| Working Paper |
File Downloads |
Abstract Views |
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3 months |
12 months |
Total |
Last month |
3 months |
12 months |
Total |
| A Never-decisive and Anonymous Criterion for Optimal Growth Models |
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0 |
0 |
9 |
0 |
1 |
1 |
42 |
| A Non-dictatorial Criterion for Optimal Growth Models |
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0 |
0 |
35 |
0 |
0 |
1 |
366 |
| A Stylized Energy-Economy Model for France |
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0 |
0 |
0 |
0 |
0 |
1 |
6 |
| A Stylized Energy-Economy Model for France |
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0 |
0 |
0 |
0 |
0 |
0 |
4 |
| A Stylized Energy-Economy Model for France |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
| A never-decisive and anonymous criterion for optimal growth models |
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0 |
0 |
0 |
0 |
1 |
1 |
8 |
| A never-decisive and anonymous criterion for optimal growth models |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
8 |
| A non-dictatorial criterion for optimal growth models |
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0 |
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45 |
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0 |
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195 |
| A non-dictatorial criterion for optimal growth models |
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0 |
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16 |
0 |
0 |
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50 |
| A non-dictatorial criterion for optimal growth models |
0 |
0 |
0 |
17 |
0 |
0 |
0 |
78 |
| A note on the consequences of an endogenous discounting depending on the environmental quality |
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0 |
0 |
92 |
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2 |
2 |
174 |
| A note on the consequences of an endogenous discounting depending on the environmental quality |
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0 |
0 |
31 |
0 |
0 |
1 |
46 |
| A note on the consequences of an endogenous discounting depending on the environmental quality |
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0 |
0 |
1 |
0 |
0 |
1 |
6 |
| A stylized applied energy-economy model for France |
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0 |
2 |
104 |
1 |
2 |
8 |
267 |
| Abatement technology adoption under uncertainty |
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0 |
0 |
0 |
0 |
0 |
0 |
5 |
| Abatement technology adoption under uncertainty |
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0 |
0 |
0 |
0 |
0 |
1 |
32 |
| Abatement technology adoption under uncertainty |
0 |
0 |
0 |
0 |
1 |
2 |
3 |
11 |
| Analyse économique des politiques environnementales |
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0 |
0 |
0 |
0 |
0 |
1 |
19 |
| Benefit-Cost Analysis for Climate Action |
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0 |
0 |
1 |
0 |
1 |
4 |
12 |
| Benefit-Cost Analysis for Climate Action |
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0 |
0 |
0 |
0 |
2 |
7 |
29 |
| Carbon tax and OPEC's rents under a ceiling constraint |
0 |
0 |
0 |
4 |
0 |
0 |
2 |
16 |
| Carbon tax and OPEC's rents under a ceiling constraint |
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0 |
0 |
2 |
0 |
0 |
0 |
6 |
| Carbon tax and OPEC's rents under a ceiling constraint |
0 |
0 |
0 |
11 |
0 |
0 |
1 |
39 |
| Chosen Energy Sufficiency: Preference Shocks and Behavioural Biases |
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0 |
0 |
0 |
0 |
0 |
0 |
0 |
| Chosen Energy Sufficiency: Preference Shocks and Behavioural Biases |
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0 |
0 |
0 |
0 |
0 |
0 |
0 |
| Comment concilier développement économique et environnement ? |
