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Jonathan D. Libber
Jlibber Consulting


   December 7, 2011



                      1
   Worked for 31 years in U.S. EPA’s
    enforcement program
   Godfather of the Models
   Contact information
    ◦ (410) 358-4616
    ◦ jlibberconsulting@gmail.com
    ◦ www.Jlibberconsulting.wordpress.com




                                            2
1.   Overview of EPA’s Civil Penalty
     Approach
2.   Calculating the Economic Benefit
     Component of Penalties
3.   Calculating the Gravity (Seriousness) of
     the Violation Component of Penalties
4.   Actual BEN Model Calculation: The
     DUDE Case (If Time Permits)

                                                3
 Overview of
 EPA’s Civil
 Penalty
 Approach



                4
 EPA’s response must:
 ◦ Deter violators from repeated
   noncompliance
 ◦ Deter similarly situated
   regulatees from violating the law



                                       5
Deterrence




             Always Comply
             Noncompliers
             Rest of Companies




                                 6
 Revocation of an environmental permit
 Temporary or permanent closure
 Fines and Penalties
  ◦ Note that only with fines can you
    adjust the sanction to fit the
    violation. The rest are all or nothing
 To ensure consistency and
  assessment of appropriate
  penalties, EPA has adopted penalty
  guidance
 Agency issued generic penalty policy
  in 1984
 All subsequent penalty guidance
  follows the approach laid out in that
  policy.
                                          8
 Three  step process
 ◦ Calculate economic savings
 ◦ Calculate seriousness (gravity) of
   the violation
 ◦ Apply adjustment factors



                                        9
   Cornerstone of EPA’s approach is to
    recapture savings gained from delayed or
    avoided compliance
   Law-abiding entities should not be placed
    at a competitive disadvantage with
    competitors that fail to comply
    ◦ Approach is totally generic. It applies
      whenever the violator saves money by
      violating the law.

                                                10
Calculating the
Economic Benefit
Component of
Penalties


                   11
   Three types of economic benefit
    ◦ Benefit from delayed costs (e.g. installs
      the equipment 2 years late)
      All the money will get spent, but two years
       late.
      Violator has had the use of that money for
       two years.
      In a very simple sense, the benefit is based
       on the interest alone, not the principle



                                                      12
   Benefit from avoided costs (e.g. skips all the
    operation and maintenance expense on that
    equipment for those two years)
       None of the operation and maintenance
        money is going to get spent until the firm is
        finally in compliance. None of it is delayed.
       In a very simplistic sense, we are seeking both
        the principle and the interest.



                                                          13
   Benefit from an illegal competitive advantage
    or illegal profits (e.g. selling banned pesticides
    to pesticide applicators on the black market)
       There are no delayed or avoided costs associated
        with smuggling DDT into New York City.
       It is like selling cocaine on the street corner
       The essence of this type of benefit is that there is
        no way to make this money other than violating
        the law.
       With the BEN type benefit, the firm can make all
        the money it wants, but it just needs to do it in a
        clean way.


                                                               14
   BEN calculates the economic benefit of
    noncompliance with environmental
    requirements.
   Based on generally accepted financial
    principles.
   Uses default values for the more difficult to
    find parameters (tax rates, inflation rate
    and cost of capital).
    ◦ If violator furnishes its own reliable
      financial data, we use its data instead of
      ours.
   Very user-friendly model.

                                                    15
From 1975 to 1984, total national
penalties averaged $6 million per year
1985 (BEN’s first year) total was $22
million
1999 total was $167 million (record
high)
2008 total was $127 million
2009 total was $91 million
N.B. Other factors involved in
increase, but BEN at least facilitated the
increase in penalties
                                             16
   Required Inputs
    ◦ Case Name, Analyst’s Name, Agency Name
    ◦ Tax Status
    ◦ State
    ◦ Penalty Payment Date
    ◦ Run name
    ◦ Capital Investment
    ◦ One-time, nondepreciable expenditure
    ◦ Annual expenses
    ◦ Date of Noncompliance
    ◦ Date of Compliance


                                               17
   Optional Inputs (Model Provides Default
    Values for These Variables)
    ◦ Discount Rate
    ◦ Inflation Rate
    ◦ Useful Life of Equipment
    ◦ Deselect Tax Deductibility for One-Time
      Nondepreciable Cost
    ◦ Deselect “Delayed Not Avoided”
    ◦ Specific Cost Estimates


                                                18
 Judges have generally accepted the
  concept of benefit recapture.
 In almost all published decisions
  against for-profit entities, the judges
  have ordered recapture as long as the
  Agency, State or citizen group had a
  clear approach to calculating benefit.


