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Measuring Clean Technologies at
the Firm Level
Damien Dussaux (PSL Mines ParisTech Cerna)
OECD Workshop
« Combining economic and environmental microdata »
Paris, July 10/11
Why is it important?
o Evaluating environmental policies
 Long run effect on competitiveness (Green race and first mover
advantage)
 Clean Air Act’s Best Available Control Technology
o Analyse diffusion of clean technologies
 Trade policies
 Intellectual Property Right
o Evaluating innovation policy
 Ademe finance clean investments via Programme d’Investissements
d’Avenir
 Bpifrance finance SMEs via Fonds Ecotechnologies or Prêt Vert
Typology of indicators
1. Innovation in clean technologies
o Patents in clean technologies (PATSTAT)
o Introduction of material or energy saving innovation (CIS)
2. Adoption of clean technologies
o Pollution Abatement Cost and Expenditure (Antipol)
o Investment in energy efficiency (Insee)
3. Consequences of technology adoption
o Total Factor Productivity and Material productivity
o Energy intensity and Pollution intensity
o Green goods and services
Community Innovation Survey (CIS)
o Conducted in several European countries:
 1997, 2001, 2005, 2007, 2009, 2011, 2013, 2015
 Industry, wholesale, transport, some services.
o Stratified (activity, size) sample of 20,000 French firms >=
10
o Set of questions evolve
o Some surveys include questions regarding the importance
of:
 material saving innovations
 pollution abatement
 labour saving innovations and others
o For all waves, firms can answer
1. not relevant,
Weak panel
structure
Discrete
Choice Model
Fixed-effects
not feasible
CIS panel structure
Number of
years
available
Number
of firms
Percentage
1 58,713 70%
2 15,723 19%
3 5,046 6%
4 2,032 2%
5 1,092 1%
6 554 < 1%
7 424 < 1%
8 228 < 1%
Only a few firms
are sampled
several years
Almost no
panel
structure
Source: French CIS, manufacturing.
Variable Obs Mean Std. Dev. Min Max
Process innovation (0/1) 20,856 0.95 0.2 0 1
Product innovation (0/1) 15,666 0.98 0.1 0 1
Material saving 46,177 0.96 1.1 0 3
Labour saving 33,491 1.5 1.2 0 3
Flexibility 51,344 1.7 1.1 0 3
Environmental impacts 46,179 1.0 1.1 0 3
Market share increase 33,534 2.2 1.0 0 3
Range of products 33,532 2.2 1.0 0 3
Quality improvement 33,493 2.2 1.0 0 3
CIS summary statistics
Source: French CIS, manufacturing
Discrete Choice Model Estimations are
biased
o « Fixed-effects » Probit
 Inclusion of dummy variables for each unit
 Incidental parameters problem  persistent bias
decreasing in T (Neyman and Scott, 1948)
o Solutions exist but require good panel structure
 Conditional MLE in the binary logit model is a solution
(Chamberlain, Review of Economic Studie, 1980)
 Carro (Journal of Econometrics, 2007)’s Modified MLE
reduces bias from O(1/T) to O(1/T²)
Pollution Abatement Cost and
Expenditure (PACE)
o Antipol (Insee) survey asks plants (siret) about their investment in capital
or knowledge to protect the environment:
 Waste water, air pollution, solid waste,
 Noise, Soil, Biodiversity,
 Energy efficiency not covered
o Around 11,000 industrial plants sampled yearly:
o all plants ≥ 250 employees surveyed
o plants between 20 and 249 employees randomly sampled
o Sampled stratified on economic activity and size
o 80% of the plants respond
o Current expenditure are collected every 3 year since 2004
o Distinction between end of pipe and integrated technologies
Antipol panel structure
Number of
years available
Number
of firms
Percentage
1 10,980 27%
2 6,720 17%
3 4,662 12%
4 4,554 11%
5 2,528 6%
6 2,039 5%
7 1,402 3%
8 1,101 3%
9 952 2%
10 750 2%
Etc…
Only a few plants
are sampled
several years
Weak
panel
structure
Source: Antipol
Variable Obs Mean Std. Dev. Min Max
Capital expenditure 131,222 238 1,775 0 295,292
End of pipe investment 131,335 197 1,599 0 295,292
Integrated investment 131,261 41 621 0 82,000
End of pipe – Air 105,677 41 475 0 37,896
Integrated – Air 92,735 18 278 0 37,383
End of pipe – Solid
waste
105,987 19 280 0 63,745
Integrated – Solid waste 91,943 2 39 0 4,373
Current expenditure 9,516 284 1,351 0 79,541
Environmental tax paid 17,621 148 730 0 54,805
Antipol summary statistics
Source: French Antipol. Thousand
euros.