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0 |
0 |
0 |
0 |
2 |
5 |
48 |
| Commerce et climat: pour une réconciliation |
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0 |
0 |
1 |
0 |
0 |
1 |
10 |
| Commerce et climat: pour une réconciliation |
0 |
0 |
0 |
27 |
0 |
1 |
2 |
64 |
| Confronting the Carbon Pricing Gap: Second Best Climate Policy |
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0 |
0 |
0 |
0 |
0 |
3 |
8 |
| Confronting the Carbon Pricing Gap: Second Best Climate Policy |
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0 |
0 |
0 |
0 |
0 |
0 |
0 |
| Confronting the Carbon Pricing Gap: Second Best Climate Policy |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
| Confronting the Carbon Pricing Gap: Second Best Climate Policy |
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2 |
3 |
53 |
1 |
3 |
8 |
49 |
| Confronting the carbon pricing gap: Second best climate policy |
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0 |
2 |
8 |
0 |
0 |
2 |
12 |
| Confronting the carbon pricing gap: Second best climate policy |
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1 |
5 |
17 |
0 |
1 |
21 |
39 |
| Consumer preferences, aquaculture technology and the sustainability of fisheries |
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0 |
2 |
32 |
0 |
0 |
2 |
103 |
| Cost-Benefit Analysis For Climate Action |
1 |
4 |
11 |
13 |
1 |
7 |
23 |
30 |
| Critical raw materials for the energy transition |
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0 |
2 |
5 |
1 |
3 |
12 |
26 |
| Critical raw materials for the energy transition |
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0 |
0 |
0 |
0 |
0 |
0 |
0 |
| Critical raw materials for the energy transition |
1 |
1 |
2 |
2 |
1 |
1 |
5 |
7 |
| Critical raw materials for the energy transition |
0 |
0 |
0 |
18 |
0 |
0 |
1 |
15 |
| Critical raw materials for the energy transition |
0 |
1 |
1 |
17 |
0 |
1 |
4 |
35 |
| Demo-economic equilibria when childbearing age is endogenous |
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0 |
0 |
85 |
0 |
2 |
3 |
164 |
| Demographic-economic equilibria when the age at motherhood is endogenous |
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0 |
1 |
85 |
0 |
0 |
3 |
204 |
| Demographic-economic equilibria when the age at motherhood is endogenous |
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0 |
0 |
0 |
0 |
0 |
2 |
8 |
| Demographic-economic equilibria when the age at motherhood is endogenous |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
11 |
| Eléments sur l'actualisation et l'environnement |
0 |
0 |
0 |
32 |
0 |
0 |
1 |
221 |
| Eléments sur l'actualisation et l'environnement |
0 |
0 |
0 |
16 |
0 |
0 |
0 |
106 |
| Eléments sur l’actualisation et l’environnement |
0 |
0 |
0 |
14 |
0 |
0 |
3 |
71 |
| Energy Transition with Variable and Intermittent Renewable Electricity Generation |
1 |
1 |
7 |
135 |
2 |
6 |
24 |
340 |
| Gouverner. Un enjeu essentiel |
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0 |
0 |
0 |
2 |
4 |
5 |
5 |
| Gouverner. Un enjeu essentiel |
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0 |
0 |
0 |
3 |
4 |
4 |
4 |
| Gouverner. Un enjeu essentiel |
0 |
0 |
0 |
0 |
2 |
5 |
5 |
5 |
| Growth, Environment and Uncertain Future Preferences |
0 |
0 |
0 |
39 |
0 |
1 |
2 |
117 |
| Growth, Environment and Uncertain Future Preferences |
0 |
0 |
0 |
7 |
0 |
0 |
0 |
18 |
| Growth, Environment and Uncertain Future Preferences |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
442 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
7 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
7 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
36 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
26 |
0 |
0 |
1 |
93 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
14 |
0 |
0 |
1 |
32 |
| Hartwick's rule and maximin paths when the exhaustible resource has an amenity value |
