2,904 research outputs found
Future Waste Scenarios for Sweden based on a CGE-model
No full textOver the last decades, waste quantities have grown steadily in close relation to economic growth. To tackle the problem of continuing waste growth within the EU, waste prevention was listed among four top priorities in the EU Sixth environment Action Programme. A Computable General Equilibrium (CGE) model is here used for projecting future quantities of hazardous and non-hazardous waste in Sweden to 2030. The effects of driving forces behind waste generation are illustrated by comparing the results of waste projections for a Baseline scenario and four alternative scenarios. The scenarios differ mainly in GDP growth rates and in the assumptions about future waste intensities of the economic activities of firms and households. We use a high-resolution data set on waste flows of 18 various types of non-hazardous waste and 16 various types of hazardous waste attributed to six waste-generating sources for the base year 2006. Waste generated in the scenarios, thus, relate to firms’ material input, output, employees, capital scrapping and fuel combustion as well as households’ consumption. The impact of economic growth in increasing the generation of nonhazardous and hazardous waste is apparent when comparing the growth of waste from 2006 to 2030 in the five scenarios. On the contrary, technological change resulting in less waste intensive production processes and changed behaviour among households, making their activities less waste intensive, have a strong reducing effect, especially on generation of non-hazardous waste relating to firms’ material input.general equilibrium model; waste generation; decoupling; waste intensities waste scenarios.
Nitrogen and Sulphur Outcomes of a Carbon Emissions Target Excluding Traded Allowances - An Input-Output Analysis of the Swedish Case
No full textA cost-effective policy instrument to attain the Swedish carbon emission target, suggested by the Government’s commission on flexible mechanisms of the Kyoto protocol, is the purchase of emission allowances within the EU trading scheme, instead of reducing domestic CO2 emissions at higher costs. Also, proposed by the commission, is that only grandfathered, but not imported emission allowances, should be accounted for in the carbon emissions target. This formulation of the target is now under consideration by the Swedish Environmental Protection Agency as instructed in Sweden’s Budget Bill for 2007. The nitrogen and sulphur outcomes of these suggestions for the climate policy are here assessed in the view of Sweden’s official emission projections for 2010 and 2020. In view of the historical emission multipliers and the analysis presented here, the proposed climate policy does not conform to Sweden’s interim targets for nitrogen oxides (NOx) and sulphur dioxide (SO2). Although, the CO2 emission target could be attained at the least costs through emission trading, an environmental policy which brings also SO2 and NOx emissions to the acceptable levels requires additional policy instruments aiming at the exclusive reduction of these emissions. The findings here suggest that these reductions would correspond to decreases of the SO2/GDP and NOx/GDP ratios by 8 and 12 per cent, respectively. The emission multipliers of aggregate demand for CO2-permit trading and non-trading sectors, are calculated by exploiting the environmental accounting matrix of Sweden for 2000 within the framework of an inter industry model.Emission multipliers; carbon trading; emission/GDP ratio; environmental goals
The EMEC model: Version 2.0
No full textThe present paper introduces a new version of an applied general equilibrium model of the Swedish economy: Environmental Medium Term Economic Model (EMEC). The model is used at NIER for analysing economic implications for households and firms of the Swedish environmental policy. The economy and the environment interact in the model and thus, we can analyse the economic implica-tions of various environmental policy measures, such as a CO2-tax, a CO2-ceiling and CO2-trading. The model captures also ancillary benefits of climate policy for NOx, SO2, PM10 and PM20. This new version of EMEC, in addition, analyses the effects of road user charges and the economic impact of environmental policy measures on six types of households, as transport demand is represented in a much more detail and as households are distributed, by disposal income and residence. Furthermore, the model distinguishes 26 industries, 33 composite commodities, 26 consumer goods, two kinds of labour and eight pollutants. The model produces results for endogenous variables, which can be interpreted fully in terms of the model’s theory, data and the assumptions underlying the exogenous variables.CGE-model; Sectors; Pollutants; Factors of production; Substitution; Sweden
In Search of a Method for Measuring the Output Gap of the Swedish Economy
No full textThis paper describes and evaluates measures of trend (or potential) output in order to improve the measuring and understanding of the current state of the Swedish economy. The target group of the paper is primarily policy makers and analysts in Sweden and international organisations who study the Swedish economy and give recommendations concerning appropriate stabilization policies. The views expressed are those of the authors and do not necessarily represent the ones of neither the National Institute of Economic Research nor the Ministry of Finance.
