Health impact briefing · Severn, Maryland · May 2026

This is not an inconvenience.
It is a health exposure.

Aircraft noise at this location peaks 27.7 dB above the normal background acoustic environment — in the range that public health authorities have linked to cardiovascular disease, sleep disruption, and cognitive harm in children. This briefing translates the measurements into what they mean for the people living underneath the flight path.

70.2 dBA peak · bedroom window · 6:55 AM
27.7 dB above normal background
54 / 58 events with no recovery time between them

Measurements: TrueNoise Community Noise Observatory · Severn, MD · A321 takeoff overflight 19 May 2026, 06:55 AM · Extended session same location · Calibrated against TA657A Type 2 reference meter · See methodology for full detail

Section 1

What 70.2 dBA actually sounds like

Sound levels in dBA are not intuitive. The decibel scale is logarithmic — every 10 dB increase represents roughly a doubling of perceived loudness. These reference points translate the measurement into everyday experience:

Normal conversation
60 dBA
Two people talking at normal volume
Vacuum cleaner (3 ft away)
70 dBA
Busy restaurant · busy street
This aircraft · bedroom window
70.2 dBA
Peaked for approximately 4 seconds at 6:55 AM
Kitchen blender
80–85 dBA
On the counter next to you

This aircraft, at the bedroom window, was as loud as having a vacuum cleaner running right next to the bed. It was not a distant hum. It was a foreground sound.

The psychoacoustic measurement — perceived loudness in sones — peaked at 21. The sone scale is built so that doubling means twice as loud to a person. A score of 21 sones is roughly fifteen to twenty times louder than ordinary conversation. The phon measurement of 84 corresponds to the level at which two people in the same room have to stop talking and wait for the noise to pass before continuing — speech becomes unintelligible without raising voices significantly.


Section 2

How loud relative to the normal acoustic environment

The measurement that matters most is not the peak level in isolation — it is how far that peak is above the location's normal background. The baseline acoustic floor at this location is 42.5 dBA (LA90 — the level exceeded 90% of the time, which approximates the true background). That is a properly quiet residential environment: birds, the occasional distant car, an HVAC fan cycling on.

The aircraft peak was 70.2 dBA — 27.7 dB above the normal background. Every 10 dB is roughly a doubling of perceived loudness. This aircraft was perceived as approximately six to seven times louder than the quiet morning it interrupted.

It was not a marginal increase. It was a categorical change in the soundscape — a foreground industrial sound dropped into what is otherwise a quiet residential morning. No amount of habituation eliminates the physiological response to that kind of intrusion. The body responds whether or not the mind has learned to expect it.


Section 3

Sleep disturbance — why 6:55 AM matters

The time of day matters enormously in noise health research. 6:55 AM falls within the World Health Organization's defined night and early morning sensitivity window, when the human body is most vulnerable to noise-induced harm. What does 70.2 dBA at the bedroom window actually mean for someone sleeping inside?

🪟
Windows closed (typical residential construction)
Building envelope reduces exterior sound by approximately 25 dB. Indoor bedroom level: approximately 45 dBA. WHO's threshold for sleep disturbance is 40 dBA indoors. This event very likely caused at least a partial awakening — the kind where the sleeper does not fully wake but sleep stage shifts, heart rate spikes, and stress hormones release without the eyes ever opening.
🌬
Windows open (summer, common in this climate)
Indoor level: approximately 60 dBA. Sufficient to fully wake an adult. Sufficient to wake a child. Sufficient to end a sleep cycle that cannot simply be resumed.
🧒
Children — particularly vulnerable
Research consistently shows aircraft noise exposure during sleep affects reading comprehension scores, behavioral self-regulation, and cognitive development when exposure persists for years. These are not temporary effects — they accumulate.

Section 4

The pattern matters more than any single event

A single 70 dBA overflight is startling. What makes this a health exposure rather than an inconvenience is the pattern in which events arrive.

Recovery deficit

From an extended session at this location: aircraft events arrived approximately once every 6 minutes and 41 seconds. Of 58 intervals between events, 54 were shorter than 15 minutes.

