Economic Analysis of Expedited New Use Rule for 10 7 Chemical Substances (EPA Docket EPA
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# Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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- OPPT -2011-0941)

Contract # EP -W- 08 - 010
August 8, 2012

-- Does not contain TSCA CBI –

Economic and Policy Analysis Branch Economics, Exposure and Technology Division Office of Pollution, Prevention, and Toxics U.S. Environmental Protection Agency 1200 Pennsylvania Avenue Washington, DC 20460

### This Page Was Intentionally Left BlankEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Contributors The EPA analyst responsible for this report was Stephanie Suazo of the Economic and Policy Analysis Branch; Economics, Exposure and Technology Division; Office of Pollution Prevention and Toxics. Analytical and draft preparation support was provided by Abt Associates Inc. under EPA Contract No. EP -W08-010.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Executive Summary
This Economic Analysis estimates the potential costs of Significant New Use Rules (SNURs) covering 107 chemicals that have been the subject of TSCA premanufacture notices (PMNs)

. Appendix A lists each regulated chemical’s generic or specific chemical name and Chemical Abstract Service Registry Number (CASRN) (if non-confidential). The SNURs are being published under the rule making docket number EPA- HQ - OPPT -2011-0941 as direct final rules. The SNURs define “Significant New Uses” that trigger EPA notification requirements. To submit a Significant New Use Notice or request a SNUR modification, a firm incurs a modest submission cost, plus costs of any additional data generated to support the submission

. By avoiding a Significant New Use, a firm can avoid submission costs, but may incur other compliance costs . For example, it may incur costs associated with restricting chemical re leases to water or preventing worker exposure

. The options available to a firm considering the manufacture, import, and/or processing of a chemical covered under a SNUR, and the types of associated costs to the firm, are summarized in Table ES -1

. It should be noted that the costs listed in Table ES -1 may be incurred for reasons other than the SNUR. The costs of avoiding a Significant New Use are attributable to the SNUR only if, in the absence of the SNUR, the firm would have adopted a different approach. For example, a SNUR may de fine any use other than that described in the PMN as a Significant New Use. If the PMN submitter would have conformed to the uses described in the PMN even without the SNUR, then any associated costs of adhering to the PMN uses would not be due to the SNUR . Costs to a PMN submitter of practices required by a TSCA Section 5(e) Consent Order would be attributable to the Consent Order, not the SNUR. If a processor would have workers wear gloves even without SNUR requirements, then the gloves costs would not be attributable to the SNUR. The costs in Table ES -1 are attributable to the SNUR only if the firm adopts a different approach due to the Significant New Use Rule.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table ES -1 . Compliance Options and Associated Costs Incurred by a Firm due to SNUR

Option 1 Costs Quantified Costs per Chemical ( 2011$) 2

1 Manufacture, import, or process in a way that avoids a Significant New Use, such as limiting water releases, engaging in PMN uses

only, importing only, limiting volumes, providing workplace protection, or providing hazard communications. All SNUR chemicals require ongoing recordkeeping. In addition, many SNUR chemicals may in volve costs of complying with water release restrictions and foregoing non

- PMN uses; these costs were

not quantified for this report. Costs for worker protection and hazard communication apply to relatively few chemicals, but are quantified. Typically, annual costs for recordkeeping are under $ 1,188 . For the few SNUR chemicals where these apply, annual costs for worker protection may be $37, 412 or more and for haz

- comm is $1,08 8.

2 Submit a request for modification or revocation of the SNUR (§721.185). Cos ts of submitting a request for modification or revocation, including costs of developing supporting data (e.g., testing, if needed). $6, 0 71 submission cost plus any testing costs. 3 EPA receives very few such

requests, typically 0

- 3 per year

.

3 Electronic submission of a Significant New Use Notice (SNUN), indicating to EPA that the

firm would like to manufacture, import, or process the chemical for a Significant New Use as defined in the SNUR. Costs of electronically submitting a SNUN (including SNUN recordkeeping and user fee 4 ) plus ongoing recordkeeping. Rarely, a firm may choose to conduct toxicity or fate testing to support the SNUN, but such testing is not required by law. $8, 5 71 submission cost (including SNUN recordkeeping and $2,500 fee) 4,5 plus ongo ing recordkeeping costs of under $1,188 . EPA usually receives well under ten SNUNs in a year. Based on review of recent SNUNs, it appears that firms rarely conduct toxicity or fate testing to support a SNUN (such testing would be voluntary).

4 Petition EPA for an equivalency determination to consider alternative controls to prevent

release or exposure that are equivalent to those identified in the SNUR (§721.30). Costs of submitting an electronic request for equivalency determination. $6, 0 71 one
- time submission cost.

5 Do not manufacture, import, or process the substance except for

R&D (the R&D exemption is covered in 40 CFR §721.47). Cost of profits foregone due to delaying or avoiding commercial activity that would otherwise be pursued. R&D recordkeeping costs if manufacture for R&D. Costs not quantified.

Notes: Section numbers refer to 40 CFR §721 (in the Code of Federal Regulations). Costs come from Table 3 through Table 8

. 1 Firms may follow multiple Options simultaneously

. 2 Quantified co sts are attributable to the SNUR Significant New Use definition only if a firm would not otherwise follow the specified practices. $37, 412 is the annual cost for dermal protection selection; impermeability testing, heavy

- duty gloves, and a lower

- cost respirator (see Table 5 ). Some firms ma y have export notification costs (see Chapter 3 of this report).

3 See Appendix D for costs of individual tests recommended in current and recent SNURs.

4 EPA char ges a nominal flat fee of $2,500 for a PMN or SNUN submission.

5 SNUR chemicals not on the TSCA Inventory are “new” chemicals requiring a PMN, so some firms may need to make a submission before commercial production or import, even in the absence of a SNU R (see Section 2.3 of this report).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table of Contents

1 Introduction ................................................................................................................................... 1-1
1.1 Statutory Authority and Significant New Uses under the Proposed SNURs ........................ 1-1
1.2 Summary of Methodology .................................................................................................... 1-2
1.3 Organization of this Report ................................................................................................... 1-2

2 Costs of a Significant New Use Rule (SNUR), by Option ........................................................... 2-3
2.1 Comply with SNUR Limits (Option 1) ................................................................................. 2-5
2.1.1 Hazard Communication .......................................................................................... 2-6
2.1.2 Protection in the Workplace .................................................................................... 2-7
2.1.3 Recordkeepin g....................................................................................................... 2-12
2.1.4 Hidden Costs: production volume limits, limiting releases to water, PMN uses, import-only, and disposal .................................................................................................... 2-13
2.2 Request Modification or Revocation of a SNUR (Option 2) .............................................. 2-14
2.2.1 Costs of Developing and Submitting Testing Data ............................................... 2-14
2.2.2 Costs for Submitting a Request for Modification or Revocation of a SNUR ....... 2-15
2.2.3 Other Costs ............................................................................................................ 2-16
2.2.4 Total Costs for Option 2 ........................................................................................ 2-16
2.3 Submit SNUN (Option 3) ................................................................................................... 2-16
2.3.1 SNUR “New” Chemicals ...................................................................................... 2-17
2.3.2 Advance Compliance Exemption .......................................................................... 2-18
2.3.3 Costs for Submitting a SNUN ............................................................................... 2-18
2.3.4 Potential for Subsequent Regulatory Actions ....................................................... 2-18
2.4 Request Equivalency Determination (Option 4) ................................................................. 2-19
2.5 Decide Not to Produce Chemical (Option 5) ...................................................................... 2-19
2.6 Su mmary of Costs for Each Option .................................................................................... 2-19

3 Export Notification Costs .............................................................................................................. 3-1
3.1 Estimated Number of Annual Export Notifications per Exporter ......................................... 3-1Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 3.2 Exporter Costs ....................................................................................................................... 3-2
3.2.1 Estimated Submission (Mail ing) Costs ................................................................... 3-2
3.2.2 Compile and Maintain the List of Products ............................................................ 3-2
3.2.3 Write or Revise Export Notification ....................................................................... 3-3
3.2.4 Check Orders and Send Notifications ..................................................................... 3-3

4 Agency Costs .................................................................................................................................. 4-1
4.1 SNUN Processing Costs ........................................................................................................ 4-1
4.2 Export Notification Processing Burden ................................................................................ 4-4

5 Additional Analyses ....................................................................................................................... 5-1
5.1 Regulatory Flexibility Act (RFA) ......................................................................................... 5-1
5.2 Unfunded M andates Reform Act (UMRA) ........................................................................... 5-1
5.3 Paperwork Reduction Act (PRA) .......................................................................................... 5-2
5.4 Executive Order 12866, Regulatory Planning and Review ................................................... 5-2
5.5 Executive Order 13132, Federalism ...................................................................................... 5-2
5.6 Executive Order 12898, Environmental Justice .................................................................... 5-2
5.7 Executive Order 13045, Protection of Children .................................................................... 5-2
5.8 Executive Order 13175, Tribal Governments ....................................................................... 5-2
5.9 Executive Order 13211, Energy Supply, Distribution, or Use .............................................. 5-3
APPENDIX A: List of PMNs and their Chemical Names .............................................................. A-1
A PPENDIX B: Inflators and Wage Rates ........................................................................................ B-1
APPENDIX C: Costs of Hazard Communication, Protection in the Workplace, and Recordkeeping Requirements ................................................................................................................ C-1
APPENDIX D: Costs of Testing ............................................................................................................ 1
APPENDIX E: References ..................................................................................................................... 1Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### List of Tables
Table ES -1. Compliance Options and Associated Costs Incurred by a Firm due to SNUR ........................ iii Table 1. Summary of Compliance Options and Associated Costs Potentially due to a SNUR ................. 2-4 Table 2. Production and Use Restrictions/Requirements ........................................................................... 2-6 Table 3. Annual Costs of Hazard Communication Requirements ............................................................. 2-7 Table 4. Annual Costs of Workplace Protection Requirement .................................................................. 2-9 Table 5. Sample Costs of Workplace Protection ..................................................................................... 2-11 Table 6. Annual Costs of Recordkeeping Requirements (40 CFR §721.125) ......................................... 2-13 Table 7. Sample Costs of Recommended Testing ................................................................................... 2-14 Table 8. Costs of Requirement to Modify/Revoke SNUR or Submit SNUN .......................................... 2-16 Table 9. Derivation of Total Mailing Cost for 12 Notices ......................................................................... 3-2 Table 10. TSCA 12(b) Export Notification Cost per Notification ............................................................. 3-3
Tabl e 11. Agency Costs for SNUN and Other Submission Review and Processing ................................. 4-3 Table 12. TSCA 12(b) Export Notification Cost: Agency Burden per Activity (2011$) .......................... 4-4
Table A

- 1. PMNs and Chemical Names Referenced in this Economic Analysis ..................................... A-1
Table B

- 1. Derivation of Loaded Wage Rates .......................................................................................... B-4
Table B -2. Derivation of Industrial Hygienist Wage Rate (NAICS 31, 32, 33) ....................................... B-5
Table B -3. Derivation of Inflation Fac tors ................................................................................................ B-7
Table C -1. Annual Costs of Labeling for Distribution in Commerce [40 CFR §721.72(b)(2)] ............... C-3
Table C -2. Annual Costs of Labeling for Use in Workplace [40 CFR §721.72(b)(1)] ............................ C-4
Table C -3. Annual Costs for Material Safety Data Sheets (MSDSs) [40 CFR §721.72(c)] ..................... C-4
Table C -4. Annual Costs for Employee Training, Per Chemical [40 CFR §721.72(d)] ........................... C-5
Table C -5. Annual Costs for Dermal Protection Selection [40 CFR §721.63(a)(1)] ................................ C-6
Table C -6. Annual Costs of Impermeability Testing [40 CFR §721.63(a)(3)] ......................................... C-7
Table C -7. Annual Cost of Gloves [40 CFR §721.63(a)(2)(i)] ................................................................. C-8
Table C -8. Annual Cost of Protective Eyewear [40 CFR §721.63(a)(2)(iii)] ........................................... C-9
Table C -9. Annual Cost of Protective Clothing [40 CFR §721.63(a)(2)] ................................................. C-9Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table C -10. Crosswalk Between SNUR Text and Respirator Types at 40 CFR §721.63(a)(5) ............. C-11
Table C -11. Annual Per-Chemical Costs for Respiratory Protection [40 CFR §721.63(a)(4)] .............. C-13
Table C -13. Recordkeeping Estimates from Kearney 1988a and 1988b ................................................ C-22
Table C -14. Annual Per-Chemical Costs of Recordkeeping Requirement [40 CFR 721.125] ............... C-23
Table D -1. Cost Estimates for Test Guidelines Cited in SNURs .............................................................. D-3
Table D

- 2. Default Parameters for Species, Route, and Study Type ..................................................... D-15
Table D

- 3. Persistent Bioaccumulative Toxic (PBT) Tiered Testing Requirements .............................. D-17Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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## 1 Introduction This report presents the U.S. Environmental Protection Agency (EPA), Office of Chemical Safety and Pollution Prevention ’s (O CSPP ) ’s analysis of the potential costs incurred as a result of direct final Significant New Use Rules (SNURs) being promulgated for 107 chemical substances which have gone through premanufacture notice (PMN) review. 1 

### The SNURs are being published under the rulem aking docket number OPPT -2011-0941. Appendix A lists the generic or specific chemical name and Chemical Abstract Service Registry Number ( CASRN) (if non-confidentia l) for each PMN.


### 1.1 Statutory Authority and Significant New Uses under the Proposed SNURs
EPA may promulgate a SNUR for a substance when ( 1) the substance is the subject of a section 5(e) Consent Order (40 CFR §721.160), or (2) the Agency determines that acti vities other than those described in the PMN may result in significant changes in human exposure or environmental release levels and/or that concern exists about the substance’s health or environmental effects (40 CFR §721.170). In contrast to PMN requirem ents, which apply mainly to manufacturers and importers ( TSCA § 5(a)(1)(A), 40 CFR §720.22), the SNUR applies to processors as well as to manufacturers and importers ( TSCA § 5(a)(1)(B), 40 CFR §721.5). Each substance analyzed here was the subject of at lea st one premanufacture notice submitted under the Toxic Substances Control Act (TSCA), and is now being regulated as a result of PMN review

. For the current rulemaking, 66 of the 107 chemicals have commenced commercial manufacture or import and so are listed on the TSCA Inventory; they are no longer “new” chemicals. For chemicals in this type of rulemaking, SNUR requirements are sometimes based on past Consent Orders entered into with a PMN or SNUN submitter under TSCA Section 5(e). For the current rulemaking, SNUR requirements for 8 of the 107 substances are based on prior Consent Orders. EPA promulgates a SNUR to designate specific activities involving the chemical substance that EPA has determined constitute a “ significant new use. ” No person may manufacture or process a chemical substance for a significant new use, unless they submit a significant new use notice (SNUN) to EPA at least 90 days in advance

. Examples of typical “ signi ficant new uses ” that can trigger the requirement to submit a SNUN (if EPA has promulgated a SNUR applying these requirements to a specific chemical) include:

• Domestic manufacture in the United States

• Manufacture of a particular aggregate or annual volume

• Use other than that specified in the PMN

• Releases to water resulting in a surface water concentration exceeding a specified amount

1 This report covers chemicals that went through PMN review and are part of an expedited rulemaking. The relevant Office of Management and Budget Information Collection Request number is ICR No. 0574 (OMB Control Number 2070

- 0012). EPA also promulgates SNUR s through conventional rulemaking t hat are covered by ICR No. 1188 (OMB Control Number 2070

- 0038).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### • Handling the chemical without employing specified personal protective equipment (e.g., gloves, goggles, respirators) or hazard communication (haz

- comm) measures (e.g., label, MSDS, worker training) If EPA does not promulgate a SNUR for a given chemical, then these requirements would not apply (unless they apply to a PMN submitter via a §5(e) Consent Order). If EPA has promulgated a SNUR containing these types of significant new use designations, as long as the person does not engage (nor intend to engage) in any activities defined by the SNUR as a significant new use, then that person may proceed to handle the chemical without submitting a SNUN.


### 1.2 Summary of Methodology This analysis quantifies, to the extent possible, the costs to society of the proposed rule by identifying the costs to industry ass ociated with complying with the rule , and the costs to EPA of administeri ng the rule. Types of i ndustry costs analyzed include those for worker protection, hazard communication, testing, submission of required information , export notification, and recordkeeping. Agency costs include reviewing and processing the data received as a result of the rule. Data sources for this analysis include burden estimates derived from previous information collection requests and economic analyses for related rules, compensation data acquired from government publications, and supplementary market research to produce an estimate of the universe of affected entities and measure the impact of the proposed rule on small entities. In previous economic analyses of SNURs, EPA identified those requirements under Subparts A, B, C, and D of 40 CFR §721 that may indirectly impose costs on manufacturers, importers, and processors of PMN substances (e.g., EPA, 1989). Some of these costs, such as providing personal protective equipment under §721.63, were estimated in earlier SNUR economic analyses and are presen ted as part of this analysis

. Resources were not available to quantify other costs, such as for limiting releases to water, avoiding uses not listed in the PMN, or keeping production below a specified level; they are described only qualitatively. It was not feasible within available resources to aggregate costs , or to estimate how often costs are actually incurred as a result of SNURs , except for costs of SNUN submissions.


### 1.3 Organization of this Report The remainder of this report estimates the quantified por tion of costs potentially associated with SNURs such as those included in this rulemaking . Chapter 2 presents estimates of the costs that could be incurred by manuf acturers, importers, and/or processors under the various SNUR options. Chapter 3 addresses export notification costs . Chapter 4 addresses costs to EPA of administering the SNURs, while Chapter 5 presents an analysis of other impacts, as required by various statutes and executive orders

. Appendix A lists the chemicals that are subject to the proposed SNURs. Appendix B provides the wage rates and inflators used in this analysis

. Other appendices give cost estimation details and references.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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## 2 Costs of a Significant New Use Rule (SNUR), by Option
A SNUR specifies requirements that a firm must meet if it chooses to manufacture, import, or process a PMN chemical without engaging in a Significant New Use that would trigger notification to EPA

. A SNUR also requires recordkeeping for anyone manufacturing, importing, or processing the SNUR chemical

. A SNUR recommends testing, but does not requi re testing . EPA rarely receives results of tests performed specifically to support a SNUN
. Table 1 sets forth possible responses to a SNUR

. A firm may select more than one course of action. For example, it may produce a chemical in a way that avoids a Significant New Use, while simultaneously submitting a Significant New Use Notice for a proposed new use. These options are described below along with the ir costs.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table 1 . Summary of Compliance Options and Associated Costs Potentially due to a SNUR

Option 1 Costs Quantified Costs per Chemical ( 2011$) 2

1 Manufacture, import, or process in a way that avoids a Significant New Use, such as limiting water releases, engaging in PMN uses only, importing

only, limiting volumes, providing workplace protection, or providing hazard communications. All SNUR chemicals require ongoing recordkeeping. In addition, many SNUR chemicals may involve costs of complying with water release restrictions and foregoing
non
- PMN uses; these costs were not quantified for this report. Costs for worker protection and hazard communication apply to relatively few chemicals, but are quantified. Typically, annual c osts for recordkeeping are under $1,188 . For the few SNUR chemicals where these apply, annual costs for worker protection may be $37, 412 or more and for haz

- comm is $1,08 8.

2 Submit a request for modification or revocation of the SNUR (§721.185). Costs of submitting a request for modification or revocation, including costs of developing supporting data (e.g., testing, if needed). $6, 0 71 submission cost plus any testing costs. 3 EPA receives very few such

requests, typically 0

- 3 per year

3 Electronic submission of a Significant New Use Notice (SNUN), indicating to EPA that the firm would like to manufacture, import, or process the chemical for a Significant New Use as defined in the SNUR. Costs of electronically submitting a SNUN (including SNUN recordkeeping and user fee 4 ) plus ongoing recordkeeping. Rarely, a firm may choose to conduct toxicity or fate testing to support the SNUN, but such testing is not required by law. $8, 571 submission cost (including SNUN recordkeeping and $2,500 fee) 4,5 plus ongoing recordkeeping costs of under $1,188 . EPA usually receives well under ten SNUNs in a year. Based on review of recent SNUNs, it appears that firms rarely conduct toxicity or fate testing to support a SNUN (such testing would be voluntary).

4 Petition EPA for an equivalency determination to consider alternative controls to prevent release or exposure that are equivalent to those identified in the SNUR (§721.30). Costs of submitting an electronic request for equivalency determination. $6, 0 71 on e- time submission cost.

5 Do not manufacture, import, or process the substance except for R&D (the R&D exemption is covered in 40 CFR §721.47). Cost of profits foregone due to delaying or avoiding commercial activity that would otherwise be pursued. R&D recordkeeping costs if manufacture for R&D. Costs not quantified.

Notes: Section numbers refer to 40 CFR §721 (in the Code of Federal Regulations). Costs come from Table 3 through Table 8

. 1 Firms may follow multiple Options simultaneously

. 2 Quantified co sts are attributable to the SNUR Significant New Use definition only if a firm would not otherwise follow the specified practices. $37, 412 is the annual cost for dermal protection selection; impermeability testing, heavy

- duty gloves, and a lower

- cost respi rator (see Table 5 ). Some firms may have export notification costs (see Chapter 3 of this report).

3 See Appendix D for costs of individual tests recommended in current and recent SNURs.

4 EPA charges a nominal flat fee of $2,500 for a PMN or SNUN submission.

5 SNUR chemicals not on the TSCA Inventory are “new” chemicals requiring a PMN, so some firms may need to make a submission before commercial production or import, even in the absence of a SNUR (see Section 2.3 of this report).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 2.1 Comply with SNUR Limits (Option 1) A firm can avoid engaging in a Significant New Use and submitting a SNUN by meeting all applicable SNUR requirements. The firm may also pursue this option temporarily by complying with SNUR restrictions while also pursuing other options such as making a submission to EPA. If it does avoid engaging in a Significant New Use (and if the chemical is on the TSCA Inventory or if the firm has already submitted a PMN), no notice to EPA is requi red. 2 

### Table 2 shows the types of requirements a firm must meet to avoid engaging in a Significant New Use

. The Significant New Use designation in a SNUR for a specific chemical reflect s either the use sce nario described in the PMN for that chemical (what the submitter was already planning to do) or the requirements in the 5(e) Consent Order resulting from the PMN submission . Thus , it is likely that the typical PMN submitter will incur no added costs of com plying with the SNUR requirements so as to avoid a Significant New Use

. However, if there is any export of these chemicals, the re will be export notification costs that result from the TSCA Section 12 (b) requirements that are automatically triggered for c hemicals regulated under TSCA Section 5 (see Chapter 3 for details).

2 Under the Toxic Substances Control Act § 3(9), if a chemical is not on the TSCA Inventory, it is a “new chemical.” Prior to manufacture or import of a new chemical for general commercial use, a notice must be filed with EPA under Section 5(a)(1)(A) of TSCA (40 CFR §720.3 and 40 CFR §720.22).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table 2 . Production and Use Restrictions/Requirements

40 CFR Reference (Code of Federal

Regulations) Restriction/Requirement N umber of Chemicals Affected 1 Sample Costs Per Chemical

( 201 1$) §721.63 Workplace protection 27 $12 ,439 to $37 ,412 §721.72 Hazard communication 4 $1,08 8 Industrial Commercial, and Consumer Activities (§721.80) §721.80(a, b, c) Enclosed use only 0 Not quantified §721.80(d, e) Use at site only 0 Not quantified §721.80(f) Import only (do not manufacture) 7 Not quantified §721.80(g, h, i) Use only as intermediate 1 Not quantified §721.80(j, k) Engage only in uses listed in PMN or Consent Order 54 Not quantified
§721.80(l, m, n, o) Limits non

- industrial uses 4 Not quantified §721.80(p, q, s, t) Limit production volume 4 Not quantified §721.80(r, u) Volume

- triggered testing 2 Not quantified §721.80(v, w, x, y) Restricts physical form of chemical 44 Not quantified Disposal, water release, recordkeeping §721.85 Disposal 0 Not quantified §721.90 Limit releases to water Not quantified §721.125 3 Recordkeeping for all manufacturers, 10 7 Up to $1 , 1 88
Notes:

1 Some chemicals have more than one type of restriction.

2 $12, 439 is the annual cost for dermal protection selection and heavy duty gloves. $37, 412 is the annual cost for dermal protection selection; heavy duty gloves, impermeability testing/evaluation of manufacturer specifications, and a lower

- cost respirator (see Table 5 ).

3 This excludes SNUN recordkeeping under §721.40. See the recordkeeping discussion in Appendix C

. Source : Costs are summarized in Table 3 , Table 4 , and Table 6 , and derived in Appendix C

. 

