Methodology
How claims on this site are sourced.
A short page explaining the source hierarchy, what counts as evidence here, what is editorially excluded, and how the documented-vs-provisional split is signposted on the site.
Source hierarchy
- Institutional public-health guidance — World Health Organization Europe noise fact sheet and night-noise guideline; CDC and EPA materials where applicable; OSHA and NIOSH for occupational standards.
- Peer-reviewed clinical and acoustical literature — for cardiovascular, sleep-architecture, cognitive, and infrasound claims. Sourced via the published reviews and meta-analyses summarized on each page; primary citations are listed on Sources.
- Primary regulatory text — for statements about specific bans (California AB 1346, D.C. Law 22-281, municipal ordinances), the underlying bill or ordinance text is the canonical source.
- Trade and policy reporting — for current-state implementation notes (CARB enforcement updates, municipal-ban map maintenance), reputable advocacy organizations and trade press are used as a starting point and cross-checked against primary documents.
Documented vs. provisional
The site is honest about which claims rest on a firm published base and which rest on more provisional ground. Pages flag this where it applies. The split, in summary:
Documented (peer-reviewed or institutional)
- WHO night-noise guideline of less than 40 dB(A) outside bedrooms; less than 30 dB(A) in bedrooms
- Approximately 40% of the EU population exposed to road-traffic noise above 55 dB(A); more than 30% above 55 dB(A) at night
- Cardiovascular effects of chronic noise — elevated blood pressure, heart-attack risk, stroke risk
- Aircraft-noise cognitive impairment in children
- Cortisol–melatonin antagonism
- California AB 1346 (2021) phasing out gas-powered lawn equipment
- OSHA permissible exposure limit of 90 dB(A) TWA; NIOSH recommended exposure limit of 85 dB(A) TWA
- Vic Tandy infrasound research (Journal of the Society for Psychical Research, 1998) on 18 Hz standing waves and physiological / perceptual effects
Provisional or contested
- Specific magnitudes of cardiovascular damage attributable to gas-powered backpack blowers vs. other residential noise sources — the dose-and-modulation profiles are not yet measured at the granularity that would tighten this further
- Field prevalence of pulsed-white-noise sources in consumer residential devices — under-studied
- The full magnitude of EMF–melatonin interaction with noise-induced cortisol
- The dose-response curve for sleep-architecture fragmentation in habituated subjects who report not noticing the noise — the direction is well-supported, the curve less so
What is editorially excluded
- Naming individuals. The site does not identify specific landscape workers, property owners, residents, or contractors.
- Diagnostic claims about specific people. Symptoms are described in general terms, not pinned to identified persons.
- Medical, legal, or policy advice for specific situations. Specific situations need professionals.
- User-generated content. No comment system, no forum, no submission form.
- Speculative claims about intent. The site argues that the equipment functions in a particular way regardless of operator intent; it does not impute malicious intent to operators.
Corrections
If a claim is wrong or has become outdated — a regulation has changed, a study has been retracted, a citation is mis-attributed — the page is updated promptly. Email at /sources/.