But yesterday I got Redmi Note 10 and I can't find these alarm sounds anywhere. When I go to the alarm and choose ringtone, I just get into some stupid Mi Store with tons of short sounds. No option to choose the dynamic alarms. But when I go to my alarms on the Note 8 Pro, the nature alarm is selected, but even then when I click on ringtones where it says "nature alarm", I get into the same MIUI 12 store crap and get the same tones as I do on the Note 10. I cant find nature alarm on the Note 8 Pro, even though it is activated right now.

Research on the effects of Mobile phone radio frequency emissions on biological systems has been focused on noise and vibrations as auditory stressors. This study investigated the potential effects of exposure to mobile phone electromagnetic field radiation, ringtone and vibration on anxiety-like behaviour and oxidative stress biomarkers in albino wistar rats. Twenty five male wistar rats were randomly divided into five groups of 5 animals each: group I: exposed to mobile phone in switched off mode (control), group II: exposed to mobile phone in silent mode, group III: exposed to mobile phone in vibration mode, group IV: exposed to mobile phone in ringtone mode, group V: exposed to mobile phone in vibration and ringtone mode. The animals in group II to V were exposed to 10 min call (30 missed calls for 20 s each) per day for 4 weeks. Neurobehavioural studies for assessing anxiety were carried out 24 h after the last exposure and the animals were sacrificed. Brain samples were collected for biochemical evaluation immediately. Results obtained showed a significant decrease (P < 0.05) in open arm duration in all the experimental groups when compared to the control. A significant decrease (P < 0.05) was also observed in catalase activity in group IV and V when compared to the control. In conclusion, the results of the present study indicates that 4 weeks exposure to electromagnetic radiation, vibration, ringtone or both produced a significant effect on anxiety-like behavior and oxidative stress in young wistar rats.


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Because animals produce so many different types of sounds, developing algorithms to detect, recognize, and classify a wide range of acoustic signals can be challenging. In the past, detection and classification tasks were performed by an experienced bioacoustician who listened to the sounds and visually reviewed spectrographic displays (e.g., for birds by Baptista and Gaunt 1997; chipmunks by Gannon and Lawlor 1989; baleen whales by Stafford et al. 1999; and delphinids by Oswald et al. 2003). Before the advent of digital signal-analysis, data were analyzed while enduring the acrid smell of etched Kay Sona-Graph paper and piles of 8-s printouts removed from a spinning recording drum littering laboratory tables and floors. Output from a long-duration sound had to be spliced together (see Chap. 1). Many bioacoustic studies generated an enormous amount of data, which made this manual review process at best inefficient, and at worst impossible to accomplish.

In this chapter, we present an overview of methods for detection and classification of sounds along with examples from different taxa. No single method is appropriate for every research project and so the strengths and weaknesses of each method are summarized to help guide decisions on which methods are better suited for particular research scenarios. Because algorithms for statistical analyses, automated detection, and computer classification of animal sounds are advancing rapidly, this is not a comprehensive overview of methods, but rather a starting point to stimulate further investigations.

Some bioacousticians identify and classify sounds based on the mechanism of sound production. For example, one syllable in insect song corresponds to a single to- and fro-movement of a stridulatory anatomy or one cycle of a forewing opening and closing in the field cricket (Gryllus spp.). McLister et al. (1995) defined a note in chorusing frogs as the sound unit produced during a single expiration. Classifying sound types by their mode of production perhaps is less ambiguous and unequivocal, but there are limited data on the mechanisms of sound production in many animals.

