L8: Policy with imperfect information; Criteria 6-9 Flashcards
Estimation of costs and benefits is necessary where the info available to the EPA is ___
Why would it not be efficient to search for info?
Estimation of costs and benefits is necessary where the info available to the EPA is imperfect
Those who possess the info may have little incentives to truthfully reveal it
Identifying abatement benefit is a two-stage process:???
▪ Identifying abatement benefit is a two-stage process:
(i) the impact of abatement must be established and
(ii) monetary valuations attached. Yet valuation is beset by theoretical & practical problems. Even no consensus on validity of current valuation techniques.
Name the 4 criteria for policy instrument choice that depend on certainty.
Dependability
Flexability
Costs of use underuncertainty
Information requirements
Dependable if it can be relied on to meet a ___ ___
▪ Emissions quantity controls and price controls will have known _____ outcomes
▪ With full knowledge of the____ _ _ _ function the emissions __ ___can be determined to achieve a target level of emissions
▪ Once that tax rate is introduced, ____ takes place at the desired level, as shown in the top half of the next slide where a single aggregate MCA is drawn with certainty on behalf of the EPA
Dependable if it can be relied on to meet a predetermined target
▪ Emissions quantity controls and price controls will have known quantity outcomes
▪ With full knowledge of the aggregate MCA function the emissions tax rate can be determined to achieve a target level of emissions
▪ Once that tax rate is introduced, abatement takes place at the desired level, as shown in the top half of the next slide where a single aggregate MCA is drawn with certainty on behalf of the EPA
Draw the graphs of a comparison of emissions taxes and marketable permissions permits when abatement costs are uncertain
Slide 8
▪ Consider one particular form of imperfect info- the EPA does not know the position of the ___ MCA function with certainty. Difference in outcomes between price-based (____ and ____) and quantity-based instruments (____ and ___ ____).
▪ With emissions tax the amount of ____ that results from any given rate of tax will not be certainly known, as it depends on the unknown position of the abatement cost function.
▪ Licences & ____ permits are dependable in terms of abatement (although there will be uncertainty about the size of abatement costs and, with marketability, the ____ of permits).
▪ Uncertainty with regard to the true MCA for a price system translates into uncertainty about the ___ of abatement. Uncertainty with regard to the true MCA for a quantity system translates into uncertainty about ___ or costs. The differing way in which uncertainty
affects taxes and permits is shown in the bottom half of Fig 7.1 (_ possible MCA functions).
▪ Consider one particular form of imperfect info- the EPA does not know the position of the aggregate MCA function with certainty. Difference in outcomes between price-based (taxes and subsidies) and quantity-based instruments (licences and marketable permits).
▪ With emissions, tax the amount of abatement that results from any given rate of tax will not be certainly known, as it depends on the unknown position of the abatement cost function.
▪ Licences & marketable permits are dependable in terms of abatement (although there will be uncertainty about the size of abatement costs and, with marketability, the price of permits).
▪ Uncertainty with regard to the true MCA for a price system translates into uncertainty about the quantity of abatement. Uncertainty with regard to the true MCA for a quantity system translates into uncertainty about prices or costs. The differing way in which uncertainty
affects taxes and permits is shown in the bottom half of Fig 7.1 (3 possible MCA functions).
It is sometimes claimed that emissions ____ and ___-_____ licences allow the EPA to control emissions more dependably than ____ under uncertainty
▪ Some __ ___ ___ instruments are not dependable e.g. technology requirements because the emissions outcome cannot be known beforehand.
It is sometimes claimed that emissions quotas and non-tradable licences allow the EPA to control emissions more dependably than permits under uncertainty
▪ Some CAC instruments are not dependable e.g. technology requirements because the emissions outcome cannot be known beforehand.
Flexibility:
Where decisions are made with___ ___, the flexibility of an instrument is of little or no value.
▪ But with uncertainty, the EPA might need to learn adaptively by ___ ___ ___, and to change the rates or levels at which instruments are applied as new information arrives.
▪ Generally, the more flexible an instrument is, the better. But it is ____ to find any general conclusions about the relative flexibility of different instruments.