0 |
0 |
0 |
88 |
0 |
0 |
1 |
319 |
| How important are uncertainty and dynamics for environmental and climate policy? Some analytics |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
33 |
| How important are uncertainty and dynamics for environmental and climate policy? Some analytics |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
18 |
| How long can excess pollution persist? The non-cooperative case |
0 |
0 |
0 |
4 |
0 |
0 |
8 |
34 |
| How long can excess pollution persist? The non-cooperative case |
0 |
0 |
0 |
20 |
0 |
1 |
2 |
78 |
| How to Get the Blanchard-Kahn Form from a General Linear Rational Expectations Model |
0 |
0 |
0 |
790 |
0 |
0 |
0 |
1,881 |
| How to get the Blanchard-Kahn form from a general linear rational expectations model |
1 |
1 |
3 |
28 |
1 |
1 |
8 |
87 |
| International Emissions Trading Scheme and European Emissions Trading Scheme: What Linkages? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
5 |
| International Emissions Trading Scheme and European Emissions Trading Scheme: What Linkages? |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
24 |
| International Emissions Trading Scheme and European Emissions Trading Scheme: what linkages ? |
0 |
0 |
0 |
14 |
0 |
2 |
3 |
61 |
| International Emissions Trading Scheme and European Emissions Trading Scheme: what linkages ? |
0 |
0 |
0 |
9 |
0 |
1 |
1 |
45 |
| International Emissions Trading Scheme and European Emissions Trading Scheme: what linkages? |
0 |
0 |
0 |
134 |
0 |
0 |
0 |
402 |
| International Emissions Trading Scheme and European Emissions TradingScheme: what linkages? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
| International Emissions Trading Scheme and European Emissions TradingScheme: what linkages? |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
16 |
| Intertemporal emission permits trading under uncertainty and irreversibility |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
23 |
| Intertemporal emission permits trading under uncertainty and irreversibility |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
7 |
| Is aquaculture really an option? |
0 |
0 |
0 |
18 |
0 |
0 |
0 |
12 |
| Is aquaculture really an option? |
0 |
0 |
0 |
37 |
0 |
1 |
1 |
81 |
| Is shale gas a good bridge to renewables? An application to Europe |
0 |
0 |
0 |
0 |
0 |
2 |
3 |
27 |
| Is shale gas a good bridge to renewables? An application to Europe |
0 |
0 |
0 |
0 |
0 |
1 |
3 |
99 |
| La France peut-elle atteindre l'objectif du Facteur 4 ? Une évaluation à l'aide d'un modèle stylisé énergie-économie |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
9 |
| La France peut-elle atteindre l'objectif du Facteur 4 ? Une évaluation à l'aide d'un modèle stylisé énergie-économie |
0 |
0 |
0 |
0 |
0 |
2 |
2 |
10 |
| La France peut-elle atteindre l’objectif du Facteur 4 ? Une évaluation à l’aide d’un modèle stylisé énergie-économie |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
11 |
| La France peut-elle atteindre l’objectif du Facteur 4 ? Une évaluation à l’aide d’un modèle stylisé énergie-économie |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
10 |
| La croissance optimale d'une economie polluante: durabilite economique versus durabilite ecologique |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
462 |
| La hausse de la fiscalité carbone devra revenir dans le débat public |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
62 |
| La politique optimale de séquestration du carbone par les sols agricoles en France |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
5 |
| La politique optimale de séquestration du carbone par les sols agricoles en France |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
20 |
| La politique optimale de séquestration du carbone par les sols agricoles en France |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
