- 1Key Laboratory of Marine Chemistry Theory and Technology, Ministry of Education, Ocean University of China, Qingdao, China
- 2Laboratory for Marine Ecology and Environmental Science, Qingdao National Laboratory for Marine Science and Technology, Qingdao, China
- 3Key Laboratory of Ocean and Marginal Sea Geology, South China Sea Institute of Oceanology, Chinese Academy of Sciences, Guangzhou, China
Long-chain alkyl diols (LCDs) can be used as organic geochemical proxies for paleoceanographic change, especially in marginal sea areas where large volumes of sediments are deposited rapidly and continuously. However, little is known about the applicability and response on a millennium scale in relation with existing records in those sediments. We reconstruct changes in upwelling and terrestrial organic matter (OM) input in core sediments from the Zhejiang Fujian coastal station (T08) and Yangtze River Estuary station (T06) in the inner shelf of the East China Sea (ECS) over the last millennium, using the LCD based proxies: diol index 2 (DI-2), and FC321,15-diol. Our results show that DI-2 values ([(C28+C30)1,14-diols]/([(C28+C30)1,13-diols]+[(C28+C30)1,14-diols])) at T08 decrease significantly during 600–400 yr BP but increase gradually after 400 yr BP. The FC321,15-diol proxy ([C321,15-diol]×100/([(C28+C30)1,13-diols]+[(C30+C32)1,15-diols])) at T06 shows marked fluctuations during 1000–800 yr BP, followed by a significant decline during 800–500 yr BP but a subsequent increase from 500 to 300 yr BP. We find that variations in DI-2 values are broadly consistent with changes in the strength of the East Asian Summer Monsoon (EASM) and the Kuroshio Current and are likely linked to changes in the frequency and intensity of the El Niño-Southern Oscillation (ENSO). The increased strength of the EASM causes greater offshore movement of the upper layer of seawater, which in turn triggers upwelling of bottom waters formed by Kuroshio subsurface waters. We find that variations in FC321,15-diol proxy are controlled mainly by the East Asian Winter Monsoon (EAWM) and the Yangtze River discharge. By increasing the strength of the EAWM, southward transportation of material deposited in the estuary of the Yangtze River by the ECS coastal currents is promoted. In addition, we synthesize records of other organic geochemical indicators nearby core sediments in the ECS; these records emphasize the importance of reconstructing the evolutionary history of upwelling and subdividing the relative inputs of terrestrial OM. Our study provides a new means for reconstructing the evolution of upwelling and terrestrial OM input in the inner shelf of the ECS over the last millennium.
1 Introduction
Long chain alkyl diols (LCDs), which are composed of a long alkyl chain containing groups at C1 and a mid-chain position (Versteegh et al., 1997), are biomarkers that have been used as palaeoenvironmental proxies (e.g., Lattaud et al., 2017a; Zhu et al., 2018). The 1,13- and 1,15-diols are produced by eustigmatophyte algaes, which are mainly freshwater species (Rampen et al., 2014a), and only a few exist in the marine environment (Balzano et al., 2018; Rampen et al., 2022). It has been found that C321,15-diol content is higher in areas strongly influenced by river runoff and lower in relatively open marine environments (Versteegh et al., 1997; Rampen et al., 2014a), leading to the suggestion that this diol is produced in situ in rivers (de Bar et al., 2016). As a result, the riverine organic matter (OM) input index FC321,15-diol, which is based on relative C321,15-diol content, is proposed and successfully applied to reconstruct the evolutionary history of riverine OM input over the Quaternary (Lattaud et al., 2017a; Lattaud et al., 2017b). The calculation is based on the following equation:
1,14-diols are commonly found in marine sediments. The biological sources of 1,14-diols are Proboscia diatoms, which are often abundant in upwelling regions (Sinninghe Damsté et al., 2003; Rampen et al., 2007; Rampen et al., 2008). Two diol proxies (DI) based on the relative ratios of 1,14-diols to non-upwelling diols, DI-1 and DI-2, were proposed to quantify upwelling intensities in the Arabian Sea (Rampen et al., 2008) and the Antarctic (Willmott et al., 2010), respectively. The DI-1 and DI-2 are calculated as follows:
Later studies revealed that abundances of C301,15-diol in DI-1 index were more sensitive to changes in annual mean sea surface temperature than those of 1,13-diols in DI-2 index (Rampen et al., 2012). DI-1 values were also shown significantly correlated with nutrient (N, P and Si) concentrations (Rampen et al., 2012). As result, DI-2 index are less subjected to the influence from environmental factors, and can be applied in reconstructing coastal upwelling intensities.
