Protection from Acoustic Trauma Is Not a Primary Function of the Medial Olivocochlear Efferent System

Abstract

The medial olivocochlear (MOC) efferent system is an important component of an active mechanical outer hair cell system in mammals. An extensive neurophysiological literature demonstrates that the MOC system attenuates the response of the cochlea to sound by reducing the gain of the outer hair cell mechanical response to stimulation. Despite a growing understanding of MOC physiology, the biological role of the MOC system in mammalian audition remains uncertain. Some evidence suggests that the MOC system functions in a protective role by acting to reduce receptor damage during intense acoustic exposure. For the MOC system to have evolved as a protective mechanism, however, the inner ears of mammals must be exposed to potentially damaging sources of noise that can elicit MOC-mediated protective effects under natural conditions. In this review, we evaluate the possibility that the MOC system evolved to protect the inner ear from naturally occurring environmental noise. Our survey of nonanthropogenic noise levels shows that while sustained sources of broadband noise are found in nearly all natural acoustic environments, frequency-averaged ambient noise levels in these environments rarely exceed 70 dB SPL. Similarly, sources reporting ambient noise spectra in natural acoustic environments suggest that noise levels within narrow frequency bands are typically low in intensity (<40 dB SPL). Only in rare instances (e.g., during frog choruses) are ambient noise levels sustained at moderately high intensities (~70–90 dB SPL). By contrast, all experiments in which an MOC-mediated protective effect was demonstrated used much higher sound intensities to traumatize the cochlea (100–150 dB SPL). This substantial difference between natural ambient noise levels and the experimental conditions necessary to evoke MOC-mediated protection suggests that even the noisiest natural acoustic environments are not sufficiently intense to have selected for the evolution of the MOC system as a protective mechanism. Furthermore, although relatively intense noise environments do exist in nature, they are insufficiently distributed to account for the widespread distribution of the MOC system in mammals. The paucity of high-intensity noise and the near ubiquity of low-level noise in natural environments supports the hypothesis that the MOC system evolved as a mechanism for “unmasking” biologically significant acoustic stimuli by reducing the response of the cochlea to simultaneous low-level noise. This suggested role enjoys widespread experimental support.

INTRODUCTION

Cochlear outer hair cells are mechanically active and provide the exquisite sensitivity and frequency selectivity characteristic of the mammalian auditory system. Because outer hair cell function is modulated by descending, medial olivocochlear (MOC) efferent neurons, the MOC system is an important component of a mechanically active cochlea. While the specific physiological and psychophysical effects of MOC activity on audition are well documented (e.g., Brown et al. 1983; Winslow and Sachs 1987; Kawase et al. 1993; May and McQuone 1995; Liberman et al. 1996; Lima da Costa et al. 1997; Smith 1998), the actual biological role of the MOC system is less clear (cf. Guinan 1996). In this regard, the current neurophysiological data are inconclusive, suggesting that the MOC system could play two very different roles in mammalian hearing.

First, a number of investigators have provided evidence that the MOC system suppresses the response of the cochlea to concurrent noise and, in so doing, helps to “unmask” transient acoustic stimuli (Nieder and Nieder 1970; Winslow and Sachs 1987, 1988; Dolan and Nuttall 1988; Kawase and Liberman 1993; Kawase et al. 1993; Liberman and Guinan 1998). These sources support the hypothesis that the MOC system evolved as a means of improving the signal-to-noise ratio and the dynamic range of the peripheral auditory system.

Second, Rajan (1988a,b, 1995a,b, 1996, 2000, 2001a), Rajan and Johnstone (1983, 1988a,b,c), and others (Handrock and Zeisberg 1982; Liberman and Gao 1995; Reiter and Liberman 1995; Zheng et al. 1997) have shown that the presence and extent of threshold shifts following intense, high-frequency sound exposure are increased after deactivation of the MOC system, or are decreased when the MOC system is stimulated with either electrical stimulation of the olivocochlear tracts or acoustic stimulation of the contralateral ear. These results support the hypothesis that the MOC system evolved as a protective mechanism that acts to reduce receptor damage during intense noise exposure. By contrast, several studies using similar experimental designs have shown no evidence for MOC-based protective effects (Hildesheimer et al. 1990; Liberman 1991). As is shown later in this analysis, the stimulus conditions that failed to demonstrate efferent protection in some studies overlap in both frequency and intensity the stimuli that are reported to evoke efferent protection in other similar experiments, highlighting the variability of the protective effect (cf. Guinan 1996).

In this review we evaluate the hypothesis that the MOC system evolved to protect the inner ear from naturally occurring environmental noise (the “protection hypothesis”). The reason for this test, as Guinan (1996) has pointed out, is that it is currently unknown whether or not potentially damaging environmental noise was sufficiently common to have influenced the evolution of the MOC system. We first survey the available literature that describes the characteristics of ambient noise in different natural acoustic environments. We then review published reports describing the stimulus parameters necessary to demonstrate a role for the MOC efferent system in protecting the cochlea from noise-induced trauma. By comparing these two sources of data, we are able to determine whether environmental noise that is known to occur under natural conditions may be sufficiently intense to elicit the protective effects of the MOC system. If such protective effects are not induced by naturally occurring acoustic stimuli, it is unlikely that the MOC system could have evolved to protect the inner ear from acoustic trauma.

DISTRIBUTION OF THE MOC SYSTEM AMONG MAMMALS

The auditory end organs of all tetrapods (including mammals) receive an efferent innervation (Roberts and Meredith 1992; Fritzsch 1992, 1997). However, it is currently unknown whether monotremes, which lack some features of the inner ear shared by marsupial and placental mammals (Ladhams and Pickles 1996), possess an MOC system. All species that have been definitively shown to possess an MOC system are included within four orders of placental mammals (Primates, Chiroptera, Carnivora, Rodentia) and two orders of marsupials (Dasyuromorphia and Didelphimorphia; Table 1). If one assumes that MOC systems in these orders are inherited from a common ancestor and retained in most descendent taxa, then it is likely that all placental and marsupial orders share MOC efferent innervation of cochlear outer hair cells. The distribution of character states among known taxa thus suggests that the MOC system is a general feature of the mammalian auditory system that must have arisen no later than the time of divergence between marsupial and placental mammals (ca. 173 million years before present; Kumar and Hedges 1998).

Table 1.

Taxa known to possess medial efferent innervation of outer hair cells

Taxa known to possess medial efferent innervation of outer hair cells
Order	Genus	Common name (source)
Carnivora	Felis	Cat (Warr and Guinan 1979; Guinan et al. 1983; Liberman et al. 1990)
	Canis	Dog (Weber et al. 1987)
Chiroptera	Pteronotus	Moustached bat (Bishop and Henson 1987, 1988)
	Artibeus	Neotropical fruit bat (Aschoff and Ostwald 1987)
	Phyllostomus	Spear-nosed bat (Aschoff and Ostwald 1987)
	Tadarida	Free-tailed bat (Aschoff and Ostwald 1987)
	Rhinopoma	Mouse-tailed bat (Aschoff and Ostwald 1987)
Dasyuromorphia	Sminthopsis	Dunnart or Marsupial mouse (Henson and Henson, unpublished data)
Didelphimorphia	Didelphis	Opossum (Henson and Henson, unpublished data)
Primates	Homo	Human (Nadol 1983, 1990)
	Pan	Chimpanzee (Nadol and Burgess 1990)
	Macaca	Macaque monkey (Sato et al. 1997, 1999)
	Saimiri	Squirrel monkey (Thompson and Thompson 1986)
	Otolemur	Bush baby (Thompson and Thompson 1995)
Rodentia	Mus	Mouse (Campbell and Henson 1988)
	Rattus	Rat (Aschoff and Ostwald 1987, 1988; Robertson et al. 1989)
	Cavia	Guinea pig (Aschoff and Ostwald 1987, 1988)
	Chinchilla	Chinchilla (Azeredo et al. 1999)
	Pachyuromys	Fat-tailed gerbil (Aschoff et al. 1988)
	Meriones	Mongolian gerbil (Aschoff et al. 1988)
	Mesocricetus	Golden hamster (Simmons et al. 1996)

