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The aluminum distribution and translocation in two citrus species differing in aluminum tolerance



Many citrus orchards of south China suffer from soil acidification, which induces aluminum (Al) toxicity. The Al-immobilization in vivo is crucial for Al detoxification. However, the distribution and translocation of excess Al in citrus species are not well understood.


The seedlings of ‘Xuegan’ [Citrus sinensis (L.) Osbeck] and ‘Shatianyou’ [Citrus grandis (L.) Osbeck], that differ in Al tolerance, were hydroponically treated with a nutrient solution (Control) or supplemented by 1.0 mM Al3+ (Al toxicity) for 21 days after three months of pre-culture. The Al distribution at the tissue level of citrus species followed the order: lateral roots > primary roots > leaves > stems. The concentration of Al extracted from the cell wall (CW) of lateral roots was found to be about 8 to 10 times higher than in the lateral roots under Al toxicity, suggesting that the CW was the primary Al-binding site at the subcellular level. Furthermore, the Al distribution in CW components of the lateral roots showed that pectin had the highest affinity for binding Al. The relative expression level of genes directly relevant to Al transport indicated a dominant role of Cs6g03670.1 and Cg1g021320.1 in the Al distribution of two citrus species. Compared to C. grandis, C. sinensis had a significantly higher Al concentration on the CW of lateral roots, whereas remarkably lower Al levels in the leaves and stems. Furthermore, Al translocation revealed by the absorption kinetics of the CW demonstrated that C. sinensis had a higher Al retention and stronger Al affinity on the root CW than C. grandis. According to the FTIR (Fourier transform infrared spectroscopy) analysis, the Al distribution and translocation might be affected by a modification in the structure and components of the citrus lateral root CW.


A higher Al-retention, mainly attributable to pectin of the root CW, and a lower Al translocation efficiency from roots to shoots contributed to a higher Al tolerance of C. sinensis than C. grandis. The aluminum distribution and translocation of two citrus species differing in aluminum tolerance were associated with the transcriptional regulation of genes related to Al transport and the structural modification of root CW.


Acidification of arable soils has increased in China from 1980 to 2000 s [1]. Soil acidification significantly accelerates aluminum (Al) solubilization from minerals when the soil pH is less than 5.0 [2]. The excess Al in the soil disturbs the nutrient and water balance of the rhizosphere, thereby reducing crop yield [3], and represents one of the most limiting factors to crop production in tropical and subtropical regions [4]. For instance, it was reported that rice grain yield decreased by 28–62% [5], and wheat grain yield decreased by 23–100% [6] under Al toxicity.

The citrus orchards in south China frequently suffer from Al toxicity induced by soil acidification [7]. For instance, our investigation of 319 soil samples from citrus orchards in Fujian province of China revealed an average pH of 4.34, over 90% of which had a pH less than 5.0 [8]. Under field conditions, excess Al significantly inhibited the root development of Citrus aurantium L. [9]. Accordingly, the citrus fruit yield also decreased significantly under Al toxicity [10]. In sandy culture, the biomass of citrus seedlings was depressed by Al toxicity, inducing the oxidative stress and the photosynthetic inhibition of citrus seedlings [11]. Likewise, in the hydroponic culture, high Al concentration induces chlorotic and mottled leaves, thick root tips and less fibrous roots of citrus rootstocks [12].

Plant tolerance to excess Al mainly relies on the inhibition of Al uptake and the restriction of Al translocation [13]. Excess Al accumulates primarily in the roots of citrus seedlings [14, 15]. Furthermore, Al partitioning at the cellular level shows that the plant root CW is the primary location for Al-binding for most crops [16]. The CW was constituted mainly by polysaccharides, such as pectin, cellulose and hemicellulose (HC). However, it is still debatable which CW component contributes most to the Al-binding under high Al concentrations. For instance, Yang et al. [17] reported that HC is the main pool for Al accumulation in Arabidopsis. Differentially, Ye et al. [18] proposed that the CW pectin contributed mainly to Al binding in Panax notoginseng, a native plant adapted to acid soil. To our knowledge, the Al distribution pattern and the primary Al repository sites in citrus species are still less clear. Moreover, the potential mechanisms regarding the Al distribution and translocation in citrus species are not fully understood and documented.

Genes associated with Al transport and redistribution have been explored. For instance, the gene encoding Al Sensitive 3 (ALS3) has been identified in Arabidopsis and is responsible for Al transport from roots to shoots [19]. Moreover, the upregulation of Al-specific transporter Nramp (natural resistance-associated macrophage protein) has been proven to enhance rice Al sensitivity [20]. Our transcriptional study on Al-treated citrus roots also indicated the roles of Cs3g18690.1 and Cs6g05460.1 in Al transport and detoxification [21].

We have evaluated the Al tolerance of 12 citrus species and cultivars in 2009 at an AlCl3·6H2O concentration of 0, 0.2, 0.6, 1.0 and 1.6 mM [22]. The results indicated C. sinensis is Al-tolerant and C. grandis is an Al-sensitive species. Further studies were carried out to investigate the different responses of C. sinensis and C. grandis to Al stress at bio-physiological [11, 23], transcriptional [19, 24] and proteomic levels [25, 26]. However, potential Al-tolerant mechanisms in relation to Al distribution and translocation of citrus species are less well understood. In the present study, seedlings of C. sinensis (Al-tolerant) and C. grandis (Al-sensitive) were cultured by hydroponics using the nutrient solution without Al3+ (as a Control) or with 1.0 mM Al3+ (as Al toxicity). The Al distribution and translocation were investigated by CW fragmentation to explore the primary Al-binding sites of citrus species. The study also examined the relative expression of genes associated with Al distribution, the kinetics analysis of Al adsorption and desorption, and FTIR analysis of the root CW of two citrus species. The objective of the study is to increase our understanding of the physiological mechanisms underlying the adaptation of citrus species to excessive levels of Al.