The East China Sea (ECS) is an important marginal sea influenced by the Yangtze River discharge, which inputs 2–5 Mt/yr of particulate organic carbon (POC) and 0.9 Mt/yr of dissolved organic carbon (DOC) to the ECS every year (Wu et al., 2007). The high concentrations of POC are possibly related to particulate OM input from local vegetation sources and OM produced in situ in the river (Wu et al., 2007). The OM, which is delivered by the Changjiang Diluted Water (CDW), enters the shallow sea and is transported southward along the Zhejiang Fujian Coastal Current (ZFCC) in winter (Beardsley et al., 1985; Hu, 1994; Wang, 1998; Wang et al., 2008). Its passage is then blocked by the Taiwan Warm Current (TWC), causing deposition in the coastal zone and forming the depocenter in the inner shelf of the ECS (Guo et al., 2003; Liu et al., 2007). Under the influence of the CDW, the ECS near the Yangtze River Estuary (YRE) is significantly influenced by river input (Liu et al., 2007), which makes it an excellent location for the application of proxy for riverine OM input.
Furthermore, due to the shoreward invasion of Kuroshio subsurface water (KSSW), there is all-year-round coastal upwelling in the ECS (Mao et al., 1964; Hu et al., 1980; Ding, 1983; Xu, 1986; Luo and Yu, 1998; Jing et al., 2007), making it a suitable location for investigating past changes in coastal upwelling. In summer, southerly winds prevail along the Zhejiang and Fujian coasts, causing an increase in upwelling intensity (Jing et al., 2007). Moreover, during El Niño-like states, enhanced local wind stress leads to intensified upwelling and high nutrient content in surface waters (Zhu et al., 2018). However, due to the lack of proxy indicating the past changes in upwelling intensity, the evolutionary history of the coastal upwelling system in the ECS since the Late Holocene still remains unclear.
In this study, we analyze the compositional changes of LCDs in sediments from two cores (Figure 1) spanning the past 1000 years from the depocenter in the inner shelf of the ECS. Diol proxies are used to reconstruct upwelling intensity in the coastal upwelling areas of Zhejiang and Fujian and riverine OM input in the YRE. Combined with other palaeoenvironmental records, we conduct a preliminary investigation into the mechanisms behind environmental changes in the upwelling area along the Zhejiang and Fujian coast and the area closer to the YRE.
Figure 1 A map showing the locations of cores T06 and T08 and the circulation system in the ECS. The area marked by the gray shadow represents the depocenter of the ECS inner shelf and we use the following abbreviations: Kuroshio Current—KC; Taiwan Warm Current—TWC; Zhejiang Fujian Coastal Current—ZFCC; Changjiang Diluted Water—CDW. 255, THB-2, MD06-3040, DD2, B3-1A, F10C, and F11A denote the cores from which we compile data for comparison with our records. The black dashed circle represents main upwelling cell (Liu et al., 2007). (A detailed list of abbreviations and references to previous studies can be found in Supplementary Materials).
2 Samples and methods
2.1 Regional environment and sampling
The ZFCC, the TWC, the KSSW, and the CDW make up the circulation system of the ECS (Lee and Chao, 2003; Wu et al., 2018; Figure 1). The coastal areas of Zhejiang and Fujian in the ECS are mainly influenced by upwelling, which is caused by the combined effects of the southeasterly monsoon and the KSSW (Lie et al., 2003; Yang et al., 2011). Numerical model has shown that phosphorus-rich deep water is transported to the coastal areas of Zhejiang and Fujian by the KSSW before being upwelled to the surface water off the coast of Zhejiang (Yang et al., 2013), enhancing the primary production in the region. The process is enhanced by a strong southeasterly monsoon (Lie et al., 2003). The nearby YRE areas of the ECS are mainly influenced by the CDW. In summer, the CDW expands mainly to the northeast of the ECS, while CDW moves mostly southward along the shore in winter (Wang, 1998).
Cores T06 (122.671°E, 29.499°N, water depth 49 m) and T08 (122.472°E, 28.504°N, water depth 65 m) were recovered from the northern part of the depocenter of the ECS inner shelf (Figure 1). The cores were collected using gravity corers on the R/V Dong Fang Hong 2 in 2011 during the Project 973 Cruise. All samples were stored at −20°C before analysis.
