Abstract
Introduction
The small-strain shear modulus (
This article introduces a new noninvasive method to estimate frequency-dependent Rayleigh wave
The subsequent sections of this article are organized as follows: first, we cover important background information on attenuation and damping. Second, we present a concise overview of the FDBF technique introduced in the work by Lacoss et al. (1969) and the FDBFa wavefield conversion methodology proposed in the work by Aimar et al. (2024a), along with the integration of these methods within our proposed NFDBFa approach. Then, synthetic studies are presented to showcase the capabilities of the proposed NFDBFa approach and inform best practices for its application. The synthetic studies offer valuable insights into the influence of 2D array size and proximity to noise sources on attenuation estimates. For example, it is demonstrated that the optimal 2D ambient noise array design principles for attenuation estimation differ from the principles governing 2D array design for phase velocity estimation. Finally, we demonstrate the practical utility of our proposed NFDBFa technique through a field application at a deep, soft soil site in Logan, Utah, USA. In this field application, phase velocity and attenuation coefficients are extracted from surface wave data and then simultaneously inverted to develop deep
Background
Seismic wave attenuation is commonly attributed to three mechanisms: material damping, geometric spreading, and apparent attenuation (Zywicki, 1999). Material damping, or anelastic attenuation, arises from the collective interaction of diverse mechanisms (Johnston et al., 1979). These factors encompass frictional losses among solid particles and fluid flow losses due to the relative motion between solid and fluid phases, a phenomenon particularly notable in coarse-grained soils (Biot, 1956; Walsh, 1966, 1968; Stoll, 1974). Fine-grained soils, however, showcase more intricate phenomena influenced by electromagnetic interactions between water dipoles and microscopic solid particles (Lai, 1998). This intrinsic material damping is typically approximated as frequency-independent (i.e. hysteretic), particularly within the frequency range spanning 0.1–10 Hz (Aki and Richards, 1980; Shibuya et al., 1995), commonly considered in seismic site response studies. However, the assumption that material damping is frequency-independent is debated in the literature, as discussed in the work by Lai and Özcebe (2016) and the references therein.
The attenuation of seismic waves due to material damping in a continuum is related to the damping ratios of both compression waves (
Geometric or radiation damping involves the spread of a fixed amount of energy over a broader area or volume as the wavefront moves away from the source. Take, for instance, a harmonic unit point load applied along the normal direction to the surface of a homogeneous and isotropic half-space; this perturbation generates both body waves and Rayleigh waves. The body waves propagate radially from the source, forming a hemispherical wave front, while Rayleigh waves travel outward along a cylindrical wave front. As these waves travel, they traverse an expanding volume of material, leading to a decrease in energy density as the distance from the source increases. In the interior of the half-space, the amplitude of the body waves attenuates in proportion to
Apparent attenuation includes wave scattering, which arises from the interaction of waves with heterogeneities along the seismic path (O’Doherty and Anstey, 1971; Spencer et al., 1977), and the reflection and transmission of seismic waves at interfaces and mode conversions (Rix et al., 2000). Therefore, apparent attenuation is highly site-specific and difficult to generalize.