The Al distribution at the tissue level of citrus species

As shown in Fig. 1.0 mM Al treatment significantly increased Al content in lateral roots (Fig. 1a) and primary roots (Fig. 1b) compared to the Control in seedlings of two citrus species. A significant increase of Al content was also found in the Al-treated leaves and the stems in C. grandis seedlings (Fig. 1c and d). However, no significant difference in Al content was observed in the Al-treated leaves and stems of C. sinensis seedlings compared to the Control. The comparison between citrus species shows that the leaves and stems of C. grandis had remarkably higher Al content than C. sinensis under Al treatment. In contrast, C. sinensis lateral roots had a notably higher Al content than those of C. grandis under high Al concentration. Additionally, the Al content at tissue level was found to be lateral roots > primary roots > leaves > stems under Al stress.

Fig. 1
figure 1

The effects of Al toxicity on Al distribution in lateral roots A, primary roots B, leaves C and stems D of C. sinensis and C. grandis seedlings. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 1.0 mM Al3+ (1.0 mM Al toxicity, pH 4.3) for 21 days. The values represent mean ± SE (N = 5). Significant differences (p ≤ 0.05) between treatments are indicated by different letters

The Al distribution at CW fragments of citrus species

The results of Fig. 2 show the Al content significantly increased in the Al-treated root CW of two citrus species compared to Control. The Al level in the root CW was about 8 to 10 times higher than the lateral roots under Al toxicity. Compared to C. grandis, C. sinensis had a significantly higher Al content in the Al-treated root CW. Differentially, no significant difference of Al content was found among the CW residues after the removal of pectin from the root CW in two citrus species in both the control and the Al toxicity treatment.

Fig. 2
figure 2

The Al content in different root CW components of C. sinensis and C. grandis seedlings. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 1.0 mM Al3+ (1.0 mM Al toxicity, pH 4.3) for 21 days. Dry lateral roots were used for CW extraction and Al quantification. The values represent mean ± SE (N = 5). Significant differences (p ≤ 0.05) between treatments are indicated by different letters

The relative expression of genes associated with Al transport and distribution

The relative expression of genes involved in Al transport and distribution of two citrus species was presented in Fig. 3. Compared to the Control, Al toxicity upregulated the expression of Cs6g03670.1 (3 A) and Cg1g021320.1 (3B) significantly in roots of two citrus species. Besides, the relative expression level of Cs6g03670.1 and Cg1g021320.1 was significantly higher in C. grandis compared to C. sinensis under Al toxicity. Differentially, the relative expression of Cs3g18690.1 was upregulated in C. sinensis while downregulated remarkably in C. grandis (3 C). Compared to Control, no significant difference in the relative expression of Cs6g05460.1 was found in Al-treated roots of C. sinensis. However, the Al toxicity upregulated the relative expression Cs6g05460.1 in C. grandis roots compared to Control (3D).

Fig. 3
figure 3

Relative expression levels of Cs6g03670.1 A, Cg1g021320.1B, Cs3g18690.1C and Cs6g05460.1D in the lateral roots of C. sinensis and C. grandis seedlings under Al toxicity. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 1.0 mM Al3+ (1.0 mM Al toxicity, pH 4.3) for 21 days. The lateral roots of citrus seedlings were harvested for RNA extraction and real-time PCR. The gene relative expression level was normalized to the Control sample. The values represent mean ± SE (N = 5). Significant differences (p ≤ 0.05) between treatments are indicated by different letters

The Al adsorption and desorption analysis of root CW of citrus species

The CW of the lateral root of two citrus species was extracted for kinetics analysis of Al adsorption and desorption within 600 min. As shown in Fig. 4a, Al uptake in the root CW of C. sinensis was higher in comparison to C. grandis, indicating the root CW of C. sinensis had a higher capacity for Al binding than C. grandis. Moreover, the relative desorption rate in Fig. 4b showed that the lateral root CW of C. sinensis had a higher Al-binding rate than that of C. grandis. By comparison, C. sinensis had a lower Al desorption rate compared to C. grandis up to 600 min.

Fig. 4
figure 4

The Al Adsorption A and desorption B kinetics of lateral root CW of C. sinensis and C. grandis. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) for 21 days. The lateral root CW samples were extracted for Al adsorption and desorption kinetics analysis within 600 min

The FTIR spectra of lateral root CW

The alterations of CW composition and structure by Al toxicity were revealed by FTIR analysis (Fig. 5). The wavenumber of spectra from two citrus species and related assignments were listed in Table 1. The results show that the root CW of the Control from two citrus species had almost the same band position, indicating the similar composition of chemical groups of the root CW. However, band positions shifted under Al toxicity differentially in two citrus species. For instance, the vibration located at 3400 cm− 1 was moved to 3396 cm− 1 in C. grandis by Al toxicity. The vibration was shifted from 2856 cm− 1 to 2858 cm− 1 in C. sinensis and 2858 cm− 1 to 2860 cm− 1 in C. grandis by Al toxicity. It was also strikingly to find that most band positions from 1800 cm− 1 to 800 cm− 1, associated with polysaccharides, amide and ester, were shifted in both of two citrus species by Al toxicity. Apart from the band position shift, the relative absorbance at most band positions was also decreased by Al toxicity in two citrus species compared to the Control (Fig. 5a and b). The digital subtraction spectra were generated by subtracting the Al-treated spectra from the Control spectra of the CW of two citrus species, respectively. As found in Fig. 5c, the band intensity of the C. grandis was stronger than that of C. grandis overall. The OPLS-DA (orthogonal partial least-squares discrimination analysis) on the relative absorbance also reflected a more apparent separation between the Control and Al-toxic CW of C. grandis than C. sinensis (Fig. 5d).