2.2 Sample analyses
2.2.1 Radiocarbon dating and age model reconstruction
About 15–20 mg mixed benthic foraminifera (mainly are Ammonia Compressiuscula and Ammonia ketienziensis) were picked out from six horizons in cores T06 and T08 for AMS (accelerator mass spectrometry) 14C dating at Beijing University. The radiocarbon dates were converted to calendar ages using the Calib6.1.1 program (Stuiver and Reimer, 2016), with the local marine reservoir correction (ΔR) set to −128 ± 35 year (Kong and Lee, 2005). The age model was established by linear interpolation between calibrated ages. The base of the 247-cm-long T08 core was dated to 3589 yr BP, and the base of the 270-cm-long T06 core was dated to 9036 yr BP. Dating data of two cores are shown in Supplementary Materials (S1). Since LCDs measurement required a large number of samples and the study mainly focused on the changes in the late Holocene, the T08 core was sampled at 5 cm and the front section of the core samples (120 cm) was analyzed (about the past 1010 yr BP); the T06 core was sampled at 2 cm, and the front section of core samples (40 cm) was analyzed (about the past 1050 yr BP). The 14C age mode of core T08 has been reported by Wu et al. (2018). The 14C data of core T06 indicate that the sedimentary rate of the front section (40 cm) is about 0.049 cm/yr over the last 1000 years, closed to that of the adjacent core PC-6 (122.567°E, 28.968°N; about 0.054 cm/yr; Xiao et al., 2005).
2.2.2 Biomarker analysis
About 10 g freeze dried samples were grounded, and the internal standards (n-C24D50 and n-C19H39OH) were added. They were extracted ultrasonically 8 times with dichloromethane (DCM): methanol (MeOH; 3:1, v:v), followed by centrifuging. After that, all extracts were combined, dried under an N2 stream, hydrolyzed with 6% KOH–MeOH solution and extracted into n-hexane. The neutral lipids were purified using silica gel chromatography by elution with DCM : MeOH (95:5, v:v). The fraction containing alcohols was converted to derivative with N,O-bis(trimethylsilyl)-trifluoroacetamide (BSTFA) at 70 °C for 1 h prior to analyzing.
Qualitative analysis of the biomarkers was performed using gas chromatography–mass spectrometry tandem instrument (GC–MS–MS, Agilent 7890A-G70001B). Separation was achieved with a 30 m × 0.25 mm capillary column (HP-5MS) coated with 0.32 μm film thickness and He as the carrier gas at 2 mL/min. Oven temperature programming was 70–130 °C at 20 °C/min, 130–310 °C at 4 °C/min, and holding at 310 °C for 15 min. The ion source was operated in the electron ionization (EI) mode at 70 EV, and the full scan mode was analyzed in the m/z range of 50–600 amu. Single ion monitoring (SIM) method was carried out according to the characteristic ion mass charge ratio of different diols (de Bar et al., 2017).
3 Results
Four LCDs were detected in the sediment samples from core T06 (Figure 2A). C301,15-diol was present in the highest concentrations (accounting for 57%–74% of total diols, average = 64%, n = 21) followed by C281,14-diol (9%–30%, average = 19%, n = 21), C321,15-diol (8.8%–20%, average = 14%, n = 21), and finally C281,13-diol (0%–8.8%, average = 3.9%, n = 21). Six LCDs were detected in sediment samples from core T08 (Figure 2B). Again, C301,15-diol was the major diol in this core (accounting for 65%–79% of total diols, average = 72%, n = 22) followed by C321,15-diol (7%–12%, average = 9.4%, n = 22), C281,14-diol (3.9%–15%, average = 8.9%, n = 22), C301,14-diol (3.4%–7.1%, average = 5.2%, n = 22), and finally the 1,13-diols (1.4%–4.0%, average = 2.3% for C301,13-diol; 0.4%–3.2%, average = 2.0% for C281,13-diol, n = 22). Overall, the distribution of LCDs in the sediments from cores T06 and T08 shows that C301,15-diol is the dominant component, 1,14-diols are the second most abundant, and 1,13-diols are present in the lowest proportions, which is consistent with what is known about the surface sediments of the ECS (He et al., 2020).
Figure 2 Downcore variations in the relative contents of various diols species in sediment samples from (A) core T06 and (B) core T08. The contents of C301,13-diol and C301,14-diol are below the detection limit in core T06.
