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Original Articles

Multiple scattering correction factor estimation for aethalometer aerosol absorption coefficient measurement

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Pages 160-171 | Received 15 Aug 2018, Accepted 15 Nov 2018, Published online: 21 Dec 2018

Abstract

We estimate the multiple scattering correction factor (Cref), which is an empirical constant required to correct aerosol absorption coefficient (σap) measurements for the multiple scattering artifacts of aethalometer, using a multiplier derived from a linear regression method (CrefLRL). Estimated CrefLRL values during the Cheju ABC Plume Monsoon EXperiment (CAPMEX) are 3.99 (405 nm), 4.48 (532 nm), and 5.46 (781 nm) using aethalometer and 3-wavelength PhotoAcoustic Soot Spectrometer (PASS-3). The difference between these CrefLRL values and those of a previous study (CrefW03) are ˗8.0% (405 nm), 20.1% (532 nm), and 30.2% (781 nm); the difference is greater at larger wavelengths because the linear regression line intercept is larger. CrefW03 varies by up to 121% with increasing aerosol absorption coefficient (σap) at 532 and 781 nm, whereas CrefLRL varies by only 36.8%. CrefW03 and CrefLRL determined during CAPMEX were applied to year-round aethalometer σap measurements (σapW03 and σapLRL, respectively) at Gosan (GSN), Lulin (LLN), and Alert (ALT) stations. σapW03 and σapLRL were compared to concurrent σap measurements from Continuous Light Absorption Photometer (CLAP; σapCLAP). At GSN, the bias difference and root mean square difference of σapW03 from σapCLAP are ˗23.1 and 25.8%; however, those of σapLRL from σapCLAP are ˗9.0 and 17.9%, respectively. LLN and ALT both exhibit a greater difference between σapW03 and σapCLAP than between σapLRL and σapCLAP. This suggests that CrefLRLcan be applied to year-round aethalometer measurements. Furthermore, σapLRL agrees better with σapCLAP than σapW03 in all three environments.

Copyright © 2019 American Association for Aerosol Research

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1. Introduction

Filter-based optical instruments, such as aethalometer (Hansen, Rosen, and Novakov Citation1984), particle soot absorption photometer (PSAP; Bond, Anderson, and Campbell Citation1999), and multi-angle absorption photometer (MAAP; Petzold and Schönlinner Citation2004), measure the change in light attenuation (ATN) across an aerosol-laden filter to retrieve the aerosol absorption coefficient (σap). Filter-based optical instruments have been widely used to measure σap; however, they typically suffer from measurement artifacts. Specifically, the multiple scattering effect (MSE) is one of the largest sources of uncertainty in filter-based optical instruments (Bond, Anderson, and Campbell Citation1999; Petzold and Schönlinner Citation2004; Sheridan et al. Citation2005; Subramanian et al. Citation2007; Virkkula et al. Citation2007; Lack et al. Citation2008; Kondo et al. Citation2009; Moosmüller, Charkrabarty, and Arnott Citation2009; Müller et al. Citation2011; Di Biagio et al. Citation2017; Ogren et al. Citation2017). Many previous studies have suggested MSE correction methods for aethalometer by applying a multiple scattering correction factor (Cref). Weingartner et al. (Citation2003; hereafter, W03) suggested a σap correction scheme that determined Cref based on σap measured by aethalometer relative to that measured by a reference instrument. Arnott et al. (Citation2005; hereafter, A05) suggested subtracting a portion of related aerosol light scattering measurements to correct for particle scattering, based on experiments with laboratory-generated aerosols and ambient aerosols. Schmid et al. (Citation2006; hereafter, S06) modified the W03 scheme by adopting the single scattering albedo (SSA) to correct for the particle scattering artifact using ambient aerosols. Collaud Coen et al. (Citation2010; hereafter, C10) suggested a σap correction scheme for ambient aerosols. Despite the various improvements made by many studies, the basis of Cref determination has not been changed substantially from W03. It is still necessary to reduce the effect of any measurement artifact induced during the Cref determination procedure because not only the aethalometer but also the reference instruments include their own measurement artifacts (Arnott et al. Citation1999, Citation2003; Petzold and Schönlinner Citation2004; Ajtai et al. Citation2010; Nakayama et al. Citation2015).

