ARTICLES Chinese Science Bulletin 2004 Vol. 49 No. 15 1637ü1641 Analysis of carbon isotopes in airborne carbonate and implications for aeolian sources 1 1 1 CAO Junji , WANG Yaqiang , ZHANG Xiaoye , 2 2 1 Lee Shuncheng , Ho Kinfai , CAO Yunning 1 & LI Yang 1. SKLLQG, Institute of Earth Environment, Chinese Academy of Sciences, Xi’an 710075, China; 2. Department of Civil and Structural Engineering, The Hong Kong Polytechnic University, Hong Kong, China Correspondence should be addressed to Cao Junji (e-mail: cao@loess. llqg. ac.cn) Abstract Methods were developed to determine the mass ratios of carbon isotopes in trace amounts of aerosol carbonate. A Finnigan MAT 252 mass spectrometer fitted with an on-line Kiel device was to determine the 13C/12C ratio in CO2 produced from the carbonate. A study using these methods was conducted to characterize the carbonate carbon isotopes in aerosol samples collected in Xi’an on dusty and normal days during March and April 2002. Results of the study demonstrate that insights into the origin of the dust can be deduced from its isotopic composition. That is, the δ 13C of carbonate for dust storm samples ranged from −1.4‰ to −4.2‰, and this is consistent with sandy materials in dust source regions upwind. In contrast, for non-dusty days δ13C ranged from −7.5% to −9.3‰, which is more similar to fine particles emitted from local surface soils. Comparisons of dust storm aerosols with surface soils from source regions and with aerosol samples collected downwind indicate that the δ 13C values did not change appreciably during longrange transport. Therefore, carbon isotopes have the potential for distinguishing among source materials, and this approach provides a powerful new tool for identifying dust provenance. Keywords: aerosol, carbonate, carbon isotopes, dust provenance. prevailing winds of middle latitude and deposited in East Asia, and is found in near-surface atmosphere and deepsea sediments in the remote Pacific. These dust increases alkalinity of surface sea, changes acid-alkali balance, and enhances seawater to absorb atmosphere CO2. This phenomenon was confirmed by paleo-environmental records in Japan Sea sediments. Carbonate plays the roles of “alkalinity pump” and “biological pump” in seawater and rainwater, respectively, which have significant contributions to the reduction of the atmospheric CO2 during the last glacial period[5]. Since carbonate plays diverse roles in land, atmosphere and ocean systems, it has even been said to induce “Carbonate Mysteries” in the global climatic system[6]. Even the concentrations of carbonate are generally low from nD100 ngCm−3[7] to 3 µgCm−3[8] in ambient atmosphere, they can reach high levels in the atmosphere of northern China, especially under dust storm atmosphere as they can account for 15%[9] in TSP (absolute concentrations are not clear). The specific information about carbonates in the atmosphere is pitifully small because there has not been a convenient method of carbonate analysis for particles collected on the filters. The basic methodology for airborne carbonate can be divided into two types: one is acidification method[7,10], i.e. with HCl release from the carbonate in the filters; the other is optical method[11], i.e. with X-ray diffraction phase analysis. However, few researches focus on the measurement of airborne carbonate carbon isotopes and its implications. Carbonates from different origins and sources have different carbon isoü topes[12 14], so it is possible to use carbonate carbon isotope to estimate its potential source regions and characteristics. This paper provides a new method to determine carbonate carbon isotope in aerosol samples for the first time and discusses the implications of δ13C for dust origins. 1 Aerosol sampling and chemical analysis Atmospheric aerosol, as an important driven factor, has become one of the hotspots in international global change study[1]. Within the past decade there has been increasing interest in airborne carbonate because of its important role in atmospheric chemistry, global climate and radiative forcing[2,3]. Carbonate can affect atmospheric chemistry and aerosol characteristics because its alkalinity favors uptake of SO2 and NOx and conversion to SO4 and NO3 on the surface, as well as direct deposition of HNO3 and H2SO4 from the gas phase. Moreover, carbonate reacts directly or indirectly with sulfuric, nitric and some organic acid (such as acetic acid) through homogeneous and nonhomogeneous chemical reactions[4]. In addition, large amount of dust emitted from Central Asia is carried by Sampling station is located on a high dust storm occurrence city, Xi’an, which is situated at the south margin of the Loess Plateau. Aerosol samples were collected in this site in non-dust storm and dust storm periods from March to April in 2002. PM2.5 (aerodynamic diameter less than 2.5 µm) samples were collected using mini-volume samplers (Airmetrics, USA) operating at flow