It is noteworthy that mono-unsaturated 1,14-diols are not detected in sediment samples from cores T06 or T08. The reason may be that the degradation of mono-unsaturated 1,14-diols is preference to saturated 1,14-diols (Rampen et al., 2014b). Moreover, previous study in the surface sediments of the ECS showed that nutrient diol index (NDI) based on 1,14-diols did not correlate well with nutrient concentrations, which may be related to the increase in silicate content due to nutrient input from freshwater such as the Yangtze River (He et al., 2020). This nutrient structure would hinder the growth of Proboscia diatoms which biosynthesize the 1,14-diols (Sinninghe Damsté et al., 2003).
4 Discussion
4.1 Evolution of upwelling intensity based on DI-2 proxy
The δ13C of total organic carbon (δ13CTOC) is readily influenced by sources (Hedges et al., 1997), plant type (Goñi et al., 1998) and microbial OM contribution (O’Leary, 1988). The δ13C values in aquatic algae are around -20‰, while the average δ13C values is -27‰ in terrestrial C3 plants and -14‰ in terrestrial C4 plants (Meyers, 1997). Previous studies have demonstrated that Yangtze River is the main source of terrestrial input along the Zhejiang coast, and the C3 plants dominates throughout the entire basin (Wu et al., 2007). Therefore, the variations in δ13CTOC values reflect the relative contribution of marine OM to C3 plants in the study area. More positive δ13CTOC values indicate higher marine OM contribution or marine productivity. In core T08, during the 1000–600 yr BP, the DI-2 values slightly decline within the range from 0.74 to 0.71, which we interpret as a relatively decreased marine productivity, as the δ13CTOC values vary from −21.9‰ to −22.1‰ (Wu et al., 2018; Figures 3B, C). The lowest DI-2 values and the most negative δ13CTOC values indicate low contribution of marine OM over the period of 600–400 yr BP, and the positive trend in DI-2 values and δ13CTOC values indicate enhanced marine OM contribution during the 400–100 yr BP (Wu et al., 2018; Figures 3B, C). We consider that the DI-2 proxy in core T08 reflects productivity changes and, therefore, upwelling intensity.
Figure 3 Records of DI-2 values in cores T06 and T08 and other environmental indicators over the past 1000 years: (A) DI-2 proxy record from core T06; (B) DI-2 proxy record from core T08; (C) δ13CTOC record from core T08, the solid line indicates a 5-point average (Wu et al., 2018); (D) EASM record reconstructed from oxygen isotope ratios (δ18O) of stalagmites in Dongge Cave, the solid line indicates a 10-point average (Wang et al., 2005); (E) Holocene KC index from the Northwest Pacific reconstructed from the abundance of the KC indicator Pulleniatina obliquiloculata in core 255 (Jian et al., 2000); and (F) ENSO index over the last millennium based on the event model, the solid line indicates a 5-point average (Moy et al., 2002).
Based on the variations in DI-2 values in core T08, we divide the time series into three periods: Period I (1000–600 yr BP), Period II (600–400 yr BP), and Period III (400 yr BP to the present). During Period I, the DI-2 values change slightly, fluctuating within the range of 0.74–0.82 with an average value of 0.78 (n = 10; Figure 3B). Analysis of the oxygen isotope ratios (δ18O) of stalagmites in Dongge Cave, indicates the relatively steady intensity of East Asian Summer Monsoon (EASM) in the period I (Wang et al., 2005; Figure 3D). The relatively constant values in the abundance of planktonic foraminifer Pulleniatina obliquiloculata during the period I, suggest a steady Kuroshio Current (KC) intensity at that time (Jian et al., 2000; Figure 3E). During period II, the DI-2 values decrease significantly, reaching the lowest value (0.55) at 500 yr BP, when the EASM and KC also weaken (Jian et al., 2000; Wang et al., 2005; Figures 3B, D, E). During Period III, the strength of the EASM gradually increases but the KC intensity is relatively steady, and the DI-2 values show an increasing trend (Jian et al., 2000; Wang et al., 2005; Figures 3B, D, E). In summary, these records indicate that the variations in EASM and the KC control the intensity of coastal upwelling in the ECS since the last 1000 years. This is consistent with modern investigation on coastal upwelling of the ECS (Jing et al., 2007; Yang et al., 2011; Yang et al., 2013). In addition, global climate fluctuations can affect regional variations in upwelling intensity. Downcore fluctuations in DI-2 values from core T08 show similar characteristics to records of El Niño-Southern Oscillation (ENSO) over the last millennium (Moy et al., 2002; Figures 3B, F), suggesting that an increase in the frequency and intensity of ENSO events may result in an increase in upwelling intensity along the Zhejiang and Fujian coasts in the ECS. Previous investigations have shown that ENSO is responsible for variations in local wind stress and thus upwelling intensity, and that strong upwelling events occur after strong El Niño warm events (Kuo et al., 2004; Hong et al., 2009; Zhu et al., 2018). This suggests that the influence of ENSO events on the DI-2 proxy in this area of the ECS cannot be excluded.