In this study, we propose a Cref determination method and validate its effects on accompanying aerosol optical properties, including σap, SSA, and the absorption Ångström exponent (AAE). Our determination method uses a linear regression line (LRL) method outlined in Section 3.1. Estimated Cref values are then validated by applying them to year-round continuous aethalometer measurements and comparing our values to simultaneous measurements from other filter-based optical instruments in Section 3.2.

2. Methodology

2.1. Measurements and stations

A summary of the measurement setup is shown in . Multi-year measurement data from Gosan (GSN; 33.29°N, 126.17°E, 72 m a.s.l.; maritime), Lulin (LLN; 23.47°N, 120.87°E, 2862 m a.s.l.; high altitude), and Alert (ALT; 82.49°N, 62.51°W, 190 m a.s.l.; Arctic) stations were analyzed. An identical measurement protocol (WMO Citation2016) was implemented at all three stations. A brief description of the location, environment and measurements is given in Schmeisser et al. (Citation2017) and Andrews et al. (Citation2018). From August to September, 2008, the Cheju ABC plume monsoon experiment (CAPMEX) field campaign was performed at GSN (Flowers et al. Citation2010; Ramana et al. Citation2010).

Table 1. Instrument setup for σap measurements during CAPMEX and at GSN, LLN, and ALT.

2.2. Instrumentation

2.2.1. Aethalometer

A 7-wavelength aethalometer (AE-31, Magee Scientific Corp., Berkeley, CA, USA) measures the change of ATN and reports it as an equivalent black carbon mass concentration (Mebc). During CAPMEX and at GSN, the aethalometer was operated without any imposed size cut, with a flow rate of 3.9 L min−1, using an extended-range spot size (1.67 cm2) and a temporal resolution of 5 min. At LLN, the aethalometer was operated with a flow rate of 4.0 L min−1, using a high-sensitivity spot size (0.5 cm2). At ALT, the aethalometer was operated with a flow rate of 3.9 L min−1, using a high-sensitivity spot size (0.5 cm2). Müller et al. (Citation2011) reported that the noise level is 0.8 Mm−1 within 470–880 nm over a 3-min average. Aethalometer σap values were retrieved using the W03 scheme in this study, which is discussed more in Section 2.3.

2.2.2. Photoacoustic soot spectrometer (PASS-3)

A 3-wavelength Photoacoustic soot spectrometer (PASS-3, Droplet Measurement Technologies Inc., Longmont, CO, USA) (Flowers et al. Citation2010) was operated to obtain σap at 1 L min−1 and a 10 min time-base during CAPMEX. Even though PASS-3 measurement precision can be influenced by factors such as acoustic noise and RH, PASS-3 was set as the reference instrument of CAPMEX in this study because it is free from filter-induced measurement artifacts (Arnott et al. Citation2000; Citation2003; Lack et al. Citation2008). The manufacturer reported that the detection limit of PASS-3 is 10, 10, and 3 Mm−1 (2 second-averaged) at 405, 532, and 781 nm, respectively (http://www.dropletmeasurement.com/photoacoustic-soot-spectrometer-three-wavelength-pass-3-0). Using Equation (S4) (Supplementary Information C), this corresponds to 0.58, 0.58, and 0.17 Mm−1 for 10-min averages at 405, 532, and 781 nm, respectively. Flowers et al. (Citation2010) provide a more detailed description of PASS-3 measurements during CAPMEX.

2.2.3. Continuous light absorption photometer (CLAP)

The continuous light absorption photometer (CLAP) is a mechanically and electronically improved version of PSAP; the LRL slope of CLAP σap (σapCLAP) to PSAP σap is 0.94 (standard deviation: 0.08) and the intercept is small (mean: 0.1) for three wavelengths (Ogren et al. Citation2017). CLAP is operated at GSN, LLN, and ALT with ∼1 L min−1 and 1-min time-based measurements. σapCLAP was retrieved using corrections derived by Bond, Anderson, and Campbell (Citation1999) and Ogren (Citation2010).

