The Possibilities of Using Common Buckwheat in Phytoremediation of Mineral and Organic Soils Contaminated with Cd or Pb

Abstract

The results of this study provided accurate guidance on the possibility of using common buckwheat (Fagopyrum esculentum Moench) in phytoremediation practices for mineral soil or organic soils contaminated with Cd or Pb. Based on a model pot experiment, the tolerance of buckwheat to elevated contents of cadmium and lead in organic and mineral soils was examined. The soils were differentiated into neutral and acidic, and amended with metals at doses of 10 mg Cd kg⁻¹ DM and 100 mg Pb kg⁻¹ DM of soil. The growth, development, biomass, translocation coefficient, and tolerance index (TI) of the tested plants were examined. The use of metals caused a weakening of plant growth and development, as well as intensified chlorotic and necrotic changes to the buckwheat leaves. The application of Cd caused a statistically significant decrease in shoot biomass. The plants growing in organic acidic soil were most vulnerable to Cd toxicity. The (TI) values confirm the generally low tolerance of buckwheat to Cd, except for the treatment in organic neutral soil, and the high tolerance of this plant to Pb in all the studied soils.

1. Introduction

Common buckwheat is a plant with many uses, and studies concerning the tolerance of this plant to soil metal in polluted areas are essential, both in phytoremediation practices and, in crop production planning and management. Understanding the capability of this plant to absorb toxic metals such as Cd and Pb from different soils is also important in the context of ecology and public health safety. Buckwheat contains antioxidants (routine, quercetin, and others) and has pro-health effects, therefore this plant is used in medicine.

The problem of environmental pollution with heavy metals, such as Cd, Pb, Cu, Ni, Zn, and others, and their toxicity to living organisms has attracted the attention of researchers [1,2]. Soil pollution is particularly relevant in areas surrounded by various industrial plants, metallurgical plants, steel mills, combined heat and power plants. Moreover, the constantly high level of world metal mining, processing, and the resulting waste are a source of environmental pollution [3]. For this reason, large areas of soils in the world within industrial regions, are restricted for food production due to the maximum permissible levels of metals in plants. Appropriate recommendations were set by EU regulation [4]. Cadmium and lead are currently considered to be toxic metals, whose presence in the soil in higher amounts than the natural biogeochemical background may threaten the natural environment. Plants, which are part of this environment in the soil–plant–animal–human system, as a result of taking up metal from the soil contribute to its further circulation [5,6]. Some plant species have developed mechanisms that allow an increased uptake of a toxic components without harming their body, but the risk of harmfulness or toxicity in subsequent links of the trophic chain, remains. For this reason, research that focuses on remediation methods for soils contaminated with metals is often carried out. Much attention is particularly paid to two phytoremediation techniques: phytoextraction and phytostabilization [7,8]. In the course of phytoextraction, the soil is cleaned of excess toxic metals by removing plants that have accumulated them in their biomass. The goal of phytostabilization is to limit the mobility and bioavailability of metals by growing plants that absorb them and retain them in their root system. In addition, the vegetation cover limits the spread of soil particles with contaminants into the ecosystem.

Scientists are conducting research to assess the potential of common buckwheat for phytoremediation [9]. Harada and Hatanaka [10] found higher concentrations of cadmium in the plants of the Polygonaceae family, compared to other studied plant families. Confirmation of the usefulness of buckwheat in phytoremediation techniques may have practical significance. When assessing a plant, many factors and the complexity of the process should be considered.

Common buckwheat Fagopyrum esculentum Moench (Polygonaceae), which was the subject of the present study, is an annual, dicotyledonous plant with a very short vegetation period (70–90 days). Buckwheat is distinguished by its good use of nutrients contained in the soil and does not require intensive mineral fertilization. It has a high resistance to pests and diseases, and therefore does not require special chemical protection. The aerial parts of buckwheat, especially the seeds, are used mainly for food purposes. Due to the presence of antioxidants (routine, quercetin, and others) and its pro-health effects, this plant is used in medicine.

Our study intended to show (i) how the presence of Cd and Pb in different soil types affects the growth of common buckwheat; (ii) if the growth of the plant and the biomass obtained, and thus the tolerance for a given metal, changes under the influence of the presence of another metal ion; and (iii) how experimental factors (soil, metals, pH) affect the process of transporting metals from the roots to the aerial parts of the studied plant.