Multiple approaches have been proposed to characterize the attenuation of seismic waves. One such technique involves the spectral decay parameter, kappa (κ), which describes the amplitude decay of the ground-motion acceleration spectrum at high frequencies. κ and its site-specific and source/path components encapsulate various damping mechanisms, including material damping and wave scattering (e.g. Anderson and Hough, 1984; Ktenidou et al., 2015; Parolai et al., 2022). Laboratory tests and in situ methods have also been proposed to estimate
Surface wave testing became popular in the 1980s as an effective way to non-invasively develop 1D layering and
Ambient noise surveys typically employ 2D arrays of surface seismic sensors due to the a priori unknown location of the ambient noise sources. Unlike linear arrays, 2D arrays allow for the determination of wave propagation direction, which is necessary for resolving the true phase velocity (Cox and Beekman, 2011). While 2D ambient noise array measurements have been referred to using several names, in this article, we will refer to them as microtremor array measurements (MAM; Ohrnberger et al., 2004; Teague et al., 2018). A schematic representation of a typical survey using both active and ambient noise arrays is presented in Figure 1a. The active-source array in Figure 1a is in accordance with the MASW method (Park et al., 1999), using a linear array of receivers to capture the wavefield generated by active sources off each end of the array. Example waveforms recorded by 24 receivers placed in-line with one of the active sources to the left of the array are depicted in Figure 1b. The ambient-wavefield array depicted in Figure 1a is in accordance with MAM testing, where surface sensors are deployed in a 2D circular pattern (note that other 2D geometries are also permissible). Example ambient noise waveforms recorded by nine sensors in the circular array are depicted in Figure 1d. Figure 1c schematically illustrates phase velocity dispersion data that are commonly extracted from active-source MASW waveforms and ambient noise MAM waveforms using various well-known wavefield transformation techniques (Vantassel and Cox, 2022). Examples of these techniques include FDBF (Lacoss et al., 1969), high-resolution frequency-wavenumber (

Schematic illustrating the data acquisition and processing stages of active-source and ambient-wavefield surface wave testing used to extract phase velocity and phase attenuation data. Panel (a) presents a typical acquisition setup consisting of concentric MASW and MAM arrays, featuring active sources for the MASW array and an ambient wavefield for the MAM array. Panel (b) shows waveforms from a single active-source location collected using the MASW array, while Panel (c) presents the combined phase velocity dispersion data resulting from MASW and MAM FDBF processing. Panel (d) depicts the ambient noise waveforms collected from the MAM array. In Panel (e), phase attenuation data processed through active-source FDBFa and ambient-wavefield NFDBFa techniques are illustrated.
As noted above, much more effort has been devoted to extracting phase velocity information from surface wave approaches than to extracting attenuation information. Nonetheless, multiple active-source methods have been developed to estimate the attenuation of surface waves. The methods introduced in the work by Lai (1998), Lai et al. (2002), Rix et al. (2000), Xia et al. (2002), and Foti (2004) are founded on assessing the spatial decay of Rayleigh waves, a phenomenon that is influenced by both
While important research on extracting phase attenuation coefficients using active-source methods is ongoing, similar to phase velocity data, combining active-source and ambient noise methods is desirable for resolving attenuation data over a broader frequency band. The majority of ambient noise techniques aimed at estimating the attenuation of surface waves were developed for regional scale estimation (Haendel et al., 2016; Parolai et al., 2022). Only a limited number of approaches have considered local scales that hold relevance for engineering purposes, such as site-specific seismic ground response analyses or dynamic vibration studies. These local-scale approaches are predominantly based on retrieving attenuation properties from the cross-correlation of seismic noise (e.g. Albarello and Baliva, 2009; Haendel et al., 2016; Parolai, 2014). Albarello and Baliva (2009) proposed a methodology that reconstructs the Green’s function based on the temporal derivative of averaged cross-correlations from noise recordings obtained by pairs of geophones, thereby incorporating attenuation effects into the process. They further validated this approach by demonstrating its potential in estimating attenuation coefficients at two distinct sites. Parolai (2014) estimated the Rayleigh phase velocity and attenuation coefficients by fitting a damped zero-order Bessel function, introduced in the work by Prieto et al. (2009), using data generated from the space correlation function introduced by Aki (1957). To mitigate the impact of uneven source distribution on cross-correlations, Haendel et al. (2016) employed a higher-order noise cross-correlation technique to extract the phase velocity and attenuation coefficient of Love waves. They illustrated that their approach yields correlation functions with higher signal-to-noise ratios (SNRs) compared with simple noise cross-correlations.
The importance of seismic noise cross-correlation methods cannot be underestimated. Nonetheless, in theory, the reconstruction of the full Green’s function requires the noise wavefield energy to be equally partitioned in all directions (Sánchez-Sesma and Campillo, 2006; Snieder et al., 2007). This is a highly specific condition that is rarely met rigorously by ambient noise on Earth (Cupillard and Capdeville, 2010; Haendel et al., 2016; Tsai, 2011). Furthermore, while travel time measurements from cross-correlation of ambient noise are theoretically understood, amplitude measurements lack a corresponding theoretical background, except when the noise is equipartitioned (Snieder et al., 2007; Tsai, 2011). Studies by Cupillard and Capdeville (2010) and Tsai (2011) have shown that attenuation estimates using cross-correlations are significantly influenced by the distribution of the noise sources. In light of the challenges posed by the equipartitioning condition for the reconstruction of the full Green’s function in ambient noise studies (Sánchez-Sesma and Campillo, 2006; Snieder et al., 2007), and considering the limitations highlighted in the work by Cupillard and Capdeville (2010) and Tsai (2011) regarding the influence of noise source distribution on attenuation estimates, we introduce a paradigm-shifting approach herein for calculating attenuation coefficients from ambient noise. This novel method not only eliminates the need for an equipartitioned noise wavefield but also remains robust in the face of uneven noise source distribution, marking a departure from existing methodologies.
