A Practical Guide for Developers, Operators, and Consultants
Federal & State Regulatory Framework | Compliance Pathways | Best Practices
Virginia has emerged as one of the world’s premier data center markets, with unprecedented development concentrated in Northern Virginia’s “Data Center Alley” in Loudoun, Prince William, and Fairfax counties, which is touted as the largest data center market in the world. This rapid growth has placed air permitting squarely in the critical path of project development. Understanding federal and state air quality requirements, and navigating them strategically, is essential for developers, operators, and their consultants.
This article provides a comprehensive overview of the air permitting framework applicable to data centers in Virginia, from foundational federal law through state-specific requirements and practical guidance.
For operators, the question is no longer limited to whether methane emissions are being managed. The question is whether emissions performance can be supported with data that is consistent, traceable, and ready for review.

Federal Air Quality Law: The Regulatory Foundation
The Clean Air Act (CAA) and Its Amendments
The Clean Air Act (CAA), first enacted in 1963 and substantially amended in 1970, 1977, and 1990, establishes the overarching federal framework for air quality regulation in the United States. Several of the CAA’s major structural elements are directly relevant to data center permitting.
The 1970 amendments directed the U.S. Environmental Protection Agency (EPA) to establish the National Ambient Air Quality Standards (NAAQS), which are health- and welfare-based thresholds for criteria pollutants including ozone (O3), particulate matter (PM), carbon monoxide (CO), sulfur dioxide (SO₂), nitrogen dioxide (NO₂), and lead (Pb). States must demonstrate attainment with NAAQS through enforceable State Implementation Plans (SIPs).
The CAA establishes two parallel pre-construction permitting programs based on attainment status:
- In areas that meet NAAQS, the Prevention of Significant Deterioration (PSD) program requires new major stationary sources to undergo pre-construction review, apply Best Available Control Technology (BACT), and conduct air quality modeling to demonstrate that air quality will not deteriorate significantly.
- In areas that do not meet NAAQS, Nonattainment New Source Review (NNSR) imposes more stringent requirements, including the application of Lowest Achievable Emission Rate (LAER) technology and the procurement of emissions offsets to compensate for new pollution.
Title V of the Clean Air Act Amendments of 1990 (CAAA of 1990) created a comprehensive federal operating permit program for major stationary sources. Title V permits consolidate all applicable air quality requirements into a single, federally enforceable document subject to EPA oversight and enhanced public participation.
Separately, the CAA authorizes EPA to establish New Source Performance Standards (NSPS), which are technology-based emission limits for new, modified, and reconstructed stationary sources by category, and National Emission Standards for Hazardous Air Pollutants (NESHAP) governing toxic substances such as benzene, formaldehyde, and mercury at the source-category level.
Key Federal Standards Applicable to Data Center Equipment
Air permitting for data centers is primarily driven by the engines and turbines used for backup power and/or onsite power generation, and several federal standards apply directly to this equipment.
Stationary Engine Standards (NSPS)
NSPS Subpart IIII, Standards of Performance for Stationary Compression Ignition Internal Combustion Engines, governs diesel-fueled reciprocating engines, setting emission limits for NOx, CO, hydrocarbons (HC), and particulate matter (PM) based on manufacture date and engine displacement.
NSPS Subpart JJJJ, Standards of Performance for Stationary Spark Ignition Internal Combustion Engines, covers natural gas-fueled reciprocating engines, with emission limits for NOx, CO, VOC, and formaldehyde.
Turbine Standards (NSPS)
Natural gas-fired stationary combustion turbines are regulated under NSPS Subpart KKKK (and predecessor Subpart GG), which establish NOx and SO₂ standards for new and modified units. On January 15, 2026, NSPS Subpart KKKKa provides updated performance standards reflecting more current emission control technologies for new turbines (new being after December 13, 2024).
NESHAP Standards for Engines
NESHAP Subpart ZZZZ, National Emission Standards for Hazardous Air Pollutants for Stationary Reciprocating Internal Combustion Engines (RICE), applies to both compression ignition and spark ignition RICE units at major and area sources of HAPs. It establishes work practice standards (such as oil change intervals and catalyst inspections) and, for certain units, numerical emission limits for HAPs including CO and formaldehyde.
