1 Introduction

The construction of dams along a river channel traps large amounts of sediments within the resulting reservoirs (Cattanéo et al. 2021). This accumulation of sediment provides the material basis for the formation and evolution of the water level fluctuation zone (WLFZ) within reservoirs (Bao et al. 2015a; Liro 2019). The WLFZ represents the primary wetlands in reservoirs (Anderson et al. 2018; Cattanéo et al. 2021). It has a range of ecological functions, including the burial and release of carbon (Keller et al. 2021; Jia et al. 2022), nutrients, and pollutants (Weber and Opp 2020; Singh et al. 2021).

Iron-bearing magnetic minerals (e.g., hematite and magnetite) in soils/sediments of WLFZ play important roles in the accumulation, migration, and transformation of pollutants (e.g., heavy metals and microplastics) and organic carbon (Dong et al. 2023; Hamdan et al. 2023). This is because they are capable of absorbing and accumulating pollutants, and rereleasing them as well when dissolution of iron minerals occurs under reducing conditions (Maher et al. 2008; Alagarsamy and Hoon 2018). Additionally, iron-bearing magnetic minerals, especially the active ones, are capable of retaining organic carbon in soils/sediments by absorption and co-precipitation with organic matters, and promoting its remineralization (Patzner et al. 2020; Dong et al. 2023). The understanding of the spatial distribution of magnetic minerals, their provenance, and water dynamics influencing their deposition within the WLFZ would provide the basis for future deeper analyses of the relationship between the sedimentation process, the deposition of magnetic minerals, and the migration and transformation processes of pollutants and organic carbon under the influences of water level fluctuations in reservoirs.

The Three Gorges Reservoir (TGR), located in the upper reach of the Yangtze River in China, is the results of the Three Gorges Dam, which is the largest hydropower project in the world. The fluctuation of water level between altitudes of 145 and 175 m in the TGR leads to the formation of the WLFZ spanning a length of 5578 km and covering an area of 348.93 km2 (Su et al. 2017). Consequently, the WLFZ of the TGR provides an ideal example to understanding the accumulation process of magnetic minerals in the WFLZ of reservoirs.

Environmental magnetism, known for its simplicity, rapidity, non-destructiveness, and cost-effectiveness, has been widely used to investigate the category, grain size, and content of magnetic minerals (Dearing et al. 1981; Thompson and Oldfield 1986; Oldfield 1991; Maher and Thompson 1999; Liu et al. 2012). Additionally, magnetic properties of sediments are capable of indicating the provenance and sedimentation dynamics influencing the magnetic properties of sediments from lacustrine, oceanic, and riverine environments (Thompson and Oldfield 1986; Maher and Thompson 1999; Franciskovic-Bilinski et al. 2014; Ahmed and Maher 2018; Chaparro et al. 2020). Currently, there are few studies investigating the accumulation process of magnetic minerals in the WLFZ of the reservoirs and lakes by using environmental magnetism. For the TGR, Luo et al. (2013) conducted a study on the magnetic properties of suspended sediments from the Yangtze River, and Yang et al. (2023) investigated the relationship between magnetic minerals and heavy metal pollutions within the WLFZ of the TGR. However, there are still lacks of detailed analyses of spatial distribution of magnetic mineral at different elevations and difference reaches within the WLFZ of the TGR, as well as their provenance and links to sedimentation dynamics.

In this study, we carry out measurements of environmental magnetism for sediments collected from various altitudes within the WLFZ, as well as nearby side-slope soils, at ten sites spanning from the tail to the head of the TGR (Fig. 1). We also assembled previously reported data on magnetic properties of suspended sediments in the upstream and tributaries flowing into the TGR. Additionally, we consider nearby side-slope soils and suspended sediments representing magnetic signals of potential sources for sediments in the WLFZ. Basing on results of magnetic properties of sediments from the WLFZ and potential sediment sources, we aim to understand the spatial distribution and provenance of magnetic minerals in sediments within the WLFZ of the TGR, and sedimentation dynamics influencing their deposition. This research will provide theoretical foundations for future deeper understanding of the impact of magnetic minerals on the retaining/releasing pollutants and organic carbon in the WFLZ of reservoirs under the influences of water-level fluctuations.

Fig. 1
figure 1

The Geographical locations relevant to this study. Panel (a) shows the location of the watershed of the Yangtze River, in China, panel (b) presents the location of the Three Gorges Reservoir in the watershed of the Yangtze River, and panel (c) highlights the specific sample sites in the TGR. In panel (b), the distribution of main rock types in the Yangtze River watershed is depicted based on work by Yang et al. (2009). The yellow stars in panel (b) represent suspended samples collected in 2011, as referenced in Luo et al. (2013). The black stars in panel (c) correspond to the sample sites investigated in this study

2 Materials and methods

2.1 Study area

The TGR extends approximately 660 km from Chongqing to Yichang in the upper reach of the Yangtze River (Fig. 1) and has a catchment area of 100,000 km2. The TGR reaches its highest water level of 175 m (above sea level) in the dry season (from October to April), and the base level of 145 m in the wet season (from May to September). At its highest water level, the TGR has a water surface area of 1080 km2 and a storage capacity of 39.3 billion m3.