This article builds upon Aimar et al.’s (2024a) work on developing an FDBFa technique for estimating
Wavefield conversion proposed by Aimar et al. (2024a)
The method introduced in the work by Aimar et al. (2024a) to estimate Rayleigh wave attenuation (
Consider the harmonic, exponentially decaying displacement wavefield,

Schematic illustrating the wavefield conversion approach proposed in the work by Aimar et al. (2024a) to extract attenuation coefficients (
This wavefield conversion can also be extended to a broadband wavefield, comprising a superposition of monochromatic plane waves by exponentiating the wavefield in the frequency domain with the power of the imaginary number. To address numerical artifacts introduced by the wrapped phase on the pseudo wavefield, Aimar et al. (2024a) recommended normalizing
Noise frequency-domain beamforming—attenuation
The inherent challenge in ambient noise measurements stems from the lack of
In the NFDBFa approach, the first step is to partition the noise data collected by a 2D array of
where
where
where
Even though there are similarities between the FDBFa method proposed in the work by Aimar et al. (2024a) for estimating
Figure 3 presents examples of the FDBF and NFDBFa responses obtained from a synthetic wavefield recorded by a 10-receiver circular MAM array for a single frequency and single time window. The array comprises nine sensors equally spaced on the perimeter of the circle and one sensor in the middle. The FDBF method is used to estimate

Schematic illustrating the FDBF and NFDBFa responses obtained from an ambient noise wavefield recorded by a 10-receiver circular MAM array for a single frequency and single time window. Panel (a) presents the
Figure 3c and d display the
NFDBFa evaluation with synthetic wavefields
This section uses synthetic data to validate the effectiveness of the NFDBFa approach in estimating phase attenuation from ambient noise recorded using MAM arrays. Specifically, the approach is tested on two soil models: a half-space model and a single layer above a half-space model. All numerical simulations discussed in this section were executed using Salvus (Afanasiev et al., 2019), a comprehensive 2D and 3D full-waveform modeling software suite based on the spectral element method. The simulations were performed on the Texas Advanced Computing Center’s (TACCs) high-performance cluster Lonestar6 using two compute nodes, with an allocation provided by DesignSafe-CI (Rathje et al., 2017).
Half-space model
This subsection presents a simple wave propagation simulation consisting of a single surface source generating body and surface waves propagating through a half-space soil model. Despite the simplicity of the model, the outcomes obtained from this simulation offer key insights into the attenuation of a wavefield generated by a surface source and elucidate the capabilities of the NFDBFa approach. Figure 4 depicts a schematic plan view illustrating the source location and MAM array configurations employed in the half-space simulation. The wavefield was generated by a point source acting in the vertical direction at coordinates (0, 0, 0) in an x, y, z cartesian coordinate system. The source was a single Ricker wavelet with a center frequency of 5 Hz. This source function produces broadband energy over a frequency range of approximately 1–10 Hz. The wavefield emanating from the source was recorded using five circular MAM arrays, each comprising 10 sensors, with one sensor at the center and nine sensors evenly spaced around the perimeter. In this article, the arrays are named using the convention “C” followed by the diameter of the array, where “C” denotes that the array is circular. Therefore, the first array, located 2 km away from the source and with a diameter of 1 km, is denoted as C1000 at 2 km. The remaining four arrays, concentrically centered 5 km from the source, have diameters of 60 (C60), 300 (C300), 1000 (C1000 at 5 km), and 2000 m (C2000). It is noteworthy that, although currently only the vertical component of the displacement wavefield is used in NFDBFa, each sensor recorded both horizontal and vertical displacement components, and plans for using all components from noise recordings are ongoing. In addition, the NFDBFa processing operated independently of any knowledge about the source location, mirroring the conditions of an ambient noise MAM survey and ensuring an unbiased analysis.

Plan view of the source (star symbol) and receiver (inverted triangle symbols) configurations used for synthetic wavefield simulations. The source was a single Ricker wavelet with a center frequency of 5 Hz. The wavefield was recorded using five MAM arrays. The first array (C1000 at 2 km) has a diameter of 1 km and is positioned 2 km from the source. The remaining four arrays are concentrically centered 5 km away from the source and have diameters of 60 m (C60), 300 m (C300), 1 km (C1000 at 5 km), and 2 km (C2000), respectively.