| La taxation de l'énergie |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
32 |
| La taxation de l'énergie |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
13 |
| La taxe carbone doit-elle être la même dans tous les pays ? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
| La taxe carbone doit-elle être la même dans tous les pays ? |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
5 |
| La taxe carbone doit-elle être la même dans tous les pays ? |
0 |
0 |
0 |
0 |
0 |
1 |
2 |
7 |
| La transition énergétique: objectif ZEN |
0 |
0 |
0 |
0 |
1 |
6 |
21 |
98 |
| La transition énergétique: objectif ZEN |
0 |
0 |
0 |
0 |
0 |
2 |
2 |
33 |
| Le concept d'épargne véritable est-il adapté pour mesurer la durabilité du développement économique ? |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
7 |
| Le concept d'épargne véritable est-il adapté pour mesurer la durabilité du développement économique ? |
0 |
0 |
0 |
0 |
1 |
2 |
4 |
23 |
| Le concept d'épargne véritable est-il adapté pour mesurer la durabilité du développement économique ? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
7 |
| Macroeconomics and the environment |
0 |
0 |
0 |
0 |
0 |
1 |
3 |
15 |
| Macroeconomics and the environment |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
34 |
| More Gas, Less Coal, and Less CO2? Unilateral CO2 Reduction Policy with More than One Carbon Energy Source |
0 |
0 |
0 |
57 |
1 |
1 |
1 |
73 |
| More Gas, Less Coal, and Less CO2? Unilateral CO2 Reduction Policy with More than One Carbon Energy Source |
0 |
0 |
0 |
36 |
1 |
2 |
2 |
83 |
| Optimal Use of a Polluting Non-Renewable Resource Generating both Manageable and Catastrophic Damages |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
25 |
| Optimal Use of a Polluting Non-Renewable Resource Generating both Manageable and Catastrophic Damages |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
| Optimal Use of a Polluting Non-Renewable Resource Generating both Manageable and Catastrophic Damages |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
4 |
| Optimal energy transition with variable and intermittent renewable electricity generation |
0 |
0 |
2 |
5 |
0 |
0 |
8 |
18 |
| Optimal energy transition with variable and intermittent renewable electricity generation |
0 |
0 |
2 |
2 |
0 |
0 |
6 |
10 |
| Optimal use of a polluting non renewable resource generating both manageable and catastrophic damages |
0 |
0 |
1 |
24 |
0 |
0 |
2 |
107 |
| Pour la taxe carbone. La politique économique face à la menace climatique |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
68 |
| Pour la taxe carbone. La politique économique face à la menace climatique |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
9 |
| Pour le climat: une taxe juste, pas juste une taxe |
0 |
0 |
0 |
0 |
0 |
2 |
5 |
45 |
| Prevention And Mitigation Of Epidemics: Biodiversity Conservation And Confinement Policies |
0 |
0 |
0 |
5 |
0 |
0 |
1 |
26 |
| Prevention and Mitigation of Epidemics: Biodiversity Conservation and Confinement Policies |
0 |
0 |
0 |
12 |
0 |
0 |
1 |
49 |
| Prevention and Mitigation of Epidemics: Biodiversity Conservation and Confinement Policies |
0 |
0 |
0 |
6 |
0 |
0 |
1 |
5 |
| Prevention and Mitigation of Epidemics: Biodiversity Conservation and Confinement Policies |
0 |
0 |
0 |
2 |
0 |
0 |
1 |
10 |
| Prevention and mitigation of epidemics:Biodiversity conservation and confinement policies |
0 |
0 |
0 |
1 |
0 |
0 |
1 |
19 |
| Prevention and mitigation of epidemics:Biodiversity conservation and confinement policies |
0 |
0 |
0 |
6 |
0 |
0 |
2 |
40 |
| Ressources renouvelables et incertitude sur lespréférences des générations futures |
0 |
0 |
0 |
32 |
0 |
2 |
2 |
113 |
| Ressources renouvelables et incertitude sur lespréférences des générations futures |
0 |
0 |
0 |
12 |
0 |
0 |
1 |
28 |
| Should the Carbon Price Be the Same in All Countries? |
0 |
0 |
1 |
40 |
0 |
0 |
1 |
12 |