CLAP cannot strictly be the reference instrument for a comparison of aethalometer Cref because CLAP is another filter-based optical instrument. Nevertheless, CLAP was employed as the reference for comparison of multi-year measurements at GSN, LLN, and ALT because CLAP exhibits lower uncertainties than aethalometer for spot area size (aethalometer ∼8%, CLAP 2%), instrumental noise (aethalometer ∼0.42 Mm−1, CLAP ∼0.07 Mm−1), and unit-to-unit variability (aethalometer ∼20%, CLAP ∼4%) (Müller et al. Citation2011; Ogren et al. Citation2017). Ogren et al. (Citation2017) reported that the noise level of the CLAP attenuation coefficient (i.e., raw absorption coefficient without any correction) is approximately 0.2 Mm−1 for a 1-min average. Although simultaneous observations of CLAP and PASS are not available in this study, it is worth noting that σap from PSAP and PASS were well matched (e.g., Lack et al. Citation2008). Aerosols were sampled by the CLAP with both a PM1 and PM10 size cut; however, PM1 data were not analyzed in this study because of the comparison with aethalometer, which have no imposed size cut.

2.3. Data processing and quality assurance

Measurement data were averaged to an hourly resolution for the comparison, then a standard temperature and pressure (STP; 0 °C and 1013.25 hPa) correction was applied. During CAPMEX, σap values with high nephelometer RH (> 70%) were excluded from the analysis to avoid hygroscopic effects of the measurement (Arnott et al. Citation2003; Kim et al. Citation2006; Fierz-Schmidhauser et al. Citation2010).

2.3.1. Retrieval of σap from aethalometer measurement

EquationEquations (1)–(3) show the aethalometer σap retrieval scheme suggested by W03. (1) ATNi= 100·lnIiIo,i(1) (2) σatn,i=AiQi·ΔATNi(i1)Δti(i1)(2) (3) σap,i= σatn,iCref·RATNi= σatn,iCref·1f1lnATNiln10ln50ln10+1(3)

where ATN is the light attenuation by filter-deposited aerosols, Io and I are emitted and particle attenuated light intensity, respectively. Q, t and A are flow rate, time and spot size area, respectively. σatn is the attenuation coefficient, which is the raw aethalometer absorption coefficient without any correction applied, R(ATN) is the filter-loading correction, and f is the shadowing factor. i represent the ith data point. Supplementary Information (A) summarizes the notations used in this study (subscripts indicate the type of parameter; superscripts indicate the method or instrument used to retrieve the parameter). Although S06 and C10 schemes are improved versions of W03, C10 reported that the W03 scheme agrees well with reference instruments and does not modify the spectral characteristics of σap for all aerosol types in a comparison among several existing schemes including W03, A05, and S06. Therefore, the W03 scheme, which has the simplest multiple scattering compensation, was selected to retrieve aethalometer σap in this study.

2.3.2. Determination method of Cref

CrefW03 is determined using EquationEquation (4). (4) CrefW03 = 1NiNσatn,i/R(ATNi)σap,iref =1NiNσap,iflcσap,iref(4) where σapflc is σatn with the filter-loading effect corrected by dividing by R(ATN) and N represents the number of total data points. σapref is the σap measured by the reference instrument (PASS-3 during CAPMEX; CLAP at GSN, LLN, and ALT). CrefW03 is determined by dividing σapflc by σapref, but partly corrected only for the filter-loading effect to extend the sample number. Moreover, the ratio between σapflc and σapref can also be retrieved by the slope of the least-square LRL between the two measurements, assuming that they are linearly correlated (Wilkinson and Rogers Citation1973). Ideally, the LRL between σatn and σapref does not have an intercept; however, it is possible that the LRL intercept is non-zero and is large enough to have a non-negligible impact on the determination of Cref. Cref determined by the least-square linear regression method (CrefLRL) is defined in EquationEquation (5). (5) CrefLRL= a = 1NiNσatn,i/RATNibσap,iref= 1NiNσap,iflcbσap,iref(5) where a is the slope and b is the intercept, when the LRL equation between σapflc and σapref is y=ax+b. Assuming b is zero or negligible, EquationEquation (5) will be the same as EquationEquation (4). Otherwise, the LRL method, which is forced through the origin, will produce equal results to those of EquationEquation (4). Hence, b is the factor that induces the difference between CrefW03 and CrefLRL (see Supplementary Information B for more details).

