PART A OF THE SUPPORTING STATEMENT
Determine Percentage of High Evaporative Emissions
Vehicles in the On-Road Fleet
OMB Control Number 2060-NEW
USEPA Agency Form Number 2292.01
Table of Contents
1.0 IDENTIFICATION OF THE INFORMATION COLLECTION 1
1(a) Title of the Information Collection 1
1(b) Short Characterization/Abstract 1
2.0 NEED FOR AND USE OF THE COLLECTION 2
2(a) Need/Authority for the Collection 2
2(a)(1) Need for Emissions Inventories for Light-Duty Vehicles 2
2(a)(2) The National Academy Report on Emissions Inventory Modeling 4
2(b) Practical Utility/Users of the Data 5
3.0 NONDUPLICATION,
CONSULTATIONS, AND OTHER COLLECTION
CRITERIA 5
3(b) Public Notice Required Prior to ICR Submission to OMB 5
3(d) Effects of Less Frequent Collection 6
4.0 THE RESPONDENTS AND THE INFORMATION REQUESTED 7
4(a) Respondents/NAICS Codes 7
4(b)(i) Data Items, Including Recordkeeping Requirements 8
4(b)(ii) Respondent Activities- 8
5(b) Collection Methodology and Management 9
5(c) Small Entity Flexibility 9
6.0 ESTIMATING THE BURDEN AND COST OF THE COLLECTION 10
6(a) Estimating Respondent Burden 10
6(b)(ii) Capital and Operations Costs 10
6(c) Agency Burden and Cost 11
6(g)(i) Burden Statement for Evaporative Emissions Testing 14
The collection is entitled:
Evaporative Emissions from Light-Duty Vehicles.
In response to recommendations from the National Research Council of the National Academy of Sciences, EPA has initiated a systematic data collection designed to improve the methods and tools used by the Agency to estimate the number of light-duty vehicles with high levels of evaporative emissions. Data to be collected include vehicle type, recent repair history and “in-use” or “real-world” evaporative emission rates.
The collection is a test program, to be conducted by the Office of Transportation and Air Quality (OTAQ) in the Office of Air and Radiation (OAR). This study will combine novel, newly developed test procedures with statistical survey design to estimate the number of vehicles with high evaporative emissions. The new procedures have been developed in a pilot study that preceded the actual test program. The new test procedures employ new technology and test methods that promise to substantially reduce the cost of evaporative emissions measurement as well as improve the accuracy of these estimates.
This phase of the test program will be conducted in Region 6, and participation in the program shall be voluntary. The pilot program used to develop these new procedures was conducted in EPA Region 8, and participation in it was also voluntary. In this second phase, evaporative emissions will be measured using a variety of methods that will include Remote Sensing, a hydrocarbon sniffer designed for automotive applications, and an evaporative emission test system that has been developed for use in the California I/M program by the Bureau of Automotive Repair. Data will be collected during this second phase of the program at on-road sites using RSD and at a specified location for those owners that agree to participate in the program. The RSD data collection phase will provide screening data that will be used to solicit vehicle owners. The RSD data collection will incur no burden cost on the vehicle owner as these measurements will be made as the vehicle drives by the RSD van during normal operation. Measurements performed at the specified location will incur a burden cost on the vehicle owner and this concern is addressed below. Those owners solicited that agree to participate in the program shall be provided with a rental car and their vehicle immediately subjected to the test protocol outlined below as resources permit. Following quality-assurance and analysis, the data will be stored in OTAQ’s Mobile Source Observation Database.
The information collection will involve 1,000 respondents, requiring xxx hours to complete at a total cost to those respondents of $168,545. For the agency, the collection will require 8,670 hours at a total cost to the agency of approximately $1,302,231.
