Highlights
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Stable isotope and element fingerprints can track the geographical origin of tobacco.
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The discrimination accuracy at two spatial scales was >97%.
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The importance of indicators ranking differs with the spatial scale of the evaluation.
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This study establishes the first traceability fingerprints dataset of tobacco.
Keywords: Geographical origin, Stable isotopes, Elements, OPLS-DA modeling, Tobacco
Abstract
Tobacco is a widely cultivated cash crop, but it is often smuggled and sold illegally. Unfortunately, there is currently no way to verify the origin of tobacco in China. In an effort to address this issue, we conducted a study using stable isotopes and elements from 176 tobacco samples at both provincial and municipal scales. Our findings revealed significant differences in δ13C, K, Cs, and 208/206Pb at the provincial-level, and Sr, Se, and Pb at the municipal level. We created a heat map at the municipal level, which showed a similar cluster classification to geographic grouping and provided an initial assessment of tobacco origins. Using OPLS-DA modeling, we achieved a 98.3% accuracy rate for the provincial scale and 97.6% for the municipal scale. It is worth noting that the importance of rankings of variables varied depending on the spatial scale of the evaluation. This study offers the first traceability fingerprint dataset of tobacco and has the potential to combat mislabeling and fraudulent conduct by identifying the geographical origin of tobacco.
1. Introduction
Tobacco (Nicotiana tabacum L.) is one of the most widespread cash crops globally (Tang et al., 2020, Wu et al., 2013). It is widely consumed for pleasure, such as in edible oils, and utilized as a treatment for postoperative pain (Matthews, Fu, Dana, & Chou, 2016) as well as agricultural pesticides (Simon-Delso et al., 2015). Tobacco has long been cultivated and produced in China. The Southwest Tobacco region, including Yunnan (YN), Guizhou (GZ), and Sichuan (SC) provinces is the most renowned and primary production area, known for the fragrant aroma, golden color, mild effect, and pure taste of the produced tobacco (Li et al., 2019). YN tobacco accounts for 50% of Chinese production, with 750,000 tons of flue-cured tobacco grown on 320,000 ha of land each year (G. Liu & Liu, 2010). There are concerns related to tobacco smuggling, illicit sales, and inferior or counterfeit tobacco entering the marketplace (Nguyen, Giang, & Pham, 2020). The distinction of flue-cured tobacco by appearance and smell only allows criminals to mislabel the origin of tobacco, increasing profits to the detriment of consumers. It is therefore of paramount importance to uncover ways to effectively profile flue-cured tobacco, as well as determine and authenticate its geographical origin.
Recently, stable isotopes combined with multi-element analyses have been used to determine the geographical origins of various agricultural products based on the correlation of isotopes and elements with ecological environments (Opatić, Nečemer, Budič, & Lojen, 2018; C. Wang et al., 2020). Geographical authentication of crops (Wadood et al., 2022, Wang et al., 2020), fruit (Muoz-Redondo, Bertoldi, Tonon, Ziller, & Moreno-Rojas, 2021), tea (Wang et al., 2022, Xia et al., 2021), garlic (Nie et al., 2022), Chinese herbal medicine (Hua et al., 2020), and aquatic products (Luo, Jiang, Chen, Zheng, Liu, & Yang, 2019) has allowed for an essential guarantee of safety and quality. Carbon isotope (δ13C) levels in plants are strongly correlated with temperature and light conditions associated with photosynthesis (Hu et al., 2016, Xia et al., 2022). The isotopic composition of nitrogen (δ15N) is impacted by fertilizers and soil contributions (Liu, Liu, Qian, Song, & Yuan, 2020). Hydrogen and oxygen isotopes in crops primarily rely on precipitation and water-use efficiency. The geographical location (altitude, latitude) exerts a significant impact on plants. Dansgaard et al. reported that δ2H and δ18O values decrease alongside increasing latitude, altitude, and distance inland (Dansgaard, 1964). Several key element contents (Liu et al., 2019) and isotope ratios, including 207/206Pb (Wang et al., 2020), and 87/86Sr (Petrini, Sansone, Slejko, Buccianti, Marcuzzo, & Tomasi, 2015) are assimilated by plants and can serve as efficient traceability tools to identify their geographical origin. Additionally, chemometric statistical analyses, such as Principal Component Analysis (PCA) (Abdi & Williams, 2010) and Orthogonal Partial Least Squares Discrimination Analysis (OPLS-DA) (Boccard & Rutledge, 2013), have been successfully utilized to comprehensively extract feature variables from geographic fingerprint information.
