
Introduction
Americans spend approximately 90% of their time indoors, yet indoor pollutant concentrations can be two to five times higher than outdoor levels. Despite these striking statistics, no comprehensive federal law governs indoor air quality in non-occupational settings.
While the Clean Air Act and EPA's National Ambient Air Quality Standards (NAAQS) regulate outdoor air, indoor environments remain largely unregulated. Building managers, safety professionals, and monitoring teams are left navigating a complex patchwork of voluntary standards, occupational limits, and certification benchmarks.
Exposure to indoor air pollutants is linked to respiratory illness, cardiovascular disease, cognitive impairment, and in severe cases, cancer. This guide cuts through that complexity, covering:
- Which pollutants to monitor and why they matter
- What concentration thresholds trigger action
- How to maintain sensor accuracy through proper calibration
- When to escalate to professional intervention
TLDR: Key Takeaways
- No single federal agency governs IAQ; standards are set by ASHRAE, EPA, OSHA, WHO, and voluntary programs like WELL and LEED
- Monitor six primary pollutants: CO2, PM2.5, VOCs, carbon monoxide, radon, and humidity
- ASHRAE 62.1 is the primary US commercial building ventilation standard
- Sensor accuracy requires annual calibration with NIST-traceable reference gases
- Improve IAQ through source control, increased ventilation, and MERV 13+ filtration
Why Indoor Air Quality Standards Matter
The Health Stakes
Indoor air pollutant exposure drives serious health outcomes. PM2.5 is strongly associated with cardiovascular and respiratory mortality, while elevated CO2 directly impairs cognitive function and decision-making. Vulnerable populations—children, elderly individuals, and those with existing respiratory conditions—face elevated risk.
The Regulatory Gap
Unlike outdoor air, which the EPA regulates through the Clean Air Act and NAAQS, indoor air quality has no equivalent comprehensive federal framework. State and local governments set their own standards, while voluntary guidelines from ASHRAE, WHO, and green building certifications like WELL step in to provide guidance.
Recognized Consequences of Poor IAQ
Poor IAQ produces three recognized clinical outcomes:
- Sick Building Syndrome (SBS): Occupants experience acute symptoms—headaches, eye irritation, fatigue—that improve after leaving the building, with no single identifiable cause
- Building Related Illness (BRI): A clinically diagnosable condition, such as Legionnaire's disease, traced directly to specific airborne contaminants in the building
- Multiple Chemical Sensitivity (MCS): Recurring symptoms—headaches, weakness, respiratory distress—triggered by low-level chemical exposures that most people tolerate without reaction

Key Indoor Air Pollutants and Their Threshold Limits
IAQ guidelines use two types of limits: health-based thresholds (lowest level where harm occurs) and feasibility-based limits (achievable safe exposure levels). Thresholds vary by pollutant and issuing body.
Particulate Matter (PM2.5 and PM10)
PM2.5 particles (smaller than 2.5 microns) penetrate deep into lung tissue, causing cardiovascular inflammation and measurable cognitive impairment. The EPA's 2024 annual standard is 9.0 µg/m³, while WELL v2 sets an indoor threshold of less than 15 µg/m³.
Health Canada has determined there is no fully safe indoor level of PM2.5, recommending source reduction practices rather than relying solely on threshold compliance.
For PM10 (particles smaller than 10 microns), ASHRAE Standard 62 sets a maximum 24-hour exposure of 0.15 mg/m³ (150 µg/m³). Inhalable particles (PM10) affect upper respiratory systems; respirable particles (PM2.5) reach deep lung tissue.
Carbon Dioxide (CO2)
CO2 is an indicator of ventilation adequacy rather than a direct toxin at typical indoor concentrations. ASHRAE 62.1 targets indoor CO2 no more than 700 ppm above outdoor ambient (typically 300–400 ppm outdoors). Japan's standard sets a 1,000 ppm absolute limit.
Levels above 1,000 ppm are associated with measurable cognitive decline and drowsiness, making CO2 monitoring particularly important in offices, classrooms, and conference rooms.
Volatile Organic Compounds (VOCs)
VOCs are carbon-based chemicals that off-gas at room temperature from a range of common sources, including:
- Building materials, flooring, and carpeting
- Furniture, paints, and adhesives
- Cleaning products and personal care items
WELL v2 sets a Total VOC (TVOC) limit of 500 µg/m³ and a formaldehyde-specific limit of 27 ppb.
New furniture and building materials are common culprits. VOC emissions follow a multi-exponential decay trend, with concentrations of formaldehyde, benzene, and toluene highest in the first weeks to months after installation. VOC spikes following renovations or new furnishings are a primary cause of WELL audit failures.
Carbon Monoxide (CO) and Other Combustion Gases
Carbon monoxide is a colorless, odorless gas that binds to hemoglobin and can be fatal at high concentrations. Key thresholds vary significantly:
- EPA: 9 ppm over 8 hours
- OSHA: 50 ppm TWA (time-weighted average)
- WHO: 26 ppm (1-hour guideline)