Federal Construction Permitting: New Source Review
Overview of the NSR Framework
Before a major new stationary source can be constructed, or an existing source can undergo a major modification, it must obtain a pre-construction permit under the New Source Review (NSR) program. Which NSR track applies depends on the attainment status of the area where the source will be located.
- In attainment areas, major sources and major modifications that trigger PSD thresholds must obtain a PSD construction permit. This involves a lengthy review process including air quality modeling, a BACT analysis, public notice and comment, and potentially additional control requirements.
- In nonattainment areas, facilities meeting NNSR thresholds face an even more burdensome process: LAER analysis, which is more stringent than BACT; emissions offsets equal to or greater than new emissions, sometimes at a ratio greater than 1:1; and extensive public participation.
Both programs consider “project” emissions, which may encompass the entire facility or a defined subset, depending on how the project is characterized under applicable regulations.
Key Concept: What Is a ``Project``?
The definition of “project” under NSR is complex and highly consequential. Under EPA’s rules, a project is generally the sum of all physical changes and changes in the method of operation at a stationary source that are part of a common design or plan.
Improper scoping of a project can result in either unanticipated NSR applicability or regulatory scrutiny after the fact.
Data center developers should work with experienced environmental counsel early to define project boundaries correctly.
Avoiding Major NSR: The Synthetic Minor Source Strategy
Because major NSR, particularly NNSR in nonattainment areas, can be extraordinarily time-consuming, costly, and operationally constraining, data center developers routinely seek to avoid triggering it.
The primary mechanism is to permit as a Synthetic Minor Source: a facility that would otherwise be a major source based on its physical potential to emit, but that accepts federally enforceable operating limits on hours of operation, fuel consumption, or both, to keep allowable emissions below major source thresholds. These limits are incorporated into a state-issued construction permit, making them legally binding and federally enforceable.
Careful engineering and permitting strategy are essential to this approach. Operating limits must be achievable given the facility’s real-world operational needs, including emergency response, maintenance testing, and operator training, while keeping emissions below applicable thresholds.
In Virginia, as discussed below, limiting generator operating hours is the standard method for maintaining synthetic minor status for data center backup generators.
State Air Quality Programs
Role of State Programs
While the CAA establishes the federal framework, implementation and enforcement are largely delegated to individual states through EPA-approved State Implementation Plans (SIPs).
Each state must maintain an air quality program that includes enforceable air pollution control regulations specifying emission limits, control requirements, and operational standards; air permitting programs that implement NSR at the state level and include key thresholds and exemptions that vary by state; and air compliance and enforcement programs covering inspection, monitoring, recordkeeping, reporting, and permit condition enforcement.
Federal construction permitting (NSR/PSD/NNSR) is typically administered at the state level by state environmental agencies, though EPA retains review authority, particularly for Title V facilities, and can object to permits that do not comply with federal requirements. This delegation means that state agencies are the primary point of contact for permit applications, and state-specific rules, guidance, and practice will govern the permitting process. For Title V facilities, EPA input should be anticipated and factored into project timelines.
State Construction vs. Operating Permits
It is important to distinguish between construction permits and operating permits, two distinct but related authorizations.
- Construction permits are required before construction or modification of emission sources and in NSR terms may be major (PSD or NNSR) or minor (state minor or synthetic minor). Some states require only registration of equipment; others require a full permit with technical review. States may also impose more stringent short-term requirements such as BACT analyses even for minor sources.
- Operating permits govern ongoing facility operations. At the federal level, Title V operating permits are required for major sources and consolidate all applicable emission requirements into a single document. At the state level, minor and synthetic minor sources may also be required to obtain state operating permits depending on the state’s program design. Even when a data center qualifies as a minor or synthetic minor source for construction permitting purposes, it may still be subject to federal operating permit requirements, a distinction that should be confirmed with the relevant state agency early in the project.
Emissions Sources at Data Centers
Primary Emission Sources
Air permitting for data centers is driven primarily by the trend towards onsite self-generation in addition to backup power generation systems installed to maintain uptime during grid outages.