A limited number of papers have been published on stable isotope tracing to identify the geographic origin of tobacco. A previous study (Jamin, Naulet, & Martin, 1997) tentatively interpreted the multi-element and multi-site isotopic analysis of nicotine from tobacco leaves which indicated the influence of environmental factors on nicotine isotopic parameters. Similarly, a combination of δ2H and δ15N values may be suitable for distinguishing foreign counterfeits of Canadian cigarettes (Binette, Lafontaine, Vanier, & Ng, 2009). Elemental and isotopic compositions combined with chemometrics have been addressed in one study focused on preserving the quality and geographic traceability of Umbrian tobacco (Bontempo, Bertoldi, Franceschi, Rossi, & Larcher, 2021). To the best of our knowledge, there is currently no published research related to tracing the origin of flue-cured tobacco in China. Additionally, the accuracy of authentication or variable importance of agricultural product discrimination is necessarily related to the spatial scale considered (Xiong et al., 2022). Investigation of more spatial scales is particularly necessary for accurately determining the traceability and authenticity of tobacco.
Here we aim to fill this gap in tobacco research and explore the characterization and classification of stable isotopes and elements in tobacco grown in China. Additionally, we explored authentication and differentiation at provincial and municipal scales. We profiled YN, GZ, and SC as the main producing provinces, as well as five cities in YN: Puer (YNPE), Qujing (YNQJ), Yuxi (YNYX), Wenshan (YNWS), and Chuxiong (YNCX) (Fig. 1 and Table S1), to construct a model usable at both provincial and municipal scales, and to compare accuracy and importance of different variables. This study provides a technical basis for enhancing the quality and traceability of tobacco.
2. Material and methods
2.1. Sample collection and preparation
A total of 176 tobacco samples were collected in August 2020 from YN Province, GZ Province, and SC Province. The YN samples were collected between 21°8′–29°15′ N and 97°31′–106°11′ E (Fig. 1), at cultivation altitudes up to 2500 m. The GZ samples were collected from 24°37′–29°13′ N and 103°36′–109°35′ E, at altitudes ranging from 500 to 1800 m. The sites of SC samples were between 26°3′–29°18′ N and 100°4′–103°53′ E, with altitudes ranging from 1158 to 2758 m. Among the samples, 52 were harvested from GZ, 40 from SC, and 84 from YN. The 84 from YN were further divided into 18 samples from YNPE, 22 from YNQJ, 10 from YNYX, 18 from YNWS, and 16 from YNCX. The samples were numbered according to their locations. The collected tobacco leaves were initially roasted according to the market requirements for finished tobacco leaves (GB2635-1992) before being ground into a powder with a mortar for preservation. The samples were subsequently oven-dried at 70℃ to constant weight before experimental analysis.
2.2. Stable isotope analysis
All stable isotope analyses were carried out using a Flash 2000 HT elemental analyzer connected to the 253 Plus IRMS instrument (Thermo Fisher, USA) via a GC IsoLink combustion or pyrolysis interface (Thermo Fisher, USA). Approximately 1.5 mg of powdered samples were packed into capsules for analysis of δ13C and δ15N, and the combustion tubes were heated to 960 °C. Additionally, 0.5 mg of powdered samples were packed into capsules for δ2H analysis and a high-temperature cracking tube was placed at 1,380 °C for analysis. High-purity helium gas was used as the carrier gas and high-purity CO2, N2, and H2 were used as reference gasses, respectively.