The half-space constitutive soil parameters are presented in Figure 5a, where

Homogeneous half-space wavefield simulation: Panel (a) presents a cross-section view of the configuration of the source and receivers shown in Figure 4, along with the half-space soil properties. Panel (b) shows the decay of particle vertical displacement as a function of distance from the source for five distinct frequencies, each normalized by its maximum amplitude at the source. Panel (c) presents the particle displacement decay patterns from Panel b, with distance now normalized by the wavelength for each frequency. Panel (d) shows the particle ellipticities for each frequency, expressed as the horizontal particle displacement divided by the vertical particle displacement, with the dotted horizontal line indicating the theoretical ellipticity calculated based on the Poisson’s ratio of the half-space soil model.
Before describing the application of the NFDBFa method, some preliminary features of the amplitude decay versus distance are discussed, as they directly influence attenuation estimates. To better observe this decay pattern, the wavefield emanating from the source was recorded every 10 m along the free surface. Those time histories were then filtered at discrete frequencies, so the amplitude decay at each frequency could be observed. The decay of Fourier amplitudes with distance from the vertical Ricker wavelet source for frequencies 1, 2, 3, 4, and 5 Hz is shown in Figure 5b and c. In Figure 5b, the amplitudes for each frequency are normalized by their respective maximum values at the source and plotted on a log scale, while the distances are not normalized and plotted on a linear scale. In contrast, in Figure 5c, the distances from the source are normalized by the Rayleigh wave fundamental mode wavelength (
It is worth noting that in 3D layered media, oscillating amplitude decay of Rayleigh waves due to geometric spreading has been reported and accounted for in attenuation studies, as observed in the work of Lai (1998). Thus, in layered media, wave amplitude oscillations can be more pronounced and may extend beyond 10
To further demonstrate the more severe near-field effects associated with amplitude decay, Figure 5d presents the simulated wavefield ellipticity, expressed through the horizontal-to-vertical (H/V) ratio of particle displacement amplitude, measured with distance in wavelengths for the same frequencies outlined in Figure 5b. The ellipticity also displays oscillations that decrease and stabilize at normalized distances greater than about 10
The synthetic time histories recorded by the C1000 at 2 and the C1000 at 5 km MAM arrays (refer to Figures 4 and 5) were processed using the FDBF and NFDBFa methods to estimate phase velocity and attenuation, respectively, as illustrated in Figure 6. Figure 6 aims to highlight the impact of wave amplitude decay patterns on the attenuation estimates. In terms of abilities to resolve phase velocity, both the C1000 arrays seem to perform approximately the same, whether 2 km away from the source (Figure 6a) or 5 km away from the source (Figure 6b). However, on inspecting Figure 6c and d, it becomes evident that the array located 5 km from the source (i.e. Figure 6d) provides more reliable attenuation estimates at lower frequencies compared with the array closer to the source. This observation can be explained by referring to Figure 5b, where the amplitude decay patterns measured by the array positioned 2 km from the source are shaded in pink. It is apparent that in close proximity to the source, the low-frequency waves have not traveled a sufficient number of wavelengths, resulting in amplitude decay that does not conform to pure exponentials (i.e. linear decay in log scale). However, by the time these waves reach the array positioned 5 km from the source (blue shading in Figure 5b), the oscillations in amplitude decay have diminished significantly, approaching a pure exponential decay. Therefore, it is noteworthy that in an ambient noise survey, even though the source location is unknown, if the noise source is close to the array in terms of wavelengths traveled by the desired frequency, it may lead to unreliable and scattered attenuation results. Nonetheless, Figure 6c and d clearly demonstrate the reliability of the new NFDBFa approach in retrieving phase attenuation estimates over a broad range of frequencies.

Half-space wavefield simulation: phase velocity (top) and phase attenuation (bottom) dispersion data estimated with FDBF and NFDBFa, respectively, from 1 km arrays positioned at two distinct distances from the ambient noise source: (left) at two kilometers (C1000 at 2 km), and (right) at five kilometers (C1000 at 5 km).