After the impoundment, the TGR receives approximately 70% of the sediments discharged from the upstream of the Yangtze River (Yang et al. 2018). According to the Changjiang Water Resources Commission (2003–2017), sedimentation deposition in the TGR has reached 1679 million tonnes (Mt), with an average deposition flux of approximately 111 Mt per year. Since 2013, sediment discharge into the TGR has decreased significantly by approximately 90%, primarily due to the construction of cascade reservoirs upstream of the Yangtze River (Guo et al. 2019; Yan et al. 2022).

Mesozoic purple sand shales or mudstones of the Jurassic Shaximiao Group (J2s) are distributed widely in the TGR basin and are characterized by high weathering propensity. Correspondingly, purple soil, the weathering product of purple mudstones, is a dominant soil type in the study area (Wei et al. 2018). Additionally, early Triassic to Middle Triassic carbonate rocks also distribute in the TGR basin (Fig. 1b). The climate in the TGR basin is characterized by a humid subtropical monsoon climate, with an annual precipitation varying from 1100 to 1400 mm and an annual mean temperature of ~ 18 ℃.

2.2 Sediment collection

In July 2018, ~ 300 sediment samples from the WLFZ and nearby side-slope soils were collected at 10 specific sites (Fig. 1 and Table 1) from the tail to the head of the TGR by using a steel soil driller with a diameter of 3.5 cm. At the Jiangjing-Zhongba, Jiangjin-Gujiatuo, Nan’an, and Yichang sites, sediments from the WLFZ were obtained at a single elevation and labeled as submerged samples in Table 1. For the Fuling, Zhongxian, Wanzhou, Yunyang, Fengjie, and Wushan sites, sediments from the WLFZ were collected at altitudes ranging from 145–155 m, 155–165 m, and 165–175 m, respectively, wherever it is possible for sampling (Table 1). Side-slope soil samples were collected from nearby farmlands or forests located above the WLFZ and are annotated as subaerial samples or samples with altitudes higher than 175 m (> 175 m) in Table 1. At each altitude, a minimum of three soil or sediment sections with depths of 30 cm were randomly selected. Three subsamples were collected at depths of 0–10 cm, 10–20 cm, and 20–30 cm within each section. However, due to the thin sediment/soil layers, subsamples were only obtained at depths of 0–10 cm and 10–20 cm (Table 1) at Jiangjing-Gujiatuo site and at altitudes > 175 m at Wanzhou site. The latitudes and longitudes of the 10 WLFZ sites, the altitudes of the samples collected at each site, the number of soil or sediment sections, and the depths of subsamples within each section are provided in Table 1.

Table 1 Information for samples collected from the WLFZ and nearby side slopes in the TGR

To reveal provenance of magnetic minerals in sediment within the WLFZ of the TGR, we assembled previously reported magnetic results of suspended sediment samples from various locations in the main channel of the TGR, as well as upstream regions and tributaries of the Yangtze River (Luo et al. 2013). These samples are considered as potential sources for sediments in the WLFZ. Specifically, four samples (YD-3 to YD-7) were collected from the upstream of the Yangtze River. One suspended sediment sample (YD-8) was taken from the main stream of the TRG, as shown in Fig. 1b and Table 2. Additionally, we collected four suspended sediment samples from the tributaries of the upstream of the Yangtze River including the Jialingjiang River (sample JLJ), the WuJiang River (sample WJ), the Tuojiang River (sample TJ), and the Minjiang River (sample MJ), as depicted in Fig. 1 and Table 2 (Luo et al. 2013).

Table 2 The previously reported magnetic results of suspended samples collected from the upstream of the Yangtze River and its tributaries (Luo et al. 2013)

These suspended sediment samples were collected in 2011 during the flooding season between July and September (Luo et al. 2013), during which sediment discharged from the upstream contributes up to ~ 90% of the total sediment load into the TGR. To ensure suspended sediments were representative at each sampling location, about 100 L of water were collected at a depth of about one-quarter of the total water depth when the boat was anchored in the middle of the river. All samples were collected in the upstream of a boat to avoid artificial pollution. Water samples were then filtered through a 0.45 μm cellulose acetate membrane to isolate suspended sediments. Subsequently, the suspended matters on the filter membrane were rinsed into a clean beaker using ultrapure water and dried in an oven at 40 ℃.