Table 1 The infrared absorption frequencies of the CW and tentative assignment. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 1.0 mM Al3+ (1.0 mM Al toxicity, pH 4.3). The lateral root CW samples were extracted for FTIR spectra analysis
Fig. 5
figure 5

The FTIR spectra of the lateral root CW in the region of 4000–500 cm− 1 A, 1800–800 cm− 1 B, digital subtraction spectra C and the OPLS-DA of relative absorbance D of two citrus species. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 1.0 mM Al3+ (1.0 mM Al toxicity, pH 4.3). The lateral root CW samples were extracted for FTIR spectra analysis. The digital spectra represent Control CW minus Al toxic-CW. The values represent mean ± SE (N = 5)


Citrus fruit trees are superbly adapted to the acid soils with potentially high concentrations in south China [21]. Understanding of Al partition and mobilization in vivo is pivotal to revealing the mechanism of Al tolerance of citrus species. Moreover, discerning Al binding sites in citrus species is of great significance in the development of Al mitigation strategies. The present study addressed these challenges. Hydroponic culture has been widely used to explore the ion behavior of citrus species [35, 36]. Compared to our previous study in sandy culture with a 1.0 mM Al treatment for 18 weeks [23], the present 21 days’ hydroponic culture of citrus species resulted in almost the same Al level in leaves, indicating a reliable treatment for this study.

It has been shown that Al-induced phytotoxicity has many target sites from the apoplast to symplast in higher plants [37]. Accordingly, plant species vary in Al-tolerance and have evolved different strategies to cope with Al toxicity based on Al distribution and translocation. Plant species native to acid soils are often found to retain excess Al in insensitive roots, protecting leaves from metabolic disruption [38]. For instance, Kopittke et al. [13] reported that the Al-tolerant wheat accumulated more than four times of Al in roots compared to the sensitive line. Similarly, the higher Al content on the root apex was also observed in Al-tolerant common bean compared to an Al-sensitive genotype [39]. The present results support a greater accumulation of Al in roots under Al stress compared to shoots in citrus species (Fig. 1). Furthermore, the results also demonstrated that a significantly higher Al storage in lateral roots but significantly lower Al content transported to the shoots in C. sinensis compared to C. grandis under Al stress. Likewise, the higher Al translocation of C. grandis than C. sinensis was also found in 1.0 mM Al-treated citrus seedlings under 18 weeks’ sandy culture [11]. The relative expression level of genes directly involved in Al transport of citrus species indicated lower expression of Cs6g03670.1(ALS3) and Cg1g021320.1(Nramp6) could result in less Al transport from roots to shoots in C. sinensis compared to C. grandis (Fig. 3 A and 3B), which was in line with our previous investigation [40]. However, the Al stress within 21 days in the present study did not significantly affect the biomass accumulation of two citrus species (data not shown). With the stress duration increased to 15 weeks, the C. sinensis seedlings had remarkably higher biomass accumulation than C. grandis in both leaves and roots (Additional file 1: Figure S1). Conclusively, the relatively higher Al tolerance of C. sinensis is related to less Al translocation from the roots to shoots.

The plant root CW is the first defense against Al toxicity. Clarkson et al. [41] revealed that over 85% of Al accumulated on the CW of barley roots, and for woody plants, more than 88% of total Al was localized in the root CW of the conifer [42]. In the present study, the CW of citrus lateral roots accumulates about 8 to 10 times higher Al content than lateral roots, indicating the prominent roles of the root CW in Al immobilization of citrus species. Interestingly, the ratio of CW-binded Al is very close to the finding of Al-treated tea (Camellia sinensis) roots [43]. Moreover, the comparison of Al distribution in CW fractions suggests pectin has the greatest affinity for Al of CW polysaccharides in citrus roots. The contribution of pectin in Al sequestration was also reported in rice roots [44]. Li et al. [45] proposed that a high density of carboxylic groups on the pectin contributes to Al binding. Further studies regarding pectin content and related structural deformation of roots under Al stress of citrus species are needed to reveal the role of pectin in Al detoxification.

Ma et al. [46] reported that the CW of Al sensitive wheat had higher Al retention than Al tolerant cultivar under 10 µM Al within a 9 h exposure time. By contrast, we observed that a remarkably higher Al content in the CW of C. sinensis lateral roots than that of C. grandis (Fig. 2), which is consistent with the higher Al content of lateral roots in C. sinensis than C. grandis. Therefore, we propose that the Al distribution pattern in higher plants depends on the toxic intensity, such as Al level and stress duration. For example, the Al tolerant cultivar exclude Al encountering weak Al stress, which resulted in less Al accumulation. However, when the Al exclusion is not enough for Al detoxification, the excessive Al will be transported and redistributed in vivo, such as Al stabilization on the roots or CW.

The adsorption and desorption kinetics demonstrated that the root CW of C. sinensis, an Al-tolerant species, had a higher Al affinity than C. grandis (Fig. 4). By contrast, the root CW of C. grandis exhibited a lower Al adsorption and a higher Al desorption, indicating less tight Al-binding on the root CW, which would facilitate higher Al translocation from apoplast to symplast. Therefore, we infer that Al-tolerant woody plants tend to retain excess Al on the root CW to diminish Al translocation owing to their high retention capacity of the root systems. Besides, the Al binding firmly on roots is economical for Al resistance considering the energy cost during Al translocation. The findings of the present study also implied that organic material prepared from CWs is promising in alleviating the Al toxicity of the citrus plants in acidic red soils.