| Should the Carbon Price Be the Same in All Countries? |
0 |
0 |
1 |
1 |
0 |
1 |
2 |
8 |
| Should the Carbon Price Be the Same in All Countries? |
0 |
0 |
0 |
43 |
0 |
0 |
1 |
21 |
| Should the carbon price be the same in all countries ? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
7 |
| Should the carbon price be the same in all countries ? |
0 |
0 |
0 |
46 |
0 |
0 |
0 |
132 |
| Should the carbon price be the same in all countries? |
0 |
0 |
0 |
44 |
0 |
0 |
1 |
185 |
| Should we extract the European shale gas? The effect of climate and financial constraints |
0 |
0 |
0 |
33 |
0 |
0 |
1 |
7 |
| Should we extract the European shale gas? The effect of climate and financial constraints |
0 |
0 |
1 |
39 |
0 |
0 |
1 |
82 |
| Should we extract the European shale gas? The effect of climate and financial constraints |
0 |
0 |
0 |
63 |
0 |
1 |
2 |
73 |
| Special Issue on Environmental and Natural Resource Economics: Introduction |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
7 |
| Special Issue on Environmental and Natural Resource Economics: Introduction |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
23 |
| Special Issue on Environmental and Natural Resource Economics: Introduction |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
8 |
| The Direction of Technological Change on Renewable or Non-Renewable Resource Exploitation: The Implication of Bounded Efficiency Improvements |
0 |
0 |
0 |
11 |
0 |
0 |
0 |
31 |
| The Direction of Technological Change on Renewable or Non-Renewable Resource Exploitation: The Implication of Bounded Efficiency Improvements |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
8 |
| The Economics of Border Carbon Adjustment: Rationale and Impacts of Compensating for Carbon at the Border |
0 |
0 |
0 |
2 |
1 |
3 |
10 |
28 |
| The Economics of Border Carbon Adjustment: Rationale and Impacts of Compensating for Carbon at the Border |
0 |
0 |
0 |
0 |
0 |
2 |
4 |
18 |
| The Energy Transition Agenda: An Economic Perspective |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
3 |
| The Energy Transition Agenda: An Economic Perspective |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
2 |
| The Value of Biodiversity as an Insurance Device |
0 |
0 |
0 |
24 |
0 |
0 |
2 |
27 |
| The Value of Biodiversity as an Insurance Device |
0 |
0 |
0 |
0 |
0 |
1 |
2 |
13 |
| The Value of Biodiversity as an Insurance Device |
0 |
0 |
0 |
2 |
0 |
0 |
3 |
35 |
| The Value of Biodiversity as an Insurance Device |
0 |
0 |
3 |
79 |
0 |
0 |
4 |
198 |
| The Zero Discounting and Maximin Optimal Paths in a Simple Model of Global Warming |
0 |
0 |
0 |
40 |
0 |
1 |
1 |
119 |
| The Zero Discounting and Maximin Optimal Paths in a Simple Model of Global Warming |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
9 |
| The Zero Discounting and Maximin Optimal Paths in a Simple Model of Global Warming |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
12 |
| The Zero discounting and maximin optimal paths in a simple model of global warming |
0 |
0 |
0 |
13 |
0 |
0 |
1 |
16 |
| The Zero discounting and maximin optimal paths in a simple model of global warming |
0 |
0 |
0 |
38 |
0 |
0 |
0 |
99 |
| The optimal carbon sequestration in agricultural soils: Do the dynamics of the physical process matter? |
0 |
0 |
0 |
1 |
0 |
2 |
2 |
32 |
| The optimal carbon sequestration in agricultural soils: Do the dynamics of the physical process matter? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
39 |
| The optimal carbon sequestration in agricultural soils: Do the dynamics of the physical process matter? |
0 |
0 |
0 |
0 |
0 |
2 |
2 |
29 |
| The optimal carbon sequestration in agricultural soils: does the dynamics of the physical process matter? |
0 |
0 |
0 |
16 |
0 |
2 |
3 |
64 |
| The optimal carbon sequestration in agricultural soils: does the dynamics of the physical process matter? |
0 |
0 |
0 |
76 |
0 |