2.3 Magnetic measurements

In this study, all samples collected from the WLFZ and side-slope soils in the TGR were naturally air-dried for magnetic measurements. These samples, as well as those reported in Luo et al. (2013), were all prepared and measured in the following standardized procedures. Specifically, about 2 g of sediments were placed in a plastic cubic box with a standard width of 2 cm. These allowed for the measurement of magnetic susceptibility, anhysteretic remanent magnetization (ARM), and isothermal remanent magnetization (IRM). For the measurement of temperature-dependent susceptibility (κ-T) curves and parameters using MicroMag 3900, the sediment samples were lightly ground using an agate mortar.

Low-frequency (976 Hz, χlf) and high-frequency (15616 Hz, χlf) magnetic susceptibility were measured using a MFK1-FA Kappa-bridge. Frequency-dependent magnetic susceptibility (χfd%) was defined as ((χlfhf)/χlf)*100 (Thompson and Oldfield 1986; Oldfield 1991). Anhysteretic remanent magnetization (ARM) was determined using a 100 mT peak alternating field with a 0.05 mT DC field superimposed, and was measured using an AGICO JR-6A spinner magnetometer. Isothermal remanent magnetization (IRM) was induced in two DC fields using an EUSCI DPM1 pulse magnetizer. Saturation isothermal remanent magnetization (SIRM) was induced at 1000 mT, and a reverse field of 300 mT (IRM-300mT) was applied using an EUSCI DPM1 pulse magnetizer. Remanence magnetization measured at each step was assessed using an AGICO JR-6A spinner magnetometer. S-300 mT was defined as (SIRM-IRM-300mT)/(2*SIRM)*100%, while hard IRM (HIRM) was defined as (SIRM- IRM-300 mT)/2 (Thompson and Oldfield 1986; Walden et al. 1999; Liu et al. 2012).

To provide stronger evidence for the identification of the type, grain size, and content of magnetic minerals, several representative subsamples were carefully selected for additional rock magnetic measurements. The temperature-dependent susceptibility (κ-T) curves were measured in an argon atmosphere, ranging from room temperature up to 700 °C and then back to room temperature. This was done using a MFK1-FA Kappabridge equipped with a CS-3 high-temperature furnace. Hysteresis loops, stepwise IRM, and FORC diagrams were obtained employing a MicroMag 3900 automated vibrating sample magnetometer in a maximum field of 1000 or 2000 mT (Muxworthy et al. 2002; Roberts et al. 2014). The hysteresis parameters were calculated after subtracting the paramagnetic contributions. To estimate the domain state and hence grain size of the magnetic particles, a Day plot was employed, referring to Dunlop (2002).

3 Results

3.1 Rock magnetic results and their indications of characteristics of magnetic minerals

The heating κ-T curves for representative samples obtained from the WLFZ or side-slope soils in the TGR (Fig. 2a-i) exhibit a gradual increase below ~ 200 ℃, reaching a maximum around ~ 300 ℃. This behavior is commonly observed in samples such as Zhongxian 155–165 m (Fig. 2d) and Fengjie 145–155 m (Fig. 2g), indicating the unblocking of fine-grained magnetic particles near the superparamagnetic/single domain (SP/SD) boundary (Deng et al. 2004). The subsequent decrease in magnetic susceptibility above 300 ℃, as seen in Fig. 2d and f–h, is generally attributed to the conversion of ferrimagnetic maghemite to weakly hematite (Deng et al. 2006; Ao et al. 2010). An increase in magnetic susceptibility above ~ 400 ℃ is likely caused by the transformation of iron-bearing paramagnetic minerals to magnetite (Deng et al. 2006), while a rapid drop in magnetic susceptibility at around 580 ℃, representing the Curie point of magnetite, indicates the presence of magnetite.

Fig. 2
figure 2

The temperature-dependent magnetic susceptibility curves (κ-T curves) for representative samples extracted from the water-level fluctuation zone at various sites within the Three Georges Reservoir

The hysteresis loops for these representative samples (Fig. 3a-i) exhibit a rapid rise belove ~ 200 mT and do not fully close even at 500 mT, indicating the coexistence of low-coercivity maghemite/magnetite and high-coercivity hematite, consistent with the indications from the κ-T curves. In the case of samples Zhongxian 145–155 m (Fig. 3c), Yunyang 165–175 m (Fig. 3e), and Wushan 155–165 m (Fig. 3h), their hysteresis loops display a weak wasp-waist shape, suggesting the significant contribution of hematite (Jiang et al. 2022). The relatively slower saturation of IRM acquisition curves and unsaturation of IRM even at 2000 mT provide further evidence for the presence of a large amount of hematite in these samples (Fig. 4a). Sample Wushan > 175 m (Fig. 3i) exhibits a typical hysteresis shape characteristic of high-coercivity hematite (Jiang et al. 2022). The very slowly acquisition of IRM and the incomplete saturation of IRM even at 2000 mT for sample Wushan > 175 m (Fig. 4a) further support the presence of a substantial amounts of hematite.