The term “light-duty high evaporative emission vehicles” refers to passenger cars and trucks less than 8500 lbs. GVWR with high evaporative emissions. Light-duty evaporative emissions contribute substantially to mobile source hydrocarbon emissions. Although it is believed light-duty evaporative emissions may contribute as much as one-third of the mobile source HC inventory, this figure has not been quantified empirically due to the difficulty in accurately and inexpensively measuring these emissions. Light-duty fuel consumption in the United States was 74,085 million gallons in 2005, and any HC emissions either from exhaust or evaporation will not only impact the environment, but will also incur a loss in fuel economy.
An emissions inventory is an estimate of the quantity of a pollutant emitted to the atmosphere in a given geographic area during a given time period. For example, an inventory can represent the quantity of carbon monoxide emitted by various sources in Washtenaw County, Michigan during the spring of 2004. Within an inventory, emissions are typically allocated by source category, with sources classified as “stationary,” “area”, or “mobile.” Stationary sources include large facilities with identifiable emissions outlets, such as coal-fired power plants or industrial boilers. Area sources include activities for which emissions are diffuse. Examples include feedlot operations, dry cleaners or wildfires. As the name implies, mobile sources move from place to place. They include light-duty vehicles (cars and trucks), as well as other categories such as heavy-duty (greater than 8500 lbs. GVWR) and nonroad equipment.
The USEPA Office of Transportation and Air Quality (OTAQ) has developed and supports the MOBILE model to estimate emissions from motor vehicles, and work is currently underway on a new modeling tool known as MOVES that will replace MOBILE in the near future. Both models estimate fleet emissions for motor vehicles expressed in g/mile and derived as complex weighted averages of emission rates for various vehicle types; however MOBILE does this using fleet emission factors and user input activity data, while MOVES will use fleet inventory data with default activity rates available to the user. To develop an inventory (tons/yr), model users combine emission factors with estimates of usage, expressed as miles traveled by different types of vehicles, such as cars, light trucks, buses, and heavy trucks. A typical source of usage data is “vehicle miles traveled”(VMT) as estimated by the Federal Highway Administration’s Highway Performance Monitoring System (HPMS).
The MOBILE model is used by various agencies for several differing but related purposes. The Environmental Protection Agency is a primary user. The Office of Transportation and Air Quality (OTAQ) relies on MOBILE to estimate emissions reductions due to proposed emissions standards for light-duty vehicles. Additionally, the Office of Air Quality Planning and Standards (OAQPS) uses MOBILE as one tool in development of the National Emission Inventory (NEI). The NEI is a comprehensive database of emissions inventories, updated and published by EPA every three years, (1996, 1999, 2002, etc.). The NEI includes emissions estimates from stationary, point, area and mobile sources for each county in the nation.
MOBILE is also extensively used by state and county agencies principally to assess or plan for compliance with the Clear Air Act (CAA). Two important programs under the CAA are the National Ambient Air Quality Standards (NAAQS) and the Regional Haze Rule (RHR). In implementation of these programs, technical support from EPA is important, particularly with respect to estimation of emissions from passenger vehicles, because local agencies typically lack the technical and financial resources to develop independent inventories.
The NAAQS are standards that regulate concentrations of several air pollutants including sulfur dioxide, carbon monoxide, nitrogen dioxide, ozone and fine particles that can be detrimental to human health or damage vegetation or property. The standards specify maximum concentrations, with corresponding time periods over which average concentrations are calculated (averaging periods). For example, the terms “1-hour” and “8-hour” ozone represent average ozone concentrations calculated over periods of one hour and eight hours, respectively, for which different standards are in effect. If local monitoring consistently shows no violations of the standards for a given pollutant in a given geographic area, EPA can designate that area as “in attainment” for that pollutant. However, if monitoring shows violations for one or more standards, EPA can designate it as “in non-attainment” for one or more pollutants. For nonattainment areas, state and local agencies prepare “State Implementation Plans” (SIPs) to demonstrate how compliance will be reached or maintained over specific timetables.
Light-duty gasoline vehicles are estimated to contribute roughly 54% of the overall VOC mobile-source inventory of 8.3 million short tons in 2002. If one accepts that evaporative emissions account for 30% of these VOC emissions, the mass of evaporative VOC losses is roughly 1.4 million tons per year.
