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HomeMy WebLinkAbout30710 / 80-15May 15, 1980 # 15 RESOLUTION PURPOSE: Application and Initiation of Air Quality Monitoring Grant INTTIATED BY: Department of Community Development SdHEREAS, the City of Oshkosh has i�een determined to be a secondary nonattainment arca, and 4IHEREAS, the City of Oshkosh is in�erested in controlling the oarticulate mztter emissions which have placed it in this secondary nonattainment area, and WHEREAS, the University of Wisconsin-Oshkosh has agreed to eza�nd the existing monitoring network in Osfikosh, and to conduct tests �o deternine the exact nature of these particulate emissions, and WHEREAS, the Department of Natural Aesources has agreed to participate in rthe5e tests fox the entrapmen� of vehicular dust by paying for the expansion of the City's Street Sweep- ing Program, NOS�I, THEREfORE, BE IT RESOLVED that the City of Oshkosh enters into this Interagency Agreement with the University of Wisconsin-Oshkosh and the Department of Natural Resources, in accordance with the attached Interagency Agreement and Proposal for a Demonstration Project, The City Manager is herehy authorized to ad�inister this prograr.i. - 15 - S',�E'?'T^»D BY APP. OVED ' " °"' � �C�.i) . Control o� �art�culate Matter Emzssions from Nontradztional Sources in � Oshkosh, Wisconsin � A Proposal for a Demonstration Project 1. INTRODUCTION Traditional sources of particulate matter emission are those sources that have historically been oP concern to air pollution control programs. Fuel combustion, solid waste incineration and industrial process sources, including both "stack-vented" and "fugitiVe" emissions, comprise this group of particulate sources. Fugitive emissions are defined as particles emitted from any source other than a smokestack of flue. Traditional fugitive emissions are particles which escape to the atmosphere from industrial facilities through windows, doors, vents, etc. rather than through a stack, flue or emission control device. Nontraditional sources of particulate emissions are those sources which have historically not been of concern to air pollution control programs. This group of sources includes entrainment of dust by vehicular traffic on paved and unpaved roads and parking lots, motor vehicle exhaust, automobile brake and tixe wear, construction and demolition activity, agricultural tilling, and wind erosion from natural nonvegetated surfaces and agricultural fields. Most of these nontraditional sources are fugitive emission sources. The Need for this Stud c Section 107Cd) of the Clean Air Act Amendments of 1977 requires each State to designate any areas in the State which have not attained the National Ambient Air Quality Standards matter (TSP) as nonattainment areas �' � � CNAAQS) for total suspended particulate The Federal Register contains a list of areas in Wisconsin which have been designated as nonattainment for either primary or secondary standards or designated as unclassifiable. An unclassifiable designation is necessary when there is a lack of sufficient usable data with which a classification can be made. Section 110Ca)Cl) of the Clean Air Act requires states to submit an imple- mentation plan which provides for the achievement of the primary standards by December 31, 1982 and the secondary standards as expeditiously as / practicable. The Act specifies conditions that must be included in a State implemenfation plan CSIP). One of these conditions is that the State shall show, in the interim prior to achieving the standards, reasonable further progress towards meeting the standards. This includes such reductions as may be achieved from existing sources in nonattainment areas through the adoption, at a minimum, of reasonably available control technology CRACT). The U.S. Environmental Protection Agency has interpreted these SIP Revision requirements to include adoption of all necessary emission limitations and legally enforceable rules for traditional sources, and a commitment to control non-traditional sources if necessary for attainment, The commitment to control non-traditional sources of TSP emissions shall take the form of a schedule to develop, submit, and implement the legal],y enforceable procedures and programs for controlling non-traditional parti- culate matter sources. To provide for clean air in Wisconsin and to meet the requixements of the Clean Air Act, the State of Wisconsin has adopted legally enforceable rules ..2 -. ` � �� requiring existing traditional particulate matter emission sources whose emissions have significant impact upon primary and associated secondary TSP nonattainment areas to meet emission limits requiring the application of RACT. A second set of RACT rules applying to sources which have significant impact upon secondary nonattainment areas not associated with primary nonattainment areas is presently being adopted. These new RACT particulate emission limitations are more stringent than the old limitations and will result in air quality improvements in TSP nonattainment areas. However, analyses of TSP samples collected in many of Flisconsin's nonattainment areas indicate that nontraditional sources are major