for a particular period of time<br />
or lead to development of PPP model for E-<strong>waste</strong> management.<br />
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