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Journal of Arid Land
Journal of Arid Land  2023, Vol. 15 Issue (2): 218-230    DOI: 10.1007/s40333-023-0004-9     CSTR: 32276.14.s40333-023-0004-9
Research article     
Exogenous addition of nitrate nitrogen regulates the uptake and translocation of lead (Pb) by Iris lacteal Pall. var. chinensis (Fisch.) Koidz.
SUN Mengjie1, GUO Shiwen2, XIONG Chunlian3, LI Pinfang1,*()
1College of Land Science and Technology, China Agricultural University, Beijing 100193, China
2College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, China
3Yibin Ecological Environment Monitoring Center, Sichuan 644099, China
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Abstract  

Since Pb is a non-biodegradable inorganic pollutant and a non-essential metal, its long-term presence in soil poses a great threat to the environment. Iris lactea Pall. var. chinensis (Fisch.) Koidz., a perennial dense bush herb with high resistance of Pb and wide adaptability, was used in pot experiments to study the effects of exogenous nitrate N (NO−3−N) on the absorption and transportation of Pb and plant growth under different Pb concentrations. Then, the mechanism of NO−3−N affecting Pb and nutrient uptake and transport was explored. The concentration of Pb in the experiment ranged from 0 to 1600 mg/kg, and the added concentration of NO−3−N was 0.0-0.3 g/kg. The results showed that I. lactea was highly tolerant to Pb, and the shoot fraction was more sensitive to varied Pb concentrations in the soil than the root fraction. This protective function became more pronounced under the condition of raised Pb concentration in the soil. When the concentration of Pb in the soil reached 800 mg/kg, the highest Pb content of I. lactea was found under the condition of 0.1 g/kg of NO−3−N addition. When Pb concentration in the soil increased to 1600 mg/kg, the increase in NO−3−N addition promoted Pb uptake by the root. To ensure the well growth of I. lactea and the effect of remediation of Pb-contaminated soil, the recommended concentration of NO−3−N in the soil is 0.1 g/kg. This result provides a theoretical basis for exogenous N regulation of phytoremediation of Pb-contaminated soil.

Key words： Iris lactea      nitrate nitrogen      plant nutrient      lead accumulation      absorb      transport     
Received: 31 May 2022      Published: 28 February 2023
Corresponding Authors: *LI Pinfang (E-mail: pfli@cau.edu.cn)
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SUN Mengjie, GUO Shiwen, XIONG Chunlian, LI Pinfang. Exogenous addition of nitrate nitrogen regulates the uptake and translocation of lead (Pb) by Iris lacteal Pall. var. chinensis (Fisch.) Koidz.. Journal of Arid Land, 2023, 15(2): 218-230.

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http://jal.xjegi.com/10.1007/s40333-023-0004-9     OR     http://jal.xjegi.com/Y2023/V15/I2/218

pH EC
(μS/cm)		 CEC
(cmol/kg)		 SOM
(g/kg)		 Total N
(g/kg)		 Available P
(mg/kg)		 Available K
(mg/kg)		 Total Pb
(mg/kg)
8.22 198.00 13.81 12.67 0.59 13.06 146.32 17.56
Table 1 Physical-chemical properties of the soil
Treatment Pb (mg/kg) NO−3−N (g/kg)
CK (control) 0 0.0
Pb0N1 0 0.1
Pb0N2 0 0.2
Pb0N3 0 0.3
Pb1N0 800 0.0
Pb1N1 800 0.1
Pb1N2 800 0.2
Pb1N3 800 0.3
Pb2N0 1600 0.0
Pb2N1 1600 0.1
Pb2N2 1600 0.2
Pb2N3 1600 0.3
Table 2 Experimental treatment
Step Extraction form Chemical reagents and extraction condition
1 Acid soluble Taking 1 g of air dried soil into a 100-mL centrifuge tube, adding 40 mL of 0.11 mol/L HOAc, shaking at 22°C (±5°C) for 16 h, centrifuging for 20 min at 3000 r/min, and then transferring the supernatant to a polyethylene bottle.
2 Reducible Adding 40 mL of 0.5 mol/L NH2OH•HCl (pH 1.5) solution containing 25 mL HNO3 to the solid residue in step 1, shaking at 22°C (±5°C) for 16 h, centrifuging for 20 min at 3000 r/min, and then transferring the supernatant to a polyethylene bottle.
3 Oxidizable Adding 10 mL of 8.8 mol/L H2O2 (pH 2-3) to the solid residue in step 2, keeping at room temperature for 1 h, and water bathing at 85°C (±2°C) for 1 h. When heated to a volume less than 3 mL, adding another 10 mL of H2O2, then water bathing at 85°C (±2°C) for 1 h. When heating to a volume less than 1 mL, adding 50 mL of 1 mol/L NH4OAc (pH 2), centrifuging for 20 min at 3000 r/min, and then transferring the supernatant to a polyethylene bottle.