Interpreting Wage Bargaining Norms
No full textFrom the mid-1990s onwards, Swedish wage bargaining has been characterised by informal co-ordination of the wage claims of big unions and bargaining cartels. In particular, it has been understood that the manufacturing sector should lead by first agreeing on a pay increase, whereafter the service sector and public sector unions choose a similar increase. We analyse his setup with two possible theoretical interpretations: (i) the manufacturing sector as a tackelberg leader and (ii) a normative role for the manufacturing sector’s pay increase, upported either by unmodelled social pressure or a modeled loss aversion (envy) of the heltered sector unions. The conclusion of the analysis is that the normative or leading role of one sector – in the Swedish case the manufacturing sector – can potentially bring big benefits for employment and output. Generalising an idea suggested by Lars Calmfors and Anna Larsson, our analysis also generates a rudimentary theory of why the wage increase norm sometimes binds and sometimes not. A comparison of the model predictions and the observed outcomes of the last five wage bargaining rounds in Sweden suggests that the model is generally consistent with the empirical observations: wage moderation and norm observance are stronger when the manufacturing industry’s initial relative wage is low.wage bargaining; bargaining co-ordination
Analysing future solid waste generation - Soft linking a model of waste management with a CGE-model for Sweden
No full textParallel to the efforts of the EU to achieve a significant and overall reduction of waste quantities within the EU, the Swedish parliament enacted an environmental quality objective stating that ‘the total quantity of waste must not increase …’ i.e. an eventual absolute decoupling of waste generation from GDP. The decoupling issue is ad-dressed, in the present paper, by assessing future waste quantities, for a number of economic scenarios of the Swedish economy to 2030 with alternative assumptions about key factors affecting waste generation and waste management costs. We use an integrated top-down/bottom-up approach by linking a CGE-model of the Swedish economy with a systems engineering model of the Swedish waste management system. In this way, we can in more detail consider the interaction between waste generation and waste management costs (waste disposal prices) when assessing future waste quantities. A relative decoupling of waste generation takes place in all scenarios, i.e. total waste quantities increase at a lower rate than GDP. Absolute decoupling, which re-quire total waste quantities to stabilize or to reduce, does not take place in any of the scenarios. This means that the present Swedish Environmental quality objective of stabilizing waste quantities is not met in any of the scenarios with total waste genera-tion levels of 110 per cent up to nearly 200 per cent of that in 2006. The overall impression from our analysis is that costs are high for reducing waste generation irrespective of the type of waste reduced. In other words, the waste treat-ment costs are low compared to the costs for reducing waste. This situation also means that the use of policy instruments, which induce substitution by increasing the price of waste disposal services, will have very small reducing effects on the generation of all types of waste unless the price increase brings about an introduction of waste preventing techniques and affect households in the direction of a less waste intensive behaviour. For example, the policy instruments used must affect the pattern of household consumption pattern more directly, as a differentiation of the value added tax, rather than to be directed towards the waste management sector. Economic policy instruments introduced in the waste management sector are more likely to affect the choice of waste management solutions than prevent waste generation. Linking a macroeconomic and a systems engineering model for waste manage-ment, gives us a tool useful also for capturing the macroeconomic effects, such as GDP growth and structural changes, when designing policy instruments intended to prevent waste generation or take waste management in a more sustainable direction.general equilibrium model; systems engineering; solid waste; waste management; waste generation; decoupling; EMEC; NatWaste; top-down/bottom-up; waste policy instruments
Costs of Climate Policy when Pollution Affects Health and Labour Productivity. A general Equilibrium Analysis Applied to Sweden
No full textMuch of the debate over global climate change involves estimates of the direct costs of global climate change mitigation. Recently this debate has included the issue of ancillary benefits. These benefits consist mainly of health improvements. Although it is generally acknowledged that air pollution affects respiratory health, and that valuations of these impacts make up a significant proportion of the damage costs of air pollution, these impacts are often neglected when evaluating the costs of climate policy. Since reducing greenhouse gases has the effect of also reducing other pollutants affecting human health and labour productivity these effects should be taken into consideration. The analysis incorporates a linkage between air pollution and health effects into a general equilibrium model for Sweden through a theoretical consistent framework. Results from recent Swedish concentration-response and contingent valuation studies are used to model direct disutility and indirect health effects that negatively affects the productivity of labour. The costs of feedback effects on health and productivity are compared in three different scenarios for attaining the Swedish carbon dioxide target with alternative projected emission levels in the baseline scenario as well as alternative harmful emission levels. Results show that not including feedback effects could mean overstating the costs of climate policy. The magnitude of these effects are, however, very sensitive to projected emission levels and to the judgement of harmful emission levels.air pollution; ancillary benefits; climate policy; general equilibrium; health
