Universitat Politècnica de Catalunya Michel André MEUST: Real-time Monitoring of Noise and Acoustic Events in Cetacean Acoustic Niches.

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Universitat Politècnica de Catalunya Michel André MEUST: Real-time Monitoring of Noise and Acoustic Events in Cetacean Acoustic Niches

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Effects of Noise on Marine Mammals: Mitigation actions & long-term monitoring Baseline to be used for future assessment Identifying the contribution of different noise sources Controling the effects of noise on cetaceans

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Monitoring existing noise sources

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Controling the effects of noise on Cetaceans Automated classification methods to detect and identify acoustic sources Need for establishing standards to measure noise

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Controling the effects of noise on Cetaceans Marine soundscape * Cetacean whistles and calls * Cetacean clicks, bursts, creaks, buzzes... * Tonal, impulsive and broadband ship noise * Explosions * Sonar, echosounder, * Waves, rain, bubbles, etc. * etc. Challenging for automated classification methods

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Controling the effects of noise on Cetaceans Need for establishing standards to measure noise INDICATORS FOR GOOD ENVIRONMENTAL STATUS FOR UNDERWATER NOISE AND OTHER FORMS OF ENERGY Task Group 11 for the European Marine Strategy Framework (International Council for the Exploration of the Sea)

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques TG11 Energy ATTRIBUTECriteria to assess the descriptorIndicators to be measured Underwater noise - Low and mid- frequency impulsive sound High amplitude impulsive anthropogenic sound within a frequency band between 10Hz and 10 kHz, assessed using either sound energy over time (Sound Exposure Level SEL) or peak sound level of the sound source. Sound thresholds set following review of received levels likely to cause effects on dolphins; these levels unlikely to be appropriate for all marine biota. The indicator addresses time and spatial extent of these sounds. The proportion of days within a calendar year, over areas of 15’N x 15’E/W in which anthropogenic sound sources exceed either of two levels, 183 dB re 1µPa 2.s (i.e. measured as Sound Exposure Level, SEL) or 224 dB re 1µPa peak (i.e. measured as peak sound pressure level) when extrapolated to one metre, measured over the frequency band 10 Hz to 10 kHz Underwater noise – High frequency impulsive sounds Sounds from sonar sources below 200 KHz that potentially have adverse effects, mostly on marine mammals, appears to be increasing. This indicator would enable trends to be followed. The total number of vessels that are equipped with sonar systems generating sonar pulses below 200 kHz should decrease by at least x% per year starting in [2012]. Underwater noise – low frequency continuous sound Background noise without distinguishable sources can lead to masking of biological relevant signals, alter communication signals of marine mammals, and through chronic exposure, may permanently impair important biological functions. Anthropogenic input to this background noise has been increasing. This indicator requires a set of sound observatories and would enable trends in anthropogenic background noise to be followed. The ambient noise level measured by a statistical representative sets of observation stations in Regional Seas where noise within the 1/3 octave bands 63 and 125 Hz (centre frequency) should not exceed the baseline values of year [2012] or 100 dB (re 1µPa rms; average noise level in these octave bands over a year). Underwater noise – low frequency continuous sound The ambient noise level measured by a statistical representative sets of observation stations in Regional Seas where noise within the 1/3 octave bands 63 and 125 Hz (centre frequency) should not exceed the baseline values of year [2012] or 100 dB (re 1µPa rms; average noise level in these octave bands over a year).

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques audio data stream Segment 1Segment 2Segment 3Segment 4Segment 6Segment 5... Localisation Tracking Classifier 1 Classifier 2... Stage 2 Discard sea noise Assign broad categories Stage 1 FM-tonal sounds Impulses... Sperm whales Beaked whales Pilot whales Dolphins Ships Sonar... Bearing, Position Trajectory, … Stage 3 Real-Time Mitigation Long term assessment and Control of the effects of anthropogenic sources on marine organisms (i.e. whales)... Public outreach Education End users Administration

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Controling the effects on Cetaceans Functional groups according to auditory characteristics Estimated BandwidthGenus represented Low frequency7Hz to 22 kHz Baleana, Caperea, Eschrichtius, Megaptera, Balaenptera (13 species/subspecies) Mid frequency150 Hz to 160 kHz Steno, Sousa, Tursiops, Stenella, Delphinus, Lagenodelphis, Lagenorhynchus, Lissodelphis, Grampus, Peponocephala, Feresa, Pseudorca, Orcinus, Globicephala, Orcaella, Physeter, Delphinapterus, Monodon, Ziphius, Berardius, Tasmacetus, Hyperoodon, Mesoplodon (57 species/subspecies) High Frequency200 Hz to 180 kHz Phocoena, Neophocaena,Phocoenoides, Plaanista, Inia, Kogia, Lipotes, Pontoporia, Cephalorhynchus (20 species/subspecies) Cetacean Acoustic Niches

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques Underwater vehicles, e.g.gliders Radio-linked, expandable or moored stand-alone buoys Deep-sea or shallow water cabled observatories Underwater neutrino telescopes Existing recordings

Universitat Politècnica de Catalunya Laboratori d’Aplicacions Bioacústiques