Furthermore, among mammals for which the anatomy is known, the majority (21 of 24 species) possess cochlear outer hair cells that receive MOC innervation (Table 1). This broad distribution across six orders and 16 families of mammals is striking; it suggests that the MOC system has been maintained by stabilizing selection in most mammalian groups despite pronounced differences in habitat and ecology. Indeed, the only mammals that are known to lack MOC innervation of outer hair cells are the microchiropteran bats Hipposideros and Rhinolophus (Bruns and Schmieszek 1980; Aschoff and Ostwald 1987; Bishop and Henson 1987, 1988; Ostwald and Aschoff 1988) and the blind mole rat Spalax ehrenbergi (Raphael et al. 1991). Although it is currently not known why these taxa have lost their MOC systems, all three genera demonstrate extreme specialization of the auditory apparatus for high-frequency (Hipposideros and Rhinolophus) or low-frequency (Spalax) hearing (Bruns 1976a,b; Bruns and Schmieszek 1980; Bruns et al. 1988; Burda et al. 1989; Dannhof and Bruns 1991; Raphael et al. 1991), and may thus be considered atypical models for general mammalian auditory anatomy and function.

ENVIRONMENTAL EVIDENCE: MEASUREMENTS OF AMBIENT NOISE LEVELS

Our literature search revealed 23 sources reporting environmental sound levels under natural or seminatural conditions (Table 2). “Natural” acoustic environments are here defined as environments that lack significant anthropogenic (human-generated) sound sources. It is important to bear in mind that this definition does not preclude the possibility that some of the environmental sound levels reported in our survey were influenced by human activity (e.g., through selective clearing of forests or reduction of species densities). For instance, Table 2 includes sources reporting ambient sound pressure levels in a pasture (Brenowitz 1982a) and a botanical garden (Brown and Schwagmeyer 1984). Given the comparative paucity of descriptions of natural environmental noise, however, we feel that a relatively inclusive standard is warranted.

Table 2.

Environmental noise levels (biotic and abiotic sources)

Environmental noise levels (biotic and abiotic sources)
Source	Location	Date and time	Notes	Ambient noise level
Saby and Thorpe (1946)	Barro Colorado Island and a site near Gamboa, Panama (lowland tropical forest)	24-h cycle	Measurements are the daily range of integrated intensity of ambient noise within two frequency bands: 0–10 and 15–25 kHz. Source includes plots of the spectral distribution of ambient noise from 8 to 25 kHz.	Barro Colorado Island: 0–10 kHz: ~47–~62 dB SPL 15–25 kHz: <45 dB SPL Near Gamboa: 0–10 kHz: ~42–~53 dB SPL 15–25 kHz: <55 dB SPL
Price (1971)	Rural Vancouver Regional District, Canada	Mar–Jun 1971	Measurements were taken on days with low winds and represent the peak ambient noise level (L10).	Day: 58 dB A Night: 53 dB A
EPA (1972)	Grand Canyon North Rim, AZ	24-h cycle	Measurements represent the residual noise level (L90) and were taken in the presence and absence of cricket choruses.	Without cricket chorus: 16 dB A During cricket chorus: 32 dB A
Rosen and Lemon(1974)	Near Montreal and Rockway, Quebec (pond and lake)	May–Jun 1971–1973 19.00–24.00 h	Measurements represent the range of ambient noise levels of 19 evenings in the presence and absence of frog choruses.	Without frog chorus: 24–53 dB SPL During frog chorus: 60–81 dB SPL
Morton (1975)	Panama (lowland tropical habitats: monsoon forest, forest edge, and grassland)	Unknown	Measurements were made at sites chosen for uniformity of habitat and flatness of terrain.	Forest:   0.5 kHz, 23 dB SPL   1 kHz, 20 dB SPL   1.6 kHz, 22 dB SPL   2 kHz, 22 dB SPL   2.5 kHz, 22 dB SPL   3 kHz, 26.5 dB SPL   4 kHz, 31 dB SPL   8 kHz, 38 dB SPL Forest edge:   0.5kHz, 23 dB SPL   1 kHz, 20 dB SPL   2 kHz, 22 dB SPL   4 kHz, 31 dB SPL   8 kHz, 35 dB SPL Grassland:   0.5 kHz, 30 dB SPL   1 kHz, 20 dB SPL   2 kHz, 20 dB SPL   4 kHz, 20 dB SPL   8 kHz, 20 dB SPL
Luz and Smith (1976)	Otero Mesa, New Mexico	Apr 1975 07.30 h	Measurements made in 6- to 12- knot winds	36–40 dB A
Waser and Waser(1977)	Edea, Cameroun and Kibale, Uganda (tropical forest)	Edea: 06.00–21.00 h Kibale: 24-h cycle	Measurements (C-weighted) represent the range of ambient noise from 0.05 to 7.5 kHz over the period sampled. Peak noise levels at Edea occurred in the presence of cicada and orthopteran choruses.	Edea: ~55–~80 dB SPL Kibale: ~40–~50 dB SPL
Tuttle and Ryan(1982)	Barro Colorado Island and Bohio, Panama (lowland tropical forest)	Jan–Apr 1981	Measurements made 3 cm above the ground near streams, in both the presence and the absence of frog choruses at 3 sites.	Site 1: 57–71 dB SPL Site 2: 53–57 dB SPL Site 3: 51–66 dB SPL
Narins (1982)	Luquillo Mountains, Caribbean National Forest, eastern Puerto Rico (tropical rainforest)	May–Jun 1980 24-h cycle	Measurements represent the range of biotic noise over a 24-h cycle, quantified using octave filters centered at 1 and 2 kHz (centered on components of the frog’s call). Peak SPL levels occurred in the presence of nocturnal frog choruses.	Octave band centered at 1 kHz: ~48–~80 dB SPL Octav band centered at 2 kHz: ~48–92dB SPL
Brenowitz (1982a); see also Brenowitz (1982b)	Near Ithaca, NY (upland field)	1980–1981 05.20–20.20 h	Measurements represent the daily range of mean ambient noise levels measured on a linear unweighted scale. Source includes plots of the spectral distribution of ambient wind-generated noise from 0 to 10 kHz.	48–76 dB SPL
Schwartz and Wells 1983)	Gamboa, Panama (flooded field)	Jun–Aug 1981–1982 19.30–23.30 h	Measurements made during a frog chorus.	75–80 dB SPL
Brown and Schwagmeyer (1984)	Matthaei Botanical Gardens, MI, and a field near the University of Missouri, Columbia	10.00–15.00 h	Measurements are the average of 30 random samples analyzed in octave bands from 0.125 to 16 kHz. Source includes plots of the spectral distribution of ambient noise from 0.125 to 16 kHz.	Maximum (0.125 kHz): ~60 dB SPL Minimum (16 kHz): ~25 dB SPL
Brenowitz et al. 1984)	Near Ithaca, NY (shallow ponds)	Apr–Jun	Measurements (A-weighted) were made at two sites with a minimum of 25 male spring peeper tree frogs.	Without frog chorus: 33–52 dB A During frog chorus: 64–82 dB A
Ryan and Brenowitz 1985)	Parque Nacional Soberano, Panama (forest and grassland)	Jul 1983 06.00–08.00 h	Measurements were made near the ground and 1.5 m above the ground for a period of several minutes and represent the average maximum rms sound pressure level. Source includes plots of the spectral distribution of ambient noise from 0 to 10 kHz in two habitats at 06.00, 07.00, and 08.00 h.	Forest: 64 dB SPL Grassland: 55 dB SPL
Waser and Brown (1986); (see also Brown and Waser 1984; Brown and Waser 1984)	Kibale, Uganda (rainforest) Kakamega, Kenya (rainforest) Mchelelo, Uganda (riverine forest and savanna)	Kibale: Sept 1974 Kakamega: July 1981 Mchelelo: Aug 1981 06.00–18.00 h	Measurements are the average of samples at least 30 s long taken from a minimum of four locations within each habitat. Source includes plots of the spectral distribution of ambient noise from 0 to 10 kHz in three habitats.	Rainforest:   0.063 kHz, 40 dB SPL   0.125 kHz, 31 dB SPL   0.2 kHz, 27 dB SPL   0.5 kHz, 25 dB SPL   1 kHz, 28 dB SPL   2 kHz, 32 dB SPL   4 kHz, 34 dB SPL Riverine forest:   0.063 kHz, 40 dB SPL   0.125 kHz, 35 dB SPL   0.2 kHz, 34 dB SPL   0.5 kHz, 33 dB SPL   1 kHz, 31 dB SPL   2 kHz, 30 dB SPL   4 kHz, 33 dB SPL Savanna:   0.063 kHz, 33 dB SPL   0.125 kHz, 28 dB SPL   0.2 kHz, 26 dB SPL   0.5 kHz, 23 dB SPL   1 kHz, 24 dB SPL   2 kHz, 23 dB SPL   4 kHz, 25 dB SPL
Odendaal et al. (1986)	Flinders Ranges, South Australia	May–Nov	Measurements were made along slow to fast-moving creeks at seven sites in the presence and absence of frog choruses.	Maximum noise level without frog chorus: 40–50 dB SPL Minimum noise level during frog chorus: 57–63.3 dB SPL
Gerhardt and Klump (1988)	Near Savannah, Georgia (pond)	Unknown	Measurements (C-weighted) were made 10 m from the edge of a pond containing more than 100 calling male green tree frogs.	84–87 dB SPL
Römer et al. (1989)	Near Perth, Western Australia (woodland)	Dec 1986 16.00–22.00 h	Measurements were made 1 m above ground at two sites during a bushcricket chorus. Source includes plot of the spectral distribution of ambient noise from 0 to 40 kHz.	Site 1: ~50–60 dB SPL Site 2: ~40 dB SPL
Páez et al. (1993)	La Selva, Costa Rica (tropical forest)	Aug 1991 07.00–11.00 h	Measurements were made in the arboretum of the La Selva Biological Station both in the absence of cicada calls and in the presence of a full cicada chorus.	No cicadas: <60 dB SPL Cicadas calling: 60–86 dB SPL
Reiman and Terhune (1993)	Bay of Fundy, Canada (nearshore coastal waters)	May–Jul 1992 09.00–15.00 h	Measurements were made 9 cm above ocean’s surface on calm days (wind <5 km/h) with no rain.	0.5 kHz, 15 dB SPL 1 kHz, 12 dB SPL 2 kHz, 9dB SPL 4 kHz, 2 dB SPL
NPS (1995)	Grand Canyon National Park, AZ Hawaii Volcanoes National Park and Haleakala National Park, HI	Summer and fall 1992	Measurements represent the range of ambient noise recorded at several sites within each park. The upper limit represents the ambient noise level that was exceeded only 5% of the time at the noisiest site, while the lower limit represents the ambient noise that was exceeded 95% of the time at the quietest site.	Grand Canyon National Park (15 sites near river): ~15–~58 dB A Grand Canyon National Park (8 sites at rim): ~10–~53 dB A Hawaii Volcanoes National Park (4 sites):14–~43 dB A Haleakala National Park (4 sites): ~8–~30 dB A
Penna and Solís (1998)	Southern Chile (temperate marsh and bog)	Nov and Dec 1990–1992 07.30–19.00 h	Measurements are peak noise levels that were recorded at ground level during calm days only and in the absence of frog calls.	Marsh: 62.6 dB SPL Bog1: 59.3 dB SPL Bog2: 50.8 dB SPL Bog3: 74.9 dB SPL
Aubin and Jouventin (1998)	Possession Island, Southern Indian Ocean (shoreline)	Dec 1995–Jan 1996 11.00–12.00 h	Measurements were made 2 m from edge of king penguin colony on calm days (wind <10 km/h). Source includes plot of the spectral distribution of ambient noise from 0 to 8 kHz	74.1 ± 3.4 dB SPL