One of the most common methods for detecting animal sounds from recordings is to measure the energy, or amplitude, of the incoming signal in a specified frequency band and to determine whether it exceeds a user-defined threshold. If the threshold within the frequency band is exceeded, the sound is scored as being present. The threshold value typically is set relative to the ambient noise in the frequency band of interest (e.g., Mellinger 2008; Ou et al. 2012). A simple energy threshold detector does not perform well when signals have low signal-to-noise ratio (SNR) or when sounds overlap. A number of techniques have been devised to overcome these problems, including spectrogram equalization (e.g., Esfahanian et al. 2017) to reduce background noise, time-varying (adaptive) detection thresholds (e.g., Morrissey et al. 2006), and using concurrent, but different, detection thresholds for different frequency bands (e.g., Brandes 2008; Ward et al. 2008). Apart from finding individual animal sounds, energy threshold detectors also have been successfully applied to the detection of animal choruses, such as those produced by spawning fish, migrating whales (Erbe et al. 2015), and chorusing insects or amphibians. These choruses are composed of many sounds from large and often distant groups of animals and so individual signals often are not detectable in them. Choruses can last for hours and significantly raise ambient levels in a species-specific frequency band (Fig. 8.6).

In general, entropy measures the disorder or uncertainty of a system. Applied to communication theory, the information entropy (also called Shannon entropy; Shannon and Weaver 1998) measures the amount of information contained in a data stream. Entropy is computed as the negative product of a probability distribution and its logarithm. Therefore, a strongly peaked probability distribution has low entropy, while a broad probability distribution has high entropy. If applied to an acoustic power spectral density distribution, entropy measures the peakedness of the power spectra and detects narrowband signals in broadband noise (Fig. 8.8). Spectral entropy has successfully been applied to animal sounds; for example, from birds, beluga whales (Delphinapterus leucas), bowhead whales, and walruses (Erbe and King 2008; Mellinger and Bradbury 2007; Valente et al. 2007).

Quantitative classification of animal sounds is based on measured features of sounds, no matter whether these are used to manually or automatically group sounds with the aid of software algorithms. These features can be measured from different representations of sounds, such as waveforms, power spectra, spectrograms, and others. A large variety of classification methods have been applied to animal sounds, many drawing from human speech analysis.

In discriminant function analysis (DFA), canonical discriminant functions are calculated using variables measured from a training dataset. One canonical discriminant function is produced for each sound type in the dataset. Variables measured from sounds in the test dataset are then substituted into each function and each sound type is classified according to the function that produced the highest value. Because DFA is a parametric technique, it is assumed that input data have a multivariate normal distribution with the same covariance matrix (Afifi and Clark 1996; Zar 2009). Violations of these assumptions can create problems with some datasets. One of the main weaknesses of DFA for animal sound classification is that it assumes classes are linearly separable. Because a linear combination of variables takes place in this analysis, the feature space can only be separated in certain, restricted ways that are not appropriate for all animal sounds. Figure 8.17 shows the DFA separation of California chipmunk (genus Neotamias) taxa that are morphologically similar but acoustically different, using six variables measured from their sounds.

In addition to being successfully implemented in human speech recognition, HMMs have been used to classify the sounds produced by birds (Kogan and Margoliash 1998; Trawicki et al. 2005, Trifa et al. 2008, Adi et al. 2010), red deer (Cervus elaphus; Reby et al. 2006), African elephants (Clemins et al. 2005), common dolphins (Sturtivant and Datta 1997; Datta and Sturtivant 2002), killer whales (Brown and Smaragdis 2008, 2009); beluga whales (Clemins and Johnson 2005; Leblanc et al. 2008), bowhead whales (Mellinger and Clark 2000), and humpback whales (Suzuki et al. 2006). HMMs perform as well as, or better than, both GMMs and DTW (Weisburn et al. 1993; Kogan and Margoliash 1998) and are becoming more common in animal classification studies.

Placing sounds into categories is not always straightforward. Sounds produced by a particular species often contain a great deal of variability caused by different factors (e.g., location, date, age, sex, and individuality), which can make it difficult to define categories. In addition, sound categories are not always sharply demarcated, but instead grade or gradually transition from one form to another. It is important to be aware of the challenges in a particular dataset. Below are some types of variation that can be encountered in the classification of animal sounds. 2351a5e196

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