3. Results and discussion

3.1. Determination of Cref during CAPMEX

shows a comparison between σapflc and σapPASS3 during CAPMEX. The Cref determination results during CAPMEX are summarized in .

Figure 1. Comparison between σapflc and σapPASS3 during CAPMEX (dashed line (black) is the LRL; color scale indicates the occurrence).

Figure 1. Comparison between σapflc and σapPASS3 during CAPMEX (dashed line (black) is the LRL; color scale indicates the occurrence).

Table 2. Results of Cref determination during CAPMEX.

It was observed that σapflc and PASS-3 (σapPASS3) are linearly correlated with each other (R2 ∼ 0.76–0.90). The LRL between σapflc and σapPASS3 is y = 3.99x–2.07 (405 nm), y = 4.48x + 6.92 (532 nm), and y = 5.46x + 6.22 (781 nm). CrefLRL was determined using the slope (a) of the LRL (3.99, 4.48, and 5.46 at 405, 532, and 781 nm, respectively) and CrefW03 was determined using EquationEquation (4). The difference between CrefLRL and CrefW03 is statistically significant at all three wavelengths after considering that the difference is larger than the standard error of a (SEa; see Supplementary Information C). Likewise, b is statistically significant at all wavelengths considering the standard error of b (SEb). The percentage differences of CrefW03 from CrefLRL are –8.0 (405 nm), 20.1 (532 nm), and 30.2% (781 nm); they are relatively large at 532 and 781 nm because the LRL intercept is larger at 532 and 781 nm than at 405 nm. Considering EquationEquations (1)–(3), it can be inferred that the difference between Cref is propagated to σap and that σapW03 is smaller than σapLRL by approximately –8% (405 nm), 21% (532 nm), and 25% (781 nm).

The box-whisker plot in shows CrefW03 and CrefLRL values segmented by the 10th percentile interval of σapPASS3. The maximum σapPASS3 values are 32.05 (405 nm), 18.92 (532 nm), and 11.19 Mm−1 (781 nm). At 405 nm, both CrefW03 and CrefLRL are relatively stable with increasing σapPASS3 percentile. In contrast, segmented CrefW03 varies with increasing σapPASS3 percentile at 532 and 781 nm. The 0–10th percentile whisker plot of CrefW03 reaches up to 19.8 (532 nm) and 26.2 (781 nm). shows the average segmented Cref value and its difference from the total Cref value (unsegmented). In the 0–10th percentile bin, the average CrefW03 is larger than that of CrefLRL by a factor of 0.71 (405 nm), 1.94 (532 nm), and 2.15 (781 nm). However, in the 90–100th percentile of σapPASS3, the segment bin-averaged CrefW03 is larger than that of CrefLRL by a factor of 1.01 (405 nm), 0.91 (532 nm), and 0.92 (781 nm). CrefW03 and CrefLRL values become closer in the 90–100th percentile.

Figure 2. Box-whisker plot of (a) CrefW03 and (b) CrefLRL segmented by percentiles of σapPASS3 (bottom and top whiskers represent the 5th and 95th percentiles; horizontal lines of the box represent the 25th, 50th, and 75th percentiles of Cref; dashed line (green) represents Cref; cross (red) represents the average value of each percentile of σapPASS3; 0–10 on the x-axis represents the interval between the 0 and 10th percentile of σapPASS3). Numbers in parentheses in x-axis are the range of σap in each bin (unit in Mm1).

Figure 2. Box-whisker plot of (a) CrefW03 and (b) CrefLRL segmented by percentiles of σapPASS3 (bottom and top whiskers represent the 5th and 95th percentiles; horizontal lines of the box represent the 25th, 50th, and 75th percentiles of Cref; dashed line (green) represents Cref; cross (red) represents the average value of each percentile of σapPASS3; 0–10 on the x-axis represents the interval between the 0 and 10th percentile of σapPASS3). Numbers in parentheses in x-axis are the range of σap in each bin (unit in Mm−1).

Table 3. σapPASS3-segmented Cref and their percentage difference from the unsegmented average of Cref during CAPMEX.