The 15-minute threshold is not arbitrary. The human stress response — the cortisol spike triggered by an acoustic startle — requires approximately 15 minutes to fully resolve under normal conditions. When the next noise event arrives before the previous one has physiologically dissipated, stress hormones do not return to baseline. They compound. Not occasionally elevated — continuously elevated.

This is the mechanism by which environmental noise causes physical disease. Not the single loud event. The relentless interval.

The World Health Organization has linked this pattern of chronic noise exposure to the following documented health outcomes:

❤️
Cardiovascular disease and stroke
Each 10 dBA increase in long-term aircraft noise exposure is associated with approximately 12% higher risk of heart disease and stroke. Peaks at this location are well above this threshold; event density compounds the effect through the cortisol mechanism.
🩸
Hypertension
Particularly associated with nighttime and early morning exposure, even when the person does not consciously notice the sound. The body responds to the acoustic stimulus regardless of subjective awareness.
🧠
Type 2 diabetes
Likely mediated through chronic stress hormone disruption of metabolic function. The cortisol pathway connects acoustic stress to metabolic disease through well-understood endocrine mechanisms.
📚
Cognitive impairment in children
Particularly affecting reading comprehension and memory tasks. Documented in the RANCH study across multiple European countries and school populations. Effects are dose-dependent and persist with continued exposure.
😔
Anxiety, depression, tinnitus
Well-documented dose-response relationships in noise-exposed populations. Tinnitus and stress-related health complaints in adults exposed long-term. These are not self-reported inconveniences — they appear in clinical datasets and insurance records.

These are not speculative effects. They are documented in large epidemiological studies — most notably the HYENA study in Europe (cardiovascular outcomes across five countries) and the RANCH study (children's cognitive outcomes near major airports). Jarup et al., Environmental Health Perspectives (2008) · Stansfeld et al., The Lancet (2005)


Section 5

What this data can and cannot say

Intellectual honesty requires stating what the evidence supports and what it does not.

What we can say with confidence
  • The acoustic exposure at this location meets the conditions WHO has linked to the health endpoints above
  • The intrusion magnitude — 27.7 dB above background — is large enough to cause acute startle responses and sleep disruption
  • The event density (9.1 per hour, 54 of 58 intervals under the stress-recovery threshold) is in the range associated with chronic stress mechanisms
  • The measurement system is calibrated against a Type 2 reference meter and validated across three aircraft types, two flight phases, and two microphones — all within IEC Class 2 tolerance
What we cannot say
  • That any specific person at this address has developed a specific disease because of these aircraft
  • That long-term outcomes will follow the same dose-response curves observed in European studies — those populations differ
  • That health effects scale linearly from a small dataset

Health outcomes are statistical at the population level, not deterministic at the individual level. What has been measured is the dose. The disease outcomes are probabilistic. The science does not say "this person will develop heart disease" — it says "people exposed to this much aircraft noise, on average, develop cardiovascular disease at measurably higher rates."


Closing

From the numbers to the human stakes

The parent whose afternoon in the backyard with his children is interrupted every seven minutes is not imagining things. The interruption is real, the noise is loud, and the cumulative pattern of those interruptions — repeated daily for years — falls within the range of exposure that established medical evidence links to cardiovascular and cognitive harm. The science does not say he will develop heart disease. It says people exposed to this much aircraft noise, on average, do so at measurably higher rates.

The person jarred awake at 6:55 AM is not being sensitive. The noise reached the WHO threshold for sleep disturbance inside a closed bedroom. The body responded whether or not consciousness registered the event.

This is a residential location experiencing an exposure pattern that public health authorities have linked to documented harms. It is not an inconvenience. It is a population-scale health exposure. And it is measurable, characterizable, and now documented.

TrueNoise exists to make that documentation possible at community scale — with calibrated instruments, rigorous methodology, and transparent data — so that the conversation with regulators can move from "residents are complaining" to "here is what the evidence shows."