At the request of Congress, the National Academy of Sciences published a report on EPA’s Inspection and Maintenance program (NRC 2001). A committee of technical experts was given the primary charge of reviewing I/M programs across the nation as well as the role of the MOBILE model in these programs. The committee concluded that there is currently no accurate inexpensive way to identify vehicles with high evaporative emissions. The recommendations in this NRC report along with those in an earlier NRC study (2000) have influenced the concept and design of EPA’s new inventory model for highway vehicles, the Motor Vehicle Emissions Simulator (MOVES). Similarly, this study is intended as a necessary step in an effort to respond to the need to develop test procedures to identify vehicles with high evaporative emissions and quantify the level of these emissions.
The legislative basis for this data collection is Section 103(a)(1)(2)(3) of the Clean Air Act, which requires the Administrator to: “conduct ... research, investigations, experiments, demonstrations, surveys, and studies relating to the causes, effects, extent, prevention, and control of air pollution, ...” and “cooperate with ... pollution control agencies and other appropriate public or private agencies, institutions, and organizations, and individuals in the conduct of such activities, ...” and “conduct investigations and research and make surveys concerning any specific problem of air pollution in cooperation with any air pollution control agency ...”
In addition, Section 103(b)(1) of the Clean Air Act authorizes the Administrator to: “collect and make available, through publications and other appropriate means, the results of and other information, including appropriate recommendations by him in connection therewith, pertaining to such research and other activities.” The full text of the relevant sections is provided in Appendix A.1.
The principal users of the data will be EPA technical staff, for purposes of estimating the evaporative emissions from the national fleet. This data will be used to characterize the fleet evaporative emissions as the Agency develops the MOVES model. Little data on the fraction of high evaporative emissions vehicles exist and this study would be a landmark study that would define the fraction of high evaporative emissions vehicles in the fleet.
Finally, analysis and evaluation of this initial data set from San Antonio will enable evaluation of the cost-effectiveness of the design as proposed. In addition, these results will guide and inform sample size analyses. Data collected will provide highly valuable estimates of variability in key variables, as well as scenarios and expected differences needed for more refined power analyses. Specific analyses to be performed are described in Part B of this Supporting Statement, in sections 2(b)(ii), “Sample Sizes,” and in Section 5(b), “Data Analysis.”
In development of this collection, EPA has attempted to locate sources of data that would partially or wholly duplicate the information to be collected. No such duplication was found. EPA searched published literature for terms related to light-duty evaporative emissions measurement. No duplication of the data collection effort was found. To our knowledge, no other agency has a proven method to identify and measure emissions from high evaporative vehicles in the field.
The initial announcement of the public comment period for the proposed ICR amendment was placed in the Federal Register on February 14, 2008. However, a “second” Federal Register Notice will be published concurrent with submission of this collection to OMB.
Technical Consultations. In the development of this collection, we consulted with professionals with expertise in survey methodology and statistics, RSD and on-road HC measurement both in academia and the private sector. Specific parties and contact information is listed below:
Hugh Williamson, Ph.D. Engineering Scientist CACI Technologies, Inc. 11211 Taylor Draper Lane, Suite 115 Austin, Texas 78759 (512)406-3618 |
Dennis McClement Sierra Research 1801 J Street Sacrament, CA 95811 916-444-6666 |
Jim Sidebottom Colorado Department of Health 4300 Cherry Creek Dr. Denver, CO 80246 303-692-3149 |
Drew Rau Remote Sensing – ESP Colorado 5175 Marshall Street Arvada, Colorado 80015 O: 303-456-7035 C: 303-961-5641
|
Mia Zmud NuStats 206 Wild Basin Road, Building A - Suite 300, Austin, Texas 78746 512 306 9065 |
Rob Santos Urban Institute 202 261 5904 |
This supporting statement was prepared by:
Sandeep Kishan
Tim DeFries, Ph.D.