It is noteworthy that the DI-2 values in core T06 are not consistent with the trends seen in records of the EASM strength and the KC intensity. For example, during Period II, both the strength of the EASM and the KC decrease significantly (Jian et al., 2000; Wang et al., 2005), while the DI-2 values in core T06 show a slight increase (Figures 3A, D, E). This is likely that at T06, the contents of C301,13-diol and C301,14-diol are below the detection limit, and the low C281,13-diol content may have led to large deviations in the calculated DI-2 values. Hence, the DI-2 index is not applicable at T06 station.
4.2 Reconstructing the history of terrestrial OM input using the FC321,15-diol proxy
Based on variations in FC321,15-diol proxy in core T06, we identify three periods: Period I (1000–800 yr BP), Period II (800–500 yr BP), and Period III (500–300 yr BP). During Period I, FC321,15-diol values increase and then decrease, fluctuating within the range of 14.98–19.52, with an average value of 17.65 (n = 6; Figure 4A). East Asian Winter Monsoon (EAWM) records reconstructed with average particle size in the<45 µm size fraction in core DD2 indicate a relatively strong and then weakened EAWM during Period I (Xiao et al., 2004; Figures 1, 4C). During Period II, the FC321,15-diol values decline significantly, and the minimum value (11.56) occurs at about 540 yr BP, when the strength of the EAWM also decreases (Xiao et al., 2004; Figures 4A, C). During Period III, the FC321,15-diol values increase, consistent with the strengthening variations in Yangtze River discharge and the EAWM (Xiao et al., 2004; Wang et al., 2014; Figures 4A, C, D). The enhanced runoff from the Yangtze River, inferred from the modal grain size of the fine silt fraction from core MD06-3040 (Wang et al., 2014; Figure 1), leads to the increased volume of material transported by the CDW (Yang et al., 1992; Li et al., 2007). Meanwhile, the intensified EAWM would increase southward transportation of material deposited in the YRE by the ECS coastal current (Liu et al., 2007). In addition, we observe that the main phases of increased FC321,15-diol proxy in core T06 coincide well with intervals of increased Asian dust emissions at 850–750 and 540–370 yr BP (Chen et al., 2020; Figures 4A, E). A marked increase in dust storm activity is related to an enhanced EAWM (Yang et al., 2022; Figures 4C, E). In conclusion, our study indicates that the EAWM and CDW are the main mechanisms controlling riverine OM input into the Yangtze River since the last 1000 years.
Figure 4 Records of FC321,15-diol proxy in cores T06 and T08 and other environmental parameters over the past 1000 years: (A) FC321,15-diol proxy in core T06; (B) FC321,15-diol proxy in core T08; (C) EAWM strength, as reconstructed from average particle size in the<45 µm size fraction in core DD2 (Xiao et al., 2004); (D) Yangtze River discharge, as inferred from the modal grain size of the fine silt fraction from core MD06-3040 (Wang et al., 2014); and (E) changes in Asian dust activity, as inferred from Lake Gonghai, northern China (Chen et al., 2020). The black dashed line indicates that the main phases of increased FC321,15-diol values at T06 correspond well to increases in Asian dust emissions.
Although the terrestrial realm is an important source of OM to the ECS, it shows a spatial limitation. The trend of FC321,15-diol values in core T08 is inconsistent with records of EAWM intensity or Yangtze River discharge. For example, during the 900–600 yr BP interval, FC321,15-diol values decrease and then increase in core T08, showing an opposite trend to that of EAWM intensity (Xiao et al., 2004; Figures 4B, C). Furthermore, during the period of 500–300 yr BP, FC321,15-diol values fluctuate, while the Yangtze River discharge and the strength of the EAWM increase (Xiao et al., 2004; Wang et al., 2014; Figures 4B–D). Since core T08 is away from the YRE, terrestrial OM input has less influence on it in comparison to core T06.