The results of this study are presented in δ notation according to international standards, and the values were calculated as follows:
where δ i E is the delta value of the sample for element E (H, N, C) with heavier mass number i in parts per thousand (‰), and R sample and R reference are the molar ratios of heavy to light isotopes, respectively in the sample and the international reference (Nie, Shao, Zhang, Li, & Yuan, 2021). Among them, δ13C was associated with the international standard Vienna-Pee Dee Belemnite (VPDB); δ15N was relative to atmospheric AIR; δ2H was correlated with Standard Mean Ocean Water (SMOW). Reference materials (IAEA-International Atomic Energy Agency, Vienna, Austria) were used to calibrate the reference gas through two-point normalization, including USGS 40 (l-glutamic Acid, δ13CVPDB-LSVEC = –26.39 ± 0.04 ‰, δ15NAIR = –4.52 ± 0.06 ‰) and USGS41a (l-glutamic Acid, δ13CVPDB-LSVEC = +36.55 ± 0.08 ‰, δ15NAIR = +47.55 ± 0.15 ‰), USGS84 (Sicilian olive oil, δ2HVSMOW-SLAP = −140.4 ± 3.1 ‰, δ18OVSMOW-SLAP = +26.36 ± 0.50 ‰, δ13CVPDB-LSVEC = −28.80 ± 0.09 ‰), and USGS86 (Tropical Vietnamese peanut oil, δ2HVSMOW-SLAP = −207.4 ± 4.5 ‰, δ18OVSMOW-SLAP = +18.76 ± 1.03 ‰, δ13CVPDB-LSVEC = −30.63 ± 0.09 ‰). The analytical precision was lower than ± 0.2‰ for C, ± 0.2‰ for N, and ± 2.0‰ for H, respectively.
2.3. Elemental analysis
Around 0.25 g of flue-cured tobacco samples were weighed and digested in a microwave digester (ETHOS ONE, Milestone, Italy) using HNO3-H2O2 (v:v = 6:1, mL) system, and the digested samples were diluted to 50 mL with ultrapure water (≥18MΩ, Milli-Q Element ultrapure water treatment system, Millipore, USA). A mixture of internal standard solutions (10 ng/mL) of Ge (GSB 04-1728-2004), In (GSB 04-1731-2004), and Bi (GSB 04-1719-2004) were prepared using standards purchased from the National Center of Analysis and Testing for Nonferrous Metals and Electronic Materials (Beijing, China) to monitor and check instrumental drift. 30 mineral parameters, and 5 isotope ratios (84Sr/86Sr, 87Sr/86Sr, 88Sr/86Sr, 207Pb/206Pb, and 208Pb/206Pb), were measured using an inductively coupled plasma-mass spectrometer (ICP-MS, Agilent 7900, Agilent Technologies, Tokyo, Japan). The elements were separated into two groups based on their concentrations. This first group of samples was directly injected for analysis, including Li, Cr, Co, Ni, Cu, Ga, As, Rb, Cd, Cs, Ba, Pb (Multi-elemental calibration standard 2A, Agilent Technologies), Sn, Sb (Multi-elemental calibration standard-3, Agilent Technologies), Y, La, Pr, Nd, Sm, Dy, Er, Tl (Multi-elemental Solution 1, SPEX CertiPrep.), while the second group of samples was diluted 10 times, and the elements in this group included Na, Mg, Al, K, Mn, Zn, Se, and Sr (Initial calibration verification standard, Agilent Technologies). The limits of detection (LODs) for the above elements were 2.06, 0.02, 0.01, 0.05, 0.04, 0.01, 0.03, 0.01, 0.004, 0.004, 0.08, 0.03, 0.01, 0.01, 0.003, 0.004, 0.001, 0.008, 0.005, 0.001, 0.002, 0.001, 0.47, 0.10, 0.45, 0.37, 0.02, 0.21, 0.26, and 0.02 μg/kg, respectively. Instrumental reproducibility (RSDs) for concentration was lower than ± 5.0%. The accuracy of spiking experiments was in the range of 85.8%–110% for all elements. A cation exchange column (AG500W-X8200-400 mesh) was used to separate Sr-Rb, followed by ICP-MS analysis. The ICP-MS experimental parameters consisted of 10 acquisition times, 1000 repeated scans, and an integration time of 5 s. The accuracy of the instrument was lower than 0.1%.
