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凋落物生物炭施用量对翠芦莉污泥适应性及重金属吸收的影响

朱洁怡, 冯嘉仪, 盛晗, 彭维新, 吴道铭, 张学平, 金玲玲, 曾曙才

朱洁怡, 冯嘉仪, 盛晗, 等. 凋落物生物炭施用量对翠芦莉污泥适应性及重金属吸收的影响[J]. 华南农业大学学报, 2023, 44(4): 504-512. DOI: 10.7671/j.issn.1001-411X.202210006
引用本文: 朱洁怡, 冯嘉仪, 盛晗, 等. 凋落物生物炭施用量对翠芦莉污泥适应性及重金属吸收的影响[J]. 华南农业大学学报, 2023, 44(4): 504-512. DOI: 10.7671/j.issn.1001-411X.202210006
ZHU Jieyi, FENG Jiayi, SHENG Han, et al. Effects of litter biochar addition on sludge adaptability and heavy metal uptake of Ruellia simplex[J]. Journal of South China Agricultural University, 2023, 44(4): 504-512. DOI: 10.7671/j.issn.1001-411X.202210006
Citation: ZHU Jieyi, FENG Jiayi, SHENG Han, et al. Effects of litter biochar addition on sludge adaptability and heavy metal uptake of Ruellia simplex[J]. Journal of South China Agricultural University, 2023, 44(4): 504-512. DOI: 10.7671/j.issn.1001-411X.202210006

凋落物生物炭施用量对翠芦莉污泥适应性及重金属吸收的影响

基金项目: 国家自然科学基金(31971629)
详细信息
    作者简介:

    朱洁怡,硕士研究生,主要从事园林生态学研究,E-mail: yi953699379@qq.com

    通讯作者:

    金玲玲,副教授,硕士,主要从事应用数学研究,E-mail: jinlingling@scau.edu.cn

    曾曙才,教授,博士,主要从事森林生态学研究,E-mail: sczeng@scau.edu.cn

  • 中图分类号: S682.19;X703;X53

Effects of litter biochar addition on sludge adaptability and heavy metal uptake of Ruellia simplex

  • 摘要:
    目的 

    探究凋落物生物炭不同添加量对种植在污泥+土壤混合基质中的翠芦莉Ruellia simplex生长及重金属吸收累积的影响,以期为城市污泥和园林废弃物资源化利用提供参考依据。

    方法 

    通过盆栽试验,分析添加0、1.5%、3.0%和4.5%凋落物生物炭[占基质的质量分数(w),分别记为CK、F1.5、F3.0和F4.5]对翠芦莉生长、根系形态和生理以及养分和重金属吸收累积的影响。

    结果 

    与CK相比,F1.5处理显著增加翠芦莉株高、根系生物量、地上部生物量及全株生物量。植株生物量随w增加呈逐渐下降趋势,F4.5处理翠芦莉生物量显著低于CK,表现出“低促高抑”的特点。翠芦莉总根长、根表面积、平均直径、根体积在F1.5处理中达到最大,且均随w增加而逐渐减小。各处理中,F1.5处理根系可溶性蛋白和丙二醛(MDA)含量均最低,超氧化物歧化酶(SOD)活性最大;翠芦莉根系SOD活性随w增加呈下降趋势,但可溶性蛋白和MDA含量的变化趋势相反。与CK相比,各处理均不同程度提高了翠芦莉地上部及根部对N、P、K的吸收,不同程度降低了翠芦莉植株Cd、Cu含量,提高了Pb、Ni含量,N、P、K、Cd、Cu、Pb累积量均随w增加呈下降趋势;F1.5处理的翠芦莉植株N、P、K、Cd、Cu、Pb、Ni累积量均显著大于CK。

    结论 

    添加w为1.5%的凋落物生物炭可以显著促进翠芦莉生长和Pb、Cu、Cd、Ni的吸收累积,过量添加会抑制植物生长并影响其对基质中重金属的吸收效果,在实际应用中应合理控制生物炭的施用量。

    Abstract:
    Objective 

    To explore the effects of different addition amounts of litter biochar on growth, heavy metal absorption and accumulation of Ruellia simplex planted in the sludge + soil mixed matrix, and provide a reference for the resource utilization of municipal sludge and garden waste.