Only publications reporting absolute noise levels relative to a stated reference intensity were considered for this analysis. Most of these sources (Price 1971; EPA 1972; Rosen and Lemon 1974; Luz and Smith 1976; Waser and Waser 1977; Brenowitz 1982a,b; Tuttle and Ryan 1982; Schwartz and Wells 1983; Brenowitz et al. 1984; Ryan and Brenowitz 1985; Odendall et al. 1986; Gerhardt and Klump 1988; Römer et al. 1989; Páez et al. 1993; National Park Service 1995; Aubin and Jouventin 1998; Penna and Solís 1998) present frequency-averaged environmental noise levels in dB A or dB SPL. Six sources, however, present absolute noise intensity levels in dB SPL within multiple frequency ranges (Saby and Thorpe 1946; Morton 1975; Narins 1982; Brown and Schwagmeyer 1984; Waser and Brown 1986; Reiman and Terhune 1993). Of this latter group, the numeric values for noise levels provided by Morton (1975), Waser and Brown (1986), and Reiman and Terhune (1993), as well as the maximum noise levels reported by Narins (1982) within octave bands centered at 1 kHz (~79 dB SPL) and 2 kHz (~92 dB SPL), are replotted in Figure 1. The environmental noise levels shown in Figure 1 thus provide a representative cross-section of the total data set shown in Table 2. The noise levels reported by Reiman and Terhune (1993) represent primarily abiotic noise in a calm, nearshore marine setting. By contrast, Morton (1975) and Waser and Brown (1986) document noise levels in tropical forests and grasslands that are rich in biotic noise generated by birds and insects. Narins’ (1982) peak noise levels across a narrower frequency range represent the highest naturally occurring noise measurements in Table 2.

Figure 1.

Diagrammatic plot of naturally occurring noise conditions and stimulus parameters employed in experimental studies of MOC-mediated protection from acoustic trauma. Natural environmental noise levels are plotted (open circles) for four studies giving absolute acoustic measurements across a range of frequencies (Morton 1975; Narins 1982; Waser and Brown 1986; Reiman and Terhune 1993; see text and Table 2 for description). Frequency and intensity parameters that have been employed in studies of MOC-mediated protection studies, from Table 3, are plotted as those sinusoidal stimulus conditions that yielded a protective effect (open diamonds); those sinusoidal stimulus conditions that failed to demonstrate a protective effect (open squares); the noise band exposures against which the MOC demonstrated a protective effect (solid lines), and the noise band conditions against which the MOC had no apparent protective effect (dashed lines). All noise bands (for both environmental noise and protection studies) are plotted as overall dB SPL vs. total frequency range because insufficient details were provided to plot these acoustic conditions in terms of spectral level.