2.4. Statistical analysis and chemometrics methods
Univariate analyses were carried out using SPSS (ver. 23.0, IBM, USA) to determine differences within the samples. Regional differences were assessed by one-way analysis of variance (ANOVA) and post-hoc Tukey’s HSD tests considering origin discrimination, a p-value ≤ 0.05 was considered statistically significant. Hierarchical Clustering Analysis (HCA) was performed using the Multi Experiment Viewer (MeV, ver. 4.9.0) software.
Orthogonal partial least-squares discriminant analysis (OPLS-DA), a supervised recognition tool, is an orthogonal exchange correction based on partial least-squares discriminant analysis (PLS-DA), which is able to filter out noise unrelated to the classification signal and improve the analytical effectiveness of the model. Key characteristic variables used to discriminate the origin of samples were identified according to variable loadings and importance for the projection values (VIPs > 1 indicates the importance). Chemometric analyses (OPLS-DA) were carried out with SIMCA 14.1 software (Umetrics, Umeå, Sweden). The drawing of VIP plots based on stable isotope and element content was accomplished using chiplot software (website address: https://www.chiplot.online/).
3. Results and discussion
3.1. Distribution of isotopes and elements in flue-cured tobacco at a provincial scale
Analytical results of three stable isotopes (δ13C, δ15N, and δ2H) in flue-cured tobacco were compared at provincial scales (Fig. S1). According to ANOVA, there were significant differences (p < 0.05) in the δ13C and δ15N values obtained from tobacco samples across three different geographical origins, as indicated by the superscripts with different letters. The average δ13C value of the sample from SC was the highest (−25.5‰), followed by that of YN (−28.1‰) and GZ (−29.3‰). This may be due to cooler weather and higher sunlight intensity in SC, which could lead to preferential 13C uptake during photosynthesis and lower CO2 respiration (Buchmann et al., 1996, Evans and Von Caemmerer, 2013). The δ15N values from YN (0.1 ± 1.2 ‰) were highest, significantly higher than SC samples (−1.9 ± 1.3 ‰), indicating that soil nutrients may have an impact on the nitrogen isotope signature. Mean δ2H values from YN, GZ, and SC were −113.7 ± 12.7‰, −112.8 ± 6.3‰, and – 121.7 ± 15.6‰, respectively. YN and GZ had higher mean δ2H values which are likely due to exposure to a more tropical (humid and warm) climate than the SC Province. Distinct climates and altitude factors that covary with geographical characteristics impart significant variations in δ2H value. Due to its wider production range and altitude range (500–2500 m), YN samples are the focus of analysis into the relationship between altitude differences and hydrogen isotope fractionation. As shown in Fig. S2, δ2H values significantly increased along with altitude increases. More positive values were found in 2000–2500 m (−110.0‰) followed by 1500–2000 m (−112.7‰), 1200–1500 m (−113.1‰), and more negative values were observed in 500–1200 m (−121.1‰). Our findings were consistent with previous research (Dansgaard, 1964).
Table 1 summarizes the content of 35 elements (including 5 isotope ratios) in 176 tobacco samples at the provincial scale. Tobacco from the three regions had significant differences for most elements (p < 0.05), except for Mn, Co, Sn, Pb, and 84/86Sr. The majority of the tobacco from the YN and SC had higher levels of the considered elements than GZ regions. For example, Na, Cs, and Sr were more abundant in YN tobacco, with mean values of 37.7 mg/kg, 62.3 μg/kg, and 276.5 mg/kg, respectively. Higher levels of Ba and Pr were found in SC samples, with mean values of 35.9 mg/kg and 149.1 μg/kg, respectively. However, GZ tobacco showed higher values of Li and Mg (4.1 mg/kg and 4.5. mg/g). It is worth noting that the concentration of rare earth elements (RREs) in GZ tobacco was generally lower than in tobacco from other regions, likely due to the different distributions of RREs in the growth soils. Previous studies have indicated the essentiality of these parameters in food authentication (Bontempo et al., 2011). Strontium and lead isotopes are important lithologic and mineral indicators, characterized by varied geological and soil conditions, and can be used for geographic traceability of agricultural products (Wang et al., 2020). As shown in Table 1, 87/86Sr, 88/86Sr, 207/206Pb, and 208/206Pb ratios in tobacco harvested from Guizhou were significantly lower than in YN and SC tobacco (p < 0.05).