Jim Lindner, Ph.D.
Eastern Research Group
5608 Parkcrest Drive
Austin, TX 78731-4947
512-407-1830
For each respondent, participation in the study is a one-time event. Thus, periodic reporting is not requested or required.
Participation in the program by each owner is on a voluntary basis. Further, this information collection complies with the guidelines in the Paperwork Reduction Act (5 CFR 1320.5(d)(2)). Specifically, the collection does not require the respondents to:
Report information to EPA more often than quarterly;
Prepare a written response to a collection in fewer than 30 days after receipt;
Submit more than one original document;
Retain any records for more than three years;
Participate in a statistical survey that is not designed to produce data that can be generalized to the universe of study;
Use a statistical data classification that has not been reviewed and approved by OMB;
Submit any information that they may consider to be confidential, without EPA demonstrating that it has instituted procedures to protect the information’s confidentiality to the extent permitted by law.
Data will be collected under a pledge of confidentiality for exclusively statistical purposes, therefore EPA will not use or disclose survey results in identifiable form for any non-statistical purpose.
To protect the confidentiality of respondents, the following items allowing direct identification of individuals will not be disclosed or directly linked to survey results under any circumstances.
Participant name(s)
Participant address(es)
Participant phone number(s)
Participant contact name(s)
Vehicle Identification number (VIN)
The following additional items will be protected from disclosure as necessary to protect individual respondents from identification through indirect means. The methods considered for prevention indirect disclosures are briefly described for each item, drawing on approaches recommended for the protection of public-use microdata by the Federal Committee on Statistical Methodology (FCSM 2004).
The questionnaires do not ask any sensitive questions pertaining to sexual attitudes/behavior or religious beliefs.
As defined in Part B, section 2(a), respondents to the survey will be owners of light-duty cars and trucks. This sector is fairly well-defined and we anticipate our sampling of this population will provide a representative sample based on the statistical methods outlined in Part B of this ICR.
We define the target population in more detail in Part B, section 2(a).
Reporting Items. All items that respondents will be requested to report are listed and described in Part B, Section 4.
Recordkeeping Items. This collection will not request or require respondents to compile or maintain any records.
Respondent activities for this data collection include:
Respond to initial contact via letter or phone call to agree to participate
Appear at designated testing facility for portable SHED (PSHED) measurements
Complete solicitation process – transfer vehicle to contractor
Complete vehicle exit paperwork
Possible participation in off-site lab testing
The following sections describe Agency activities related to survey design, oversight, and analysis, maintenance and distribution of the information collected. The primary activities associated with the actual collection of information will be performed by EPA personnel or contractors hired by the Agency.
In conduction of the survey, the agency will perform the following activities:
Develop research questions
Develop a plan for conducting a study to answer the questions
Develop data forms and test procedures
Conduct Pilot testing
Analyze Pilot Study data
Refine testing methodology
Modify Data forms and test procedures
Conduct Main Study
Collect and quality-assure data
Perform data analysis
Publish report and findings of the study
The questions to be used to solicit owners to participate in this study shall be developed jointly between EPA, ERG and NuStats. Techniques similar to those used by EPA and ERG during a recent study in Kansas City involving owner solicitation and participation will be employed.
The questionnaire to be used for the owner survey once they have agreed to participate will be given to each owner when they arrive at the facility for PSHED testing. Due to the brevity and simplicity of the questionnaire, we do not anticipate any hardship to the vehicle owner in completing it quickly during the interview process with the technician.
