• <tr id="yyy80"></tr>
  • <sup id="yyy80"></sup>
  • <tfoot id="yyy80"><noscript id="yyy80"></noscript></tfoot>
  • 99热精品在线国产_美女午夜性视频免费_国产精品国产高清国产av_av欧美777_自拍偷自拍亚洲精品老妇_亚洲熟女精品中文字幕_www日本黄色视频网_国产精品野战在线观看 ?

    Root Morphology and Anatomy Affect Cadmium Translocation and Accumulation in Rice

    2021-10-18 08:34:52XiaoAnwenChenDantingLiWaiChinYeZhihong
    Rice Science 2021年6期

    Xiao Anwen, Chen Danting, Li Wai Chin, Ye Zhihong

    Research Paper

    Root Morphology and Anatomy Affect Cadmium Translocation and Accumulation in Rice

    Xiao Anwen1, 2, Chen Danting1, Li Wai Chin2, Ye Zhihong1

    (School of Life Sciences, Sun Yat-sen University, Guangzhou 510006, China; Department of Science and Environmental Studies, The Education University of Hong Kong, 999077 Hong Kong, China)

    Paddy fields contaminated with cadmium (Cd) present decreased grain yield and produce Cd-contaminated grains. Screening for low-Cd-accumulating cultivars is a useful method to reduce the amount of Cd in the grains. The present study aimed to examine the roles of the root morphology and anatomy in Cd translocation and accumulation in rice plants. Twenty-two rice cultivars were used in the first experiment, after which two cultivars [Zixiangnuo (ZXN) and Jinyou T36 (JYT36)] were selected and used in subsequent experiments under hydroponic conditions. The results showed that there were significant differences in Cd concentrations in the shoots (ranging from 4 to 100 mg/kg) and the Cd translocation rates (shoot/root) (from 7% to 102%) among the 22 cultivars, and the shoot Cd concentration was significantly correlated with the Cd translocation rate of the 22 cultivars under 0.1 mg/LCd treatment.Compared with cultivar ZXN, JYT36 had greater root Cd uptake and accumulation but lower shoot Cd accumulation and Cd translocation rate.The number of root tips per surface area of cultivar ZXN was greater than that of JYT36, while the average root diameter was lower than that of JYT36. Compared with ZXN, JYT36 had stronger apoplastic barriers, and the Casparian bands and suberin lamellae in the root endodermis and exodermis were closer to the root apex in both the control and Cd treatments, especially for suberin lamellae in the root exodermis with Cd treatments, with a difference of 25 mm. The results also showed that, compared with ZXN, JYT36 had greater percentages of Cd bound in cell walls and intracellular Cd but lower Cd concentrations in the apoplastic fluid under the Cd treatment. The results suggested that Cd translocation, rather than root Cd uptake, is a key process that determines Cd accumulation in the rice shoots. The root morphological and anatomical characteristics evidently affect Cd accumulation in the shoots by inhibiting Cd translocation, especially via the apoplastic pathway. It was possible to pre-screen low-Cd-accumulating rice cultivars on the basis of their rootmorphology, anatomical characteristics and Cd translocation rate at the seedling stage.

    apoplastic pathway; Cd stress; Cd translocation; Cd accumulation; rice; root morphology and anatomy

    Owing to mining and other human activities, large areas of paddy fields in Asia have been contaminated with cadmium (Cd) (Williams et al, 2009; Wang et al, 2018). Compared with other food crop and vegetable species, rice can accumulate Cd more effectively from contaminated soils (Grant et al, 2008; Shi et al, 2019). Paddy fields contaminated with Cd produce rice grains containing Cd, which is a major contributor to the intake of Cd by residents (Zhuang et al, 2014). As a nonessential element, Cd is toxic and can result in human diseases, such as cancer and itai-itai disease (Nordberg et al, 2002). To avoid damage from Cd, it is necessary and critical to reduce Cd accumulation in the rice grains. Screening for rice cultivars that accumulate low amounts of Cd in the grains has been considered a useful method to reduce the health risk of rice consumption (Chi et al, 2018; Chiao et al, 2019, 2020).

    In rice plants, the major transport processes that influence Cd accumulation in the grains include root uptake and transfer of Cd from the roots to the shoots by xylem loading, redistribution by the nodes of Cd through intervascular transfer, and leaf blade remobilization of Cd to the grains by the phloem stream (Uraguchi and Fujiwara, 2013). Of these three processes, the first process is considered the key process for determining grain Cd accumulation (Liu et al, 2007; Rodda et al, 2011; Uraguchi and Fujiwara, 2012, 2013).

    The differences in Cd uptake and translocation among rice cultivars point to an interesting phenomenon.Huang et al (2017) reported that some rice cultivars exhibit greater Cd uptake by their roots but lower Cd accumulation in their aboveground parts.These differences may be due to different abilities to translocate Cd from the roots to the shoots among the cultivars (Liu et al, 2003, 2007).Cd translocation from the roots to the shoots occurs mainly through two pathways: the cell-to-cell pathway (including the symplastic and transmembrane pathways) and the apoplastic pathway (Kreszies et al, 2018). Research has focused on the cell-to-cell pathway in rice (Uraguchi and Fujiwara, 2012), but few studies have focused on the apoplastic pathway. Plants can regulate the apoplastic pathway via the formation of apoplastic barriers, which decreases and hinders the transport of water and ions by apoplastic pathway (Ma and Peterson, 2003; Tao et al, 2017). Because of the negative effect on ion transport, the formation of apoplastic barriers probably affects ion accumulation in the aboveground parts of plants (Lux et al, 2011). Compared with those of maize roots grown in hydroponics, the apoplastic barriers of maize roots grown in aeroponics developed much stronger, resulting in greater Cd accumulation in maize grown in hydroponics (Redjala et al, 2011). Similarly, inand, the clones/ecotypes have more mature apoplastic barriers and accumulate less Cd in the aboveground parts of the plants (Lux et al, 2004; Tao et al, 2017). In rice plants, apoplastic barriers are also considered to have an inhibitory effect on Cd translocation (Huang et al, 2019; Qi et al, 2020). In addition to the root anatomy, the root morphology may also influence Cd translocation. For example, maize cultivars with a greater root average diameter more effectively inhibit Cd translocation (Maksimovi? et al, 2007). Rice plants with fewer tips per surface area may have lower Cd translocation (Huang et al, 2019).However, currently, whether variation in the root anatomy and morphology of rice cultivars leads to differences in Cd translocation and accumulation in aboveground parts is unclear.

    The present study aimed to investigate the relationship between Cd translocation and Cd accumulation in the shoots of rice plants and the roles of the root morphology and anatomy in rice Cd translocation and accumulation. The hypotheses in the present study were as follows: 1) variation in the root morphology and anatomy resulted in differences in Cd translocation from the roots to the shoots and Cd accumulation in shoots among rice cultivars, and 2) lower Cd- accumulating rice cultivars tended to have stronger root apoplastic barriers to reduce Cd translocation from the roots to the shoots compared with greater Cd-accumulating cultivars. To test these hypotheses, hydroponic experiments were set up to 1) study Cd accumulation, translocation and their relationship in 22 rice cultivars in experiment 1, after which two cultivars with obvious differences in Cd accumulation in the shoots and translocation ability from the roots to the shoots were selected, and 2) investigate the changes in root morphology and anatomy in the two selected cultivars in different Cd treatments and analyze their roles in rice Cd translocation and accumulation. When rice plants are grown in low-Cd-contaminated soil, hydroponic screening is recognized as a more efficient method for pre-screening cultivars (Rout and Das, 2002). Moreover, in previous research, the modelling parameters from hydroponic experimentswere correlated with the Cd concentrations in brown rice grown in the field, indicating that the results of hydroponic experiments have certain guiding significance for the field (Chiao et al, 2019). Therefore, for both hydroponics and fields, this study would provide an improved understanding of the roles of the root morphology and anatomy in Cd translocation and accumulation in rice plants.

    RESULTS

    Accumulation and translation rates of Cd in 22 rice cultivars

    After 21 d of treatment with 0.1 mol/L Cd, the plant growths of eight rice cultivars were inhibited with their tolerant indexes ranged from 90% to 100% (Fig. S1), and the growing parameters of 22 rice cultivars were shown in Table S1.Cd tended to accumulate in the roots rather than in the shoots (Fig. 1). The ranges of Cd concentration in the shoots of the 22 rice cultivars tested were 4 to 100 mg/kg. The concentration of Cd in the shoots of rice cultivar Zixiangnuo (ZXN) was significantly greater than those of the other cultivars, and the Cd concentration of Jinyou T36 (JYT36) was one of the lowest recorded (Fig. 1-A).

