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Biomedical Journal of Scientific & Technical Research

January, 2020, Volume 24, 3, pp 18238-18247

Research Article

Research Article

Spatial Variations of Phytochemistry in Salvia Miltiorrhiza and Environmental Factors

Xiaoyu Chen1, Chao He1, Jie Cui1, Binbin Yan2, Yeye Geng3, Junling Hou3*, Wenquan Wang1,3,4* and Weixu Chen5

Author Affiliations

1Institute of Medicinal Plant Development, Chinese Academy of Medicinal Sciences and Peking Union Medical Collage, Beijing, China

2College Pharmacy, Chengdu University of Traditional Chinese Medicine, Chengdu, China

3School of Chinese Materia Medica, Beijing University of Chinese Medicine, Beijing, China

4Engineering Research Center of Good Agricultural Practice for Chinese Crude Drugs, Ministry of Education, Beijing, China

5Shang yao hua yu (LinYi) Tradtional chineese Medicine Resouces Co.,Ltd, Shandong, China

Received: December 03, 2019 | Published: January 08, 2020

Corresponding author: Wenquan Wang, Institute of Medicinal Plant Development, Chinese Academy of Medicinal Sciences and Peking Union Medical Collage, Beijing, China

Junling Hou, School of Chinese Materia Medica, Beijing University of Chinese Medicine, Beijing, China

DOI: 10.26717/BJSTR.2020.24.004051

Abstract

To provide a basis for controlling the quality of Salvia miltiorrhiza Bunge under artificial cultivation, the present work was designed to evaluate the fingerprinting and six major bioactive compounds, that is, salvianolic acid B (SAB), rosmarinic acid (RA), dihydrotanshinone I (DTSI), cryptotanshinone (CTS), tanshinone I (TSI) and tanshinone IIA (TSIIA), in major production areas in China and analyse the correlations with such factors as climate, geography and soil. The results showed that RA and SAB responded similarly to the environment factors, and RA contributed more to the phytochemical differentiation and displayed significant positive correlations with Ca and Tp and negative correlations with monthly precipitation. DTSI, CTS, TSI and TSIIA responded similarly to the environment factors, of which, DTSI and TSI were significantly correlated with environmental factors. DTSI and TSI displayed negative correlations with monthly and annual average temperature and DTSI displayed positive correlation with Mn and Zn. It was concluded that chemical variations of S. miltiorrhiza were strongly correlated with soil, and phenolic acids displayed significant negative correlations with monthly precipitation and tanshinones displayed significant negative correlations with environmental changes of temperature.

Keywords: Bioactive Components; Climate; Geography; Soil Characteristics

Abbreviations: SAB: Salvianolic Acid B; RA: Rosmarinic Acid; DTSI: Dihydrotanshinone I; CTS: Cryptotanshinone; TSI: Tanshinone I; TSIIA: Tanshinone IIA; PCA: Principal Component Analysis; AP: Available Phosphorus; AN: Available Nitrogen

Introduction

Salvia miltiorrhiza Bunge (Danshen in Chinese) is a traditional Chinese medicine which is used to treat cardiovascular disease, cerebrovascular disease, and other diseases [1,2], and its main two bioactive components, terpenoids and phenolic acids, contribute to these remarkable functions [3]. Phenolic acids (e.g., salvianolic acid B (SAB) and rosmarinic acid (RA)) have attracted research interest due to their antioxidant, antiatherosclerosis, and neuroprotective activities [4-6]. Tanshinones is one group of lipid-soluble bioactive ingredients in S. miltiorrhiza, which has a range of pharmacological effects, such as anticancer, antioxidant, antibacterial, and antiinflammatory activities [7-11]. The tanshinones mainly include dihydrotanshinone I (DTSI), cryptotanshinone (CTS), tanshinone I (TSI) and tanshinone IIA (TSIIA) [12]. Because of these efficacies and bioactivities, S. miltiorrhiza has been an important medicinal plant used both in Chinese medicinal formulas. Despite its long history of massive cultivation, much remains to be learned about the origin of phytochemical variation in S. miltiorrhiza, which is not only of theoretical significance in understanding the biological functions of metabolites and their evolution but also critical for quality control of S. miltiorrhiza in good agricultural practice.