The objective of the study was to determine, based on a model pot experiment, the tolerance of buckwheat to Cd or Pb, and its usefulness for the phytoremediation of organic and mineral soils. The soils differed in pH value (acidic or neutral) and in organic matter content. The buckwheat growth, development, biomass, and certain chemical indicators, depending on soil type, pH, and Cd or Pb addition, were determined.

2. Materials and Methods

2.1. Soils

The research was based on the results obtained in a two-year pot experiment carried out on two organic and mineral soils, with different pH values. The uncontaminated soils were sampled in agricultural areas of Lubelskie region (Poland). Soil material was taken from the surface layer (0–20 cm). The following soils, according to Polish Soils Classification [11], were used to fill pots:

• Podzolic soils, Typical podzolic soils—developed from light loamy sand,
• Organic soils, (fibric peat soils),
• Organic soils, (sapric peat soils).

The neutral reaction of mineral soil was obtained by applying calcium carbonate (CaCO₃) to mineral acidic soil, so as to double the hydrolytic acidity. The main agrochemical properties of the soils, determined before the experiment started, are listed in

Table 1. Agrochemical characteristics of soils used for the experiment.

Parameter		Mineral Neutral/Acidic	Organic Neutral	Organic Acidic
Particle size distribution:			not determined	not determined
1–0.1 Ø mm	%	74
0.1–0.2 Ø mm	%	18
<0.02 Ø mm	%	8
pHKCl		7.2/4.6	7.2	3.6
Organic C	%	1.32	18.7	64.0
Total:
Pb	mg kg−1	5.49	16.65	20.98
Cd	mg kg−1	0.10	0.43	0.30
Zn	mg kg−1	20.00	44.50	80.00

.

2.2. Pot Experiment

The soil material was transferred to 5 dm³ volume pots. The pots contained 4.8 kg of organic acidic soil, 5.5 kg of organic neutral soil, and 6.4 kg of mineral soil. Each soil was treated with 10 mg kg⁻¹ dry mass (DM) Cd (Cd(NO₃)₂) and 100 mg kg⁻¹ DM Pb (Pb(NO₃)₂). Metals were introduced once before sowing. Metal rates were applied to the soils according to the following scheme:

• 0 = control with no metal addition,
• Pb = Pb(II) in an amount of 100 mg kg⁻¹ DM,
• Cd = Cd(II) in an amount of 10 mg kg⁻¹ DM.

All soils were fertilized with N, P, and K using mineral salts: NH₄NO₃, 0.10 g N kg⁻¹ soil; CaHPO₄, 0.07 g P kg⁻¹ soil; and KCl, 0.15 g K kg⁻¹. The NH₄NO₃ dose was divided into two equal parts and applied to all pots before and after sowing. During the experiment, the mineral soil humidity was adjusted to 60% of maximum water capacity, and 80% in the case of organic soils, by keeping water in pots at a constant weight.

Common buckwheat (Fagopyrum esculentum Moench) was a follow-up crop to rapeseed (Brassica napu L.). Seeds of the test plant were sown on 15 June. To prevent incomplete seedling emergence for the experiment, more seeds were sown than the number of plants planned for each pot. After successful germination, seedlings were thinned to 10 plants per pot. Plants were kept under natural light at all times. Plant growth and development were observed every day in the growing season. Plants were harvested during the flowering phase by cutting out the aerial parts (shoots). After harvesting, plants roots were separated from the soil and rinsed with deionized water. Then, the aboveground biomass (shoots) and roots were weighed. The plant samples were oven-dried to determine their dry matter.

2.3. Soil and Plant Chemical Analyses

The collected soil samples were air-dried, then ground in a porcelain mortar and sieved through 1-mm mesh. The soil samples were determined for:

-

mineral soil granulometric composition using Casagrande’s aerometric method with Prószyński’s modifications,

-

pH, potentiometry in 1 M KCl,

-

organic matter (C_org.), Tiurin’s method,

-

contents of organic matter in organic soils, by annealing,

-

contents of Cd and Pb in soils, analyzed after digesting the soil samples in the mixture of concentrated acids HCl and HNO₃ in the ratio of 3:1 (aqua regia).

Individual metals (Cd and Pb) were quantified in solution by means of flame atomic absorption spectrometry (AAS) on a Hitachi Z-8200 apparatus.