The Al binding resulted in modification of the root CW, which could be assessed by FTIR analysis [47, 48]. The results of this study show that almost no new characteristic peaks emerged indicating less effect of Al toxicity on the types of functional groups on the CW by Al toxicity overall in two citrus species. The modification of CW by Al stress is mainly dependent on the abundance of chemical groups on the root CW of citrus species. For instance, the spectra at 3400 cm− 1 (-OH stretching), was shifted to 3396 cm− 1 under Al stress in C. grandis, suggesting the changes in hydrogen-bonding mode and the damaging of connections between CW components by Al toxicity (Table 1). The results support less Al tolerance of C. grandis than C. sinensis by considering the flexible deformation of hydrogen bonds between molecules [26]. Also, a previous study has shown that the absorbance at 1740 and 1649 cm− 1 represents the absorption of the esterified and non-esterified carboxyl groups of pectin, respectively [49]. The present results of downregulated relative absorbance at 1740 cm− 1 and 1649 cm− 1 were coincident with significantly higher Al accumulation in the pectin (Fig. 5c), suggesting the role of CW pectin in Al-binding under Al toxicity. Besides, it is also interesting to find that the vibrations from 1200 cm− 1 to 900 cm− 1 (Table 1), which belong to the polysaccharide fingerprint region [50], shifted and decreased under Al toxicity. The results indicated that the altered structure and content of CW polysaccharides under Al toxicity would affect the Al binding on the root of citrus species. Both of the digital subtraction spectra (Fig. 5c) and the OPLS-DA (Fig. 5c) of relative absorbance in two citrus species supported a greater alteration of the CW in C. grandis compared to C. sinensis, such as more severe damage under Al toxicity. Similarly, a higher relative absorbance of the upper leaves corresponding to a much obvious symptom of boron deficient orange seedlings compared to lower leaves has also been reported based on the FTIR analysis [35]. Further studies based on isotope labeling of Al and pectin deformation and polysaccharides quantification of the citrus root CW are needed to disclose the Al spatial and temporal distribution of Al.


At the tissue level, citrus lateral roots were the primary Al-binding site under Al toxicity. At the subcellular level, the pectin of the CW was most abundant in the Al-accumulation of citrus species. Compared to C. grandis, a less tolerant citrus species, C. sinensis had a higher Al retention on the root CW and a lower Al translocation efficiency from roots to shoots upon exposure to toxic levels of Al (1.0 mM Al). Both the transcriptional regulation of genes related to Al transport and the structural modification of root CW contributed to the Al translocation of two citrus species. Future investigations on the Al partition and translocation mediated by CW modification are necessary to fully elucidate the mechanisms of Al tolerance in citrus species.


Plant culture and treatments

The citrus species ‘Xuegan’ [Citrus sinensis (L.) Osbeck] and ‘Suanyou’ [Citrus grandis (L.) Osbeck] used in the study were identified by Professor Lin-tong Yang of Fujian Agriculture and Forestry University (Fuzhou, China) and deposited as living materials for research purposes in the demonstration orchard of Fujian Academy of Forestry Sciences (FAFS). In December 2018, citrus fruits were harvested under the permission of Professor Xiang-xi Xiao in FAFS and stored in a fridge at 4 ℃. For germination, the seeds of C. sinensis and C. grandis were sown in a plastic tray filled with clean river sand at the greenhouse in early April of 2019. Four weeks after germination, seedlings of uniform size (about 10 cm) were transferred to black tanks containing nutrient solution and aerated for 30 min every two hours. The nutrient solution contained 1 mM KNO3, 1 mM Ca(NO3)2, 0.1 mM KH2PO4, 0.5 mM MgSO4, 10 µM H3BO3, 2 µM MnCl2, 2 µM ZnSO4, 0.5 µM CuSO4, 0.065 µM (NH4)Mo7O24 and 20 µM Fe-EDTA. The pH of the nutrient solution was adjusted to 4.30 using 1 M HCl or NaOH and was replaced every two days. Three months after transplanting, the plants were subjected to the treatments with 0 (Control) or 1.0 mM Al (Al toxicity) in the nutrient solution described above (pH 4.30). The samples of citrus leaves, stems, primary roots and lateral roots were divided and collected 21 days after treatments when visible leaf chlorosis appeared on Al-treated C. grandis leaves.

Quantification of Al at the tissue level

The leaves, stems, primary roots and lateral roots of citrus species were dried and digested in HNO3/HClO4 (5:1, v/v), and Al content was quantified according to Hsu [51].

Quantification of Al on CW fractions of citrus lateral roots

The crude CW of citrus lateral roots was extracted according to Zhong and Lauchli [52] with modifications. Briefly, about 50 mg citrus lateral root was powdered and polled into a centrifuge tube with 5 mL ice-cold 75% ethanol for 20 min on ice. The samples were then centrifuged at 1000 g for 10 min. The supernatant was discarded, and the resulting pellets were centrifugated at 17,000 g for 10 min three times with 5 mL 80% ethanol, methanol-chloroform mixture (1:1, v/v) and acetone, respectively. The final pellets were pooled as crude CW after being dried and weighed.