It is known that medicinal plants have developed their own defense system by producing secondary metabolites which are important sources for pharmacological active products in response to environmental stresses [13,14]. A variety of environmental factors, such as climate, geographic distribution, radiation, and soil nutrition, have been proven to significantly influence the secondary metabolite profile [15-18]. There have been also some researches about influence of the ecological factors on the bioactive ingredients of S. miltiorrhiza [19,20], but which mostly focus on single factor effect. For example, the study of WANG Wei et al. [21] on the effect of soil moisture on contents of S. miltiorrhiza which reported an appropriate drought stress during cultivation is beneficial for the raise of phenolic acids. The changes of key enzyme gene expression of rosmarinic acid biosynthesis pathway during heat stress was studied [22]. And the study of YU yange et al. [23] on the relationship between inorganic elements in wild-growing plants of S. miltiorrhiza and its soil. Additional investigations into the metabolic profile of plant populations of one species inhabiting varied environments are therefore necessary to understand the complex relationships between secondary metabolites and the habits in which they are produced [18].

It was proposed that global climate change influenced overall ecosystem functions, including the secondary metabolic profiles of plants. Our previous study also implied that the local environment may play an important role in the quality of cultivated S. miltiorrhiza [24]. This raised our interest to test whether the environmental parameters influence the phytochemical diversity in cultivated S. miltiorrhiza, and which is/are the most contributive one(s). Therefore, we enlarged our sampling to include five main regions of cultivation of S. miltiorrhiza in China with more plants, as well as the corresponding climatic and geographic data and soil samples, aiming to further investigate the secondary metabolic variation of cultivated S. miltiorrhiza among geographical regions and assess the effects of different environmental variables on phytochemical variation in terms of both the overall chromatographic fingerprint and six single major compounds of S. miltiorrhiza. This work will provide a reference for controlling the quality of S. miltiorrhiza during cultivation.

Materials and Methods

Sampling

Five major cultivation regions for S. miltiorrhiza throughout eastern and central China were included for sampling in November 2017. According to the sampling principle, three quadrats were set for each sampling sites, and five batches of plant samples were collected for each quadrat according to the diagonal cross. The identity of the plants was authenticated by Professor Wenquan Wang of Institute of Medicinal Plant Development. Soil samples are collected diagonally from each quadrangle. Geographic coordinates and altitude were recorded using a global positioning system see details in Table 1 & Figure 1.

Table 1: Detailed Information of All Sampling Sites.

Figure 1: Sample location of S. miltiorrhiza.

Phytochemical Analyses with HPLC

The plant samples were dried uniformly in drying ovens at 40 ℃ and crushed after 0.355mm mesh sieve. The phytochemical diversity of S. miltiorrhiza was presented in terms of variations of both overall chromatographic fingerprints and major single compounds. The present methods followed those in Gao et al. [25] with minor modification. Analyses were performed on an Thermo Scientific DionexUltiMate 3000 Series liquid chromatograph, consisting of Ulimate 3000 Pump and a Ulimate 3000 Autosampler connected to a Ulimate 3000 Variable UV detector. The reference material for RA, SAB, DTSI, CTS, TSI and TSIIA were obtained from Shanhai Winherb Medical Techonligy Co.,Ltd. All reference material had a purity of at least 98%. An accurately weighed sample powder (0.5g) was ultrasonically extracted with 50 mL of 75% methanol for 10 min. The solutions were filtered through a 0.22μm membrane before HPLC analysis. The chromatographic separation was performed on an HPLC WondaSil C18 column (4.6mm×250mm, 5μm) using a gradient of methanol (A) and 0.01% aqueous phosphoric acid (B). The gradient program was performed as follows: 0-4 min, 35% A; 4-12 min, 35-39% A; 12-30 min, 39-45% A; 30-35 min, 45-75% A; 35-40 min, 75% A; 40-65 min, 75-85%, with flow rate of 1mL·min-1, column temperature of 30 ℃, and wavelength of 270nm. The six major compounds presented on the chromatograms of S. miltiorrhiza, including two hydrophilic Phenolic acids (RA and SAB) and four lipophilic diterpene (DTSI, CTS, TSI and TSIIA), were identified and quantified by corresponding reference compounds.

