Reference · Animal Impact

Animal Impact Panels

The Animal Impact group is where MuirWave turns a source and a location into the numbers a marine-noise impact assessment actually has to contain: the per-hearing-group impact ranges that a regulator expects to see. This page walks every control in the Impact Ranges panel, explains what comes out the other end, and shows how the two export formats work.

The Impact panel computing: receptor and convention selectors, source-type, TL model, hammer energy, strike count and exposure model, with the ANIMAL IMPACT group in the panel rail and the MIT chip in the top bar.
The ANIMAL IMPACT group. Its rail tiles are Impact, Mitigation and Export Methodology. Shown: Impact computing a complete pile-driving scenario — receptor and convention at the top, the source description below, with the governing MIT range chip in the top bar. Until the four scenario parameters are set, the panel shows a checklist prompt instead (the no-defaults gate).
§01

What's in the group

Three tiles sit under Animal Impact in the rail (iPad / Mac) or dock (iPhone). One does the work today; one is reserved for a later release; one exports what the first produced.

01
Impact Ranges
The working panel. Computes the impact-range table per hearing group for your source and pin. Everything else on this page is about this tile.
02
Mitigation PRO
The noise-abatement screening panel (§08). Pick an abatement system, see the mitigated-vs-unmitigated impact ranges per hearing group, the insertion-loss curve, and the operational measures — an MuirWave Pro feature. All mitigation lives here; the Impact Ranges panel itself stays the unmitigated baseline.
03
Export Methodology
An action tile. Turns the panel's current selections into a self-contained methodology document — Markdown or PDF. Covered in §07.
Everything here needs a complete scenario first. Until all four scenario parameters are entered in Acoustics Setup — frequency, source level, source depth and receiver depth — the Impact Ranges panel shows a SCENARIO INCOMPLETE checklist instead of numbers. It never builds a table on hidden defaults.
§02

How your inputs become the table

Every control in the panel feeds one of three stages: it either picks which criteria apply, sets the source level being propagated, or chooses how sound spreads with range. The panel then inverts that geometry per hearing group to find the range at which the received level drops to each threshold.

PANEL INPUTS CRITERIA + SOURCE ON-DEVICE INVERSION READOUT RECEPTOR Mammals · Fish + Turtles CONVENTION / IMPACT NMFS · Southall / Mort · Inj SOURCE Impulsive · Non-imp · Cont SOURCE LEVEL BLOCK Hammer · Strikes Exposure —or— SL · Freq TL MODEL 20·log r · 15·log r Threshold catalogue NMFS 2024 / Southall 2019 Popper 2014 (fish) M-weighting per hearing group Effective SL @ 1 m peak + cumulative SEL₂₄ₕ (unmitigated) Per-group range solve r where SL − TL(r) = threshold computed on device GOVERNING TABLE PEAK · SEL₂₄ₕ GOVERNING = larger Summary + ramp largest zone · soft-start BSH 750 m gate on Mitigation panel source level in → injury range out, per group
Input map. Receptor + convention pick the threshold pair; the source block sets the level being propagated; the TL model sets the spreading law. MuirWave solves for the range at which the received level meets each group's threshold, then the governing range is the larger of the peak and SEL isopleths. The same table then drives the summary and the soft-start ramp; under German jurisdiction it also feeds the BSH 750 m gate on the Mitigation panel.
§03

The core controls

These segmented pickers appear for every scenario, top to bottom, and decide which criteria and spreading law the table is built from.

ControlOptionsWhat it does
RECEPTOR Mammals · Fish + Turtles Chooses the whole taxonomy. Mammals runs the marine-mammal hearing groups against auditory-injury thresholds; Fish + Turtles runs the Popper 2014 fish and sea-turtle groups instead.
CONVENTION NMFS 2024 · Southall 2019 Mammals only. Selects the matched threshold-and-weighting pair. The two are never mixed — an inline note lists exactly which groups the ranges move on when you switch. (Replaced by IMPACT for fish.)
IMPACT Mortality · Injury Fish + Turtles only. Picks which Popper 2014 severity table to compute against — mortality / potential mortal injury (Table 4.3), or recoverable injury (Table 4.2).
SOURCE Impulsive · Non-impulsive · Continuous The physical character of the noise. Impulsive = pile-driving, seismic airgun, UXO; Non-impulsive = vibratory piling, drilling; Continuous = turbine, shipping. This choice swaps the source-level block below (§04 vs §05).
TL MODEL 20·log r · 15·log r The spreading law used to invert range. 20·log r is spherical (deep-water free field); 15·log r is the practical / shallow-water monopile convention used by BSH and Subacoustech. MuirWave picks a sensible default per source type (15·log r for impulsive, 20·log r for non-impulsive / continuous) — override it if your site guidance differs.
Peak vs SEL, in one line. Peak SPL is the single loudest instant (unweighted, impulsive sources only). SEL₂₄ₕ is the frequency-weighted sound energy summed over 24 hours of activity. The governing range is whichever of the two reaches further — for the most sensitive porpoise group, peak usually wins near the pile.
§04