### The costs of meeting the haz- comm, protective equipment, and recordkeeping requirements are quantified for this report

. Appendix C presents a more detailed derivation of these costs. The export notification costs are summarized in Chapter 3 . Complying with requirements to avoid a Significant New Use also may result in additional costs that affect a significant number of the chemicals, such as costs associated with limiting releases to water, that were not quantified for this report ; these costs are also summarized below.
2.1.1 Hazard Communication
Requirements

. Each SNU R may require firms that manufacture, import, or process one of the PMN substances to implement a haz

- comm program for the applicable chemical , or else submit a SNUN. For p urposes of the economic analysis, it is assumed that each facility has in place a haz

- comm program consistent with that required by OSHA’s Hazard Communication standard (29 CFR 1910; November 25, 1983). Much of the haz -comm cost methodology used in this an alysis came from a 1989 EPA report, Economic Analysis of Final Significant New Use Rules: General Provisions for New Chemical FollowupEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### (EPA, 1989). The cost estimates provided here are for one chemical produced at one site , assumed to have 25 exposed workers and roughly a 10,000 kilogram annual shipment volume. Higher volumes would increase costs, although not necessarily proportionately. The major elements of a haz -comm program that could apply to a SNUR chemical, based on the requirements in §721.72, are:

• Revision of the existing written haz -comm program to incorporate information about the chemical [§721.72(a)];

• Creation of labels and application of labels to containers used for distributing the chemical in commerce [§721.72(b)];

• Creation of labels or signage and posting of hazard data in areas of the facility where the chemical is used or stored [§721.72(b)];

• Creation and distribution of material safety data sheets (MSDSs) [§721.72(c)]; and

• Employee awareness training on w here and how the chemical is used, the hazards associated and availability of hazard information about the chemical, and protective equipment and other measures in place to reduce and minimize exposure to the chemical [§721.72(d)].

Costs

. The annual costs of compliance with the haz- comm requirements for PMN substances subject to haz- comm requirements appear in Table 3

. Further, the costs are for substan ces with full haz

- comm requirements, and may overstate haz

- comm costs for substances with partial requirements . Appendix C gives the detailed cost derivation.
Table 3 . Annual Costs of Hazard Communication R equirements
Requirement Co st ( 2011$) 1,2 Hours Update written program $ 211 4 Labeling Distribution in commerce $140 0.5 Use in the workplace $383 1.5 MSDS preparation $141 2.25 Employee training $214 6.75 TOTAL $1, 08 8 15

Notes: 1 Figures are rounded to whole dollars. Substances not subject to all of these requirements may have lower costs. See Table C -1 through Table C -4 , and Section C.1.1 for derivations.

2 Hourly labor costs are derived in Table B -1

.


### 2.1.2 P rotection in the Workplace
Requirements. Under 40 CFR §721.63, manufacturers, importers, or processors must comply with worker protection requirements as specified in the SNUR on the regulated chemical, or else submit a SNUN

. The
core components of the worker protection requirements include provision of personal protective equipment (PPE) such as gloves, goggles, protective clothing, and respirators.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### In some cases, EPA specifies the type of PPE required

. In other cases, EPA requires adequate dermal protection but does not specify particular PPE

. Instead, it requires the employer to evaluate worker exposure conditions and hazards, and select appropriate PPE. Generally the employer is also required to determine that dermal PPE is impervious to the PMN substance by one or both of the following methods : (1) perform impermeability testing on the PPE under the exp ected conditions of exposure, and/or (2) rely on equipment manufacturers' specifications. Employers not already providing adequate dermal protection would need to do so.
Costs. Annual costs for worker protection items are shown in Table 4 below. The derivation of the sample minimum and maximum annual costs for worker protection is found in Table 5

. The costs of worker protection were originally e stimated in a 1989 EPA report, Economic Analysis of Final Significant New Use Rules: General Provisions for New Chemical Follow

- Up ( EPA, 1989 ), as a range of costs, depending on the assumed number of worker-days of exposure. This report uses the high end of the assumptions about worker-day exposure, updated to adjust for inflation. The estimates are for one chemical at one site with 25 exposed workers; actual costs would vary with the number of workers. Appendix C gives the detailed cost derivation.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table 4. Annual Costs of Workplace Protection Requirement

Personal Protective Equipment and Requirement Citation at 40 CFR Unit Cost ( 2011 $) 1 Quantity Required 1 Total Annual Cost 2 ( 20 11$) Dermal Protection Selection §721.63(a)(1) 10 hours industrial hygienist (IH) time $ 52.63 10 $ 526 Impermeability Testing §721.63(a)(3) Impermeability Test $1, 335 1 $1, 335 Evaluation of Manufacturer's Specifications $ 211 1 $ 211 Gloves §721.63(a)(2)(i) Standard (disposable) $0.60 6,250 $3,767 Heavy

- duty butyl $47.65 250 $11,913 Protective clothing §721.63(a)(2) [ii]

- Full

- body (coverall with hood) $85.77 75 $6,433 [iv]

- Coverall (no hood) $50.80 75 $3,810 Eyewear §721.63(a)(2)(iii) Standard goggles $5.68 75 $426 Heavy

- duty goggles $8.48 75 $636 Respirator Types 3 Supplied

- air respirator operated in pressure demand or continuous flow mode and equipped with a tight

- fitting full facepiece. [similar to §721.63(a)(5)(ii)] $1,127 25 $28,171
Supplied

- air respirator operated in pressure demand or continuous flow mode and equipped with a hood or helmet or tight

- fitting facepiece (either half - or full

- face). [similar to §721.63(a)(5)(iii)] $1,306 25 $32,660

Air

- purifying respirator equipped with a tight

- fitting full facepiece and High Efficiency Particulate Air (HEPA) filters.[similar to §721.63(a)(5)(iv)] $937 25 $23,428

Air

- purifying, tight

- fitting respirator (either half

- or full

- face) equipped with N100 (if aerosols absent), R100, or P100 filters. [similar to §721.63(a)(5)(iv)] $937 25 $23,428

Powered air

- purifying, tight

- fitting full

- face respirator equipped with N100 (if oil aerosols absent), R100, or P100 filters. [similar to §721.63(a)(5)(v)] $3,367 25 $84,175

Powered air

- purifying respirator equipped with a tight

- fitting facepiece (either half - or full

- face) and HEPA filters. [similar to §721.63(a)(5)(v)] $3,367 25 $84,175

Powered air

- purifying respirator equipped with a loose

- fitting hood or helmet and High Efficiency Particulate Air (HEPA) filters. [similar to §721.63(a)(5)(vi)] $2,621 25 $65,517Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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1 Quantities assume: 1) 25 workers exposed 250 days per year; 2) standard gloves replaced daily and heavy

- duty gloves replaced every 25 days; 3) respirator units replaced annually and cartridge sets replaced every five days (50 cartridges sets per year); 4) goggles and protective clothing replaced three times yearly.

2 Total annual costs were calculated using unrounded unit cost estimates, and may not equal the product of the rounded estimate s shown in this table.

3 This table lists respirator choices that t ypically would satisfy SNUR requirements for a particular chemical, for current and recent SNURs. Future SNURs may list different choices. The citations in brackets refer to respirator types listed at 40 CFR. While t he SNURs no longer reference the §721.63(a)(5) categories, costs in this analysis are based on costs estimated in 1997 for the §721.63(a)(5) categories. See Table C

- 10 for the crosswalk betwe en respirator types in SNURs and in this table. The respirator “unit cost” is per worker. Total respirator costs include costs of the respirator plus the costs of any add

- on items such as hoods, helmets, cartridges, filters, and caps, if these items are required for a particular respirator.
Source: Appendix C , Tables Table C -5 through Table C

- 11

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### The costs of purchasing protective equipment are derived in Appendix C , and have been annualized based on the assumptions listed above regarding t heir use and lifetime in the workplace

. Costs for evaluating hazards when PPE is not specified in the SNUR are based on estimates of the reasonable time required for a safety professional to perform such evaluations . Costs for conducting impermeability tes ting are based on consultation with PPE vendors, as described in Appendix C

. Table 4 summarizes the annual costs associated with protection in the workplace, including the PPE itself, as well as selecting required dermal protection, and performing impermeability testing and/or evaluating manufacturer's information.
Table 5 shows a sample of the minimum and maximum annual cost of workplace protection, assuming 25 workers who are exposed for 250 hours per year. The minimum cost includes the cost of heavy -duty butyl gloves, and 10 hours of an industrial hygienist’s time for dermal protection selection. The maximum cost includes the cost of gloves, dermal protection, impermeability testing, and the annual cost of the least expensive respirator and filters for 25 workers.
Table 5 . Sample Costs of Workplace Protection

Cost Element Annual Cost ( 2011 $) Example #1: Gloves and Dermal Protection Selection Heavy

- duty butyl Gloves $11,913 Dermal Protection Selection $ 526 Total per site with 25 workers $12, 4 39 Example #2: Gloves , Testing, and Respirator Heavy

- duty butyl Gloves $11,913 Dermal Protection Selection $ 526 Impermeability Test $1, 335 Evaluation of Manufacturer's Specifications $ 211 Least Cost Respirator $23,428 Total per site with 25 workers $37, 412
Source : Table 4

. 

### In cases where the SNUR specifies the type of protective gear, the estimates assume workers would not otherwise wear adequate protective equipment. To the extent that workers would otherwis e be adequately protected (as a result of the company ’s own safety program related to other chemical hazards, or to comply with OSHA ’ s PPE standards), these costs may be an overestimate of the actual costs. In some cases, the SNUR requires dermal protection but does not specify any particular gear , allowing regulated companies to make that determination

. Table 4 shows costs of assessing needs and demons trating impermeability . These cost estimates would reflect a situation where the dermal protection is already in place but the manufacturer must demonstrate that it is adequate

. If companies also have to purchase additional protective gear, incremental costs attributable to the SNUR would include the added items

. For example, if a firm already providing gloves and goggles determined that it would have to add protective clothing to avoid engaging in a Significant New Use, this would increase costs even if particular protective clothing is not specified in the SNUR.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 2.1.3 Recordkeeping
Requirements

. Under 40 CFR §721.40, recordkeeping is required for SNUN submitters . This recordkeeping cost was included in the SNUN submission cost and is not separately estimated here. 3 

### In addition, the SNURs specify recordkeeping requirements for manufacturers, importers, and processors, by identifying paragraphs selected from 40 CFR §721.125(a) through (k). These recordkeeping requirements apply even if the firm does not engage in a reportable New Use or make a submission to EPA, so long as it manufactures, imports, or processes the chemical. The recordkeeping requirements vary by chemical

. For example, only chemicals that must establish a Hazard Communications program to avoid a Significant New Use would be required to keep records documenting their haz -comm program. (For firms producing under the R&D exemption, R&D recordkeeping would be needed. R&D recordkeeping costs were not estimated for this report.) SNUR recordkeeping requirements essentially involve copying and filing relevant records, including those related to manufacturing, importing, or processing volumes; shipment amounts and customer information; clothing impermeability determinations; the hazard communication program including labels and MSDS copies; compliance with disposal and water discharge limitations; and/or compliance with restrictions on volumes, nature of manufacture or use, or on the chemical’s physical form (powder, liquid etc.).
Costs

. Annual costs for com pliance with 40 CFR §721.125 recordkeeping requirements are low, but do potentially apply to all SNUR chemicals, and the recordkeeping could continue for years

. Costs are presented in Table 6 and derived in Appendix C

. They are estimated for one chemical at one site, and include technical and clerical labor time, photocopying charges, and costs for records storage.
Table 6 summarizes recordkeeping costs by requirement at 40 CFR §721.125

. The totals in Table 6 provide the cost if all recordkeeping requirements in paragraphs §721.125 (a) through (k) were required; this would seldom, if ever, be the case for a single chemical.

3 For example, OPPT’s Information Collection Request (ICR) for TSCA Section 5(a)(2) Significant New Use Rules for Exi sting Chemicals (Renewal), October 11, 2005, estimated SNUN recordkeeping costs at 5.67 hours (EPA, 2005b, page 12).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### Table 6 . Annual Costs of Recordkeeping Requirements (40 CFR §721.125) 40CFR §721.1252 Cost Element Cost ( 201 1 $ ) 1 Hours (a)(b)(c) Volumes & sales/transfer data $336 7.11

(d)(e) Protective clothing [§721.63] and $13.86 0.29

(f) Haz com program [§721.72] $173 3.67 (g) Label copies [§721.72(b)] $3.46 0.07 (h) MSDS copies [§721.72(c)] $3.46 0.07 (i) Use limitations compliance [§721.80] $173 3.67 (j) Disposal compliance [§721.80] $416 8.80 (k) Water discharge compliance [§721.90] $69.28 1.47 TOTAL $1,188 25.15
Notes:

1 Recordkeeping applies to all SNUR chemicals. This table does not cover recordkeeping for SNUN submissions. See Appendix C Table C

- 14 for derivations.



### 2.1.4 Hidden Costs: p roduction volume limits, limiting releases to water , PMN uses, import
- only, and disposal
Several types of costs that may be incurred by complying with the significant new use designations are not quantified in this report , including production volume limits, r elease s to water, disposal, and other use restrictions . For example:

• Keeping production volume below specified limits to avoid a Significant New Use could result in a decrease in profits; a potential “hidden” cost. A firm producing for sale may have to restrict its sales of the chemical. If the chemical is for internal use, it may have to substitute to a less cost

effective chemical.

• A producer could incur costs of determining whether discharges to water would constitute a Significant New Use and of limiting releases in order to avoid the Significant New Use.

• Similarly, avoiding uses not li sted in the original PMN could result in “hidden” costs of foregone profits if the firm cannot market the chemical for certain applications . If the firm wants to use the chemical for internal use, it may have to substitute to other chemicals or technologie s that cost more or have lesser performance resulting in higher production costs.

• Importing could be costlier than manufacturing a PMN substance in the United States.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 2.2 Request Modification or Revocation of a SNUR (Option 2) Under 40 CFR §721.185, EPA may modify or revoke a SNUR upon review of a submittal from a manufacturer, importer, or processor

. Consequently, the second option for a firm is to request modification or revocation of the SNUR. According to New Chemical Progra m records EPA receives few modify/revoke requests (typically up to three per year) due to SNURs. This option may have some or all of the following associated costs:

• One

- time costs of testing to develop health and environmental effects data for a chemical subject to the SNUR;

• One -time costs of submitting a request for modification or revocation;

• Ongoing costs of complying with SNUR restrictions (Option 1 in this report) or of avoiding production while the modification request is being processed (Option 5). The firm may also incur costs of complying with any SNUR restrictions that are not ultimately revoked or may incur hidden costs of avoiding production altogether.
These costs are discussed below.
2.2.1 Costs of Developing and Submitting Testing Data
40 CFR §721.185(b)(1) requires that a modification request include “information sufficient to support the request.” For each PMN substance, the SNUR identifies health, ecological, and/or fate/transport/transformation testing that would help characterize the risks associated with the substance

. However, there is no requirement for a requester to perform the recommended tests or even to perform testing at all . It is possible that some of the recommended tests, or other tests, would be performed b y the submitter to support a request for modification and revocation of a SNUR. For informational purposes, costs for various tests recommended in SNURs over the years are listed in Appendix D . If no additional testing is performed to support a modification request, costs may be similar to costs of a SNUN – discussed later in this section – minus the user fee.
Table 7 below provides an example of potential costs if a firm were to perform a standard set of basic ecotoxicity tests to support a request to modify or revoke a SNUR

. Table 7 . Sample Costs of Recommended Testing

Test Guideline Test D escription Estimated Cost ( 2011$) Ecotoxicity Base Set OPPTS 850.5400 Algal Toxicity, Tiers I and II $18,873 OPPTS 850.1010 Daphnid Acute Toxicity $15,619 OPPTS 850.1075 Fish Acute Toxicity $21,524 Sample TOTAL Testing Cost: $56,016Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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Source: Costs are from Table D-1

.



### 2.2.2 Costs for Submitting a Request for Modification or Revocation of a SNUR
The costs associated with submitting a request for modification and revocation of a SNUR (or of submitting a SNUN ) are estimated to be similar to the costs for preparing a PMN submission, except that there is no user fee for the modify/revoke request

. The PMN submission costs came from EPA ’s 1994 Regulatory Impact Analysis of Amendments to Regulations for TSCA Section 5 Premanufacture Notifications, which relied on industry estimates of the effort needed to collect and compile all data required for a PMN submission, prepare the form, submit the form and data to EPA, and maintain a file of the submission (EPA, 1994, Ta ble III -2 and pages III-11, -12, and -13). The 1994 estimates were based on a survey conducted by the Chemical Manufacturers Association (CMA, 1991), which became the American Chemistry Council

. The burden associated with PMN submission and preparation has been adjusted to reflect burden reductions resulting from the 2009 final PMN Electronic Reporting (ePMN) Rule that requires the electronic submission of all TSCA section 5 notices. 4 

### Electronic submission of SNUN forms is expected to remove all clerical b urden associated with preparing a SNUN (EPA, 2009a, p.7). In addition, electronic submission is expected reduce all recordkeeping burden associated with SNUN submissions by fifty percent

. Because, the recordkeeping burden for PMNs was not estimated separately, for the purposes of this report we assume this burden reduction is captured in the removal of all clerical burden. 5 

### In the 1994 EPA report, the average effort required to prepare and submit a PMN was 95 to 114 hours. This burden is reduced to 83 to 100 hours after accounting for the ePMN savings (EPA, 2009a)

. This included recordkeeping for the submission, but the recordkeeping cost was not broken out. For this analysis, the costs of a preparing a SNUN were derived using the averages of the hours for each type of labor from the 1994 report, after adjusting for the ePMN savings. The method of calculating hourly loaded labor costs is described in Appendix B

.

4 Economic Analysis of Expedited Significant New Use Rules for 2 5 Chemical Substances: EPA Docket OPPT

- 2009

- 092 2, was the first report to c onsider the burden reductions resulting from electronic submission of SNUN forms and requests for equivalency determination. Previously , all burdens were based upon 1994 paper submission estimates.

5 The Economic Analysis of the Premanufacture Notification Electronic Reporting Final Rule (EPA, 2009a) reported a 0.5 hour clerical and a 0.5 hour technical burden associated with recordkeeping in addition to the burden estimates from the 1994 RIA (EPA, 1994, p. III

- 14). These burden estimates (the 0 .5 for clerical burden and 0.5 for technical burden) are based on the recordkeeping burden for polymer exceptions and not the recordkeeping burden associated with PMN submissions. Therefore, for this analysis, the 0.5 hour for clerical labor and the 0.5 ho ur for technical labor were removed. It is important to note that for this analysis, clerical burden changes are not applicable because the entire clerical burden is assumed to be eliminated under the electronic reporting requirements . In summary, we do not include the one hour recordkeeping burden (0.5 hour for clerical, 0.5 for technical) reported in the ePMN EA

.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 2.2.3 Other Costs

EPA’s review of the submitter ’ s request may cause delays in the start of manufacturing or processing activities . Such delays could cause the company to forego oppor tunities to earn profits for the duration of the review period

. Alternatively, the submitter may elect to produce under the constraints of the SNUR during the review period, so as to avoid a Significant New Use. EPA may not revoke all SNUR provisions as a result of the request

. If the company is allowed to continue production and chooses to do so, it would bear costs of complying with any SNUR restrictions that are not revoked. Costs of complying with SNUR restrictions pending EPA modification or revocation were discussed under Option 1.
Table 8 . Costs of Requirement to Modify/Revoke SNUR or Submit SNUN

Labor Category Average Hours Loaded Wage Rate 1 (201 1 $) Total Labor Cost ( L oaded W age x Average H ours) Request to Modify SNUR (Option 2) SNUN (Option 3) Equivalency Determination

(Option 4) Clerical 2 0 $29.63 $0 $0 $0 Technical 3 74.2 $64.66 $4,798 $4,798 $4,798 Managerial 3 18 $70.72 $1,273 $1,273 $1,273 Subtotal 92.2

-- $6,071 $6,071 $6,071 User F ees (SNUN only) $0 $2,500 $0 TOTAL $6,071 $8,571 $6,071 Test Costs Sometimes Rarely
Notes:

1 Loaded wages include fringe benefits and overhead. See Appendix B of this report for derivation. Wage rates presented in this table are rounded values; however, unrounded values are used to calculate total labor costs. For this reason, total labo r costs may not equal the product of rounded values.

2 The estimate of no clerical burden is taken from the Economic Analysis of the Premanufacture Notice Electronic Reporting Final Rule (EPA, 2009a, page 7)

. 3 Hours range for each technical and managerial labor is from the PMN Amendments RIA (EPA, 1994, Table III

- 2)

.


### 2.2.4 Total Costs for Option 2
The total costs associated with requesting a modification or revocation of a SNUR include the costs of generating new supporting data plus the administrative cost of preparing the submission.


### 2.3 Submit SNUN (Option 3) Under 40 CFR §721.5, manufacturers, importers, or processors who would like to undertake a Significant New Use of a substance listed in a SNUR are required to submit a Significant New Use Notice (SNUN) at least 90 days before the firm plans to commence the manufacture, import, or processing of the substance. For example, they could submit a SNUN if they wish to produce above the volume limit listed in theEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### SNUR for a given chemical, since any production beyond that volume would be defined as a Significant New Use. The SNUN provides EPA with the opportunity to evaluate the intended use and, if necessary, to prohibit or limit that activity before it occurs . The notice form used to submit a SNUN is the same as that for a PMN, a nd the costs of submitting a SNUN are estimated based on the costs incurred to submit a PMN. This option could have the following costs:

• One

- time costs of the SNUN and $2,500 user fee. (However, in some cases, a notification may be needed for reasons other than the SNUR; see Section 2.3.1 below.)

• Ongoing costs of complying with SNUR restrictions to avoid engaging in a Significant New Use (Option 1 in this report) or of avoiding production while the SNUN is being processed (Option 5); costs of recordkeeping , and of complying with any restrictions resulting from the SNUN review.