Finally, the performance of the NFDBFa in the presence of incoherent noise is investigated. For this purpose, Figure 7 illustrates the influence of incoherent noise and array size on phase attenuation estimates using the same half-space simulation results. The analysis focuses on the four arrays of different sizes concentrically centered 5 km from the source (refer to Figures 4 and 5a). Incoherent noise was introduced to the signal, with a target SNR at 20 dB, which resulted in the frequency-dependent amplitude decay patterns depicted in Figure 7a (compared to Figure 5b). Figure 7b to e display the attenuation estimates obtained using the C60, C300, C1000, and C2000 MAM arrays, respectively. It becomes evident that larger arrays yield more accurate attenuation estimates in the presence of incoherent noise. Figure 7a elucidates the rationale behind this enhanced performance for larger arrays across all frequencies. The C2000 MAM array samples a significantly larger area, enabling it to discern the exponential amplitude decay even in the presence of noise. The C60 MAM array samples a significantly smaller area, and thus is considerably more sensitive to amplitude fluctuations caused by incoherent noise, resulting in the significant scatter observed in the attenuation estimates shown in Figure 7b.

Half-space wavefield simulation with noise: Panel (a) shows the amplitude decay of the same five frequencies depicted in Figure 5 but now with added incoherent noise to the signal, setting the SNR at 20 dB. Panels (b) to (e) present the predicted phase attenuation data from the NFDBFa analysis for four arrays concentrically centered at 5 km from the source, with diameters of 60 m (C60), 300 m (C300), 1 km (C1000 at 5 km), and 2 km (C2000), respectively.
Figure 8 further illustrates the impact of array size on resolving attenuation coefficients by showcasing the

Half-space wavefield simulation with noise: Panels (a) through (d) present the
Layer above a half-space model
The performance of the NFDBFa approach on a synthetic model consisting of a single layer above a half-space is illustrated in this subsection. The model’s constitutive small-strain parameters, and the source and receiver configurations are provided in Figure 9a. For this synthetic study, 150 vertical point sources with varying forcing functions and trigger times were activated. The sources were triggered 5 km away from the center of a 1-km diameter circular array consisting of 10 sensors: one in the center and nine equally distributed around its perimeter (just like the C1000 at 5 km MAM array depicted in Figure 4). The waveforms recorded by the array are depicted in Figure 9b. These waveforms were subsequently processed using FDBF and NFDBFa to derive the Rayleigh wave phase velocity dispersion data shown in Figure 9c and the phase attenuation data shown in Figure 9d, respectively. The theoretical Rayleigh wave phase velocity dispersion and attenuation curves for the model are also presented in Figure 9c and d, respectively. In these figures, the fundamental theoretical mode is denoted as Mode 1, while the first higher mode is denoted as Mode 2.

Layered model simulation: Panel (a) presents the soil properties used in the simulation for the soil layer and the half-space, along with the surface sources and 1 km receiver array located 5 km from the source (C1000 at 5 km). Panel (b) displays the waveforms collected from the C1000 array. In Panel (c), the good agreement between the theoretical Rayleigh wave phase velocity curves (Mode 1 and Mode 2) and the experimental phase velocity data obtained through the FDBF approach on the original wavefield is demonstrated. Finally, Panel (d) showcases the good agreement between the theoretical modal attenuation curves and the experimental modal attenuation data extracted from the converted wavefield using the proposed NFDBFa approach.
The FDBF method is able to extract experimental phase velocity dispersion data from the synthetic wavefield that well matches the theoretical dispersion curves and captures the transition from Mode 1 to Mode 2 at approximately 7 Hz. A strong agreement is also observed between the theoretical attenuation curves and the experimental attenuation data extracted from the synthetic wavefield using the NFDBFa method, particularly for Mode 1. The attenuation data shifts to Mode 2 at the same frequency where the phase velocity dispersion data transitions to Mode 2. A similar observation regarding the relation between the frequencies at which phase velocity and attenuation mode transitions occur was also reported in the work by Aimar et al. (2024a) using MASW data. The observation that phase velocity and phase attenuation data tend to shift modes at identical frequencies is potentially significant, as patterns in attenuation modes are generally more complex than those in phase velocity modes.
The effectiveness of the proposed NFDBFa approach has been successfully demonstrated through the analyses conducted on synthetic datasets, as discussed above. Now, we shift our focus to applying this approach to real field data, offering a thorough demonstration of its effectiveness in a practical, real-world situation.