Cadmium and lead contents were determined in plant samples by applying the AAS technique after plant material digestion in concentrated H₂SO₄ with the addition of H₂O₂.

2.4. Data Analysis

The trial was arranged in a randomized blocks method. The design of the experiment included six pots in four replicates in mineral soil, and six pots in four replicates in organic soils.

Data obtained from experiments were statistically processed by means of variance analysis with Tukey confidence intervals. Differences were considered to be significant at p = 0.05 and highly significant at a p = 0.01 level of significance.

The tested plants were calculated for two indices (TI and TF) recommended for the evaluation of plants for phytoremediation. The tolerance index (TI) is the ratio between a biomass of treated plants (g DM pot⁻¹) and the biomass of control plants (g DM pot⁻¹). It specifies the degree of inhibition of plant growth in Cd or Pb contaminated soil and is helpful for evaluating the tolerance of common buckwheat to an excess of metals when growing in contaminated soils.

The translocation factor (TF) was calculated as the ratio of metal concentration (mg kg⁻¹) in the shoots and roots of the tested plant (TF = C_shoots/C_roots). In our experiment, this allowed evaluating the buckwheat’s ability to translocate Cd and Pb from roots to aerial parts when the plant was grown in mineral or organic soils at different pH.

3. Results

3.1. The Growth of Common Buckwheat Plants

Common buckwheat was sown in mid-June after harvesting spring rape. Plant emergence was even in all treatments. Plants from treatments in organic soils were slightly higher and better developed than ones from the treatments in mineral soil. After 2 weeks, plants grown in organic neutral and organic acidic soils were 12 cm and 7 cm high, respectively, and showed no symptoms of chlorosis. Common buckwheat sown in mineral soils grew slower compared to treatments in organic soils. The lamina of the crops, however, were larger and more saturated by chlorophyll (dark green color of leaves), particularly in the Pb treatment. At the edges older plant leaves, mild necrotic changes, often combined with chlorosis in Cd and Pb treatments, were observed. In plants grown in acidic mineral soil, purple discolorations were also found. The generative phase first began in plants in organic neutral soil, and was later in plants in mineral acidic soil. Plants growing in the soil developed from high peat (organic acidic), had less generative shoots than the plants in other treatments. Although buckwheat is a plant that tolerates low soil pH well, its growth in acidic soils, both mineral and organic, was slower, and the impact of metals was more severe. In the Pb treatment, the leaves underwent curling toward the center of the leaf blade, and deformations occurred. The weakest growth of plants was observed in acidic soils contaminated with cadmium. In the full flowering phase, just before the buckwheat harvest (end of July), yellowing and dropping of the oldest leaves were observed in organic soils.

3.2. Effects of Cadmium and Lead on Common Buckwheat Shoot Biomass

Experimental factors (type of soil and pH, metal addition) significantly modified the aerial (shoots) biomass (g DM pot⁻¹) of the tested plants (Figure 1). Significant interactions between soil and pH, as well as soil and cadmium, used in the experiment were also recorded. In organic soil, the average biomass of buckwheat shoots was higher (13.3 g pot⁻¹) than in mineral soil (11.3 g pot⁻¹). The soil pH was also a factor that significantly affected plant growth. In neutral soils, the growth of the buckwheat shoots was faster than in acidic ones, which resulted in a two-fold increase in biomass (16.6 g pot⁻¹) compared to the acidic soil (8.0 g pot⁻¹).

The effect of cadmium on the average biomass of the tested plant shoots was also significant. In the treatment with Cd addition, the obtained biomass amounted to, on average, 11.1 g per pot⁻¹, while in the control to 12.7 g per pot⁻¹).

The soil type and its reaction differentiated the aerial biomass of common buckwheat in the following, decreasing order: organic neutral > mineral neutral > mineral acidic > organic acidic. With regard to the control (12.2 g pot⁻¹), a significant buckwheat biomass decrease also occurred in the Cd treatment in mineral soil (8.8 g pot⁻¹), while in the case of “Pb” treatments (both mineral and organic soils) and the “Cd” treatment in organic soil no significant dependence of soil type on biomass amount was confirmed. Moreover, no significant influence of pH (acidic, neutral) on buckwheat shoot biomass in treatments with metals (“Cd”, “Pb”) was found.