Soil Analyses

The collected soil samples were air-dried before screening through 40 mesh. The following attributes of each sample were analyzed: pH, content of available nitrogen (An), available phosphorus (Ap) and available potassium (Ak). Soil analyses were performed according to the method of Bao [26]. Six microelements, Fe, Mn, Ca, Cu, Zn, B and content of total nitrogen (Tn), total phosphorus (Tp) and total potassium (Tk) were provided by Chinese medicine resources geospatial grid information database at Beijing (http://www.tcm-resources.com/).

Climatic Data

Annual and monthly average temperature and precipitation were respectively acquired from the weather stations nearest the sampling sites, which are available from Chinese medicine resources geospatial grid information database at Beijing (http:// www.tcm-resources.com/).

Statistical Analyses

We examined the environmental correlations with both chromatographic fingerprints and the six single compounds based on comparisons within each set of the parameters. We extracted 15 characteristic peak areas comprising the fingerprint of each plant sample from the chromatograms. The variation of chromatographic fingerprints was computed via Cosine similarity comparison and principal component analysis (PCA) using SPSS19.0. Oneway ANOVA (multiple comparison) was performed to determine the statistical significance of content differences of the six major chemicals among the samples from different regions using SPSS 19.0. The test of homogeneity of variances was performed for the data before multiple comparisons, if equal variances are assumed, selected Duncan as post hoc test method; otherwise, selected TamhaneT2. Furthermore, redundancy analysis and PLS regression analysis were carried out using Canoco5.0 and Simca-P 12.0 software packages, respectively, to indicate correlation and contribution of the environmental factors with/to chromatographic fingerprints of S. miltiorrhiza. Pearson correlation analysis was applied to test the correlations between the six major components and environmental parameters using SPSS 19.0. The soil characters and environmental differentiation were also analyzed via ANOVA and PCA, respectively.

Results

Climatic, Geographic, and Soil Characteristics of the Cultivation Regions

S. miltiorrhiza has strong growth suitability and is widely distributed. The regions where the cultivated samples were collected are located from 119.0296° E to 104.536373° E, 38.4852° N to 31.0019° N. The annual rainfall in these regions varied from 423 to 1141mm, and the average yearly temperature ranged from 11.7 to 17.0 ℃. Obvious distinctions in geographic factors exist between the sites. Sichuan (SC) is at the highest elevation in altitude and is at the minimum longitude, whereas Shandong (SD) is at the lowest altitude and the maximum longitude. In latitude, Hebei (HB) is at the maximum latitude, whereas SC is at the minimum (Table 1 & Figure 1). These distinctions result in climatic differences among regions. The sampling sites in SC had the highest annual average temperature and precipitation, whereas those in HB were the opposite. The monthly average temperatures were highest in SC, with January to April and October to December had a significantly higher level, except June, July and August were highest in Henan (HN). The soil was slightly alkaline in most sites, except for HB. None of the regions were deficient in nutrients, and the soil in HB and SC exhibited distinctive high concentration of available nitrogen, and the concentration of available potassium in HB was significantly higher. The concentration of organic matter in HN and SC was significantly lower. PCA of climatic and soil factors showed that the environment of the Shanxi (SX) site was closest to the HN site, these sites were distributed in the center of the plot, whereas the HB site was near to the SD site and the SC site was the most distal site (Figure 2). The determinant bringing about these results was temperature, and the next was precipitation.

Figure 2: PCA plot for climatic and soil factors of 40 samples of S. miltiorrhiza from the five studied regions.

Phytochemical Variation of S. miltiorrhiza

Most samples showed general consistency with the main model fingerprint(M40)in the Cosine similarity analysis (>0.90) (Table 2). However, the highest mean similarities of 0.959 and 0.947 were presented in the HN and SC population, respectively, with lesser deviations of 0.068 and 0.052, indicating stable chemical profiles in these populations, whereas the SX population exhibited the lowest similarity of 0.878 with great deviation of 0.146. Moderate values were generated in the HB and SD populations (0.921±0.057 and 0.916±0.110, respectively). We used hierarchical clustering method to analysis 40 samples of 15 common peak areas. Furthermore, the PCA demonstrated the contributing rate of three principal components reached 49.43%, 14.98% and 9.14%, respectively and the PCA plot shows the SX site was closest to the SC site (Figure 3). The loading values of PCA indicated that the fifth, fourth and fifteenth (tanshinone IIA) peaks were the most contributive variable on the first axis and the second peak (RA) was the most on the second axis.