The recordings of natural acoustic environments shown in Table 2 were made under a wide variety of environmental conditions and document ambient environmental noise generated by both biotic and abiotic factors. In spite of this diversity of environmental conditions (e.g., ground cover, vegetation, species assemblages, etc.) and recording techniques, the sources in Table 2 suggest that the great majority of natural acoustic environments are characterized by relatively modest (<70 dB SPL) ambient noise levels. Primary sources of abiotic noise include wind, rain, and wave action. Most wind-generated noise has a characteristic spectrum, with the dominant power peaks present at low frequencies (below 200–500 Hz; Brenowitz 1982a; Brown and Schwagmeyer 1984; Brown and Waser 1984; Ryan and Brenowitz 1985). Water-generated noise sources have similar low-frequency spectra with peaks that extend to higher frequencies, though virtually all energy is contained at frequencies below 4.5 kHz (cf Tuttle and Ryan 1982). For example, at frequencies above 2.0 kHz, the energy present in any one particular frequency band does not exceed 20 dB SPL in the water-generated noise spectra figured by Tuttle and Ryan (1982).

The most intense sources of natural ambient noise, however, are biotic (Table 2). Significant biotic noise sources include bird-song and frog and insect choruses. Indeed, a number of recordings were made with the intention of documenting the noise levels produced by chorusing frogs (e.g., Narins 1982; Schwartz and Wells 1983; Gerhardt and Klump 1988) and insects (e.g., Römer et al. 1989; Páez et al. 1993). Recordings made in the midst of frog choruses account for most of the noisiest reported environments. As noted previously, Narins (1982) documented the highest peak noise levels (Fig. 1) of any source included in Table 2. Within an octave band centered at 2.0 kHz, Narins reported that noise levels in a Puerto Rican montane rainforest vary from a minimum of ~48 dB SPL to a peak of ~92 dB SPL over a 24-h period. Noise levels within an octave band centered at 1.0 kHz were somewhat lower, ranging from ~48 to ~79 dB SPL. Furthermore, peak sound levels between 1.4 and 2.8 kHz at this locality were maintained near or above 80 dB SPL from 18.00 to 06.00 h. These relatively intense but spectrally restricted noise levels may be directly attributed to the nocturnal calling of leptodactylid tree frogs because the frequency ranges measured by Narins (1982) encompass the most intense frequency components of the frogs’ chorus. The unusually high and sustained noise levels reported by Narins (1982), however, are not typical of all tropical forest sites. For instance, Waser and Brown (1986) found maximum ambient noise levels of only about 40 dB SPL at the rainforest sites of Kibale in Uganda and Kakamega in Kenya. These maximum values for African rainforest sites are comparable to the minimum ambient noise levels reported by Narins (1982) in Puerto Rico. Similarly, Ryan and Brenowitz (1985) reported maximum ambient noise levels of 64 dB SPL at a lowland tropical forest site in Panama.

The unusually high environmental noise levels reported by Narins (1982) seem, therefore, to be the result of the distinctive frog fauna present in the Luquillo Mountains of Puerto Rico rather than a general characteristic of tropical rainforests. Gerhardt and Klump’s (1988) recording of 87 dB SPL peak ambient noise during a chorus of green tree frogs (made in a pond, near Savannah, Georgia) provides further evidence of an association between high ambient noise levels and chorusing frogs rather than any specific environment. Indeed, maximum ambient noise levels reported in the presence of chorusing frogs are often in excess of 70 dB SPL, regardless of location (e.g., 71 dB SPL, Tuttle and Ryan 1982; 80 dB SPL, Schwartz and Wells 1983; 82 dB A, Brenowitz et al. 1984). It is important to bear in mind, however, that in most cases these relatively high sound pressure levels are maintained only within the restricted area (usually a pond or watercourse) near the chorusing frogs. As with all other point sources of noise, the intensity of a localized frog chorus will fall off rapidly with distance (i.e., by at least 6 dB per doubling of the distance due to spherical spreading, with additional attenuation due to physical obstructions in the environment; Brenowitz 1982a,b; Ryan and Brenowitz 1985).

Additional reports of natural acoustic environments with substantial biotic sound levels come from Páez et al. (1993), who recorded in a Costa Rican rainforest during a full cicada chorus (60–86 dB SPL), from Waser and Waser (1977), who documented noise levels of 70–80 dB SPL during a cicada chorus in the Edea coastal forest of Cameroun, and from Aubin and Jouventin (1998), who recorded at the periphery of a colony of king penguins (~74 dB SPL). High peak sound levels were also reported by Brenowitz (1982a), who collected data in a pasture near Ithaca, New York (peak = 76 dB SPL). Brenowitz (1982a) noted, however, that this frequency-averaged measurement may disproportionately reflect the relatively high intensity of wind-generated, low-frequency background noise. Such noise falls partly outside the range of hearing of many mammals and may be of little import in assessing the vulnerability of the inner ear to acoustic trauma. Conclusions based on the data presented in Table 2 may thus be considered conservative because the frequency-averaged measurements of background noise reviewed here are likely to overestimate the danger posed by natural ambient sound pressure levels. Significantly, data from studies for which absolute sound intensity levels were published for specific frequency ranges demonstrate that the ambient noise levels within any specific frequency band rarely exceed 40 dB SPL (Fig. 1).

It is important to note that under extreme environmental conditions, noises greater than about 92 dB SPL (the highest ambient noise level shown in Table 3) probably do occur in nature. Many such instances, however, probably represent sound events that are sufficiently short in duration (e.g., thunder) that they could not activate the “slow” MOC effect that is thought to be responsible for MOC-mediated protection (Liberman and Gao 1995; Reiter and Liberman 1995). Furthermore, if sustained noise levels greater than 92 dB SPL do occur naturally (e.g., perhaps at the bases of large waterfalls or during intense storms), the environmental conditions represented in Table 3 are diverse enough to suggest that any such “extreme” natural sound environments must be very rare and discontinuously distributed in both time and space.

Table 3.

Studies of MOC protection, describing noise exposure conditions and effects of de-efferentation