3.3. Effects of Cadmium and Lead on Common Buckwheat Root Biomass

The type of soil, in relation to the roots, unlike the above-ground parts of buckwheat, did not significantly affect the dry mass yield (g DM pot⁻¹), Figure 2. However, the soil pH and the metals proved to be a factor significantly modifying the underground (roots) DM of the buckwheat. For a neutral reaction, the root biomass was almost twice as high as in acidic soils (1.5 g pot⁻¹ and 0.8 g pot⁻¹, respectively).

The use of lead resulted in an increase in root biomass (1.4 g pot⁻¹), while cadmium reduced its content (0.9 g pot⁻¹) significantly compared to the control (1.2 g pot⁻¹).

The soil type and its reaction were factors that significantly affected root biomass only in organic soils. In organic neutral soil, the growth of the buckwheat roots was better than in organic acidic soil, which resulted in an almost four-fold increase in biomass, as compared to the acidic soil.

The stimulating effect of lead at a dose of 100 mg kg⁻¹ DM of soil on the biomass of buckwheat roots was noted both in mineral and organic soils, but a highly significant increase (2.9 g pot⁻¹) compared to the control (1.3 g pot⁻¹) was recorded only in mineral soil. On the other hand, cadmium significantly reduced the root biomass in mineral soil compared to the control.

No significant influence of pH (acidic, neutral) and metals (“Cd”, “Pb”) on buckwheat root biomass was found.

3.4. Tolerance Index (TI)

Tolerance index (TI) indicates the plant’s tolerance to toxic metals and helps to assess the usefulness of the plant in phytoextraction (

Table 2. The indices of Fagopyrum esculentum tolerance to Cd and Pb when grown in different soils.

Treatment		TI *		TF **
Soil	Metal	Shoots	Roots	Cd	Pb
Mineral acidic	0	1.00	1.00	4.50	0.64
	Pb	1.15	1.23	4.56	0.04
	Cd	0.61	0.29	1.74	1.16
Mineral neutral	0	1.00	1.00	1.21	0.62
	Pb	0.99	1.04	2.39	0.21
	Cd	0.79	0.54	1.77	0.83
Organic acidic	0	1.00	1.00	2.78	0.77
	Pb	0.99	1.10	2.51	0.56
	Cd	0.91	1.16	5.11	0.69
Organic neutral	0	1.00	1.00	0.91	0.45
	Pb	1.03	1.23	0.60	0.07
	Cd	1.05	1.19	0.47	0.26

TI * = biomass of plants in treated (Cd or Pb) soil /biomass of plants in untreated (0, control) soil. TF ** = metal (Cd or Pb) concentration in aerial parts of plant (mg kg⁻¹)/metal (Cd or Pb) concentration in roots (mg kg⁻¹).

). The calculated TI values showed a different tolerance of buckwheat relative to cadmium and lead. The lowest TI values, 0.61 and 0.29 for buckwheat shoots and roots, respectively, were recorded in Cd amended mineral acidic soil. Similarly, in the case of neutral mineral soil contaminated with Cd, low index values of 0.74 in shoots and 0.54 in roots were found. In the remaining treatments (“Pb”), the TI was relatively high, and ranged from 0.99 to 1.23. The index value, TI = 0.91, implicating a slightly reduced tolerance of plant shoots, was also reported for organic acidic soil in the Cd treatment. The obtained data confirm the generally low tolerance of buckwheat in relation to Cd, except for plants from the treatments in organic neutral soil, and the high tolerance to Pb in both mineral and organic soils.

3.5. Translocation Factor (TF)

The translocation factor (TF) is fundamental for the evaluation a plant’s usefulness in phytostabilization. This parameter was very high for Cd in buckwheat in most of treatments, ranging from 1.21 to 5.11 (Table 2). The exception were the treatments in neutral organic soil, where TF values were low and ranged from 0.07 to 0.26, which means that the plant transported to the aerial parts between 7% and 26% of the cadmium contained in the roots.

Much lower TF values were calculated for lead than for cadmium in buckwheat. Only in plants from acidic mineral soil contaminated with cadmium did the TF for lead exceed the threshold value (TF < 1), reaching the level TF = 1.16. In other treatments, this parameter was at a much lower level (0.04–0.83) than the required threshold value (TF < 1). The lowest TF values for lead were found in treatments with the addition of lead (0.04–0.56).