Fig. 3
figure 3

The hysteresis loops for typical samples taken from the water-level fluctuation zone at various sites in the Three Georges Reservoir. It should be noted that all samples have been corrected for paramagnetism

Fig. 4
figure 4

The isothermal remanent magnetization (IRM) acquisition curves (a) and the Day plot (Dunlop 2002) of magnetic hysteresis parameters (b). Both panels feature representative samples collected from the water-level fluctuation zone at various sites within the Three Georges Reservoir

The Day-plot (Fig. 4b) analysis reveals that the magnetic minerals present in the sediments of the WLFZ and nearby side-slope soils in the TGR are primarily contributed by pseudo single-domain (PSD) particles or a mixture of single domain (SD) and multiple domain (MD) particles (Dunlop 2002). This observation is further supported by the first-order reversal curve (FORC) diagrams for these samples (Fig. 5). Their FORC diagrams exhibit a closed-contour structure in the central region, with peak Bc values ranging from 10 to 15 mT and contours spreading along the Bu axis within the range of -50 to 50 mT (Muxworthy et al. 2002; Roberts et al. 2014). For sample Fengjie 145–155 m (Fig. 5g), the presence of larger closed concentric contours suggests a higher contribution from fine-grained SD particles (Roberts et al. 2014), corroborating the explanations derived from the κ-T curve analysis for this particular sample. Sample Wushan > 175 m exhibits a narrow but elongated closed-contour structure extending to ~ 140 mT on the FORC diagram (Fig. 5i), indicating the presence of typical fine-grained SD hematite (Jiang et al. 2022). This observation aligns with its location falling near the SD range on the Day-plot (Fig. 4b).

Fig. 5
figure 5

The FORC diagrams for representative samples obtained from the water-level fluctuation zone at various sites within the Three Georges Reservoir

3.2 Magnetic properties for sediments from different altitude of the WLFZ and for nearby side-slope soils

In general, the magnetic parameters of samples obtained from the WLFZ exhibit similar variations to those of the adjacent side-slope soils, particularly in terms of χfd%, χlf, SIRM, and χARMlf. In more detail, the sediment samples collected from the WLFZ and the nearby side-slope soils can be divided into four sections based on the variations of magnetic parameters (Fig. 6). These sections include the Jiangjin-Zhongba to Fuling section, Zhongxian to Yunyang section, Fengjie to Wushan section, and Yichang section. The first three sections correspond to the upper reach, middle reach, and lower reach of the TGR, respectively, while the samples from Yichang are located downstream of the Three Gorges Dam.

Fig. 6
figure 6figure 6

The Box-whisker plots illustrating the magnetic parameters of sediment samples collected from the WLFZ and nearby side-slope soils. The blue and red colored plots represent data from this study. The green colored plots represent previously reported results of suspended samples collected from the Jinshajiang River, including samples YD-3 to YD-5 (refer to Table 4 and Fig. 1b) as documented in Luo et al. (2013). The purple colored plot represents previously reported results of suspended samples collected from tributaries located upstream of the Yangtze River, including samples MJ from the Minjiang River, TJ from the Tuojiang River, JLJ from the Jialingjiang River, and WJ from the Wujiang River (see Table 4 and Fig. 1b) based on Luo et al. (2013). Lastly, the orange colored plot signifies samples YD-6 to YD-8 (Fig. 1b), which are suspended sediment samples taken from the main stream of the Yangtze River, specifically the section where the Minjiang River meet the Yangtze River down to the middle section of the TGR (illustrated as “the TGR main channel” in the figure) (Luo et al. 2013)