    The Cd concentrations in the roots ranged from 75 to 142 mg/kg. Interestingly, for cultivar ZXN, the Cd concentration was relatively high in the shoots, but was relatively low in the roots, while in cultivar JYT36, the situation was opposite (Fig. 1-A and -B).For cultivars Liangyoupeijiu, JYT36, Nanjin 44, Nuoyou 1, Suyunuo, Tianyou 2168, Xinnuo 1 and Xiangwannuo 1, the Cd translocation rates (shoot/root) were lower than 7%, but that of cultivar ZXN was 102%, which was significantly greater than those of the other cultivars (< 0.05) (Fig. 1-C).The Cd concentrations in the shoots of the 22 cultivars were significantly and positively correlated with their Cd translocation rates (shoot/root) (Fig. 1-D). However, the Cd concentrations in the shoots of the same cultivars were not correlated with the Cd concentrations in the roots (Fig. S2).

    According to the Cd concentration in rice plant tissues and their translocation ability, two cultivars (JYT36, with higher Cd concentration in the roots, and lower Cd concentration in the shoots and Cd translocation rate, and ZXN, with the opposite properties) were selected for further research.

    Hydroponic experiment using two cultivars

    Cd tolerance and accumulation in rice

    The growth of the two rice cultivars was inhibited under Cd stress, with the longest root length, shoot height and biomass decreasing with increasing Cd concentrations. At 2.5 mg/L Cd concentration, the growth of the two rice cultivars was inhibited significantly (< 0.05) compared with the control (Table S2). The concentrations of Cd in the roots of JYT36 were greater than those of ZXN in both the 0.5 and 2.5 mg/L Cd treatments. The Cd concentration in the shoots of ZXN was significantly greater than that of JYT36 in the 0.5 mg/L Cd treatment (< 0.05) (Fig. S3).

    Concentration-dependent and time-dependent Cd uptake kinetics

    The concentration-dependent uptake kinetics experiment assessed both low- and high-affinity uptake systems. The Cd uptake ability of cultivar JYT36 was significantly greater than that of ZXN in both the low- and high-affinity uptake systems (Fig. 2-A and -B). When the Cd concentration was greater than 2500 nmol/L, the uptake curves of the two cultivars tended to be horizontal, which indicated that Cd absorption tended to be saturated (Fig. 2-A). Compared with cultivar ZXN, the uptake curve of JYT36 tended to be a linear correlation (Fig. 2-B). In the time-dependent uptake kinetics experiment, the Cd uptake ability of cultivar JYT36 was also significantly greater than that of ZXN (Fig. 2-C). Within 0?10 min, the Cd uptake level increased rapidly with increasing treatment time. After 30 min, the uptake curves of the two cultivars tended to be horizontal. Themaxandmof JYT36 were 134.3% and 78.2% greater than those of ZXN, respectively (Table S3), which together indicated that cultivar JYT36 had a greater uptake ability than ZXN did, which was consistent with the results presented in Fig. 2.

    Fig. 1. Cd concentrations in shoots (A) and roots (B), Cd translocation rate (shoot/root) (C), and correlation between Cd concentration in shoots and Cd translocation rates (shoot/root) (D) of 22 rice cultivars with 0.1 mg/L Cd treatment for 3 weeks.

    LYPJ, Liangyoupeijiu; JYT36, Jinyou T36; SYN, Suyunuo; XN1H, Xinnuo 1; TY2168, Tianyou 2168; NY1H, Nuoyou 1; QXY200, Qianxiangyou 2000; TY122, Tianyou 122; NJ44, Nanjing 44; TY998, Tianyou 998; XWN1H, Xiangwannuo 1; WFY128, Wufengyou 128; TXZ, Texianzhan;ZY808, Zhongyou 808; SY402, Shanyou402; PZ163, Peiyou 163; TY196, Tianyou 196; HY665, Huayou 665; ZD097, Zhongdao 097; SHN, Suihongnuo; ST1H, Shengtai 1; ZXN, Zixiangnuo.

    Data are Mean ± SE (= 4). Different lowercase letters indicate significant differences among the cultivars at< 0.05.

    Fig. 2. Concentration-dependent and time-dependent kinetics for Cd uptake by rice roots of cultivars Zixiangnuo (ZXN) and Jinyou T36 (JYT36).

    A, High-affinity uptake kinetics of Cd in the two cultivars.

    B, Low-affinity uptake kinetics of Cd in the two cultivars.

    C, Time-dependent kinetics of Cd in the two cultivars.

    The 10 d old intact seedlings were treated for 30 min in A and B, and treated with 180 nmol/L Cd in C. Data are Mean ± SE (= 3). Data with different lowercase letters mean significant differences between the treatments at< 0.001 (A) and< 0.05 (B).

    Characteristics of root morphology and anatomical structure under Cd stress

    Root morphology

    The number of root tips per cm2(surface area) of the two cultivars significantly and rapidly decreased with increasing Cd concentrations (Table 1). In the control and 0.5 mg/L Cd treatments, the numbers of root tips per surface area of cultivar ZXN were 82.4% and 130.0% greater than those of JYT36, respectively.The average root diameter of ZXN increased with increasing Cd concentrations and that of JYT36 significantly increased in the 0.5 mg/L Cd treatment compared with the control.The average root diameter of JYT36 was 43.0% and 28.0% greater than that of ZXN in the control and 0.5 mg/L Cd treatments, respectively (Table 1).

    Root anatomy

    Apoplastic barriers contain the Casparian bands and suberin lamellae. The present results showed that the Casparian bands and suberin lamellae of the endodermis developed earlier than those of the exodermis (Fig. 3). Moreover, the Casparian bands developed before or at the same time as the suberin lamellae (Fig. 3). The sites of the Casparian bands and suberin lamellae in the endodermis and exodermis of the two cultivars were closer to the root apex in the Cd treatment compared with the control (Figs. 3, 4 and 5).

    Table 1. Parameters of root morphology in rice with treatments of 0.5 and 2.5 mg/L Cd for 4 weeks.

    ZXN, Zixiangnuo; JYT36, Jinyou T36.

    Data are Mean ± SE (= 8). Data with different lowercase letters mean significant differences between the treatments in the same cultivar. **,< 0.01 and ***,< 0.001 mean significant differences between the cultivars in the same treatment.

    Whether under Cd stress or not, the development of the apoplastic barriers was different between the two cultivars (Figs. 3, 4 and 5). Compared with cultivar ZXN, the development of Casparian bands and suberin lamellae in the endodermis and exodermis of JYT36 occurred earlier in both the control and 2.5 mg/L Cd treatments (Fig. 3). In cultivar JYT36, the zones of endodermal Casparian band development were between 1 and 5 mm from the root apex, while in cultivar ZXN, the zones were further away from the apex, ranging between 10 and 30 mm (Fig. 3). Similarly, the deposition of the endodermal suberin lamellae in the roots of JYT36 occurred 5 mm from the root apex in the control and 1 mm from the root apex in the 2.5 mg/L Cd treatment, while that of ZXN occurred at 40 mm in the control and at 10 mm in the 2.5 mg/L Cd treatment (Fig. 3). In the control, Casparian bands and suberin lamellae in the exodermis of JYT36 occurred at 30 and 40 mm, which were 20 and 10 mm closer to the root apex than those of ZXN, respectively. When treated with 2.5 mg/L Cd, the exodermal Casparian bands and suberin lamellae of JYT36 matured at 5 mm, which were 15 and 25 mm closer than those of ZXN, respectively.

    Fig. 3. Schematic representation of endodermal and exodermal apoplastic barriers of two rice cultivars in control (CK) and Cd (2.5 mg/L) treatments.

    ZXN, Zixiangnuo; JYT36, Jinyou T36. Casparian bands and suberin lamellae in endodermis are represented by red and green lines, respectively. Casparian bands and suberin lamellae in exodermis are represented by brown and blue lines, respectively. The dotted lines indicate the early and immature deposition of the barriers and solid lines represent the Casparian bands or suberin lamellae which have developed maturely in the zone.