The dry crude CW from the lateral roots of citrus seedlings was further fractioned according to Yang et al. [17] Briefly, the dry crude CW was added into ammonium oxalate (containing 0.1% NaBH4, pH = 4.0) (5 mg CW/1mL solution) in a boiling water bath for one hour and centrifuged at 17,000 g for 10 min for three times to remove the pectin, the resulting pellet (CW-pectin) was pooled and dried. The CW-pectin fraction was extracted by 4% KOH (containing 0.1% NaBH4) or 24% KOH (containing 0.1% NaBH4) under room temperature three times for 24 h in total to further remove the hemicellulose 1 (HC-1) and hemicellulose 2 (HC-2). The pooled pellets were CW-pectin fractions without HC1 (CW-pectin-HC1) and HC2 (CW-pectin-HC1-HC2), respectively. The Al content of the CW and CW fractions (CW-pectin, CW-pectin-HC1 and CW-pectin-HC1-HC2) was quantified according to the method described above. The Al content of CW and CW fractions was expressed as mg · g− 1 DW (dry weight) of lateral roots.

The relative expression analysis of genes involved in Al translocation

Lateral roots of two citrus species were harvested for the relative expression analysis of genes (Cs6g03670.1, Cg1g021320.1, Cs3g18690.1 and Cs6g05460.1) involved in Al translocation according to Wu et al. [40]. Briefly, total RNA in lateral roots was extracted using TRIzol reagent (Invitrogen, Carlsbad, CA, USA). The Fastking FIRST STRAND cDNA synthesis kit (Tiangen, Beijing, China) was used for cDNA synthesis following the manufacturer’s instructions. RT-qPCR was performed using 2 RealStar Green Fast Mixture (Genstar, China) in CFX96™ Real-Time System according to the manufacturer’s instructions. The 20 µL reaction system contained 10 µL iQ SYBR green supermix, 0.5 µL each of 10 µM primers, 1.0 µL (5 ng) DNA template, and 8.0 µL RNAase-free H2O. The program consisted of initial denaturation at 95 C for 2 min, followed by 40 cycles of 95 C for 10 s, 57 C for 35 s and 72 C for 30 s. Citrus genes actin (Cs1g05000.1) was used as internal references [53]. The primers were designed using Primer Premier 5 software (Premier Biosoft Ltd., Palo Alto, CA, USA) based on the gene sequences from Citrus Genome Database ( and listed in Table 2. The data were processed by the method of 2−ΔΔCT according to Livak and Schmittgen [54]. The gene relative expression was normalized to Control. The fold changes of each gene were used for statistical analysis. There were 4 biological replications with 3 technical replicates of each.

Table 2 Genes and their primers for relative expression analysis using RT-qPCR

Al adsorption and desorption kinetics

The Al adsorption and desorption kinetics were performed according to Zheng et al. [55] with modifications. Briefly, the adsorption solution of 0.5 mM Al3+ in 0.5 mM CaCl2 (pH 4.30) was pumped by a peristaltic pump at 0.2 mL/min through a 2 mL column loaded with 10 mg root CW for Al adsorption. The solution after CW adsorption was then collected by a fraction collector at 20 min intervals until the Al content was equal to the adsorption solution. The residue Al3+ left in the system was washed by 0.5 mM CaCl2 (pH 4.5) at 0.6 mL/h for 1 h before Al desorption by 2.5 mM CaCl2 (pH 4.30) at 0.2 mL/h until the Al concentration in the collector was below the detection limit. Finally, the Al content in the fraction collector was quantified, and the kinetics were analyzed within 600 min. The Al absorption and desorption kinetics were performed three times independently.

FTIR spectra analysis

2 mg dry CW of citrus lateral root was mixed with 200 mg KBr and pressed into a disk by FW-5 A Pressor. The IR spectra of CWs ranging from 4000 − 400 cm-1 were recorded using Vertex 70 spectrometer with a resolution of 4 cm-1 and 32 scans per sample. The obtained spectra were normalized and baseline-corrected by OPUS management software before being exported to Excel. The data of FTIR spectra were processed by Origin Pro 2020b (OriginLab Corporation, USA). The OPLS-DA was performed in SIMCA 14.1 (Umetrics AB, Umea, Sweden).

Data analysis

Data analysis was performed by two-way analysis of variance, and significant differences (P < 0.05) among treatments were statistically evaluated by two-way ANOVA using Duncan’s test, using the SPSS 16.0 (SPSS Corp., Chicago, IL, USA). All the values are presented as means ± SE. Figures except OPLS-DA were generated by using Sigmaplot 12.0.

Availability of data and materials

The DNA sequences are accessible in Citrus Genome Database ( All data analyzed in this study are included in this published article and its additional files.



Al sensitive 3


cell wall


dry weight


Fourier transform infrared spectroscopy




natural resistance-associated macrophage protein


orthogonal partial least-squares discrimination analysis


  1. Guo JH, Liu XJ, Zhang Y, Shen JL, Han WX, Zhang WF, Christie P, Goulding KWT, Vitousek PM, Zhang FS. Significant acidification in major Chinese croplands. Science. 2010;327(5968):1008–10.

    Article  CAS  PubMed  Google Scholar 

  2. Lindsay WL, Walthall PM. The solubility of aluminum in soils. In: The environmental chemistry of aluminum. Boca Raton: CRC Press; 2020. pp. 333–61.

    Chapter  Google Scholar 

  3. Li J, Su L, Lv A, Li Y, Zhou P, An Y. MsPG1 alleviated aluminum-induced inhibition of root growth by decreasing aluminum accumulation and increasing porosity and extensibility of cell walls in alfalfa (Medicago sativa). Environ Exp Bot. 2020;175:104045.