In the upper reach (from Jiangjin-Zhongba to Fuling), both the samples from side-slope soils (samples from altitudes > 175 m or unsubmerged samples in Fig. 6) and the samples from the WLFZ (submerged samples and samples from altitudes < 175 m in Fig. 6) exhibit low χfd% values, with an average of ~ 0.9% (Fig. 6a). This indicates a minimal presence of fine-grained superparamagnetic/single domain (SP/SD) particles (Maher 1988; Oldfield and Yu 1994). The sediment from the WLFZ and the nearby side-slope soils at Nan’an display high HIRM (Fig. 6c) values and low S-300mT values (Fig. 6d), with average values of 541.5*10−5Am2 kg−1 and 79.9%, respectively, indicating a substantial concentration of hematite (Bloemendal et al. 1992; Walden et al. 1999). These observations align with the inferences derived from the κ-T curves, hysteresis loops, and IRM curves for representative samples from the WLFZ. Other samples in the upper reach exhibit lower HIRM values but higher S-300mT values, suggesting a relatively greater contribution of magnetite and maghemite. All samples in the upper reach display relatively high χARM (Fig. 6b), χlf (Fig. 6e), and SIRM (Fig. 6f) values, with average values of 298.7*10−8m3 kg−1, 128.1*10−8m3 kg−1 and 2824.6*10−5Am2 kg−1, respectively, further supporting the inferences of a high content of magnetite and maghemite. χARM/SIRM (Fig. 6g) and χARM/χ (Fig. 6h), commonly used indicators of the grain size of magnetic minerals (Liu et al. 2012), display the lowest values within the TGR, suggesting a high concentration of coarse-grained magnetic mineral particles. Comparatively, sediment from the WLFZ (submerged samples and those from altitudes lower than 165 m) exhibit lower values of χfd%, χARM, χARM/SIRM, and χARM/χ than samples from the side-slope soils (unsubmerged samples and those from altitudes > 175 m). These differences indicate that the magnetic particles in sediments from the WLFZ are coarser than those in the nearby side-slope soils.

Compared to the upper reach, the HIRM values remain at a similar level for sediments from altitudes between 165–175 m of the WLFZ and side-slope soils in the middle reach from Zhongxian to Yunyang. However, the S-300mT values decrease rapidly for these samples. This change pattern in HIRM and S-300mT suggests a higher relative content of hematite and a lower concentration of magnetite and maghemite. The decreases in χlf, SIRM, and χARM values further support the inference of a reduction in the concentration of magnetite and maghemite. In the middle reach, samples from altitudes of 145–155 m and 155–165 m show increased values of χlf, SIRM, χARM, and S-300 mT compared to samples at altitudes higher than 165 m, indicating an increase in the content of magnetite/maghemite. Additionally, χfd%, χARM/SIRM and χARM/χ values for all samples in the middle reach are larger than those for samples in the upper reach, indicating the presence of relatively finer magnetic particles in the middle reach compared to the upper reach.

For the lower reach from Fengjie to Wushan, the χlf, SIRM, HIRM and S-300mT values for all samples display a similar level to those in the middle reaches, suggesting a similar composition of magnetic minerals in the middle and lower reaches. Furthermore, there is an increasing trend in the concentration of magnetite and maghemite from the upper to the lower part of the WLFZ at Site Wushan, as indicated by the increasing trends of χlf, SIRM, and S-300mT, which are similar to those observed in the middle reach. In contrast, for samples at Fengjie, the content of magnetite/maghemite displays a decreasing trend from the upper to the lower part of the WLFZ, as inferred by HIRM, χlf, SIRM and S-300mT. Rapid increases in χfd%, χARM, χARM/SIRM and χARM/χ values for all samples at Fengjie and Wushan indicate a higher concentration of fine grain-sized SP and SD magnetic particles. Moreover, the content of SP/SD magnetic particles is higher for samples at altitudes higher than 165 m compared to samples at altitudes lower than 165 m.

For samples at Site Yichang, located downstream of the Three Gorges Dam, all magnetic parameters display a similar level to those in the lower reach from Fengjie to Wushan. The χfd% and χARM/SIRM values for submerged samples at Yichang are lower than those of unsubmerged samples, indicating a higher content of coarse-grained magnetic particles.

4 Discussions

Sedimentation hydrodynamic is a crucial factor that influences the accumulation of magnetic minerals in sediments of the WLFZ, and is primarily regulated by the strength of natural floods, the patterns of water-level fluctuations, and the morphology of the river channel, etc. (Skalak et al. 2013; Liro 2019). Sediment supply from various sources also influences the characteristics of magnetic minerals in sediments of the WLFZ (Kouhpeima et al. 2011; Pulley and Foster 2017). In this section, we firstly analyze the magnetic properties of the three potential sediment sources for the WLFZ of the TGR. Subsequently, we discuss how the magnetic properties of sediments within this zone link to sediment provenance and hydrodynamic conditions.

4.1 Magnetic property changes in different sediment sources of the WLFZ of the TGR

In analyses of sediment provenance in reservoirs, the classification of sediment sources exhibits variability, depending on the characteristics of the catchment, the sensitivity of proxies to different sources, and the availability of data, etc. (Tiecher et al. 2017; Rachels et al. 2020). In the TGR, previous studies have identified three primary of sediment sources, including the distal, the regional, and the proximal source (Wang et al. 2021a, b; Yan et al. 2022). The distal source is primarily supplied by rivers in the upper Yangtze River region, such as the Jinshajiang River, the Minjiang River, the Tuojiang River, and the Jialingjia river (Fig. 1) (Yan et al. 2022). The regional source comprises sediment contributed by adjacent tributaries of the Yangtze River within the TGR watershed, such as the Xiaojiang River and the Daninghe River (Fig. 1) (Zhou et al. 2020; Yan et al. 2022). The proximal source involves sediment derived from nearby side-slope soils due to soil erosion (Wang et al. 2021a, b).