    To display the differences in the root anatomy structure between the two cultivars in the different Cd treatments, pictures of the section at 20 mm from the root apex were selected. In the control, the endodermal Casparian band of cultivar ZXN did not appear, but cultivar JYT36 developed an endodermal Casparian band and suberin lamellae (Figs. 4-A, 4-B, 5-A and 5-B). Moreover, the two cultivars had no exodermal Casparian bands or suberin lamellae in the control (Figs. 4-E, 4-F, 5-E and 5-F).

    Cd subcellular distribution

    The results from the Cd subcellular distribution experiment showed that Cd in the roots was transformed into bound Cd (Cd bound in the cell wall and membrane), intracellular Cd and Cd in the apoplastic fluid.Cd in the roots was distributed mainly in the cell and was bound to the cell wall, while the amount of Cd in the apoplastic fluid was lower (Fig. 6-A).Compared with cultivar ZXN, JYT36 had more bound and intracellular Cd in the roots in the Cd treatment. With Cd treatment, the bound Cd in JYT36 was 17%?21% greater than that in ZXN. In the 0.5 mg/L Cd treatment, the intracellular Cd in the roots of JYT36 was 1.55 times greater than that of ZXN (Fig. 6-A), while the Cd concentration in the apoplastic fluid in JYT36 roots was significantly lower than that in ZXN roots (Fig. 6-B).

    Fig. 4. Comparison of development of Casparian bands at 20 mm distance from rice root tips with treatments of control and 2.5 mg/L Cd for 4 weeks.

    A to D are endodermis sections, and E to H are exodermis sections; A, C, E and G are cultivar Zixiangnuo, and B, D, F and H are cultivar Jinyou T36; A, B, E and F are in the control treatment, and C, D, G and H are in 2.5 mg/L Cd treatment. Arrow heads refer to the Casparian bands. Scale bars are 20 μm in A, B, E, F and G, and 50 μm in C, D and H.

    Fig. 5. Comparison of development of suberin lamellae at 20 mm distance from rice root tips with treatments of control and 2.5 mg/L Cd for 4 weeks.

    A to D are endodermis sections, and E to H are exodermis sections; A, C, E and G are cultivar Zixiangnuo, and B, D, F and H are cultivar Jinyou T36; A, B, E and F are in control treatment, and C, D, G and H are in 2.5 mg/L Cd treatment. Scale bars are 20 μm in A, B, E and F, and 50 μm in C, D, G and H.

    DISCUSSION

    Cd translocation determined Cd accumulation in shoots

    The accumulation of Cd in the shoots is affected by root Cd uptake and Cd translocation from the roots to the shoots (Uraguchi and Fujiwara, 2013). In the present study, the Cd concentrations in the shoots of the 22 cultivars were not correlated with the Cd concentrations in the roots (Fig. S2), which indicated that Cd uptake by rice roots was not a determining factor in the Cd concentration in the shoots. In addition, in both the concentration-dependent and time-dependent uptake kinetics experiments, the Cd uptake ability of cultivar JYT36 was significantly greater than that of ZXN (< 0.05), and themaxof JYT36 was 2.34 times over that of ZXN (Fig. 2 and Table S3), which was consistent with the fact that the Cd concentration in the roots of JYT36 was significantly higher than that of ZXN (Fig. 1-B). However, the Cd concentration in the aboveground parts of cultivar ZXN was higher than that of JYT36 (Figs. 1-A and S3), which indicated that the Cd uptake ability by the roots was not directly responsible for the differing Cd accumulations in the aboveground parts in the two rice cultivars. Uraguchi et al (2009) also reported that the Cd uptake ability of rice cultivar Habataki (high Cd concentration in the grains) is lower than that of cultivar Sasanishiki (low Cd in the grains), which also indicated that Cd uptake by the roots may not be as important to Cd accumulation in the aboveground rice parts (e.g., the grains). In summary, the root Cd uptake kinetics was not directly responsible for the differing Cd accumulation in the aboveground parts in the rice cultivars studied.

    Fig. 6. Distribution of Cd in rice roots with treatments of 0.5 and 2.5 mg/L Cd for 4 weeks.

    A, Cd bound in cell wall and intracellular Cd.

    B, Cd concentration in the apoplastic fluid.

    ZXN, Zixiangnuo; JYT36, Jinyou T36. Data are Mean ± SE (= 3). * and ** mean significant differences between the cultivars in the same treatment at the 0.05 and 0.01 levels, respectively.

    In this study, the positive correlation between the Cd translocation rate (shoot/root) and Cd concentration in the shootssuggested that Cd translocation from the roots to the shoots, rather than root Cd uptake, plays a key role in Cd accumulation in the aboveground parts of the rice plants (Fig. 1-D), which was consistent with the results of Uraguchi et al (2009). Therefore, Cd translocation from the roots to the shoots can explain the difference in Cd accumulation in the aboveground parts of the rice plants in the two cultivars, while the Cd translocation rate (shoot/root) of cultivar ZXN was significantly greater than that of JYT36 (< 0.05) (Figs. 1-A, 1-C and S3). The present results showed that Cd translocation from the roots to the shoots, rather than root Cd uptake ability, is a key step in determining Cd accumulation in the above- ground parts of rice plants.

    Strong apoplastic barriers, a large average root diameter and a small number of root tips resulted in low Cd translocation

    Cadmium translocation from the roots to the shoots is influenced largely by the channel between the root epidermis and xylem, and the formation of apoplastic barriers can limit Cd translocation to the xylem (Lux et al, 2011; Huang et al, 2019). Compared with ZXN, the formation sites of the Casparian bands and suberin lamellae in the endodermis and exodermis of JYT36 occurred closer to the root apex, and the development of the apoplastic barriers occurred earlier (Fig. 3). At the same site in the roots, whether in the control or Cd treatment, the Casparian bands and suberin lamellae in the endodermis and exodermis of JYT36 were more mature than those of ZXN, which indicated that, compared with ZXN, JYT36 had stronger apoplastic barriers (Figs. 4 and 5).In the root endodermis and exodermis, root apoplastic barriers developed from the cell wall owing to the deposition of hydrophobic biomacromolecule polymer lignins and suberins (Schreiber et al, 1999; Man et al, 2018), indicating that more lignin and suberin depositions usually built a stronger apoplastic barrier. On account of the hydrophobic properties, the strong apoplastic barriers are physical barriers, which make the cell wall less penetrable and protect against Cd radial transport to the xylem in the stele. This would slow apoplastic fluid and decrease the Cd concentration in apoplastic fluid, resulting inthe Cd transported by the apoplastic pathwaybeing intercepted and absorbed by the cell near the barrier (Redjala et al, 2011; Yamaguchi et al, 2011), indicating that the intracellular Cd in the roots may increase. These previous results were consistent with the present results: compared with ZXN, JYT36, which had stronger apoplastic barriers, had higher concentrations of intracellular Cd in the roots and obviously lower Cd concentrations in the apoplastic fluid (< 0.05) (Fig. 6-B). Moreover, lignin in root apoplastic barriers contains many functional groups, which can effectively integrate Cd into the cell wall (Parrotta et al, 2015; Loix et al, 2017). The present results showed that roots with stronger apoplastic barriers (cultivar JYT36) can effectively combine and retain more Cd in the form of bound Cd (Fig. 6-A). These two processes greatly decreased Cd mobility and retained more Cd in the roots of JYT36 compared with ZXN (Fig. S3).These results suggested that rice roots with stronger apoplastic barriers have a greater ability to limit Cd translocation, which was consistent with the results of other plant species (e.g., maize) reported by Redjala et al (2011). The inhibitory effect of apoplastic barriers on Cd was realized mainly through affecting Cd translocation via the apoplastic pathway.

    The average root diameter reflects the distance of water and Cd radial flow from the epidermis to the xylem directly, and an increase in the root diameterenhances the resistance to Cd translocation (Maksimovi? et al, 2007). In the present study, the average root diameter of cultivar JYT36 (low Cd-translocation ability) was significantly larger than that of ZXN (high Cd-translocation ability), which reflected that JYT36 better inhibited Cd translocation (Table 1). The number of root tips is an important index to measure root ion uptake because the apical zone of the root is the region where cation absorption is the most active (Boominathan and Doran, 2003). Generally, only in the root apex and the region where lateral roots emerge can cations enter the xylem through the apoplast pathway, which can translocate Cd cations well (White, 2001; Moore et al, 2002). The number of root tips reflects the effective area of Cd absorption directly and influences the Cd load in the root xylem. The number of root tips per cm2of surface area of cultivar JYT36 was significantly lower than that of ZXN, which reflected that Cd mobility in the JYT36 roots was less than that in ZXN, allowing for the retention of more Cd (Table 1).