- Diesel and natural gas backup generators, which are reciprocating engines regulated under NSPS Subpart IIII (for diesel) or NSPS Subpart JJJJ (for natural gas), as well as NESHAP Subpart ZZZZ, are the dominant source of regulated air emissions, producing NOx, CO, VOC, particulate matter, and hazardous air pollutants.
- Natural gas combustion turbines, used at some large facilities for prime or backup power, are subject to NSPS Subpart KKKK or KKKKa.
Beyond primary generation equipment, other emission sources must be inventoried in air permit applications. Some examples include:
- Fuel cells are an emerging technology for backup or primary power whose emission profiles vary by technology type. Emissions controls such as oxidation catalysts or selective catalytic reduction (SCR) systems may be required by permit or regulation.
- Evaporative cooling equipment (cooling towers) can be a source of particulate matter from mineral deposits in water drift and, under certain conditions, may raise concerns about Legionella.
- Diesel storage tanks are a source of VOC emissions through tank breathing, standing, and filling losses, and depending on tank size and throughput may be subject to emission standards or permit requirements of their own.
Early Permitting Considerations
Why Air Permitting Must Be Addressed Early
Air permitting is frequently underestimated as a project development constraint. In reality, a permitting strategy can directly influence fundamental project decisions – site selection, facility design, equipment choices, construction phasing, and ownership structure – making early engagement with the permitting process essential.
The location of the data center matters immediately: Site location is among the most consequential decisions in data center permitting and development. A site’s attainment status under the Clean Air Act — whether it meets National Ambient Air Quality Standards (NAAQS) for regulated pollutants — determines which permitting pathway applies and at what thresholds. For ozone nonattainment areas in particular, where both NOx and VOC emissions are implicated, the distinction between Prevention of Significant Deterioration (PSD) and Nonattainment New Source Review (NNSR) carries significant practical consequences: NNSR imposes stricter major source thresholds and additional offset requirements that can materially affect project feasibility, cost, and timeline.
Resource availability (e.g., fuel, water, and land) must be evaluated not just at the time of siting but across the project’s operational life, as constraints in any of these areas can threaten long-term viability.
The type of location can introduce additional complexity. Rural sites offer significant advantages in space, lower land costs, reduced public visibility, and typically fewer community opposition concerns; however, they require upfront infrastructure investment to establish grid connectivity and utilities or self-generation facilities. Urban sites, by contrast, benefit from existing infrastructure but present considerably greater challenges — including higher land costs, limited room for expansion, and heightened scrutiny from neighboring communities, regulators, and the public.
Facility location in or near environmental justice communities is an increasingly consequential factor in both regulatory review and community acceptance. For example, in 2026 Virginia approved a new law, HB1266, directing the Department of Environmental Quality (DEQ) to update its “Environmental Justice in the Permitting Process Guidance Memo”. It requires state agencies to consider the cumulative pollution impacts on historically marginalized communities before approving new industrial permits.
Finally, location type and resource availability factors may have implications for securing rights-of-way and surface use agreements.
Data center facility size: the number and capacity of generators required scales directly with IT load, and more generators mean more emissions and potentially a higher permit classification, depending in large part on where the facility is located.
Facility size is often a function of location characteristics. For example, urban sites present a strategic constraint beyond initial development: expansion is often limited by surrounding density, zoning boundaries, and land availability, meaning the footprint of the facility may ultimately be dictated by the location itself rather than operational need. Rural sites, by contrast, better preserve optionality – typically offering room to scale as demand grows.
Supply chain concerns and timing. Even once a site is selected and sized appropriately, infrastructure and equipment availability introduce a separate layer of risk. Supply chain constraints can significantly delay procurement of critical hardware, raising a practical question: by the time equipment is delivered and the facility is operational, will that location still align with the market conditions, power availability, and customer demand that made it attractive in the first place? Site selection and equipment lead times must therefore be evaluated in tandem, not in isolation.