Table 1.
Provincial scale | YN (n = 84) | GZ (n = 52) | SC (n = 40) | P |
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Li | 2.2 ± 2.6b | 4.1 ± 5.2a | 3 ± 3.4ab | * |
Na | 37.7 ± 35.1a | 22 ± 11.9b | 13.7 ± 35.6b | *** |
Mg | 2 ± 2.6b | 4.5 ± 2.2a | 3.8 ± 1.6a | *** |
Al | 0.3 ± 0.2a | 0.1 ± 0.05b | 0.2 ± 0.2a | *** |
K | 7.3 ± 10.2b | 24.4 ± 5.3a | 25.8 ± 8.3a | *** |
Cr | 0.5 ± 0.3a | 0.2 ± 0.1b | 0.5 ± 0.3a | *** |
Mn | 0.2 ± 0.1a | 0.2 ± 0.1a | 0.3 ± 0.3a | ns |
Co | 0.3 ± 0.2a | 0.3 ± 0.2a | 0.4 ± 0.4a | ns |
Ni | 0.8 ± 0.4a | 0.5 ± 0.3b | 0.9 ± 0.8a | *** |
Cu | 12.2 ± 7.1a | 6.1 ± 3.7b | 6 ± 4.2b | *** |
Zn | 47.4 ± 13.8a | 45.4 ± 15.5ab | 37.8 ± 20.2b | ** |
Ga | 73.4 ± 47.7a | 31.8 ± 17.2b | 91.3 ± 105.1a | *** |
As | 0.3 ± 0.2a | 0.1 ± 0.04b | 0.1 ± 0.01b | *** |
Se | 0.3 ± 0.6a | 0 ± 0.1b | 0.5 ± 0.3a | *** |
Rb | 7.3 ± 5.0a | 3.6 ± 1.8b | 3.4 ± 1.9b | *** |
Y | 0.4 ± 0.4a | 0.1 ± 0.1b | 0.4 ± 0.7a | *** |
Cd | 5.6 ± 4.8a | 3.1 ± 2.2b | 2 ± 1.2b | *** |
Sn | 61 ± 59.7a | 59.3 ± 30.7a | 63.2 ± 44.7a | ns |
Sb | 41.2 ± 28.8a | 34.9 ± 16.4ab | 24.5 ± 28b | * |
Cs | 62.3 ± 28.3a | 13.6 ± 8.7c | 32.5 ± 24.8b | *** |
Ba | 25.7 ± 16b | 23 ± 11.3b | 35.9 ± 29.3a | ** |
La | 0.9 ± 0.9ab | 0.3 ± 0.3b | 1.2 ± 2.8a | * |
Pr | 114.1 ± 90.3a | 40.9 ± 27.4b | 149.1 ± 275.5a | ** |
Nd | 0.4 ± 0.3a | 0.1 ± 0.1b | 0.5 ± 0.8a | *** |
Sm | 69.4 ± 47.2a | 20.3 ± 11.5b | 69.7 ± 88.4a | *** |
Dy | 48.3 ± 35.6a | 12.5 ± 6.8b | 42.4 ± 67.5a | *** |
Er | 21.3 ± 15.5a | 6.4 ± 3.3b | 17.8 ± 27.6a | *** |
Tl | 45.0 ± 23.8a | 42.1 ± 25.3a | 26.0 ± 19.5b | *** |
Sr | 276.5 ± 327.7a | 64.6 ± 33.2b | 69.6 ± 39.7b | *** |
Pb | 1.5 ± 1.5a | 1.2 ± 0.4a | 1 ± 0.9a | ns |
84/86Sr | 0.1 ± 0.01a | 0.1 ± 0.01a | 0.1 ± 0.01a | ns |
87/86Sr | 1.5 ± 0.5a | 1.2 ± 0.3b | 1.1 ± 0.2b | ** |
88/86Sr | 9.2 ± 0.1b | 9.2 ± 0.1b | 9.4 ± 0.2a | *** |
207/206Pb | 0.8 ± 0.01b | 0.8 ± 0.01b | 0.9 ± 0.01a | *** |
208/206Pb | 2.1 ± 0.05a | 2.1 ± 0.03b | 2.1 ± 0.02a | *** |
p-value of the ANOVA; ns: p-value > 0.05, *:0.05 > p-value > 0.01, **: 0.01 > p-value > 0.001, ***: p-value ≤ 0.001. Different letters on each variable denote differences between different geographical origins.