Studies of MOC protection, describing noise exposure conditions and effects of de-efferentation
Authors	Species	Exposure details	Results	Conclusions of study
Cody and Johnstone (1982)	Guinea pig	10.0 kHz sinusoid, 107 dB SPL for 1 min	TTS to ipsilateral exposure was reduced with contralateral stimulation or contralateral cochlear destruction.	Acoustic activation of the efferent syste might be responsible for reduced threshold shifts.
Handrock and Zeisberg (1982)	Guinea pig	4-kHz octave-band noise, 120 dB SPL for 5 min or 125 dB SPL for 30 min	For 120 dB SPL exposure, there was no effect of de-efferentation on PTS; for 125 dB SPL exposure, de-efferentation resulted in significantly greater PTS after 8 days compared with normal animals.	Results suggest MOC might offer PTS protection from high-SPL, long-duration noise exposures.
Rajan and Johnstone (1983)	Guinea pig	10.0 kHz sinusoid, 97 or 103 dB SPL for 1 min	TTS to monaural exposure was reduced when contralateral stimulation, matched in frequency, was concurrent with exposure. The effect was lost when strychnine was given to block MOC.	MOC action can provide protection from intense noise exposure to cochlea.
Rajan (1988a)	Guinea pig	10.0 kHz sinusoid, 103 dB SPL for 1 min	TTS was reduced with electrical stimulation of COCB at IVth ventricle; protection was blocked by strychnine. COCB protection persisted after cessation of electrical stimulation. Effects were blocked by COCB lesion	COCB action might protect cochlea from intense monaural tone exposure TTS. Persistence of COCB protection is not accomplished in cochlea, but centrally.
Rajan (1988b)	Guinea pig	10.0 kHz sinusoid, 97, 101, 103, or 106 dB SPL for 1 min	TTS at 14 kHz was reduced for highest-level monaural exposure tones in presence of COCB stimulation at IVth ventricle. COCB protection is greater at the highest electrical pulse rates.	COCB protection is graded in effectiveness. Level of MOC protection increases with exposure conditions that produce the largest TTS.
Rajan and Johnstone (1988a)	Guinea pig	10.0 kHz sinusoid, 103 dB SPL for 1 min	TTS was reduced with electrical stimulation of COCB at round window; protection was blocked by strychnine. COCB protection persisted after cessation of electrical stimulation. Effects were blocked by COCB lesion.	COCB acts to protect cochlea from monaural acoustic trauma; COCB protection persists for up to 7 min poststimulation for 1 min COCB stimulation period. Persistent effects are not due to cochlear effects but result from “resetting” of some entral site.
Rajan and Johnstone (1988b)	Guinea pig	10 kHz sinusoid, 97, 101, 103, or 106 dB SPL for 10 s to 30 min	TTS was reduced with electrical stimulation of COCB at round window; protection was blocked by strychnine. The greater the potential damage of exposure, the greater the COCB protection; increases in COCB stimulation rate increased protection at mid- and high TTS exposures.	COCB acts to protect cochlea against TTS. Protection level is graded, increases with TTS level, increases with COCB stimulation rate/level.
Rajan and Johnstone (1988c)	Guinea pig	10 kHz sinusoid, 97, 101, 103, 106, or 110 dB SPL for 30 s or 1 min	TTS reduced with low-level contralateral acoustic stimulation; protection blocked by OCB lesion. The greater the potential damage of exposure, the greater the protection; increases in acoustic stimulation level increased protection at mid- and high TTS exposures. Protection was evident only with TTS level over 25 dB. Contralateral-induced protection persists.	COCB stimulated by contralateral sound acts to protect cochlea against TTS in a manner similar to that seen with electrical stimulation of COCB at IVth ventricle or round window. Protection persists for 5–7 min by activation of “central” site, which antidromically stimulates cochlea, rather than persistence acting in cochlea.
Hildesheimer et al. (1990)	Guinea pig	4.0 kHz sinusoid, 120 dB SPL for 20 min	De-efferentation or destruction of contralateral cochlea resulted in statistically less TTS. De-efferentation alone did not affect TTS. Destruction of contralateral ear resulted in greater TTS in de-efferented ear.	Data suggest no consistent efferent protection. Authors suggest inconsistencies with other studies showing protection may be due to specifics of experimental/stimulus conditions.
Liberman (1991)	Cat	6.0 kHz sinusoid, 100 dB SPL for 10 min. Exposure tone intensities were balanced in the two ears (intensity-balanced binaural exposures)	Within subjects, no differences were seen in comparisons of the PTS in normal and de-efferented ears. There was no protective effect of direct electrical stimulation of the efferents on floor of IVth ventricle.	In contrast with guinea pig studies, these studies suggest efferents are not involved in protecting the ear from noise trauma and suggests that differences in findings in other studies may be due to species differences, contribution of middle ear muscles, and/or cochlear blood flow changes.
Patuzzi and Thompson (1991)	Guinea pig	10.0 kHz sinusoid, 115 dB SPL for 60 or 150 s	TTS in CM and CAP measures was reduced in presence of low-level contralateral acoustic stimulation. This effect was lost when the MOC is sectioned. Interanimal variability in TTS was reduced following MOC lesions.	MOCs offer protection from acoustic trauma. Reductions in interanimal variability suggests MOCs have varying tonic effects on normal cochlear function across subjects.
Takeyama et al. (1992)	Guinea pig	2.0 kHz sinusoid, 110–130 dB SPL for 3–30 min	With electrical stimulation of COCB, TTS was reduced. Reduction in TTS, however, was evident only with TTS of >50–55 dB; with TTS <50 dB, there was no benefit of COCB stimulation.	Electrical stimulation of COCB can elicit protective mechanism for high-level acoustic trauma.
Liberman and Gao (1995)	Guinea pig	Narrowband noise (500 Hz bandwidth, centered at 10.0 kHz), 109 or 112 dB SPL for 2 h	109 dB SPL: No statistical differences in PTS or hair cell/stereocilia damage between normal and de-efferented ears. 112 dB SPL: Small statistical PTS difference, but no histologic differences between normal and de-efferented ears.	For conditions tested, there was no significant protective effect of MOC on CAP PTS or resulting hair cell damage for these relatively long-duration exposures. Given site of damage to the 112 dB SPL, they suggest the PTS protection observed is due to “slow” efferent effect.
Rajan (1995a)	Cat	3.0, 7.0, or 11.0 kHz sinusoids at 100 dB SPL for 10 min	Unilateral COCB cuts produced greatest TTS in the de-efferented ear for 11.0 kHz binaural exposures but not for 3.0 kHz or monaural exposures. MEMs had no effect on TTS.	OCB protection effects comparable in cats and guinea pigs. MOC protection might be frequency dependent.
Rajan (1995b)	Cat	3.0, 5.0, 7.0, 11.0, 15.0, 20.0 kHz sinusoids at 100–106 dB SPL for 7 to 40 min	The magnitude of the TTS was frequency and intensity dependent and required binaural exposure. The magnitude of protection increased with exposure intensity.	The magnitude of OCB protection to binaural exposures are frequency and intensity dependent. Across frequencies, protection was comparable for different exposure intensities that would produce comparable damage.
Reiter and Liberman (1995)	Guinea pig	6.0, 8.0, and 10.0 kHz sinusoids at 104–118 dB SPL for 1–5 min	OC is activated by electrical stimulation at IVth ventricle. Protection evident at 8.0 and 10.0 kHz for 1–2 min exposures. Protective effect is lost when OC stimulation preceded exposure.	Circumstantial evidence that protection occurs at 8.0 kHz and above, where “slow” efferent effects are observed, and not at 6.0 kHz, where “fast” OC effects are apparent, suggests protection is based on “slow” OC response.
Rajan (1996)	Cat	11.0 kHz sinusoid at 10 dB SPL for 10 min	Magnitude of OCB-mediated protection was unchanged over extended recording intervals (~30 h).	Because OCB-mediated protection did not change over time, but COCB contralateral suppression effects have been shown in some studies to change with time, OCB protection is mediated by a different efferent subgroup.
Zheng et al. (1997)	Chinchilla	105 dB SPL, broadband noise, for 6 h. Noise band “shaped” to produce “flat” hearing loss	Following noise exposure, de-efferented ears showed significant depression of DPOAE amplitudes and I/O functions compared with control and sham ears. There were no significant differences in CM amplitudes, I/O functions, or OHC loss following acoustic trauma between control and de-efferented ears.	Authors suggest data indicate that de-efferentation increases susceptibility to acoustic trauma. With de-efferentation, susceptibility to noise trauma is evident at low as well as high frequencies.
Rajan (2000)	Cat	13.0 kHz sinusoid at 100 dB SPL for 15 min	In the absence of efferents, moderate noise increases acoustic trauma to exposure tone. In normal ear, added noise increases efferent protection.	Author suggests added moderate noise activates efferents that are not otherwise stimulated by 100 dB SPL binaural tones, thus increasing efferent protection. In a de-efferented ear, the otherwise harmless noise exacerbates the TTS caused by the tonal exposure.
Zheng et al. (2000)	Chinchilla	150 dB pSPL, 100 impulses, 50 s total duration	No difference in TTS or loss of OHCs between control and de-efferented ears. De-efferentation resulted in a significantly greater PTS and loss of IHCs.	OHC susceptibility to acoustic trauma unaffected by de-efferentation. Significant increase in PTS and greater loss of IHCs following de-efferentation suggests MOC might play a role in protecting ear from noise trauma. It is unclear, however, why de-efferentation affects IHCs and not OHCs.
Rajan (2001a)	Cat	11 kHz sinusoid at 100 dB SPL for 10 min	Ipsilateral TTS is reduced in the unilaterally exposed (normal) ear when there is a partial unilateral hearing loss in the contralateral ear, due to “chronic resetting of noise susceptibility.” In cases of partial unilateral hearing loss, binaural exposure exacerbates the TTS. With total unilateral hearing loss, TTS in the normal ear was reduced.	The effects of intense sound exposure are different in bilaterally normal ears and in conditions of unilateral hearing loss. They also suggest CMOCs and UMOCS may exert different effects at the OHCs.
Rajan (2001c)	Cat	Narrowband noise 1.0–6.0 kHz (40 min) or 8.0–13.0 kHz (15 min) at 100 dB SPL	For both noise bands, the crossed-MOC offered small protection against noise trauma at frequencies within the exposure noise band. At frequencies above the noise band, it exacerbated the TTS. The uncrossed MOC showed no protective effects within the 1.0–6.0 kHz noise band, but showed a small protection for the frequencies within the 8–13.0 kHz noise band. The uncrossed MOC protected against the crossed-MOC-induced-high-side frequency increased susceptibility.	The crossed and uncrossed MOC subsystems interact in complex ways to affect the susceptibility of the cochlea to noise trauma and may form the basis for a contrast-enhancement mechanism to increase the detection of tones in noise.

