[{"data":1,"prerenderedAt":-1},["ShallowReactive",2],{"detail-sidebar-cat-1-en-105":3,"doc-seo-191832-105":53,"doc-detail-191832-en":118},{"code":4,"msg":5,"data":6},0,"success",[7,14,19,24,29,34,39,44,49],{"id":8,"doc_module":9,"doc_module_name":10,"category_name":11,"show_sort_weight":12,"slug":13},11,1,"Template","Presentations",90,"presentations",{"id":15,"doc_module":9,"doc_module_name":10,"category_name":16,"show_sort_weight":17,"slug":18},12,"Resumes",80,"resumes",{"id":20,"doc_module":9,"doc_module_name":10,"category_name":21,"show_sort_weight":22,"slug":23},14,"Invoices",70,"invoices",{"id":25,"doc_module":9,"doc_module_name":10,"category_name":26,"show_sort_weight":27,"slug":28},15,"Posters",60,"posters",{"id":30,"doc_module":9,"doc_module_name":10,"category_name":31,"show_sort_weight":32,"slug":33},16,"Social Media",50,"social-media",{"id":35,"doc_module":9,"doc_module_name":10,"category_name":36,"show_sort_weight":37,"slug":38},17,"Forms",40,"forms",{"id":40,"doc_module":9,"doc_module_name":10,"category_name":41,"show_sort_weight":42,"slug":43},18,"Letters",30,"letters",{"id":45,"doc_module":9,"doc_module_name":10,"category_name":46,"show_sort_weight":47,"slug":48},21,"Paper Templates",5,"papers-templates",{"id":50,"doc_module":9,"doc_module_name":10,"category_name":51,"show_sort_weight":4,"slug":52},158,"General","general-158",{"code":4,"msg":54,"data":55},"ok",{"site_id":56,"language":57,"slug":58,"title":59,"keywords":60,"description":61,"schema_data":62,"social_meta":111,"head_meta":113,"extra_data":115,"updated_unix":117},105,"en","2021-24202-ghgs-and-vocs-performance-standards-for-affected-sources","2021-24202 - GHGs and VOCs Performance Standards for Affected Sources","","Draft regulatory performance requirements outline proposed BSER and corresponding GHG and VOC standards for multiple affected source categories, including fugitive emissions from well sites at different baseline methane thresholds, compressor stations, Alaska North Slope sources, storage vessels with VOC PTE thresholds, pneumatic controllers, and well liquids unloading. The document specifies monitoring and repair frequencies using OGI, identifies optional EPA Method 21 screening with a defined leak threshold, and sets repair timelines, with additional controls such as capture-and-route to control devices and use of zero-emissions controllers.",{"@graph":63,"@context":110},[64,80,101],{"@type":65,"itemListElement":66},"BreadcrumbList",[67,71,74,77],{"item":68,"name":69,"@type":70,"position":9},"https://docshare.wps.com","Home","ListItem",{"item":72,"name":10,"@type":70,"position":73},"https://docshare.wps.com/template/",2,{"item":75,"name":36,"@type":70,"position":76},"https://docshare.wps.com/template/forms/",3,{"item":78,"name":59,"@type":70,"position":79},"https://docshare.wps.com/template/2021-24202-ghgs-and-vocs-performance-standards-for-affected-sources/191832/",4,{"url":78,"name":59,"@type":81,"image":82,"author":87,"headline":59,"publisher":90,"fileFormat":93,"inLanguage":57,"description":61,"dateModified":94,"datePublished":95,"encodingFormat":93,"isAccessibleForFree":96,"interactionStatistic":97},"DigitalDocument",{"url":83,"@type":84,"width":85,"height":86},"https://docshare.wps.com/thumbnails/2021-24202-ghgs-and-vocs-performance-standards-for-affected-sources/191832.png","ImageObject",442,249,{"name":88,"@type":89},"Logic","Person",{"url":68,"name":91,"@type":92},"DocShare","Organization","application/pdf","2026-09-28","2026-09-03",true,{"@type":98,"interactionType":99,"userInteractionCount":47},"InteractionCounter",{"@type":100},"ViewAction",{"@type":102,"mainEntity":103},"FAQPage",[104],{"name":105,"@type":106,"acceptedAnswer":107},"What emission control or repair actions are proposed beyond monitoring?","Question",{"text":108,"@type":109},"The requirements include capture and routing of emissions to control devices or processes, installation/use of low-bleed or zero-emissions pneumatic controllers, and replacing compressor rod packing based on measured leak rates or routing emissions to a process. For liquids unloading, it calls for minimizing or eliminating venting using non-venting techniques or best management practices.","Answer","https://schema.org",{"og:url":78,"og:type":112,"og:title":59,"og:site_name":91,"og:description":61},"article",{"robots":114,"canonical":78},"index,follow",{"doc_id":116,"site_id":56},191832,1790082974,{"code":4,"msg":5,"data":119},{"doc_id":116,"user_id":120,"nickname":88,"user_avatar":121,"doc_module":9,"category_id":35,"category_name":36,"doc_title":59,"doc_description":61,"doc_content":122,"file_id":123,"file_url":124,"file_type":125,"file_size":126,"view_count":47,"is_deleted":4,"is_public":9,"is_downloadable":9,"audit_status":9,"page_count":127,"language":128,"language_code":57,"site_id":56,"html_lang":57,"table_of_contents":129,"faqs":130,"seo_title":131,"seo_description":61,"update_tm":132,"read_time":133},1099513958762,"https://ap-avatar.wpscdn.com/avatar/1000023916a998db790?x-image-process=image/resize,m_fixed,w_180,h_180&k=1784791008015729253","| Subpart | Source type | Applicable dates |\n| --- | --- | --- |\n| 40 CFR part 60, subpart OOOO ........................