In this study, we also categorize the provenance of magnetic minerals in sediment within the WLFZ of the TGR into the distal source, regional source, and proximal source. We propose that the nearby side-slope soils serve as the proximal source. Additionally, the lower part of the WLFZ receives sediment contribution from the upper part of the WLFZ due to bank collapse (Bao et al. 2015b, 2018). Nearby side-slope soils collected from altitudes higher than 175 m at each site can be used to represent the magnetic properties of the original soils in the upper part of the WLFZ. This assumption is based on the similar geographic environment shared by the original soils in the upper part of the WLFZ and the side slope soils above the WLFZ prior to the impoundment of the TGR. Considering the distinct differences in magnetic properties between suspended sediments from the Jinshajiang River (a major tributary) and those from tributaries of the Yangtze River within the TGR, specifically from the point where the Minjiang River meets the Yangtze River to the head of the TGR (Fig. 1 and Table 2), we classify sediments derived from the Jinshajiang River as the distal source, and sediments derived from the tributaries of the Yangtze River within the TGR as the regional source.

Previously reported elevated values of χlf, χARM, SIRM, and S-300mT for suspended sediments from the upper Yangtze River (Fig. 1; samples YZ-3 to YZ-5 in Table 2 and green-colored samples in Fig. 6) suggest the primary presence of magnetite/maghemite (Luo et al. 2013) originating from the Fe-Ti oxide ore body of the Emeishan Large Igneous Province located near Panzhihua City, southwest of Sichuan Province (Howarth et al. 2013). The suspended sediments from the main tributaries of the Yangtze River, specifically between Minjiang and the TGR (samples JLJ, WJ, TJ, MJ in Table 2, Fig. 1 and purple samples in Fig. 6), exhibit lower concentration of magnetite/maghemite but relatively higher percentages of hematite compared to the distal source (Luo et al. 2013). These magnetic properties of the tributary sediments are attributed to the prevalence of Mesozoic purple sand shales containing abundant hematite and the yellow soils derived from early Triassic to Middle Triassic carbonate rocks in the Sichuan Basin and TGR basin (Luo et al. 2013). The main rock types in the watersheds of smaller tributaries in the TGR, such as the Daninghe River, the Xiaojiang River, and the Tangxi River, are also predominantly composed of purple sand shales and carbonate rocks. Hence, it is inferred that samples JLJ, WJ, TJ, and MJ can serve as representatives of the magnetic properties of the regional sources.

Different magnetic properties are observed for side slope soils at various sections of the TGR. In the upper reach, from Jiangjin-Zhongba to Fuling, the magnetic minerals present in side slope soils are primarily coarse magnetite/maghemite, accompanied by varying amounts of hematite, indicating the magnetic properties associated with purple sand shales and yellow soils in this region. In the middle reach, from Zhongxian to Yunyang, the magnetic minerals are characterized by a significant contribution of hematite, as suggested by the low values of S-300mT. The considerable presence of hematite suggests that side-slope soils in the middle reach primarily develop on bedrocks composed of Mesozoic purple sand shales, corresponding to the distribution of purple sand shales along the main stream of the Yangtze river in this section of the TGR (Zhong et al. 2019). In the lower reach, from Fengjie to Wushan, side slope soils exhibit abundant hematite and high concentration of fine-grained SP/SD magnetic particles, as indicated by the high values of χfd%. The presence of SP/SD magnetic particles in soils is typically attributed to the pedogenesis process (Ding et al. 2020; Ouallali et al. 2023). The high content of SP/SD particles is likely due to well-developed side-slope soils in this region, potentially influenced by the persistent high levels of forest cover in the surrounding mountainous areas (Teng et al. 2019).