    Article  CAS  Google Scholar 

  4. Xia H, Riaz M, Zhang M, Liu B, El-Desouki Z, Jiang CC. Biochar increases nitrogen use efficiency of maize by relieving aluminum toxicity and improving soil quality in acidic soil. Ecotox Environ Safe. 2020;196:110531.

    Article  CAS  Google Scholar 

  5. Kang DJ, Seo YJ, Futakuchi K, Vijarnsorn P, Ishii R. Effect of aluminum toxicity on flowering time and grain yield on rice genotypes differing in Al – tolerance. J Crop Sci Biotech. 2011;14(4):305–9.

    Article  Google Scholar 

  6. Valle SR, Carrasco J, Pinochet D, Calderini DF. Grain yield, above-ground and root biomass of Al – tolerant and Al – sensitive wheat cultivars under different soil aluminum concentrations at field conditions. Plant Soil. 2009;318:299–310.

    Article  CAS  Google Scholar 

  7. Yan L, Riaz M, Wu XW, Du CQ, Liu YL, Jiang CC. Ameliorative effects of boron on aluminum induced variations of cell wall cellulose and pectin components in trifoliate orange (Poncirus trifoliate (L.) Raf.) rootstock. Environ Pollu. 2018;240:764–74.

    Article  CAS  Google Scholar 

  8. Li Y, Han MQ, Lin F, Ten Y, Lin J, Zhu DH, Guo P, Weng YB, Chen LS. Soil chemical properties, ‘Guanximiyou’ pummelo leaf mineral nutrient status and fruit quality in the southern region of Fujian province, China. J Soil Sci Plant Nut. 2015;15(3):615–28.

    Google Scholar 

  9. Lin ZY, Myhre DL. Citrus root growth as affected by soil aluminum level under field conditions. Soil Sci Soc Am J. 1990;54(5):1340–4.

    Article  CAS  Google Scholar 

  10. Li D, Li X, Han QZ, Zhou YZ, Dong JL, Duan ZQ. Phosphorus application improved the yield of citrus plants grown for three years in an acid soil in the three gorges reservoir area. Sci Hortic. 2020;273:109596.

    Article  CAS  Google Scholar 

  11. Guo P, Qi YP, Cai YT, Yang TY, Yang LT, Huang ZR, Chen LS. Aluminum effects on photosynthesis, reactive oxygen species and methylglyoxal detoxification in two citrus species differing in aluminum tolerance. Tree Physiol. 2018;38(10):1548–65.

    Article  CAS  PubMed  Google Scholar 

  12. Silva CM, Cavalheiro MF, Bressan ACG, Carvalho BMO, Banhos OFAA, Purgatto E, Harakava R, Tanaka FAO, Habermann G. Aluminum-induced high IAA concentration may explain the Al susceptibility in Citrus limonia. Plant Growth Regul. 2019;87(1):123–37.

    Article  CAS  Google Scholar 

  13. Kopittke PM, McKenna BA, Karunakaran C, Dynes JJ, Arthur Z, Gianoncelli A, Kourousias G, Menzies NW, Ryan PR, Wang P. Aluminum complexation with malate within the root apoplast differs between aluminum resistant and sensitive wheat lines. Front Plant Sci. 2017;8:1377.

    Article  PubMed  PubMed Central  Google Scholar 

  14. Chen LS, Yang LT, Guo P, Jiang HX. Tang N.Aluminum toxicity and fruit nutrition. In: Fruit Crops. Amsterdam: Elsevier; 2020. p. 223–40.

  15. Yang TY, Qi YP, Huang HY, Wu FL, Huang WT, Deng CL, Yang LT, Chen LS. Interactive effects of pH and aluminum on the secretion of organic acid anions by roots and related metabolic factors in Citrus sinensis roots and leaves. Environ Pollut. 2020;262:114303.

    Article  CAS  PubMed  Google Scholar 

  16. Li CX, Yan JY, Ren JY, Sun L, Xu C, Li GX, Ding ZJ, Zheng SJ. A WRKY transcription factor confers aluminum tolerance via regulation of cell wall modifying genes. J Integ Plant Biol. 2020;62(8):1176–92.

    Article  CAS  Google Scholar 

  17. Yang JL, Zhu XF, Peng YX, Zheng C, Li GX, Liu Y, Shi YZ, Zheng SJ. Cell wall hemicellulose contributes significantly to Al adsorption and root growth in Arabidopsis. Plant Physiol. 2011;155(4):1885–92.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  18. Ye Y, Dai CY, Gu LP, Qu Y, Yang XY, Chen Q, Liu DQ, Wang CX, Cui XM. Distribution pattern of aluminum in Panax notoginseng, a native medicinal plant adapted to acidic red soils. Plant Soil. 2018;423(1):375–84.

    Article  CAS  Google Scholar 

  19. Larsen PB, Geisler MJ, Jones CA, Williams KM, Cancel JD. ALS3 encodes a phloem-localized ABC transporter‐like protein that is required for aluminum tolerance in Arabidopsis. Plant J. 2005;41(3):353–63.

    Article  CAS  PubMed  Google Scholar 

  20. Xia J, Yamaji N, Kasai T, Ma JF. Plasma membrane-localized transporter for aluminum in rice. P Natl Acad Sci. 2010;107(43):18381–5.

    Article  CAS  Google Scholar 

  21. Guo P, Qi YP, Yang LT, Lai NW, Ye X, Yang Y, Chen LS. Root adaptive responses to aluminum-treatment revealed by RNA-Seq in two citrus species with different aluminum-tolerance. Front Plant Sci. 2017;8:330.