Notably, the percentage difference between segmented CrefW03 and total CrefW03 varies by ±121.0% at all wavelengths; i.e. 13.1 (405 nm), –26.5 (532 nm), and –26.1% (781 nm) in the 90–100th percentile. The minimum percentage difference between segmented CrefW03 and total CrefW03 occurs in the 30–60th percentile. Conversely, the segmented average of CrefLRL lies between ±36.8% at all wavelengths; i.e. 3.0 (405 nm), –2.9 (532 nm), and 4.2 (781 nm) in the 90–100th percentile. The minimum percentage difference of segmented CrefLRL from total CrefLRL occurs during the 90–100th percentile. CrefLRL does not change with increasing σapPASS3 relative to CrefW03. This suggests that CrefLRL produces less extreme values and is less affected by low signal-to-noise ratio (SNR).

CrefW03 and CrefLRL are compared to values derived in previous studies in . Even though their measurement environment and wavelengths are not equal, Cref values from previous studies range from approximately 2–5. Cref can be separated into two groups by aerosol type: fresh soot (black) and ambient (coated/mixed) soot aerosols. Pure diesel soot and pure PALAS soot of W03 and kerosene soot of A05, which were laboratory-generated fresh soot aerosols, are relatively lower and their Cref values agree closely with other aerosol types with values of approximately 2, regardless of the reference instrument type. For ambient aerosols (including coated/mixed), unlike fresh aerosols, Cref exhibits increased values and a more dispersed distribution. This is likely because ambient aerosols consist of a more complex mixture of various aerosol species than fresh soot aerosols. Higher Cref values of approximately 2.8–5.4 were observed for ambient aerosols. Coating/mixing during the ambient aging procedure increases particle absorption efficiency, as well as the MSE, resulting in high Cref (Fuller, Malm, and Kreidenweis Citation1999; Lack et al. Citation2008; Gyawali et al. Citation2009; Knox et al. Citation2009; Cappa et al. Citation2012; Bond et al. Citation2013; Wang et al. Citation2014).

Figure 3. Cref values from previous studies and those determined in this study (black: Cref using a filter-free instrument and laboratory-generated/fresh soot; blue: Cref using a filter-based optical instrument and ambient/coated aerosols; red: Cref using a filter-free instrument and ambient/coated aerosols).

Figure 3. Cref values from previous studies and those determined in this study (black: Cref using a filter-free instrument and laboratory-generated/fresh soot; blue: Cref using a filter-based optical instrument and ambient/coated aerosols; red: Cref using a filter-free instrument and ambient/coated aerosols).

The Cref of ambient aerosols can be divided into two groups according to the reference instrument type: filter-free reference instruments (red) and filter-based optical instruments (blue). The Cref of W03, A05, and S06 were determined using a filter-free reference instrument and are distributed around 3.7–5.4. CrefLRL values during CAPMEX lie between the Cref values of A05 and S06. This is reasonable considering the type of reference instrument and the measurement environment. CrefLRL during CAPMEX was determined using PASS-3 (A05: difference between extinction and scattering; S06: PhotoAcoustic Spectrometer, PAS) and the polluted maritime environment (A05: suburban; S06: remote area of Amazon basin). Cref values of C10 and Backman et al. (Citation2017) range from 2.8 to 4.1. Backman et al. (Citation2017) reported a Cref value of 3.1 using PSAP, CLAP, and MAAP at six Arctic stations. Saturno et al. (Citation2017) also reported Cref of 4.9–6.3 (637 nm) in Amazon region. In this study, CrefLRL was determined by setting PASS-3 as the reference instrument (CAPMEX) and by setting CLAP as an arbitrary reference (GSN, LLN, ALT). As shown in the next section, the estimated CrefLRL values (528 nm) using CLAP are 3.67 (GSN), 3.85 (LLN), and 3.71 (ALT). Even though the measurement periods do not correlate, CrefLRL values during CAPMEX are higher than CrefLRL values at GSN. Furthermore, they are lower than those determined using the reference instrument, including those measured during CAPMEX. These results also lie within the range of previous research results using a filter-based optical reference instrument. Many comparison studies have reported that the σap of a filter-based optical instrument is larger than that of a filter-free instrument by a factor of 1.1–4.1 (Arnott et al. Citation2003; Virkkula et al. Citation2005; Torres et al. Citation2016). Specifically, liquid phase coating, organic aerosol fraction, organic gases, and their modification by filter media induce this difference (Subramanian et al. Citation2007; Lack et al. Citation2008; Lim et al. Citation2014; Shrestha et al. Citation2014; Vecchi et al. Citation2014). Therefore, it is likely that the organic (or liquid) portion of the aerosols increases the difference of σap between filter-based optical and filter-free instruments. This difference is then propagated into the difference of Cref. It is likely that both the aerosol and instrument type affects the determination of Cref.