Ownership structure and source aggregation deserve careful analysis at the outset. Whether multiple data center buildings, power generation facilities, or other emission sources will be treated as a single aggregated source depends on ownership, proximity, and operational relationships. Common ownership – even across nominally separate LLCs – can result in combined emissions that trigger major source status. In Virginia, VADEQ Guidance Document APG-204 addresses aggregation in detail and should be reviewed early. Finally, construction phasing can affect how project emissions are calculated and whether NSR applies to individual phases or the combined project.
Additional Permitting Considerations
How generators will be categorized, emergency versus non-emergency, significantly affects permissible operating hours and applicable regulatory standards. Emergency generators are subject to more favorable operating conditions but are limited in the total runtime, hence, they may not be dispatched for demand response or used to sell power to the grid in ways that would compromise their emergency designation. Data center customers often impose contractual uptime and reliability requirements that can drive generator operating hours into conflict with permit-imposed limits, a tension that must be resolved in the permitting strategy.
The need for add-on emission controls – oxidation catalysts, diesel particulate filters, selective catalytic reduction – must be evaluated both technically and financially. Controls may be required to achieve synthetic minor status or to comply with applicable standards, and their capital cost can be substantial.
The trend toward larger onsite power generation in response to utility grid limitations adds further complexity: gas turbines or fuel cells introduced as primary generation sources can bring additional emission inventories, potentially different ownership structures, and more intricate permitting scenarios.
Air dispersion modeling is required for PSD and major source construction permits and is increasingly expected for state major permits; it evaluates ground-level concentration impacts on nearby receptors and must demonstrate compliance with NAAQS and applicable increment standards.
The Three Strategic Pillars of Air Permitting
Air permitting strategy for data centers ultimately revolves around three interrelated considerations that must be balanced against one another:
- Regulatory burden: the difference between major source and synthetic minor permitting is enormous in terms of cost, time, operational restrictions, and ongoing compliance obligations, making qualification as a synthetic minor source the primary goal in most cases.
- Operational flexibility: permit conditions – particularly limits on operating hours or fuel consumption – directly constrain how and when generators can run, and insufficient flexibility can create real operational risk during extended outages or maintenance and testing cycles.
- Capital cost: emissions controls required to meet permit conditions or applicable standards represent a significant capital expenditure, and the cost-benefit tradeoff between control technologies and permitting strategies must be evaluated carefully.
Evolving Challenges
The air permitting landscape for data centers is evolving rapidly, driven by several converging forces.
New and evolving EPA and state rules continue to tighten emission standards and expand regulatory coverage.
Public opposition to data centers on grounds of noise, visual impact, water use, electricity rates, and air quality is growing in many markets, including Virginia, and community perception can affect permitting timelines and project feasibility.
Utility grid constraints are driving some data centers to pursue significantly larger onsite generation capacity, fundamentally changing the emissions profile and permitting complexity.
As development expands beyond established markets, developers and their consultants may encounter state and local agencies with limited experience processing data center air permit applications, introducing additional uncertainty into the process.
Virginia Air Permitting
Virginia’s Nonattainment Geography
Virginia’s air quality attainment status varies significantly by region and has direct implications for which permitting pathway applies and what major source thresholds govern.
Northern Virginia – Alexandria City, Arlington County, Fairfax City, Fairfax County, Falls Church City, Loudoun County, Manassas Park City, Manassas City, and Prince William County – is classified as a moderate nonattainment area for the 2015 8-hour ozone NAAQS. In this area, the major source thresholds for NNSR purposes are 100 tons per year (tpy) for both NOx and VOC.
Portions of Northern Virginia also fall within EPA’s designated Ozone Transport Region (OTR), which overlaps with the nonattainment area and imposes more stringent ozone precursor controls, including a reduced major source threshold of 50 tpy for VOC.
The remainder of Virginia is in attainment for ozone, where the higher PSD major source thresholds apply, typically 250 tpy for most source categories, or 100 tpy for sources in a listed category.
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Key Takeaway for Northern Virginia
NOx and CO tend to be the primary regulated emissions from data center generators, because they are associated with internal combustion of fossil fuels. Diesel gensets may have the additional concern of PM. Northern Virginia’s moderate nonattainment status for ozone, and the role of NOx as an ozone precursor, means that NOx emissions are subject to 100 tpy and that NNSR, rather than PSD, applies to major sources. Emissions offsets are scarce in Northern Virginia, making it difficult to avoid trigging NNSR. Even so, many operators may find that access to the world’s largest data center hub justifies the added compliance cost.