OSHA acknowledges many of its PELs are outdated, having been adopted in 1970 without revision. Practitioners should cross-reference NIOSH Recommended Exposure Limits (RELs) and ACGIH Threshold Limit Values (TLVs) for more current guidance.
Radon and Humidity
Radon is the second leading cause of lung cancer in the US. The EPA's indoor action level is 4 pCi/L, a threshold also adopted by WELL v2 Feature A04 testing requirements.
Relative humidity should be maintained between 30–60% per ASHRAE Standard 55. Levels above 60% trigger condensation and mold growth, while levels below 30% cause respiratory irritation and increased susceptibility to infection.
Major IAQ Standards and Regulatory Frameworks
No single federal indoor air quality law exists in the US. Compliance depends on identifying which framework applies to your building type, occupancy, or certification goal—and these frameworks are not mutually exclusive.
ASHRAE Standards 62.1, 62.2, and 55
ASHRAE 62.1 applies to commercial buildings, while 62.2 applies to residential buildings. These are the primary US ventilation standards, widely adopted into building codes through model codes like the International Mechanical Code.
ASHRAE 62.1 sets minimum outdoor air supply rates by space type and occupancy density. The 2025 edition refines humidity control requirements and adds emergency ventilation controls to address atypical operating modes like wildfire smoke events.
Standard 55 covers thermal comfort separately, addressing temperature, humidity, thermal radiation, and air speed for occupant satisfaction.
EPA and OSHA Standards
Understanding the EPA and OSHA roles side by side clarifies what is enforceable versus advisory:
- EPA: Sets NAAQS for six outdoor criteria pollutants, maintains an indoor radon guideline at 4 pCi/L, and publishes the Clean Air in Buildings Challenge—but stops short of enforceable indoor limits for most pollutants
- OSHA: Permissible Exposure Limits (PELs) cover 500+ substances in occupational settings, though OSHA explicitly acknowledges most PELs are inadequate; they were adopted in 1970 without updates
- NIOSH/ACGIH: Practitioners should reference these for more current occupational exposure thresholds
WELL v2, LEED v4.1, and Voluntary Certification Programs
WELL v2 is the most comprehensive voluntary IAQ certification, requiring continuous monitoring for CO2, PM2.5, TVOC, and humidity. WELL Platinum projects must provide real-time dashboard access to occupants.
LEED v4.1 EQ credits reward post-construction flush-out or air testing, supplying 14,000 cubic feet of outdoor air per square foot before occupancy. LEED Operations + Maintenance credits require ongoing ventilation monitoring.
For residential construction specifically, EPA's Indoor airPLUS program provides design and construction requirements targeting the same IAQ protection goals.
WHO Guidelines and International Context
Beyond US frameworks, international benchmarks shape how practitioners set targets. WHO's 2021 Global Air Quality Guidelines lowered the recommended annual PM2.5 level to 5 µg/m³—well below current US standards. While voluntary, WHO guidelines influence national policy globally and serve as a reference baseline for practitioners.
Health Canada's residential IAQ guidelines are another useful reference, offering specific exposure limits for formaldehyde and other VOCs. In the absence of US federal limits for these compounds, Canadian thresholds serve as a practical benchmark for monitoring programs.
How to Monitor Indoor Air Quality
Effective IAQ monitoring begins with identifying which pollutants are most likely present based on building type, occupancy, and known sources—then selecting appropriate sensor technology.
Sensor Types and What They Measure
Primary sensor technologies:
- NDIR (Non-Dispersive Infrared): Most accurate CO2 measurement for commercial use
- Laser particle counters: PM2.5 and PM10 detection
- MOX (Metal Oxide Semiconductor) or PID (Photoionization Detector): VOC detection
- Electrochemical sensors: Carbon monoxide measurement
- Capacitive sensors: Humidity and temperature monitoring

Sensors must be positioned in the breathing zone (3–6 feet above floor), away from direct sources (cooking equipment, printers) and HVAC drafts. Placement directly affects data quality and compliance documentation validity.
Sensor Calibration and Accuracy: The Critical Link
IAQ sensors drift over time. NDIR CO2 sensors and MOX VOC sensors both experience measurable drift within 12–18 months, meaning an uncalibrated sensor reporting "within threshold" produces scientifically invalid compliance data.
Annual calibration against certified reference gas standards is required for ASHRAE 62.1 and WELL v2 compliance evidence. NIST-traceable calibration gas standards are essential for verifying and maintaining sensor accuracy across CO, CO2, VOC, and other IAQ monitoring applications. Suppliers such as SpecGas Inc. produce NIST-traceable CO, CO2, and formaldehyde calibration mixtures at PPM and PPB levels in disposable field-ready cylinders, designed specifically for annual IAQ sensor calibration workflows.
With calibrated sensors in place, the next decision is how frequently to collect data—and that depends on your building type, certification goals, and budget.
Continuous vs. Periodic Monitoring and Investigation Protocol
Continuous monitoring (preferred): IoT-based sensors provide real-time data for commercial buildings pursuing WELL/LEED certification or managing multi-zone HVAC systems. Continuous data reveals patterns, enables demand-controlled ventilation, and documents compliance.
Periodic spot-check investigations: Portable instruments work for smaller facilities or investigating specific complaints. They do miss temporal variations, though, and may not capture peak exposure events.
Basic IAQ investigation protocol:
- Gather background building data (HVAC specs, occupancy patterns, recent renovations)
- Interview occupants about symptoms, timing, and location patterns
- Take measurements at multiple locations and heights throughout affected zones
- Analyze data for patterns, anomalies, and threshold exceedances
- Document findings with corrective action plans and follow-up schedules