4.3 Comparison of organic geochemical indicators in the ECS
Previous studies have suggested that natural features such as upwelling, CDW, and East Asian Monsoon (EAM) exert some of the major controls on marine ecology in the study region (Xing et al., 2011; Wang et al., 2012; Duan et al., 2014; Xing et al., 2016; Cao et al., 2017; Wang et al., 2019; Guo et al., 2020). Here, we assume upwelling is associated with increased phytoplankton productivity which is reconstructed by the sum of the concentrations of brassicasterol, dinosterol, and C37 alkenones (∑(A + B + D)) (Wu et al., 2018; Wang et al., 2019). We find that downcore variations in ∑(A + B + D) values in cores T08, F11A, F10C, and B3-1A are similar to DI-2 variations in core T08, all of which show an overall increasing trend during the past 1000 years (Figures 5Aa–e). For example, the relatively constant values in ∑(A + B + D) and DI-2 during Period I, and significantly increased ∑(A + B + D) values and DI-2 values during Period III (Wu et al., 2018; Wang et al., 2019; Figures 5Aa–e). This is attributed to a mechanism whereby enhanced KC activity and intensified upwelling supply a eutrophic environment that favors the growth of phytoplankton. However, during Period II, there are some differences between the ∑(A + B + D) and DI-2 records. At this period, the DI-2 values decrease significantly, while no apparent variations in ∑(A + B + D) values are observed in the four cores (Wu et al., 2018; Wang et al., 2019; Figures 5Aa-e). This could be interpreted that productivity changes are influenced by factors other than upwelling, such as the CDW (Duan et al., 2014; Cao et al., 2017; Guo et al., 2020) and the EAM (Wang et al., 2012; Cao et al., 2017). Therefore, the LCD based upwelling index provides a means to indirectly quantify the change in upwelling intensity for assessing the impact of upwelling on ecosystems, and plays a crucial role in future assessments and predictions of offshore fishery resources and ecological catastrophes.
Figure 5 Organic geochemical indicators synthesis for reconstructing changes in upwelling intensity and tracing terrestrial OM input in the ECS. (A) Phytoplankton productivity records: (a) DI-2 record from core T08; ∑(A + B + D) records, (A,B,D refer to alkenones, brassicasterol, and dinosterol, respectively) used here to represent changes in phytoplankton productivity, from (b) core T08 (Wu et al., 2018), (c) core F11A (Wang et al., 2019), (d) core F10C (Wang et al., 2019), and (e) core B3-1A (Wang et al., 2019); (B) Terrestrial OM input records: (a) FC321,15-diol proxy in core T06; (b) LCA/MSCA ratio in core MD06-3040 (Zheng et al., 2018); (c) OEP proxy in core MD06-3040 (Zheng et al., 2018); (d) BIT index in core T08 (Zhou et al., 2020); (e) TOC values in core THB-2 (Hu et al., 2014); (f) δ13C values in core THB-2 (Hu et al., 2014).
Besides, the sources of terrestrial OM are various, including soils, terrestrial higher plants and rivers. The FC321,15-diol proxy can be used to infer riverine OM input and to distinguish the contribution of riverine OM (Lattaud et al., 2017a; Lattaud et al., 2017b). It is thought that the BIT index reflects the contribution of fluvial soil OM (Hopmans et al., 2004), and the LCA/MSCA and OEP proxies reflect the contribution of terrestrial higher plants to terrestrial OM input (Zheng et al., 2018). The comparison of FC321,15-diol proxy with other terrestrial proxies including TOC and δ13C values, BIT index, LCA/MSCA ratio, and OEP proxy in the inner shelf of the ECS (Hu et al., 2014; Zheng et al., 2018; Zhou et al., 2020), indicates that only FC321,15-diol proxy has similar trend with TOC and δ13C values during the past 1000 years (Figure 5B). This further indicates that terrestrial OM in the ECS originates from various sources and multiple proxies for terrestrial OM would be helpful to understand the past changes in terrestrial input in this region.