Field application and validation
A surface wave field-testing campaign was conducted at the Drainage Farm Site in Logan, Utah, USA (refer to Figure 10), a property owned by Utah State University (USU). Structural geology indicates that Southern Cache Valley, encompassing the Drainage Farm Site and located in the northeastern part of the Basin and Range province, is a graben bounded by high-angle normal faults (Williams, 1962). The site is underlain by Paleozoic rocks, which are overlain by Tertiary formations, such as the Wasatch and Salt Lake formations, composed of conglomerate, siltstone, and tuffaceous sandstone. In certain areas of Cache Valley, these formations reach thicknesses of up to 2440 m (Evans et al., 1996). The near-surface geology of the Drainage Farm Site is characterized by sediments from ancient Lake Bonneville, which receded to form the Provo shoreline. These sediments include alluvial, lacustrine, and deltaic deposits (Evans et al., 1996; Williams, 1962). Well logs presented by Williams (1962) reveal alternating layers of silt and clay, sand, and gravel above the Salt Lake formation. Moreover, limited deep well logs from the vicinity of the Drainage Farm Site indicate that rock can be encountered at depths ranging from 176 to more than 350 m (Perez, 1969).

Plan view of the MASW and MAM arrays employed for testing at the Drainage Farm Site in Logan, Utah, USA. The concentric MAM arrays featured diameters of 60 (C60), 300 (C300), and 700 m (C700), while the MASW array comprised 24, 4.5 Hz vertical geophones, spanning 46 m.
The goal of the testing was to collect a high-quality surface wave dataset that could be used for attenuation studies to validate the proposed NFDBFa technique. The field testing involved both active-source MASW testing and ambient noise MAM testing. The sensor array configurations used for MASW and MAM at the Drainage Farm Site are illustrated in Figure 10. MASW testing was performed using 24, 4.5 Hz vertical geophones placed with a spacing of 2 m between successive geophones, resulting in an array length of 46 m. Wavefields with strong Rayleigh wave content were actively generated by striking vertically on a strike plate with a sledge hammer. The sledge hammer was used at eight distinct “shot” locations that were offset by 5, 10, 15, and 20 m relative to the first/last geophone off each end of the array. Five distinct sledge hammer blows were recorded at each location for subsequent stacking to increase the SNR (Foti et al., 2018). MAM testing used three concentric circular arrays that were aligned with the middle of the MASW array, as depicted in Figure 10. The three arrays were 700, 300, and 60 m in diameter, and will be referred to as C700, C300, and C60, respectively. Each array consisted of nine evenly distributed three-component broadband seismometers (Nanometrics Inc. Trillium Compact 120s seismometers) along its circumference to capture ambient vibrations. The three arrays did not record data simultaneously; instead, the nine sensors were used to collect noise data for each of the MAM arrays one array at a time. First, the sensors recorded seismic noise for 13 h and 30 min for the C700 array. Subsequently, the sensors were relocated to their designated locations for the C60 and C300 arrays, recording ambient noise for 1.5 and 3 h, respectively.
For Rayleigh wave phase velocity dispersion analysis, MASW data were analyzed using the FDBF method with cylindrical wave steering (Zywicki and Rix, 2005), as coded in the open-source surface wave processing package swprocess (Vantassel, 2021). This processing was coupled with the multiple source offset technique for identifying near-field contamination and quantifying dispersion uncertainty (Cox and Wood, 2011; Vantassel and Cox, 2022). As a result, eight phase velocity estimates were obtained for each frequency, corresponding to one phase velocity estimate from each of the eight shot locations. MASW Rayleigh wave dispersion data influenced by near-field effects or significant offline noise were trimmed before calculating phase velocity dispersion statistics.
The three-component beamforming approach (Wathelet et al., 2018) coded in the open-source software package Geopsy (Wathelet et al., 2020) was used to generate Rayleigh wave phase velocity dispersion data for each of the MAM arrays. The recorded time for each array was discretized into blocks, with each block further divided into at least 30 time windows. The window lengths were selected to contain at least 30 cycles (periods) at the lowest processing frequency that could be extracted from each MAM array (Vantassel and Cox, 2022). For each MAM array, eight phase velocity estimates were extracted at each analyzed frequency using the three-component beamforming (Wathelet et al., 2018) approach to ensure consistency with the eight phase velocity estimates obtained from the MASW processing. Spurious dispersion data stemming from high-amplitude noise in the near field (e.g. traffic noise close to the sensors) and incoherent noise were manually eliminated before calculating dispersion statistics. Ambient noise phase velocity dispersion data from all MAM arrays were combined with the active phase velocity dispersion data obtained from MASW processing, as shown in Figure 11a. The combined data, used to compute mean and ± one standard deviation dispersion estimates (Vantassel and Cox, 2022), are displayed in Figure 11b relative to the individual MASW and MAM dispersion data points for the Drainage Farm Site.