    Compared with ZXN, the Cd uptake ability of JYT36 was greater, resulting in greater Cd accumulation in the roots. However, JYT36 had more mature apoplastic barriers in the roots, a larger average root diameter and a smaller number of root tips per surface area in both the control and Cd treatments to inhibit Cd translocation (especially by the apoplastic pathway), resulting in more Cd retained in the rice roots in the form of bound and intracellular Cd,alow Cd translocation rate (shoot/root)and low Cd accumulation in the aboveground parts. It was possible to pre-screen low- Cd-accumulating rice cultivars according to their rootmorphology, anatomical characteristics and Cd translocation rate (shoot/root) at the seedling stage.

    To further test the conclusions of this study, it would be meaningful to further study whether the effect of the root morphology and anatomy on Cd translocation is identical in other rice cultivars from differentsubspecies (includingand),and field experiments are needed. Moreover, searching for root morphology- and anatomy-determining genes and their related underlying mechanisms could contribute to the screening of low-Cd-accumulating cultivars.

    METHODS

    Experiment 1. Cd accumulation in 22 rice cultivars

    Twenty-two rice cultivars with different Cd accumulation levels in their grains were chosen according to our previous study (Chi et al, 2018), and their information is summarized in Table S4. The seeds were surface-sterilized with 30% H2O2solution for 15 min and washed with deionized water, and then germinated in sterilized petri dishes containing moistened filter paper in a controlled chamber (28 oC and 70% relative humidity) (Wu et al, 2011). When radicles appeared, the seeds were transferred to moist acid-washed quartz sand, after which they were allowed to grow unabated for 2 weeks (Armstrong and Armstrong, 2005).

    Uniform rice seedlings were transplanted into plastic vessels. To simulate paddy soil conditions, the rice seedlings were incubated with deoxygenated 25%-strength Hoagland’s nutrient solution comprising 0.1% agar (Hoagland and Arnon, 1938; Kotula et al, 2009). Half of rice seedlings were incubated with 0.1 mg/L CdCl2(sample for Cd accumulation, translocation and Cd tolerance index determination), and half were incubated without Cd (control, sample for Cd tolerance index determination) after a 7-day pre-culture period. The nutrient solutions were adjusted to pH 5.5 and renewed every 4 d during the growth period. All vessels were arranged randomly in a controlled greenhouse with natural light supplemented by sodium light, a day/night temperature of 28 oC/22 oC, a day/night photoperiod of 14 h/10 h and a relative humidity of 70%. Four replicates were prepared for each treatment. After 21 d, the plants were carefully washed with deionized water and separated into shoots and roots.

    Rice growing parameters and Cd tolerance index

    The longest root length, plant height, and shoot and root fresh weights of the rice plants were determined. The tolerance index was used to measure the Cd tolerance of different rice cultivars (Wilkins, 1987) and was calculated according to the following equation: Cd tolerance index (%) = The longest root length (Cd treatment) / The longest root length (control) × 100%.

    Cd accumulation and translocation

    Rice shoot and root samples were oven-dried at 60 oC and then milled into powder for Cd analyses. The powder of the rice sample was microwave-digested in 5 mL concentrated HNO3(16 mol/L), and the digests were filtered and diluted with 25 mL deionized water. The total concentrations of Cd in the digests of the rice samples were analyzed by an atomic absorption spectroscopy (AAS) (Hitachi, Japan).The Cd translocation rate (shoot/root) was used to measure the Cd translocation abilities of different rice cultivars, which were determined according to the following equation: Cd translocation rate (shoot/root) = (Cd concentration in the shoots / Cd concentration in the roots) × 100%.

    Experiment 2. Root properties of two selected cultivars

    On the basis of the results of Experiment 1, two rice cultivars (ZXN and JYT36) with obvious differences in their Cd- translocation ability were selected forfurther study. Cultivar ZXN had high Cd accumulation in the aboveground parts, a high Cd translocation rate (shoot/root) and low Cd accumulation in the roots, while cultivar JYT36 had a low Cd translocation rate (shoot/root) and Cd accumulation in the aboveground parts and high Cd accumulation in the roots. The seedling preparation was similar to Experiment 1. The seedlings were divided into four parts in hydroponics for the following tests.

    1) Uniform rice seedlings of the two selected cultivars were incubated in deoxygenated 1/4-strength Hoagland’s nutrient solution comprising 0.1% agar (Hoagland and Arnon, 1938; Kotula et al, 2009). Every 4 d, the nutrient solution was renewed. After 4 weeks, uniform rice seedlings were rinsed with deionized water and then used to determine the root uptake kinetics.

    2) Uniform rice seedlings were incubated in deoxygenated 1/4-strength Hoagland’s nutrient solution (Hoagland and Arnon, 1938). Cadmium (CdCl2) was applied to the nutrient solution at 0 (control), 0.5 and 2.5 mg/L. The nutrient solution was renewed every 4 d. After 28 d, the rice roots were washed with deionized water and harvested for root morphology determination.

    3) To analyze theroot anatomy, uniform seedlings of the two cultivars were incubated with deoxygenated 1/4-strength Hoagland’s nutrient solution (Hoagland and Arnon, 1938) comprising 0 (control) and 2.5 mg/L Cd for 4 weeks, and then the roots were washed with deionized water and harvested.

    4) To determine the Cd accumulation in rice tissues and Cd subcellular distribution in the roots, uniform seedlings of the two cultivars were incubated with deoxygenated 1/4-strength Hoagland’s nutrient solution (Hoagland and Arnon, 1938) comprising 0.5 and 2.5 mg/L Cd for 4 weeks. The samples were divided into shoots and roots and washed with deionized water.

    Concentration-dependent and time-dependent uptake kinetics

    The Cd uptake kinetics in the roots was assessed according to the modified method described by Uraguchi et al (2009). The roots were excised and incubated with test solution that contained Cd. All the test solution contained 5.0 mmol/L 2-(-morpholino)-ethanesulphonic acid (MES) and 0.5 mmol/L Ca(NO3)2, with the pH adjusted to 5.6 using KOH. The concentration-dependent uptake kinetics experiment assessed low-affinity uptake systems (0, 89, 178, 445 and 890 nmol/L Cd) and high-affinity uptake systems (0, 132, 660, 2 640 and 6 600 nmol/L Cd), in which the treatment time was 30 min. In the time-dependent uptake kinetics experiment, the Cd concentration in the test solution was 180 nmol/L, and the treatment times were 5, 10, 30, 60, 120 and 180 min. The test solution was renewed every 30 min. After incubation, the rice roots were rinsed for 15 min with ice-cold phosphate solution that consisted of 1 mmol/L K2HPO4, 5 mmol/L MES and 0.5 mmol/L Ca(NO3)2to remove absorbed Cd from the root-free space. Finally, the roots were washed with deionized water and oven-dried at 60 oC, after which the Cd concentrations in the roots were analyzed by AAS. Four rice seedlings composed one replicate, and three replicates were prepared for each treatment.

    Root morphology

    Uniform rice seedlings from the control, 0.5 and 2.5 mg/L Cd treatments were selected. Tomeasure the root morphology, the fresh roots were washed, scanned and analyzed by a WinRHIZO root scanner (Regent, STD4800, Canada) (Redjala et al, 2011). The number of root tips per cm2of surface area and the average diameter were determined.Eight replicates were prepared for each treatment.

    Root anatomy (apoplastic barriers)

    Healthy and uniform adventitious roots (with similar length of approximately 10 cm) of the two cultivars from the control and 2.5 mg/L Cd treatments were selected. To analyze the development of apoplastic barriers (Casparian bands and suberin lamellae), the roots were embedded in tissue-freezing medium (Sakura Finetek, USA) and frozen. Afterwards, cross-sections of each root were taken by a freezing microtome (Thermo Microm HM560, Germany) at the following distances from the root tip: 1, 5, 10, 20, 30, 40, 50 and 60 mm. The root sections were attached to glass slides treated with polylysine. To detect the development of Casparian bands, sections were stained for 1 h with 0.1% berberine hemisulphate and then for 30 min with 0.5% aniline blue (Lux et al, 2005; Kotula et al, 2009). For suberin lamellae, sections were stained with 0.1% Sudan red 7B for 5 h (Lux et al, 2005). After being stained, the sections were viewed and documented with a fluorescence microscope (Zeiss Imager, Z1, Germany) and a digital camera (Nikon, D1, Japan). Five replicates were prepared for each treatment.