rates of 5 LCmin−1. Sampling ranged from 8 to 24 h for dust storm periods and normal days periods (Table 1). All the samples were collected on 47 mm Whatman (Whatman, UK) quartz microfibre filters (QM/A). The filters were preheated at 900 k for 3 h before use in order to remove potential carbonate contaminations. Detailed procedures refer to reference[15]. Aerosol mass concentrations were determined gravimetrically using an electronic microbalance (Mettle M3, Switzerland) with a 1 µg sensitivity at the Institute of Chinese Science Bulletin Vol. 49 No. 15 August 2004 1637 DOI: 10.1360/03wd0375 ARTICLES Earth Environment, CAS (IEECAS) (Table 1). The samples were analyzed for carbonate carbon using DRI Model 2001 (Thermal/Optical Carbon Analyzer) with a standard operation process[7]. The concentrations of carbonate (CO32−) were converted from carbonate carbon (C) directly by a factor of 5. 2 Carbon isotope measurement ( Determination of aerosol sample amounts. Carbon isotope analysis on carbonate has been widely applied in deep-sea sediment, soil, coral and stalagmite studies[16]. In this paper, the classic McCrea method[17] for carbonate analysis is utilized. The stable carbon and oxygen isotope measurements for trace amount of carbonate on the filters were performed on a Finnigan MAT 252 mass spectrometer (Thermo Finnigan, Germany) fitted with an on-line Finnigan automatic carbonate reaction system (“Kiel device”) (Thermo Finnigan, Germany). Carbonate (shown as CaCO3) on the filters were determined by 100% phosphoric acid. The following is the equation of chemical reaction: 2H3PO4 + 3 CaCO3 = Ca3(PO4)2 + 3 H2O + 3CO2 (1) The above reaction should be carried out in the condition of superfluous H3PO4, just to ensure the reaction to be finished completely and also to avoid isotope fractionation. The most suitable CO2 pressure from the reaction should be around 400800 µb on the MAT 252 isotope ratio mass spectrometer, and the pressure being higher or lower than this range will spoil the results. Therefore, via experiments the appropriate filter area is 13 cm2 and the proper quantity of H3PO4 is 1015 drops. () CO2 preparation. The filters were cut into few small pieces and put into the glass test tube, and then baked about 1 h at 70. Once the vacuum arrived at the standard (less than 150 µb), H3PO4 was dropped to react with carbonate. The reaction was stabilized under the constant temperature (70) for 600 s, the impurity gases were eliminated in another 90 s. Then CO2 was transferred to a liquid nitrogen dewar in −170 liquid itrogen. Impurity gas was eliminated by different gas condensation points, CO2 was purified, and then the dewar was heated to release the CO2 to another dewar, and at last all CO2 in the dewars was released and transferred to ion source for carbon isotope analysis. () Mass spectrum measurement. The purified CO2 was measured using MAT-252 to determine carbon isotope ratio. The difference between carbon isotopes was denoted by δ: δ sample = (Rsample/Rstandard − 1)1000‰, (2) 13 where Rsample is the ratio of sample carbon isotope, i.e. C/ 12 C, Rstandard is the ratio of standard carbon isotope. The isotopic results are reported in δ13C as per mil deviation from PDB standard. The standard deviation is ± 0.1‰ for the analysis. All the above experiments were completed in the stable isotope laboratory at IEECAS. 3 Results and discussion Two dust storm events occurred in Xi’an on 20 March, 2002 and 14 April, 2002, respectively. Five day back-trajectories (NOAA HYSPLIT model) showed that dust storm on 20 March originated from mid-Asia, passed Xinjiang and arrived at Xi’an, then spread over 18 provinces in the downwind regions to the east (Fig. 1). Sugimoto[18] and Chung[19] also observed the influence of this dust storm over Beijing and Chongwon-Chongju (Korea), respectively. Another dust storm originated from Taklimakan Desert and dust cloud arrived at Xi’an along the north margin of Qinghai-Tibet Plateau. This dust storm event was also detected by Yulin Aerosol Observation Station 600 km north of Xi’an[20]. The mass concentrations of PM2.5 and carbonate were very high during dust storm period (Table 1). The concentration of PM2.5 in Xi’an was as high as 350 µgm−3 on 20 March while TSP in Beijing reached peak Table 1 The comparison of PM2.5 in dust storm and normal atmospheres PM2.5 concentration Carbonate * concentraSampling date and duration Carbonate/PM2.5 (%) /µgCm−3 tion /µgCm−3 a) δ13C (‰) No. Sample type 1 dust storm March 20, 8 h 350.4 52.5 15.0 −1.4 2 dust storm March 20, 16 h 268.4 27.6 10.3 −2.6 3 dust storm March 21, 24h 352.8 44.4 12.6 −2.8 4 dust storm April 14, 8 h 847.8 131.7 15.5 −3.4 5 dust storm April 14, 14.5 h 686.9 96.9 14.1 −4.2 6 normal days March 23, 24 h 307.5 24.0 7.8 −7.5 7 normal days April 9, 24 h 212.4 10.0 4.7 −8.3 8 normal days April 11, 24 h 204.0 27.4 13.4 −6.9 9 normal days April 12, 24 h 213.9 31.4 14.7 −9.3 10 normal days April 13, 24 h 208.8 21.2 10.2 −9.2 a) CaCO3 shows as calcite. 