contributors to nonattainment. Tn addition, the air dispersion modeling analyses done for several nonattainment areas indicate that application of the new RACT emission limitations to traditional sources will not result in attainment of the TSP NAAQS. Thus, in many nonattaS,nment areas there is a need to control particulate matter emissions from nontraditional sources if the standards are to be achieved. As part of its revised STP, the State of Wisconsin has adopted a commitment to develop regulations limiting emissions from nontraditional sources. Methods for controlling particulate matter emissions from nontraditional sources include such activities as street sweeping and/or vacuuming, paving or unpaved streets and parking lots, revegetation of Vacant lots, and treating unpaved surfaces wi.tt� water� ozl or other chemicals, L�.tt1e is known about the,effectiveness of these nontrad�tional souree control techniques. Hence, there is a need for demonstration projects, sucIi as -3- the one proposed here, which will evaluate the effect on air qualit of"the application of an actual nontraditional particulate emission control program in a Wisconsin nonattainment area. The City of Oshkosh contains a TSP secondary nonattaznment area (See Figure 1), Laboratory Analyses of particulate samples collected �n Oshkosh indicate nontraditional sources to be major contributors to the high TSP concentra- tions. DNR estimates of particulate matter emission in Oshkosh support the filter analysis findings. The DNR estimates that about 2069 tons of particulate matter were emitted from all sources in Oshkosh in 1978. About 62 percent of those 2069 tons C1289 tons� came fxom nontraditional sources. The DNR estimated that 1036 tons of the 1289 tons came from entrainment of dust from paved roads. Thusn that one nontraditional source category accounted for about SOo of all particulate matter emzssions in Oshkosh in 1978. The air dispersion modeling analysis done by the DNR Por Oshkosh indicates that the application of the new RACT emission limits to existing traditional sources in Oshkosh will result in a small improvement in air quality, but will not result in attainment of the TSP standards. It will� thus, be necessary to control particulate matter emissions from nontraditional sources to attain the standards. For the various reasons cited above, Oshkosh is an ideal place to test the emission control technique of street stveeping and document its efrect upon air quality. This proposed demoiistration project will compliment a demonstration project already �one in Milwaukee and another one proposed for Superior, Wisconsin. The results of this study wi11 be used by the Wisconsin DNR in the development of rules to control nontraditional emissions in Oshkosh and other Wisconsin nonattainment areas. �4- Participating Agencies in-the Proposed Study �� _ � The following three agencies will participate in the proposed study: 1. The City of Oshkosh 2. The University of Wisconsin-Oshkosh 3. The Wisconsin Department of Natural Resources The City of Oshkosh wi11 be the lead agency and prime initiator in the study. As such, they will be responsible for the bu�iget and seeing tfiat the project is carried out in a timely fashion street sweeping program. The City will also conduct the actual The University.of Wisconsin-Oshkosh will operate the proposed TSP monitoring network and will perform laboratory analyses of some of the collected TSP samples. The Wisconsin DNR will provide funding, monitoring support and technical support for the project. The DNR will also contract with a testing laboratory to have selected TSP samples analyzed. 2. OBJECTIVES OF THE PROPOSED STUDY Overall Objective The overall objective of the proposed study is to test the nontraditional particulate matter emission control technique of street sweeping in the Oshkosh TSP nonattainment area and to evaluate its effectiveness in reducing TSP concentrations. The overall objective will be accomplished by May 1, 1981. �S, Specific Objectives � �� To support the overall objective, the specific objectives of this proposed study are: 1. To better characterize the spatial extent of the Oshkosh secondary TSP nonattainment area and provide monitoring data for further analysis Ctask 10�), 2. To quantify the contribution of particulate matter emissions £rom nontraditional sources relative to the TSP concentrations sampled. CTask 20�). 3. To identify specific nontraditional sources contributing to TSP con- centrations by laboratory analyses of the TSP samples collected CTask 200). 4. To demonstrate the nontraditional particulate emission control technique of street sweeping through a physical experiment, and to evaluate that control technique based on social, economic, and technical factors (Task 300). 5. To recommend strategies for the control of fugitive dust emissions from nontraditional sources so as to attain and maintain the TSP NAAQS Statewide. 3. STUDY DESIGN � , The overall study design consists of a before-during-after type experiment to be conducted during the spring, summer, and fall of 1980. '.t.'