Note: Extreme, Severe, and Serious Nonattainment limits are 10 tpy, 25 tpy, and 50 tpy, respectively.
Main Air Permitting Pathways in Virginia
Virgina Department of Environmental Quality (VADEQ) administers four main permitting pathways for data centers, distinguished by the level of facility-wide emissions relative to applicable thresholds.
Synthetic Minor NSR. The preferred pathway for the vast majority of Virginia data centers. A facility accepts federally enforceable limits on generator operating hours (or fuel consumption) to keep potential emissions below major source thresholds. Permit applications are reviewed by VADEQ’s regional offices and do not require public comment in most cases, making this the fastest and least costly pathway.
State Major Source Permit. Required when facility-wide emissions exceed Title V operating permit thresholds but remain below major NSR thresholds. Applications are subject to air quality modeling and a mandatory public comment period, making the process longer and more expensive than the synthetic minor pathway. VADEQ requires air dispersion modeling because the permit goes to public notice, and applicants should expect a longer permitting timeline.
PSD Permit (Attainment Areas). Required for sources in attainment areas whose facility-wide emissions exceed one or more major source thresholds. PSD is a federal pre-construction permitting program administered by VADEQ with EPA oversight. The process requires a BACT analysis, air quality modeling, public notice and comment, and ongoing compliance monitoring and reporting. Permitting timelines of one to two years are typical.
Nonattainment NSR (NNSR). Required for sources in nonattainment areas, including Northern Virginia, whose facility-wide emissions exceed NNSR thresholds. In addition to LAER, which is more stringent than BACT, NNSR requires emissions offsets that are extremely scarce in Northern Virginia. The combination of process burden, cost, and offset availability creates significant project risk. Major sources triggering either PSD or NNSR are also required to obtain a Title V operating permit, which consolidates all permit conditions but subjects the facility to enhanced compliance oversight, reporting obligations, and substantially higher fees.
New Tier 4 Equivalent Engine Requirement
Effective July 1, 2026, VADEQ requires that air permit applications for data centers submitted on or after that date must specify the use of Tier 4 equivalent engines. New diesel engines must meet a NOx emission standard of 0.6 g/bhp-hr, consistent with EPA’s Tier 4 nonroad engine standards; compliance with Tier 4 standards is required, but add-on controls are not mandated if the engine can comply without them.
Applicants demonstrate compliance by comparing worst-case emissions factors against Tier 4 standards with a 1.25 scaling factor applied. New stack testing standards also apply under VADEQ Guidance APG-576 and HB-507 legislation; where the two conflict, the legislation governs.
The Tier 4 equivalent requirement does not apply to administrative or redundant generators, and fire pump and water pump engines are exempt as they are not engine-generator sets.
For projects seeking to obtain permits under prior standards before the July 1, 2026 effective date, applicants should submit as complete an application as possible and consider pulling permit filings forward. Importantly, permits expire if there is a gap of more than 18 months between obtaining the permit and commencing construction, unless an extension is granted by the state. Nonetheless, this a timeline that should be factored into project scheduling.
Emergency Generator Operating Limitations
Virginia’s regulatory treatment of emergency generators with respect to operating permits involves several nuanced requirements that differ meaningfully from federal rules and from other states’ approaches.
Virginia does not adopt the federal NSPS definition permitting up to 50 hours of non-emergency operation per year. Instead, VADEQ applies a stricter interpretation, and utility-curtailed operations are treated differently depending on the circumstances of the curtailment.
READ MORE: VADEQ Clarification #2025-01
Emergency generators may operate when primary utility power is disrupted. Under VADEQ’s September 2025 guidance, an unforeseeable grid outage with less than 14 days’ notice qualifies as an emergency, permitting operation of permitted equipment.