1638 Chinese Science Bulletin Vol. 49 No. 15 August 2004 ARTICLES Fig. 1. Isentropic trajectory back in time from Xi’an (1.5 km altitude) on 20 March and 14 April, 2002, at 0000 UTC. values to 11000 µgCm−3 in the same day[18]. PM2.5 in Korea also reached 331 µgCm−3 on 23 March[19]. In addition, the concentration of PM2.5 of 8 h sampling was as high as 847.8 µgCm−3 on 14 April and its average daily concentration reached the highest value, 767.4 µgCm−3, which is 11 times as higher as the PM2.5 average daily concentration of 65 µgCm−3 according to USA National Ambient Air Quality Standards (NAAQS) (China has no PM2.5 national standard currently). This implied dust storm exerted a severely negative influence on atmosphere environment. On the same day, TSP concentration in Yulin was 4650 µgCm−3[20]. With high dust loading, carbonate in aerosol was rather high and its average daily concentration ranged from 40.1 to 114.3 µgCm−3. The percentages of carbonate in PM2.5 in the two dust storms were 10.3% and 15.5%, respectively, with an average of 13.5%. This value is close to that in Luochuan loess profile (11.1%)[12], showing that the carbonate from northwest source regions was high before it transported to the Loess Plateau by wind, which leads to high primary carbonate in loess. This result is consistent with Wen’s speculation[12]. The percentage of airborne carbonate under dust storm atmosphere was also close to the percentage of carbonate (11.8%) in surface samples on Taklimakan desert[14], which were collected from desert source regions in northwest China. However, measurement for airborne carbonate was less, especially in dust storm. Fortunately, carbonate concentration in TSP was found to be 6.3 µgCm−3, which was measured by a Japanese scientist in Kosan, Korea during the dust storm on 20 March[21]. This result corresponds to 53.5 µgCm−3 carbonate (calculated with CaCO 3 ) which also corresponds to our observed result. The comparison of carbonate percentages between non-dust storm and normal atmospheres is summarized in Chinese Science Bulletin Vol. 49 No. 15 August 2004 Table 1. Although carbonate percentages in normal days samples varies, the difference of two kinds of samples is not notable. Some researchers have put forward that the increase of carbonate carbon concentration (the content of carbonate carbon larger than 1%, i.e. 8.3% carbonate) in aerosol can be used as an indicator of dust storm event[9]. From the above comparisons, it is not correct to only use the increase of carbonate carbon concentration as an indicator [6] of dust storm. Actually even though there is no dust storm in winter, Asian dust never stops ground-based transporting from the source regions to the east and south of China. Because it is almost stable for carbonate percentage in Asian dust from source regions, in deposition regions, no matter what dust mass concentration is, there is no large change existing in carbonate percentage, unless obvious chemical reactions with some acidic aerosol occurs during dust transport. Figure 2 shows the distribution of carbon and oxygen isotopes for 10 dust storm samples. The isotopic composition of carbonate for surface soils, loess and paleosol in the Loess Plateau as well as surface soils in the modern dust source regions have been shown in the figure for comparison in order to differentiate the potential sources of carbonate. The previous studies demonstrated that δ13C of carbonate in different sizes was similar for surface soils, which showed that wind erosion had no impact on the change of isotopic composition for surface soils in dust source regions. In addition, there were little differences in carbon isotope of carbonate for size-separated loess (paleodust) samples at Luochuan loess profile and Huanxian loess profile, the differences of δ13C in coarse (>45 µm) and fine (<2 µm) particles were less than −2‰ [22]. Moreover, three sets of size-separated samples had been collected in Xi’an on 18 March and 16 April, 1998 and 13 April, 2000, respectively. All the isotope differences of carbonate carbon in PM2.5 and TSP are less than −2‰ (unpublished data), which fluctuate in the natural range. Therefore, isotope data in PM2.5 can be well comparable to those in surface soils and loess samples. The isotopic compositions of dust storm samples and normal samples with high carbonate contents are presented in Fig. 2. Distinct differences of carbon isotope can be seen from Fig. 2 for normal and dust storm samples, i.e. carbon isotope ranged from −1.4% to −4.2‰ for dust storm samples, while ranging from −7.5% to −9.3‰ for normal days samples. According to Fig. 1, dust storm on 20 March transported through Badain Juran Desert, Hexi Corridor, Tengger Desert and Ulan Buh Desert. Carbonate carbon isotopes of surface soils in these dust source regions are −0.2‰, −1.7‰, −2.6‰ and −2.7‰, respectively (Fig. 2), which are close to the values of this dust storm (Table 1). Moreover, Japanese