    Method 

    A pot experiment was conducted to analyze the effects of adding 0 (CK), 1.5% (F1.5), 3.0% (F3.0) and 4.5% (F4.5) of litter biochar on growth, root morphology, physiology, nutrient and heavy metal uptake and accumulation of Ruellia simplex.

    Result 

    Compared with CK, F1.5 significantly increased plant height, root biomass, shoot biomass and whole plant biomass. The plant biomass decreased gradually with the increase of biochar addition. The biomass of F4.5 was significantly lower than that of CK, showing the characteristic of “low promotion and high inhibition”. Total root length, root surface area, average diameter and root volume of Ruellia simplex reached the maximum in F1.5 treatment, and all of them gradually decreased with the increase of biochar addition. Among all treatments, the contents of soluble protein and malondialdehyde (MDA) in roots of F1.5 were the lowest, and the activity of superoxide dismutase (SOD) was the highest. The SOD activity of roots showed a downward trend with the increase of biochar addition, while the change trends of soluble protein and MDA contents were opposite. Compared with CK, all treatments increased the uptakes of N, P and K of R. simplex shoots and roots to different degrees, reduced the contents of Cd and Cu in R. simplex plant to different degrees, and increased the contents of Pb and Ni. The accumulative amounts of N, P, K, Cd, Cu, and Pb in R. simplex plant showed a downward trend with the increase of biochar addition, and the accumulative amounts of N, P, K, Cd, Cu, Pb and Ni of F1.5 were significantly higher than those of CK.

    Conclusion 

    The addition of 1.5% litter biochar significantly promoted R. simplex growth, absorption and accumulation of Pb, Cu, Cd and Ni, but excessive addition would inhibit plant growth and affect the repair effect of substrate. Therefore, the applied amount of biochar should be controlled reasonably in the practical application process.

  • 图  1   凋落物生物炭添加量对翠芦莉根系形态的影响

    各图中柱子上方不同小写字母表示处理间差异显著(P<0.05,Duncan’s 法)

    Figure  1.   Effect of litter biochar addition on the morphology of Ruellia simplex roots

    Different lowercase letters on bars of each figure indicated significant differences among treatments (P<0.05, Duncan’s test)

    图  2   凋落物生物炭添加量对翠芦莉根系生理的影响

    各图中柱子上方不同小写字母表示处理间差异显著(P<0.05,Duncan’s 法)

    Figure  2.   Effect of litter biochar addition on the physiology of Ruellia simplex roots

    Different lowercase letters on bars of each figure indicated significant differences among treatments (P<0.05, Duncan’s test)

    图  3   凋落物生物炭添加量对翠芦莉养分含量的影响

    各图中相同植物部位柱子上方不同小写字母表示处理间差异显著(P<0.05,Duncan’s 法)

    Figure  3.   Effect of litter biochar addition on the nutrient content of Ruellia simplex

    Different lowercase letters on bars of the same plant part in each figure indicated significant differences among treatments (P<0.05, Duncan’s test)

    图  4   凋落物生物炭添加量对翠芦莉单株养分积累量的影响

    各图中相同植物部位柱子上方不同小写字母表示处理间差异显著(P<0.05,Duncan’s 法)

    Figure  4.   Effect of litter biochar addition on the nutrient accumulation per plant of Ruellia simplex

    Different lowercase letters on bars of the same plant part in each figure indicated significant differences among treatments (P<0.05, Duncan’s test)

    表  1   供试基质的基本性质

    Table  1   Basic properties of experimental materials

    材料
    Meterial
    pHw/(g·kg−1)w/(mg·kg−1)
    有机质
    Organic matter
    全氮
    Total N
    全磷
    Total P
    全钾
    Total K
    碱解氮
    Available N
    速效磷
    Available P
    速效钾
    Available K
    CuPbCdNi
    土壤 Soil 5.77 15.41 0.70 0.38 2.71 26.83 15.27 65.23 17.31 29.56 0.18 10.10
    污泥
    Sewage sludge
    7.52 96.54 7.35 4.81 6.43 428.50 611.08 413.27 423.66 48.51 19.88 47.96
    下载: 导出CSV