3.2. Geographical profiling of isotopes and elements at a municipal scale
Similarly, 84 tobacco samples collected from 5 cities in YN province at a municipal scale were analyzed for stable isotopes (Fig. 2). Mean δ13C values for each city ranged from −28.5‰ to −27.1‰, consistent with the range observed in C3 plants (−34‰ ∼ −24‰) (Krueger & Reesman, 1982). We found no differences across most cities, with the exception of YNYX. According to the weather conditions in Yunnan Province in 2020, the temperature of YNYX was higher than that of other regions, resulting in a higher δ13C value. Geographical δ13C trends were in alignment with a large-scale investigation of δ13C in leaves across China (MX et al., 2017). Additionally, YNYX tobacco leaves showed higher δ15N values compared to the other four cities. For different cities, a decreasing δ2H trend of YNQJ (−99.3 ± 1.4‰) > YNWS (−106.6 ± 4.5‰) > YNPE (−118.4 ± 4.8‰) > YNYX (−123.0 ± 3.6‰) > YNCX (−130.2 ± 9.6‰) was observed. This is primarily because the precipitation in YNCX and YNYX during the tobacco leaf growth period (May to July) is relatively low compared to other regions. In addition, major YNQJ samples were collected in high-altitude areas compared to YNWS and YNPE. Overall, differences in stable isotopes are chiefly due to latitudinal effects, precipitation, light irradiance conditions, and photosynthetic reactions (Sanchez-Bragado, Serret, Marimon, Bort, & Araus, 2019).
The full results of the elemental analysis are presented in Table S2. YNQJ samples were richer in Zn, Rb, Cd, 207/206Pb, and 208/206Pb compared to other tobacco samples. Na, Mg, Al, K, Ga, Sn, and Pb contents were significantly higher in YNYX tobacco than in tobacco grown in other regions, while the 208/206Pb ratio was lower. YNWS tobacco leaves were richer in rare earth elements (Y, La, Pr, Nd, Sm, Dy, Er, and Tl) and contained lower levels of 207/206Pb than tobacco from the other four cities. YNCX tobacco had the highest Sr concentration, with mean values of 896.8 mg/kg.
Minerals are acquired from the soil, fertilizers, and industrial pollution by growing tobacco plants. Lead isotopes (208/206Pb) from soil mineralization reflect the soil origin and geological age, increasing geographic resolution as lithology varies by region (Zhang, Sun, Zhou, Fan, Zhai, & Yin, 2002). In our study, 87/86Sr values of tobacco from YNQJ (1.8 ± 0.1%) and YNWS (1.9 ± 0.7%) were more positive than findings from YNYX (1.0 ± 0.03%) and YNCX (0.9 ± 0.1%). This is likely due to the content of 87Sr produced by the radioactive decay of 87Rb in the bedrock of each area being different, resulting in 87/86Sr having regional characteristics (Durante et al., 2021).