    Cd accumulation in rice plant tissues and Cd subcellular distribution in rice roots

    Healthy and uniform rice seedlings from the 0.5 and 2.5 mg/L Cd treatments were selected. The Cd concentrations in the shoot and root tissues were determined by AAS. The Cd concentrations in the apoplastic fluid, symplast and cell wall were determined by the method described by Ye et al (2012). Fresh rice roots were washed with deionized water and then soaked in ice-cold 5 mmol/L Na2-EDTA solution for 10 min to remove Cd adsorbed onto root surfaces. After being washed with deionized water again, the roots were cut transversely into 1 cm segments and gently rocked for 1 h in 25 mL deionized water at room temperature. The total Cd accumulation in the filtrate was the Cd in the apoplastic fluid. After collecting the apoplastic fluids, the sample was milled to powder in liquid nitrogen and then homogenized with 10 mL ice-cold extraction buffer [50 mmol/L HEPES (C8H18N2O4S), 1.0 mmol/L DTT (C4H10O2S2), 500 mmol/L sucrose and 5.0 mmol/L ascorbic acid, and adjusted to pH 7.5 with NaOH]. The homogenate was centrifuged at 4 000 ×at 4 oC for 15 min. After centrifugation, the supernatant was designated as the symplast fraction, and the pellet was designated as the cell wall fraction. The cell wall fractions were then dried at 70 oC and digested by concentrated HNO3. The Cd concentrations in the apoplastic fluid, symplast (intracellular Cd) and cell wall (bound Cd) were analyzed by AAS.

    Quality control and statistical analyses

    Blanks and plant standard material (GBW-07603, China Standard Materials Research Center, Beijing, China) were used for quality control. Recoveries from the reference materials ranged from 84.1% to 92.3% for Cd analysis. Origin 8.0 and Excel 2007 softwares were used to create the artwork. The data were analyzed using the SPSS 19.0 statistical package, and the data are presented as the Mean ± SE. The treatment means were compared via the Duncan multiple comparison test.

    ACKNOWLEDGEMENTS

    This study was supported by the National Key Research and Development Program of China (Grant No. 2018YFD0800700), the National Natural Science Foundation of China (Grant No. 31670409), the General Research Fund Proposal of Hong Kong, China (Grant No. RG21/2020-2021R), and the Faculty of Liberal Arts and Social Sciences of the Education University of Hong Kong, China (Grant No. 04548 (IRS-10)).

    SUPPLEMENTAL DATA

    The following materials are available in the online version of this article at http://www.sciencedirect.com/journal/rice-science; http://www.ricescience.org.

    Fig. S1. Cd tolerance index of 22 rice cultivars grown in solution with treatment of 0.1 mg/L Cd for 3 weeks.

    Fig. S2. Correlation between Cd concentration in shoots and roots of 22 rice cultivars with treatment of 0.1 mg/L Cd for 3 weeks.

    Fig. S3. Cd concentration in roots and shoots of two rice cultivars with 0.5 and 2.5 mg/L Cd treatments for 4 weeks.

    Table S1. Growing parameters of 22 rice cultivars grown in solution with treatments of 0 (control) and 0.1 mg/L Cd for 3 weeks.

    Table S2. Effects of Cd stress on growth of two rice cultivars with treatments of 0.5 and 2.5 mg/L Cd for 4 weeks.

    Table S3. Kinetic parameters for Cd influx into rice roots of cultivars ZXN and JYT36.

    Table S4. Rice cultivars used.

    Armstrong J, Armstrong W. 2005. Rice: Sulfide-induced barriers to root radial oxygen loss, Fe2+and water uptake, and lateral root emergence., 96(4): 625?638.

    Boominathan R, Doran P M. 2003. Cadmium tolerance and antioxidative defenses in hairy roots of the cadmium hyperaccumulator,., 83(2): 158?167.

    Chi Y, Li F, Tam N F Y, Liu C, Ouyang Y, Qi X, Li W C, Ye Z H. 2018. Variations in grain cadmium and arsenic concentrations and screening for stable low-accumulating rice cultivars from multi-environment trials., 643(1): 1314?1324.

    Chiao W T, Syu C H, Chen B C, Juang K W. 2019. Cadmium in rice grains from a field trial in relation to model parameters of Cd-toxicity and -absorption in rice seedlings., 169: 837?847.

    Chiao W T, Chen B C, Syu C H, Juang K W. 2020. Aspects of cultivar variation in physiological traits related to Cd distribution in rice plants with a short-term stress., 61: 27.

    Grant C A, Clarke J M, Duguid S, Chaney R L. 2008. Selection and breeding of plant cultivars to minimize cadmium accumulation., 390: 301?310.

    Hoagland D R, Arnon D I. 1938. The water culture method for growing plants without soil., 347: 1?39.

    Huang G, Ding C, Guo F, Li X G, Zhou Z G, Zhang T L, Wang X X. 2017. The role of node restriction on cadmium accumulation in the brown rice of 12 Chinese rice (L.) cultivars., 65(47): 10157?10164.

    Huang L, Li W C, Tam N F, Ye Z H. 2019. Effects of root morphology and anatomy on cadmium uptake and translocation in rice (L.)., 75: 296?306.

    Kotula L, Ranathunge K, Schreiber L, Steudle E. 2009. Functional and chemical comparison of apoplastic barriers to radial oxygen loss in roots of rice (L.) grown in aerated or deoxygenated solution., 60(7): 2155?2167.

    Kreszies T, Schreiber L, Ranathunge K. 2018. Suberized transport barriers in, barley and rice roots: From the model plant to crop species., 227: 75?83.

    Liu J G, Liang J S, Li K Q, Zhang Z J, Yu B Y, Lu X L, Yang J C, Zhu Q S. 2003. Correlations between cadmium and mineral nutrients in absorption and accumulation in various genotypes of rice under cadmium stress., 52(9): 1467?1473.

    Liu J G, Qian M, Cai G L, Yang J C, Zhu Q S. 2007. Uptake and translocation of Cd in different rice cultivars and the relation with Cd accumulation in rice grain., 143(1/2): 443?447.

    Loix C, Huybrechts M, Vangronsveld J, Gielen M, Keunen E, Cuypers A. 2017. Reciprocal interactions between cadmium- induced cell wall responses and oxidative stress in plants., 8: 1867.

    Lux A, Sottniková A, Opatrná J, Greger M. 2004. Differences in structure of adventitious roots inclones with contrasting characteristics of cadmium accumulation and sensitivity.,120(4): 537?545.

    Lux A, Morita S, Abe J, Ito K. 2005. An improved method for clearing and staining free-hand sections and whole-mount samples., 96(6): 989–996.

    Lux A, Martinka M, Vaculik M, White P J. 2011. Root responses to cadmium in the rhizosphere: A review., 62(1): 21?37.

    Ma F, Peterson C A. 2003. Current insights into the development, structure, and chemistry of the endodermis and exodermis of roots., 81: 405?421.

    Maksimovi? I, Kastori R, Krsti? L, Lukovi? J. 2007. Steady presence of cadmium and nickel affects root anatomy, accumulation and distribution of essential ions in maize seedlings., 51(3): 589–592.

    Man Y, Zhao Y Y, Ye R, Lin J X, Jing Y P. 2018.cytological and chemical analysis of Casparian strips using stimulated Raman scattering microscopy., 220: 136?144.

    Moore C A, Bowen H C, Scrase-Field S, Knight M R, White P J. 2002. The deposition of suberin lamellae determines the magnitude of cytosolic Ca2+elevations in root endodermal cells subjected to cooling.,30(4): 457–466.

    Nordberg G, Jin T Y, Bernard A, Fierens S, Buchet J P, Ye T T, Kong Q H, Wang H F. 2002. Low bone density and renal dysfunction following environmental cadmium exposure in China., 31(6): 478?481.

    Parrotta L, Guerriero G, Sergeant K, Cai G, Hausman J F. 2015. Target or barrier? The cell wall of early- and later-diverging plants vs cadmium toxicity: Differences in the response mechanisms., 6: 133.