Impulsive: the pile-driving block

With SOURCE set to Impulsive, MuirWave opens a built-in pile-driving source library so you don't have to hand-enter source levels. Three extra controls appear:

ControlStopsMeaning
HAMMER 300 · 1900 · 2300 · 3000 · 4000 · 5400 kJ Hammer blow energy, from a small inshore pile (300 kJ) up to a large monopile hammer (5400 kJ). The published peak and single-strike SEL for the class are read straight from the library. Default 3000 kJ — the Dogger Bank Teesside A class, the validation reference.
STRIKES 500 · 1000 · 2000 · 3000 · 4000 · 6000 Number of blows to drive the pile. This sets the cumulative SEL₂₄ₕ offset (+10·log₁₀ N — each doubling of strikes adds ≈ 3 dB), so more strikes push the SEL isopleths further out. Default 2000.
EXPOSURE Stationary · Fleeing How the animal is assumed to accumulate the 24-hour dose. Fleeing (default) has the receptor swim radially away at ≈ 1.5 m/s — the realistic individual-based assessment EIA practice expects. Stationary holds it in place for every strike — the conservative NMFS User-Spreadsheet screening upper bound.

A caption under the pickers confirms the representative hammer, the unmitigated source levels (SL_peak and SEL_ss at 1 m) and the cumulative SEL₂₄ₕ offset, so you can sanity-check the state at a glance.

§05

Non-impulsive & continuous: the generic block

There is no published hammer library for vibratory piling, drilling, turbines or shipping, so with SOURCE set to Non-impulsive or Continuous the pile-driving block is replaced by two direct inputs you set yourself:

FieldRangeMeaning
Source Level 100 – 240 dB re 1 µPa @ 1 m The source's broadband level. Default 180 dB — an indicative starting point; substitute your site-measured value.
Frequency 10 Hz – 50 kHz The dominant source frequency, on the same log slider used elsewhere in MuirWave (default 500 Hz). The auditory weighting is applied here — a real vibratory or turbine source has a meaningful dominant tone, unlike a broadband hammer.
These inputs are panel-local. Editing the source level or frequency here never touches your Ray Path scenario — the Impact panel is a self-contained calculator. For continuous sources MuirWave treats the source as radiating for the full 24 hours (conservative for intermittent activity): SEL₂₄ₕ = source level + 10·log₁₀(86 400 s).
§06

Reading the outputs

Below the controls the panel stacks up to four readouts. Which ones appear depends on your receptor, source type and compliance jurisdiction.

  1. The impact-range table
    One row per hearing group — five for mammals (NMFS: LF / HF / VHF / PW / OW; Southall relabels the two pinniped rows PCW / OCW — codes expanded in the Glossary: LF baleen whales, HF dolphins, VHF porpoises, PW/OW seals & sea lions), four for fish + turtles. Four columns: HEARING GROUP, PEAK (impulsive only), SEL₂₄ₕ† (the dagger flags the accumulation assumption), and GOVERNING. The governing range — the larger of peak and SEL — is highlighted in cyan; that's the radius that matters for that group.
  2. The summary headline
    A large cyan number: the largest mitigation zone across all groups (or the largest mortality / injury isopleth for fish), with the driving group named beneath. A checkmark badge means it's a trustworthy metric; a warning glyph appears only when a stationary screening SEL is driving the headline — a conservative upper bound, not a submission figure.
  3. The soft-start ramp
    Mammals + impulsive only. A six-row table showing the largest governing range at every hammer-energy stop, with your current hammer highlighted — a visual aid for the JNCC-style ≥ 30-minute soft-start that escalates from low to operational energy. It recomputes on a background task, so the panel stays responsive.
  4. The compliance footer & assumptions
    A footer shows the active jurisdiction (flag, short label and a one-line summary of its rule), and below it an ASSUMPTIONS block spells out every simplification — the single-coefficient TL model, the source-spectrum treatment, that soft-start isn't modelled (≈ −1 dB on SEL₂₄ₕ), and that beyond ≈ 3500 m an impulsive signature degrades to non-impulsive (Hastie et al. 2019) — plus the exact citation. Nothing is hidden from a reviewer.
The compliance jurisdiction is set in Settings, not here. Go to Settings → Compliance Jurisdiction to choose from NMFS (United States), BSH (Germany), JNCC (United Kingdom), EPBC + OEI (Australia) or Southall 2019 (International). That choice decides the footer wording and whether the BSH gate appears on the Mitigation panel; both panels read it automatically.
§07