• Rarely, the SNUN submitter may elect to perform some of the te sting recommended in the SNUR as a way to characterize effects of a chemical

. These tests are not mandatory, and firms do not usually conduct testing to support a SNUN, so any such costs are likely to be zero or low. The assumption regarding testing is ba sed on an analysis of the 18 SNUNs submitted over a three

- year period, from 2005 through 2007. A list of human health tests submitted to EPA with PMNs and SNUNs was also available from a confidential database maintained by EPA ’s O ffice of Pollution Prevent ion and Toxics Risk Assessment Division

. Only one SNUN described toxicity or environmental fate testing that seemed reasonably likely to have been performed to support a SNUN

. In that case, two relatively low

- cost tests (fish acute toxicity and daphnid acute toxicity) may have been conducted to support a SNUN, although it is also possible that the testing was done for some other reason not apparent in the SNUN itself . A substantial portion of the SNUNs did provide or reference test results

. However, in almo st all cases, the testing appeared to have been conducted for reasons other than a SNUR. For example, the SNUN might include laboratory reports that had already been submitted for a PMN for the same chemical

. 2.3.1 SNUR “New” Chemicals

If a SNUR chemical is not on the TSCA Inventory and a potential manufacturer or importer has not yet filed a PMN, submission costs may be incurred but are not attributable to the SNUR.
All SNUR chemicals in this rulemaking were the subject of at least one PMN. For PMN chemicals to be added to the TSCA Inventory, manufacturing (or import) must have commenced, with notification to EPA through a Notice of Commencement, or NOC. Thus, SNUR chemicals not yet in commercial manufacture (or import) are not on the TSCA Inventory

. They legally remain “new” chemicals subject to PMN requirements. For “new” chemicals, firms who have not yet submitted a PMN must notify EPA 90 days before manufacturing/importing the chemical for commercial purposes. This submission is still designated a PMN but may contain information demonstrating the submitter intends to engage in a significant new use. Either way, the firm uses the same submission form and provides the data listed at 40 CFR §720.45

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### Consequently, for this special situation, the submission cost is incurred due to PMN requirements, not due to the SNUR

. (See EPA ’s 1997 Chemistry Assistance Manual for Premanufacture Notification Submitters for an overview of New Chemicals requirements [EPA, 1997]).
2.3.2 Advance Compliance Exemption
Another option available to firms before the SNUR is promulgated is to seek an advance compliance exemption under 40 CFR §721.45(h). The submission cost for this option is the same as that for a SNUN, but by negotiating an advance compliance agreement with EPA a firm might diminis h any loss of profits due to delay

. This option is not available after the SNUR is promulgated.
2.3.3 Costs for Submitting a SNUN
As with Option 2 above (Request Modification or Revocation of a SNUR), the costs for submitting a SNUN are estimated to be equivalen t to the costs of completing a PMN submission. If the SNUN is submitted at the same time as a request to modify a SNUR (Option 2), the added cost would be less than shown here due to overlap in information in the two submissions

. Table 8 shows the costs of preparing a SNUN

. 2.3.4 Potential for Subsequent Regulatory Actions
The Agency recognizes that if submission of a SNUN does result from a SNUR, the Agency m ay take additional regulatory actions under TSCA

. These additional regulatory actions might be necessary to further evaluate an intended new use and associated activities, or to prohibit or limit that activity before it occurs to prevent unreasonable risk of injury to human health or the environment. It is not known what specific subsequent regulatory actions, if any, the Agency may determine are necessary after reviewing a SNUN . Any such actions are highly dependent on the circumstances surrounding the ind ividual SNUN (e.g., available information and scientific understanding about the chemical and its risks at the time the SNUN is being reviewed)

. Should the Agency’s review of the SNUN result in further regulatory actions, the Agency will initiate and follow the appropriate procedures for taking those actions. Included in those procedures would be an assessment of the costs and benefits of those actions. Subsequent regulatory action may be a Consent Order under TSCA Sectio n 5(e). Assessments of costs and benefits for a Consent Order would be limited, similar to those supporting PMN reviews leading to Consent Orders, in contrast to the in -depth benefit- cost analyses prepared under some other TSCA Sections. The description above was a dapted from text in Economic Analysis of the Significant New Use Rule for Chloranil , January 8, 2008 , Section 2.4; and Economic Analysis of the Final Significant New Use Rule for 183 Perfluoroalkyl Sulfonates , August 20, 2007, Section 3.4. Both r eports are from the U.S. EPA Office of Pollution Prevention and Toxics, Economic and Policy Analysis Branch. The nature of the follow -up regulatory action and benefit/cost analysis may differ between SNUNs for newer chemicals submitted as a result of a direct final rulemaking such as this one, and SNUNs for older chemicals such as chloranil and most perfluoroalkyl sulfonates.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### 2.4 Request Equivalency Determination (Option 4) Under 40 CFR §721.30, EPA may review applications from facilities who propose alternative methods of controlling or preventing exposures or releases to those specified in the SNUR. In these cases, EPA evaluates the alternatives using an abbreviated review process

. As shown in Table 8 , the costs of submitting an equivalency determination request are expected to be the same as those for submitting a SNUN except that no user fee is required. For this option the EPA review period is 45 days compared to 90 days for a SNUN, therefore any potential loss of profits due to delays may be less than for a SNUN under Option 3. In addition to the costs of submitting the equivalency determination request, each submitter will also incur costs to develop data to support the request . However, total costs of the equivalency option should be no more than the costs of complying with controls in the SNUR to avoid a significant new use

-- for example, controls related to workplace protection or environme ntal release

. Otherwise, presumably there would be no incentive for the submitter to choose this alternative. Finally, to produce the chemical following EPA review, the submitter would incur costs from recordkeeping and from any restrictions not waived (se e Option 1).


### 2.5 Decide Not to Produce Chemical (Option 5) Some firms may find that the costs of meeting the SNUR requirements and/or restrictions (Option 1) or preparing a SNUN or other submission (Options 2, 3, or 4) are financially unattractive. In these ca ses, the firm could choose not to manufacture, import, or process the PMN substance. While this option avoids the costs of meeting the specifications in the SNUR or submitting a request for some alternative, it entails the “hidden” cost of the profit that will be foregone as a result of not engaging in the commercial activity originally planned. For example, if the firm does not produce the SNUR substance, then it will forego the profit it would have achieved by producing it. That foregone profit is a poten tial “hidden” cost of Option 5 . Similarly, if the firm would have used the SNUR substance in the production of another product and must substitute to a more costly substance, it will incur those additional costs of production . If the firm elects to produce for R&D purposes only, it may have costs associated with R&D recordkeeping attributable to the SNUR.
Firms that exercise Option 5 may still incur export notification costs, if they export any existing stockpiles of the product . This cost is quantified in Chapter 3 below.


### 2.6 Summary of Costs for Each Option
Table 1 , above, gave an overview of compliance options. Table 3 through Table 6 summarized the quantified portion of potential costs of either following restrictions to avoid engaging in a Significant New Use, or of making a submission to EPA. Table 7 presented sample testing costs

. Costs are for one chemical at one site, and – where volume is relevant – are based on standard assumptions th at include 25 exposed workers per site and, for haz

- comm costs, annual shipments of about 10,000 kilograms per site

. Costs are not otherwise adjusted for the nature of the chemical or process, volume, location, or other firm

specific or chemical

- specific factors.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### As mentioned above, costs are estimated for one chemical at one site, not for aggregate production

. Resources were not available to estimate aggregate costs . Among other things, it is not known how many firms are affected by the SNURs. EPA receives a handful of Significant New Use Notices per year due to SNURs. However, if a SNUR chemical is on the TSCA Inventory, a firm may use the chemical in a way that avoids a Significant New Use (Option 1), and never make a submission. It is not known how many firms are affected but do not make a submission . Also, it is not known whether firms avoid the chemical altogether specifically due to the SNUR

. However, at least for the years immediately following SNUR promulgation, these numbers are likely to be small

. This is because the chemicals in this type of SNUR rulemaking are still relatively new – as Appendix A indicates, most were submitted to EPA as PMNs in the past four Federal fiscal years – and, in addition, often have confidential chemical identities.

• For firms manufacturing, importing, or processing within SNUR restrictions to avoid a Significant New Use (Option 1), quantifiable costs can range from about $1,200 (if the only added cost is for recordkeeping) to over $37,000 per chemical if the firm must add worker protection measures such as gloves, protective clothing, and respirators that it would not otherwise use

. Most chemicals are also subject to costs that could be significant but are not quantified in this report, such as restrictions on releases to water or on other aspects of use.

• For submissions to EPA (Options 2, 3, and 4), the basic one- time submission cost is estimated at $6,071, including recordkeeping for the submission. For the SNUN (Option 3), EPA also collects a $2,500 fee.

• One objective of the rule is that EPA will be able to regulate prospective manufacturers, importers, or processors of a listed chemical substance before the described significant new use of that chemical substance occurs, provided that regulation is warranted pursuant t o TSCA sections 5(e), 5(f), 6 or 7 . Consequently, after submitting a SNUN, the firm may need to comply with restrictions as a result of the SNUN review process, possibly leading to further costs similar to those in Option 1.

• Rarely , f irms may choose to per form toxicity and/or environmental fate testing to support a SNUN (Option 3) . S uch testing is not mandatory. C osts for such testing are expected to be zero for most SNUNs and expected to be l ow for the few SNUNs for which a submitter might voluntarily perform such testing.

• Companies that might have manufactured, imported, or processed a chemical in the absence of the SNUR may incur “hidden” costs, such as loss of profits from delayed or foregone sales, if they avoid the chemical altogether (Option 5)

. T hese costs were not quantified.

• Companies may incur costs from more than one Option, for example if they temporarily produce in conformance with SNUR restrictions while submitting a SNUN and waiting the required 90 days plus any extensions

. For some firms, costs may be attributable to EPA’s New Chemicals review process, but not to the SNUR itself . For example, a firm may already be bound by a TSCA Section 5(e) Consent Order following review of its PMN, so that the SNUR based on the 5(e) order imposes no add ed costs for that firm

. As another example, in rulemakings where a SNUR chemical is not on the TSCA Inventory, firms that haveEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### not yet submitted a PMN must submit one to EPA before commercial production/import, with or without the SNUR (see Section 2.3 , SNUR “New” Chemicals)

. If the SNUR reflects the PMN use scenario, and the PMN submitter would stick to the PMN uses even in the absence of a SNUR, then there would be no added costs for the PMN submitter attributable to the SNUR . Also, firms may also incur worker protection, haz -comm and other costs for reasons other than the SNUR, so that SNUR requirements may impose no added costs. 6

6 Earlier SNUR economic analyses calculated possible haz

- comm, worker protection, testing, and other costs for each PMN chemical ( EPA, 2007b , Ta bles 9, 10, D

- 4)

. The chemical

- specific tables were dropped from a later SNUR economic analysis ( EPA, 2007c )

. They reflected SNUR requirements and “recommended” testing, but were not otherwise tailored to the particular situation, and so were unreliable predictors of actual SNUR costs.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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## 3 Export Notification Costs
Under Section 12(b) of TSCA, exporters must notify EPA if they export or intend to export a chemical subject to various TSCA sections (40 CFR §707.60 through 75). For TSCA 5(a)(2) (the section under which EPA promulgates significant new use rules) and certain other TSCA sections, this is a one

- time notification requirement 7 

### per destination country for each exporter of a chemical substance. After receiving a notification from a firm, EPA notifies the importing country and the United States State Department (40 CFR §707.70). To calculate the burden associated with making export notifications, EPA first estimated the average annual number of export notificatio ns made by an exporter, in Section 3.1

. EPA then derived the annual and per notification burden associated with preparing and submitting an export n otification, in Section 3.2

. 8 

### EPA estimated the average burden associated with making a single notification, but did not estimate either the total number of exporters of a SNUR chemical or the number of notifications per SNUR chemical

. This is because the SNURs apply to a variety of different chemicals with a variety of unrelated uses, manufactures, and processors, making it impractical within the r esources available for this report to assess the potential number of exporters and importing countries per chemical

. Most underlying data in this section come from the 2009 TSCA Section 12(b) ICR, ICR No.: 0795.13 [Information Collection Request for] Notification of Chemical Exports - TSCA Section 12(b) Supporting Statement for Request for OMB Review under the Paperwork Reduction Act (EPA, 2009b), with updating for inflation

. 

### 3.1 E stimated Number of Annual Export Notifications per Exporter
EPA ’s 2009 TSCA Section 12(b) ICR estimated that th e average exporter making notifications will make 12 notifications per year

. 9 

### This includes notifications resulting from SNURs and notifications resulting from other TSCA activities

. A notification is typically no more than one page per chemical/country combination, and one notification mailing often include s multiple chemicals and/or destination countries. 10

7 On November 14, 2006, EPA revised the export notification requirement for chemicals subject to TSCA §5(a)(2), 5(b), 5(e)(1) and 5(e)(2) from an annual to a one

- time requirement per destination country for each exporter (November 14, 2006, 71 FR 66234). 8 Beginning with this report ( Economic Analysis of Expedited Significant New Use Rules for 2 5 Chemical Substances: EPA Docket OPPT

- 2009

- 0922 ) , the cost per notification is presented as well as the cost for the average submitter making export notifications. 9 EPA calculated the average number of export notifications per exporter in the 2009 TSCA Section 12(b) ICR (EPA, 2009b) by dividing the estimated number of submitted notifications (3,500) by the estimated number of exporters (300 ). 10 Based on review by an EPA economist of notifications received under TSCA Sections 4, 5 and 6 over approximately three weeks in early 2010.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### The percent of notifications due to PMN SNURs is unknown, and it is also unknown how many
n otifications may result from this rulemaking , as not all manufacturers may choose to export a chemical, or they may make several notifications for a single chemical.


### 3.2 Exporter Costs The 2009 TSCA Section 12(b) ICR (EPA, 2009b, page 11, Ta ble 3), estimated the annual export notification cost for an exporter under the one-time export notification requirement. These costs include the cost to the exporter of compiling a list of their products that are subject to TSCA Section 12(b) requirements , writing or revising an export notification letter to EPA, checking the outgoing shipments, and sending the notification letters with the associated shipping costs. The per -notification cost was calculated based on the average burden per firm making notif ications

. Exporters making more notifications per year may benefit from economies of scale and have lower costs per notification; those making fewer notifications may have higher costs per notification.
3.2.1 Estimated Submission (Mailing) Costs
Regulated companies will incur mailing costs for export notifications delivered to EPA. Notifications are assumed shipped via the U.S. Postal Service (USPS) as first

- class registered mail with a return receipt (USPS, 2012). The estimated per -shipment and annual mailing costs incurred by individual submitters are detailed in Table 9

. Table 9. Derivation of Total Mailing Cost for 12 Notices
P ostal Service Cost Registered mail, regular, with $0 declared value $10.95 Return receipt, requested at time of mailing (receive by mail) $2.35 Postage, regular First Class, up to 1 ounce $0.45 Cost per export notice

- Subtotal $13.75 × 12 Total Mailing Cost for 12 Notices $165.00
Source: Mailing rates are from the US Postal Service web site as of March 2012 ( https://www.usps.com/ship/service

- chart.htm )

. The mailing method comes from the Economic Analysis of the Proposed Change to TSCA Section 12(b) Export Notification Requirements, November 2005 (EPA, 2005a) , as clarified in a later SNUR economic analysis (EPA, 200 7 c, Table 8 ).



### 3.2.2 Compile and Maintain the List of Products
Since TSCA §12(b) information collection activity has been in place for over twenty years, most respondents will have already developed a list of their products subject to TSCA §12(b) export notification

. Respondents need only check for new regulations promulgated and any new products exported by the company. Updating the list is estimated to take an average of one hour of technical time, which may also include some proportion of legal time (EPA, 2009b). The total burden can vary from two hours per year up to two hours per month, depending on the number of products exported by the company and the number of their products subject to TSCA §12(b) (EPA, 2009b ).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA
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### The number of submitters per year who report under TSCA §12(b) has varied over time, rising from around 160 in 1991 to over 460 in 2000, and declining since. In the most recent TSCA §12(b) ICR, EPA estimated there would be approximately 300 submitters per year in near-future years (EPA, 2009b). Of these 300 submitters, EPA estimated that 200 companies were near the lower b urden estimate of 2 hours per year, and 100 companies were near the upper estimate of 24 hours per year. Compiling the list for all respondents was therefore estimated to take 2,800 hours (2 hours × 

### 200 firms plus 24 hours × 

### 100 firms), or an average of ab out 9.3 hours of technical time per firm per year for 12 notifications per year (EPA, 2009b ).
3.2.3 Write or Revise Export Notification
Companies that export chemicals subject to TSCA §12(b) reporting must prepare an export notification to send to EPA when expor t shipments are made. Time for initial preparation of the export notice may vary depending on whether the company has prior experience with this requirement. This step is estimated to take an average of one hour of technical time (which may also include so me proportion of legal time) per firm per year for 12 notifications per year (EPA, 2009b ).
3.2.4 Check Orders and Send Notifications
Companies that export chemicals subject to TSCA §12(b) reporting must check outgoing shipments against the list of their products described above . A form letter notifying EPA and providing the required data must be printed and mailed within the required time period. This process is estimated to take an average one half hour of clerical time per export notification or 6 hours for 12 notifications (EPA, 2009 b). The burdens and associated costs for each notification activity are provided in Table 10 below

. Table 10

. TSCA 12(b) Export Notification Cost per Notification
Technical Clerical Total $/Hr Hours 201 1$ $/Hr Hours 201 1$ 201 1$ Hours Compile list $64.66 9.3 $601

-- -- -- $601 9.3 Write letter $64.66 1 $64.66

-- -- -- $65 1 Check order and send

-- -- -- $29.63 6 $178 $178 6 Mailing cost 1

-- -- -- -- -- -- $16 5

- Total per facility 2` 10.3 $666 6 $178 $1,00 9 16.3 Total per Notification 0.86 $55.50 0.50 $14.81 $ 84.06 1.36
Notes:

1 Mailing costs reflect March 2012 USPS rates and can be found in Table 9

. 2 An average facility submitting notifications is assumed to submit 12 export notifications per year.
Source: Appendix B of this report derives technical and clerical hourly labor costs

. Other costs are from ICR No.: 0795.13 [Information Collection Request for] Notification of Chemical Exports - TSCA Section 12(b) Supporting Statement f or Request for OMB Review under the Paperwork Reduction Act (EPA, 2009 b , p.10), and are updated to 2011 dollars

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## 4 Agency Costs
This SNUR is expected to generate Agency costs for both SNUN review and processing, and export notification processing

. Because it is unknown how many SNUNs and export notifications will be submitted as a result of this rulemaking, all Agency costs are estimated at the per

- case level and are not aggregated to estimate the total Agency burden. Sectio n 4.1 describes the burden to the Agency of reviewing and processing a single SNUN submission . Section 4.2 derives the Agency burden of processing and reviewing export notifications.


### 4.1 SNUN Processing Costs EPA’s costs to review and process industry submissions (SNUNs, requests to modify or revoke the SNUR, and requests for equivalency determinations) are assumed to be the same as EPA costs to review PMNs and are presented in Table 11

. Costs to review and process industry submissions – SNUNs, requests to modify a SNUR, and requests for equivalency determination – are assumed to be simila r to EPA costs to review PMNs. 11 

### The list of review steps, es ti mates of staff

- year full

- time equivalents (FTEs), estimates of extramural costs, and the percent of chemicals requiring a particular review step are derived from the costs for processing PMN sub missions in Table VII -1 of a 1994 EPA report, Regulatory Impact Analysis of Amendments to Regulations for TSCA Section 5 Premanufacture Notifications (EPA, 1994). The Agency burden associated with processing a SNUN has been adjusted to reflect burden reduc tions resulting from the 2009 final PMN Electronic Reporting (ePMN) Rule that requires the electronic submission of all TSCA section 5 notices. 12 

### The ePMN rule affects SNUN submissions and requests for equivalency determination, but not requests to modify o r revoke a SNUR

. However, for simplicity, this analysis continues to assume that Agency per

- submission costs are the same for all three types of submissions

. Electronic submission of SNUN forms is expected to reduce Agency burden by 16.5 percent (EPA, 2009a, p.28). The GS levels used for Agency staff reflect the judgment of Agency staff familiar with the PMN/SNUN review process

. The salary of a Full Time Equivalent EPA staff was calculated using GS -13 Step 5 salary data (OPM, 201 1). The original PMN cost estimates were for GS 12 and were presented as low and high estimates, based on the most junior (Step 1) and the most senior (Step 10) GS

- 12 pay rates, respectively

. However, this analysis uses the higher GS

- 13 staff level and, for simplicity, a single intermediate pay rate (Step 5) within that GS level

. A loading factor of 1.6 was applied to the salary to reflect fringe benefits and overhead (EPA, 1992). The loaded salary calculations are described in Appendix B.

11 For an overview of the PMN review process, see the Chemistry Assistance Manual for Premanufacture Notification Sub mitters, EPA, 1997.

12 Economic Analysis of Expedited Significant New Use Rules for 2 5 Chemical Substances: EPA Docket OPPT

2009

- 092 2, was the first report to consider the burden reductions resulting from electronic submission of SNUN forms and requests for equivalency determination

. Previously , all burdens were based upon 1994 paper submission estimates

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### For each review step, the “EPA staff” cost is calculated by multiplying the number of FTEs (in the first column) by the fully loaded average salary

. This shows EPA staff cost for chemicals requiring the selected review step. The Extramural Cost column shows costs for contractor support and other outside purchases for chemicals requiring the selected review step, inflated from 1993 prices, as explained in Appendix B

. The Percent of Cases is a weighting factor applied to reflect the fact that not all chemicals require each review step

. For example, in the PMN process, all chemicals require Administrative Prescreening, but not all chemicals require the intensive scrutiny of “Standard Review.” The three types of submissions resulting from a SNUR may have weighting factors that differ from each other and from the weighting factors for PMNs

. Changes in weighting factors could cause actual review costs to be higher or lower than calculated here

. Fo r example, some SNUNs require little review because they are determined to be “invalid” – i.e. not required in the first place

. However, often a SNUN may take more Agency time than a typical PMN because of factors such as the need to retrieve old PMN records from archives, and the likelihood that more data requiring EPA review is submitted with a SNUN than would be submitted on average with a PMN

. Resources were not available to update the review hours to reflect the current review process or to tailor the cost estimates to SNUNs

. Therefore, for this analysis, the review steps and weighting factors are assumed to be the same as those derived in 1994 for PMNs. The Weighted Cost column is calculated by multiplying the Unweighted Costs (EPA staff cost plus extr amural costs) by the percentage of cases requiring this review step

. Weighted costs are then multiplied by the burden reduction of 16.5 percent to account for burden savings generated electronic submission. This calculation yields total Agency costs for su bmission review and processing shown in Table 11

.Economic Analysis of Expedited New Use Rule for 107 Chemical Sub stances (EPA Docket EPA

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### Table 11 . Agency Costs for SNUN and Other Submission Review and Processing

view Steps EPA staff (FTE) Cost Extramural Cost 2 Unweighted Cost Pct. of Cases Weighted Cost 3 ePMN Burden Reduction 4 Weighted Cost with ePMN Burden Reduction FTE fraction Cost per FTE 1 FTE Total ( 201 1 $ ) 1993 $ 201 1$ (a) (b) (c)=(a)*(b) (d) (e) (f)=(c)+(e) (g) (h)=(f)*(g) (i) (j)=(h)*(1-(i)) Pre

- notice C onsultation 0.0024 $161,446 $387 $4.00 $6.91 $394 41% $162 0.165 $135 Administrative Prescreen/Notice R eceipt/ U ser F ee 0.0024 $161,446 $387 $92.00 $158.87 $546 100% $546 0.165 $456 CRSS (Chemical Review and Search Strategy) 0.0025 $161,446 $404 $268 $462.80 $866 100% $866 0.165 $723 SAT (Structure Activity Team) 0.0006 $161,446 $96.87 $14.00 $24.18 $121 100% $121 0.165 $101.07 Engineering/Exposure 0.0015 $161,446 $242 $56.00 $96.70 $339 100% $339 0.165 $283 Exposure/Fate 0.0008 $161,446 $129 $0.00 $0.00 $129 100% $129 0.165 $108 Focus 0.0009 $161,446 $145 $23.00 $39.72 $185 100% $185 0.165 $154 Standard Review Functions 0.0219 $161,446 $3,536 $511 $882.43 $4,418 29% $1,281 0.165 $1,070 Division Directors Meeting 0.0129 $161,446 $2,083 $113 $195.14 $2,278 15% $342 0.165 $285 Order Development/Negotiation Review 0.0171 $161,446 $2,761 $22.00 $37.99 $2,799 3% $83.96 0.165 $70.11 Post Order Data Review 0.0886 $161,446 $14,304 $0.00 $0.00 $14,304 3% $429 0.165 $358 Order Modification 0.2167 $161,446 $34,985 $0.00 $0.00 $34,985 3% $1,050 0.165 $876 New Chemical SNUR Development 0.0277 $161,446 $4,472 $85.00 $146.78 $4,619 7% $323 0.165 $270 Notices of Commencement 0.0012 $161,446 $194 $40.00 $69.07 $263 31% $81.47 0.165 $68.03 FOIA (Freedom of Information Act) Requests 0.0333 $161,446 $5,376 $287 $495.61 $5,872 1% $58.72 0.165 $49.03 CBI (Confidential Business Information) Substantiation 0.0004 $161,446 $64.58 $3.00 $5.18 $69.76 100% $69.76 0.165 $58.25
TOTAL $6,067 0.165 $5,066
Notes:

1 GS

- 13 Step 5 salaries loaded with benefits and overhead

. See Table B -1 derivation.

2 Extramural costs consist of contracting support and other purchases directly attributable to the PMN review process inflated from 1993 prices as described in Appendix B

. 3 Weighted costs were calculated using unrounded unit cost estimates, so results may differ from calculations using the rounded values shown in this tabl e.

4 Electronic submission is expected to generate a cost savings of 16.5% to the Agency (EPA 2009a, p. 28). Sources: FTEs per review step, 1993 extramural costs, and percent of cases are from EPA, 1994 Table VII

- 1, GS

- 13 salaries are from OPM, 2011

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### 4.2 Export Notification Processing Burden Under TSCA Section 12(b), exporters must notify EPA if they intend to export chemicals sub ject to SNURs, as described in Chapter 3 above. The Agency burden and cost due to TSCA §12(b) export notification result from three tasks

. In the first task, EPA receives export notifications from companies that intend to export one of the chemicals subject to TSCA §12(b) (EPA, 2009b). In the second task, EPA staff prepares separate notification letters that are subsequently reviewed and delivered to importing countries, their embassies, or representatives , and to the importing country’s US embassies (EPA, 2009b). (S ee Table 9 for the cost of mailing one notification). The third task is comprised of EPA staff response s to public inquiries and other TSCA 12(b) activities. The work of responding to non- routine requests for information and clarification from industry and importing countries, and of handling other tasks associated with the TSCA §12(b) program, was estimated to require roughly 400 hours per year (EPA, 2009b). Since the current rulemaking covers only a very small percent of the chemicals subject to TSCA 12(b) reporting, a very small percent of such activity will be attributable to the current rulemaking.