    Qi X L, Tam N F, Li W C, Ye Z H. 2020. The role of root apoplastic barriers in cadmium translocation and accumulation in cultivars of rice (L.) with different Cd- accumulating characteristics., 264: 114736.

    Redjala T, Zelko I, Sterckeman T, Legué V, Lux A. 2011. Relationship between root structure and root cadmium uptake in maize., 71(2): 241?248.

    Rodda M S, Li G, Reid R J. 2011. The timing of grain Cd accumulation in rice plants: The relative importance of remobilisation within the plant and root Cd uptake post- flowering., 347: 105–114.

    Rout G R, Das P. 2002. Rapid hydroponic screening for molybdenum tolerance in rice through morphological and biochemical analysis., 48: 505?512.

    Schreiber L, Hartmann K, Skrabs M, Zeier J. 1999. Apoplastic barriers in roots: Chemical composition of endodermal and hypodermal cell walls., 50: 1267–1280.

    Shi Y J, Xu Y F, Ni Z Y, Wang J W, Li D, Zhang M K. 2019. Difference of Cd accumulation in main crops in Hangzhou and its influencing factors., 60(7): 1230?1233. (in Chinese with English abstract)

    Tao Q, Jupa R, Luo, J P, Lux A, Kovac J, Wen Y, Zhou Y M, Jan J, Liang Y C, Li T Q. 2017. The apoplasmic pathway via the root apex and lateral roots contributes to Cd hyperaccumulation in the hyperaccumulator., 68(3): 739?751.

    Uraguchi S, Mori S, Kuramata M, Kawasaki A, Arao T, Ishikawa S. 2009. Root-to-shoot Cd translocation via the xylem is the major process determining shoot and grain cadmium accumulation in rice., 60(9): 2677?2688.

    Uraguchi S, Fujiwara T. 2012. Cadmium transport and tolerance in rice: Perspectives for reducing grain cadmium accumulation., 5(1): 5.

    Uraguchi S, Fujiwara T. 2013. Rice breaks ground for cadmium- free cereals., 16(3): 328–334.

    Wang F J, Zhang Y T, Guo Q X, Tan H F, Han J H, Lin H R, Wei H W, Xu G W, Zhu C. 2018. Effects of exogenous 5-aminolevulinic acid and 24-epibrassinolide on Cd accumulation in rice from Cd-contaminated soil., 25(6): 320?329.

    White P J. 2001. The pathways of calcium movement to the xylem., 52: 891–899.

    Wilkins D A. 1987. The measurement of tolerance to edaphic factors by means of root growth., 80: 623–633.

    Williams P N, Lei M, Sun G, Huang Q, Lu Y, Deacon C, Meharg A A, Zhu Y G. 2009. Occurrence and partitioning of cadmium, arsenic and lead in mine impacted paddy rice: Hunan, China.,43(3): 637?642.

    Wu C, Ye Z H, Shu W S, Zhu Y G, Wong, M H. 2011. Arsenic accumulation and speciation in rice are affected by root aeration and variation of genotypes.,62(8): 2889–2898.

    Yamaguchi N, Mori S, Baba K, Kaburagi-Yada S, Arao T, Kitajima N, Hokura A, Terada Y. 2011. Cadmium distribution in the root tissues of solanaceous plants with contrasting root-to-shoot Cd translocation efficiencies., 71(2): 198?206.

    Ye J, Yan C L, Liu J C, Lu H L, Liu T, Song Z F. 2012. Effects of silicon on the distribution of cadmium compartmentation in root tips of(S., L.) Yong., 162: 369–373.

    Zhuang P, Lu H, Li Z, Zou B, McBride M B. 2014. Multiple exposure and effects assessment of heavy metals in the population near mining area in South China., 9(4): e94484.

    Ye Zhihong (lssyzhh@mail.sysu.edu.cn); Li Wai Chin (waichin@eduhk.hk)

    14 November2020;

    1 March2021

    Copyright ? 2021, China National Rice Research Institute. Hosting by Elsevier B V

    This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/)

    Peer review under responsibility of China National Rice Research Institute

    http://dx.doi.org/10.1016/j.rsci.2021.03.003

    (Managing Editor: Wu Yawen)