    Article  PubMed  PubMed Central  Google Scholar 

  22. Jiang HX, Chen LS, Han S, Zhang JF, Lin JQ. Effects of Aluminum on the Growth of Young Citrus Seedlings. Chin Agric Sci Bull. 2009;25(04):167–70. (in Chinese).

    Google Scholar 

  23. Zhang H, Li XY, Chen LS, Huang ZR. The photosynthetic performance of two citrus species under long-term aluminum treatment. Photosynthetica. 2020;58(2):228–35.

    Article  CAS  Google Scholar 

  24. Guo P, Qi YP, Huang WL, Yang LT, Huang ZR, Lai NW, Chen LS. Aluminum-responsive genes revealed by RNA-Seq and related physiological responses in leaves of two Citrus species with contrasting aluminum-tolerance. Ecotox Environ Safe. 2018;158:213–22.

    Article  CAS  Google Scholar 

  25. Jiang HX, Yang LT, Qi YP, Lu YB, Huang ZR, Chen LS. Root iTRAQ protein profile analysis of two citrus species differing in aluminum-tolerance in response to long-term aluminum-toxicity. BMC Genomics. 2015;16:949.

    Article  PubMed  PubMed Central  Google Scholar 

  26. Li H, Yang LT, Qi YP, Guo P, Lu YB, Chen LS. Aluminum toxicity-induced alterations of leaf proteome in two citrus species differing in aluminum tolerance. Int J Mol Sci. 2016;17(7):1180.

    Article  PubMed Central  Google Scholar 

  27. Iqbal M, Saeed A, Zafar SI. FTIR spectrophotometry, kinetics and adsorption isotherms modeling, ion exchange, and EDX analysis for understanding the mechanism of Cd2+ and Pb2+ removal by mango peel waste. J Hazard Mater. 2009;164(1):161–71.

    Article  CAS  PubMed  Google Scholar 

  28. Chen SH, Cheow YL, Ng SL, Ting ASY. Mechanisms for metal removal established via electron microscopy and spectroscopy: a case study on metal tolerant fungi Penicillium simplicissimum. J Hazard Mater. 2019;362:394–402.

    Article  CAS  PubMed  Google Scholar 

  29. Deng PY, Liu W, Zeng BQ, Qiu YK, Li LS. Sorption of heavy metals from aqueous solution by dehydrated powders of aquatic plants. Int J Environ Sci Te. 2013;10(3):559–66.

    Article  CAS  Google Scholar 

  30. Sigee DC, Dean A, Levado E, Tobin MJ. Fourier – transform infrared spectroscopy of Pediastrum duplex: characterization of a micro – population isolated from a eutrophic lake. Eur J Phycol. 2002;37:19–26.

    Article  Google Scholar 

  31. Abidi N, Hequet E, Cabrales L, Gannaway J, Wilkins T, Wells LW. Evaluating cell wall structure and composition of developing cotton fibers using Fourier transform infrared spectroscopy and thermogravimetric analysis. J Appl Polym Sci. 2008;107(1):476–86.

    Article  CAS  Google Scholar 

  32. Farinella NV, Matos GD, Arruda MAZ. Grape bagasse as a potential biosorbent of metals in effluent treatments. Bioresource Technol. 2007;98(10):1940–6.

    Article  CAS  Google Scholar 

  33. Saha PD, Chakraborty S, Chowdhury S. Batch and continuous (fixed – bed column) biosorption of crystal violet by Artocarpus heterophyllus (jackfruit) leaf powder. Colloids Surf B. 2012;92:262–70.

    Article  Google Scholar 

  34. Guibaud G, Tixier N, Bouju A, Baudu M. Relation between extracellular polymers’ composition and its ability to complex Cd, Cu and Pb. Chemosphere. 2003;52(10):1701–10.

    Article  CAS  PubMed  Google Scholar 

  35. Liu GD, Dong XC, Liu LC, Wu LS, Jiang CC. Boron deficiency is correlated with changes in cell wall structure that lead to growth defects in the leaves of navel orange plants. Sci Hortic. 2014;176:54–62.

    Article  CAS  Google Scholar 

  36. Yan L, Riaz M, Wu X, Du CQ, Liu YL, Lv B, Jiang CC. Boron inhibits aluminum-induced toxicity to citrus by stimulating antioxidant enzyme activity. J Environ Sci Heal C. 2018;36(3):,145–63.

    Article  CAS  Google Scholar 

  37. Zheng SJ, Yang JL. Target sites of aluminum phytotoxicity. Biol Plant. 2005;49(3):321–31.

    Article  CAS  Google Scholar 

  38. Watanabe T, Osaki M. Mechanisms of adaptation to high aluminum condition in native plant species growing in acid soils: a review. Commun Soil Sci Plan. 2002;33:1247–60.

    Article  CAS  Google Scholar 

  39. Rangel AF, Rao IM, Horst WJ. Intracellular distribution and binding state of aluminum in root apices of two common bean (Phaseolus vulgaris) genotypes in relation to Al toxicity. Physiol Plant. 2009;135(2):162–73.

    Article  CAS  PubMed  Google Scholar 

  40. Wu YM, Wang YY, Zhou YF, Meng X, Huang ZR, Chen LS, Yang LT. Analysis of interacting proteins of aluminum toxicity response factor ALS3 and CAD in Citrus. Int J Mol Sci. 2019;20(19):4846.

    Article  CAS  PubMed Central  Google Scholar 

  41. Clarkson DT. Interactions between aluminium and phosphorus on root surfaces and cell wall material. Plant Soil. 1967;27(3):347–56.