A heat map generated by hierarchical Pearson’s clustering was constructed to study the main sources of variability at the municipal scale based on their stable isotopes and elemental profile (Fig. S3). HCA, an unsupervised pattern recognition technique, can more comprehensively and intuitively reveal correlations between variables (stable isotopes and elements) and geographic origin. Two primary tobacco clusters were evaluated based on the mean of the 35 variables. The first group included YNYX and YNCX tobacco, while the second group included all other regions. YNPE and YNQJ tobacco leaves formed a subgroup in the second group, as well as WS. These clusters are strongly correlated with geographic location (Fig. 1). YNYX and YNCX tobacco aligned with longitude and adjacent, lower Y, La, Pr, Nd, Sm, Dy, Er, Tl contents, and 87/86Sr ratio, and had higher Na, Mg, K, Cr, and Cu values. However, YNPE, YNQJ, and YNWS tobacco had lower Sn, Pb, δ13C, Al, Se, Sr, Cr, Na, Mg, and K contents and an increased 87/86Sr ratio. HCA results provide a preliminary indication of tobacco origins, with cluster classification aligned to geographic grouping.
3.3. Geographical origin discrimination at two geographical scales
The biplots (Scores-Loading plot) for OPLS-DA models for distinguishing YN, GZ, and SC tobacco at the provincial scale are displayed in Fig. 3A. The biplots simultaneously visualize scores centroid and loading plots to interpret the observations with respect to individual variables. 176 tobacco samples were divided into three categories using 35 variables. LV1 and LV2 explained 11.6% and 7.4% of the variance of raw data, respectively. The R2Y (0.827) and Q2 (0.78) of the model indicated sufficient predictability, where R2Y explained a proportion of cumulative component variance in the model data, and Q2 represented the predictability of the model. The loading distribution of variables indicated that Cs, 208/206Pb, Cu, and Cr were representative variables for YN tobacco, while δ13C, K, and 88/86Sr were more representative of SC tobacco. GZ tobacco was correlated with Mg. Cross-validation (Table 2) of this model resulted in a total discriminant accuracy of 98.3%. The cross-validation discriminant accuracies were 96.4% for the YN province and 100% for both the GZ and SC provinces (Table 2). Similar to prior reports on potatoes (Opatić et al., 2018) and olive oil (Benincasa, Lewis, Perri, Sindona, & Tagarelli, 2007), we observed that the “fingerprint” of rare earth elements played a significant role in the geographical authentication of tobacco.
Table 2.
Scales | Date | Discriminant attribution | Discriminant accuracy |
---|---|---|---|
Provincial scale |
YN | 81/84 | 96.4% |
GZ | 52/52 | 100% | |
SC | 40/40 | 100% | |
Total | 173/176 | 98.3% | |
Municipal scale | YNPE | 18/18 | 100% |
YNQJ | 21/22 | 95.5% | |
YNYX | 10/10 | 100% | |
YNWS | 17/18 | 94.4% | |
YNCX | 16/16 | 100% | |
Total | 82/84 | 97.6% |
At the municipal scale, stable isotope and multi-element authentication of five sites in the YN province are displayed in Fig. 3B. Tobacco samples were separated into five groups according to their geographical origins. Plots of samples and variables projected from the first two latent variables (LV1 and LV2) generally distributed samples into five clusters with a slight overlap between the YNQJ and YNWS regions, where LV1 and LV2 explained 27.1% and 12.2% variance of raw data, respectively. YNCX tobacco was correlated with Sr, Se, and Ba. YNPE tobacco was correlated with the 208/206Pb and 207/206Pb ratios. YNQJ tobacco was characterized by Rb and 208/206Pb. YNWS tobacco was characterized by Cd, Sb Tl, 88/86Sr, and δ2H variables. YNYX samples were linked to Pb, As, and Sn. Cross-validation (Table 2) of this model resulted in a total discriminant accuracy of 97.6%. The prediction accuracy was 95.5% for tobacco from YNQJ and 94.4% for YNWS samples, while the remaining three regions could be accurately identified (100%). This can be explained, by YNQJ and YNCX being geographically adjacent and having similar climates in the middle and later stages of flue-cured tobacco growth compared to other regions. Overall, stable isotopes and elemental analysis of tobacco combined with chemometrics provide a promising approach for origin traceability in small growing zones.