ISO-declared grid emergencies are subject to additional limitations under NSPS Subparts IIII and JJJJ as well as VADEQ’s own rules. Scheduled maintenance checks and readiness testing, whether monthly, quarterly, or annual planned runs, are permitted but count against the operating hour limits specified in the permit. Unscheduled maintenance, testing, and operator training are similarly subject to hour limits and tracked separately from scheduled testing.
READ MORE: VADEQ Issued Air Permits for Data Centers
For newer air permits, VADEQ imposes ozone season restrictions running from May 1 through September 30, from 7:00 AM to 5:00 PM. Except during an integration period immediately following startup, generators may not operate for planned, non-emergency reasons during this period without a waiver from VADEQ. Critically, operating hours or fuel consumption limits in the permit encompass all generator operations — emergency, non-emergency, maintenance, and testing — and must be managed accordingly.
Source Aggregation in Virginia
One of the most consequential and often misunderstood issues in Virginia data center air permitting is source aggregation — the regulatory practice of treating multiple nearby emission sources as a single stationary source for permitting purposes.
Per VADEQ guidance (Clarification #2025-02), sources with the same owner and the same business function located less than 0.25 miles from each other may be considered a single source. Sources less than 0.125 miles apart will generally be aggregated; those between 0.125 and 0.25 miles are evaluated case by case.
VADEQ follows ownership to the ultimate parent entity, meaning that different LLCs with a common ultimate owner will be treated as the same owner for aggregation purposes — a different LLC does not by itself establish separate ownership. The aggregation question is particularly acute for data centers with co-located or adjacent power generation facilities.
VADEQ has indicated that aggregation of a power generation facility with a nearby data center — even if the two are owned by nominally different entities — is likely when they have the same functional relationship. This has significant implications for campus-style developments and for data centers served by third-party power providers.
Local Governing Body Requirements and Environmental Justice
For greenfield data center sites, VADEQ requires that applicants submit site suitability and value forms to the relevant local governing body – the county or city in which the facility will be located. The locality must sign both forms before VADEQ will deem the application complete, making early engagement with local officials an important step in the permitting process.
Portable engines that meet the definition of nonroad engines – portable and on site for less than 12 months – are exempt from air permitting regardless of quantity or purpose, whether prime or backup generation. Because no air permit is required, ozone season restrictions do not apply to these units. However, public perception and community concerns about noise and air quality remain relevant considerations even for exempt equipment.
Environmental justice is an increasingly prominent regulatory consideration. Under HB 1266, VADEQ is developing guidance to evaluate cumulative environmental impacts on environmental justice communities, with a public information comment period expected in Summer 2026 and official public comment in Fall 2026. Final permitting guidance is required by December 31, 2026. HB 256 directs many localities to develop comprehensive plans and EJ strategies as well. Developers should track this evolving framework and anticipate that EJ considerations may affect permit review timelines and outcomes.
HB1266 Environmental Justice in Permitting Process Guidance Memo; DEQ to publish an updated version
Virginia Permitting Timelines, Costs, and Best Practices
Permitting Timelines
Virginia does not offer an expedited permitting option, making early application submission critical to meeting project construction schedules. Typical VADEQ processing times range from four to six months for a Synthetic Minor NSR permit, six to twelve months for a State Major permit combined with a Title V operating permit, and one to two years for Major NSR or PSD permits. These timelines assume a complete application; incomplete submissions will be held or returned pending additional information, extending the process further. Permit complexity directly affects preparation and review time. More complex permits demand more time for both preparation and review.
Permitting Costs
The table below summarizes applicable VADEQ permit fees. Fees increase annually by the Consumer Price Index (CPI) and are assessed per permit action rather than per piece of equipment — an arrangement that benefits large projects with many generators. Annual emissions fees, calculated based on actual regulated pollutant tonnage emitted, are separate from and in addition to the permit fees shown.
VAEQ Permitting Fees
| Permit Type | Initial Permit Fee | Amendment/Renewal | Typical Timeline |
|---|---|---|---|
| Synthetic Minor NSR | $4,240 | $1,413 | 4–6 months |
| State Major + Title V | $35,334 + $49,467 | $21,200 (Title V renewal) | 6–12 months |
| Major NSR / PSD | $89,041 + $49,467 | $14,133 (Major NSR) | 1–2 years |
The table reflects government filing fees only and excludes costs associated with permit planning, preparation, legal review, and related activities. Operators should plan accordingly — permit preparation takes time, and costs increase with permit complexity.