How to Improve Indoor Air Quality When Thresholds Are Exceeded
The Three Foundational Strategies
The EPA and ASHRAE recognize three primary strategies to reduce indoor air pollutants:
1. Source ControlIdentify and remove or isolate pollutant sources:
- Replace high-VOC materials with low-emission alternatives
- Properly maintain combustion equipment
- Remediate moisture-damaged surfaces before mold develops
- Relocate printers and copiers to dedicated ventilated spaces
2. VentilationIncrease outdoor air supply:
- Adjust outside air damper positions to increase fresh air intake
- Implement demand-controlled ventilation using CO2 sensor feedback
- Run HVAC systems before and after occupancy to flush spaces
- Open windows strategically when outdoor air quality permits
3. Supplemental Filtration and Air CleaningASHRAE recommends MERV 13 filters as the minimum for commercial buildings post-pandemic, with MERV 14 or HEPA filtration where higher particle removal efficiency is required.
Can an air purifier remove VOCs? Activated carbon air purifiers can reduce certain VOC concentrations, but effectiveness varies considerably by compound and device type. Activated carbon has finite capacity, requires regular replacement to avoid breakthrough, and performs poorly against low molecular weight aldehydes like formaldehyde or gases such as CO.

Air purifiers are a supplemental measure. They should not replace source control and increased ventilation as primary strategies.
Post-Renovation Flush-Out Protocols
Without documented ventilation flush-out before reoccupation, new construction and renovation projects routinely produce TVOC levels well above WELL certification limits. LEED v4.1 recognizes building flush-out and pre-occupancy air testing as best practices, requiring 14,000 cubic feet of outdoor air per square foot of floor area.
Best practices for post-renovation flush-out:
- Increase ventilation during and after delivery of new furnishings
- Allow adequate off-gassing time before extended occupancy
- Run HVAC systems at 100% outside air for 72+ hours before occupants return
When to Escalate to an IAQ Professional
Basic remediation addresses most threshold exceedances, but some situations call for deeper expertise. Engage a Certified Industrial Hygienist (CIH) when:
- Symptoms persist after basic remediation attempts
- Radon levels exceed 4 pCi/L or mold contamination is suspected
- Buildings house vulnerable populations (healthcare settings, schools, daycare)
- Legal or liability concerns require a documented professional investigation
- Complex multi-zone buildings need systematic investigation protocols
Frequently Asked Questions
How do you monitor indoor air quality?
IAQ is monitored using sensors for specific pollutants (CO2, PM2.5, VOCs, CO, humidity) placed in the breathing zone of occupants, with data compared against ASHRAE, EPA, or WELL thresholds. Sensors must be calibrated regularly against NIST-traceable reference gas standards to produce accurate, legally defensible readings.
What is the standard for indoor air quality?
There is no single comprehensive federal IAQ standard in the US. ASHRAE 62.1 is the primary commercial ventilation standard, EPA sets an indoor radon limit (4 pCi/L), and OSHA governs occupational exposure limits. WELL v2 and LEED v4.1 provide voluntary certification benchmarks for broader pollutant sets.
What is a safe level of PM2.5 indoors?
The EPA annual average standard is 9.0 µg/m³, matching WELL v2's threshold. Health Canada has concluded there is no safe level of indoor PM2.5. Focus on source reduction (no indoor smoking, range hood use during cooking) and proper HVAC filtration (MERV 13+) to minimize exposure.
Can an air purifier remove VOCs?
Activated carbon air purifiers can reduce certain VOC concentrations, though effectiveness varies by compound and device. They supplement — but don't replace — source control (low-VOC materials) and increased ventilation. Carbon filters also require regular replacement to stay effective.
What are the symptoms of toxic air in the house?
Common symptoms include headaches, eye and throat irritation, fatigue, dizziness, coughing, sneezing, skin irritation, and difficulty breathing. Symptoms that improve when leaving the building are a key indicator of Sick Building Syndrome requiring investigation.
Are VOCs in new furniture?
Yes. New furniture, flooring, and building materials commonly off-gas VOCs including formaldehyde, benzene, and toluene. Concentrations peak in the first weeks after installation — increase ventilation during delivery and allow adequate off-gassing time before extended occupancy.