\u003Cbr>40 CFR part 60, subpart OOOOa ......................\u003Cbr>40 CFR part 60, subpart OOOOb ......................\u003Cbr>40 CFR part 60, subpart OOOOc ...................... | New, modified, or reconstructed sources  \u003Cbr>New, modified, or reconstructed sources  \u003Cbr>New, modified, or reconstructed sources   Existing sources ............................................... | After August 23, 2011 and on or before September 18, 2015.\u003Cbr>After September 18, 2015 and on or before November 15, 2021.\u003Cbr>After November 15, 2021.\u003Cbr>On or before November 15, 2021. |\n\n\n| Affected source | Proposed BSER | Proposed standards of performance for GHGs and\u003Cbr>VOCs |\n| --- | --- | --- |\n| Fugitive Emissions: Well Sites with Baseline Emissions >0 to \u003C3 tpy 1 Methane.\u003Cbr>Fugitive Emissions: Well Sites ≥3 tpy Methane.\u003Cbr>(Co-proposal) Fugitive Emissions: Well Sites with Baseline Emissions ≥3 to \u003C8 tpy Methane. | Demonstrate actual site emissions are reflected in calculation.\u003Cbr>Monitoring and repair based on quarterly monitoring using OGI 2.\u003Cbr>Monitoring and repair based on semiannual monitoring using OGI. | Perform survey to verify that actual site emissions are reflected in calculation.\u003Cbr>Quarterly OGI monitoring following appendix K. (Optional quarterly EPA Method 21 monitoring with 500 ppm defined as a leak) .\u003Cbr>First attempt at repair within 30 days of finding fugitive emissions. Final repair within 30 days of first attempt.\u003Cbr>Semiannual OGI monitoring following appendix K. (Optional semiannual EPA Method 21 monitoring with 500 ppm defined as a leak) .\u003Cbr>First attempt at repair within 30 days of finding fugitive emissions. Final repair within 30 days of first attempt. |\n\n\n| Affected source | Proposed BSER | Proposed standards of performance for GHGs and\u003Cbr>VOCs |\n| --- | --- | --- |\n| (Co-proposal) Fugitive Emissions: Well Sites with Baseline Emissions ≥8 tpy Methane.\u003Cbr>Fugitive Emissions: Compressor Stations\u003Cbr>Fugitive Emissions: Well Sites and Compressor Stations on Alaska North Slope.\u003Cbr>Fugitive Emissions: Well Sites and Compressor Stations.\u003Cbr>Storage Vessels: A Single Storage Vessel or Tank Battery with PTE 4 of 6 tpy or More of VOC.\u003Cbr>Pneumatic Controllers: Natural Gas Driven that Vent to the Atmosphere.\u003Cbr>Pneumatic Controllers: Alaska (at sites where onsite power is not available—continuous bleed natural gas driven) .\u003Cbr>Pneumatic Controllers: Alaska (at sites where onsite power is not available—intermittent natural gas driven) .\u003Cbr>Well Liquids Unloading ...............................\u003Cbr>Wet Seal Centrifugal Compressors (except for those located at single well sites) .\u003Cbr>Reciprocating Compressors (except for those located at single well sites) . | Monitoring and repair based on quarterly monitoring using OGI.\u003Cbr>Monitoring and repair based on quarterly monitoring using OGI.\u003Cbr>Monitoring and repair based on annual monitoring using OGI.\u003Cbr>(Optional) Screening, monitoring, and repair based on bimonthly screening using an advanced measurement technology and annual monitoring using OGI.\u003Cbr>Capture and route to a control device  \u003Cbr>Use of zero-emissions controllers ............\u003Cbr>Installation of low-bleed pneumatic controllers.\u003Cbr>Monitor and repair through fugitive emissions program.\u003Cbr>Perform liquids unloading with zero methane or VOC emissions. If this is not feasible for safety or technical reasons, employ best management practices to minimize venting.\u003Cbr>Capture and route emissions from the wet seal fluid degassing system to a control device or to a process.\u003Cbr>Replace the reciprocating compressor rod packing based on annual monitoring (when measured leak rate exceeds 2 scfm 7 ) or route emissions to a process. | Quarterly OGI monitoring following appendix K. (Optional quarterly EPA Method 21 monitoring with 500 ppm 3 defined as a leak) .\u003Cbr>First attempt at repair within 30 days of finding fugitive emissi","cbCaiuQOd0eJtbKT","https://ap.wps.com/l/cbCaiuQOd0eJtbKT","pdf",1828263,154,"English","# Proposed BSER and Affected Sources\n## Affected source categories\n## Monitoring and repair standards\n## Optional EPA Method 21 and leak definition\n## Repair timelines and emission controls","[{\"question\":\"What emission control or repair actions are proposed beyond monitoring?\",\"answer\":\"The requirements include capture and routing of emissions to control devices or processes, installation/use of low-bleed or zero-emissions pneumatic controllers, and replacing compressor rod packing based on measured leak rates or routing emissions to a process. For liquids unloading, it calls for minimizing or eliminating venting using non-venting techniques or best management practices.\"}]","2021-24202 - GHGs and VOCs Performance Standards for Affected Sources | PDF",1788411068,54]