Experimental phase velocity and attenuation data extracted from MASW and MAM testing at the Drainage Farm Site in Logan, UT, USA. Panel (a) displays the experimental phase velocity dispersion data of Rayleigh waves processed from an MASW array and three circular MAM arrays, with diameters of 60, 300, and 700 m. Panel (b) showcases the mean and ± one standard deviation of the experimental Rayleigh wave phase velocity dispersion data derived from the combined MASW and MAM datasets. Panel (c) displays the experimental phase attenuation data from MASW and three circular MAM arrays. Panel (d) illustrates the mean ± one standard deviation of the experimental phase attenuation data calculated from the combined MASW, C300, and C700 MAM arrays.
The cylindrical FDBFa (CFDBFa) approach, as proposed in the work by Aimar et al. (2024a), was employed to derive attenuation estimates from the MASW data. The CFDBFa algorithm accounts for Rayleigh wave geometric spreading by considering the cylindrical shape of the wavefront. Mirroring the MASW phase velocity dispersion analysis, the multiple source-offset technique was used for quantifying attenuation uncertainty. Thus, eight attenuation estimates were extracted from the MASW data at each analyzed frequency using CFDBFa. For the MAM attenuation estimates, the new NFDBFa approach introduced in this study was employed. Geometric spreading was not accounted for, as the distance between the MAM arrays and the ambient noise sources was unknown. However, no nearby sources were observed during acquisition, so we believe that the plane wave approximation is acceptable. The recorded time for each array was discretized into eight blocks, with each block further divided into 30 windows. Consequently, the window length employed for each MAM array can be determined by dividing the total recording time of the array by the product of 8 blocks and 30 windows (i.e. 240). Similar to MAM phase velocity dispersion analysis, the window lengths were selected to contain at least 30 periods at the lowest processing frequency that could be extracted from each MAM array (Vantassel and Cox, 2022). Averaging the estimates from all windows within each block yielded a single data point per block, thus providing eight unique attenuation estimates per frequency. This processing approach ensured that an equal number of attenuation data points were obtained at each frequency for all of the MASW and MAM arrays. The combined ambient noise attenuation data from all MAM arrays and the active attenuation data from the MASW array are plotted together in Figure 11c. A good agreement is observed between the attenuation estimates derived from the MASW array and those obtained from the C300 and C700 arrays for frequencies ranging from 4 to 10 Hz. The MASW testing did not generate coherent attenuation data at frequencies less than 4 Hz, due to the limitations of the active sledge hammer source. However, the MAM testing was able to extract coherent attenuation data at frequencies below 1 Hz. The agreement observed between the active-source and ambient noise attenuation estimates serves as compelling evidence for the efficacy of the proposed NFDBFa approach. However, it is notable that there is significant scatter in the attenuation estimates obtained using the C60 array. This variability is likely caused by the challenges previously discussed in regard to using smaller MAM arrays for attenuation studies, as the phase velocity data extracted from the C60 array was very good (refer to Figure 11a). Hence, the attenuation data from the C60 array were removed prior to calculating attenuation statistics. The combined attenuation estimates from the MASW, C300, and C700 arrays, and the mean and ± one standard deviation attenuation estimates obtained from those three arrays, are depicted in Figure 11d. While a noticeable agreement exists among the three arrays, there is significantly greater scatter in the attenuation estimates (Figure 11d) compared to the phase velocity dispersion estimates (Figure 11c). Quantitatively, the coefficient of variation (i.e. the standard deviation normalized by the mean) for the phase velocity experimental data ranges between 0.05 and 0.07, whereas the coefficient of variation for phase attenuation is generally an order of magnitude larger, around 0.5 and increasing up to 0.6–0.8 at high frequencies. The larger uncertainty observed at frequencies above 9.5 Hz in Figure 11d results from the divergence between the MASW and MAM attenuation estimates, which may stem from the inability of the MAM arrays in this experiment to provide reliable attenuation estimates beyond this frequency. Nonetheless, the coefficient of variation values of the experimental attenuation data is consistent with results reported by other studies (e.g. Aimar, 2022; Rix et al., 2000). The application of the new NFDBFa approach in this field test showcases its effectiveness in estimating attenuation coefficients from ambient noise wavefield data.