                                            19
 Calculating   the
 Gravity
 (Seriousness) of
 the Violation
 Component of
 Penalties

                      20
- Factors   to Consider
 ◦ Actual or possible harm
 ◦ Importance to regulatory scheme
 ◦ Size of violator
 ◦ Duration of the violation




                                     21
 Factors   to Consider
 ◦ Degree of willfulness and/or
   negligence.
 ◦ Degree of
   cooperation/noncooperation.
 ◦ History of noncompliance.
 ◦ Ability to pay.
    Three other EPA computer models
     to evaluate such claims.
 ◦ Other unique factors.


                                       22
 ABEL,   INDIPAY and MUNIPAY
 ◦ Assess the ability to afford
   environmental expenditures of
   businesses, individuals and
   municipalities, respectively.




                                   23
 Actual   BEN
 Model
 Calculation: The
 DUDE Case



                    24
 Private dry-cleaning business (S-
  Corporation) was built before
  emissions requirements were in place.
 After standards were implemented
  (compliance required by January
  1, 2008), DUDE installed cheap fix
  piece of equipment that did not in any
  way reduce the emissions, at a cost of
  $50,000 on May 1, 2006.


                                           25
   Eventually EPA forced DUDE to comply by
    spending $750,000 on August 1, 2012.
    DUDE began to incur annual operating costs
    of $60,000 at this time. These figures
    come from a consultant’s report dated July
    2, 2011.
   DUDE will also be required to pay a penalty.
    Hearing to take place June 28, 2012.
    Penalty to be paid six months later.


                                                   26
   First Scenario
       Calculate the economic benefit
       that DUDE gained as a result of
       noncompliance, assuming a
       penalty payment date six
       months after the scheduled
       hearing.


                                         27
   Second Scenario
      Delora’s lawyer produces a
      document about the expenses
      associated with the installed
      equipment and expected useful life
      to argue that the useful life entry
      should be 20 years, not BEN’s 15-
      year standard value. Calculate the
      revised economic benefit.

                                            28
Results from BEN – First
 Scenario
- BEN calculates DUDE’s economic
  benefit to be $447,390.
- We do not give Delora credit for her
  initial “pollution control”
  expenditure of $50,000, because it
  appears unrelated to compliance.


                                         29
Results from BEN – Second
 Scenario
 The new economic benefit is
 $409,140, assuming a 20-year useful
 life. A longer useful life reduces the
 economic benefit, all other assumptions
 held constant.