5 Conclusion
We generated diol proxies records in two sediments cores (cores T08 and T06) from the inner shelf of the ECS to investigate the evolution of the coastal upwelling system and terrestrial OM input in the area over the last millennium. At T08 station from the coastal upwelling area, the variations in DI-2 values are associated with the changes in the intensity of the EASM and the KC. During Period I (1000–600 yr BP), DI-2 values show a stable yet fluctuating trend, and the upwelling of the nutrient-rich KSSW is steady under the influence of a stable EASM. During Period II (600–400 yr BP), DI-2 values decrease significantly, with the lowest value at about 500 yr BP. The collaborative weakening of the EASM and KC would have meant that offshore movement of the upper layer of seawater is reduced and the nutrient contents of the bottom waters formed by the KSSW off the coast of Zhejiang also decrease. During Period III (from 400 yr BP to the present), when DI-2 values increase, the KC is relatively stable, and the strength of the EASM gradually increases; this would have meant that upward transportation of nutrients increases resulting from enhanced offshore movement of the upper layer of seawater. Additionally, fluctuations in DI-2 values in the core T08 show similar characteristics to changes in the Holocene ENSO index over the last millennium. This suggests that the increased frequency and intensity of ENSO events may strengthen upwelling along the Zhejiang and Fujian coasts.
At T06 station near to the YRE, FC321,15-diol variations are linked with the changes in the intensity of the EAWM and Yangtze River discharge during the past 1000 years. During Period I (1000–800 yr BP), FC321,15-diol values increase and then decrease, with high values corresponding well to intervals of strengthened EAWM; a stronger EAWM would have promoted southward transportation of material deposited in the YRE by the ECS coastal current. During Period II (800–500 yr BP), FC321,15-diol values decrease significantly and the EAWM strength declines; weakening of the EAWM would have led to a decrease in southward transportation along the ECS coast. During Period III (500–300 yr BP), FC321,15-diol values increase. During this period, intensified Yangtze River discharge would have caused an increase in the volume of material stored in the estuary, and the stronger EAWM would have elevated the southward transportation of materials deposited in the YRE by the ECS coastal current. In addition, intensified Asian dust emissions would have generated increasing amounts of sediments for eolian transportation during the past 1000 years, which leads to greater terrestrial OM input.
Data availability statement
The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation. The raw data can be found in the Supplementary Material.
Author contributions
CS: Writing - Original draft preparation, Data curation, Validation. TD: Methodology, Measurement. TZ: Investigation. TG: Investigation. RoX: Core Dating. LX: Conceptualization, Supervision, Writing - Review and Editing. RB: Supervision, Writing - Review and Editing. YZ: Methodology. RuX: Writing Editing. BW: Figure Editing. All authors contributed to the article and approved the submitted version.
Funding
This study is funded by the National Natural Science Foundation of China (41876073, 92058207, and 42076037), the National Basic Research Program of China (973 Program 2010CB428901) and the Fundamental Research Funds for the Central Universities (Grant: 2020042010). This paper is also granted Taishan Young Scholars (Grant: tsqn202103030) and Shandong Natural Science Foundation (Grant: ZR2021JQ12).
Acknowledgments
We appreciate the constructive comments from the associate editor Prof. Zhaohui Zhang and two reviewers. We would like to thank the South China Sea Institute of Oceanography, Chinese Academy of Sciences and Peking University for their support of 14C age dating.
Conflict of interest
The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
Publisher’s note
All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fmars.2022.1027561/full#supplementary-material
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Keywords: long-chain alkyl diols, upwelling intensity, terrestrial organic matter input, inner shelf of the East China Sea, Late Holocene
Citation: Song C, Dang T, Zhang T, Ge T, Xiang R, Xing L, Bao R, Zhou Y, Xiao R and Wu B (2022) Evolutions of upwelling and terrestrial organic matter input in the inner shelf of the East China Sea in the last millennium revealed by long-chain alkyl diols proxies. Front. Mar. Sci. 9:1027561. doi: 10.3389/fmars.2022.1027561
Received: 25 August 2022; Accepted: 17 October 2022;
Published: 03 November 2022.
Edited by:
Zhaohui Zhang, Zhejiang University, ChinaReviewed by:
Zeynep Erdem, Royal Netherlands Institute for Sea Research (NIOZ), NetherlandsDing He, Hong Kong University of Science and Technology, Hong Kong SAR, China
Copyright © 2022 Song, Dang, Zhang, Ge, Xiang, Xing, Bao, Zhou, Xiao and Wu. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.
*Correspondence: Lei Xing, eGluZ2xlaUBvdWMuZWR1LmNu; Rui Bao, YmFvcnVpQG91Yy5lZHUuY24=