To ensure data quality for interview information, each interview response will be reviewed for completeness and internal consistency. Emissions and activity data collected via instrumentation will be quality-assured through use of computer algorithms. Time series for key variables will also be plotted and visually checked on a case-by-case basis. Quality-assurance steps for data collected are discussed in Part B, Section 5(a), “Data Preparation.” Following quality-assurance, electronic data will be directly transferred into database software. Computer files containing interview responses will be stored or managed in spreadsheet software, such as Microsoft Excel®, or database software such as Microsoft Access® or Microsoft FoxPro®. Analyses will be performed using SAS, version 8.2®, or SPSS, version 9®. Data will be stored in the “Mobile Source Observation Database,” (MSOD), an Oracle® database residing on an Agency server. This database is available to the public on request on CDROM, and can also be accessed from the server via a viewer based on Microsoft Access®. Thus, users need not be equipped with Oracle software or expertise to access the database.
As described above, collection methods for the survey have been designed to keep the burden of participation to a bare minimum. Additionally, participation in the program is voluntary, giving owners the option of not participating if they so choose.
The tentative schedule below assumes OMB clearance for this collection will be obtained by November, 2008. For each task, we show the date targeted for its completion.
Design questionnaire and sampling plan October, 2008
Collect RSD Samples, October, 2008
Field Validation & Questionnaire, October/November, 2008
Submit Draft Report November, 2008
Submit Final Report December, 2008
The burden estimates calculated in this section are inclusive of both the fall pilot and the balance of the program in the spring of 2009.
Table A.1 presents initial estimates of burden and cost for respondents participating in the collection. The initial RSD screening will be done non-intrusively and will therefore not impact the owner in any way. Initial contact with the vehicle owners will take no more than 1 hour. This will involve a letter sent by U.S. mail and a follow-up phone call outlining the program and requesting participation. All owners contacted will receive an incentive for their time spent responding to the phone solicitation. Those owners who agree to participate shall also be reimbursed for their time. It is estimated that the time required for those who participate will be approximately 1 hour total in travel time to and from the testing facility, and an additional 2 hours for the actual PSHED test measurements.
Table A.1 presents estimated burden and cost to respondents.
For respondents, participation in this collection will not require any labor. Thus, there is no labor cost represented in Table A.1.
For respondents, participation in this collection will not require any capital or startup costs, and there will be no operating or maintenance costs. Thus, no costs in either of these two categories are represented in Table A.1.
Information Activity |
Respondent Time |
Labor cost* |
No. Respondents |
Total Time |
Total Cost |
|||
|
|
|
|
hrs |
($/hr) |
|
hrs |
($) |
Read Mail out |
0.1 |
$ 25.93 |
100001 |
1000 |
$ 25,930 |
|||
Respond to Solicitation Phone Call |
0.25 |
$ 25.93 |
100001 |
2500 |
$ 64,825 |
|||
Complete solicitation process - transfer vehicle to contractor to and from |
1 |
$ 25.93 |
10002 |
1000 |
$ 25,930 |
|||
Participate in on-site emissions testing |
2 |
$ 25.93 |
10002 |
2000 |
$ 51,860 |
|||
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Total |
6500 |
$ 168,545 |
* Source: |
EMPLOYER COSTS FOR EMPLOYEE COMPENSATION— JUNE 2007,Bureau of Labor Statistics, US Dept of Labor |
11000 for fall pilot and 9000 for spring balance of program
2100 for fall pilot and 900 for spring balance of program
Table A.2 presents Agency burden and cost for the program. In all cases, separate estimates are presented for Contractor personnel and Agency staff.
Table A.2 presents estimated agency labor hours for each activity listed above. We have separated labor hours into two components, those hours to be worked by Agency staff and those to be worked by contractor personnel. In general, the contractor will perform the emissions measurements, solicit the vehicle owner, handle the necessary paperwork and perform initial quality assurance, following which the contractor will transfer the data to EPA. Agency personnel will then load the results into an EPA database and perform quality-assurance and substantive analyses.
For contractor personnel, most of the time represents preparation for the field work, arranging the field logistics, vehicle solicitation, data collection, emissions measurement, equipment QA/QC and data entry. These activities are assumed to take 30 man hours per vehicle on average, respectively.