VIP plots of stable isotope and multi-element at provincial and municipal scales were obtained from the OPLS-DA model above. The rankings of the importance of given variables (VIP > 1) were different between the two scales (Fig. 4). For the provincial scale, the most important variable was δ13C, followed by K, Cs, 208/206Pb, 88/86Sr, Cu, Cr, δ15N, As, Al, Rb, Mg, Sm, Sr, and Cd. For the municipal scale, the most discriminant variable was Sr, closely followed by Se, Pb, Sb, Rb, Tl, Mg, Cu, As, Cd, 208/206Pb, Sn, Ba, Na, K, δ2H, δ15N, and 84/86Sr. While K, Sr, 208/206Pb, Cu, As, Rb, Mg, Cd, and δ15N were key variables across both provincial and municipal scales, their contributions were different. Moreover, the number of discriminant variables for municipal-scale authentication was more pronounced than at the provincial scale. The elements Se, Pb, Sb, Sn, Ba, Na, δ2H, and 88/86Sr were important for municipal scale authentication, but not necessarily for the provincial scale, while δ13C was relevant for provincial scale authentication, which is similar to observations in D. officinale (Xiong et al., 2022). Additionally, the contour lines of δ13C and K calculated using spatial interpolation also indicate significant differences across the three provinces. The distribution of Sr and Se is significantly different for the municipal scale (Fig. S4). This result indicates that stable isotopes and elemental indicators have different distribution patterns in flue-cured tobacco at different spatial scales.
4. Conclusion
Our study indicates that stable isotope and element fingerprinting in combination with statistical analysis (e.g., OPLS-DA) can effectively differentiate tobacco obtained from different regions. Isotope and elemental indicators can provide information regarding the geographical origin of flue-cured tobacco at two spatial scales. At the provincial scale, YN had higher values of Na, Cs, and Sr and lower values of K concentration than GZ and SC. At the municipal scale (considering YNPE, YNQJ, YNYX, YNWS, and YNCX) the key variables for tobacco authentication were Sr, Se, and Pb. Furthermore, the discriminant accuracy at the provincial scale was higher (max 98.3%) than at the municipal scale (max 97.6%). The importance of ranking stable isotopes and elements differs with the spatial scale being evaluated.
Stable isotopes and elemental concentrations may be impacted by the varietal and inter-annual differences, while our research is limited to data from one year. This work established a foundation for small region traceability of tobacco, but discrimination accuracy based on samples from a single year may not be comprehensive. More sampling sites from across different provinces would also make the conclusion more dependable at the provincial scale. Further investigation is therefore needed to assess the influence of regions, years, seasons, and climate change on stable isotopes and elemental contents.
Author contributions
Lili Cui: conceptualization, data curation and writing-original draft; Huan Chen: data curation; Yuwei Yuan and Jing Nie: formal analysis and writing-review; Fengpeng Zhu, Shulei Han, and Ya’ning Fu: methodology; Hongwei Hou: investigation and supervision; Qingyuan Hu: funding acquisition and project administration; Zengping Chen: software and validation. The final version was approved by all authors.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgement
This work was supported by the Provincial and Ministerial Major Project of China under grants 110202001006 (XX-02).
Footnotes
Supplementary data to this article can be found online at https://doi.org/10.1016/j.fochx.2023.100716.
Contributor Information
Hongwei Hou, Email: qsfctc@163.com.
Qingyuan Hu, Email: huqy1965@163.com.
Zengping Chen, Email: zpchen@hnu.edu.cn.
Appendix A. Supplementary data
The following are the Supplementary data to this article:
Data availability
Data will be made available on request.
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Associated Data
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Supplementary Materials
Data Availability Statement
Data will be made available on request.