    久久这里只有精品中国| 国产片特级美女逼逼视频| 一本久久精品| 成人性生交大片免费视频hd| 国产乱来视频区| 99热这里只有是精品在线观看| 欧美日韩精品成人综合77777| 婷婷色麻豆天堂久久 | 国产伦一二天堂av在线观看| 三级经典国产精品| 成年女人看的毛片在线观看| 黄片无遮挡物在线观看| 美女国产视频在线观看| 国产国拍精品亚洲av在线观看| 七月丁香在线播放| 噜噜噜噜噜久久久久久91| 美女xxoo啪啪120秒动态图| 国产免费视频播放在线视频 | 日韩欧美精品v在线| 少妇人妻一区二区三区视频| 亚洲av男天堂| 久久精品影院6| 最近视频中文字幕2019在线8| 99九九线精品视频在线观看视频| 一个人免费在线观看电影| 国产免费视频播放在线视频 | 最近最新中文字幕免费大全7| 亚洲精品成人久久久久久| 一级黄色大片毛片| 亚洲精品日韩在线中文字幕| 色吧在线观看| 久久精品综合一区二区三区| 一本久久精品| 18禁动态无遮挡网站| 国产又黄又爽又无遮挡在线| 国产精品99久久久久久久久| 亚洲国产精品sss在线观看| 午夜a级毛片| 国产成人精品婷婷| 欧美zozozo另类| videossex国产| a级毛片免费高清观看在线播放| 九九热线精品视视频播放| 美女内射精品一级片tv| 干丝袜人妻中文字幕| 人妻系列 视频| 精品一区二区三区视频在线| 内地一区二区视频在线| 国产精品不卡视频一区二区| 身体一侧抽搐| 伊人久久精品亚洲午夜| 国产又黄又爽又无遮挡在线| 久热久热在线精品观看| 亚洲五月天丁香| 有码 亚洲区| 国产精品一区二区三区四区久久| 国产乱人视频| 国产免费又黄又爽又色| 三级毛片av免费| 亚洲va在线va天堂va国产| 熟女人妻精品中文字幕| 亚洲av电影不卡..在线观看| 男人狂女人下面高潮的视频| 成人综合一区亚洲| 国产亚洲精品av在线| 亚洲成人av在线免费| 午夜a级毛片| 嫩草影院入口| 午夜精品一区二区三区免费看| 波野结衣二区三区在线| 99久久精品热视频| 99久久精品国产国产毛片| 亚洲天堂国产精品一区在线| ponron亚洲| 99在线人妻在线中文字幕| 久久久久网色| 高清视频免费观看一区二区 | 99久久精品热视频| 亚洲最大成人手机在线| 亚洲成av人片在线播放无| 国产极品天堂在线| 99九九线精品视频在线观看视频| 如何舔出高潮| 美女脱内裤让男人舔精品视频| av免费观看日本| 99久久无色码亚洲精品果冻| 乱码一卡2卡4卡精品| 欧美最新免费一区二区三区| 国产成人免费观看mmmm| 亚洲欧美中文字幕日韩二区| 亚洲,欧美,日韩| 国产真实伦视频高清在线观看| 久久久久久久午夜电影| 国产精品伦人一区二区| 国产精品1区2区在线观看.| 久久婷婷人人爽人人干人人爱| 99国产精品一区二区蜜桃av| 国产在视频线在精品| 三级经典国产精品| 五月玫瑰六月丁香| 三级国产精品片| 日韩国内少妇激情av| 久久精品久久久久久噜噜老黄 | 亚洲电影在线观看av| 99久久中文字幕三级久久日本| 六月丁香七月| 亚洲av中文字字幕乱码综合| 国产真实伦视频高清在线观看| 在线观看美女被高潮喷水网站| 一级毛片我不卡| 久久99热6这里只有精品| 高清在线视频一区二区三区 | 免费播放大片免费观看视频在线观看 | 毛片女人毛片| 在线播放无遮挡| 97人妻精品一区二区三区麻豆| 久久综合国产亚洲精品| 尤物成人国产欧美一区二区三区| 亚洲电影在线观看av| 九色成人免费人妻av| 亚洲高清免费不卡视频| 99热这里只有是精品在线观看| 午夜免费男女啪啪视频观看| 精品久久久久久久久亚洲| 男女视频在线观看网站免费| 久久久久久久亚洲中文字幕| 日本五十路高清| 午夜亚洲福利在线播放| 免费黄网站久久成人精品| 精品国产一区二区三区久久久樱花 | 国产成人a∨麻豆精品| 精品人妻一区二区三区麻豆| 日韩av不卡免费在线播放| av在线天堂中文字幕| 99在线视频只有这里精品首页| 国产色婷婷99| 少妇人妻一区二区三区视频| 国产高清有码在线观看视频| 一级毛片aaaaaa免费看小| 欧美精品一区二区大全| 一二三四中文在线观看免费高清| 中文字幕免费在线视频6| 亚洲成人av在线免费| 亚洲av成人av| 啦啦啦啦在线视频资源| 亚洲第一区二区三区不卡| 亚洲欧洲日产国产| 晚上一个人看的免费电影| 波野结衣二区三区在线| 国产国拍精品亚洲av在线观看| 国产成人aa在线观看| 久久亚洲国产成人精品v| 日本色播在线视频| 禁无遮挡网站| 国产伦理片在线播放av一区| 色噜噜av男人的天堂激情| 亚洲高清免费不卡视频| kizo精华| 美女黄网站色视频| 国产精品一二三区在线看| 亚洲欧美日韩东京热| 美女黄网站色视频| 色视频www国产| 看十八女毛片水多多多| 国产成人精品婷婷| 99热这里只有精品一区| 22中文网久久字幕| 午夜亚洲福利在线播放| 免费人成在线观看视频色| 日韩欧美精品v在线| 国产精品久久久久久av不卡| av专区在线播放| 亚洲自拍偷在线| 两个人视频免费观看高清| 国产一区亚洲一区在线观看| 一本一本综合久久| 麻豆成人av视频| 男人舔奶头视频| 国产成人精品婷婷| 亚洲aⅴ乱码一区二区在线播放| 日本wwww免费看| 我的女老师完整版在线观看| 深爱激情五月婷婷| 毛片女人毛片| 色尼玛亚洲综合影院| 中文资源天堂在线| 亚洲中文字幕日韩| 26uuu在线亚洲综合色| 最近视频中文字幕2019在线8| 国产在视频线精品| 国产中年淑女户外野战色| 国产综合懂色| 亚洲无线观看免费| 边亲边吃奶的免费视频| 日本wwww免费看| 免费大片18禁| 18禁动态无遮挡网站| 久久久久久久久久久免费av| 久久久精品94久久精品| 久久精品国产亚洲av天美| 成人毛片60女人毛片免费| 久久综合国产亚洲精品| 免费黄网站久久成人精品| 成人毛片60女人毛片免费| 最近中文字幕高清免费大全6| 亚洲欧美精品综合久久99| 国产精品久久久久久久电影| 免费观看性生交大片5| av在线老鸭窝| 看非洲黑人一级黄片| 99久国产av精品国产电影| 日日摸夜夜添夜夜添av毛片| 国产一区亚洲一区在线观看| 亚洲不卡免费看| 欧美一区二区精品小视频在线| 18禁在线播放成人免费| 啦啦啦观看免费观看视频高清| 亚洲真实伦在线观看| 天天躁日日操中文字幕| 国产激情偷乱视频一区二区| 亚洲美女视频黄频| a级毛色黄片| 国产熟女欧美一区二区| 日日摸夜夜添夜夜爱| 国产精品野战在线观看| 我的女老师完整版在线观看| 午夜精品国产一区二区电影 | 天堂影院成人在线观看| 国产一区二区在线观看日韩| 欧美xxxx性猛交bbbb| 免费看光身美女| 一边亲一边摸免费视频| 久久精品国产亚洲av天美| 日韩一本色道免费dvd| 免费搜索国产男女视频| 精品久久久久久久人妻蜜臀av| 成人毛片a级毛片在线播放| 免费观看性生交大片5| 久久精品熟女亚洲av麻豆精品 | 97人妻精品一区二区三区麻豆| 男插女下体视频免费在线播放| 欧美高清成人免费视频www| 精品一区二区免费观看| 国产精品伦人一区二区| 国产av在哪里看| 美女cb高潮喷水在线观看| 亚洲成av人片在线播放无| 国产成人91sexporn| 国产精华一区二区三区| 久久久久久久久久久免费av| 青青草视频在线视频观看| 精品99又大又爽又粗少妇毛片| 日本免费在线观看一区| 亚洲av熟女| 99热精品在线国产| 国产不卡一卡二| 国产麻豆成人av免费视频| 亚洲成色77777| 中国国产av一级| 中文在线观看免费www的网站| 精品一区二区三区人妻视频| 一级毛片我不卡| 国产成人freesex在线| 国产国拍精品亚洲av在线观看| 亚洲欧美精品综合久久99| 午夜福利高清视频| 免费观看的影片在线观看| 精品酒店卫生间| 欧美性猛交黑人性爽| av黄色大香蕉| 久久久久精品久久久久真实原创| 最近的中文字幕免费完整| 欧美日韩综合久久久久久| 一级二级三级毛片免费看| 国产探花在线观看一区二区| 亚洲18禁久久av| 亚洲人成网站在线播| 免费看a级黄色片| 99久国产av精品国产电影| 亚洲色图av天堂| 免费大片18禁| 99热精品在线国产| 亚洲av福利一区| 18禁动态无遮挡网站| 汤姆久久久久久久影院中文字幕 | 日韩亚洲欧美综合| 插逼视频在线观看| 亚洲精品影视一区二区三区av| 成人综合一区亚洲| 精品午夜福利在线看| 精品久久久久久成人av| 精品久久久久久久久亚洲| 99热6这里只有精品| 亚洲第一区二区三区不卡| 天天躁日日操中文字幕| 伊人久久精品亚洲午夜| 观看美女的网站| 国产精品野战在线观看| 国产黄a三级三级三级人| 亚洲精品一区蜜桃| 精品国产三级普通话版| 老司机福利观看| 2022亚洲国产成人精品| 秋霞在线观看毛片| 久久久午夜欧美精品| 男人和女人高潮做爰伦理| 欧美最新免费一区二区三区| 18禁在线无遮挡免费观看视频| 