STIMULUS CONDITIONS NECESSARY TO DEMONSTRATE MOC-BASED PROTECTION

Criteria for inclusion of protection studies

A literature search of studies explicitly investigating the role of the efferent tracts in protecting the ear from trauma recovered a large number of primary sources. Table 3 summarizes the findings of the 22 protection studies that form the basis for our subsequent discussion and analysis. The traumatizing stimulus conditions employed in these studies are also plotted in Figure 1, irrespective of their duration (the effects of exposure duration are considered below).

Three experimental studies were excluded from this analysis. Two studies (Horner et al. 1998, 2001) are not considered here because they blocked MOC efferent function pharmacologically rather than through surgical cutting, and may therefore have resulted in deactivation of additional systems that could affect auditory thresholds (e.g., the sympathetic nervous system). A third study, by Chen et al. (2000), is also excluded because the methods and data presented were confusing and inconsistent with the conclusions given by the authors.

Lastly, although there is clearly some overlap with the studies reviewed in this work, we will not consider here the effect known as “conditioning,” “toughening,” or “priming” (cf. Rajan and Johnstone 1988a,c; Rajan 2001b). In the conditioning paradigm, exposure to one intense sound can reduce the susceptibility of the ear to subsequent intense noise exposures (Canlon et al. 1988). This effect, however, has recently been shown to be unrelated to MOC efferent action (Yamasoba and Dolan 1998; Yoshida et al. 1999; Yoshida and Liberman 2000).

Summary of MOC protection studies

Table 3 shows that most of the MOC efferent protection studies reviewed here (17 of 22) used high-level pure tone stimulation to traumatize the ear. Among these “pure tone” studies, the stimulus conditions in which a protective effect was demonstrated (Fig. 1, open diamonds) ranged in frequency from 2.0 to 20.0 kHz and in intensity from 100 to 150 dB SPL (peak level). Surprisingly, the stimulus conditions that failed to demonstrate MOC protection in similar studies (Fig. 1, open squares) are roughly comparable, ranging from 2.0 to 10.0 kHz and from 97 to 130 dB SPL. The highly analytic, sinusoidal signals used in these experiments differ radically from the complex frequency spectra found in natural environmental noise (Ryan and Brenowitz 1985; Aubin and Jouventin 1998), although some animal vocalizations, such as the biosonar signals of bats (cf. Griffin 1958) and nonhuman primate calls (cf. Green 1975; Seyfarth et al. 1980), do consist of frequency-modulated signals that are relatively tonal in nature.

Broadband noise stimuli, which more closely approximate the spectral complexity of natural environmental noise, have been used in four protection studies. First, Handrock and Zeisberg (1982) studied the ability of octave-band noise centered at 4.0 kHz to elicit MOC protection in guinea pigs. In this study, the MOC system appeared to reduce noise trauma at 125 dB SPL but not at 120 dB SPL exposure. Second, Liberman and Gao (1995) studied the effects of narrowband (500 Hz bandwidth) noise centered at 10.0 kHz on compound action potential thresholds in guinea pigs. Ears that had been surgically de- efferented had greater threshold shifts than did normal ears when exposed to 112 dB SPL noise, but there was no difference in threshold shifts when the ears were exposed to 109 dB SPL noise. Third, Zheng et al. (1997) compared the effects of 105 dB SPL broadband noise exposure, shaped to produce a flat threshold shift, in chinchillas with normal and surgically de-efferented ears. Evoked electrophysiological potentials showed no differences in normal and de-efferented ears, although otoacoustic emission amplitudes and input/output measures (measures of outer hair cell function) were depressed in de-efferented ears as compared with normal ears. Zheng et al. concluded that the MOC system decreases the susceptibility of the cochlea to intense noise. Fourth, Rajan (2001c) exposed cats to 100 dB SPL narrowband noise at either 1.0–6.0 kHz (40 min) or 8–13.0 kHz (15 min). To determine the relative contribution of the crossed and uncrossed MOC tracts to the protective phenomenon, Rajan compared threshold shifts following noise exposure in (1) normal animals and (2) animals in which the different MOC subgroups had been lesioned. The comparisons showed a complex pattern of responses where, depending on the frequency of the temporary threshold shift (TTS) relative to the exposing noise band, the MOC tracts could either protect or exacerbate the threshold shift. The net affect of the MOC action, however, was protective.

One additional study, by Zheng et al. (2000), used extremely high-level [150 dB (peak level) SPL] impulse noise to damage the cochleas of chinchillas. The authors described a relative increase in inner hair cell damage with de-efferentation but no difference in outer hair cell survival following impulse noise exposure. Although these findings are difficult to explain in terms of known MOC innervation patterns and physiology, Zheng et al. (2000) concluded that their data were consistent with the MOC functioning to reduce susceptibility to intense noise exposures.

DISCUSSION: THE MOC SYSTEM DID NOT EVOLVE FOR A PROTECTIVE FUNCTION

Comparison of natural environmental noise and experimental stimuli

Natural selection occurs as a result of the interaction between an organism’s phenotype and a given environmental parameter (sensu lato). Such environmental parameters (e.g., predation, ambient temperature, intraspecific competition, etc.) lead to genetic and morphological changes within populations by favoring differential survival and/or reproductive success among variant phenotypes. In other words, evolution by natural selection is dependent upon environmental effects on organismal fitness. In order to support the hypothesis that a specific environmental condition is either detrimental or beneficial to an organism’s fitness, one must first demonstrate that such conditions are indeed present in the organism’s natural environment.

The protection hypothesis proposes that the mammalian MOC system has evolved to insulate the organ of Corti from potentially damaging environmental noise. Even a cursory comparison of the data presented in Tables 2 and 3 and represented graphically in Figure 1, however, shows that the intense sound levels (100–150 dB SPL) used to demonstrate MOC-based protection under experimental conditions are higher (and in most cases substantially higher) than the ambient noise levels in all documented natural acoustic environments. This finding is contrary to the expectations of the protection hypothesis and strongly suggests that the experimental conditions necessary to evoke MOC-mediated protection of the cochlea have no analog in nature. Furthermore, while relatively intense ambient noise levels of about 80–90 dB SPL do occur naturally, these exceptional noise conditions are geographically rare and discontinuously distributed. By contrast, comparative studies of mammalian auditory systems suggest that MOC cochlear efferents are shared by the great majority of placental and marsupial species, which inhabit a diverse range of natural habitats. The fact that a functional MOC system has evidently been retained by most mammalian lineages for at least 175 million years despite considerable ecological differences between species suggests that the selective factors that have maintained the mammalian MOC system must be nearly universal in natural acoustic environments. Relatively high-intensity natural ambient noise (~80–90 dB SPL) clearly does not fit this criterion.