For agency staff, we assume that agency personnel will be involved in the weekly management of the project, provide oversight and arrange emissions equipment, as necessary. Agency staff will also be involved in reviewing the data collected on a regular basis and for will provide technical input throughout the program. For analysis, we assume that agency staff will spend about 10% of the hours spent by contractor personnel.
Contract Labor Costs. The average contract labor cost for this effort is $100 per hour as listed in Table A2.
Agency Labor Costs. Labor Costs for EPA staff were taken from the 2008 Locality Schedule for Civilian Federal Employees in the Detroit area. Based on the Schedule, we have assumed average hourly labor costs of $56.00 for managerial personnel, $52.09 for technical personnel and $21.65 for clerical personnel. These assignments correspond to levels of GS-15-1, GS-13/14-7 and GS-7-5, respectively. We have multiplied the hourly labor rates by a “benefits multiplier” of 1.6, to represent the total cost of employment for Federal staff (OEI, 1999).
Capital costs during the pilot and main study include costs for site set up, PSHED set up, RSD van acquisition for testing site, equipment and tools. Operation and maintenance include costs for participant incentives, compensation, participant rental cars, RSD field deployment, calibration and audit gases and contractor travel.
Form Approved
OMB Control No. 2060-NEW
Approval expires dd/mm/yyyy
EPA is conducting a statistical survey to characterize the fraction of high emitting evaporative emissions in the national gasoline light duty fleet. The initial RSD screening will be done non-intrusively and will therefore not impact the owner in any way. Performing the initial solicitation of the owner will take approximately 1.0 hour. It is estimated that the time required for those who participate will be approximately 1 hour total in travel time to and from the testing facility, and an additional 2 hours for the actual PSHED test measurements. Vehicles would be recruited on a voluntary basis. The public reporting and recordkeeping burden for this collection of information is estimated to average 2.0 hours per response. Burden means the total time, effort, or financial resources expended by persons to generate, maintain, retain, or disclose or provide information to or for a Federal agency. This includes the time needed to review instructions; develop, acquire, install, and utilize technology and systems for the purposes of collecting, validating, and verifying information, processing and maintaining information, and disclosing and providing information; adjust the existing ways to comply with any previously applicable instructions and requirements; train personnel to be able to respond to a collection of information; search data sources; complete and review the collection of information; and transmit or otherwise disclose the information.
An agency may not conduct or sponsor, and a person is not required to respond to, a collection of information unless it displays a currently valid OMB control number.
To comment on the Agency's need for this information, the accuracy of the provided burden estimates, and any suggested methods for minimizing respondent burden, including the use of automated collection techniques, EPA has established a public docket for this ICR under Docket ID No. EPA-HQ-OAR-2008-0118, which is available for public viewing at the Air and Radiation Docket in the EPA Docket Center (EPA/DC), EPA West, Room 3334, 1301 Constitution Ave., NW, Washington, DC.
The EPA Docket Center Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through Friday, excluding legal holidays. The telephone number for the Reading Room is (202) 566-1744, and the telephone number for the Air and Radiation Docket is (202) 566- 1742.
An electronic version of the public docket is available at www.regulations.gov. This site can be used to submit or view public comments, access the index listing of the contents of the public docket, and to access those documents in the public docket that are available electronically. When in the system, select “search,” then key in the Docket ID Number identified above. Also, you can send comments to the Office of Information and Regulatory Affairs, Office of Management and Budget, 725 17th Street, NW, Washington, DC 20503, Attention: Desk Office for EPA. Please include the EPA Docket ID No. (EPA-HQ-OAR-2008-0118) and OMB control number (2060-NEW) in any correspondence.
Bureau of Labor Statistics. 2003. Employer Costs for Employee Compensation-June 2003. USDL: 03-446. U.S. Department of Labor, Washington, D.C.
Federal Committee on Statistical Methodology. 2004. Report of Statistical Disclosure Limitation Methodology. Subcommittee on Disclosure Limitation Methodology. Statistical Policy Office, Office of Information and Regulatory Affairs, Office of Management and Budget. Statistical Policy Working Paper 22. http://www.fcsm.gov/working-papers/spwp22.html. May, 2004.