Beca use it is unknown how many, if any, notifications EPA will receive or send as a result of the current rulemaking, the costs to the Agency are presented per activity

. 13 

### The burden for the first two A gency activit ies is provided in Table 12 below

. To estimate the Agency cost, hourly burden s are multiplied by the loaded wage rate of a GS -13, Step 5, which is derived in Appendix B

. Table 12

. TSCA 12(b) Export Notification Cost: Agency Burden per Activity ( 201 1 $)

Agency Activity Hours per Activity FTE per Activity1 Loaded GS

- 13, Step 5 FTE Wage Rate Mailing Cost Total Agency Cost per Activity
(a) (b) = (a)/2,080 (c) (d) (e) = ((b)*(c))+(d) Process an incoming notification from an exporting company 0.1 0.000048 $161,446 $7.76

Prepare and mail a notification to an importing country 0.5 0.000240 $161,446 $13 .75 $52. 56

Notes:
1 The burden associated with an Agency activity is the burden for the Agency to process one incoming notification, or to prepare and mail an outgoing notification Source: Appendix B of this report derives Agency labor costs

. Mailing costs are from Table 9 of this report. Other burdens are from ICR No.: 0795.13 [Information Collection Request for] Notification of Chemical Exports - TSCA Section 12(b) Supporting Statement for Request for OMB Review under the Paperwork Reduction Act (EPA 2009b), updated for inflation

.

13 Beginning with th e report Economic Analysis of Expedited Significant New Use Rules for 2 5 Chemical Substances: EPA Docket OPPT

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- 0922 , the Agency cost per activity is presented, and not the entire Agency costs resulting from export notifications.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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## 5 Additio nal Analyses

This chapterpresents additional analysis of other potential impacts of this rulemaking, as required under various statutes and executive orders.


### 5.1 Regulatory Flexibility Act (RFA) The Regulatory Flexibility Act (RFA) (5 U.S.C. 601 et. seq.), as amended by the Small Business Regulatory Enforcement Fairness Act, requires regulators to consider the impact of regulations on small entities, in particular small businesses . The requirement to submit a SNUN applies to any person (including small or large entities) who intends t o engage in any activity described in the rule as a significant new use. Where a use is new, by definition no small or large entities presently engage in such activities. Although some small entities may decide to manufacture or process a substance for the new use after the SNUR is promulgated, EPA receives very few SNUNs, and few of those are submitted by small entities. In response to the promulgation of SNURs covering over 1000 chemical substances, the Agency receives only a handful of SNUNs per year. Fo r example, the number of SNUNs was four in Federal fiscal year 2005, eight in FY2006, six in FY2007, eight in FY2008, seven in FY2009, two in 2010, and ten in 2011 (EPA, 2012), for an average of 6 per year from all SNURs. EPA has no reason to believe that this SNUR would alter the pattern of SNUN submissions that EPA has historically seen. In addition, the estimated reporting cost for submission of a SNUN is minimal regardless of the size of the firm, averaging about $ 8,6 00 including SNUN recordkeeping and reporting costs. The Agency currently offers some relief to certain small businesses with sales (including those of subsidiary/parent companies) of less than $40 million per year by reducing the SNUN submission fee from $2,500 to $100. This lower fee reduces the cost of submitting a SNUN to about $6,2 00 for smaller firms. During the six year period from 2005-2010, only three submitters self- identified as small in their SNUN submission 14 

### (EPA, 2012). EPA believes the cost of subm itting a SNUN is relativ ely sm all compared the cost of developing and marketing a chemical new to firm and that the requirement to submit a SNUN generally does not have a significant economic impact. In response to a SNUR, firms could also decide to request an equivalency determinatio n or a request for SNUR modification or revocation. The submission cost for these requests is about $6,100 . EPA believes this cost to be low compared to the cost of developing and marketing a chemical new to the firm. The expected number of requests is als o expected to be small. In general, EPA receives from zero to three modification/revocation requests per year due to SNURs, therefore it is unlikely that a substantial number of small entities would be affected.


### 5.2 Unfunded Mandates Reform Act (UMRA)
EPA has determined that this regulatory action does not impose any enforceable duty, contain any unfunded mandate, or otherwise have any effect on small governments subject to the requirements of sections 202, 203, 204, or 205 of the Unfunded Mandates Reform Act of 1995 (Public Law 104-4).

14 The three “small” submitters were identified by review of actual SNUN submissions from the years 2005

- 2010.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### 5.3 Paperwork Reduction Act (PRA) According to the Paperwork Reduction Act (PRA), 44 USC 3501 et seq., an agency may not conduct or sponsor, and a person is not required to respond, to a collection of information that requires Offic e of Management and Budget (OMB) approval under the PRA, unless it has been approved by OMB and displays a currently valid OMB control number

. The information collection requirements related to this action have already been approved by OMB pursuant to the PRA under OMB control number 2070-0012 (EPA, 2007a). This action does not impose any additional burden requiring OMB approval.


### 5.4 Executive Order 12866, Regulatory Planning and Review Executive Order 12866, Regulatory Planning and Review, requires OMB review for rules with an impact on the economy of $100 million or more, or with any other potential significant impact. OMB has previously determined that these types of SNURs are not a “significant regulatory action” that would require OMB review under this Executive Order.


### 5.5 Executive Order 13132, Federalism Executive Order 13132, Federalism (64 FR 43255, August 10, 1999), requires EPA to develop an accountable process to ensure “meaningful and timely input by State and local officials in the development of regul atory policies that have federalism implications.” This action will not have a substantial direct effect on States, on the relationship between the national government and the States, or on the distribution of power and responsibilities among the various l evels of government, as specified in Executive Order 13132, entitled Federalism (64 FR 43255, August 10, 1999).


### 5.6 Executive Order 12898, Environmental Justice This action does not involve special considerations of environmental justice related issues as requ ired by Executive Order 12898, Federal Actions to Address Environmental Justice in Minority Populations and Low -Income Populations (59 FR 7629, February 16, 1994).


### 5.7 Executive Order 13045, Protection of Children Executive Order 13045, Protection of Children from Environmental Health Risks and Safety Risks (62 FR 19885, April 27, 1997), requires EPA to identify and assess environmental health and safety risks that may disproportionately affect children

. This type of analysis is required for rules that will have an impact of $100 million or more only. The impact of these SNURs will be less than $100 million and therefore no analysis of such impacts on children is required.


### 5.8 Executive Order 13175, Tribal Governments
Executive Order 13175 is Consultation and Coordination with Indian Tribal Governments (59 FR 22951, November 6, 2000). This rule does not have Tribal implications because it is not expected to have substantial direct effects on Indian Tribes.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### 5.9 Executive Order 13211, Energy Supply, Distribution, or Use This rule is not subject to Executive Order 13211, entitled Actions Concerning Regulations That Significantly Affect Energy Supply, Distribution, or Use (66 FR 28355, May 22, 2001), because this action is not expected to affect energy supply, distribution, or use.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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## APPENDIX A: List of PMNs and their Chemical Names
Table A -1. PMNs and Chemical Names Referenced in this Economic Analysis

No
. PMN 1 CAS RN 2 Name 2 1 P

- 96

- 308 N/A Aminoalkanol (generic) 2 P

- 96

- 1021 206565

- 90

- 4 Fatty acids, C 18 - unsatd., dimers, reaction products with 1

- 3 P

- 96

- 1022 206565

- 89

- 1 Fatty acids, C 18 - unsatd., dimers, reaction products with 1

- 4 P

- 97

- 823 N/A Tetra alkyl ammonium salt (generic) 5 P

- 98

- 141 N/A Phosphoric acid ester (generic)

6 P- 98

- 142 N/A Phosphoric acid ester (generic)

7 P

- 98

- 1028 24748

- 23

- 0 1,2,4,5,7,8

- Hexoxonane, 3,6,9

- triethyl

- 3,6,9

- trimethyl

8 P

- 99

- 184 559

- 40

- 0 Cyclopentene, 1,2,3,3,4,4,5,5

- octafluoro

9 P

- 99

- 214 15290

- 77

- 4 Cyclopentane, 1,1,2,2,3,3,4

- heptafluoro

10 P

- 99

- 1179 73936

- 80

- 8 Phenol, 2

- (1

- methyl

- 1

- phenylethyl)

- 4

- (1,1,3,3

- tetramethylbutyl)

- 11 P

- 99

- 1217 N/A Amine neutralized phosphated polyester (generic) 12 P

- 99

- 1218 N/A Amine neutralized phosphated polyester (generic) 13 P

- 99

- 1280 N/A Sulfonic acid, linear xylene alkylate, mono, sodium salt (generic) 14 P

- 99

- 1281 N/A Sulfonic acid, linear xylene alkylate, mono, sodium salt (generic) 15 P

- 99

- 1282 N/A Sulfonic acid, linear xylene alkylate, mono, sodium salt (generic) 16 P

- 00

- 346 N/A Dialkyl hydroxybenzenealkanoic acid ester (generic) 17 P

- 00

- 635 4427

- 96

- 7 1,3

- Dioxolan

- 2

- one, 4

- ethenyl 18 P

- 00

- 1165 200013

- 65

- 6 Diphosphoric acid, polymers with ethoxylated reduced Me esters of reduced 19 P

- 01

- 382 309934

- 68

- 7 1,2

- Benzenedicarboxylic acid, di

- C7

- 14

- branched and linear alkyl esters 20 P

- 01

- 383 309934

- 69

- 8 1,2

- Benzenedicarboxylic acid, di

- C6

- 14

- branched and linear alkyl esters 21 P

- 01

- 470 N/A Ethoxylated alkylphenol sulfate, ammonium salt (generic) 22 P

- 01

- 499 63947

- 56

- 8 Propanol, mercapto

23 P

- 01

- 500 374078

- 75

- 8 2

- Propen

- 1

- ol, reaction products with hydrogen sulfide, distn. residues 24 P

- 01

- 762 4277

- 06

- 9 1,9

- Cyclohexadecadiene 25 P

- 01

- 829 34748

- 97

- 5 17

- Oxabicyclo[14.1.0]heptadec

- 8

- ene 26 P

- 02

- 120 N/A Acetic acid, hydroxymethoxy

- , methyl ester, reaction products with 27 P

- 02

- 172 N/A Aromatic polyester polyol (generic) 28 P

- 02

- 285 100402

- 91

- 3 Oxirane, 2

- [[3

- (trimethoxysilyl)propoxy]methyl]

- , reaction products with 29 P

- 02

- 436 N/A Alkyd amide polyol (generic) 30 P

- 02

- 659 3865

- 34

- 7 9

- Octadecenoic acid (9Z)

- , 1,1'

- (dimethylstannylene) ester 31 P

- 02

- 796 N/A Polyglycerin alkyl ether (generic) 32 P

- 02

- 828 N/A Propoxylated ethoxylated alkylamine (generic) 33 P

- 03

- 61 87093

- 13

- 8 Oxirane, 2,2',2''

- [ethylidynetris(4,1

- phenyleneoxymethylene)]tris

34 P

- 03

- 104 N/A Tristyryl phenol alkoxylate salt (generic) 35 P

- 03

- 154 464920

- 01

- 2 1,2

- Benzenedicarboxylic acid, mixed esters with benzyl alc., cyclohexanol , 2

- 36 P

- 03

- 238 N/A Acrylate of hydroxyimide (generic) 37 P

- 03

- 282 N/A Amino

- substituted carbopolycycle (generic) 38 P

- 03

- 307 N/A Azo nickel complex (generic)Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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June 18, 2012 A-2 No
. PMN 1 CAS RN 2 Name 2 39 P

- 03

- 325 66204

- 44

- 0 Oxazolidine, 3,3'

- methylenebis[5

- methyl

40 P

- 03

- 354 1577

- 03

- 3 1

- Penten

- 3

- one, 1

- (4

- chlorophenyl)

- 4,4

- dimethyl

41 P

- 03

- 388 N/A Fatty acid amides (generic) 42 P

- 03

- 461 N/A Fatty acid, reaction products with alkanolamine (generic) 43 P

- 03

- 561 115372

- 36

- 6 2

- Propenoic acid, 2

- methyl

- , 3

- hydroxytricyclo[3.3.1.13,7]dec

- 1

- yl ester 44 P

- 03

- 563 209982

- 56

- 9 2

- Propenoic acid, 2

- methyl

- , 2

- ethyltricyclo[3.3.1.13,7]dec

- 2

- yl ester 45 P

- 03

- 564 216581

- 76

- 9 2

- Propenoic acid, 3

- hydroxytricyclo[3.3.1.13,7]dec

- 1

- yl ester 46 P

- 03

- 565 249562

- 06

- 9 2

- Propenoic acid, 2

- methyltricyclo[3.3.1.13,7]dec

- 2

- yl ester 47 P

- 03

- 566 303186

- 14

- 3 2

- Propenoic acid, 2

- ethyltricyclo[3.3.1.13,7]dec

- 2

- yl ester 48 P

- 03

- 567 220689

- 12

- 3 Phosphonium, tetrabutyl

- , 1,1,2,2,3,3,4,4,4

- nonafluoro

- 1

- butanes ulfonate 49 P

- 03

- 622 64194

- 22

- 5 2

- Propenoic acid, 1,1'

- (3

- methyl

- 1,5

- pentanediyl) ester 50 P

- 03

- 645 652968

- 34

- 8 1,3

- Benzenedimethanamine, polymers with epichlorohydrin

- polyethylene 51 P

- 03

- 865 499781

- 63

- 4 1

- Propanaminium, 3

- amino

- N

- (2

- carboxyethyl)

- N,N

- dimethyl

- , N

- coco acyl 52 P

- 04

- 107 N/A Substituted amin oethane sulfonic acid salt (generic) 53 P

- 04

- 118 659733

- 29

- 6 Hexanedioic acid, compd. with N1

- (6

- aminohexyl)

- N1

- methyl

- 1,6

- 54 P

- 04

- 275 78385

- 26

- 9 Oxetane, 3

- (bromomethyl)

- 3

- methyl

55 P

- 04

- 290 N/A Acrylate ester (generic) 56 P

- 04

- 318 N/A Polyether polyol (generic) 57 P

- 04

- 335 308074

- 73

- 9 Quaternary ammonium compounds, tris(hydrogenated tallow alkyl)methyl, 58 P

- 04

- 384 N/A Trimethylolpropane polyol, aminated (generic) 59 P

- 04

- 429 630106

- 01

- 3 Siloxanes and Silicones, Me vinyl, hydroxy

- terminated, reaction products 60 P

- 04

- 430 630106

- 00

- 2 Siloxanes and Silicones, di

- Me, Me vinyl, hydroxy

- terminated, reaction 61 P

- 04

- 431 630106

- 04

- 6 Siloxanes and Silicones, di

- Me, Me vinyl, hydroxy

- terminated, reaction 62 P

- 04

- 432 630106

- 02

- 4 Siloxanes and Silicones, Me vinyl, hydroxy

- terminated, reaction products 63 P

- 04

- 479 N/A Reaction products of alcohols, alkyl alcohols, amino alcohols and methanol 64 P

- 04

- 591 N/A Alkyl substituted amino

- benzamide (generic) 65 P

- 04

- 599 N/A Alkylbenzenes sulfonic acids, metal salt (generic) 66 P

- 04

- 600 N/A Alkylbenzenes sulfonic acids, metal salt (generic) 67 P

- 04

- 605 N/A Alkylbenzenes sulfonic acids, metal salt (generic) 68 P

- 04

- 606 N/A Alkylbenzenes sulfonic acids, metal salt (generic) 69 P

- 04

- 636 N/A Cuprate, [[[[[[[(sulfonaphthalenyl)]azo]

- (substitutedphenyl)]azo]

- 70 P

- 04

- 718 N/A Substituted aryl sulfonium polyfluorophosphate salts (generic) 71 P

- 04

- 834 N/A HDI biuret, hydroxyethyl methacrylate prepolymer (generic) 72 P

- 05

- 55 5445

- 77

- 2 Benzenepropanal,.alpha.

- methyl

73 P

- 05

- 301 N/A Trisphenol (generic) 74 P

- 05

- 417 N/A Tris

- alkyl

- alkoxy melamine polymer (generic) 75 P

- 05

- 501 N/A Reaction product of trimethylolpropane triacrylate and alkylene imine 76 P

- 05

- 634 N/A Metal silicate (generic) 77 P

- 06

- 9 N/A Amino alkoxy polydimethylsiloxane, hydroxy

- terminated (generic) 78 P

- 06

- 276 N/A Substituted alkyl ester, hydrolysis product with silica and substituted silane 79 P

- 06

- 279 N/A Substituted alkyl ester, hydrolysis product with silica and substituted silane 80 P

- 06

- 277 N/A Substituted alkyl ester, hydrolysis product with silica (generic) 81 P

- 06

- 280 N/A Substituted alkyl ester, hydrolysis product with silica (generic)Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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June 18, 2012 A-3 No
. PMN 1 CAS RN 2 Name 2 82 P

- 06

- 278 N/A Substituted silane, hydrolysis product with silica (generic) 83 P

- 06

- 281 N/A Substituted silane, hydrolysis product with silica (generic) 84 P

- 06

- 341 N/A Acrylated mixed metal oxides (generic) 85 P

- 06

- 542 N/A Tridecyl phthalate (generic) 86 P

- 06

- 616 N/A Modified triethylene glycol dithiol (generic) 87 P

- 06

- 622 5395

- 01

- 7 1,2

- Ethanediol, 1

- carbamate 88 P

- 06

- 682 N/A Surface modified magnesium hydroxide (generic) 89 P

- 06

- 694 882693

- 50

- 7 Phosphoric acid, mixed mono

- and diesters with 2

- ethyl

- 1

- hexanol and 90 P

- 07

- 11 N/A Alkylated phenol (generic) 91 P

- 08

- 29 N/A Alkylated phenol (generic) 92 P

- 07

- 107 N/A Biphenyl substituted benzopyran (generic) 93 P

- 07

- 161 N/A Alkene substituted Bis phenol (generic) 94 P

- 07

- 204 870778

- 34

- 0 Pentane, 1,1,1,2,3,3

- hexafluoro

- 4

- (1,1,2,3,3,3

- hexafluoropropoxy)

- 95 P

- 07

- 319 N/A Alkylaminoalcohol (generic) 96 P

- 07

- 320 N/A Quaternary ammonium salt (generic) 97 P

- 07

- 321 N/A Quaternary ammonium salt (generic) 98 P

- 07

- 322 N/A Quaternary ammonium salt (generic) 99 P

- 07

- 323 N/A Quaternary ammonium salt (generic) 100 P

- 07

- 324 N/A Quaternary ammonium salt (generic) 101 P

- 07

- 563 N/A Fatty acid maleic acid amide (generic) 102 P

- 07

- 564 N/A Fatty acid maleic acid amide (generic) 103 P

- 07

- 599 N/A Aromatic acrylate monomer (generic) 104 P

- 07

- 679 6470

- 20

- 8 [1,1'

- Biphenyl]

- 2,2'

- disulfonic acid, 4

- [2

- (4,5

- dihydro

- 3

- methyl

- 5

- oxo
- 1

- 105 P

- 10

- 58 N/A Partially fluorinated alcohol substituted glycol (generic) 106 P

- 10

- 59 N/A Partially fluorinated alcohol substituted glycol (generic) 107 P

- 10

- 60 N/A Partially fluorinated alcohol substituted glycol (generic) Key: PMN = Premanufacture Notice

. CAS RN = Chemical Abstract Service Registry Number.

Notes:

1 The PMN number reflects the Federal Fiscal Year and sequence of submission. For example, those starting “P

- 07” were submitted in the twelve months ending September 31, 2007.

2 If a CAS RN is identified as “N/A” meaning “Not available” and/or the chemical name is indicated to be “generic” then the chemical identity is indicated to be confidential.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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June 18, 2012 B-1 

## APPENDIX B: Inflators and W age R ates This appendix describes the derivation of the fully loaded labor rates and inflation factors used in calculating costs of labor, materials, and other inputs. Costs for this report are for year -end 2011.


### B.1 Derivation of Loaded Wage Rates
Unit labor costs are calculated by adding fringe benefits and overhead to the wage or salary to derive a fully loaded labor cost. The basic method is described in Wage Rates for Economic Analysis of the Toxics Release Inventory Program (EPA, 2002b). The resulting loaded labor rates are give n in Table B -1

. Costs are calculated for several labor categories: Managerial, Professional/ Technical, Clerical, Production Workers, Industrial Hygienists, and EPA staff. In March 2004, BLS began using the North American Industry Classification System (NAICS) codes instead of the Standard Industrial Classification (SIC) System, and the Standard Occupational Classification (SOC) system instead of the Oc cupational Classification System (OCS)

. The following table shows the crosswalk between old and new occupational titles.
EPAB Reports Labor Category BLS Old Title (OCS) BLS New Title (SOC) Managerial Executive, administrative, and managerial Management, business, and financial

Professional/Technical Professional specialty and technical Professional and related

Clerical Administrative support, including clerical Office and administrative support

Source: Employer Costs for Employee Compensation: Changes to NAICS and SOC, Table 2

. ECEC Occupational Comparability between SOC and OCS (BLS, 2006a); and Weinstein, 2004.


### B.2 Derivation of Labor Rates for Managerial, Professional/Technical, Clerical, and Production L abor
Wages and fringe benefits for managerial, professional/technical, clerical and production labor were taken from the Bureau of Labor Statistics (BLS) Employer Costs for Employee Compensation (ECEC) data, 15 

### for December, for manufacturing industries. 16

15 This follows the approach introduced in Econo mic Analysis of Expedited Significant New Use Rules for 65 Chemical Substances: EPA Docket OPPT

- 2003

- 0063 (EPA, 2007b). In earlier PMN SNUR economic analyses, such as EPA, 2003a, wage rates for production workers came from the BLS National Employment, Hours, and Earnings, Average Hourly Earnings of Production Workers, while fringe benefits were taken from the ECEC data. Here, as in EPA, 2007b , both wages and fringes for production workers come from ECEC data, for better consistency with the method of estimating labor costs for other labor categories.

16 Employer Costs for Employee Compensation Supplementary Tables December 20 11 (BLS, 2012a). This follows the approach introduced in EPA, 2007b. Earlier PMN SNUR economic analyses, such a s EPA, 2003a, used ECEC data for “All Goods Producing” sectors (manufacturing, mining, and construction). However, the manufacturing sector data seem more relevant since the SNURs mainly affect the chemicals industry.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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June 18, 2012 B-2 

### Th e cost of fringe benefits such as paid leave and insurance, specific to each labor category, are taken from the same ECEC series

. Fringe benefits as a percent of wages are calculated separately for each labor category

. For example, for December 2011 , the average wage rate for professional/technical 17 

### labor was $38.48 ; the average fringe benefit was $19.64. Fringe benefits as a percent of wages were $19.64 /$ 38.48, or approximately 51.04%. An additional loading factor of 17 percent is applied to wages to acco unt for overhead

. This approach is used for consistency with Office of Pollution Prevention and Toxics economic analyses for two major rulemakings: Wage Rates for Economic Analyses of the Toxics Release Inventory Program (EPA, 2002b), and the Revised Econo mic Analysis for the Amended Inventory Update Rule: Final Report (EPA, 2002a). This overhead loading factor is added to the benefits loading factor, and the total is then applied to the base wage to derive the fully loaded wage

. For example, the December 2011 fully loaded wage for professional/technical labor is $38.48 × (1 + 0.5104 + 0.17) = $64.66. Fully loaded costs for managerial, clerical, and production labor are calculated in a similar manner, as shown in Tabl e B -1

. 

### B.3 Derivation of Labor Rates for Industrial Hygienists
For industrial hygienists, wages were based on another BLS data series, Occupational Employment Statistics [OES], National Industry

- Specific Occupational Employment and Wage Estimates

. OES data were used because ECEC data were not available for very specific occupations

. However, the OES data covers only wages, not fringe benefits

. Therefore, the Industrial Hygienist fringe benefits continue to be based on ECEC data. 18 

### The wage rate for Industrial Hygienists is a weighted average of the hourly mean wage for Occupational Health and Safety Specialists, Standard Occupational Classification (SOC) 29-9011, and Occupational Health and Safety Technicians, SOC 29 -9012, in Manufacturing. The wage rate for each occupation was weighted by employment for the occupation. The North American Industry Classification System (NAICS) codes for Manufacturing are 31, 32, and 33 (BLS, 2005). The calculations are shown in Table B-2

. As with other labor categories, the fringe benefits factor came from the BLS Employer Costs for Employee Compensation Suppleme ntary Tables December 2011 (BLS, 2012a)

. Benefits for “professional

17 This follows terminology introduced in EPA, 2007b. Earlier SNUR economic analyses used the term “technical” labor. Here the category is called “professional/technical” labor, to make clear how it relates to BLS categories. In 2004, BLS changed from the Occupational Classification System, OCS , to the Standard Occupational Classification system, SOC. In the process, the “Professional specialty and technical” category became the “Professional and related” category. However, the coverage of the old and new occupational groups is approximately the same. See the BLS article, C omparing Current and Former Industry and Occupation ECEC Series (Weinstein, 2004 ).