Variable Obs Mean Std. Dev. Min Max
Capital expenditure 131,222 238 1,775 0 295,292
End of pipe investment 131,335 197 1,599 0 295,292
Integrated investment 131,261 41 621 0 82,000
End of pipe – Air 105,677 41 475 0 37,896
Integrated – Air 92,735 18 278 0 37,383
End of pipe – Solid
waste
105,987 19 280 0 63,745
Integrated – Solid waste 91,943 2 39 0 4,373
Current expenditure 9,516 284 1,351 0 79,541
Environmental tax paid 17,621 148 730 0 54,805
Antipol summary statistics
Source: French Antipol. Thousand
euros.
From plants to firm-level
o Antipol data and EACEI data are at the plant level
o But most economic performance indicators are at the firm level
o Also, some decisions are taken at the level of the firm
o Several ways to reconcile the datasets:
 Aggregate plant data at the firm level using employment data and merge at the
firm level
 Compute RHS that are weighted average of plant-level variables where the
weights are the plants’ share of total employees
o Within-firm reallocations are important
 Is the policy generating net employment loss or reallocation within firms?
 A good panel structure is key to do that
Firm-Level Productivity
o Estimation of production function
o 𝑦𝑖𝑡 = 𝛼𝑙 𝑙𝑖𝑡 + 𝛼 𝑘 𝑘𝑖𝑡 + 𝛼 𝑚 𝑚𝑖𝑡 + 𝜇𝑖 + 𝛿𝑡 + 𝜔𝑖𝑡 + 𝜖𝑖𝑡
o 𝜔𝑖𝑡 is Total Factor Productivity
o 𝑦𝑖𝑡 is logged output usually measured by turnover
 𝜔𝑖𝑡 is contaminated by firms mark-up  key to understand policy impacts
 Physical quantity allows to distinguish technological change from market
power
 But firms are multi-products
 Quality ?
o Material physical quantity are not available either  material
Conclusion
o Getting better but some problems remain important
o Inconsistency in the units sampled generate problems for econometric
estimations but also for aggregate analyses (output and employment
reallocation, firms entry and exit)
o Continuous measures are needed to use good models
o Some dimensions are still absent :
 R&D in green technologies,
 investment in energy efficient technologies,
 material and output physical quantities.
oEnvironmental policies can be tricky to measure e.g. (i) numerous
exemptions for fossil fuel tax (ii) direct R&D subsidies

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Measuring the Impact of Clean Technologies Using French Firm-Level Data

  • 1. Measuring Clean Technologies at the Firm Level Damien Dussaux (PSL Mines ParisTech Cerna) OECD Workshop « Combining economic and environmental microdata » Paris, July 10/11
  • 2. Why is it important? o Evaluating environmental policies  Long run effect on competitiveness (Green race and first mover advantage)  Clean Air Act’s Best Available Control Technology o Analyse diffusion of clean technologies  Trade policies  Intellectual Property Right o Evaluating innovation policy  Ademe finance clean investments via Programme d’Investissements d’Avenir  Bpifrance finance SMEs via Fonds Ecotechnologies or Prêt Vert
  • 3. Typology of indicators 1. Innovation in clean technologies o Patents in clean technologies (PATSTAT) o Introduction of material or energy saving innovation (CIS) 2. Adoption of clean technologies o Pollution Abatement Cost and Expenditure (Antipol) o Investment in energy efficiency (Insee) 3. Consequences of technology adoption o Total Factor Productivity and Material productivity o Energy intensity and Pollution intensity o Green goods and services
  • 4. Community Innovation Survey (CIS) o Conducted in several European countries:  1997, 2001, 2005, 2007, 2009, 2011, 2013, 2015  Industry, wholesale, transport, some services. o Stratified (activity, size) sample of 20,000 French firms >= 10 o Set of questions evolve o Some surveys include questions regarding the importance of:  material saving innovations  pollution abatement  labour saving innovations and others o For all waves, firms can answer 1. not relevant, Weak panel structure Discrete Choice Model Fixed-effects not feasible
  • 5. CIS panel structure Number of years available Number of firms Percentage 1 58,713 70% 2 15,723 19% 3 5,046 6% 4 2,032 2% 5 1,092 1% 6 554 < 1% 7 424 < 1% 8 228 < 1% Only a few firms are sampled several years Almost no panel structure Source: French CIS, manufacturing.