4.2 The responses of magnetic minerals in sediments of WLFZ within the TGR to sediment provenance and hydrodynamics

Generally, the magnetic properties of sediments from the WLFZ exhibit a similar variation trend, to some extent, as those of side-slope soils across the upper to lower reaches of the TGR. For instance, both the sediments in the WLFZ and the adjacent side-slope soils in the upper stream display relatively higher concentration of magnetite/maghemite compared to the middle and lower reaches of the TGR, as indicated by SIRM and χlf. Similarly, both sediments in the WLFZ and side-slope soils in the middle to lower reaches of the TGR exhibit higher hematite content and slightly higher relative concentrations of fine SP/SD magnetic particles than the upper reach. These covariations of magnetic properties between sediments within the WLFZ and side-slope soils are caused by a significant contribution of side-slope soils to WLFZ. The sediment contribution from side-slope soils can be caused by intense bank or shoreline erosion induced by water wave actions of increasing backwater level during reservoir impoundment (Pal 2017; Schalko et al. 2023). Surface runoff during the drawdown period, when the banks are exposed, also contributes to bank erosion (Bao et al. 2018). Side slopes or river banks have been found to supply large percent sediments to the WLFZ in other reservoirs as well, such as Lake Winnipeg in Canada (Rodrigues et al. 2018; Goharrokhi et al. 2022).

In particular, sediments from altitudes ranging from 165 to 175 m, such as at sites Zhongxian, Wanzhou, Yunyang, and Wushan (Fig. 6), exhibit magnetic properties more similar to side-slope soils than sediments from the lower parts (from 145 to 165 m) of the WLFZ. These magnetic properties observed in the upper part of the WLFZ are likely caused by a greater contribution of sediment from side-slope soils, or by that the upper part received limited sediment inputs from distal and regional sources and was predominantly composed of original soils. These findings align with the observations that the upper parts of the WLFZ predominantly experience sedimentation during the submersion season from October to April. This period coincides with a significant reduction in sediment discharge from the upstream of the Yangtze River and its tributaries (Tang et al. 2016, 2018). Simultaneously, bank and soil erosion at the upper part of the WLFZ are enhanced by the impact of water wave action (Bao et al. 2015a). Conversely, the lower section of the WLFZ experiences more frequent summer floods and longer flooding duration, resulting in the predominant presence of sediments originating from the Yangtze River and its tributaries (Tang et al. 2016, 2018). Compared to the WFLZ of the TGR, the absence of direct flood impacts were also used to explain sediment contributions in elevated banks of other reservoirs (Liro 2019).

In comparison, sediment samples collected from the entire WLFZ at all sites contain much lower amounts of magnetite/maghemite than suspended sediment samples collected in the Jinshajiang River (green-colored samples in Fig. 6) and suspended sediment samples in the main stream of the Yangtze River between the Minjiang River confluence and the Yangtze River to the TGR (samples YD-6, YD-7, and YD-8 in Fig. 1 and Table 2, and orange-colored sample in Fig. 6) (Luo et al. 2013), as indicated by χlf, χARM, SIRM, and S-300mT. These differences are likely caused by a significant, approximately 90%, reduction in sediment input into the TGR from the Jinshajiang River, which is known for its high content of magnetite/maghemite, since 2013, due to the construction of cascaded mega reservoirs such as Jinping-1 Reservoir, Xiangjiaba Reservoir, and Xiluodu Reservoir (Yang et al. 2018; Peng et al. 2020; Sun et al. 2021; Liu et al. 2023).

Additionally, the magnetic properties of sediments within the WLFZ exhibit distinct characteristics across different reaches of the TGR. In the upper reach, from Jiangjin to Fuling, the magnetite/maghemite particles of sediments within the WLFZ are coarser than those in the nearby side-slope soils, as well as coarser than those within the WLFZ in the middle and lower reach of the TGR, as indicated by χfd% χARM/SIRM and χARM/χ. This upper reach falls within the fluctuating backwater area in the TGR (Liu et al. 2022). Coarse-grained materials transported by upstream rivers are selectively deposited within the fluctuating backwater area during periods of intense floods (Liro 2016). In the case of the TGR, the discharge of drainage water coincides with the natural flooding season from June to August (Tang et al. 2021; Liu et al. 2022). Consequently, the upper reach stretching from Jiangjin to Fuling behaves like a natural river. The resulting strong hydrodynamics induce intense riverbed erosion and sediment transport, promoting the accumulation of coarse-grained magnetite/maghemites within the WLFZ located in the upper reaches of the TGR.

In the middle reach of the TGR, specifically from Zhongxian to Yunyang, the sediments in the lower part of the WLFZ (at altitudes between 145 and 165 m, Fig. 6) exhibit a higher abundance of magnetite/maghemite particles compared to sediments in the upper part of the WLFZ (above 165 m) and even more than sediments from the regional sources (as indicated by the purple-colored samples in Fig. 6). The middle reach of the TGR is located just within the permanent backwater area, characterized by a significantly reduction in water flow velocity (Tang et al. 2018). The decreased velocity within the permanent backwater area favors the deposition of sediments transported from the upstream during flooding season (Liro 2016, 2019; Naganna and Deka 2018). Additionally, the low-gradient of alluvial channel and the widened river valleys from Zhongxian to Yunyang facilitate sediment deposition (Steiger and Gurnell 2003; Miller et al. 2013; Ye et al. 2019). Consequently, relatively more magnetite/maghemite particles from the Jinshajiang River accumulated in the lower section of the WLFZ in this middle reach during the summer flooding season. The fining of magnetic particles in the middle reach compare to the upper reach can be attributed to rapid weakening of water flow velocity as well, combined with magnetic mineral contribution from nearby side-slope soils. This observation aligns with the longitudinal fining trend of suspended/bed sediment from the tail to the head of the TGR (Tang et al. 2018; Liu et al. 2022), and other reservoirs in the world (Liro 2016).