4. Discussion

Common buckwheat Fagopyrum esculentum (Polygonaceae) is a plant of many uses. It is grown as a cereal for humans and as a forage crop for livestock, as well as being applied in herbal medicine and beekeeping [12,13]. The areas of research on the non-food use of buckwheat include cleaning the soil of excess metals [14,15,16]. Common buckwheat is recognized as a hyperaccumulator of Pb [17]. Similarly, a high ability for Pb accumulation is displayed by Tartary buckwheat, which can grow in soil with high concentrations of this metal (10,000 mg kg⁻¹) [18]. The high buckwheat capacity for Pb²⁺ accumulation and the efficiency of the phytoremediation process can be enhanced by the presence of EDTA [19]. The results of the study by Tamura et al. [20] showed that common buckwheat grown in Pb-contaminated soil is able to absorb 8 g Pb kg⁻¹ dry mass in leaves without significant damage, while in roots 3.3 g Pb kg⁻¹. Based on these results, the authors proved that common buckwheat can be classified as an Pb-hyperaccumulator. Buckwheat is also known as a Cu and Zn accumulator [21]. It has a high Al bioaccumulation capacity (Al accumulator) and concentrates Al mainly in its leaves [22,23].

Lu et al. [24] found that the Cd accumulation in the leaves of Tartary buckwheat under Cd stress was markedly inhibited by an excess of endogenous sulfur, while the Cd concentration in roots increased significantly. The authors also concluded that the enhanced effect of surplus sulfur on antioxidant factors and antioxidant enzymes may play an important role in balancing the levels of reactive oxygen species in Fagopyrum tataricum leaves and roots.

Cadmium is highly mobile in soils in the pH range 4.5–5.5. It readily reaches plants through root uptake and translocation to the above-ground parts of plants. This element is mainly taken up by plants from the soil in the form of the ion Cd²⁺. Its uptake and transport depend on the plant species and genotype. The absorption of this metal increases at higher Cd content in the soil and at low pH values. Cadmium accumulation in plants may be also influenced by the presence of Zn in the soil solution.

Pirzadach et al. [25] revealed that Al-induced oxidative stress affected the growth indices, photosynthetic pigments, osmolytes, Al-uptake, translocation, and physiological attributes of the studied Fagopyrum species. The hyperactivity of antioxidant enzymes played a special role in the protection of buckwheat. The authors stated that the activities of the antioxidant enzymes, i.e., superoxide dismutase, ascorbate peroxidase, guaiacol peroxidase, glutathione reductase, and glutathione-S-transferase, were positively correlated with Al-treatment. Pirzadach et al. believes that Fagopyrum species have potential as a phytoremediation crop for contaminated areas.

Braud et al. [26] noticed that in moderately contaminated soils, despite an increase in the lead extraction rate with citric acid, buckwheat is not a very efficient plant for field Pb phytoextraction. Furthermore, Alves et al. [27] found buckwheat to be not very promising for Pb-phytoremediation programs.

There are many regions in Europe with large deposits of mine wastes, and many unmanaged sites contaminated with metals. Scientists have suggested that wastelands could be prepared for regular biomass production using metal tolerant vegetation or bioenergy crops (e.g., oilseed rape, buckwheat, willow) [28]. Soils that are polluted by metals and require remediation often surround historical industrial and mining plants. Due to their degradation, they have unfavorable chemical, physico-chemical, or biological properties for crop production. The premise for the use of buckwheat in phytoremediation is the fact that this plant uses soil resources better than other plant species and is able to also satisfy its nutritional requirements in soils less rich in macro- and microelements or in those contaminated by metals.

Soil type, granulometric composition, organic matter content, sorption properties, pH, and oxidoreductive potential have the greatest influence on the amount of phyto-available heavy metal that forms in the soil. Soil organic matter, in the form of humus compounds, contributes to reducing the amount of heavy metal forms available to plants, thereby producing a crop with reduced heavy metal content. Metal speciation in the soil also could affect the availability and uptake of metals by plants from the soils. The hazard of heavy metals especially increases in contaminated soil with the increase of its most mobile and bioavailable fractions. The studies of Awad et al. [29] revealed that biochar stabilized heavy metals and could reduce their solubility in contaminated soils. The authors stated that acid soluble metals decreased, while the fraction bound to organic matter increased compared to biochar untreated pots.