18 This follows the approach for calculating Industry Hygienist wages introduced in EPA, 2007b and is a change from the method used in earlier PM N SNUR economic reports such as EPA, 2003a, which used data from a 1997 professional journal salary survey.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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2011

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June 18, 2012 B-3 

### specialty and technical” occupations were used, and loaded wages were calculated as for other types of labor

. An additional loading factor of 17 percent of wages was applied for overhead

. Calculations are shown in Table B -1

. 

### B.4 Derivation of Labor Rates for EPA Staff
Agency labor costs are calculated based on annual Federal salaries for the Washington

- Baltimore area published by the Office of Personnel Management effective January 2011 (OPM, 2011). The average salary for one Full Time Equivalent (FTE) staff is estimated as the salary for a GS -13 Step 5 employee. 19 

### Multiplying the annual pay by an assumed loading factor of 1.6 to reflect Federal fringe benefits and overhead, the loaded annual salary of EPA staff was calculated to be $161,446. The Agency loading factor is from an EPA guide, Instructions for Preparing Information Collection Requests (ICRs) ( EPA, 1992 , page 30, footnote 9). The 60 percent assumption was labeled “the benefits multiplication factor” in the EPA Guide, but has been used in many EPA Office of Pollution Prevention and Toxics ICRs to reflect both fringe benefits and overhead for Federal staff. For example, it was used in an August 2000 document supporting ICR No. 1139.06 (EPA, 2000) , with the following explanation:

“The annual costs per FTE are derived by multiplying the annual pay rate by 1.6 (the benefits multiplication factor)

. The multiplication factor used is recommended in EPA's Offi ce of Policy, Planning, and Evaluation's Instructions for Preparing Information Collection Requests (ICRs) (June 1, 1992)

. An EPA internal phone call between Carol Rawie (OPPT/EETD/RIB) and Carl Koch (OPPE/RMD/IMB) on May 3, 1994, indicated that the 1.6 fa ctor included not only benefits but also overhead.” ( EPA, 2000 )

19 The GS

- 13 Step 5 is consistent with ICR No. 0574.14 (12/18/2007) (EPA, 2007a), which covers PMN SNURs. Use of this grade level follows the approac h introduced in EPA, 2007b. That report represented a change from an earlier PMN SNUR economic analysis (EPA, 2003a), which used an average of GS

- 12 Step 1 and GS

- 12 Step 10 salaries.Economic Analysis of Expedited New Use Rule for 10 7 Chemical Substances (EPA Docket EPA
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- OPPT
- 201 1- 0941 )

August 8, 2012 B-4 

### Table B -1. Derivation of Loaded Wage Rates

EPAB Labor Category Data Sources Date Wage Fringe Benefit Fringes as % wage Over

head %

wage 2 Fringe + O verhead

F actor Loaded Wages 1
(a) (b) (c) =(b)/(a) (d) (e)=(c)+(d)+1 (f)=(a) x (e)
Managerial BLS ECEC , Private Manufacturing industries , “Mgt, Business, and Financial” 3 Dec -11 $43.01 $20.40 47.43% 17% 1.64 $70.72

Professional/ Technical BLS ECEC , Private Manufacturing industries, “Professional and related“ 3 Dec

- 11 $38.48 $19.64 51.04% 17% 1.68 $64.66

Clerical BLS ECEC , Private Manufacturing industries, “Office and Administrative Support” 3 Dec

- 11 $17.69 $8.93 50.48% 17% 1.67 $29.63

Production Worker BLS ECEC , Private Manufacturing industries, “Production, transport, and material moving.” 3 Dec

- 11 $16.86 $9.32 55.28% 17% 1.72 $29.05

Industrial Hygienist Wage : BLS OES Occupat. Employ. and Wages, for Manufacturing (NAICS 31, 32, 33), average of wages for Occup. Health/ Safety Specialists (SOC 29

- 9011) and Occup. Health/Safety Technicians (SOC 29

- 9012), weighted by employment. 4

Fringes: BLS ECEC , Private Manufacturing industries, “Professional and related” 3 Wage: May -11
Fringe: Dec -11 $ 31.32

-- 51.04% 17% 1.68 $5 2.63

EPA staff FTE Annual Federal staff cost: OP M Washington

Baltimore

- Northern Virginia, DC

- MD

- PA

- VA

WV, area, GS

- 13 Step 5 pay rates, with 60% h d 5 Jan -11 $100,904 (annual) -- [Included in 60% overhead] 60% 1.6 $161,446 (annual)

Notes: 1 Wage data are rounded to the closest pennies in this table; however, in calculations using these numbers for this report, unr ounded values were used. 2 An overhead rate of 17% was used based on assumptions in Wage Rates for Economic Analyses of the Toxics Release Inventory Program (EPA, 2002b), and the Revised Economic Analysis for the Amended Inventory Update Rule: Final Report (EPA, 2002a). 3 Employer Costs for Employee Compensation Supplementary Tables December 2011, US Bureau of Labor Statistics, March 14, 2012 (BLS, 2012a ). 4 Employment and unweighted wages are from BLS Occupational Employment Statistics (National Industry

- Specific Employment and Wag e Estimates), May 201 1 (BLS, 2012e). 5 The salary is unloaded Federal GS

- 1 3 Step 5 salary for calendar 201 1 , from the Office of Personnel Management salary table for Washington

- Baltimore

- Northern VirginiaEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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2011

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June 18, 2012 B-5



### Table B
- 2

. Derivation of Industrial Hygienist Wage Rate ( NAICS 31, 32, 33)

Occupation Title (SOC C ode) Employment Mean H ourly W age Weight Weighted Wage 1 (a) (b) (c) (d) = (c) × (b) Occupational Health & Safety Specialists (29

- 9011) 9,340 $ 32.69 0.856 $ 27.99 Occupational Health & Safety Technicians (29

- 9012) 1,570 $ 23.17 0.144 $ 3.33 Industrial Hygienist (weighted average) 10,910

-- 1 $ 31.32

Notes:

1 Wage data are rounded to the closest pennies in this table; however, in calculations using these numbers for this report, unrounded values were used. Source: Employment and unweighted wages are for manufacturing (NAICS 31, 32, 33) from BLS Occupational Employment Statistics (Occupational Employment and Wages) , for May 201 1 (BLS, 2012e )

. 

### B.5 Derivation of Inflation Factors
Costs of equipment and supplies were inflated using the Consumer Price Index – All Urban Consumers; wages were inflated using the appropriate Employment Cost Index (ECI). Where both labor and equipment/supplies were involved, we used the inflation factor corresponding to the dominant cost category 20 

### . For example, test costs include a mix of labor, equipment, and supplies. Assuming that the largest component of test costs comes from labor, we used the ECI for private industry, all workers. Complete information on the derivation of the inflation factors used is given in Table B -3 below. In 2006, the Bureau of Labor Statistics (BLS) made several changes to the Employment Cost Index. The chang es are described on a BLS web page, “Change has come to the ECI,” (BLS, 2006c) and in several April 2006 Monthly Labor Review articles posted on the BLS web site: “Changes affecting the Employment Cost Index: an overview” (Caroll 2006); “Employment Cost Index Publication P lans” (Sleemi, 2006); and “Seasonal adjustment in the ECI and the conversion to NAICS and SOC” (Branch, 2006).

20 Prior SNUR economic analyses used the seasonally adjusted E CI for the total compensation , private industry white collar workers (Series ID CIS2010000W00000I) to inflate export notification and Agency extramural cost

. However, in 2008 B LS retired both the “white

- collar” and “blue

- collar” series (BLS, 2008, p. BLS

- 45) . T herefore , beginning with th e report , Economic Analysis of Expedited Significant New Use Rules for 2 5 Chemical Substances: EPA Docket OPPT

- 2009

- 092 2 , the “white

- collar” series was replaced with the not seasonally adjusted E CI for total compensation of private industry professional and related workers (Series ID CIU2010000120000I ). The

“ professional and related workers ” series was chosen because it is the only series with continuous data since 1985 , and the majority of export notification and Agency extramur al activities are performed by professional and technical labor.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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2011

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June 18, 2012 B-6 

### Under a mandate from OMB, BLS changed its classification of industries and occupations from the Stand ard Industrial Classification (SIC) and Occupational Classification System (OCS) to the North American Industry Classification System (NAICS) and Standard Occupational Classification (SOC) system . In 2006, BLS adjusted all ECI series to reflect this change. In addition to changing the industry and occupational classification systems, in 2006, BLS rebased the ECI from June 1989 = 100 to December 2005 = 100 for all current and historical non- seasonally adjusted series, including the NAICS and SIC based serie s. (Seasonally adjusted indices, including those in Table B-3 of this report, may not exactly equal 100 for December 2005 as a result of the seasonal adjustment. Seasonal adjustments are explained in Branch, 2006.) According to BLS, the official ECI for the years 1975-2005 is the SIC- OCS based series, and for subsequent years, the official ECI is the NAICS -SOC based series (Sleemi, 2006, p.8). 21 

### “Starting year” indices in Table B -3 continue to be SIC- SOC based

. Current year indices are NAICS

- SOC based

. We use indices from both the NAICS -SOC and the SIC- OCS based ECI series because neither series spans the entire period over which testing and other cos ts need to be inflated.

21 BLS has been publishing the NAICS

- SOC based ECI series since March 2001 and it became official in March 2006. The SIC

OCS based series and NAICS

- SOC series have different series ID numbers, even when they describe essentially the same population. For example the series ID for seasonally adjusted total compensation for all private industry workers is ECS10002 I for the SIC

- OCS series and CIS2010000000000I for the NAICS

- SOC series



### .Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- OPPT

2011

- 0941)

June 18, 2012 B-7



### Table B
- 3

. Derivation of Inflation Factors

Item Inflation I ndex S ource 1 Starting Y ear Index for S tarting

Y ear

(a) Index for 201 1

(b) Inflation F actor (b)/(a) 2

Chemical testing (toxicity, ecological effects etc.) BLS ECI, SA, Total comp, Private industry, All Workers, 4 th Q [BLS 2006d and 2012c ] varies varies 115.1 varies

White collar/other labor mix; equipment; supplies. Example for test costed in 1993 1993 66.5 115.1 1.731 Tests were first costed out in various years, depending on the test; inflation factors vary depending original cost date. Example for test costed in 2000 2000 83.8 115.1 1.374

Impermeability testing of gloves and other gear 3 BLS ECI, SA, Total comp, Private industry, All Workers, 4 th Q [BLS 2006d and 2012c] 1997 74.9 115.1 1.537

Export notification BLS ECI, ,Total comp, Private industry, Professional and related, 4 th Q [BLS 2012d] 4 1992 64.9 115.7 1.783

Agency Extramural costs White collar labor; equipment; supplies BLS ECI, Total comp, Private industry, Professional and related, 4 th Q [BLS 2012d ] 4 1993 67.0 115.7 1.727

Labels, placards, gloves, eyewear, clothing, respirators, file cabinet BLS CPI, All urban consumers, not SA

. CUUR0000SA0, Annual [BLS 2012b ] 1997 160.5 224.939 1.401

Photocopies Record keeping materials BLS CPI, All urban consumers, not SA

. CUUR0000SA0, Annual [BLS 2012b ] 1988 118.3 224.939 1.901Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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2011

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June 18, 2012 B-8

Notes: 1 In 2006, Bureau of Labor Statistics (BLS) Employment Cost Index (ECI) series “were rebased to December 2005 = 100 from June 1989 = 100.” The change is reflected in the indices in this table and explained on the BLS website, Employment Cost Index News Rele ase Text: Employment Cost Index, March 2006 (BLS, 2006b). The Consumer Price Index (CPI) was not rebased. “Starting year” ECI indices are SIC

- OCS based: Seasonally Adjusted (SA) ECS10002I for private industry All Workers, and not SA ECU11122I for private industry Professional and Related Workers. After 2006, ECI indices are NAICS

- SOC based: Seasonally Adjusted (SA) CIS2010000000000I for private industry All Workers, and not SA CIU2010000120000I (B) for private industry Professional, and Related workers. 2 Inflation factors are rounded to three decimal places in this table, but calculations in this report use the unrounded values . BLS CPI values were published with one decimal place through 2006 and with three decimal places after that. 3 We began using t he ECI for Private Industry All Workers in EPA, 2007b, to better reflect the labor mix for impermeability testing. Earlier PMN SNUR economic analyses used the ECI for Private Industry White Collar Workers. 4 Beginning with the report, Economic Analysis of Expedited Significant New Use Rules for 25 Chemical Substances: EPA Docket OPPT

- 2009

- 0922 , we began to use the not

- seasonally adjusted CIU2010000120000I for private industry Professional, and Related workers, instead of SA CIS2010000W00000I for private industry white collar workers because BLS retired the “white

- collar” series.Ec onomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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## APPENDIX C: C osts of H azard C ommunication , P rotection in the W orkplace , and Recordkeeping R equirements

Section 2.1 of the main text of this report discusses costs of worker protection, hazard communication (hazcomm), and recordkeeping for SNURs. This appendix presents dollar costs and labor hours of these requirements, for one chemical at one site. Some requirements listed here may not be cited in the current rulemaking, but have been cited in past SNUR rulemakings.
The haz

- comm costs reflect the annual costs of updating the written program, labeling for chemical distribution and storage, creating and distributing material safety data sheets (MSDS), and employee training . The personal protective equipment (PPE) costs reflect the annualized costs of providing required equipment (i.e., gloves, goggles, clothing, or respirators), assessing dermal protection needs associated with the chemical, and performing required impermeability testing, and/or evaluating manufacturer’s information

. Finally, the annual recordkeeping costs include labor, photocopying, and record storage costs.
To estimate the costs of haz

- comm, worker protection, and recordkeeping requirements, a number of assumptions were made, based on the original EPA analysis for generic SNUR provisions, Economic Analysis of Final Significant New Use Rule: General Provisions for New Chemical Followup (EPA, 1989). In that report, EPA estimated that the number of workers exposed to any one substance would range from 10 to 25, and that a worker potentially would be exposed to a substance for a minimum of 50 days per year to a maximum of 250 days per year. The current analysis uses the high ends of those two ranges

. Thus, each site is assume d to have 25 chemically-exposed workers requiring training and/or protective equipment, with each of them assumed to be exposed for 250 days per year.
Labor costs are derived from the United States Bureau of Labor Statistics sources as described in Appendix B

. Material costs were primarily obtained from a national safety equipment supply house catalog (LSS, 1997) and are inflated as described in Appendix B

. Costs of haz

- comm, workplace protection, and recordkeeping are discussed in Sections C.1 , C.2 , and C.3 , respectively

. Table 4 and Table 6 in the main text summarize these costs by SNUR requirement.


### C.1 Modifying the Hazard Communication Program

As mentioned in Section 2.1 , it is assumed that each facility has in place a haz

- comm program consistent with that required by OSHA’s Hazard Communication standard (29 CFR 1910; November 25, 1983), so that costs attribu table to the SNUR are costs of adding one chemical to the program . Much of the haz- comm methodology and assumptions came from the EPA report, Economic Analysis of Final Significant New Use Rules: General Provisions for New Chemical Followup (EPA, 1989 ), wh ich in turn relied partly on the 1983 OSHA study, Final Regulatory Impact and Regulatory Flexibility Analyses of the Hazard Communication Standard OSHA, 1983).
It was assumed that the haz

- comm costs would be incurred each year . For example, there would be worker turnover and need for refresher training, the MSDS would need revision due to changing information, placards would wear out (EPA, 1989). To the extent that some steps would not need repeating each year,Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### costs could be lower than estimated here . The hazard communication costs summarized in Table 3 above are detailed here.
C.1.1 Updating the Written Program
If the SNUR cites 40 CFR §721.72(a), then to av oid engaging in a Significant New Use, which would trigger other SNUR requirements, manufacturers must update their written haz-comm program to incorporate information about the chemical . The written part of the program includes data and information about hazardous chemicals present in the workplace, the hazards associated with such chemicals, procedures for employees who routinely work with or around such chemicals, procedures for non

- routine tasks that may involve exposure (e.g., tank cleaning), and personal protective equipment requirements when working with or around such chemicals. While material safety data sheets may provide much of the information needed to update the written haz

comm program, many employers may perform a more detailed asse ssment of exposure risks associated with the chemical and develop more site

- specific procedures for workers potentially exposed to such chemicals

. For purposes of the economic analysis, EPA assumes that each employer will engage the services of a professio nal industrial hygienist (IH), either in -house or on a consulting basis, for four hours to perform such an assessment

. Loaded hourly rates for IH services were calculated based on Bureau of Labor Statistics data, as described in Table B-1 and Table B -2

. Costs for the written haz -comm program, in 2011 dollars, are as follows 22



### 4 hours Industrial Hygienist time × $ 52.63 per hour = $ 211 The estimates of IH hours to update the program come from a 1998 EPA report (EPA, 1998).
C.1.2 Labeling
If the SNUR cites 40 CFR §721.72(b), then to avoid engaging in a Significant New Use, manufacturers must ensure that containers used to distribute the PMN substance in commerce are labeled with the necessary hazardous substance warnings and procedures. In addition, containers used in the workplace must bear similar labels or, alternatively, the employer must provide equivalent signage, operating procedures, or other written material to communicate hazard information to workers. The cost of providing such labeling was estimated in a 1989 EPA report (EPA, 1989) and has been updated here using more recent cost information. Standard formats are assumed to be used for creating labels or other signage, and the information required for the labels is assumed to be already available from the MSDS for the chemical (see below).
Chemicals Distributed in Commerce

. For chemicals distributed in commerce, the labeling process is assumed to require 0.5 hours of technical labor time per chemical to compile label information

. It is assumed to require 480 labels per chemical . The assumption of 480 labels per chemical is from a 1989 EPA report (EPA, 1989), and is based on the assumption that, on average, each chemical is shipped twice monthly to 20

22 Figures presented here are rounded.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### customers . This is consistent with roughly 10,000 kilograms of chemical per year shipped in 40 five-gallon containers per month ( EPA , 1989 ). 23 

### Technical labor is fully loaded with fringe benefits and overhead, as described in Appendix B . Labeling materials costs were obtained fro m a national safety equipment supply house catalog (LSS, 1997) and were inflated as described in Appendix B

. The resulting costs of labeling for ch emicals distributed in commerce, per chemical substance at one site, are shown in Table C -1

. Table C -1 . Annual Costs of Labeling for Distribution in Commerce [40 CFR §721.72(b)(2)]

Cost Element Unit Cost (1997 $) Inflation Factor Unit Cost ( 201 1$) Hours Total Cost 0.5 hours technical time

-- -- $64.66 per hour 0.5 $32 480 labels $0.16 per label 1.401 $0.22 per label

-- $108 TOTAL 0.5 $140

Note: Total costs were calculated using unrounded unit cost values and inflation factors (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: 1997 label cost, EPAB 1998, LSS 1997; cost elements, quantities, RIB 1989; inflators, labor, Table B -1 and Table B -3

. 

### Chemicals Used in the Workplace

. Workplace labeling requirements are costed by assuming the facility purchases six large (14" × 10") signs, priced at $38.30 each in 1997 dollars (LSS, 1997; EPA, 1998 )

. Costs of these signs were inflated as described in Appendix B

. These signs will be mounted in areas where the chemicals are used or formulated

. For example, a placard might be posted at each of six ves sels: a mixing tank, a reactor, two separators, and two storage vessels ( EPA, 1989). The labeling process is also assumed to require 0.5 hours of technical time to compile label information and 10 minutes of production worker time to post each placard

. Tec hnical labor costs include wages, fringe benefits, and overhead, as described in Appendix B

. The resulting per chemical, per site costs of labeling for chemicals in the workplace are shown in Table C -2

.

23 Data on PMN notices suggest that some PMN submitters expected to produce less than 10,000 kilograms per year of the SNUR chemicals, but many expected to produce much more. It is not known whether volumes listed in the PMNs w ere realized in practice. Production volumes of secondary suppliers affected by the SNUR are also unknown. Annual volumes significantly greater than 10,000 kg could lead to higher haz

- comm costs than those estimated here.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C -2. Annual Costs of Labeling for Use in Workplace [40 CFR §721.72(b)(1)]

Cost Element Unit Cost (1997$) Inflation Factor Unit Cost ( 201 1$) Hours Total Cost

0.5 hours technical time

-- -- $64.66 per hour 0.5 $32.33 6 labels or placards (14" x 10") $38.30 per item 1.401 $53.68 per item

-- $322 10 minutes per label/placard

production worker time -- -- $29.05 per hour 1.0 $29.05

TOTAL 1.5 $383

Note: Total costs were calculated using unrounded unit cost values and inflation factors (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: 1997 placard cost, EPA, 1998, LSS, 1997; cost elements and quantities, EPA, 1989; inflators and labor unit costs, Table B -1 and Table B -3

. 

### C.1.3 Preparing Material Safety Data Sheet (MSDS) Information
If the SNUR cites 40 CFR §721.72(c), then to avoid engaging in a Significant New Use, each facility is required to create, post, and distribute ma terial safety data sheets (MSDSs)

. Based on estimates in OSHA 1983, the 1989 EPA report (EPA, 1989 ) has estimated that creation of an MSDS for a chemical substance requires 2.0 hours of technical labor time and 0.25 hours of clerical time. Further, EPA ass umes that the manufacturer provides 20 copies of the MSDS to customers and retains 20 copies for use onsite, for a total of 40 copies ( EPA, 1989). The loaded hourly wage rates and the inflator used in estimating unit photocopy costs are derived in Appendix B . The resulting cost of MSDS preparation is shown in Table C -3

. Table C -3 . Annual Costs for Material Safety Data Sheets (MSDSs) [40 CFR §721.72(c)]

Cost Element Unit Cost (1988 $) Inflation Factor Unit Cost ( 2011$ ) Hours Total Cost

2.0 hours technical time

-- -- $64.66 per hour 2 $129
0.25 hours clerical time

-- -- $29.63 per hour 0.25 $7.41 40 copies $0.05 1.901 $0.10 per copy
-- $3.80 TOTAL 2.25 $141

Note: Total costs were calculated using unrounded unit cost values and inflation factors (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: Cost elements, quantities, and 1988 copy cost, RIB 1989; inflators and labor unit costs, Table B -1 and Table B -3

.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### C.1.4 Employee Training

The fin al required component of the haz-comm program is employee training, based on 40 CFR §721.72(d)

. The 1989 EPA report, Economic Analysis of Final Significant New Use Rules: General Provisions for New Chemical Follow-up (EPA, 1989 ), assumes that a training pr ogram currently is in place, but the existing program must be modified to add new information pertaining to the PMN substance. Subsequently, the training program must be expanded to include such material each time the training course is presented. Costs of modifying the program and presenting the modified program are mainly labor costs for the trainer and the trainees. Inserting the new information about the PMN substance into the training program and conducting the revised training is assumed to require 0. 5 hours of the trainer’s time . An additional 0.25 hours per trainee is estimated to be required, and an average of 25 affected workers is assumed per facility ( EPA, 1989)

. If additional production workers needed to be trained, for example because they migh t come into contact with the chemical due to spills or leaks, training costs could be higher than estimated here ( EPA, 1989 ). Labor rates for training are based on the loaded rates derived in Appendix B for chemical technicians and chemical industry production workers. The total cost of the employee training requirement is shown in Table C-4

. Table C -4. Annual Costs for Employee Training, Per Chemical [40 CFR §721.72(d)]

Cost Element Unit Cost ( 201 1$) Hours Total Cost
0.5 hours technical time (trainer) $64.66 per hour 0.5 $32.33 0.25 hours per production employee X average of 25 workers per plant = 6.25 hours $29.05 per hour 6.25 $182

TOTAL 6.75 $214

Note: Total costs were calculated using unrounded values from (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: Cost elements and quantities, EPA, 1989; labor unit costs, Table B -1

. 