� ` � �� A TSP monitoring network will be set up for the study and will be operated for the duration of the study Csix to seven manths). Monitoring will commence on or about April 15, 1980. After the monitoring networh has operated for two months Cthrough June 15) street sweeping will start. Street sweeping will be done on a regular basis for a period of three months tJune 15 to September 15), After the street scaeeping demonstration is completed, the monitoring network will be operated for an additional two months CSeptember 15 to November 15). The monitoring data will then be statistically analyzed and the "before" and "after" data will be compared with the "during" data to determine the effect oY the street sweeping program on air quality. Selected TSP samples will be analyzed in the laboratory to determine the characteristics and sources of the collected particles. 4. STUDY PLAN A. Data Collection The data to be collected during the study will be TSP concentrations and meteorological data <wind speed, wind direction, and precipitation). These are discussed in more detail below. TSP Monitorin a. Monitoring Site Selection C100-10) There are presently two permanent TSP monitoring sites in Oshkosh. For this study, three additional hi-volume air samplers wi11 be installed and operated. The sites for these new samplers will be selected jointly by staff from al1 three participants in the study. The sites will be located relative to tIie -7- � �1� streets to be swept and other TSP sources such that, considering the prevailing wind direction, they will provide data adequate to evaluate the effect of the street sweeping program on air quality. Two of the new samplers will be located downwind of the street sweeper area and the other one will be located upwind. The prevailing wind direction is from the southwest. The two permanent TSP samplers in Oshkosh w9.11 be included in the monitoring network for this study, so there wi11 be a total of five samplers involved in the study. b. Operation of the TSP Monitoring Network C1��-20) The proposed monitoring schedule for the study is as follows: During the "before" and "after" periods of the study, the three new samplers will be operated every third day and the permanent samplers will be operated on their normal schedule Cevery sixth day?. The three new samplers wi11 be operated in phase with the two permanent samplers so that all five samplers will be operated every sixth day. During the street sweeping demonstration, all five samplers will be operated every other day. The University of Wisconsin-Oshkosh is presently operating the two permanent samplers in Oshkosh. During the study� the University will also be responsible for operating the three study monitors, The University will also be respon- sible for setting up, maintenance and calibration of the samplers and for conditioning the filters and weighing them before and after the TSP samples are collected and determining the TSP concentrations. The DNR will: a) supply the University with the high-volume samplers and glass fiber filters for the study, b) assist in setting up the high-volume samplers, and c) provide ongoing quality assurance for the TSP data collected ciuring the study. ^$_ ' Meteorological Data C100-30) � � � The meteorological data to be collected during this study are hourly wind speed and direction, and daily precipitation. These data are collected in Oshkosh and they are available from the National Climactic Center in Asheville, North Carolina. The City of Oshkosh will be responsible for obtaining the meteorological data and transforming it into a useable format. B. Laboratory Analysis of Filters Selection of Filters for Analysis C200-10) A number of the hi-volume filters collected during the study will be selected for laboratory analysis. Meteorological conditions and TSP concentrations wil be considered in selecti_ng the filters for analysis. A detailed methodology for selecting filters will be developed by one or more of the participating agencies at a later date. Laboratory Analysis of the Filters C200-201 Laboratory analysis of the filters will be conducted both by the Illinois Institute of Technology Research Institute CIITRT) under contract with the Wisconsin DNR and by the University of Wisconsin-Oshkosh, The purposes of the filter analyses will be to characterize the collected particles and to determine the sources of the particles. Tt is especially desirable to distinguish between particles from nontraditional sources versus those from traditional sources and to quantitatively determine the contribution from each of the specific nontraditional source categories. Particle sizes and other optical characteristics will be determined by optical microscopy, Electron microscopy and chemical analysis may also be necessary, �� C. Demonstration Project � � �. The proposed demonstration project will consist of a regular street sweeping program to be conducted on se2ected streets in and around the Oshkosh TSP nonattainment area during the months of June, July and August, 1980. The streets to be swept and the frequency oY sweeping will be decided jointly by the City of Oshkosh and the DNR CTask 300-10). The street sweeping program CTask 300-20) will be conducted by the City of Oshkosh. D. Data Analysis and Evaluation of the Demonstration