Wang et al. [18], investigating the mechanisms of Pb tolerance and hyperaccumulation in Tartary buckwheat leaves, found that differentially expressed genes (DEGs) are involved in the mechanisms of hyperaccumulation, e.g., iron-binding proteins and membrane transport proteins. Scientists [30,31] revealed that the endogenous application of the plant hormone salicylic acid could play a pivotal role in protecting plants suffering from heavy metal stress. The authors emphasized that further studies are needed to detect salicylic acid-responsive genes, proteins, and metabolites affected by heavy metal stress. In addition, the defensive ability of buckwheat FeMT3 protein and the great responsiveness of its promoter to metal ions during exposure were found [32].

In the present study, soil type and pH were important factors affecting the growth of common buckwheat. The obtained biomass of plant shoots, depending on the type of soil and pH, was significantly decreased, in the following order: organic neutral > mineral neutral > mineral acidic > organic acidic. This sequence proves the sensitivity of Fagopyrum esculentum to acidic conditions, both in organic and mineral soils, which was expressed by the statistically significant two-fold increase in mean biomass of neutral soils (16.6 g pot ⁻¹) compared to acidic soils (8.0 g pot⁻¹). Despite the fact that buckwheat makes good use of nutrients from light soils, it has lower yields in acidic soils.

In the present study (Cd and Pb treatments), necrotic changes, often combined with chlorosis on buckwheat leaves, were found. Plants grown in acidic mineral soil also had purple discolorations, which may have indicated the lower availability of P for such a plant. Tuma et al. [33] stated a higher content of Cd in most treatments, mainly after CdSO₄ application, in the bottom yellow leaves than in upper green leaves of Avena sativa L. According to the authors this indicates the accumulation of Cd in aging tissues and its difficult reutilization.

The highest sensitivity of buckwheat to soil Cd contamination (10 mg Cd kg⁻¹ DM) was found in mineral soil. A significant effect of Cd in mineral soil on buckwheat shoot biomass decrease (8.8 g pot⁻¹) in comparison to the control (12.2 g pot⁻¹) took place. Moreover, cadmium significantly reduced the root biomass in mineral soil compared to the control. In the case of Pb applied at a dose of 100 mg kg⁻¹ DM of soil, no harmful effects were found.

In the works of different authors, the overall negative effect of cadmium and lead on the economic yield and biomass of common buckwheat and other plant species was confirmed [34]. The toxicity threshold limits of Cd for a 10% reduction in the relative yield of buckwheat, depending on the amount of FYM application, were 6.4–16.0 mg Cd kg⁻¹ dry matter in buckwheat [35].

In the present study, buckwheat most often met a condition of the plant’s suitability for phytostabilization, which is Pb transport from the roots to the above-ground part of the plant. A higher Pb translocation coefficient determined for buckwheat (TF = 1.16) occurred in acidic mineral soil contaminated with cadmium.

For Cd, except treatments in neutral organic soil, the TF was at a much higher level than the required threshold value (TF < 1). This parameter in the case of cadmium probably excludes buckwheat as a plant useful for phytostabilization purposes when growing in soil composed of light loamy sand and in organic acidic soil. According to Lou et al. [36] the translocation factor (TF) was greater in perennial ryegrass treated with Cd than with Pb, and the dose of Cd had no effect on TF.

The obtained data confirm that at the applied doses of Cd and Pb, buckwheat was less tolerant to Cd, except for plants from treatments in organic neutral soil, while it was tolerant to Pb in both mineral and organic soils. Horbowicz et al. [37] stated that Cd²⁺ ions are more harmful than Pb²⁺ for the growth of buckwheat seedlings.

5. Conclusions

The above study, carried out in different types of soil, allowed obtaining precise guidelines regarding the possibility of using buckwheat in the remediation practices of mineral soil (Typical podzolic soil) or organic soil (Peat soils) contaminated with Cd or Pb.

The soil type and its reaction significantly affected the buckwheat growth. The highest biomass of plants was obtained in organic neutral soil and the lowest in acidic neutral soil. Plants growing in organic acidic soil were also most vulnerable to Cd toxicity.

The TI (tolerance index) data confirmed the generally low tolerance of buckwheat in relation to Cd, except for plants from the treatments in organic neutral soil, and the high tolerance to Pb in both mineral and organic soils.

On the basis of the translocation factor TF, we can conclude that buckwheat has a high lead phytostabilization potential, while for cadmium it is low. This plant can be considered as a candidate for phytostabilization in Pb-polluted soils.