Best Practices for Permitting in Virginia
Engaging experienced air quality consultants and supporting environmental counsel where appropriate at the project inception stage is a high-value step a developer should consider. Air permitting strategy — including source aggregation analysis, project definition, synthetic minor operating limit design, and equipment selection — requires specialized expertise that is most effectively applied before fundamental project decisions are locked in.
Once a plan has been established, scheduling a pre-application meeting with VADEQ before submitting a permit application is strongly recommended. VADEQ staff are generally responsive, and these meetings can surface potential issues, clarify data and documentation requirements, and substantially reduce the risk of delays or requests for additional information after filing. VADEQ will issue an Initial Letter of Determination (ILOD) within 30 days of receiving a permit application, addressing outstanding questions and providing a formal completeness determination; a timely ILOD is an important early milestone that helps applicants understand what additional information is needed before substantive review begins.
Permit submittals are typically made via email to the regional air permit manager; the appropriate contact and submission format should be confirmed with VADEQ before filing. Progress on applications and previously issued permits can be tracked using VADEQ’s Virginia Permit Transparency (VPT) system and the Permitting Enhancement and Evaluation Platform (PEEP). VADEQ also maintains a dedicated data center air permitting page at https://www.deq.virginia.gov/news-info/shortcuts/permits/air/issued-air-permits-for-data-centers that provides useful reference information including issued permits.
Conclusion
Air permitting is a critical, often underestimated, element of data center development in Virginia. The regulatory framework — spanning federal CAA requirements, NSR, NSPS, NESHAP, Title V, and Virginia-specific rules administered by VADEQ — is complex and continues to evolve. The consequences of failing to navigate this framework correctly include project delays, significant additional cost, operational restrictions, and, in the most serious cases, project cancellation.
For the vast majority of Virginia data centers, the goal is to qualify as a Synthetic Minor Source by accepting federally enforceable operating limits — avoiding the time, cost, and operational constraints of major NSR. Achieving this outcome requires careful attention to project definition, source aggregation, equipment selection (particularly with the new Tier 4 equivalent requirement effective July 1, 2026), and operating limit design.
Early engagement with VADEQ, experienced environmental consultants, and legal counsel is the single most effective step a data center developer can take to ensure a smooth air permitting process. The regulatory landscape will continue to evolve — including with respect to environmental justice, emergency generator definitions, and emissions control requirements — making proactive, informed engagement with permitting authorities essential.
Disclaimer
This article is provided for general informational purposes only and does not constitute legal, engineering, or regulatory advice. Air permitting requirements are subject to change; readers should consult with qualified environmental counsel and consultants regarding their specific projects.
About the Author

Ángel E. Esparza, Ph.D., P.E., CESCO
VP of Regulatory, Sustainability & Technical Services
Ángel Esparza is Vice President of Regulatory, Sustainability, and Technical Services at Encino. He provides advisory and consulting services related to air quality initiatives, permitting, and emissions monitoring technology and systems. His more than 15 years of experience include securing funding and leading R&D initiatives in methane detection and emissions reduction as Principal Investigator; building air quality compliance programs across federal, state, and international regulations; driving environmental performance and sustainability strategy, including carbon accounting and ISO 14001:2015-certified EMS implementation; and serving as an industry voice through speaking engagements, published technical papers, and executive advisory on regulatory and business development matters.
Prior to joining Encino, Ángel held roles at Southwest Research Institute, Kinder Morgan, and GHGSat, in addition to teaching as an adjunct professor at several higher education institutions — reflecting his enduring passion for teaching and research. His wide-ranging experience spanning scientific and engineering research, technology, and the oil and gas industry gives him an integrated, multidisciplinary perspective.
Ángel has a doctorate in Environmental Science and Engineering and Master of Science and Bachelor of Science degrees in both Mechanical and Industrial Engineering. He is a licensed Professional Engineer in the State of Texas.