### C.2 Protection in the Workplace
The following section estimates costs of assessing needs for dermal protection and evaluating protective gear for impermeability, as well as the costs of gloves, goggles, protective clothing, and respirators.
C.2.1 Dermal Protection Selection
If the SNUR cites 40 CFR §721.63(a)(1), then to avoid engaging in a Significant New Use, the employer must ensure that each person who is likely to experience dermal exposure to a PMN chemical, must be provided with and is required to wear personal protective equipment (e.g., gloves) that will prevent dermal exposure to the substance. The equipment must be selected and used in accordance with 29 CFR § § 1910.132 and 1910.133 (promulgated by the Occupational Safety and Health Administration, OSHA). TheEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### selection and administration of this dermal protection is estimated to require 10 hours labor by an industrial hygieni st, annually (EPA, 1999). The wage rate of the hygienist was calculated as described in Appendix B

. The cost calculations for the dermal protection selection requirement are given in Table C -5

. This covers only costs of selecting the dermal protection needed, not costs of the items themselves

. For costs of purchasing dermal protective items, see the sections below on costs of gloves, eyewear, and clothing.
Table C -5 . Annual Costs for Dermal Protection Selection [40 CFR §721.63(a)(1)]

Cost Element Unit Cost ( 201 1$) Hours T otal Cost 1
10 hours industrial hygienist (IH) time $ 52.63 per hour 10 $ 526

Notes: Total costs were calculated using unrounded values (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: Labor rates, Table B -1 ; cost elements and quantities, EPA, 1999

. 

### C.2.2 Impermeability Testing
As part of the workplace protection requirements specified under 40 CFR §721.63(a)(3), to avoid engaging in a Significant New Use, the SNUR may require that employers demonstrate that each item of protective equipment provided (e.g., gloves) provides an impervious barrier, to protect employees from dermal exposure. Requirements outlined in §721.63(a)(3) are provided in two parts, §721 .63(a)(3)(i) and (ii)

. Th e employer may use a combination of (i) testing and/or (ii) evaluating manufacturer specifications. The following discussion is based on the Economic Analysis of Expedited Significant New Use Rules for 168 Chemical Substances and Background Support Document for Economic Analysis of Significant New Use Rules (EPA, 1998) and assumes that the manufacturer uses both testing and evaluation of manufacturer specifications

. The analysis assumes that costs are incurred annually. The first step, described at 40 CFR §721.63(a)(3)(i), is to perform actual impermeability testing

. To determine the costs of impermeability testing compliance, Best Manufacturing Company, a leading manufacturer and tester of chemical resistant articles, was consulted (Best, 1997).
As describe d in EPA, 1998 , Best used one of two methodologies for impermeability testing

. In the first method, chemical samples were submitted to Best with a specific article to be tested for impermeability

. This method was cheaper, costing $200 (1997 dollars) p er ch emical, but the burden of finding an appropriate article of protection lay with the chemical manufacturer . In the second method, the chemical manufacturer simply submitted chemical samples to Best, who in turn determined the most appropriate product, even if a competitor manufactured the product

. This method was more costly at $800 (1997 dollars) per chemical

. The second method of impermeability testing is favored in this analysis for several reasons. First, the burden of finding and submitting an article o f protection is shifted from the chemical manufacturer to the testing company, who would have greater experience in Personal Protective Equipment (PPE) selection. Second, should the article submitted fail the impermeability test, other articles may have to be submitted until satisfactory test results are obtained

. Furthermore, substances subject to SNURs may include new and/or rare chemicals, which may have undiscovered or unknown properties. This uncertainty may impede chemicalEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### manufacturers’ ability to effectively submit appropriate PPE articles for testing

. Finally, the first method is essentially a pass

- fail test

. If an article passes the impermeability test, then it is acceptable

. In the second method, several articles may be tested and compared, and, w hile one or more acceptable articles may result, the most impermeable article is always determined for the chemical

. To obtain the best article rather than merely a satisfactory article of protection, the second method of testing is more appropriate. For these reasons, unit costs of $800 per chemical (1997 dollars) are assumed for impermeability testing. The cost of the impermeability testing is assumed to be driven by labor costs of the company performing the testing, thus test costs were inflated with an Employment Cost Index as described in Appendix B . The administration of this test would also require two hours of industrial hygienist labor ( EPA, 1999 ). The second step to compliance with the workplace protection requirements at §721.63 (a)(3)(ii) is the evaluation of specifications from the manufacturer or supplier of the protective equipment. This requirement helps ensure that the protective equi pment will be impervious to the PMN chemical(s)

. The evaluation of manufacturer specifications requires an estimated four hours of industrial hygienist labor. Annual costs of the impermeability testing requirements are presented in Table C -6

. Table C -6. Annual Costs of Impermeability Testing [40 CFR §721.63(a )(3)]

Cost Element Unit Cost (1997 $) Inflation Factor Unit Cost ( 201 1$) Hours Total Cost 1
Impermeability Testing [§721.63(a)(3)(i)] Impermeability Test $800 per chemical 1.537 $1,229 per chemical $1,229 Industrial Hygienist time $ 52.63 per hour 2 $ 105.26 Subtotal 2 $ 1,335 Evaluation of Manufacturer ’ s Specifications [§721.63(a)(3)(ii)]

Industrial Hygienist time $ 52.63 per hour 4 $ 211 Subtotal 4 $ 211 TOTAL 6 $ 1,545

Notes:

1 Total costs were calculated using unrounded unit cost values and inflation factors (see Appendix B ), so results may differ from calculations using the rounded values shown in this table. Source: 1997 costs, Best, 1997; cost elements and q uantities, EPA, 1998 and EPA, 1999 ; inflators and labor rates, Table B -1 through Table B -3

. 

### C.2.3 Gloves
If the SNUR cites 40 CFR §721.63(a)(2)(i), then gloves must be worn to avoid engaging in a Significant New Use

. Gloves may also be acquired as a result of the dermal protection selection at §721.63 (a)( 1)

. If standard, disposable medical

- grade gloves are used, they are assumed to be worn and discarded by the
wor ker following each day of exposure. Each site is assumed to have 25 workers, each of them exposed 250 days per year

. This reflects the high

- side assumptions in EPA, 1989 (page 25) for the number of workers and exposure days

. Each pair was estimated to cost$0.43 in 1997 (LSS, 1997); the cost has been inflated as described in Appendix B . Total annual costs of providing disposable gloves are developed by applying theEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### assumptions above regarding the number of workers exposed (25 per site) and frequency of replacement (one pair per worker per day of exposure H 250 days of exposure per year). For some chemicals, heavy -duty gloves may be used

. They are gene rally not disposed of daily, but are more expensive

. The estimated costs of gloves purchased in compliance with SNUR Personal Protective Equipment requirements are presented below in Table C -7

. The cost estimates for each chemical assume that the more expensive heavy

- duty gloves are used in cases where the SNUR explicitly requires gloves.
Table C -7. Annua l Cost of Gloves [40 CFR §721.63(a)(2)(i)]

Cost Element Unit Cost (1997 $ per pair) Inflation Factor Unit Cost ( 201 1$ per pair) Number of Pairs Required 1 Total Cost ( 201 1$) 2
Disposable nitrile gloves (replaced daily) $0.43 1.401 $0.60 6,250 $3,767 Heavy duty butyl gloves (replaced every 25 work days) $34.00 1.401 $47.65 250 $11,913

Notes:

1 The analysis assumes that 25 workers who are exposed 250 days/year replace disposable gloves daily and replace heavy duty glo ves every 25 work days.

2 Total costs were calculated using unrounded unit cost values and inflation factors ( Table B -3 ), so results may differ from calculations using the rounded values shown in this table. Source: 1997 item costs, LSS, 1997; item type and quantity, EPA, 1998 ; inflator, Table B -3

. 

### C.2.4 Eyewear

If the SNUR cites 40 CFR §721.63(a)(2)(iii), then to avoid engaging in a Significant New Use, employer must provide eye protection. Eye protection may also be acquired as a result of the dermal protection selection at §721.63 (a)( 1)

. Protective goggles are expected to be used at a rate of one set per worker and replaced every four months

. Each site is assumed to have 25 workers, each of them exposed 250 days per year

. The SNUR may not specify the exact type of eyewear required . OSHA guidelines in 29 CFR § 1910.133 (b)( 1), however, state that protective eye and face devices purchased after July 5, 1994 shall comply with ANSI Z87.1-1989. To determine the cost of goggles that meet this standard, EPA consulted with eyewear specialists at equipment supplier LSS

. A standard pair of goggles that meets the ANSI Z87.1-1989 specification was priced at $4.05 per pair in 1997 (LSS, 1997; RIB, 1998). A price estimate for a heavy -duty pair of goggles compliant with the ANSI standard is also included in Table C -8

. The cost estimates for each chemical assume that the more expensive heavy

- duty goggles are used in cases where the SNUR explicitly requires goggles

. Costs of protective eyewear were inflated as described in Appendix B and are presented in Table C -8 below.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C -8. Annual Cost of Protective Eyewear [40 CFR §721.63(a)(2)(iii)]

Cost Element Unit Cost (1997 $ per pair) Inflation Factor Unit Cost (2011$ per pair) Number of Pairs Required 1 Total Cost ( 201 1$) 2 Standard Goggles $4.05 1.401 $5.68 75 $426 Heavy duty chemical

- splash/impact goggles $6.05 1.401 $8.48 75 $636

Notes:

1 The analysis assumes 25 workers replacing goggles three times per year.

2 Total costs were calculated using unrounded unit cost values and inflation factors (see Appendix B ), so results may differ from calculations using the rounded values shown in this table.
Source: 1997 i tem costs, LSS, 1997; item type and quantity, EPA, 1998 ; i nflator, Table B -3

. 

### C.2.5 Clothing

Costs for a standard coverall clothing set, estimated at $36.25 in 1997 (LSS, 1997), were inflated as described in Appendix B and are shown in Table C -9 below. Costs for full -body protective clothing are based on the coverall clothing set with a hood (LSS, 1997) as shown in Table C -9

. If the SNUR cites 40 CFR §721.63(a)(2)(ii) or (iv), then to avoid engaging in a Significant New Use, employers must provide protective clothing. Protective clothing may also be acquired as a result of the dermal protection selection at §721.63(a)(1)

. Protective clothing, (a)( 2)(iv), and full

- body chemical resistant clothing, (a)(2)(ii), are assumed to last four months. Each site is assumed to have 25 workers, each of them exposed 250 days per year.
Table C -9 shows estimated costs, after inflating as described in Appendix B, for a standard coverall clothing set that cost $36.25 in 1997 (LSS, 1997) and for full

- body protective clothing – the coverall clothing set with a hood – costing $61.20 in 1997 (LSS, 1997).
Table C -9 . Annual Cost of Protective Clothing [40 CFR §721.63(a)(2)]

Cost Element Unit Cost (1997 $ per set) Inflation Factor Unit Cost ( 201 1$ per set) Number Required 1 Total Cost (201 1$) 2 Coverall with hood [full

- body

clothing] §721.63(a)(2)(ii) $61.20 1.401 $85.77 75 $6,433
Coverall §721.63(a)(2)(iv) $36.25 1.401 $50.80 75 $3,810

Notes: 1 The analysis assumes 25 workers replacing coverall three times per year. 2 Totals were calculated using unrounded unit cost values and inflation factors (see Table B -3 ), so results may differ from calculations using the round ed values shown in this table. Source: 1997 item costs, LSS, 1997; item type and quantity, EPA, 1998 ; inflation factor, Table B -3

. 

### C.2.6 Respirators
For some PMN chemicals, to avoid engaging in a Significant New Use, the SNUR requires either the use of respirators or compliance with a New Chemical Exposure Limit (NCEL) . Both requirements differ byEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### chemical. 18 24 

### For costing purposes, this analysis assumes that respirators are used

. Earlier, PMN SNURs referenced specific paragraphs at 40 CFR §721.63 (a)(5) that identified fifteen types of NIOSH-approved respirator units

. Howe ver, with rulemaking docket OPPT -2003-0063 (EPA, 2007b ), PMN SNURs began to describe respirator choices directly

. Costs of the SNUR respirator choices were estimated based on the costs of the respirator in §721.63 (a)(5) that appeared to best match the SNU R descriptions.

24 EPA’s website at http://www.epa.gov/oppt/newchems/pubs/ncelmain.htm explains that in Consent Orders and subsequent SNURs, EPA can require respirators unless workplace air measurements show that air

- borne
concen trations of the chemical are below a New Chemical Exposure Limit established by EPA to protect health. NCEL provisions are modeled after Occupational Safety and Health Administration Permissible Exposure Limits (PELs), and also cover sampling and analytica l methods, monitoring, respiratory protection, and recordkeeping.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C
- 10

. Crosswalk Between SNUR Text and Respirator Types at 40 CFR §721.63(a)(5)

Respirator types at 40 CFR §721.63 (a)(5) 1 Requirement Stated in SNUR (exact SNUR wording may differ)
(ii) Category 19C Type C supplied

- air respirator operated in pressure demand or continuous flow mode and equipped with a tight

- fitting facepiece. Some SNURs may specify “full” facepiece Some SNURs may specify “or other positive pressure mode” Supplied

- air respirator operat ed in pressure demand or continuous flow mode and equipped with a tight

f itting full facepiece.
Supplied

- air respirator operated in pressure demand or other positive pressure mode and equipped with a tight

- fitting full facepiece (iii) Category 19C Type C supplied

- air respirator operated in pressure demand or continuous flow mode and equipped with a hood or helmet or tight

- fitting facepiece. Some SNURs may specify “half” or “full” facepiece. Supplied

- air respirator operated in pressure demand or cont inuous flow mode and equipped with a hood or helmet or tight

- fitting facepi ece (either half - or full

- face). (iv) Category 21C air

- purifying respirator equipped with a full facepiece and high efficiency particulate filters. Some SNURs may specify a “half" or "full" facepiece.
Some SNURs may specify “if oil aerosols absent” or o ther restrictions related to oil aerosols. Air

- purifying respirator equipped with a tight

- fitting full facepiece and High Efficiency Particulate Air (HEPA) filters.

Air

- purifying, tight

- fitting respirator equipped with N100 (if oil aerosols absent), R100, or P100 filters (either half - or full

- face). Air

- purifying, tight

- fitting respirator (either half - or full

- face) equipped with N100 (if oil aerosols absent), R100 (restricted use when oil aerosols present), or P100 (appropriate when oil aerosols present) filters.

Air purifying, tight

- fitting full

- face respirator equipped with the appropriate combination cartridges tested and approved for the gas/vapo r substance (i.e., organic vapor, acid gas, or substance

- specific cartridge) , with a particulate filter (N100 if oil aerosols are absent, R100, or P100). (v) Category 21C powered air

- purifying respirator equipped with a tight

- fitting facepiece and high efficiency particulate filters. Some SNURs may specify a “half" or "full" facepiece. Powered air

- purifying, tight

- fitting full

- face respirator equipped with N100 (if oil aerosols absent), R100, or P100 filters. Powered air

- purifying respirator eq uipped with a tight

- fitting facepiece (either half - or full

- face) and HEPA filters.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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June 18, 2012 C- 12 Respirator types at 40 CFR §721.63 (a)(5) 1 Requirement Stated in SNUR (exact SNUR wording may differ) (vi) Category 21C powered air

- purifying respirator equipped with a loose

- fitting hood or helmet and high efficiency particulate filters. Powered air

- purifying respirator equipped with a loose

- fitting hood or helmet and High Efficiency Particulate Air (HEPA) filters.

Notes:

1 The table specifies respirator types at 40 CFR §721.63 (a)(5) that are most similar to the equipment described in the SNUR text for the current and recent SNUR rulemakings

. Any significant differences between the specified respirator type at 40 CFR §721.63 (a)(5) and the SNUR text respirator type are noted in italics.


### Table C -11 gives average costs of various respirator types, both as originally estimated in 1997 and after applying inflation factors from Table B-3. It also estimates costs per plant site for a chemical requiring respirators. The respirators specified in the SNURs are typically comprised of a respirator unit and any number of the following: special cartridges (such as high efficiency particulate filters, organic vapor cartridges, and paint, lacquer, and e namel filters), hoods or helmets, and filter caps
. The costs for each site of providing respirators to chemically

- exposed workers, shown in Table 4 of Chapter 2 of the report, are calculated based on the assumptions stated there, that (1) there are 25 chemically -exposed workers requiring protective equipment, (2) respirators are replaced once a year, and (3) cartridges (and cartridge filters and caps) are replaced at a rate of one pair (two cartridges) every five of the 250 days that workers are exposed, or 50 times per year. For example, for the respirator type described at 40 CFR §721.63(a)(5)(xv), the annual cost per worker in 1997 dollars would be as follows: $10.83 per respirator + ($8.94 per cartridge × 50 cartridges/year) = $457.83 per worker. The 1997 cost was adjusted for inflation as shown in Table C -11 . Typically a SNUR describes more than one type of respirator, but only one type of respirator is needed to comply with the workplace protection requirements.Ec onomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C
- 11 . Annual Per
- Chemical Costs for Respiratory Protection [40 CFR §721.63(a)(4)]

721.63 (a)(5) par. NIOSH approval type at 40 CFR §721.63 (a)(5) (See Table C- 10 for cross

- walk to respirators in SNUR) Annu al Average Costs (1997 $) Annual Average Costs ( 2011 $) 1 Respirator Unit Cartridge Set Per Worker 2 Inflation Factor Annual Per Worker Annual Per Site (25 workers) 3 (i) 19C Type C Supplied

- air with full facepiece $804 $0.00 $804 1.401 $1,127 $28,171 (ii) 19C Type C Supplied

- air with tight

- fitting facepiece $804 $0.00 $804 1.401 $1,127 $28,171 (iii) 19C Type C Supplied

- air with hood or helmet or tight

- fitting facepiece $932 $0.00 $932 1.401 $1,306 $32,660 (iv) 21C Air

- purifying with full facepiece and high efficiency particulate filters (HEPAs) $181 $9.76 $669 1.401 $937 $23,428 (v) 21C Powered air

- purifying (PAPR) with tight fitting facepiece and HEPAs $627 $35.50 $2,402 1.401 $3,367 $84,175 (vi) 21C PAPR with loose hood or helmet and HEPAs $525 $26.89 $1,870 1.401 $2,621 $65,517 (vii) 21C Air

- purifying with HEPA and disposable respirators $12.53 $7.00 $363 1.401 $508 $12,702
(viii) 23C air

- purifying with full facepiece and combination cartridges approved for paints, lacquers and enamels (PLE) $192 $15.71 $978 1.401 $1,370 $34,250
(ix) 23C PAPR with tight

- fitting facepiece and combination cartridges approved PLE $627 $35.50 $2,402 1.401 $3,367 $84,175 (x) 23C PAPR with loose

- fitting hood or helmet and combination cartridges for PLE $525 $26.88 $1,869 1.401 $2,620 $65,500 (xi) 23C Air

- purifying with combination cartridges for PLE, including disposable respirators $14.30 $8.90 $459 1.401 $644 $16,093 (xii) 23C Air

- purifying with full

- facepiece and organic gas/vapor cartridges $192 $10.47 $716 1.401 $1,003 $25,070 (xiii) 23C PAPR with tight

- fitting facepiece and organic gas/vapor cartridges $826 $41.15 $2,884 1.401 $4,042 $101,044 (xiv) 23C PAPR with a loose

- fitting hood or helmet and organic gas/vapor cartridges $640 $41.15 $2,697 1.401 $3,780 $94,506 (xv) 23C Air

- purifying with organic gas/vapor cartridges, including disposable cartridges $10.83 $8.94 $458 1.401 $642 $16,041
Notes:

1 Annual average costs were inflated as described in Table B -3

. 2 “Respirator unit” costs include both the respirator and any required add

- ons such as hoods and helmets. A “cartridge set” includes two cartridges and any filters or caps required. Assumes cartridge sets are replaced every five days (50 times during 250 exposure days) so that each worker requires one respirator unit and 50 cartridge sets per year.

3 Totals were estimated from unrounded unit costs and inflation factors, so results may differ from calculations using the rounded values shown in this table.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C -12 shows how the average costs per NIOSH

- type respirator were calculated, based on prices of respirators listed in a 1997 catalog

. To calculate the cost of respirators that meet the NIOSH criteria, the prices of all units in the supplier catalog (LSS, 1997) that meet each NIOSH criteria were averaged

. Costs of additional items such as hoods, helmets, cartridges, and filter caps were also obtained

. These are added to the cost of the basic respirator unit if they are required under the SNUR regulation and if the unit does not already include the item. For example, §721.63(a)(5)(x) requires a hood or helmet. One model in the catalog that satisfies the requirement already includes a hood, while another unit requires that a separate hood be purchased. The cost of the hood was added to the unit cost and the combined cost was then averaged with the model with integrated hood. Many respirator specifications also require cartridges . The costs of the cartridges listed in LSS (1997) were averaged for the corresponding requirements

. In some instances, certain cartridges or filters require a secondary cartridge to function properly (e.g., some paint, lacquer and enamel filters required the organic vapors cartridges and filter retainer caps) . These additional items were priced and added to the cost for the basic cartridge before averages were taken. Some cartridge prices were unavailable from LSS (1997). For instan ce, §721.63(a)(5)(ix) and (x) require a powered air-purifying respirator (PAPR) with a paint, lacquer and enamel cartridge. The only cartridges available for these models of respirators in LSS (1997) are HEPA cartridges

. In these cases the costs of a paint , lacquer, and enamel cartridge are assumed to be the same as for a HEPA cartridge. The 1997 purchase costs of the varying types of respiratory protective equipment are shown in Table C

12

.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C
- 12

. Respirator Prices and Average Costs in 1997, by NIOSH Type

40CFR NIOSH Type Catalog Item Number Description 1 1997 Cost 1997 Average Cost 2 §721.63

(a)(5) Respirator Unit Cartridge Set

(i) 19C Type C Supplied

- air with full facepiece $804

-- 7A

- 24506 Allegro Economical Full

- Face Airline Kits, p144 $758.95 7A

- 32366 311Survivair Supplied Air Respirator Kits, p144 $849.10

(ii) 19C Type C Supplied

- air with tight

- fitting facepiece $80

-- 7A

- 24506 Allegro Economical Full

- Face Airline Kits, p144 $758.95 7A

- 32366 Survivair Supplied Air Respirator Kits, p144 $849.10
(iii) 19C Type C Supplied

- air with hood or helmet or tight

- fitting facepiece $932

-- 7A

- 29363 Allegro Hood Systems, p144 $932.15

(iv) 21C Air

- purifying with full facepiece and high efficiency particulate filters (HEPAs) $181 $10

7A

- 9838 North Full

- Face Respirator, p114 $210.10 7A

- 7122 North HEPA Cartridge, p115 $11.15 7A

- 12338 Willson Full

- Face Silicone Respirator, p116 $215.10 7A

- 7526 Willson HEPA Cartridge, p117 $11.75 7A

- 10516 3M 7800 Full

- Facepiece Respirator, p118 $202.10 7A

- 11839 3M HEPA Cartridge, p118 $7.00 7A

- 33446 Pro

- Tech Full

- Face Respirator, p122 $106.45 7A

- 3070 -1 Pro

- Tech HEPA Cartridge, p123 $9.87 7A

- 3195 Willson 1600/1700 Series Full

- Face Respirators, p124 $215.10

7A

- 3202 Willson HEPA Cartridge, p125 $12.50 7A

- 23959 AO7Star Full

- Face Respirator (Silicone), p126 $203.25 7A

- 9940 AO7Star HEPA Cartridge, p127 $9.44 7A

- 24158 MSA Advantage 1000 Full

- Face Respirator, p134 $112.60 7A

- 29946 MSA HEPA Cartridge, p134 $6.60

(v) 21C Powered air

- purifying (PAPR) with tight fitting facepiece and HEPAs $627 $36 7A

- 13599 3M Face

- Mounted PAPR System, p142 $720.00 7A

- 13601 3M HEPA Replacement Cartridge, p142 $36.50 7A

- 32505 RACAL Powerflow PAPR, p142 $534.90 7A

- 11936 RACAL Replacement Cartridge, p142 $34.50Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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40CFR NIOSH Type Catalog Item Number Description 1 1997 Cost 1997 Average Cost 2 §721.63

(a)(5) Respirator Unit Cartridge Set

(vi) 21C PAPR with loose hood or helmet and HEPAs $525 $27 7A

- 32506 RACAL Air

- Mate PAPR 12, p143 $411.05 7A

- 24505 RACAL HEPA Replacement Cartridge, p143 $24.65 7A

- 32477 RACAL Breathe

- Easy HEPA Cartridges and Turbo Unit, p141 $548.50

7A

- 12838 RACAL HEPA Replacement Cartridge $29.12 7A

- 12840 RACAL Breathe

- Easy 10 Tyvek Hood, p140 $91.30

(vii) 21C Air

- purifying with HEPA and disposable respirators $13 $7 7A

- 15255 3M 6000 Series Low

- Maintenance Respirator, p135 $10.90 7A

- 12518P 3M Adaptor, p135 $1.63 7A

- 11839 3M HEPA Cartridge, p135 $7.00Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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40CFR NIOSH Type Catalog Item Number Description 1 1997 Cost 1997 Average Cost 2 §721.63