Table 2: Comparisons of Cosine Similarity between Each Plant Sample and the main model fingerprint of S. miltiorrhiza.

Figure 3: PCA plot for chromatographic fingerprints of 40 samples of S. miltiorrhiza from the five studied regions.

We further quantified the six main bioactive components, that is, rosmarinic acid (RA), salvianolic acid B (SAB), dihydrotanshinone I (DTSI), cryptotanshinone (CTS), tanshinone I (TSI) and tanshinone IIA (TSIIA) (Figures 4A-4F). RA, DTSI, CTS and TSI were present in significantly different amounts among regions as determined by one-way ANOVA (p≤0.05). Both the average content of DTSI and CTS were highest in the HB and HN population (DTSI 0.0613 and 0.0464 %, CTS 0.3280 and 0.2396 %, respectively) and lowest in the SC and SX population (DTSI 0.0067 and 0.0249 %, CTS 0.0984 and 0.0972 %, respectively). The SX population also showed the highest average content of RA (0.3410 %). The SC population showed the lowest average content of TSI (0.0492 %). Not significant regional variations in SAB and TSIIA were detected. In the SC and SX population, hydrophilic components were low, while lipophilic components were high, which were opposite in the SD and HN population.

Figure 4: Content comparisons of rosmarinic acid

A. Salvianolic acid B

B. Dihydrotanshinone I,

C. Cryptotanshinone,

D. Tanshinone I

E. Tanshinone IIA

F. Among S. miltiorrhiza from different regions. (Error bars indicate standard deviations. Lowercase letters indicate significance at the level of 95% resulted from post hoc multiple comparison of either LSD or Tamhane T2.).

40 samples were applied to explore the correlations between environment and chemical diversity. The three plots of redundancy analysis (RDA) showed the relationships between the contents of the six compounds of S. miltiorrhiza and precipitation (Figure 5A), temperature (Figure 5B), soil factors (Figure 5C). In the Figure 5A, the correlation of ordination axis was more significant with the precipitation in July (Pr7), May (Pr5), October (Pr10) and September (Pr9). Pr7, June (Pr6) and August (Pr8) were negatively correlated with the hydrophilic compositions, especially RA. Pr5 and Pr9 were negatively correlated with the lipophilic compositions. In the Figure 5B, the average temperature in March (T3), April (T4) and annual average temperature (AT) were more closely related with the bioactive components of S. miltiorrhiza, which were negatively correlated with the lipophilic compositions. In the Figure 5C, geographic factors were more closely related with the bioactive components of S. miltiorrhiza. Longitude was negatively correlated with the hydrophilic compositions, which was positively correlated with lipophilic compositions. Latitude was also positively correlated with lipophilic compositions. Rather altitude was positively correlated with hydrophilic compositions, while negatively correlated with lipophilic compositions. Soil factors such as available phosphorus (Ap), available nitrogen (An) and microelements include Cu and Zn were more closely related with bioactive components. Cu, An and Zn were negatively correlated with lipophilic compositions.

Figure 5: RDA plot showing the relationships between the contents of the six compounds of S. miltiorrhiza and precipitation

A. Temperature,

B. Soil factors

C. Pr, average monthly precipitation of each month; Apr, annual average precipitation; T, average monthly temperature of each month; AT, annual average temperature; the subscript Arabic numbers stand for month; OM, content of organic matter; An, available nitrogen; Ap, available Phosphorus; Ak, available potassium; Tn, total nitrogen; Tp, total Phosphorus; Tk, total potassium.