National Research Council. 2000. Modeling Mobile-Source Emissions. Committee to Review EPA’s Mobile-Source Emissions Factor (MOBILE) Model. National Academy Press, Washington D.C.
National Research Council. 2001. Evaluating Vehicle Emissions Inspection and Maintenance Programs. National Academy Press, Washington D.C.
Office of Environmental Information. 1999. ICR Handbook: EPA’s Guide to Writing Information Collection Requests Under the Paperwork Reduction Act of 1995. Collection Strategies Division, U.S. Environmental Protection Agency. Washington, D.C.
APPENDIX A-1
Relevant Sections of Statutes
The Statutes relevant to this collection are '103(a) and '103(b) of the Clean Air Act, listed below:
Sec. 103. (a) The Administrator shall establish a national research and development program for the prevention and control of air pollution and as part of such program shall ‑
(1) conduct, and promote the coordination and acceleration of, research, investigations, experiments, demonstrations, surveys, and studies relating to the causes, effects (including health and welfare effects), extent, prevention, and control of air pollution;
(2) encourage, cooperate with, and render technical services and provide financial assistance to air pollution control agencies and other appropriate public or private agencies, institutions, and organizations, and individuals in the conduct of such activities;
(3) conduct investigations and research and make surveys concerning any specific problem of air pollution in cooperation with any air pollution control agency with a view to recommending a solution of such problem, if he is requested to do so by such agency or if, in his judgment, such problem may affect any community or communities in a State other than that in which the source of the matter causing or contributing to the pollution is located;
(4) establish technical advisory committees composed of recognized experts in various aspects of air pollution to assist in the examination and evaluation of research progress and proposals and to avoid duplication of research; and
(5) conduct and promote coordination and acceleration of training for individuals relating to the causes, effects, extent, prevention, and control of air pollution.
(b) In carrying out the provisions of the preceding subsection the Administrator is authorized to ‑
(1) collect and make available, through publications and other appropriate means, the results of and other information, including appropriate recommendations by him in connection therewith, pertaining to such research and other activities;
(2) cooperate with other Federal departments and agencies, with air pollution control agencies, with other public and private agencies, institutions, and organizations, and with any industries involved, in the preparation and conduct of such research and other activities;
(3) make grants to air pollution control agencies, to other public or nonprofit private agencies, institutions, and organizations, and to individuals, for purposes stated in subsection (a)(1) of this section;
(4) contract with public or private agencies, institutions, and organizations, and with individuals, without regard to sections 3648 and 3709 of the Revised Statutes (31 U.S.C. 529; 41 U.S.C. 5);
(5) establish and maintain research fellowships, in the Environmental Protection Agency and at public or nonprofit private educational institutions or research organizations;
(6) collect and disseminate, in cooperation with other Federal departments and agencies, and with other public or private agencies, institutions, and organizations having related responsibilities, basic data on chemical, physical, and biological effects of varying air quality and other information pertaining to air pollution and the prevention and control thereof;
(7) develop effective and practical processes, methods, and prototype devices for the prevention or control of air pollution; and
(8) construct facilities, provide equipment, and employ staff as necessary to carry out this Act.
In carrying out the provisions of subsection (a), the Administrator shall provide training for, and make training grants to, personnel of air pollution control agencies and other persons with suitable qualifications and make grants to such agencies, to other public or nonprofit private agencies, institutions, and organizations for the purposes stated in subsection (a)(5). Reasonable fees may be charged for such training provided to persons other than personnel of air pollution control agencies but such training shall be provided to such personnel of air pollution control agencies without charge.
File Type | application/msword |
File Title | Note: Add an Executive Summary that states the goals, and results from those goals as it relates to Qa/QC issues |
Author | A. White |
Last Modified By | ckerwin |
File Modified | 2008-11-07 |
File Created | 2008-11-07 |