  • 6. Variable Obs Mean Std. Dev. Min Max Process innovation (0/1) 20,856 0.95 0.2 0 1 Product innovation (0/1) 15,666 0.98 0.1 0 1 Material saving 46,177 0.96 1.1 0 3 Labour saving 33,491 1.5 1.2 0 3 Flexibility 51,344 1.7 1.1 0 3 Environmental impacts 46,179 1.0 1.1 0 3 Market share increase 33,534 2.2 1.0 0 3 Range of products 33,532 2.2 1.0 0 3 Quality improvement 33,493 2.2 1.0 0 3 CIS summary statistics Source: French CIS, manufacturing
  • 7. Discrete Choice Model Estimations are biased o « Fixed-effects » Probit  Inclusion of dummy variables for each unit  Incidental parameters problem  persistent bias decreasing in T (Neyman and Scott, 1948) o Solutions exist but require good panel structure  Conditional MLE in the binary logit model is a solution (Chamberlain, Review of Economic Studie, 1980)  Carro (Journal of Econometrics, 2007)’s Modified MLE reduces bias from O(1/T) to O(1/T²)
  • 8. Pollution Abatement Cost and Expenditure (PACE) o Antipol (Insee) survey asks plants (siret) about their investment in capital or knowledge to protect the environment:  Waste water, air pollution, solid waste,  Noise, Soil, Biodiversity,  Energy efficiency not covered o Around 11,000 industrial plants sampled yearly: o all plants ≥ 250 employees surveyed o plants between 20 and 249 employees randomly sampled o Sampled stratified on economic activity and size o 80% of the plants respond o Current expenditure are collected every 3 year since 2004 o Distinction between end of pipe and integrated technologies
  • 9. Antipol panel structure Number of years available Number of firms Percentage 1 10,980 27% 2 6,720 17% 3 4,662 12% 4 4,554 11% 5 2,528 6% 6 2,039 5% 7 1,402 3% 8 1,101 3% 9 952 2% 10 750 2% Etc… Only a few plants are sampled several years Weak panel structure Source: Antipol
  • 10. Variable Obs Mean Std. Dev. Min Max Capital expenditure 131,222 238 1,775 0 295,292 End of pipe investment 131,335 197 1,599 0 295,292 Integrated investment 131,261 41 621 0 82,000 End of pipe – Air 105,677 41 475 0 37,896 Integrated – Air 92,735 18 278 0 37,383 End of pipe – Solid waste 105,987 19 280 0 63,745 Integrated – Solid waste 91,943 2 39 0 4,373 Current expenditure 9,516 284 1,351 0 79,541 Environmental tax paid 17,621 148 730 0 54,805 Antipol summary statistics Source: French Antipol. Thousand euros.
  • 11. Variable Obs Mean Std. Dev. Min Max Capital expenditure 131,222 238 1,775 0 295,292 End of pipe investment 131,335 197 1,599 0 295,292 Integrated investment 131,261 41 621 0 82,000 End of pipe – Air 105,677 41 475 0 37,896 Integrated – Air 92,735 18 278 0 37,383 End of pipe – Solid waste 105,987 19 280 0 63,745 Integrated – Solid waste 91,943 2 39 0 4,373 Current expenditure 9,516 284 1,351 0 79,541 Environmental tax paid 17,621 148 730 0 54,805 Antipol summary statistics Source: French Antipol. Thousand euros.
  • 12. From plants to firm-level o Antipol data and EACEI data are at the plant level o But most economic performance indicators are at the firm level o Also, some decisions are taken at the level of the firm o Several ways to reconcile the datasets:  Aggregate plant data at the firm level using employment data and merge at the firm level  Compute RHS that are weighted average of plant-level variables where the weights are the plants’ share of total employees o Within-firm reallocations are important  Is the policy generating net employment loss or reallocation within firms?  A good panel structure is key to do that
  • 13. Firm-Level Productivity o Estimation of production function o 𝑦𝑖𝑡 = 𝛼𝑙 𝑙𝑖𝑡 + 𝛼 𝑘 𝑘𝑖𝑡 + 𝛼 𝑚 𝑚𝑖𝑡 + 𝜇𝑖 + 𝛿𝑡 + 𝜔𝑖𝑡 + 𝜖𝑖𝑡 o 𝜔𝑖𝑡 is Total Factor Productivity o 𝑦𝑖𝑡 is logged output usually measured by turnover  𝜔𝑖𝑡 is contaminated by firms mark-up  key to understand policy impacts  Physical quantity allows to distinguish technological change from market power  But firms are multi-products  Quality ? o Material physical quantity are not available either  material
  • 14. Conclusion o Getting better but some problems remain important o Inconsistency in the units sampled generate problems for econometric estimations but also for aggregate analyses (output and employment reallocation, firms entry and exit) o Continuous measures are needed to use good models o Some dimensions are still absent :  R&D in green technologies,  investment in energy efficient technologies,  material and output physical quantities. oEnvironmental policies can be tricky to measure e.g. (i) numerous exemptions for fossil fuel tax (ii) direct R&D subsidies