Exporting the methodology

The Export Methodology tile turns the panel's current selections into a self-contained methodology document — scenario inputs, propagation method, criteria and thresholds, and the per-group predicted ranges with full citations. Tap the tile, pick a format, confirm.

Markdown — free
  • A plain .md file that drops straight into §3 of an EIA or academic report.
  • Available to everyone, no upgrade needed.
  • Faithful to your live panel state — source type, receptor, accumulation model, convention, mitigation and pin depth.
PDF — MuirWave Pro
  • A branded, paginated multi-page A4 PDF — an attachable, regulator-ready deliverable.
  • The PDF is an MuirWave Pro feature; a free user is shown the upgrade screen instead of the export.
  • Identical content to the Markdown version, formatted for submission.
The export always matches the panel. There's no separate configuration step — whatever the Impact Ranges panel is showing when you export is exactly what the document records, so the two can never disagree.
§08

The Mitigation panel PRO

The second tile in the group opens a dedicated noise-abatement screening surface — and it's the only place mitigation lives. The Impact Ranges panel gives everyone the unmitigated baseline; this panel shows what a mitigation strategy actually does on top of it — per hearing group, across frequency, and with the operational measures a method statement relies on. It is an MuirWave Pro feature; a free user sees an upgrade panel with every impact-range number still visible on screen for free.

Five things stack up in the panel, all reading off the same scenario as Impact Ranges:

  1. The system picker
    Six options — None / BBC / DBBC / HSD / IHC-NMS / BBC+HSD — each applied as a broadband reduction at the source: Big Bubble Curtain (−10 dB), Double BBC (−15 dB), Hydro-Sound Damper (−9 dB), IHC Noise Mitigation Screen (−17 dB), or a stacked BBC + HSD (−19 dB). It starts at None, so the panel opens on the same unmitigated baseline as Impact Ranges. The selected system's full name and broadband reduction show beneath; a combination (BBC+HSD) notes that its value is measured, not the sum of the single systems.
  2. Frequency-dependent insertion loss
    A toggle switches the mitigation from a flat broadband number to a frequency-dependent insertion loss IL(f) — the curve below then shows where the abatement actually works. Bubble curtains and dampers are weak at the low-frequency piling peak and strongest across the mid-band, so spectral mitigation is more protective for high-frequency-hearing species (porpoises) than for low-frequency hearers (baleen whales) — a distinction a single number can't make. The amber shape under the curve is the pile's own source spectrum, so you can see the mismatch at a glance.
  3. The mitigated-vs-unmitigated trade-off
    One row per hearing group, reading 3.5 km → 720 m ×4.9 — the unmitigated governing range struck through, the mitigated range in bold, and the reduction factor as a badge. When a system fully removes a group's injury zone the row reads cleared. This is the headline an EIA reviewer wants: what the strategy buys, per species.
  4. Operational measures
    Two toggles credit measures that work by moving animals off before full power. Soft-start ramp (the JNCC ≥30-min escalation) is credited as a modest early-flee head-start for all groups. Acoustic deterrent (ADD) is credited a larger head-start — but for toothed whales only (dolphins, porpoises): seals habituate to deterrents (or are attracted to them), and ADD efficacy on baleen whales is poorly evidenced, so both are deliberately not credited. The panel says so in plain language.
  5. The BSH 750 m compliance gate
    Under a BSH (Germany) compliance jurisdiction, for impulsive mammal scenarios, this panel carries the BSH dual-threshold gate: the predicted Peak SPL against the 190 dB limit and single-strike SEL₀₅ against the 160 dB limit at exactly 750 m (the BSH StUK4 dual criterion), with a per-metric headroom badge and an overall PASS / EXCEEDED verdict. It reads off the same scenario as Impact Ranges, so the two never disagree.
Screening, not consent-grade. A SCREENING pill and a one-line disclaimer sit on the panel and carry into the methodology export: the insertion-loss values are indicative published defaults for typical North Sea conditions, not site measurements. Substitute site-specific measured attenuation and behavioural-response data for a permit submission.