4 Residual Differential subtraction method.
Table 3 BCR (Bureau of Reference, European Community) three-step sequential extraction procedure
Fig. 1 Biomass of Iris lactea in lead (Pb)-contaminated soil with exogenous nitrate nitrogen (NO−3−N). CK, 0.0 g/kg Pb and N; N0, 0.0 g/kg; N1, 0.1 g/kg, N2, 0.2 g/kg; N3, 0.3 g/kg; Pb0, 0 mg/kg; Pb1, 800 mg/kg; Pb2, 1600 mg/kg. (a), Pb0 treatment; (b), Pb1 treatment; (c), Pb2 treatment. The detailed treatment of Pb and N is shown in Table 2. Different lowercase letters within the same Pb treatment indicate significant differences among different N treatments in root or shoot at P<0.05 level according to Tukey's test. Bars are standard errors.
Fig. 2 pH value varied in Pb-contaminated soil with exogenous nitrate nitrogen (NO−3−N). CK, 0.0 g/kg Pb and N; N0, 0.0 mg/kg; N1, 0.1 g/kg, N2, 0.2 g/kg; N3, 0.3 g/kg; Pb0, 0 mg/kg; Pb1, 800 mg/kg; Pb2, 1600 mg/kg. The detailed treatment is shown in Table 2. Different lowercase letters within the same Pb treatment denote significant differences among different N treatments at P<0.05 level according to Tukey's test. Bars are standard errors.
Fig. 3 Transformation of lead (Pb) and proportions in different forms with exogenous nitrate nitrogen (NO−3−N). N0, 0.0 mg/kg; N1, 0.1 g/kg, N2, 0.2 g/kg; N3, 0.3 g/kg; Pb1, 800 mg/kg; Pb2, 1600 mg/kg. (a), Pb1 treatment; (b), Pb2 treatment. The detailed treatment is shown in Table 2. Different lowercase letters within the same Pb treatment denote significant differences among different forms of Pb at P<0.05 level according to Tukey's test. Bars are standard errors.
Fig. 4 Lead (Pb) content of Iris lactea in Pb-contaminated soil with exogenous nitrate nitrogen (NO−3−N). N0, 0.0 mg/kg; N1, 0.1 g/kg, N2, 0.2 g/kg; N3, 0.3 g/kg; Pb1, 800 mg/kg; Pb2, 1600 mg/kg. (a), Pb1 treatment; (b), Pb2 treatment. The detailed treatment is shown in Table 2. Different lowercase letters within the same Pb treatment denote significant differences among different N treatments at P<0.05 level according to Tukey's test. Bars are standard errors.
Fig. 5 Lead (Pb) accumulation content of Iris lactea in Pb-contaminated soil with exogenous nitrate nitrogen (NO−3−N). N0, 0.0 mg/kg; N1, 0.1 g/kg, N2, 0.2 g/kg; N3, 0.3 g/kg; Pb1, 800 mg/kg; Pb2, 1600 mg/kg. (a), Pb1 treatment; (b) Pb2 treatment. The detailed treatment is shown in Table 2. Different lowercase letters within the same Pb treatment denote significant differences among different N treatments at P<0.05 level according to Tukey's test. Bars are standard errors.
Fig. 6 Correlations of Iris lactea growth with absorption and transport of Pb. *, P<0.05 level.