Finally, the statistical experimental Rayleigh wave phase velocity and attenuation parameters derived from both the MASW and MAM testing (refer to Figure 11b and d) were used to invert for
The inversions performed herein involved 50,000 five-layer trial soil models with progressively increasing thicknesses, covering a comprehensive range of layer thicknesses,
The 10 best inversion results, which are those that achieved the lowest RMS error between their theoretical phase velocity and phase attenuation curves and the experimental data statistics, are shown in Figure 12. The theoretical phase velocity and attenuation curves are shown relative to the experimental data error bars in Figure 12a and b, respectively. The 10 best

Inversion results for the experimental Rayleigh wave phase velocity and attenuation data collected at the Drainage Farm Site in Logan, UT, USA. The figure highlights the 10 best-fitting models, with Panels (a) and (b) comparing the theoretical curves for phase velocity and attenuation, respectively, against the experimental data represented by mean values with ± one standard deviation error bars. Panels (c) and (d) display the 10 best
Conclusion
A new methodology for estimating frequency-dependent attenuation coefficients through the analysis of ambient noise wavefield data recorded by 2D arrays of surface seismic sensors has been presented. The approach relies on the application of an attenuation-specific wavefield conversion and FDBF. It has been termed the NFDBFa method. Importantly, using an FDBF approach, as opposed to a noise cross-correlation approach, enables the direction of ambient noise propagation to be determined for each noise window and frequency, and does not require an equipartitioned ambient noise wavefield. Furthermore, using an FDBF approach enables the phase velocity and attenuation data generated from active-source testing such as MASW to be combined with phase velocity and attenuation data generated from ambient noise testing such as MAM to span a broader frequency range. This enables the joint inversion of phase velocity and attenuation to be performed as a means to extract shear wave velocity and small-strain damping ratio profiles to significantly greater depths than previously possible using only active-source data.
2D plane strain numerical simulations were conducted to deepen our understanding of the proposed NFDBFa method. These simulations aimed to evaluate how the proximity of the MAM array to the noise source, the presence of incoherent noise, and the size of the array affect the estimates of phase attenuation. The results demonstrated that near-field effects are more pronounced and extend over greater distances for phase attenuation estimates in comparison to those considered for phase velocity estimation. Furthermore, it was discovered that larger array sizes consistently provided more accurate phase attenuation estimates across all considered frequencies, contrary to the conventional MAM design criteria used for phase velocity dispersion estimation, where larger arrays are typically preferred for resolving lower frequencies while smaller arrays excel at resolving higher frequencies. This distinction emphasizes the need for unique design criteria when planning an MAM array for attenuation estimation.
The proposed NFDBFa approach underwent validation through numerical wave propagation simulations, comparing predicted frequency-dependent phase attenuation values against theoretical phase attenuation curves for two synthetic models. Furthermore, validation of the developed technique was reinforced using MASW and MAM field data collected at the Drainage Farm Site in Logan, Utah, USA. The phase velocity and attenuation data extracted from the MASW and MAM recordings agreed well over a common bandwidth, while the ambient noise MAM data allowed the phase velocity and attenuation estimates to be extracted at significantly lower frequencies. The joint inversion of the experimental Rayleigh wave phase velocity and phase attenuation data obtained from both MASW and MAM testing facilitated the estimation of shear wave velocity and small-strain damping ratio profiles to significant depths (400 m) at the Drainage Farm Site. While these results are promising, they still need to be validated through additional invasive and laboratory testing.
As noted herein and in other studies such as the study by Aimar et al. (2024a), attenuation data are significantly more variable and more complex to understand (e.g. modal curves that repeatedly cross one another) than phase velocity data. As such, there is a need for future studies to better understand attenuation data and how to invert them to retrieve reliable in situ profiles of the small-strain damping ratio. Future efforts should involve additional numerical and experimental testing of diverse subsurface conditions, coupled with comparisons to damping estimates obtained from invasive tests, such as cross-hole and downhole testing. With the validity of this approach demonstrated on the vertical component, future research will also explore the utilization of the three components of the noise wavefield to enhance attenuation estimates beyond the current method’s capabilities.