On the other hand, Cref values generally increase with increasing wavelength. The Ångström exponent of CrefW03 (–1.01) and CrefLRL (–0.47) was much larger than those from previous works. The Ångström exponent for pure PALAS soot and pure diesel soot of W03 was estimated to be –0.06 and –0.18, respectively, whereas that for coated PALAS soot and coated diesel soot of W03 was –0.18 and –0.23, respectively. The laboratory-generated kerosene soot of A05 was estimated to be –0.15.

Finally, it is worth to noting that we did not find any significant change of CrefLRL with increasing ATN. Also, there was no special relationship among scattering coefficient, backscattering fraction, and CrefLRL.

3.2. Validation of CrefLRL by application to year-round measurements

CrefW03 and CrefLRL values determined during CAPMEX were applied to continuous aethalometer measurements at GSN, LLN, and ALT for the validation. CrefW03 and CrefLRL of PASS-3 wavelengths (405, 532, 781 nm) were adjusted to CLAP wavelengths using Ångström exponent interpolation. Adjusted CrefW03 values are 4.24 (467 nm), 4.79 (528 nm), and 5.93 (652 nm). Adjusted CrefLRL values are 4.27 (467 nm), 4.53 (528 nm), and 5.01 (652 nm). Retrieved σapW03 and σapLRL values were then compared to simultaneous σap measurements of CLAP (σapCLAP).

Period-averaged measurements of σapW03, σapLRL, and σapCLAP at GSN, LLN, and ALT are presented in , and the accompanying null hypothesis probability result of the student t-test is presented in Supplementary Information (D) . At GSN, σapW03 and σapLRL are smaller than σapCLAP at all three wavelengths. The bias differences (BD) of σapW03 and σapLRL vary with increasing wavelength, from –0.3 to –1.2 Mm−1 and –0.3 to –0.4 Mm−1, respectively. However, considering the student t-test result, the difference of σapW03 and σapLRL from σapCLAP at all three wavelengths are statistically significant (p-value >.05) except at 467 nm at ALT (because the σap level and BD are small). BD of σapW03 is –3.2 (467 nm), –12.0 (532 nm), and –23.1% (652 nm) from σapCLAP. BD of σapLRL is –3.9% (467 nm), –6.8% (532 nm), and –9.0% (652 nm) from σapCLAP. The BD/RMSD ratio of σapW03 ranges from 0.19 to 0.90, but that of σapW03 ranges from 0.22 to 0.50. This shows that the difference between σapLRL and σapCLAP is less than that between σapW03 and σapCLAP at 528 and 652 nm. Moreover, at LLN and ALT, the comparison result is consistent in that the difference between σapLRL and σapCLAP is less than that between σapW03 and σapCLAP at 528 and 652 nm. It is suggested that σapLRL agrees better with σapCLAP than σapW03 not only at GSN, but in all three environments. This result suggests that a more accurate estimation of σap not only improves the accuracy of the light absorption parameter such as SSA, but also reduces the uncertainty of the estimation of the direct radiative forcing, especially atmospheric heating by light-absorbing aerosols.

Table 4. Results of the comparison between σapW03, σapLRL, and σapCLAP at GSN, LLN, and ALT.

A linear regression of σapW03 and σapLRL to σapCLAP at GSN, LLN, and ALT is shown in , indicating a linear correlation (R2 ∼0.87-0.96). At GSN (), all LRL slopes are less than 0.84. LRL slopes between σapW03 and σapCLAP depend on the wavelength (0.84 to 0.66); however, those between σapLRL and σapCLAP remain relatively steady with varying wavelength (0.83 to 0.80) and lie closer to the 1:1 line. The ratio between σapLRL and σapCLAP changes less with increasing wavelength than that between σapW03 and σapCLAP. Moreover, the same trend is observed at LLN and ALT, in which the slope of σapLRL is steady relative to that of σapW03.