(a)(5) Respirator Unit Cartridge Set

(viii) 23C air

- purifying with full facepiece and combination cartridges approved for paints, lacquers and enamels (PLE) $192 $16

7A

- 9838 North Full

- Face Respirator, p114 $210.10 7A

- 7117 North Organic Vapors Cartridge, p115 $10.50 7A

- 7125 North Paint Spray/Mists Prefilter, p115 $2.38 7A

- 7125 -2 North Filter Covers, p115 $4.35 7A

- 12338 Willson Full

- Face Silicone Respirator, p116 $215.10 7A

- 7527 Willson Organic Vapors Cartridge, p117 $10.25 7A

- 7531 Willson Dusts/Mists/Pesticides/Paint Spray Prefilter, p117 $2.52

7A

- 7532 Willson Retainer Caps, p117 $4.00 7A

- 10516 3M 7800 Full

- Facepiece Respirator, p118 $202.10 7A

- 9279 3M Organic Vapors Cartridge, p119 $8.91 7A

- 9284 3M Paint Spray Prefilter, p119 $2.37 7A

- 9292 3M Retainer Caps, p119 $3.90 7A

- 33446 Pro

- Tech Full

- Face Respirator, p122 $106.45 7A

- 955 -4 Pro

- Tech Organic Vapors Cartridge, p123 $9.27 7A

- 9605 Pro

- Tech Paint Spray Prefilter, p123 $1.95 7A

- 3195 Willson 1600/1700 Series Full

- Face Respirators, p124 $215.10

7A

- 3197 Willson Organic Vapors Cartridge, p125 $11.22 7A

- 3203 Willson Pesticides/Paint Spray Prefilter, p125 $3.36 7A

- 3858 Willson Retainer Caps, p125 $4.27 7A

- 23959 AO7Star Full

- Face Respirator (Silicone), p126 $203.25 7A

- 9935 AO7Star Organic Vapors Cartridge, p127 $8.76 7A

- 10043 AO7Star Dusts/Mists/Paint Spray Prefilter, p127 $3.07 7A

- 10044 AO7Star Retainer Clips, p 127 $3.20

(ix) 23C PAPR with tight

- fitting facepiece and combination cartridges approved PLE $627 $36 7A

- 13599 3M Face

- Mounted PAPR System, p142 $720.00

--- Paint, Lacquer, Enamel Cartridge 3 $36.50 7A

- 32505 RACAL Powerflow PAPR, p142 $534.90

--- Paint, Lacquer, Enamel Cartridge 3 $34.50Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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40CFR NIOSH Type Catalog Item Number Description 1 1997 Cost 1997 Average Cost 2 §721.63

(a)(5) Respirator Unit Cartridge Set

(x) 23C PAPR with loose

- fitting hood or helmet and combination cartridges for PLE $525 $27 7A

- 32506 RACAL Air

- Mate PAPR 12, p143 $411.05

--- Paint, Lacquer, Enamel Cartridge 3 $24.65 7A

- 32477 RACAL Breathe

- Easy HEPA Cartridges and Turbo Unit, p141 $548.50

7A

- 12840 RACAL Breathe

- Easy 10 Tyvek Hood, p140 $91.30

--- Paint, Lacquer, Enamel Cartridge 3 $29.10

(xi) 23C Air

- purifying with combination cartridges for PLE, including disposable respirators $14 $9

7A

- 12711 Willson Freedom 2000 Series Organic Vapors Respirator, p136 $17.85

7A

- 7531 Willson Dusts/Mists/Paint Spray/Pesticides Prefilter, p136 $2.52

7A

- 13509 7A

- 33826 Willson Retainer Caps, p136 Moldex 8000 Series Half

- Mask Respirator, p139 $2.03 $10.75 7A

- 22751 Moldex Organic Vapors Cartridge, p139 $8.03 7A

- 22753 Moldex Paint Spray/Pesticides Prefilter, p139 $2.56 7A

- 22754 Moldex Retainer Caps, p139 $2.65

(xii) 23C Air

- purifying with full

- facepiece and organic gas/vapor cartridges $192 $10 7A

- 9838 North Full

- Face Respirator, p114 $210.10 7A

- 7117 North Organic Vapors Cartridge, p115 $10.50 7A

- 12338 Willson Full

- Face Silicone Respirator, p116 $215.10 7A

- 7527 Willson Organic Vapors Cartridge, p117 $10.25 7A

- 10516 3M 7800 Full

- Facepiece Respirator, p118 $202.10 7A

- 9279 3M Organic Vapors Cartridge, p119 $8.91 7A

- 9292 3M Retainer Caps, p119 $3.90 7A

- 33446 Pro

- Tech Full

- Face Respirator, p122 $106.45 7A

- 955 -4 Pro

- Tech Organic Vapors Cartridge, p123 $9.27 7A

- 3195 Willson 1600/1700 Series Full

- Face Respirators, p124 $215.10

7A

- 3197 Willson Organic Vapors Cartridge, p125 $11.22 7A

- 23959 AO7Star Full

- Face Respirator (Silicone), p126 $203.25 7A

- 9935 AO7Star Organic Vapors Cartridge, p127 $8.76Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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40CFR NIOSH Type Catalog Item Number Description 1 1997 Cost 1997 Average Cost 2 §721.63

(a)(5) Respirator Unit Cartridge Set

(xiii) 23C PAPR with tight

- fitting facepiece and organic gas/vapor cartridges $826 $41 7A

- 32473 RACAL Breathe

- Easy Organic Vapors and Turbo Unit, p141 $548.50

7A

- 12844 RACAL Breathe

- Easy 7 Full Face, p140 $277.90 7A

- 12830 RACAL Organic Vapors Replacement Cartridges, p141 $41.15

(xiv) 23C PAPR with a loose

- fitting hood or helmet and organic gas/vapor cartridges $640 $41 7A

- 32473 RACAL Breathe

- Easy Organic Vapors and Turbo Unit, p141 $548.50

7A

- 12840 RACAL Breathe

- Easy 10 Tyvek Hood, p140 $91.30 7A

- 12830 RACAL Organic Vapors Replacement Cartridges, p141 $41.15

(xv) 23C Air

- purifying with organic gas/vapor cartridges, including disposable cartridges $11 $9

7A

- 15255 3M 6000 Series Low

- Maintenance Respirator, p135 $10.90 7A

- 15256 3M Organic Vapors Cartridge, p135 $9.85 7A

- 33826 Moldex 8000 Series Half

- Mask Respirator, p139 $10.75 7A

- 22751 Moldex Organic Vapors Cartridge, p139 $8.03

Notes:

1 See Table C

- 10 for the cross

- walk between respirator types in the SNUR and in this table.

2 Average costs presented in this table are rounded to the nearest dollar figure, so results may differ from calcula tions using the rounded values shown in this table.

3 Paint, lacquer and enamel (PLE) cartridges for PAPRs were not listed in the catalog

. The costs for PLE cartridges are assumed to be the same as HEPA cartridges. Source: LSS 1997; EPAB 1999 

### C.3 Recordkeeping
There are two main types of recordkeeping requirements for the substances listed in the current SNURs: those for companies submitting a SNUN, and those for all companies that manufacture, import or process SNUR

- regulated substances, regardless of whether they have made a submission to EPA

. C.3.1 SNUN S ubmitters
Companies submitting a SNUN must keep records under 40 CFR §721.40. Some EPA reports have assumed that SNUN recordkeeping hours would be 5 percent of SNUN submission hours, or about five toEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### six hours. 25 

### Other EPA reports have estimated that electronic submission of SNUNs is expected to reduce the recordkeeping burden to approximately one hour (EPA, 2009a , p. 16 ) For this report, the SNUN recordkeeping hours were included in the SNUN submission hours (see Table 8 ) and the SNUN recordkeeping cost was not separately estimated. 26


### C.3.2 All Manufacturers, Importers, and P rocessors Whether or not they submit a SNUN, firms that manufacture, import, or process the SNUR substance must keep records based on 40 CFR §721.125(a) through (k), to document compliance with SNUR conditions for avoiding a Significant New Use. (For firms producing under the R&D exemption, R&D recordkeeping would be needed. R&D recordkeeping costs were not estimated for this report.)
Re cordkeeping requirements vary between PMN chemicals, reflecting differences in SNUR restrictions

. For all chemicals in the current SNURs, manufacturers, importers, and processors must keep records on quantities supplied or purchased under 40 CFR §721.125(a), (b), and (c). For chemicals with water discharge restrictions, companies must keep records concerning water discharge compliance, under §721.125(k). For chemicals with other use restrictions, or for those few chemicals with workplace protection or hazar d communication restrictions, companies must keep records under other 40CFR §721.125 paragraphs, to document compliance. All recordkeeping requirements essentially involve copying and filing relevant records, including those related to: manufacturing, importing, or processing volumes; shipment amounts and customer information; clothing impermeability determinations; the hazard communication program including labels and MSDS copies; compliance with other use restrictions; and/or compliance with disposal and release to water limitations

. Records must be maintained for five years from the date of their creation. Costs for compliance with the recordkeeping requirements for substances subject to a SNUR are based on the approach in Economic Analysis of Final Signi ficant New Use Rules: General Provisions for New Chemical Followup ( EPA, 1989 ) which in turn was based on Recordkeeping Costs for a Generic SNUR , prepared for EPA in 1988 by Kearney/Centaur (Kearney, 1988a). These reports drew on recordkeeping costs estimated for the Comprehensive Assessment Information Rule, CAIR . Industry recordkeeping costs for CAIR compliance were estimated in reports Kearney prepared for EPA, including Estimated Cost of the Final Comprehensive Assessment Information Rule , June 1, 1988 (Kearney, 1988b, pages 63 to 65).

25 For example, OPPT’s Information Collection Request (ICR) for TSCA Section 5(a)(2) Significant New Use Rules for Existing Chemicals (Renewal), October 11, 2005, estimates SNUN recordkeeping costs at 5.67 hours (EPA 2005b, page 12).

26 SNUN submission costs estimated in Table 8 of this report were based on PMN submission costs from a 1994 report, Regulatory Impact Analysis of Amendments to Regulations for TSC Section 5 Premanufacture Notifications (EPA, 1994). Page III

- 14 of the 1994 report refers to “the normal records kept with a PMN submission which are included in the estimates for submission costs.” Page III

- 12 identifies “maintaining a file of the submission” as part of the labor hours for the PMN reporting form. These statements imply that the 95 to 114 total hours for a PMN submission (page III

- 10 of RIB 1994) included recordkeeping hours.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### This report uses the basic Kearney (1988a and 1988b) estimates and assumptions to estimate recordkeeping costs for SNUR requirements. 27 

### Unlike Kearney (1988a), this report presents costs for each §721.125 recordkeep ing requirement separately . This report also avoids minor rounding errors by calculating from unrounded data

. However, the underlying methodology is identical to the Kearney 1988a/RIB 1989 reports, resulting in identical costs per chemical except for diffe rences due to inflation and rounding. The paragraphs that follow describe estimates and assumptions used from Kearney (1988a and 1988b). Cost per page. Recordkeeping costs are based on cost per page

. Kearney (1988a) assumes that the ratios of labor hours t o page count for each labor category, file drawer space to page count, and cost of miscellaneous supplies such as folders and labels to page count, are the same as the per

- page ratios estimated for EPA’s Comprehensive Assessment and Reporting Rule

. The CAI R estimates are given in the 1988 report, Estimated Cost of the Final Comprehensive Assessment Information Rule, June 1, 1988, page 65 (Kearney, 1988b). Table C -13 summarizes estimates from Kearney 1988a and the CAIR report (Kearney, 1988b). It also shows the derivation of costs from these estimates , after inflation. The method is as follows:

• Technical labor was estimated at 1 hour for 750 pages in the CAIR report (Kearney, 1988b, page 65), or .00133 hours per page. The analysis estimates a cost per hour and per page using fully loaded labor rates from Table B -1

.

• Clerical labor was estimated at 10 hours for 750 pages in the CAIR report (Kearney, 1988b, page 65), or .01333 hours per page. The analysis estimates a cost per hour and per page using fully loaded labor rates from Table B -1

.

• The photocopying cost from Kearney 1988a ($0.05 per page) was inflated using an inflation factor from Table B -3

.

• File space for CAIR was estimated at 1⁄4 of a four -drawer file cabinet for 750 pages (Kearney, 1988b, page 65) or 0.000333 of a cabinet per page. A standard, four

- drawer, full

- suspen sion file cabinet was priced from a national office products supplier at $195 in 1997 (BT Office Products, 1997; Item #LGM-202401; EPA, 1998). This results in $0.065 per page cost for file space, before inflation ($195 × 0.25 file cabinet/750 pages). The c ost per page was inflated using an inflation factor from Table B -3

.

• Miscellaneous materials costs were estimated at $10.00 for 750 pages in the CAIR r eport (Kearney, 1988b, page 65), or $0.0133/page before inflation. This cost per page was inflated using an inflation factor from Table B -3

.

27 This report follows the method in Economic Analysis of Expedited Significant New Use Rules for 65 Chemical Substances (EPA Docket OPPT

- 2003

- 0063) , (EPA, 2007b), which used the Kearney data to calculate the cost breakdown by recordkeeping requirement.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table C
- 13 . Recordkeeping Estimates from Kearney 1988a and 1988b
Kearney Estimates for CAIR Rule (1988 a, b) Adjusted for I nflation Per P age C ost - 201 1$

Estimate CAIR Pages Cost Per Page Cost Per Hour or Inflation F actor Cost Per Page

Labor Costs Technical 1 hour 750 0.00133 hours $64.66 $0.0862 Clerical 10 hours 750 0.01333 hours $29.63 $0.3950 Total Labor 0.01467 hours $0.4812 Material Costs Photocopying $0.05 [1988 dollars] 1 $0.050 1.901 $0.0951

File Cabinet 1/4 of cabinet priced at $195 [1997 dollars] 750 $0.065 1.401 $0.0911

Misc. Materials $10 total [1988 dollars] 750 $0.013 1.901 $0.0254

Total Materials $0.128 $0.2115 Total Cost per Page (Labor & Materials) $0.6928

Note s : Per

- page labor hours and materials costs were originally estimated in Kearney 1988b for the CAIR rule

. The CAIR per

- page costs were then used to estimate SNUR recordkeeping per

- page costs in Kearney 1988a

. This clarifies the method by which the original CAIR per

- page costs and hours were calculat ed

. It also adjusts costs for inflation using labor rates from Table B -1 and inflation factors from Table B -3

. 

### Pages per chemical at one site. In order to estimate recordkeeping costs, the analysis multiplies the costs per page for each recordkeeping element estimated in Table C -13 by the number of pages required for each SNUR recordkeeping requirement at 40 CFR §721.125 as estimated by Kearney (1998a). The Kearney data was used by EPA in its original expedited- SNUR economic analysis ( EPA, 1989). For example, maintaining MSDS copies as required at §721.125(h) would require 5 pages. The following estimates from Kearney (1988a) are also used:

• Manufacture and import volume, and sales and transfer data require 485 pages of records per year
. This reflects 40 invoices per month (see haz -comm Section C.1 above), 480 for sales/transfer and 5 for manufacturer/import (Kearney, 1988a, p.11). Disposal compliance records, if required, cover items such as waste production, shipping manifests, permits, and transfer receipts

. The 600 disposal compliance pages assume 50 pages per month (Kearney, 1988a, p.11). (This report uses slightly different terminology from EPA, 1989 : “Protective clot hing” instead of “protective gloves,” “haz -comm” instead of “employee information and training.” Recordkeeping for “impermeability determination” was not separately costed out in EPA, 1989. This report assumes it is included under “protective clothing” rec ordkeeping.)Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Cost per chemical

. Table C -14 shows annual recordkeeping activities at one site for one SNUR chemical, by CFR requirement. If all recordkeeping requirements at 40 CFR §721.125 applied to a single chemical, there would be costs for 2.3 hours of technical time, 23 hours of clerical time, 1,715 photocopies, approximately one-half of a four- drawer file cabinet, and other miscellaneous materials such as folders

. However, in reality, few if any chemicals will have all of the rec ordkeeping requirements listed in Table C-14

. Recordkeeping costs would be lower for chemicals with relatively few SNUR restrictions because fewer pag es would be needed to document SNUR compliance.

Table C -14 does not include costs of recordkeeping resulting from a SNUN submission; those costs were included in the SNUN submission cost.
Table C
- 14 . Annual Per
- Chemical Costs of Recordkeeping Requirement [40 CFR 721.125]

40CFR §721.125 2 Requirement Pages 3 Labor and M aterials C ost 1 ( 201 1 $) Hours

(a) Per Page (b) Per Chemical (c)=(a)*(b) Per Page (d) Per Chemical (e)=(a)*(d) (a)(b)(c) Volumes & sales/transfer data 485 $0.6928 $336 0.01467 7.11

(d)(e) Protective clothing [§721.63] and impermeability [§721.63(a)(3)] 20 $0.6928 $13.86 0.01467 0.29 (f) Haz

- comm program [§721.72] 250 $0.6928 $173 0.01467 3.67 (g) Label copies [§721.72(b)] 5 $0.6928 $3.46 0.01467 0.07 (h) MSDS copies [§721.72(c)] 5 $0.6928 $3.46 0.01467 0.07 (i) Use limitations compliance [§721.80] 250 $0.6928 $173 0.01467 3.67 (j) Disposal compliance [§721.80] 600 $0.6928 $416 0.01467 8.80 (k) Release to water compliance [ §721.90] 100 $0.6928 $69.28 0.01467 1.47
TOTAL 1,715 $0.6928 $1,188 0.01467 25.15
Notes:

1 This table multiplies cost per page estimates from Table C

- 13 by the number of pages estimated for each recordkeeping cost element

. (This table does not include recordkeeping for SNUN submissions required by 40 CFR §721.40.) Total costs are calculated from unrounded values and may not equal the sum and/or product of rounded values.

2 40 CFR 721.125(a) through (k) list recordkeeping that may be specified in the SNUR

. The recordkeeping specified depends on which 40 CFR §721 provisions [in brackets] were used by the SNUR to define reportable New Uses (§721.63, §721.72, §721.80, and/or §721.90)

. Few if any SNUR chemicals would require all of the recordkeeping costs listed above since few if any chemicals are subject to all of the requirements (a) through (k)

. 3 Pages count estimates for each SNUR requirement are from Kearney, 1988a.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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## APPENDIX D: C osts of T esting
EPA recognizes that TSCA Section 5 does not require developing any particular test data before submission of a Significant New Use Notice. Persons are required only to submit test data in their possession or control and to describe any other data known to or reasonably ascertainable by them . (Upon review of a SNUN, the Agency has the authority to require appropriate testing, but that is a cost of regulatory follow -up, not of the SNUN submission itself.) For informational purposes, the SNURs describe t ests recommended by EPA to provide sufficient information to evaluate the chemical substance

. However, as was explained in the discussion of SNUNs earlier in this report, it appears that firms rarely elect to do these recommended tests to support a SNUN, and especially not the higher

- cost tests

. For informational purposes, t his appendix presents estimated costs for testing often recommended for chemicals that have been the subject of PMNs and are subject to Significant New Use Rules (SNURs).


### D.1 Testing Guidelines
In the SNURs, EPA identifies a set of tests for each PMN chemical that can be used by firms making Significant New Use Notice or other submissions to EPA to characterize risks of the chemical

. The tests are recommended in the SNUR, not mandatory. They are identified by guideline numbers which c an be used to look up published test protocols. Table D -1 lists test guidelines cited in the current and recent SNUR rulemakings, and their associated costs, Table D -2 presents certain assumptions used in the analysis, and Table D -3 presents Persistent Bioaccumulative Toxic (PBT) tiered testing requirements

. The types of guidelines are described below.
D.1.1 OPPTS Harmonized Test Guidelines
Most SNUR tests are identified by their OPPTS number from the se ries of OPPTS Harmonized Test Guidelines and OPPTS harmonized public drafts not yet promulgated as OPPTS guidelines. These guidelines blended testing guidance from OPPT (published in the Code of Federal Regulations), EPA's Office of Pesticide Programs, the Organization for Economic Cooperation and Development (OECD), and other sources . The harmonized guidelines fall into several categories, including the following:

• Series 835

-- Fate, Transport and Transformation Test Guidelines

• Series 850

-- Ecological Effects Test Guidelines

• Series 870

-- Health Effects Test Guidelines They are available electronically on EPA’s website ( EPA, 2006). Cross

- references for health effects guidelines are listed at 63 FR 41847, August 5, 1998.
D.1.2 C ode of Federal Regulations
SNUR tests may also come from the Code of Federal Regulations (CFR) , identified for example as “40 CFR 799.9370” or just “799.9370.” In addition, in costing out test guidelines, this report sometimes usesEconomic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### costs for a CFR guideline when costs have not been developed for the equivalent OPPTS harmonized guideline. 40 CFR parts 795 through 798 include pre-harmonization test guidelines, typically updated before 1990. 40 CFR part 799 includes more recent TSCA test guidelines, based on harmonized test guidelines. (63 FR 41845, August 5, 1998).

D.1.3 OECD
A few SNUR tests are identified by their OECD number. The OECD guidelines may have OPPTS equivalents. For example, OECD 407 28

- Day Oral Toxicity in Rats is essentially equivalent to OPPTS 870.3050.