Stimulus intensity and duration

Based upon the foregoing considerations, it is tempting to reject the protection hypothesis outright. A number of the studies listed in Table 3, however, show protective effects at the lowest sound levels tested, so the critical question remains: What are the lowest sound intensities at which MOC-mediated protection occurs? The answer to this question is likely influenced by the species under consideration due to significant differences in absolute hearing thresholds among mammals (Fay 1988). Nonetheless, Rajan and Johnstone (1988c) have provided evidence that MOC protective effects are elicited in guinea pigs only when the traumatizing acoustic stimulus produces a temporary threshold shift greater than 25 dB, and that the magnitude of the protective effect is directly proportional to the intensity of traumatic stimulus. These results suggest that MOC-mediated protection occurs only in response to very intense acoustic overexposure. Furthermore, in the relatively few species that have been well studied (i.e., cats, guinea pigs, and chinchillas; Table 3), lower intensity thresholds for MOC protection appear to be strongly frequency dependent. For instance, in guinea pigs, Handrock and Zeisberg (1982) and Hildesheimer et al. (1990) found no MOC-mediated protection for 4.0 kHz sinusoidal or octave-band noise at 120 dB SPL, whereas Rajan (1988a,b) and Rajan and Johnstone (1983, 1988a,b,c) have consistently demonstrated MOC-mediated protection for 10 kHz tones of only ~100 dB SPL. Similarly, Rajan (1995b) has shown that the ability to evoke MOC-mediated protective effects at different frequencies is strongly dependent upon both the intensity and the duration of the traumatizing stimulus. In that analysis, lower-intensity and lower-duration thresholds for activation of MOC protection in cats were approximately 100 dB SPL for 15 min at 7 kHz compared with 106 dB SPL for 40 min at 3 kHz (Rajan 1995b).

Because the ability of noise to produce acoustic trauma is dependent on both the intensity and the duration of the traumatizing exposure, any assessment of selective environmental influences on MOC evolution must consider the duration of intense noise sources. The majority of the studies shown in Table 3 exposed test subjects to relatively short-duration stimuli, ranging from about 1 min to 2 h. Within these narrow exposure parameters and across species, experimentally demonstrated lower-intensity thresholds for MOC-mediated protection are of relatively high intensity. For instance, in guinea pigs the lowest intensities required to activate MOC protection with short-duration stimuli are between 120 and 125 dB SPL at 4 kHz (Handrock and Zeisberg 1982) and between 109 and 112 dB SPL at 10.0 kHz (500 Hz-wide noise band; Liberman and Gao 1995). Similarly, in cats, short-duration stimuli of 100–106 dB SPL can activate MOC protection for frequencies ranging between 3 and 20 kHz, while broadband noise (0.5-40 kHz) of 80 dB SPL causes no acoustic trauma in either de-efferented or efferent-intact ears (Rajan 2000). These data suggest that the lower-intensity threshold for activation of MOC-based protection by short-duration traumatizing stimuli lies somewhere between 80 and 100 dB SPL for most of the cat’s hearing range. Interestingly, for both cats and guinea pigs, the protection threshold is 100–120 dB above the animal’s respective absolute threshold (Fay 1988) at any given frequency.

While most records of environmental noise have intensities well below the lower-intensity thresholds required for MOC protection by short-duration stimuli (Fig. 1), the relatively high ambient noise levels in some natural acoustic environments have considerably longer durations than the traumatizing noise exposures used in most MOC protection studies (Table 3). For instance, at one woodland site in western Australia, Römer et al. (1989) reported ambient noise levels sustained slightly above 60 dB SPL for at least 3 h due to chorusing bushcrickets (Mygalopsis). Similarly, in Kibale, Uganda, Waser and Waser (1977) contrasted relatively low ambient noise levels in the forest canopy (between 40 and 50 dB SPL across a 24-h cycle), with noise levels near the ground, which may be sustained between about 65 and 75 dB SPL for approximately 8 h in the presence of chorusing cicadas. Narins’ (1982) recordings of biotic noise in the montane rainforests of Puerto Rico, however, provide a record of not only the most intense known natural noise levels, but also the longest sustained levels of intense noise. For nearly 12 h each evening, noise levels between 1.4 and 2.8 kHz ranged from slightly below 80 dB SPL to slightly above 90 dB SPL as a result of chorusing frogs. While Narins’ (1982) measurements are unique in terms of their intensity and duration, it is important to bear in mind that these data represent the average peak sound levels measured over 10-s intervals and sample only the narrow frequency range that encompasses the most intense component of the frog chorus.

These data on sustained noise in natural environments raise the question of whether noise levels that are of lower intensity but longer duration than the experimental conditions summarized in Table 3 may activate the protective effects of the MOC system. Unfortunately, very few studies of MOC protection have been carried out at moderate sound intensities of longer duration. This question is relevant to studies of MOC evolution because the most extreme natural noise levels (e.g., 80–90 dB SPL caused by chorusing frogs and insects) shown in Table 3 approach levels that could potentially result in permanent acoustic trauma for some mammals with intact MOC efferent systems. In chinchillas, for example, a number of studies have demonstrated susceptibility to permanent threshold shifts (PTS) as a result of long-term (6–150 days continuous), moderate-intensity (82–95 dB SPL) noise exposure (e.g., Mills 1973; Ward et al. 1981; Bohne et al. 1987; Clark et al. 1987). Because of their comparative susceptibility to acoustic trauma (e.g., Mitchell 1976; Décory et al. 1992), chinchillas may not represent the best general model for the vulnerability of the mammalian auditory system. Thus, any conclusions based upon chinchillas can be regarded as conservative.

In the experimental design that perhaps best approximates an extreme natural noise environment, Bohne et al. (1987) exposed chinchillas to 4 kHz octave-band noise at 80–86 dB SPL for 6 h per day over a 36-day period. Under these test conditions, many test animals (36% at 80 dB SPL; 50% at 86 dB SPL) showed evidence of high-frequency lesions of the organ of Corti at the end of the experiment. Similarly, Mills (1973) provided behavioral evidence of moderate PTS (8–13 dB) in chinchillas exposed to continuous 4.0 kHz octave-band noise at 86 dB SPL for 9 days. Chinchillas exposed to 80 dB SPL noise under the same experimental design, however, showed no evidence of PTS. These data suggest that 80 dB SPL is probably near the lower limit at which PTS could be expected to occur under natural conditions, since permanent acoustic trauma due to lower sound levels would likely require exposure durations that are not found in any natural acoustic environment. Because sustained noise levels significantly greater than 80 dB SPL are very rare in nature, we suggest that most natural acoustic environments would probably not cause permanent acoustic trauma to chinchillas and, by extension, most other mammals. Even if some unusual natural acoustic environments (e.g., the Luquillo Mountains of Puerto Rico; Narins 1982) have noise intensities that could potentially traumatize the cochleas of MOC-intact animals, it nevertheless remains clear that the stimulus conditions known to elicit MOC protection in experimental settings differ substantially from the noise characteristics of all natural acoustic environments.

The effects of internally generated noise

This review has thus far considered only the external acoustic environment, although several studies have demonstrated that the medial efferent system can have a significant effect on neural responses to internally generated sounds (Kawase and Liberman 1993; Kawase et al. 1993; Cazals and Huang 1996; Popelár et al. 1997; Lima da Costa et al. 1997). Given the extreme sensitivity of the mammalian auditory receptor, the cochlea responds to internal acoustic events created by blood circulation, heart contractions, respiration, body movements, and chewing. The acoustic energy for these signals, however, is low in frequency and intensity (cf. Cazals and Huang 1996; Lima da Costa et al. 1997), and the cochlear response to these signals might represent a part of the measured “spontaneous activity” of the auditory nerve (Guinan and Gifford 1988; Cazals and Huang 1996). Gnathosonic measures of the sound generated by normal dental occlusion shows that virtually all spectral energy is found in bands below 400 Hz, with the majority being present between 50 and 150 Hz (Hedzelek and Hornowski 1998; Sano et al. 2002). These findings suggest that chewing sounds are unlikely to have a significant deleterious impact on higher-frequency thresholds (i.e., at frequencies where MOC efferents are present in the cochlea).