Project C300-30) The City o� Oshkosh and its designated subcontractor will be responsible for analyzing the data collected during the study and for evaluating the air quaiity benefit of the demonstration project. This will be done by reviewing the filter analysis results and conducting statistical analyses of the TSP data collected before, during, and after the demonstration project. The City of Oshkosh will also be responsible for evaluating the social and economic costs of the street sweeping program and will evaluate the long term feasibility of this emission control strategy. The City will also be responsible for investigating the effectiveness of various local government regulations in controlling fugitive dust problems, Some 1oca1 regulations to be considered include prohibiting the construction of unpaved parking lots, requiring gravel trucks to cover their loads, and establishing vegetative screens around parking areas. CA literature search will be per£ormed as part of the background preparation in evaluating the use of vegetation in con- trolling particulate emissions.) �7-�^ E. Re ort Pre aration J�� P P � The City of Oshkosh will be responsible Por the preparation of the final report for the study. The final report and all interim reports and outputs will be reviewed and approved by �he DNR prior to publication. F. Time Schedule Table 1 Cattached) contains a time-line chart showing the time schedule for the proposed study. The estimated beginning and ending dates for each task involved in the study are shown. 5. BUDGET The attached budget CTable 2) has been prepared pursuant to conversations between the three agencies participating in the study, The Wisconsin DNR will provide funding in the form of a grant to the City of Oshkosh. The City will be responsible for allocating the funds and overseeing the budget for the study. �11� ' ..�r...-.� �,� I . ( � � , ) Llbby p ba . Fig. i �;.•',. � �• ('�� � i Ostilcoah 75P Non-Attainment Aren � t ' ��� 6 i�1 � �, �° ' I � "•,' ° ,° . - -- -- -_-_ � — � Q' .. i n / ... ,n,� � ,5 / •:'/F - e q .��.( 6.a --� — '�. -- � �� `- � = ,_ IA �ly' rV....i r . . . . . � V..- =I I I � ..� 'n'�__., r�, " V � � �i � � � n � - •„ I/ "�' � . �. 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This agreement is a subcontract between the City of Oshkosh and the University of Wisconsin-Oshkosh for the i performance of certain operations specified in the award from the DNR. I. Project Title - Control of Particulate hiatter Emissions from Nontraditional Sources in Oshkosh, Wisconsin II. Duration of Project - 7he University of Wisconsin-Oshkosh portion of the project will be performed from April 1980 through October 1980, as outlined in the attached agreement between the WDNR and the City of Oshkosh. III. Under the terms of the attached agreernent, the University of Wisconsin-Oshkosh agrees to operate the proposed TSP monitoring network, to perform laboratory analyses of some of the collected TSP samples, to provide data analysis and evaluation to the City of Oshkosh, and to prepare a final report of its findings. a. Plonitoring Net�dork - There are presently two permanent TSP monitorinq sites in Oshkosh. For this study, three additional high-volume air samplers will be installed and operated. The sites for these new samplers will be selected jointly by staff from the University, the City and the WDNR, as outlined in the project agreement (Task 100-10). b. During the "before" and "after" periods of the study, the three new samplers will be operated every third day and the perrnanent samplers will be.operated on their normal schedule (every sixth day). The three new samplers will be operated in phase with the two permanent samplers so that all five samplers will be operated every sixth day. �uring the street sweeping demonstration, all five saroplers will be operated every other day. The 41DNR will be responsible for all operations of the two permanent samplers. The University will be responsible for setting up, maintenance, and calibration of the samplers, ' for conditioning the filters and weighinq them before and after the TSP samples are collected, and for determining the TSP concentrations, as outlined in the project aqreement (Task 100-20). c. Laboratory analysis of the filters used in the samplers will be conducted as outlined in the project agreement (Task 200-20). d. The University will provide data analysis and evaluation of the demonstration project to the City, as outlined in the project agreement (Task 300-30). e. The University will submit a report on the data analysis and evaluation of the demonstration project to,the City; as outlined in the project agreement (Task 400). IV. As outlined in the grant award froin the W�NR to the City of Oshkosh, the DNR will: a. supply the University with tiie high-volume samplers and glass for the study b. assist in settin9 up the high-volume samplers c. provide ongoing quality assurance for the TSP data collected d. provide major site repairs or instrument maintenance costs fiber filters during the study ,,,�e�d�� �.y h�JICC1uCI1L L . !