                                           30
 Gracias




            31

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Penalties and benefit Chile

  • 1. Jonathan D. Libber Jlibber Consulting December 7, 2011 1
  • 2. Worked for 31 years in U.S. EPA’s enforcement program  Godfather of the Models  Contact information ◦ (410) 358-4616 ◦ jlibberconsulting@gmail.com ◦ www.Jlibberconsulting.wordpress.com 2
  • 3. 1. Overview of EPA’s Civil Penalty Approach 2. Calculating the Economic Benefit Component of Penalties 3. Calculating the Gravity (Seriousness) of the Violation Component of Penalties 4. Actual BEN Model Calculation: The DUDE Case (If Time Permits) 3
  • 4.  Overview of EPA’s Civil Penalty Approach 4
  • 5.  EPA’s response must: ◦ Deter violators from repeated noncompliance ◦ Deter similarly situated regulatees from violating the law 5
  • 6. Deterrence Always Comply Noncompliers Rest of Companies 6
  • 7.  Revocation of an environmental permit  Temporary or permanent closure  Fines and Penalties ◦ Note that only with fines can you adjust the sanction to fit the violation. The rest are all or nothing
  • 8.  To ensure consistency and assessment of appropriate penalties, EPA has adopted penalty guidance  Agency issued generic penalty policy in 1984  All subsequent penalty guidance follows the approach laid out in that policy. 8
  • 9.  Three step process ◦ Calculate economic savings ◦ Calculate seriousness (gravity) of the violation ◦ Apply adjustment factors 9
  • 10. Cornerstone of EPA’s approach is to recapture savings gained from delayed or avoided compliance  Law-abiding entities should not be placed at a competitive disadvantage with competitors that fail to comply ◦ Approach is totally generic. It applies whenever the violator saves money by violating the law. 10
  • 12. Three types of economic benefit ◦ Benefit from delayed costs (e.g. installs the equipment 2 years late)  All the money will get spent, but two years late.  Violator has had the use of that money for two years.  In a very simple sense, the benefit is based on the interest alone, not the principle 12
  • 13. Benefit from avoided costs (e.g. skips all the operation and maintenance expense on that equipment for those two years)  None of the operation and maintenance money is going to get spent until the firm is finally in compliance. None of it is delayed.  In a very simplistic sense, we are seeking both the principle and the interest. 13
  • 14. Benefit from an illegal competitive advantage or illegal profits (e.g. selling banned pesticides to pesticide applicators on the black market)  There are no delayed or avoided costs associated with smuggling DDT into New York City.  It is like selling cocaine on the street corner  The essence of this type of benefit is that there is no way to make this money other than violating the law.  With the BEN type benefit, the firm can make all the money it wants, but it just needs to do it in a clean way. 14
  • 15. BEN calculates the economic benefit of noncompliance with environmental requirements.  Based on generally accepted financial principles.  Uses default values for the more difficult to find parameters (tax rates, inflation rate and cost of capital). ◦ If violator furnishes its own reliable financial data, we use its data instead of ours.  Very user-friendly model. 15
  • 16. From 1975 to 1984, total national penalties averaged $6 million per year 1985 (BEN’s first year) total was $22 million 1999 total was $167 million (record high) 2008 total was $127 million 2009 total was $91 million N.B. Other factors involved in increase, but BEN at least facilitated the increase in penalties 16
  • 17. Required Inputs ◦ Case Name, Analyst’s Name, Agency Name ◦ Tax Status ◦ State ◦ Penalty Payment Date ◦ Run name ◦ Capital Investment ◦ One-time, nondepreciable expenditure ◦ Annual expenses ◦ Date of Noncompliance ◦ Date of Compliance 17
  • 18. Optional Inputs (Model Provides Default Values for These Variables) ◦ Discount Rate ◦ Inflation Rate ◦ Useful Life of Equipment ◦ Deselect Tax Deductibility for One-Time Nondepreciable Cost ◦ Deselect “Delayed Not Avoided” ◦ Specific Cost Estimates 18
  • 19.  Judges have generally accepted the concept of benefit recapture.  In almost all published decisions against for-profit entities, the judges have ordered recapture as long as the Agency, State or citizen group had a clear approach to calculating benefit. 19
  • 20.  Calculating the Gravity (Seriousness) of the Violation Component of Penalties 20
  • 21. - Factors to Consider ◦ Actual or possible harm ◦ Importance to regulatory scheme ◦ Size of violator ◦ Duration of the violation 21
  • 22.  Factors to Consider ◦ Degree of willfulness and/or negligence. ◦ Degree of cooperation/noncooperation. ◦ History of noncompliance. ◦ Ability to pay.  Three other EPA computer models to evaluate such claims. ◦ Other unique factors. 22
  • 23.  ABEL, INDIPAY and MUNIPAY ◦ Assess the ability to afford environmental expenditures of businesses, individuals and municipalities, respectively. 23
  • 24.  Actual BEN Model Calculation: The DUDE Case 24
  • 25.  Private dry-cleaning business (S- Corporation) was built before emissions requirements were in place.  After standards were implemented (compliance required by January 1, 2008), DUDE installed cheap fix piece of equipment that did not in any way reduce the emissions, at a cost of $50,000 on May 1, 2006. 25
  • 26. Eventually EPA forced DUDE to comply by spending $750,000 on August 1, 2012. DUDE began to incur annual operating costs of $60,000 at this time. These figures come from a consultant’s report dated July 2, 2011.  DUDE will also be required to pay a penalty. Hearing to take place June 28, 2012. Penalty to be paid six months later. 26
  • 27. First Scenario Calculate the economic benefit that DUDE gained as a result of noncompliance, assuming a penalty payment date six months after the scheduled hearing. 27
  • 28. Second Scenario Delora’s lawyer produces a document about the expenses associated with the installed equipment and expected useful life to argue that the useful life entry should be 20 years, not BEN’s 15- year standard value. Calculate the revised economic benefit. 28
  • 29. Results from BEN – First Scenario - BEN calculates DUDE’s economic benefit to be $447,390. - We do not give Delora credit for her initial “pollution control” expenditure of $50,000, because it appears unrelated to compliance. 29
  • 30. Results from BEN – Second Scenario The new economic benefit is $409,140, assuming a 20-year useful life. A longer useful life reduces the economic benefit, all other assumptions held constant. 30

Editor's Notes

  1. Rest of companies watch what you do with the violators to see if they are going to spend the money to comply.Wharton School: You are wasting your company’s money by complying if the regulatory agency is not serious about enforcement.Very tough for the honorable people a company to convince the leaders to comply if there is a strong financial incentive to violate the law.Note that not all violations involve financial motivation. Sometimes it is resistence to changing the way they operate.
  2. Fairness argument very strongly engrained in Western society. Big companies complained when President Ronald Reagan’s EPA leaders starting gutting the enforcement program.Judges very supportive.
  3. Other unique factors needs to be tightly control or you will quickly undermine all the work you are doing to craft a policy that will produce consistent results.