▪ Suggestion that ___-based incentive instruments are inflexible as there is inherently strong ___ to changes in rates.
▪ Changes in ____ and ___ are not subject to such strong resistance
Flexibility:
Where decisions are made with perfect information, the flexibility of an instrument is of little or no value.
▪ But with uncertainty, the EPA might need to learn adaptively by trail-and-error, and to change the rates or levels at which instruments are applied as new information arrives.
▪ Generally, the more flexible an instrument is, the better. But it is difficult to find any general conclusions about the relative flexibility of different instruments.
▪ Suggestion that price-based incentive instruments are inflexible as there is inherently strong resistance to changes in rates.
▪ Changes in licences and permits are not subject to such strong resistance
Flexibility:
___ ___ ___ instruments might also be more flexible relative to permit trading. Trading schemes may be ____ to design and it may not be a simple task to ___ such schemes. Piecemeal ____ could be implemented easily using CAC.
▪ Another way of thinking about these issues are whether price changes or quantity changes are ___ less desirable. Quantity changes could incur larger transactions costs
▪ ____ standards can be inflexible. They impose large ____ costs
Flexibility:
CAC instruments might also be more flexible relative to permit trading. Trading schemes may be costly to design and it may not be a simple task to modify such schemes. Piecemeal changes could be implemented easily using CAC.
▪ Another way of thinking about these issues are whether price changes or quantity changes are socially less desirable. Quantity changes could incur larger transactions costs
▪ Technological standards can be inflexible. They impose large capital costs
Choices made today using available info may turn out not to be appropriate in hindsight
▪ Such errors generate costs:
(i) Cost of
(ii) Cost of
Choices made today using available info may turn out not to be appropriate in hindsight
▪ Such errors generate costs:
(i) Cost of incorrect target
(ii) Cost of failing to attain target at least cost
Draw graph showing the costs of selecting the wrong target
where is the Total Net Social Benefit at that level of emission
slide 14
Draw the graph where the assumed MC is outside the True MC and show the loss when the emissions are higher and lower than the optimal level
slide 15,16
Firms abate emissions as long as MCA(true) is
below the tax so they emit Mt.
▪ Efficiency loss is the shortfall of benefits at Mt
compared to the maximum possible M* i.e. the
hatched area
▪ Compared with an emissions licence system, the
EPA thinks that the efficient target is LH (rather
than M*).
▪ Incorrect info leads to an insufficiently tight
control of emissions. Efficiency loss equal to the
solid area
Draw graph of the scenairo where there is an underestimation of the abatement cost?
slide 17
Emissions tax results in a loss (hatched area) that
is greater than the loss associated with licences
(solid area)
▪ The loss from a tax exceeds that from licences.
This result is dependent on how we construct the
MCA and MD functions (i.e., the slopes)
Draw an underestimation and overestimation of the abatement cost curve for a much flatter Marginal Damage curve
How does the ranking of the instruments change with the steepness of the MD curve?
▪ The above graphs are analogues of the above two situations, but are drawn with a substantially
flatter marginal damage curve.
▪ As before, both instruments generate efficiency losses with mistakes about MCA. However, the
ranking of the instruments changes as the loss is larger with licences
▪ When MCA is flatter than MD, licences are preferred to taxes as they yield smaller efficiency losses. When MCA is steeper than MD curve taxes are preferred to licences- smaller efficiency
Conclusions so far do not carry over to damage
costs.
▪ In this case, choice of instrument (quantity vs.
price-based) has no effect on the ___ ____
arising from errors in estimating damage cost
▪ The size of the loss is the same in each case.
Given the estimated MD and the MCA(true),
EPA sets a tax rate t or a quantity control L.
Realised emissions are ____ than efficient
emissions.
Conclusions so far do not carry over to damage
costs.
▪ In this case, choice of instrument (quantity vs.
price-based) has no effect on the efficiency loss
arising from errors in estimating damage cost
▪ The size of the loss is the same in each case.
Given the estimated MD and the MCA(true),
EPA sets a tax rate t or a quantity control L.
Realised emissions are greater than efficient
emissions. Shaded area is the efficiency loss