scientists collected during dust storm in Kosan, Korea on 20 March and they obtained that one of δ13C data for carbonate was −1.4‰[21], 1639 ARTICLES Fig. 2. Comparison of carbon isotopes in dust storm samples, normal days samples, loess, paleosol in the Loess Plateau, and surface soils in modern dust source regions. DS refers to dust storm samples, Normal to normal days samples, Loess to loess sample[13], Paleosol to paleosol sample in the Loess Plateau[13], Soil to the surface soils in Xi’an [12], TKLMG to Taklimakan Desert sample, KMTG to Kumutage Desert sample, BDJL to Badain Juran Desert sample[14], HXZL to Hexi Corridor samples[14], WLBH to Ulan Buh Desert sample [14], TGL to Tengger Desert sample [14], MWS to Mu Us Desert sample[14], NM to surface soil in the middle of the Inner Mongolia Plain[14] . which was very close to our observed data (No. 1 sample in Table 1). This implies that carbonate carbon isotope in the long range transport is not fractionated, so δ13C can be used as a tracer of source materials. Compared with loess-paleosol samples, δ13C in dust storm samples are close to that in loess sample (−4.2‰), while δ13C in normal days is close to those in paleosol (−7.9‰) and in Xi’an surface soil (−7.6‰). The principle of isotope evolution for carbonate carbon in desert-loess-paleosol[9] is as follows: Primary carbonates in loess are original carbonates from underlie rock and their δ13C values are greater than or close to zero. The primary carbonates are dissolved in HCO3− solutions in the course of loess formation and then they change into second carbonates. During the formation of second carbonates, the carbon isotope composition of these secondary carbonates is determined by δ13C of CO2 in the loess sediments. The loess sediment CO2 is a mixture of atmospheric and biogenic CO2 with lighter carbon isotope (around −15‰). The dissolution-precipitation processes might happen many times during the depositing of loess sediments. It causes δ13C to be rich in secondary carbonates and δ13C of secondary carbonates becomes lighter and lighter along with the increase of dissolution-precipitation processes. So δ13C in the loess is −4.2‰ while in the paleosol is −7.9‰ due to more dissolution processes. On the basis of paleosol, the carbonate in modern surface soils in Xi’an has been influenced by anthropogenic activity, and its δ13C is also depleted (−7.6‰). The δ13C of carbonate in loess profile has been used as a paleoclimate index, i.e. the 1640 more negative of the δ 13C, the more warm and humid the corresponding climate, the more biogenetically blooming the paleoenvironment, and vice versa[12]. Therefore, δ13C of carbonate in modern desert arid regions ranges from −3.6‰ to 2.1‰ (Fig. 2). While in the Loess Plateau, secondary carbonates were in favor of forming under warm and humid climate, which leads to their δ13C (−7‰ to −8‰) lower than those of desert source regions. This phenomenon has also been observed in the distribution of carbonate carbon of surface soils on northern China. Previous study showed that δ 13C of carbonate in surface soils in dust source regions was more negative with the increasing of precipitation (Fig. 2)[14]. Take Inner Mongolia (northern and northeast China) for example, δ13C of carbonate in surface soil reached to −8.3‰ (Fig. 2). Because carbonate carbon isotope in the long range transport is not fractionated evidently, δ13C of carbonate in dust storm samples is very close to those in modern sand in dust source regions. While under normal days, surface soils naturally emit fine particles into atmosphere, which leads to depleted δ13C (−9.7‰) in carbonate for normal days samples. Thus, their isotopic composition has notable difference from those of dust storm samples. Therefore, major dust sources can be inferred from their δ 13C values in carbonate under ambient air. If δ 13C is lighter (such as −9‰), it maybe comes from sandy soil, degraded grassland and local dust, having abundant precipitations and frequent anthropogenic activities. If δ 13C is heavier (such as −3‰), northwest desert regions can be considered as dominant contributions to δ13C. Therefore, δ13C of carbonate may be Chinese Science Bulletin Vol. 49 No. 15 August 2004 ARTICLES an effective tool to trace the sources for the currently complex research of source regions determination. 4 Conclusion Aforementioned analyses suggest: that a Finnigan MAT 252 mass spectrometer fitted with an on-line Kiel device III can provide an effective measurement for the isotopic composition of airborne carbonate. Contrary to carbonate content, δ13C in carbonate has distinct differences under different conditions, i.e. δ13C (−2.9‰ ± 1.0‰) in carbonate for dust storm samples was higher evidently than the normal days samples (−8.2‰ ± 1.0‰). This indicates that the isotopic composition of airborne carbonate can provide a potential power tool to trace dust origins. 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