0 |
1 |
391 |
| The optimal carbon sequestration in agricultural soils: does the dynamics of the physical process matter? |
0 |
0 |
0 |
8 |
1 |
1 |
1 |
66 |
| The value of biodiversity as an insurance device |
0 |
0 |
0 |
11 |
0 |
1 |
5 |
65 |
| The value of biodiversity as an insurance device |
0 |
0 |
0 |
29 |
0 |
0 |
1 |
35 |
| The value of biodiversity as an insurance device |
0 |
0 |
0 |
30 |
0 |
0 |
2 |
53 |
| The zero discounting and maximin optimal paths in a simple model of global warming |
0 |
0 |
1 |
57 |
0 |
1 |
3 |
169 |
| To What Extent Is Aquaculture Socially Beneficial? A Theoretical Analysis |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
| To What Extent Is Aquaculture Socially Beneficial? A Theoretical Analysis |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
37 |
| To What Extent Is Aquaculture Socially Beneficial? A Theoretical Analysis |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
8 |
| Trade and Climate: Towards Reconciliation |
0 |
0 |
0 |
28 |
0 |
0 |
1 |
38 |
| Trade and Climate: Towards Reconciliation |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
8 |
| Trade and Climate: Towards Reconciliation |
0 |
0 |
0 |
2 |
0 |
1 |
1 |
7 |
| Unilateral CO2 Reduction Policy with More Than One Carbon Energy Source |
0 |
0 |
1 |
33 |
0 |
1 |
3 |
69 |
| Unilateral CO2 Reduction Policy with More Than One Carbon Energy Source |
0 |
0 |
2 |
10 |
0 |
0 |
3 |
11 |
| Unilateral CO2 Reduction Policy with More Than One Carbon Energy Source |
0 |
0 |
1 |
9 |
0 |
0 |
2 |
10 |
| Volatility-Reducing Biodiversity Conservation Under Strategic Interactions |
0 |
0 |
0 |
44 |
1 |
1 |
4 |
62 |
| Volatility-reducing biodiversity conservation under strategic interactions |
0 |
0 |
0 |
3 |
0 |
1 |
3 |
12 |
| Volatility-reducing biodiversity conservation under strategic interactions |
0 |
0 |
0 |
4 |
1 |
1 |
3 |
17 |
| Volatility-reducing biodiversity conservation under strategic interactions |
0 |
0 |
0 |
7 |
1 |
1 |
3 |
16 |
| With Exhaustible Resources, Can A Developing Country Escape From The Poverty Trap? |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
7 |
| With Exhaustible Resources, Can A Developing Country Escape From The Poverty Trap? |
0 |
0 |
0 |
68 |
0 |
1 |
1 |
296 |
| With Exhaustible Resources, Can A Developing Country Escape From The Poverty Trap? |
0 |
0 |
0 |
70 |
0 |
0 |
0 |
123 |
| With Exhaustible Resources, Can A Developing Country Escape From The Poverty Trap? |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
6 |
| With exhaustible resources, can a developing country escape from the poverty trap? |
0 |
0 |
0 |
21 |
0 |
0 |
0 |
101 |
| With exhaustible resources, can a developing country escape from the poverty trap? |
0 |
0 |
0 |
95 |
0 |
0 |
1 |
535 |
| With exhaustible resources, can a developing country escape from the poverty trap? |
0 |
0 |
0 |
11 |
0 |
0 |
0 |
38 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
1 |
0 |
1 |
2 |
7 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
0 |
0 |
0 |
2 |
8 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
48 |
0 |
1 |
2 |
173 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
1 |
0 |
1 |
4 |
36 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
34 |
0 |
0 |
1 |
84 |
| Zero discounting and optimal paths of depletion of an exhaustible resource with an amenity value |
0 |
0 |
0 |
7 |
0 |
0 |
2 |
9 |
| Économie de l'environnement et des ressources naturelles: présentation générale |
0 |
0 |
0 |
0 |
1 |
1 |
1 |
40 |
| Économie de l'environnement et des ressources naturelles: présentation générale |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
5 |
| Économie de l'environnement et des ressources naturelles: présentation générale |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
7 |
| Total Working Papers |
5 |
11 |
57 |
3,600 |
26 |
123 |
407 |
12,528 |
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