Figure 4. Comparisons of aethalometer σap with σapCLAP. (a) σapW03 and (b) σapLRL at GSN, (c) σapW03 and (d) σapLRL at LLN, and (e) σapW03 and (f) σapLRL at ALT (black and gray dashed lines are the LRL and 1:1 line, respectively; color scale represents the occurrence).

Figure 4. Comparisons of aethalometer σap with σapCLAP. (a) σapW03 and (b) σapLRL at GSN, (c) σapW03 and (d) σapLRL at LLN, and (e) σapW03 and (f) σapLRL at ALT (black and gray dashed lines are the LRL and 1:1 line, respectively; color scale represents the occurrence).

The frequency distribution of Δσap (= σapσapCLAP) is shown in . At GSN, the peak of the ΔσapW03 distribution ranges between -0.5 and 0 Mm−1 with increasing wavelength, whereas that of ΔσapLRL remains at approximately 0 Mm−1. The period average of Δσap (vertical dashed line) equals BD in . The frequency of the negative ΔσapW03 value shows a greater increase with wavelength than that of ΔσapLRL. Even though the σap level is low, the trend is consistent at LLN and ALT in that the negative portion of the frequency distribution of ΔσapW03 also increases with increasing wavelength ().

Figure 5. Frequency distributions of Δσap [= aethalometer σapσapCLAP] at (a) GSN, (b) LLN, and (c) ALT. Solid lines indicate the distributions of Δσap (σapW03 is black; σapLRL is red; vertical dashed line is the period average).

Figure 5. Frequency distributions of Δσap [= aethalometer σap−σapCLAP] at (a) GSN, (b) LLN, and (c) ALT. Solid lines indicate the distributions of Δσap (σapW03 is black; σapLRL is red; vertical dashed line is the period average).

The SSA at each station using σapW03, σapLRL, and σapCLAP is shown in . Note that identical σsp values were used to calculate SSA at each site. At GSN, the difference of SSA between σapW03 and σapCLAP is 0.22% (467 nm), 0.83% (528 nm), and 1.58% (652 nm). The difference of SSA between σapLRL and σapCLAP is 0.28% (467 nm), 0.47% (528 nm), and 0.61% (652 nm). The SSA derived using σapLRL is closer to that using σapCLAP in magnitude and in spectral dependency at 528 and 652 nm; this is also true at LLN and ALT. The difference of SSA between σapW03 and σapCLAP is as much as ∼2.29% (652 nm) at LLN.

Figure 6. SSA retrieved at GSN, LLN, and ALT. SSA using σapW03, σapLRL, and σapCLAP are denoted as black, red, and green, respectively (σsp is identical at each station).

Figure 6. SSA retrieved at GSN, LLN, and ALT. SSA using σapW03, σapLRL, and σapCLAP are denoted as black, red, and green, respectively (σsp is identical at each station).

shows the AAE (467/652 nm) frequency distributions of σapW03, σapLRL, and σapCLAP at GSN, LLN, and ALT. At GSN, the AAE values of σapW03, σapLRL, and σapCLAP are 1.89 ± 0.35, 1.36 ± 0.35, and 1.20 ± 0.31 (). The difference of AAE values between σapLRL and σapCLAP is 13.3%, while, that between σapW03 and σapCLAP is 57.5%. This indicates that the spectral dependence of σapLRL (and CrefLRL) agrees better with σapCLAP than σapW03 (and CrefW03). The difference between AAE values of σapW03 and σapLRL propagates from Cref because the spectral dependence of Cref acts as a shift in AAE (Supplementary Information E). The AAE difference between σapLRL and σapCLAP is also smaller than that between σapW03 and σapCLAP at LLN and ALT ().

Figure 7. Frequency distributions of AÅE at (a) GSN, (b) LLN, and (c) ALT. Solid line is the distribution of σapW03 (black/right), σapLRL (red/center), and σapCLAP (green/left). Vertical dashed line is the average value.

Figure 7. Frequency distributions of AÅE at (a) GSN, (b) LLN, and (c) ALT. Solid line is the distribution of σapW03 (black/right), σapLRL (red/center), and σapCLAP (green/left). Vertical dashed line is the average value.