NO−3−N treatment Pb0 Pb1 Pb2
N0 0.4988 0.5093 0.5202
N1 0.5221 0.4553 0.5300
N2 0.5485 0.4874 0.5584
N3 0.5889 0.4887 0.5672
Table S1 Effect of NO−3−N on root/shoot ratio of Iris lactea in Pb-contaminated soil
Nutrient element Nitrate nitrogen treatment Content in shoot (g/kg) Content in root (g/kg)
Pb0 Pb1 Pb2 Pb0 Pb1 Pb2
N N0 20.82±1.52c 20.49±1.36b 15.60±1.34b 9.57±1.02a 10.46±0.33b 8.60±1.33b
N1 23.89±0.89a 21.12±0.90b 18.15±1.42a 9.55±1.14 a 10.69±0.31b 9.55±1.89a
N2 22.77±0.33ab 24.61±0.75a 17.52±0.57ab 10.55±1.02a 13.70±0.20 a 9.96±1.00ab
N3 22.12±1.47ab 16.36±0.91c 17.12±0.01ab 11.24±0.51a 13.54±3.06 c 10.17±0.70ab
P N0 6.19±0.45a 4.65±0.16b 10.71±3.62ab 10.28±1.16ab 7.53±0.47a 8.58±2.23a
N1 6.27±0.29a 6.72±0.69b 8.79±0.26ab 17.32±7.66a 8.29±0.91a 6.37±0.39a
N2 6.19±0.07a 6.81±1.02b 13.47±3.43a 2.82±0.38b 8.69±0.68a 6.73±0.48a
N3 6.46±0.06a 12.77±1.70a 4.47±0.04b 7.56±0.15b 8.64±0.54a 8.38±0.52a
K N0 31.33±0.18a 34.97±1.07a 32.94±0.59a 10.58±0.13b 12.70±0.76ab 12.48±1.37b
N1 31.85±0.79a 30.38±0.90b 31.79±1.56a 15.47±1.99a 11.51±0.64b 13.43±1.41ab
N2 28.85±0.53b 28.97±0.29c 28.42±0.28b 14.17±1.66a 11.20±0.99b 15.40±1.14a
N3 28.46±1.06b 28.61±0.40c 24.88±1.06c 13.00±0.16ab 13.54±0.86a 12.46±1.18b
Table S2 Effect of NO−3−N on N, P, and K uptake and transportation of Iris lactea in Pb-contaminated soil
Nutrient element Nitrate nitrogen treatment Accumulation in shoot Accumulation in root
(mg/plant) (mg/plant)
Pb0 Pb1 Pb2 Pb0 Pb1 Pb2
N N0 1.50±0.06ab 1.74±0.10a 1.16±0.12a 0.42±0.05a 0.46±0.05a 0.33±0.08a
N1 1.94±0.17a 1.84±0.12a 1.15±0.15 a 0.40±0.05ab 0.45±0.10b 0.32±0.10a
N2 1.40±0.03bc 1.88±0.03a 0.94±0.12ab 0.36±0.04b 0.48±0.01a 0.30±0.04a
N3 1.24±0.10c 1.15±0.04b 0.83±0.02b 0.35±0.03b 0.44±0.11b 0.28±0.07a
P N0 0.52±0.08a 0.41±0.02c 0.80±0.33ab 0.37±0.04ab 0.33±0.03 a 0.33±0.07a
N1 0.52±0.01a 0.60±0.01b 0.52±0.10ab 0.74±0.41a 0.34±0.06a 0.21±0.07ab
N2 0.38±0.01b 0.49±0.02c 0.76±0.29a 0.09±0.01b 0.30±0.02a 0.19±0.03b
N3 0.36±0.03b 0.88±0.06a 0.22±0.00b 0.24±0.02b 0.30±0.05a 0.22±0.04ab
K N0 2.44±0.24a 2.98±0.30a 2.45±0.12 a 0.43±0.10b 0.57±0.10a 0.48±0.07 a
N1 2.58±0.24a 2.64±0.11a 2.01±0.37b 0.64±0.00 a 0.48±0.12a 0.45±0.10ab
N2 1.78±0.02b 2.12±0.16b 1.52±0.19c 0.49±0.10ab 0.40±0.05a 0.46±0.08ab
N3 1.52±0.08b 2.02±0.13b 1.10±0.13c 0.41±0.05b 0.48±0.09a 0.30±0.00b
Table S3 Effect of NO−3−N on N, P, and K accumulation of Iris lactea in Pb-contaminated soil
NO−3−N treatment N P K
Pb0 Pb1 Pb2 Pb0 Pb1 Pb2 Pb0 Pb1 Pb2
N0 2.18 1.96 1.81 0.60 0.62 1.25 2.96 2.75 2.64
N1 2.50 1.98 1.90 0.36 0.81 1.38 2.06 2.64 2.38
N2 2.16 1.80 1.76 2.20 0.78 2.00 2.05 2.59 1.85
N3 1.97 1.21 1.68 0.85 1.48 0.53 2.19 2.11 2.00
Table S4 Effect of NO−3−N on transfer coefficients of N, P, and K of Iris lactea in Pb-contaminated soil
NO−3−N treatment Pb treatment
Pb1 Pb2
N0 0.08 0.10
N1 0.06 0.08
N2 0.08 0.06
N3 0.08 0.05
Table S5 Effect of NO−3−N on transfer coefficients of Pb of Iris lactea in Pb-contaminated soil
Index Acid soluble state Reducible state Oxidizable state Residual state
Pb content in root 0.972** 0.946** 0.889** 0.897**
Pb content in shoot 0.900** 0.877** 0.859** 0.875**
Table S6 Correlation between Pb forms in soil and contents of Pb in shoot and root of Iris lactea
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