    Article  CAS  Google Scholar 

  42. Heim A, Brunner I, Frey B, Frossard E, Luster J. Root exudation, organic acids, and element distribution in roots of Norway spruce seedlings treated with aluminum in hydroponics. J Plant Nutr Soil Sc. 2001;164(5):519–26.

    Article  CAS  Google Scholar 

  43. Hajiboland R, Bastani S, Bahrami-Rad S, Poschenrieder C. Interactions between aluminum and boron in tea (Camellia sinensis) plants. Acta Physiol Plant. 2015;37:54.

    Article  Google Scholar 

  44. Nagayama T, Nakamura A, Yamaji N, Satoh S, Furukawa J, Iwai H. Changes in the distribution of pectin in root border cells under aluminum stress. Front Plant Sci. 2019;10:1216.

    Article  PubMed  PubMed Central  Google Scholar 

  45. Li XW, Li YL, Qu M, Xiao HD, Feng YM, Liu JY, Wu LS, Yu M. Cell wall pectin and its methyl-esterification in transition zone determine Al resistance in cultivars of pea (Pisum sativum). Front Plant Sci. 2016;7:39.

    PubMed  PubMed Central  Google Scholar 

  46. Ma JF, Shen RF, Nagao S, Tanimoto E. Aluminum targets elongating cells by reducing cell wall extensibility in wheat roots. Plant Cell Physiol. 2004;45(5):583–9.

    Article  CAS  PubMed  Google Scholar 

  47. McCann MC, Chen L, Roberts K, Kemsley EK, Sene C, Carpita NC, Stacey NJ, Wilson RH. Infrared microspectroscopy: sampling heterogeneity in plant cell wall composition and architecture. Physiol Plant. 1997;100(3):729–38.

    Article  CAS  Google Scholar 

  48. Chen L, Carpita NC, Reiter WD, Wilson RH, Jeffries C, McCann MC. A rapid method to screen for cell-wall mutants using discriminant analysis of Fourier transform infrared spectra. Plant J Mol Biol. 1998;16(3):385–92.

    Article  CAS  Google Scholar 

  49. Chatjigakis AK, Pappas C, Proxenia N, Kalantzi O, Rodis P, Polissiou M. FTIR spectroscopic determination of the degree of esterification of cell wall pectins from stored peaches and correlation to textural changes. Carbohydr Polym. 1998;37(4):395–408.

    Article  CAS  Google Scholar 

  50. Barron C, Parker ML, Mills E, Rouau X, Wilson RH. FTIR imaging of wheat endosperm cell walls in situ reveals compositional and architectural heterogeneity related to grain hardness. Planta. 2005;220(5):667–77.

    Article  CAS  PubMed  Google Scholar 

  51. Hsu PH. Effect of initial pH, phosphate, and silicate on the determination of aluminum with aluminon. Soil Sci. 1963;96(4):230–8.

    Article  CAS  Google Scholar 

  52. Zhong HL, Lauchli A. Changes of cell wall composition and polymer size in primary roots of cotton seedlings under high salinity. J Exp Bot. 1993;44(261):773–8.

    Article  CAS  Google Scholar 

  53. Huang WL, Wu FL, Huang HY, Huang WT, Deng CL, Yang LT, Huang ZR, Chen LS. Excess copper-induced alterations of protein profiles and related physiological parameters in citrus leaves. Plants-Basel. 2020;9(3):291.

    Article  CAS  PubMed Central  Google Scholar 

  54. Livak KJ, Schmittgen TD. Analysis of relative gene expression data using real-time quantitative PCR and the 2– ∆∆CT method. Methods. 2001;25(4):402–8.

    Article  CAS  Google Scholar 

  55. Zheng SJ, Lin X, Yang J, Liu Q, Tang C. The kinetics of aluminum adsorption and desorption by root cell walls of an aluminum resistant wheat (Triticum aestivum L.) cultivar. Plant Soil. 2004;261(1):85–90.

    Article  CAS  Google Scholar 

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The authors thank Professor Richard G Donald (Dalhousie University, Halifax, Canada) for the linguistic assistance during the preparation of this manuscript.


This research was funded by the National Natural Science Foundation of China (31801950) and the Special Fund for Scientific and Technological Innovation of Fujian Agriculture and Forestry University (CXZX2019079S). The funders had no role in the design of the study and collection, analysis, and interpretation of data and in writing the manuscript.

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HZ wrote the manuscript; XL analyzed the experimental results; ML prepared the figures and tables; PH carried out the experiments; NL designed the experiment; ZH revised the drafts of the manuscript; LC reviewed drafts of the manuscript. All authors read and approved the final manuscript.

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Correspondence to Zeng-rong Huang.

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The authors declare that they have no competing interests. The author Li-Song Chen is a member of the editorial board of BMC Plant Biology.

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Additional file 1: Figure S1. 

The effects of Al toxicity on the DWs of whole plants (A), roots (B), stems (C), leaves (D), shoots (E) and ratio of root/shoot (F) of C. sinensis and C. grandis seedlings. Seedlings of C. sinensis and C. grandis were treated with nutrient solution (Control, pH 4.3) or supplemented by 0.5, 1.0 and 2.0 mM Al3+ (pH 4.3) for 15 weeks. The values represent mean ± SE (N = 6). Significant differences (p ≤ 0.05) between treatments are indicated by different letters.

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Zhang, H., Li, Xy., Lin, Ml. et al. The aluminum distribution and translocation in two citrus species differing in aluminum tolerance. BMC Plant Biol 22, 93 (2022).

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