D.1.4 OECD ’ s Guidance Manual for the Tes ting of Manufactured Nanomaterials
For some nanomaterials SNUR tests may refer to OECD’s Guidance Manual for the Testing of Manufactured Nanomaterials

. Because of the newness of nanomaterial testing test s may not have protocol numbers, but rather refer to the guidelines described in the manual.
D.1.5 PBT Category
For some chemicals, the SNUR cites tiered testing according to a testing strategy published in the Federal Register (FR), Category for Persistent, Bioaccumulative, and Toxic New Chemical Substances, Nov ember 4, 1999 (64 FR 60194), which in turn refers to a number of tests by OPPTS or OECD guideline number.
D.1.6 ASTM, NTIS, and O ther S ources Test guidelines may also come from the American Society for Testing and Materials (for example, ASTM D2035-80 Modified C oagulation

- flocculation Jar Test of Water) (www.astm.org) or other sources . The guideline for a neurotoxicity functional observational battery, NTIS PB 91-154617, is available from the National Technical Information Service (www.ntis.gov).Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### Table D -1. Cost Estimates for Test Guidelines Cited in SNURs

Guideline Test Species Route/Method Cost 201 1$ Product P roperties 830.6315 Flammability NA NA $2,300

830.7050 Absorption in Aqueous Solution: ultraviolet/visible spectra NA NA $2,325

830.7200 Melting Point / Melting Range NA 8- test average $1,380 830.7550 Partition Coefficient (n

- Octanol/Water) NA Shake Flask Method $7,212 830.7560 Partition Coefficient (n

- Oct/Water) NA Generator Column $7,665.48

830.7570 Partition Coefficient (n

- Oct/Water) NA Liquid Chromatography $5,045

830.7840 Water Solubility NA Flask Method $10,422.28 830.7860 (796.1860) x Water Solubility: Column Generator Method NA Generator Column $22,502.05

Karel Vershueren Handbook, odor and taste test Odor and taste test (in Handbook of Environmental Data on Organic Chemicals, by Karel Vershueren, 4 th Ed,Vol. 1, Page 22) NA NA *

Fate, Transport, Transformation 835.1110 Activated Sludge Sorption Isotherm NA NA $20,153 835.1220 Sediment and Soil Adsorption/Desorption Isotherm NA NA $30,910

835.1230 Sediment and S oil A dsorption/ D esorption (batch equilibrium) NA Nanoscale Materials $43,651

835.1240 Leaching and adsorption/desorption NA Nanoscale Materials $57,403 835.2110 Hydrolysis as a Function of pH NA NA $60,731 835.2120 Hydrolysis test NA NA $41,938 835.2130 Hydrolysis as a Function of pH and Temperature NA NA *Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 4 Guideline Test Species Route/Method Cost 201 1$ 835.2210 (796.3700) Photolysis in Aqueous Solution in Sunlight NA NA $121,486 835.3100 (796.3100) Aerobic Aquatic Biodegradation NA NA $16,678

835.3110 Ready Biodegradation NA Average of six methods $13,031

835.3120 Sealed

- Vessel CO2 Production Test NA NA $8,081 835.314 0 CO2 in Sealed Vessels Test NA NA * 835.3170 Shake Flask Die

- Away Test NA NA $53,137 835.3180 Sediment/Water Microcosm Biodegradation NA Flow

- through $138,942

835.3190 Aerobic Mineralization in Surface Water – Simulation Biodegradation Test NA NA *
835.3200 (OECD 302B) Inherent Biodegradation: Modified Zahn

- Wellens NA NA $10,559 835.3210 Modified SCAS Test NA NA $30,468 835.3220 Porous Pot Test NA NA $33,703 835.3400 Anaerobic Biodegradability of Organic Chemicals NA NA $12,828 835.5045 (OECD 302A) Inherent Biodegradability: Modified SCAS Test NA NA $14,822

835.5270 (795.7000) Sunlight Photolysis in Waters Containing Dissolved Humic Substances (Indirect Photolysis Screening Test) NA NA $25,624

D2035

- 80 (ASTM D 2035

- 80) Standard Practice for Coagulation

- Flocculation Jar Test of Water NA NA $4,426

OECD 303A Simulation Test - Aerobic Sewage Treatment, with measurement of loss of the parent NA NA $44,569

OECD 307 Aerobic and Anaerobic Transformation in Soil NA Flow

- through $292,278
OECD 307 Aerobic and Anaerobic Transformation in Soil NA Bio

- meter type flasks $276,289Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 5 Guideline Test Species Route/Method Cost 201 1$
OECD 308 Anaerobic transformation in aquatic sediment systems NA NA *

OECD 309 Aerobic mineralisation in surface water NA NA *

OECD 310 Ready biodegradability

- CO2 in Sealed Vessels (headspace test) NA NA *

OECD 311 (835.3400) Anaerobic biodegradability of organic compounds in digested sludge NA NA *

OECD TG 310 CO 2 in Sealed Vessels – Headspace Test NA NA *

Draft OECD Jan 2002 Phototransformation of chemicals on soil surfaces

2 soils NA Perfluorinated chemicals * Ecological Effects

850.1000 Special Considerations for Conducting Aquatic Laboratory Studies NA NA *
850.1010 (797.1300) Daphnid Acute Toxicity Daphnid Flow

- through $15,619 850.1010 (797.1300) Daphnid Acute Toxicity Daphnid Static $15,412
850.1075 (797.1400) Fish Acute Toxicity Fathead Minnow Flow

- through $21,524 850.1075 (797.1400) Fish Acute Toxicity NA Static $17,433

850.1085 Fish Acute Toxicity Test mitigated by humic acid Fathead Minnow Flow

- through *

850.1085 Fish Acute Toxicity Test mitigated by humic acid Fathead Minnow Static $18,172

850.1300 Daphnid Chronic Toxicity Test Daphnid Flow

- through $139,894 850.1350 Mysid Chronic Toxicity Test Mysid Flow

- through $44,961Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 6 Guideline Test Species Route/Method Cost 201 1$
850.1400 Fish Early Life Stage Toxicity Rainbow Trout Flow

- through $71,341

850.1400 Fish Early Life Stage Toxicity Fathead Minnow Flow

- through $48,229

850.1730 Fish BCF Fathead Minnow Flow

- through $156,076

850.1925 Site

- Specific Aquatic Microcosm Test NA NA * 850.1950 Field testing for Aquatic Organisms 3 NA NA $694,050 OECD 218 Chironomid Sediment Toxicity NA NA $29,767 850.5400 Algal Toxicity, Tiers I and II NA NA $18,873 Health Effects 870.1100 (OECD 401) Acute Oral Toxicity Rats Gavage $8,134 870.1300 (OECD 403) Acute Inhalation Toxicity Rats 4 Inhalation $17,938 870.2500 Acute Dermal Irritation Test Rabbits Dermal $6,306 870.2600 Dermal Sensitization Test Guinea Pigs NA $12,092 870.3050 (OECD 407) Repeated Dose 28

- day Oral Toxicity Test Rodents NA $60,077 870.3100 90

- Day Oral Toxicity Rats Gavage $162,941 870.3200 (OECD 410) Repeated Dose Dermal Toxicity - 21

- 28 Days Rats Dermal $115,675 870.3250 Subchronic Dermal Toxicity - 90 days Rats Dermal $172,991 870.3465 1 Subchronic Inhalation Toxicity Rats Inhalation $534,075
870.3465 (mod) Subchronic Inhalation Toxicity (w/ 60 day recovery group) Rats Inhalation $254,763

870.3465 (OECD 413) 1 Subchronic Inhalation Toxicity (90

- day exposure/180

- day retention) Rats Inhalation $445,112Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 7 Guideline Test Species Route/Method Cost 201 1$
870.3550 Reproductive/Developmental Toxicity Screening Test NA Oral *

870.3650 Combined repeated dose toxicity test with the reproductive/developmental screening test Rats NA *

870.3700 (OECD 414) Prenatal Developmental Toxicity {2 species} Rats Gavage $123,686

870.3800 Reproduction/Fertility Effects (2

- Generation Reproduction) Rats Gavage $411,738

870.4200 Carcinogenicity {2 species} (24 months) Rats Gavage $1,641,728
870.4200 Carcinogenicity {2 species} Rats Inhalation $1,302,863
870.4300 Combined Chronic Toxicity/Carcinogenicity Test Rats Gavage $1,253,934 870.5100 Bacterial reverse mutation test NA Direct plate $9,364

870.5265 Salmonella typhimurium Reverse Mutation Assay (Ames Test) NA Average of direct plate and Azo reduction $13,515

870.5385 Mammalian Bone Marrow Chromosomal Aberration Test Rats Gavage $37,836

870.5395 In Vivo Mammalian Bone Marrow Cytogenetics Tests: Erythrocyte Micronucleus Assay (Average of 1 and 3 day dosings) Mice Gavage (Average of 1 and 3 day) $22,919

870.5395 In Vivo Mammalian Bone Marrow Cytogenetics Tests: Erythrocyte Micronucleus Assay (Average of 1 and 3 day dosings) Mice Intravenous (Two test average) $22,919

870.5550 Unscheduled DNA Synthesis in Mammalian Cells in Culture Rat Hepatocytes NA $23,668

870.6100 Delayed Neurotoxicity of Organophosphorus Substances (Acute) Hens Gavage (Acute) $40,464Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 8 Guideline Test Species Route/Method Cost 201 1$
870.6100 Delayed Neurotoxicity of Organophosphorus Substances (Subchronic 28

- day) Hens Gavage (Subchronic) $97,858

870.6200 Neurotoxicity Screening Battery (Acute) Rats Gavage $163,054 870.6 3 00 Developmental Neurotoxicity Study Rats Gavage $721,600 870.7485 Metabolism and Pharmacokinetics (Tier I) Rats Gavage $47,656 870.7800 Immunotoxicity Rats Gavage $69,277

ASTM D6007

- 02 Small Scale Chamber Test to Determining Formaldehyde Concentration in Air from Wood Products NA NA *

ASTM F739

- 91 (ASTM F739) 2 Standard Test Method for Resistance of Protective Clothing Materials to Permeation by Liquids or Gases Under Conditions of Continuous Contact NA Average (Gases and Liquids) $15,144

OECD 105 Water Solubility Test NA Flask Method $7,169

OECD 112 Dissociation Constant in Water Test NA Conductometric Method $6,416

OECD 206 Avian Reproduction Test Bobwhite Quail NA $106,052

OECD 206 Avian Reproduction Test Mallard Ducks NA $114,681

OECD 303A Simulation Test - Aerobic Sewage Treatment: Activated Sludge Units NA NA $44,569

OECD 307 Aerobic and Anaerobic Transformation in Soil Test NA Flow Through $292,278 OECD 307 Aerobic and Anaerobic Transformation in Soil Test NA Bio

- meter Type Flasks $276,289

OECD 308 Aerobic and Anaerobic Transformation in Aquatic Sediment Systems Test NA NA *Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 9 Guideline Test Species Route/Method Cost 201 1$
OECD 311 Anaerobic Biodegradability of Organic Compounds in Digested Sludge Test NA NA *

OECD 314 Simulation Test to Assess the Biodegradability of Chemicals Discharged in Wastewater NA NA *

OECD 402 Acute Dermal Toxicity Rats Dermal $8,388 OECD 404 (870.2500) Acute Dermal Irritation Rabbits Dermal $6,440 OECD 405 (870.2400) Acute Eye Irritation Rabbits Eye $6,440 OECD 407 (870.3050) Repeated dose 28

- day oral toxicity study in rodents Rats Gavage (28 Days) $60,077 OECD 412 Repeated Dose Inhalation Toxicity (28

- Day Study) Rats Inhalation (28 Days) $134,508 OECD 415 One

- Generation Reproduction Toxicity Study Rats Gavage $338,253

OECD 416 Two

- Generation Reproduction Toxicity Test Rats Dietary $443,291
OECD 421 (870.3550) Reproduction/developmental toxicity screening tests Rats Gavage $70,465

OECD 422 (870.3650) Combined Repeated Dose Study with Reproductive/Developmental Toxicity Screen Rats Gavage $140,459

OECD 422 (mod) Combined Repeated Dose Study with Reproductive/Developmental Toxicity Screen (90 days w/ histopathology) Rats Gavage $264,076

OECD 425 Acute Oral toxicity: Up

- and

- down Procedure Rats Gavage $6,221 OECD 453 Combined Chronic Toxicity/Carcinogenicity Test Rats Inhalation $3,606,487
OECD 471 Salmonella Typhimurium Reverse Mutation Assay Salmonella typ. Direct P late $12,947

OECD 475 In Vivo Mammalian Bone Marrow Cytogenetics Test: Chromosomal Aberrations Rats Gavage $57,265Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 10 Guideline Test Species Route/Method Cost 201 1$ Inhalation Monitoring Data Collection Guidelines July 1, 2002 * * * *

Nanomaterial Specific Tests 5, 6
OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Dustiness Test NA EN 15051 Method $2,625

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Dry particle size distribution by count for each PMN substance in a form which has the highest content of particles smaller than 10 microns as manufactured, processed or used in the workplace at sites controlled by the Company NA STEM (scanning transmission electron microscopy) method *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Surface chemistry NA Average of Three Methods $573 7

ASTM D2565

- 99(2008) Release of MWCNTs after exposure of liquid polymer forms to sunlight: NA Consult Standard Practice for Xenon

Arc Exposure of Plastics Intended for Outdoor Applications *

ASTM E1354

- 09 Release of MWCNTs during the burning of liquid polymer forms: NA Consult Standard Test Method for Heat and Visible Smoke Release Rates for Materials and Products Using an Oxygen Consumption Calorimeter *Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 11 Guideline Test Species Route/Method Cost 201 1$

EPA method 1320 Release of MWCNTs after landfill d isposal: NA Multiple Extraction Procedure to determine the fraction of MWCNTs released during the leaching that the liquid polymer forms will undergo from repetitive precipitation of acid rain *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Configuration of Carbon Nanotube ends NA NA $766

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Release of MWCNTs during solid polymer form shipping and use NA A simple short

- term test consisting of placing the solid polymer forms in a standard rock tumbler and determining the amount of free MWCNTs after a period of l, 5, 15, and 30 days to screen for significant release of MWCNTs from the solid polymer forms. *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM C100 (>90% MWCNTs. < 7% aluminia and <5% of iron oxide) NA NA *Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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- 12 Guideline Test Species Route/Method Cost 201 1$ OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM U100 (>97% MWCNTs. <3% of iron oxide, 1% alumnia) NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CSI

- 015, a viscous resin (honey

- like) comprised of 98.5% epoxy resin, 1,5% GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM PEB

- 201, a very highly viscous resin (tar

- like paste) comprised of 64.3% polyester, 31.6% styrene, remainder GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM1

- 20, a pellet comprised of 79% polyamide, 12.5% white mineral oil, remainder GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM2

- 20 a pellet comprised of 78% polyamid resin, 22% GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM3

- 20 a pellet comprised of 79% polyamid 11, 21% GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM5

- 20 a pellet comprised of 60% polycarbonate, 20% flame retardant, 20% GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM12

- 30, a pellet comprised of cyclic butylenes trephthalate (CBT), 30% GRAPHISTRENGTH C100 NA NA *Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM CM13

- 30, a pellet comprised of 65% polyacrylic

- polyolefin, 15% acrlonitrile

- butadiene copolymer, 20% GRAPHISTRENGTHTM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials GRAPHISTRENGTH TM C M6

- 20 a granule comprised of 80%polyamid6, 20% GRAPHISTRENGTH TM C100 NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Workplace exposure monitoring and characterization testing (including byproducts) NA NA *

OECD's Guidance Manual for the Testing of Manufactured Nanomaterials Certain material characterization data NA NA *

Notes: * Indicates this cost has not been calculated for this report.
+ Indicates that EPA , EPAB staff estimated this test cost in fall of 2009 and it is more recent that the other EPA, OPPTS EPAB test cost estimate s presented in the table, the majority of which were estimated prior to 1990. 1 For some PMNs, recommended testing under guideline 870.3465 would involve an additional 3 month recovery group, as well as other evaluation beyond the standard requirements in the test guideline

. These activities would raise testing cost substantially. 1 The recommended testing for some PMN chemicals may i nclude a glove permeation test following ASTM F739 and F1194

- 99 guidelines

. ASTM F1194

- 99 is a standard guide for documenting the results of chemical permeation tests (see www.astm.org )

. The additional costs of following ASTM F1194

- 99 (average of gases and liquids) w ere not estimated for this report

. 2 Costs for field testing will be site

- specific, with a wide range of actual costs

. A report from EPA's Office of P esticide Programs estimated an a verage t est c ost of $600,00 0 for guideline 850.1950, for simulated or actual field testing for aquatic organisms (EPA, 2008a, Appendix C). 3 Performing the test on species other than rats may change the test costs

. For example, testing on rabbits is likely to increase costs. 4 F ate, transport and transformation, ecological effects, and health effects testing may be required for nanomaterials, however nano

- specific costs for these tests were not estimated for this report

. 5 While the Agency expects that analytical methodology validati on costs may be more expensive for nanomaterials than for traditional chemicals, EPA was unable to gather any information on nanomaterial

- specific analytical methodology validation and therefore uses the traditional chemical costs as a proxy. 6 The test cost is an average of the test costs for three methods: EELS, XPS (ESCA), and Auger electron spectroscopy. Source: EPA OPPTS Economic and Policy Analysis Branch cost estimates

. Many costs were estimated in the 1990s or earlier

. All have been inflated (see Table B -1 and Table B

3 for inflation index)

. Dollar costs include $4,140 or $10,055 for analytical method validation; where applicable (see text)

. Species and route or method may be specified in SNURs or may be unspecified but assumed in this table for costing purposes.Economic Analysis of Expedited New Use Rule for 107 Chemical Substances (EPA Docket EPA

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### D.2 Test Costs by Guideline

Table D -1 gives dollar cost for each test, based on assumptions and adjustments discussed below

. This section describes the d evelopment of individual test costs. EPA’s Office of Pollution Prevention and Toxics, Economic and Analysis Branch, regularly develops cost estimates of test guidelines to support TSCA rule development

. Estimates are based on assumptions about species, rou te of administration, study duration, and other aspects of methodology. Costs are calculated based on costs of labor, materials, and equipment needed to perform testing, with overhead and fee

. Many of the test costs were developed in the 1990s

. Test costs have been inflated using Employment Cost Index inflators from the Bureau of Labor Statistics (see Appendix B ). However, generally they have not been updated to reflect subsequent changes in laboratory technologies. Testing laboratories perform analytical method validation to ensure that proper dose concentrations are used in toxicity studies (EPA , 2005a , p. 3 -9). This analysis assumes that for health effects tests (e.g. 870series guidelines), tests of up to 90 days in duration have method validation costs of $3,500, and longerterm tests have validation costs of $8,500 in 2004 dollars . Using the inflation rates found in Appendix B , validation costs are $4,140 and $10,055 in 201 1 dollars. For simplicity, the method validation cost for ecological effects tests (e.g. 850 series guidelines) was assumed to be $4,140 for each test. In addition, this analysis assumes that analytical method validation costs are the same for both nanomaterials and traditional chemicals

. In cases where costs have not been estimated for the specifi ed guideline, EPA uses the cost from an approximately equivalent guideline (listed in Table D -1 and Table D -3 in parentheses) . Many of these equivalents are listed in the Federal Register at 63 FR 41847, August 5, 1998. In some cases the test protocol itself states that it is essentially equivalent to another test upon which it was based. Sometimes judgment was needed to select the closest equivalent(s)
. In some cases, EPA has not costed out the test for the species, route, duration, and/or other method listed in the SNUR, or the SNUR specifies a gu ideline but does not specify these details

. In such cases, EPA has made the adjustments described below

. The adjustments were selected based on discussions with EPA scientists and on SNUR language, published test guidelines, assumptions underlying the cost estimates in EPAB's test cost database, EPA review and Consent Order history for specific PMNs, or other sources.
D.2.1 Default Parameters
Costs for many of the guidelines have been estimated for different combinations of species, route, length of study and ot her aspects of methodology, but in some cases the SNUR may not specify all of these variables

. Where this occurs, EPA has used certain default parameters, listed in Table D -2

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### Table D
- 2

. Default Parameters for Species, Route, and Study Type
Variable Default

Species Mammals Fish Invertebrates Algae Rats Fathead minnow 1 Daphnids [Four species

-- see text]

Route/Method Mammalian Fish Invertebrates Gavage Flow

- through Flow

- through

Notes:

1 For guideline 850.1400 tests also in PBT tier tests, rainbow trout is the default species

. (See PBT discussion below.)


### D.2.2 SNUR Testing Tiers
A SNUR may recommend tiered testing . In such cases, costs are lower if only the first

- tier tests are performed, and higher if all tests listed for the chemical are performed

. Testing is “tiered” if later tests are contingent on the results of earlier tests, and/or if some tests are contingent on the firm reaching a certain chemical volume or time limit

. Some tiers are explicit in the SNUR text; others result because the SNUR references the tiered PBT Category testing described at 64 FR 60194

. D.2.3 Test Cost Assumptions and Comments
This section explains treatment of certain tests listed in this or past SNUR rulemakings.

• A SNUR may recommend algal acute toxicity testing according to OPPTS Guideline 850.5400. This guideline has been previously costed by EPA for four separate algal species ( Navicula pelliculosa, Skeletonema costatum, Anabaena flos-aquae, and Selenastrum capricornutum ). If a SNUR does not specify the algal species to be used, the average costs of the four algal species tests are used.

• For OPPTS test guideline 835.3100 (A erobic Aquatic Biodegra dation) , a SNUR may call for an additional analytical methodology to identify the isononyl phenol degradation product, which may be a substantial add -on to the basic cost. Table D -1 gives costs for 835.3100 but not for the extended test

.

• A SNUR may recommend a “modified” version of ASTM test guideline D2035-80 ( Coagulation

Flocculation Jar Test of Water)

. Table D-1 gives costs for D2035-80 but not for the additional analytical methodology.

• For test guideline OECD 422 (Combined Repeated Dose Oral Toxicity with Reproductive/ Developmental Toxicity Sc reening), a SNUR may recommend extended histopathology. Although the OECD 422 protocol does include histopathology, it is possible that extending the histopathology would increase the cost beyond that shown in Table D-1

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### • A SNUR may recommend two variations of test guideline OECD 218 (Chironomid Sediment Toxicity), one using the acute portion of the sediment and the other using the chronic portion. Costs were not determined for these two variants

. The cost of the test performed on midge under flow through conditions was used for both.

• A SNUR may recommend “a fish acute toxicity test, freshwater and marine (OPPTS 850.1075 test guideline)”

. “Freshwater and marine” refers to the name of the test, not the number of species required by EPA. The cost estimates assume only one species is used.
D.2.4 Persistent Bioaccumulative Toxic (PBT) tiered testing
A SNUR may cite tiered testing for Persistent Bioaccumulative Toxic chemical substances (PBTs) according to the testing strategy in EPA’s New Chemicals Program PBT Category document, published in the Federal Register notice, Category for Persistent, Bioaccumulative, and Toxic New Chemical Substances, November 4, 1999, at 64 FR 60194. In 64 FR 60194, there are three tiers of testing. The results of Tier 1 determine whether Tier 2 testing is needed and the results of Tier 2 testing determine whether Tier 3 testing is needed

. Table D -3 lists the tests in the PBT category document

. These tests are also listed in Table D -1

. To obtain a cost estimate for SNURs that cite PBT Category testing (64 FR 60194), costs of individual tests from 64 FR 60194 would have to be added up as appropriate, depending on the specific SNUR language . The test list would also need to be adjusted to avoid double counting tests listed in the SNUR both explicitly by guideline number, and implicitly due to their inclusion in PBT Category tiers. Other assumptions related to PBT testi ng are described below:

• The PBT category tests at 64 FR 60194 specify rainbow trout as the species for the chronic fish toxicity test, 850.1400. For SNURs that recommend PBT Category testing, 850.1400 costs would be based on using rainbow trout. If 850.1400 is recommended without PBT testing, costs would be based on using fathead minnows.

• For PBT Tier 1 ready biodegradability tests, firms may either choose among six methods in test guideline 835.3110 or follow test guideline 835.3120. The cost of 835.3110 i s calculated as the average cost of its six possible methods

. The cost estimates assume an equal chance of using either 835.3110 or 835.3120

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### Table D -3 . Persistent Bioaccumulative Toxic (PBT) Tiered Testing Requirements
PBT Tier Guideline Test Cost 201 1$

1 OPPTS 830.7560*

- or OPPTS 830.7570* Partition Coefficient (n

- Oct/Water), Generator Column method

- or Partition Coefficient (n

- Oct/Water), Liquid Chromatography method Average $7,665

$5,045 $6,355
1 OPPTS 835.2110 Hydrolysis as a Function of pH $60,731

1 OPPTS 835.3110

- or OPPTS 835.3120 Ready Biodegradability (choose one of 6 methods; cost is average of the 6)

- or - [Ready biodegradability] Sealed

- vessel CO 2 Production Test Average $13,031

$8,081 $10,556
2 OPPTS 835.3170 Shake

- flask Die

- away Test [measures biodegradability] $53,137 2 OPPTS 850.1730 Fish Bioconcentration $156,076 3 OPPTS 835.3180 Sediment/Water Microcosm Biodegradation $138,942

3 40CFR 797.1330 or 850.1300** Daphnid Chronic Toxicity Test $139,894

3 40CFR 797.1600 or 850.1400** Fish Early Life Stage Toxicity (in rainbow trout) $71,341

3 OECD 422 Combined Repeated Dose Oral Toxicity with Reproductive/ Developmental Toxicity Screening (in rats) $140,459

Total cost, all tiers (assuming all tests are conducted) $777,491
Source: 64 FR 60194, Category for Persistent, Bioaccumulative, and Toxic New Chemical Substances , November 4, 1999, at http://www.epa.gov/EPA

- TOX/1999/November/Day

- 04/t28888.htm

. Tests costs are from Table D -1

. * The PBT FR notice cites 830.7560 and 830.7570

. This tab le used costs for similar tests 796.1720 and 796.1570, respectively

. Tests 830.7550 (Partition Coefficient using Shake Flask method) and “the new ‘slow

- stir’ method currently under development by the OECD” are also mentioned as options for determining the Oct/Water partition coefficient, in the PBT FR notice Response to Comments but not in the main Testing Strategy discussion. ** PBT FR notice cites both tests as equivalents

. This table uses costs for 850.1300 and 850.1400 since they were costed out
more recently by EPA.


### D.3 T esting Costs by Chemical
Test costs attributable to a SNUN are likely to be much lower than the costs that would be implied by adding up costs of all of the testing recommended in the SNUR for that chemical, and usually are zero. 28 

### See the main text of this report for a discussion of testing.

28 A prior SNUR economic analysis calculated chemical

- specific test costs ( EPA, 2007b , Table D

- 4). Th e chemical

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## APPENDIX E: R eferences
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63 FR 41847. Test Guidelines; Notice of Availability, Federal Register, Volume 63, August 5, 1998.

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71 FR 6733. Export Notification; Proposed Change to Reporting Requirements, Federal Register, Volume 71, February 9, 2006. Available from the Federal Docket Management System as docket EPA

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.
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. U.S. EPA, Office of Pollution Prevention and Toxics, Economic and Policy Analysis Branch, Wage Rates for Economic Analysis of the Toxics Release Inventory Program. Washington, DC: June 10, 2002. EPA, 2003a. U.S. EPA, Office of Pollution Prevention and Toxics, Economic and Policy Analysis Branch. Econ omic Analysis of Expedited Significant New Use Rules for 65 Chemical Substances. Washington, DC, 2003. Available from the Federal Docket Management System as EPA

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### Kearney, 1988a. Memorandum to Bill Massouda, Reporting and recordkeeping costs for a generic SNUR, February 3, 1988. [Memo submitted to U.S. EPA/Office of Toxic Substances (now OPPT) under contract 68-02-3980 with A.T.Kearney, Inc.]. Kearney, 1988b. Estimated Cost of the Final Comprehensive Assessment Information Rule, June 1, 1988. Prepared by Ke arney/Centaur for US EPA.
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