Likewise, it is theoretically possible that the MOC system could have evolved as a protective mechanism to counteract the deleterious effects of an animal’s own intense vocalizations. While a detailed treatment of this possibility is outside the scope of this review, we feel that this scenario is unlikely for several reasons. First, the mammalian auditory system is already known to exhibit a means of reducing the effects of internally produced vocalizations in the form of the middle ear reflex. The middle ear reflex is activated by vocalizations and/or speech (Carmel and Starr 1963; Henson 1965) and can produce a significant attenuation of an auditory signal (i.e., by as much as 10–30 dB) before it can be transmitted to the cochlea.

Second, there is little evidence for correspondence between the frequency of an animal’s vocalizations and patterns of MOC innervation of the organ of Corti. For instance, in many echolocating bats (where ultrasonic pulses reach >120 dB SPL at ~50 kHz), MOC innervation is relatively uniform throughout the organ of Corti (Griffin 1958; Henson 1965). If the MOC system was necessary for protection from the intense vocalizations produced by these species, then greater MOC innervation at the acoustic fovea (which includes the region of the basilar membrane responsible for transducing the dominant frequency of the vocalization) would be expected.

Third, the ability to produce intense vocalizations is not always associated with the presence of a functional MOC efferent system. Of the three genera of mammals currently known to lack an MOC system, two are microchiropteran bats (Hipposideros and Rhinolophus) that produce extremely high-intensity vocalizations (>120 dB SPL) like many other microchiropterans. It therefore seems unlikely that MOC innervation of the cochlea would have been lost in these two genera if the MOC system plays a role in protecting the inner ear from trauma caused by high-intensity vocalizations.

Finally, some species that are known to have a highly developed MOC system do not produce intense vocalizations. For example, the vocal repertoire of domestic cats appears rather limited and may function primarily between conspecifics at close range. High-intensity calls that might serve to group distant conspecifics seem to be entirely lacking (Wemmer and Scow 1977).

If not protection, why did the MOC system evolve?

The primary goal of this article has been to answer one question: Did the MOC system evolve as a mechanism to protect the cochlea from acoustic trauma caused by high-intensity natural environmental noise? Given the results of our analysis discussed above, the answer can only be “no.” The substantial MOC protection literature (Table 3), however, clearly demonstrates that destruction of the MOC system increases the cochlea’s susceptibility to acoustic trauma from very high-intensity tones under experimental conditions. There can be little doubt that this protective effect is real, given the control and repeatability of the supporting data. How then can these data be reconciled with our conclusions?

The explanation for the repeated protection finding can be found in the fact that the action of the MOC system is suppressive in nature (Fex 1967; Konishi and Slepian 1970; Wiederhold and Kiang 1970; Buño 1978; Mountain 1980; Siegel and Kim 1982; Liberman 1989; Warren and Liberman 1989; Kawase and Liberman 1993; Kawase et al. 1993; Cazals and Huang 1996; Lima da Costa et al. 1997; Nuttall et al. 1997). In general, the magnitude of the suppressive action of MOC efferents on the various cochlear responses is proportional to the intensity of the stimulus (whether acoustic or electric) activating the MOC system (cf. Warren and Liberman 1989). Importantly, the magnitude of MOC-mediated suppression increases with the level of afferent neural activity (Guinan and Stankovic 1996). Guinan and Stankovic (1996) have shown that MOC activity can produce a reduction, in the largest case, in single-fiber discharge rate equivalent to a 50 dB attenuation of the input stimulus at BF. The attenuation, which was greatest in low-spontaneous-rate fibers, increased to stimulation levels of 50–75 dB SPL, then decreased rapidly with further increases in stimulation. In the present context, assuming that MOC activity elicited by sound is at least qualitatively similar to that elicited by electrical stimulation, MOC action would have the net effect of reducing the level of the intense noise exposure, thereby reducing the resulting damage.

One significant limitation of most previous investigations of the MOC efferent system is the failure to distinguish between the actual biological role of a system (i.e., the purpose for which the system evolved) and the performance of the system in a strictly controlled experimental context. Most experimental studies of the MOC system refer only to its “function” (e.g., Maison and Liberman 2000) and do not consider the actual selective variables that may have been involved in the evolution of the MOC system. From the perspective of evolutionary biology, “function” is an imprecise term that refers to the myriad roles that may be played by a system in a variety of contexts. As noted above, in order to help delineate the biological role of a system, it is first necessary to determine whether the stimulus conditions necessary to evoke a specific function are routinely encountered in nature. In the case of the protection hypothesis, most of the supporting evidence for protection (Table 3) clearly fails this test in light of the cumulative evidence (Table 2) that natural acoustic environments do not demonstrate sustained levels of noise that are sufficiently intense to activate experimentally demonstrated MOC protective effects. “Protective” effects thought to be mediated by MOC action (Table 3) may therefore represent epiphenomena that arise from the inherently suppressive role of the MOC system (cf. Borg et al. 1995).

These conclusions beg an additional question: If the MOC system did not evolve to protect the inner ear from acoustic trauma, then what is the biological role of the MOC system in mammalian hearing? As is clear from the data shown in Table 2 and Figure 1, all natural acoustic environments are characterized by noise spanning a wide range of frequencies. This finding is particularly relevant for tropical forested habitats, which tend to have diverse insect and vertebrate faunas that rely on acoustic signals for a variety of communicatory functions. The sources cited in Table 2 further indicate that abiotic noise is a near-ubiquitous feature of natural acoustic environments. The combined effects of both wind and water ensure that low-intensity, relatively broadband noise is present in nearly all natural environments, suggesting that the biggest problem posed by natural ambient noise may be the masking of biologically relevant acoustic signals. This universal distribution and predominantly low-to-moderate intensity of natural environmental noise thus supports the hypothesis that the MOC system evolved in the context of unmasking transient stimuli, rather than protecting the inner ear from intense noise levels. In this context, it is not surprising that noisy, relatively broadband signals, like those present in natural environments, are among the most effective in stimulating MOC efferent activity (Warren and Liberman 1989). Indeed, we expect that mammals (like most vertebrate lineages) have experienced significant selective pressure to segregate biologically relevant acoustic signals from irrelevant background noise (Waser and Brown 1984; Brown and Waser 1988; Fay and Popper 2000).

SUMMARY OF FINDINGS

Ambient noise in all natural acoustic environments is significantly lower in intensity than the experimental conditions that are known to evoke an MOC-based protective effect. The very intense traumatizing stimuli [100–150 dB SPL (peak level), primarily sinusoidal tones] used in all short-duration studies demonstrating MOC-mediated protection simply have no natural analog. Although longer duration, relatively high- intensity (~80–90 dB SPL) noise has been documented in a small number of natural acoustic environments, these noise conditions are probably not sufficient to activate the protective effects of the MOC system. Even if such relatively high-intensity noise environments can activate MOC protective effects, the rarity of such noise environments suggests that their role in the evolution of the mammalian MOC system would have been small. The substantial discrepancy between the characteristics of natural ambient noise and the experimental conditions necessary to evoke MOC-based protection provides strong evidence that the MOC system did not evolve to protect the inner ear from acoustic trauma.