In addition, on the basis of the contents of the six single compounds, Pearson correlation analysis revealed only RA and DTSI were significantly correlated with precipitation (P<0.05) and only lipophilic compositions such as DTSI and TSI were significantly correlated with average temperature (P<0.05), so only RA, DTSI and TSI were significantly correlated with a number of the environmental factors. To disclose the determining factors, the environmental variables with significant correlation above 0.3 were subject to analysis of partial least-squares (PLS) regression, which is a powerful tool for searching for key factors with an algorithm eliminating distinct collinearity among numerous variables that may result in poor stability of the model. There presents the standardized PLS regression coefficients with three components, RA, DTSI and TSI (Table 3). Precipitations in July, June (Pr7, Pr6) and Ca were computed to be the successive key factors affecting the content of RA. With regard to TSI, the most important variable was available nitrogen (An). The average temperature in March (T3), available potassium (Ak) and Mn were the influential variable to DTSI.

Table 3: Standardized PLS regression coefficients with three components, RA, DTSI and TSI.

Discussion

Our present results of PCA of fingerprint (Figure 3) and ANOVA of the contents of the single compounds consistently support the similar pattern of chemical differentiation of S. miltiorrhiza among the five regions. Chemical variation of S. miltiorrhiza in the SX and SC populations resembled each other, which were completely opposite to SD and HN populations, and HB population differed from others. The six single compounds analyzed responded differently to the environmental factors (Figure 5). Hydrophilic components, RA and SAB responded similarly to the environment factors, and RA was significantly correlated with more environmental factors. Lipophilic components, DTSI, CTS, TSI and TSIIA responded similarly to the environment factors, of which, DTSI and TSI were significantly correlated with most environmental factors. It has been suggested that SAB is derived from the RA pathway. Oxidative dimerization of hydroxystilbene occurs, and laccase has been proposed to catalyze the oxidative reaction from RA to SAB [27-29]. Tanshinones are synthesized via both the cytoplasmic mevalonate (MVA) pathway and plastidial methylerythritol phosphate (MEP) pathway [29-31].

The RDA, correlation and PLS analyses suggested that environmental variables, especially, soil factors, produced a significantly effect on the secondary metabolites in S. miltiorrhiza. Our results indicated negative correlation between lipophilic tanshinones and nitrogen, Zn and Cu. And positive correlation between lipophilic tanshinones and potassium, Mn was detected. Ca produced positive correlation with RA. It is known that N, K and P are important macronutrients for plants. N is the main constituent of proteins, chlorophyll, and enzymes involved in photosynthesis and K is needed for vital functions in metabolism, growth, and stress adaptation [32,33]. A S. miltiorrhiza plot experiment showed that plant growth and all the contents of the bioactive components responded negatively to increasing N availability, suggesting that S. miltiorrhiza is not a nitrophile [34]. And another plot experiment showed that the effects of the applications of P and K fertilizers at different growth stages on the root growth and bioactive compounds were shown to vary greatly in S. miltiorrhiza and K negatively affected the accumulations of tanshinones [35]. Microelements are very important to plants, so some scholars do studies about effect of microelements on S. miltiorrhiza. Wang B through sand culture experiments got that the mechanism of Cu and Zn on the accumulation of tanshinones may be that Cu and Zn improve the activity of peroxidase and polyphenol oxidase, which promote transformation of phenolic compounds to terpenes and therefore to increase contents of danshinones [36,37].

Mn increased the activities of PPO and POD, which promote the accumulation of tanshinones in S. miltiorrhiza [38]. So, if lack of these nutrition elements in the soil, we need to fertilizer these elements to guarantee the quality of S. miltiorrhiza. Precipitation also pronouncedly influenced hydrophilic components. Precipitation parameters displayed negative correlation with chemical variations of S. miltiorrhiza, particularly RA (Figure 5 & Table 3). A plot experiment showed that the effects of drought stress on physiological characteristics were inhibitory, and drought stress could promote the accumulation of phenolic compounds [39]. A drought stress experiment showed drought stress is more advantageous to accumulate phenolic acid composition of S. miltiorrhiza lamina [40]. Water deficit has been reported to increase the expression of different genes involved in the biosynthesis of phenolic compounds [41-43]. Temperature also showed pronounced negative correlation with lipophilic components in S. miltiorrhiza, especially DTSI and TSI. Harpagoside displayed significant positive correlations with monthly and annual average temperature, which was related to heat tolerance [44]. High temperature and strong sunshine limited the content of ginsenosides through collecting Panax ginseng samples [45]. Despite reports on the effect of temperature factors on plant secondary metabolism in natural environments, an array of similar work has been carried out in controlled conditions.