Does remediation save lives? On the cost of cleaning up arsenic-contaminated sites in Sweden
No full textSwedish environmental policy is based on 16 environmental quality objectives (Gov. Bill 2000/01:130 and Gov.Bill 2004/05:150).1 One of the most challenging objectives,‘A non toxic environment’, has two interim targets that concern remediation of contaminated sites. In sum, they state that the highest priority should be given to sites posing the highest risks to human health and the environment.2 By eliminating pollutants in soil, groundwater and sediment, the interim targets aim to reduce risks to human health and the environment. In Sweden, 83,000 sites are potentially contaminated due to previous industrial activities. According to the Swedish Environmental Protection Agency (EPA), the administrator of the governmental funds for remediation, approximately 1500 of these sites contain contaminant concentrations that could seriously harm human health and the environment (Swedish EPA, 2008a). To reach the interim targets, all these sites need to be remediated by 2050. Remediation of contaminated sites has so far cost more than SEK 3,000 million.3 The approximated cost to mitigate the potential risks at the most harmful sites is estimated at SEK 60,000 million.4 The Swedish government’s funding for remediation presently comes in the form of a directed grant (sakanslag). The directed grant, administrated by the Swedish EPA, subsidises remediation of contaminated sites that were contaminated prior to modern environmental legislation (in 1969) or for which no liable party can be found. The directed grant amounts to approximately 455 millions annually, which corresponds to about 10 percent of the annual national funds for environmental protection (Gov. Bill 2007/08:1). To make it possible to prioritise among contaminated sites, the Swedish EPA has developed a method for risk assessment called the ‘MIFO’ (i.e. the Method for Inventory of Contaminated Sites). The risk assessment does not take into account the actual exposure at a contaminated site. Risk is instead assessed based on divergence from guideline values for acceptable concentrations given a standardised (i.e. worst case) exposure situation on an individual level. This means that a site can be remediated without any individuals actually being exposed. The expected risk reduction is consequently not quantified. This eliminates the possibility of valuing the risk reduction, which should be weighed against the remediation cost. The purpose of this paper is to analyse how health effects, in the form of cancer risks, from sites contaminated by arsenic are valued implicitly in remediation. By using an environmental medicine approach that takes exposure into account, and without underestimating the potential health consequences of arsenic exposure, our purpose is to place arsenic risk management in the overall picture of live-saving interventions. In the case of cancer prevention, it is necessary to recognise that focus on an environmental carcinogen like arsenic may draw public attention – and funding – away from mental health risks like ambient air pollution and indoor radon. Although environmental pollution accounts for less than ten percent of all cancer cases (Harvard Centre for Cancer Prevention, 1996; Saracci and Vineis, 2007), environmental factors are important to recognize since they may be preventable. We emphasise, however, the inefficiency in becoming overly concerned about small risks while, at the same time, losing sight of the large risks. If society’s spending on lifesaving measures with small effects (i.e. a small number of lives saved) crowds out spending on lifesaving measures with large effects, then remediation can, in fact, even be said to waste lives. By using data on 23 arsenic-contaminated sites in Sweden, we estimate the sitespecific cancer risks and calculate the cost per life saved by using the sites’ remediation costs. Our results show that the cost per life saved through remediation is much higher than that associated with other primary prevention measures, indicating that the ambition level of Swedish remediation may be too high.
Labor-Force Participation Rates and the Informational Value of Unemployment Rates: Evidence from Disaggregated US Data
No full textThe informational value of the aggregate US unemployment rate has recently been questioned be-cause of a unit root in the labor-force participation rate; the lack of mean reversion implies that long-run changes in unemployment rates are highly unlikely to reflect long-run changes in jobless-ness. This paper shows that this critique also extends to unemployment rates for sub-populations, such as prime-aged males.Unit-root test;
The Forecasting Properties of Survey-Based Wage-Growth Expectations
No full textIn this paper, we evaluate survey-based wage-growth expectations in Sweden. Results show that the expectations are neither unbiased nor efficient forecasts. Evaluating out-of-sample forecasting performance, we find that the survey participants generally perform worse than a con-stant forecast based on reasonable assumptions regarding the inflation target and productivity growth. Our findings indicate that caution should be exercised when relying on these data for policymaking.Survey data;
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