Overall, CrefLRL (i.e., LRL method) adequately reproduces year-round aethalometer measurements and the accompanying aerosol optical properties (σapLRL, SSA, and AAE) are comparable to σapCLAP. σapLRL agrees better with σapCLAP than σapW03 for all three environments and aerosol types. Schmeisser et al. (Citation2017) compared aerosol characteristics from 24 global aerosol observation stations and classified the observed aerosol types ( and ). They also classified the environments of each station in this study as “marine polluted (GSN),” “other (LLN),” and “Arctic (ALT)” and aerosol types as “black carbon (BC) dominated (GSN),” “BC dominated (LLN),” and “small particles and low absorption (ALT),” respectively. The difference between σapW03 and σapCLAP is greatest (∼23.1% at GSN) at 652 nm, and is propagated from b (LRL intercept induced by the measurement artifact) because b is large at longer wavelengths (532 and 781 nm) when Cref is determined during CAPMEX. It is also inferred that CrefLRL is less affected by measurement artifacts at all locations and for all aerosol types than CrefW03.

4. Summary and conclusions

The multiple scattering correction factor (Cref) is one of the most uncertain parameters when retrieving the aerosol light absorption coefficient (σap) from an aethalometer. In previous studies, Cref (CrefW03) was determined as the ratio between the aethalometer σapflc (uncorrected raw σap) and the reference instrument σap. In this study, Cref (CrefLRL) was determined using the linear regression line (LRL), which reduced the measurement artifact effect. The results of this study are summarized as follows.

  • CrefLRL values determined using aethalometer and PASS-3 were 3.99 (405 nm), 4.48 (532 nm), and 5.46 (781 nm) during CAPMEX. The difference between Cref values of a previous study (CrefW03; Weingartner et al. Citation2003) and CrefLRL was -8.0% (405 nm), 20.1% (532 nm), and 30.2% (781 nm). This difference was larger at 532 and 781 nm because the LRL intercept was larger at these wavelengths (6.92 and 6.22, respectively) than at 405 nm (-2.07). CrefLRL varied by ∼36.8% with increasing percentile of σapPASS3, while CrefW03 varied by up to ∼121%. CrefLRL was less affected by the LRL intercept (induced by measurement artifacts) and showed better agreement with the results reported in previous studies. Cref can also be associated with the type of reference instrument. According to previous studies and this study, Cref values determined using filter-based optical instruments were lower (2.8–4.1) than those using filter-free instruments (3.7–5.4).

  • Cref values during CAPMEX were applied to aethalometer measurements at GSN (Gosan), LLN (Lulin), and ALT (Alert) stations and compared to CLAP measurements. The difference between aethalometer σap derived using CrefLRL (σapLRL) and σap derived using CLAP (σapCLAP) was ∼9.0% whereas the difference with σap derived using CrefW03 (σapW03) was ∼23.1% at GSN. The SSA difference between σapLRL and σapCLAP was ∼0.61%, while that between σapW03 and σapCLAP was 1.58%. Furthermore, the AAE difference between σapLRL and σapCLAP was 13.3%, while that between σapW03 and σapCLAP was 57.5%. CrefLRL was also deemed appropriate to apply to year-round aethalometer measurements at LLN and ALT, and σapLRL agreed better with σapCLAP than σapW03 for all environments and aerosol types.

In our procedure of Cref determination, the LRL intercept (induced by measurement artifacts) can be sufficiently large to change Cref. Moreover, it is also possible that either aethalometer or other reference instrument have their own measurement artifacts. Thus, the measurement artifact effect on Cref determination can be reduced by applying CrefLRL.

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Acknowledgments

The authors are thankful to technicians and operators at Gosan, Lulin and Alert stations for maintenance and calibrations of instruments. We also acknowledge Canadian Forest Service for maintain the operations of the Alert station. The authors thank Dr. M. K. Dubey for providing PASS-3 data at Gosan during the CAPMEX campaign.

Disclosure statement

No potential conflict of interests was reported by the authors.

Additional information

Funding

This research was funded by the Korea Meteorological Administration Research and Development Program under Grant KMI2018-01111.

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