�,J-0 & City of Oshkosh , ��� V. Bud9et - The City of Oshkosh shall provide funding to the University of G�lisconsin-Oshkosh on a cost-reimbursable basis to meet project objectives as follows: Task Number Task Personnel Equipment 100-20 Monitoring Site Operation $ 8486 $ 500 (travel) (including calibration, main- tenance, and data quality assurance) 200-10 200-20 300-30 400 Selection of filters for Laboratory Analysis Laboratory Analysis of Filters Data Analysis and Evaluation of Demonstration Project Report Preparation TOTAL 500 5I67 1000 500 $15653 450 $ 950 VI. Invoices - Expenditures incurred in carrying out the projeet shall be itemized and billed in triplicate on a calendar quarterly basis to the City of Oshkosh, ATTN: Each invoice must identify the project title_ Expenditures shall be itemized so as to reflect the expenditure category as outlined in the Budget above. The final quarterly payment will be provided only after all data, samples, and reports are submitted and approved by the City of Oshkosh. The final invoice must be submitted within 60 days of the end of the quarter. VII. Quality control assurance will be provided by the University of lVisconsin-Oshkosh to EPA specifics. ° VIII. Amendments or cancellation - Any amendments to/or cancellations of this agreement shall be negotiated between the University of tdisconsin-Oshkosh Project Director and the City of Oshkosh Project Director and must be in writing. IX. Project Officials - The Project Director for the University of Wisconsin-Oshkosh shall be Professor James I. Hoffman, Associate Dea�, College of Letters & Science. Each person signing this agreement represents that he or she is authorized to sign the agreer�ent and to bind his or her principal. -'�teragency Ayreement ` -3- ' � UW-0 & City of Oslikosh � BOAR� OF REGENTS OF THE UNIVERSITY OF 41ISCONSIN SYSTEM, UNIVERSITY OF WISCONSIN-OSHKOSH � �� g q'.i.^� Ja s I. Hoffman, Pr ,7ect Director �J �� � ���-�� �,� :�- H. D. Balliett, Rssistant Chancellor for Administrative Programs & Services J4fj�.sc�G .;22 / � d'tJ —� Date CITY OF OSHKOSH Date �CC�G3Q'���� o0f`'�`ID�G�JCL /!t`i1'�'�`,�J �Os3�^ 't�J�'►J'�`�l oare: ro: From: Subject: April 29, 1980 Paul Koziar - AIR/3 Dan Schranmi - LP1D Eric hlosher �jt,�c C- ,YI �'�n''t Proposed Oshkosh Street S�veeping Program STATE OF WISCONSIN �i Fr�e /te/: 4510 �, � :; _ -..J � " F� - - 'J ff�'riY tl J ��jv^'U :.. ; �E+'(1?�Tt,%iEPdT n' �v���ir9Uis�1?�i, r�1,'r; This memo presents the street sweeping program to be conducted this summer by the City of Oshkosh as part of the Oshkosh street sweeping demonstration study. This proposed street st��eeping program is based upon specific information colTected in Oshkosh as well as published reports of other street sweeping studies. The information collected in Oshkosh includes an inventory of unpaved parking lots, average daily traffic volumes on city streets, and the results of an informal survey done to determine the condition of the streets in the nonattainment area (curbed or uncurbed, paved or unpaved shoulders, dirty or• clean, etc). The reports of other street sweepin9 studies aiere published in a document entitled Control of Reentrained Dust From Paved Streets by Kenneth Axetell and Joan �ublicatto--` n No.—EPA-907%9-77-07, U.S. EPA, August 1977. Ideally, it is desirabTe to choose streets f heaviest dust loadings and relativeYy large Oshkosh nonattainment area, the streets with tend to have relatively low traffic vo]umes, of traffic are relatively clean. Both types the proposed street sweeping program. or sweepin9 ir3:ich have the traffic voluc:�s. Irr the the heaviest dust loadings while the streets with lots of streets are included in The attached map shows the streets selected for sweeping. 4lisconsin/Ohio Street, Jackson/Oregon Street, P"ain Street, and Ninth Avenue were chosen for s���eeping primarily because they are arterials u�ith heavy traffic volue�es. An area encompassing much of the centrai business district and nearby industrial areas t�ras also delineated for svreeping. Al1 streets within that area �aill be swept as part of the study program. The area includes most of the heavily travelled and dusty streets in the nonattain- ment area. All of the streets to be swept are located in the nonattainment area except for the small area on the university campus 4ihich v�as chosen for s�•ieeping because of the large unpaved parking lots located there. All of the s*_reets selected for s4veeping will be swept by the city's broom sweepers every Nonday, l{lednesday and Friday from June 16 through September 16, 1930. The tota,l lenyth of streets to be swept is 14.7 miles and they will be swept forty times during the study period. At the city's estimated labor cost of �,5.50 per mile, the labor cost of the entire street sweeping period will be $3234. Since the city normally ADJS T0: Paul Koziar R Dan Schramin - April 29, 19i30 ?, '� � � sweeps those streets once per week, the labor cost to the city for the extra sweeping �vill be two thirds of the $3234 or �2156. At a street sweeping rate of about four miles per hour, it will take the city about ' eleven hours per �aeek to svaeep the selected streets. That is about 7 1/2 hours more per tiaeek than they would normally spend sweeping those streets. 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