In tomato plants, Anthocyanins showed pronounced increased levels when lowering the growth temperature from 24 °C to 18 °C or 12 °C [46]. Accordingly, the chemical variation of lipophilic components in S. miltiorrhiza might be related to cold tolerance. The pattern of differentiation of lipophilic components also corresponds to the longitudinal and latitudinal directions, which were negative with hydrophilic components. A positive correlation between latitude and chemical diversity was detected in juniper (Juniperus communis) needles [47]. Concentrations of anthocyanidin and delphinidin in Vaccinium myrtillus fruits varied significantly across latitude, with higher values from northern latitudes, whereas another anthocyanidin, cyanidin, was opposite [48]. Therefore, different plants or even different metabolites might differ in their responses to latitudinal variation [49]. Our result indicatied that the SC and SX populations were located at the lower latitude and longitude, and the other three were at higher longitude (Table 1). The factor of latitude comprises a series of other environmental factors, among which temperature and precipitation tend to fall with the growth of latitude.

Conclusion

Our results revealed how chemical differentiation in S. miltiorrhiza varied spatially and the regulating roles of environmental factors, but genetic and cultivational measures have not been considered in our study, which may also affect the metabolite composition of S. miltiorrhiza. However, further exploration of the insights of the present work by examination of the biological and biochemical relationships between the chemical differentiation and environmental factors, germplasms, and cultivational measures would be most interesting.

References

Research Article

Spatial Variations of Phytochemistry in Salvia Miltiorrhiza and Environmental Factors

Xiaoyu Chen1, Chao He1, Jie Cui1, Binbin Yan2, Yeye Geng3, Junling Hou3*, Wenquan Wang1,3,4* and Weixu Chen5

Author Affiliations

1Institute of Medicinal Plant Development, Chinese Academy of Medicinal Sciences and Peking Union Medical Collage, Beijing, China

2College Pharmacy, Chengdu University of Traditional Chinese Medicine, Chengdu, China

3School of Chinese Materia Medica, Beijing University of Chinese Medicine, Beijing, China

4Engineering Research Center of Good Agricultural Practice for Chinese Crude Drugs, Ministry of Education, Beijing, China

5Shang yao hua yu (LinYi) Tradtional chineese Medicine Resouces Co.,Ltd, Shandong, China

Received: December 03, 2019 | Published: January 08, 2020

Corresponding author: Wenquan Wang, Institute of Medicinal Plant Development, Chinese Academy of Medicinal Sciences and Peking Union Medical Collage, Beijing, China

Junling Hou, School of Chinese Materia Medica, Beijing University of Chinese Medicine, Beijing, China

DOI: 10.26717/BJSTR.2020.24.004051

Abstract

To provide a basis for controlling the quality of Salvia miltiorrhiza Bunge under artificial cultivation, the present work was designed to evaluate the fingerprinting and six major bioactive compounds, that is, salvianolic acid B (SAB), rosmarinic acid (RA), dihydrotanshinone I (DTSI), cryptotanshinone (CTS), tanshinone I (TSI) and tanshinone IIA (TSIIA), in major production areas in China and analyse the correlations with such factors as climate, geography and soil. The results showed that RA and SAB responded similarly to the environment factors, and RA contributed more to the phytochemical differentiation and displayed significant positive correlations with Ca and Tp and negative correlations with monthly precipitation. DTSI, CTS, TSI and TSIIA responded similarly to the environment factors, of which, DTSI and TSI were significantly correlated with environmental factors. DTSI and TSI displayed negative correlations with monthly and annual average temperature and DTSI displayed positive correlation with Mn and Zn. It was concluded that chemical variations of S. miltiorrhiza were strongly correlated with soil, and phenolic acids displayed significant negative correlations with monthly precipitation and tanshinones displayed significant negative correlations with environmental changes of temperature.

Keywords: Bioactive Components; Climate; Geography; Soil Characteristics

Abbreviations: SAB: Salvianolic Acid B; RA: Rosmarinic Acid; DTSI: Dihydrotanshinone I; CTS: Cryptotanshinone; TSI: Tanshinone I; TSIIA: Tanshinone IIA; PCA: Principal Component Analysis; AP: Available Phosphorus; AN: Available Nitrogen