亚洲欧美成人精品一区二区| 久久精品综合一区二区三区| 99久久精品一区二区三区| 亚洲一级一片aⅴ在线观看| 一卡2卡三卡四卡精品乱码亚洲| 午夜福利高清视频| 2021少妇久久久久久久久久久| 欧美激情久久久久久爽电影| 免费大片18禁| 熟妇人妻久久中文字幕3abv| 美女xxoo啪啪120秒动态图| 亚洲av中文字字幕乱码综合| 久久久精品94久久精品| 少妇的逼水好多| 亚洲国产欧美在线一区| 黄色欧美视频在线观看| 国产一区亚洲一区在线观看| 久久久精品大字幕| 国产欧美另类精品又又久久亚洲欧美| 又爽又黄a免费视频| 午夜a级毛片| 嘟嘟电影网在线观看| 青春草亚洲视频在线观看| 免费人成在线观看视频色| 亚洲av免费在线观看| 别揉我奶头 嗯啊视频| 国产精品无大码| 久久精品夜色国产| 男女啪啪激烈高潮av片| 非洲黑人性xxxx精品又粗又长| 大话2 男鬼变身卡| 亚洲av免费高清在线观看| 大香蕉久久网| АⅤ资源中文在线天堂| 99久国产av精品| 国产一级毛片在线| 国产白丝娇喘喷水9色精品| 国产精品女同一区二区软件| 观看免费一级毛片| 中文欧美无线码| 久久国内精品自在自线图片| 不卡视频在线观看欧美| 99久久精品热视频| 国产人妻一区二区三区在| 欧美日韩国产亚洲二区| av在线观看视频网站免费| 99国产精品一区二区蜜桃av| 中文字幕免费在线视频6| 人妻夜夜爽99麻豆av| 亚洲精品国产成人久久av| 99热这里只有精品一区| 中文亚洲av片在线观看爽| 国产黄a三级三级三级人| 18禁动态无遮挡网站| 少妇高潮的动态图| 国产黄a三级三级三级人| 99热6这里只有精品| 国产精品国产高清国产av| 美女黄网站色视频| 婷婷色av中文字幕| 两个人的视频大全免费| 亚洲av熟女| 欧美人与善性xxx| 我要搜黄色片| 精品酒店卫生间| 亚洲国产精品成人综合色| 熟妇人妻久久中文字幕3abv| 国产成人91sexporn| 中文字幕精品亚洲无线码一区| 天堂av国产一区二区熟女人妻| 美女脱内裤让男人舔精品视频| 国产男人的电影天堂91| 亚洲国产色片| 日韩国内少妇激情av| 丰满人妻一区二区三区视频av| 日本一二三区视频观看| 亚洲国产日韩欧美精品在线观看| 亚洲成人中文字幕在线播放| 国内精品宾馆在线| 尾随美女入室| 哪个播放器可以免费观看大片| 99久久无色码亚洲精品果冻| 丝袜喷水一区| 欧美又色又爽又黄视频| 欧美zozozo另类| 成人美女网站在线观看视频| 国产三级中文精品| av在线播放精品| 精品久久久久久成人av| 汤姆久久久久久久影院中文字幕 | 久久欧美精品欧美久久欧美| 91久久精品国产一区二区成人| 亚洲丝袜综合中文字幕| 中文字幕熟女人妻在线| 特级一级黄色大片| 天天躁日日操中文字幕| 日本-黄色视频高清免费观看| 18禁裸乳无遮挡免费网站照片| 黄色配什么色好看| 18禁在线无遮挡免费观看视频| 中文字幕av在线有码专区| 中文精品一卡2卡3卡4更新| 久久人妻av系列| 亚洲一级一片aⅴ在线观看| 欧美一级a爱片免费观看看| 亚洲内射少妇av| 国产成人午夜福利电影在线观看| 国产视频首页在线观看| 伊人久久精品亚洲午夜| 午夜福利在线观看吧| 欧美区成人在线视频| 日韩高清综合在线| 亚洲欧美精品自产自拍| 乱系列少妇在线播放| 国产精品综合久久久久久久免费| 狂野欧美白嫩少妇大欣赏| 欧美日本亚洲视频在线播放| 男人狂女人下面高潮的视频| www.色视频.com| 国产综合懂色| 国国产精品蜜臀av免费| 国产探花极品一区二区| 毛片一级片免费看久久久久| 国产免费福利视频在线观看| 久久精品国产亚洲网站| 少妇丰满av| 中文字幕人妻熟人妻熟丝袜美| 99久久中文字幕三级久久日本| 国产又黄又爽又无遮挡在线| 亚洲国产欧美人成| 两性午夜刺激爽爽歪歪视频在线观看| 一二三四中文在线观看免费高清| 国产毛片a区久久久久| 天天躁日日操中文字幕| 三级国产精品欧美在线观看| 青春草国产在线视频| 美女大奶头视频| 欧美另类亚洲清纯唯美| 免费av毛片视频| 久久人妻av系列| 国产男人的电影天堂91| 尾随美女入室| 亚洲婷婷狠狠爱综合网| 寂寞人妻少妇视频99o| 乱系列少妇在线播放| 亚洲欧美精品专区久久| 国产精品久久电影中文字幕| 亚洲av免费在线观看| 午夜视频国产福利| av在线播放精品| 人体艺术视频欧美日本| 欧美xxxx性猛交bbbb| 美女大奶头视频| 亚洲国产精品国产精品| 国产成人福利小说| 国产成人一区二区在线| 69人妻影院| 三级男女做爰猛烈吃奶摸视频| 春色校园在线视频观看| 日韩av不卡免费在线播放| 嘟嘟电影网在线观看| 美女国产视频在线观看| 波多野结衣巨乳人妻| 一级毛片久久久久久久久女| 亚洲成人av在线免费| 简卡轻食公司| 精品人妻视频免费看| 国产久久久一区二区三区| 日韩欧美三级三区| 少妇的逼水好多| 亚洲av熟女| 精品熟女少妇av免费看| 午夜激情福利司机影院| 亚洲欧美成人综合另类久久久 | 国产亚洲午夜精品一区二区久久 | 国产成人a区在线观看| 国产视频首页在线观看| 三级经典国产精品| 人妻少妇偷人精品九色| 精品人妻视频免费看| 级片在线观看| 国产亚洲午夜精品一区二区久久 | 免费人成在线观看视频色| 一级毛片久久久久久久久女| 国产av码专区亚洲av| 国产人妻一区二区三区在| 成人三级黄色视频| 亚洲天堂国产精品一区在线| 一级毛片电影观看 | 免费黄色在线免费观看| 亚洲成人中文字幕在线播放| 国产成人精品一,二区| 国产视频首页在线观看| 波野结衣二区三区在线| 最近2019中文字幕mv第一页| 国产精品伦人一区二区| 国产成人免费观看mmmm| 91精品一卡2卡3卡4卡| 亚洲aⅴ乱码一区二区在线播放| 国产老妇女一区| 乱系列少妇在线播放| 3wmmmm亚洲av在线观看| 青春草视频在线免费观看| 视频中文字幕在线观看| 国产精品1区2区在线观看.| 亚洲国产色片| 少妇被粗大猛烈的视频| 久久精品熟女亚洲av麻豆精品 | 一区二区三区免费毛片| 欧美一区二区精品小视频在线| 桃色一区二区三区在线观看| 久久99热这里只有精品18| 一级毛片aaaaaa免费看小| 国产黄片视频在线免费观看| 亚洲av日韩在线播放| 男人狂女人下面高潮的视频| av又黄又爽大尺度在线免费看 | 国产成人精品婷婷| 免费看光身美女| 久久久色成人| av国产免费在线观看| av线在线观看网站| 国产视频首页在线观看| 精品不卡国产一区二区三区| 51国产日韩欧美| 在线观看一区二区三区| 天堂av国产一区二区熟女人妻| 69人妻影院| 我的老师免费观看完整版| 极品教师在线视频| 精品久久久久久久久av| 三级经典国产精品| 国产中年淑女户外野战色| www.色视频.com| 日韩在线高清观看一区二区三区| 男女视频在线观看网站免费| 日韩精品青青久久久久久| 国产91av在线免费观看| 床上黄色一级片| 久久久久久久久久久免费av| 午夜激情欧美在线| 我的女老师完整版在线观看| 国产精品99久久久久久久久| 1024手机看黄色片| 亚洲成人中文字幕在线播放| 国产精品电影一区二区三区| 国产精品久久久久久av不卡| 亚洲精品日韩在线中文字幕| 国产大屁股一区二区在线视频| 狂野欧美激情性xxxx在线观看| 伦理电影大哥的女人| 51国产日韩欧美| 亚洲国产精品专区欧美| 日韩在线高清观看一区二区三区| 18禁在线无遮挡免费观看视频| 久久久久久九九精品二区国产| 女人被狂操c到高潮| 精品午夜福利在线看| 国内精品一区二区在线观看| 水蜜桃什么品种好| 亚洲美女视频黄频| 久久亚洲国产成人精品v| 免费观看的影片在线观看| 久久国产乱子免费精品| 久久精品国产鲁丝片午夜精品| 亚洲av男天堂| 国产在线男女| 18禁裸乳无遮挡免费网站照片| 午夜福利高清视频| 麻豆av噜噜一区二区三区| 午夜a级毛片| 可以在线观看毛片的网站| 91久久精品国产一区二区成人| 中文天堂在线官网| 在线播放国产精品三级| 青春草亚洲视频在线观看| 永久网站在线| 精品久久久久久成人av| 淫秽高清视频在线观看| 99视频精品全部免费 在线| 桃色一区二区三区在线观看| 亚洲av成人av| .国产精品久久| 亚洲一区高清亚洲精品| 国产男人的电影天堂91| 亚洲成色77777| 欧美丝袜亚洲另类| 亚洲国产欧洲综合997久久,| 久久久久久久久久久免费av| 久久99热6这里只有精品| 国产亚洲91精品色在线| 人人妻人人澡人人爽人人夜夜 | 成人亚洲精品av一区二区| 精品久久久久久久久av| 欧美日韩综合久久久久久| 免费看日本二区| 久久久精品94久久精品| 久久精品91蜜桃| 99热这里只有精品一区| 日韩在线高清观看一区二区三区| 视频中文字幕在线观看| 九九在线视频观看精品| 草草在线视频免费看| 婷婷色av中文字幕| 色噜噜av男人的天堂激情| 亚洲在线观看片| 国产视频首页在线观看|