In the lower reach of the TGR, extending from Fengjie to Wushan, the increased contribution of fine SP/SD magnetic particles within WLFZ is primarily caused by intense soil erosion of nearby side slopes, where contain a significant amount of SP/SD particles in soils (Fig. 6). The steeper topography and higher altitudes in the lower reach of the TGR possibly contribute to this pattern (Ye et al. 2019). The slow water velocity in this typical permanent backwater area possibly plays a role as well. Additionally, a higher concentration of magnetite/maghemite particles in the lower part of the WLFZ at Site Wushan, compared its upper part, can be attributed to sediment influx from upstream regions of the Yangtze River during the summer flooding reason. This is similar to observations at Zhongxian, Wanzhou, and Yunyang. However, at Site Fengjie, the concentration of magnetite/maghemite in the lower part of the WLFZ is relatively lower compared to the upper part. This can be potentially attributed to limited sedimentation during the summer flooding season caused by steep slopes at this site. In other fluvial systems, it has also been observed that areas with higher relief and valley gradients exhibit reduced sedimentation in the riparian zone (Miller et al. 2013).

4.3 Limitations and uncertainties associated with the present study

It is important to acknowledge that there exist limitations and uncertainties in interpreting the response of magnetic properties to sediment provenance and hydrodynamics in the WLFZ in the TGR in this study. While sediment sources in the WLFZ in the TGR can be categorized as distal, regional, and proximal sources, and each exhibit distinct magnetic properties, the representation of the distal and regional sediment sources is constrained by a limited number of samples. Specifically, only three samples and four samples are available to characterize the magnetic properties of distal and regional sediment sources, respectively. More sediment samples from the distal and regional rivers would enhance the reliability of provenance analyses of magnetic minerals. Additionally, the hydrodynamic conditions in the middle to lower reaches of the TGR are weaker than the upper reaches, resulting in a higher accumulation of finer magnetic particles, such as SP/SD particles, in sediments. Correspondently, it is challenging to disentangle the respective contribution of hydrodynamic processes and the supply of fine SP/SD magnetic minerals from adjacent side slopes to magnetic properties observed within the WLFZ. We attribute the presence of finer magnetic minerals in the middle to lower reaches to a combination of both of the influx of magnetic minerals from nearby slopes and the reduced hydrodynamic forces. Despite these limitations and uncertainties, they do not significantly undermine our understanding of how magnetic minerals in the WLFZ of the TGR respond to sediment sources and hydrodynamic conditions.

5 Conclusions

This study investigates the magnetic properties of sediments collected at various elevations within the WLFZ at ten locations along the TGR, alongside exploring their provenance and the hydrodynamic conditions influencing their deposition. Our results reveal that the magnetic minerals found in the WLFZ are predominantly composed of magnetite/maghemite and hematite. Specifically, hematite particles, which mainly originated from nearby side-slopes soils, prevail in the higher elevations within the WLFZ (> 165 m) at all sites. Conversely, magnetite/maghemite particles, sourced from upstream basalt in the Emeishan region, prevails in the lower section (from 145 to 165 m) of the WLFZ.

Additionally, in the upper reach of the TGR, spanning from Jiangjin to Fuling, the WLFZ predominantly contains coarse-grained magnetite/maghemite particles. This composition can be primarily attributed to the strong water flow dynamics during the summer flooding season. In the middle reach, from Zhongxian to Yunyang, there is a notable disparity in the distribution of magnetic particles between the upper and lower parts of the WLFZ. The lower part contains a greater concentration of magnetite/maghemite particles dominantly sourced from the upper Yangtze River, which is caused by significantly reduced water velocity in the middle reach. Furthermore, the decreased water velocity also contributes to the presence of finer magnetic particles in the middle reach. In the lower reach, specifically from Fengjie to Wushan, there is a much higher concentration of SP/SD particles in the sediment. The increased presence of these particles can be attributed to both side-slope soil erosions and the diminished water velocity in this area. This study provides fundamental information for future investigations of how iron-bearing magnetic minerals in mediating the transport and transformation of pollutants and organic carbon within WLFZ under the influences of changes in sediment source and hydrodynamic conditions.