    表  2   凋落物生物炭添加量对翠芦莉生长的影响1)

    Table  2   Effect of litter biochar application on the growth of Ruellia simplex

    处理
    Treatment
    株高/cm
    Plant height
    生物量/g Biomass
    根部
    Root
    地上部
    Above ground
    全株
    Whole plant
    CK106.67±1.86b6.97±0.04b31.22±1.39b38.19±1.38b
    F1.5124.00±4.51a16.45±0.90a50.72±2.35a67.17±3.25a
    F3.0104.67±2.33b8.16±0.24b29.80±1.99b37.96±2.11b
    F4.598.00±3.79b5.11±0.10c20.73±0.64c25.84±0.72c
     1)表中数据为平均值±标准误,同列数据后不同小写字母表示处理间差异显著(n=3,P<0.05,Duncan’s法)
     1)The data were mean±standard error, and the different lowercase letters after data of the same column indicated significant differences among treatments (n=3, P<0.05,Duncan’s test)
    下载: 导出CSV

    表  3   凋落物生物炭添加量对翠芦莉植株不同部位重金属含量的影响1)

    Table  3   Effect of litter biochar addition on heavy metal content in different organ of Ruellia simplex w/(mg·kg−1)

    植株部位 Plant part处理 TreatmentCdCuPbNi
    根部 RootCK7.21±0.34a56.66±2.04a2.46±0.44ab1.58±0.05b
    F1.54.75±0.42b21.71±0.78d1.49±0.02b1.66±0.08b
    F3.03.58±0.77b42.17±2.31b2.70±0.36a3.95±1.08a
    F4.53.48±0.83b30.27±0.83c3.54±0.29a5.57±0.49a
    地上部 ShootCK0.62±0.13a34.18±1.01a0.60±0.21b1.04±0.13c
    F1.50.64±0.04a25.33±0.03b2.36±0.29a6.88±0.25b
    F3.00.51±0.05a13.78±0.66c1.86±0.08a4.37±0.48b
    F4.50.66±0.09a14.62±0.95c1.78±0.14a18.00±1.85a
    全株 Total plantCK1.83±0.20a38.26±0.78a0.95±0.17b1.14±0.10c
    F1.51.65±0.10ab24.44±0.22b2.65±0.62a5.61±0.18b
    F3.01.16±0.18b19.94±1.27c2.04±0.05a4.25±0.48b
    F4.51.22±0.24ab17.72±0.59c2.13±0.14a15.54±1.45a
     1)表中数据为平均值±标准误,相同部位同列数据后不同小写字母表示处理间差异显著(n=3,P<0.05,Duncan’s法)
     1)The data were mean ± standard error, and different lowercase letters after data of the same plant part on the same column indicated significant differences among treatments (n=3, P<0.05, Duncan’s test)
    下载: 导出CSV

    表  4   凋落物生物炭添加量对翠芦莉单株不同部位重金属积累量的影响1)

    Table  4   Effect of litter biochar addition on heavy metal accumulation of different organ per plant of Ruellia simplex μg

    植株部位 Plant part处理 TreatmentCdCuPbNi
    根部CK50.19±2.34b394.90±14.08a17.17±3.17a11.02±0.37b
    RootF1.577.42±3.57a356.59±19.31ab24.46±1.24a27.27±2.24ab
    F3.029.18±6.22c343.72±17.47b21.85±2.22a32.46±9.53a
    F4.517.82±4.35c154.64±1.50c18.17±1.82a28.57±2.97a
    地上部CK19.11±3.19b1064.96±26.15b19.39±7.71c32.84±5.42c
    ShootF1.532.61±2.36a1284.56±58.40a118.66±12.16a348.21±9.23a
    F3.015.43±2.06b407.97±7.45c55.54±6.04b130.48±18.18b
    F4.513.60±1.61b304.05±27.27c37.07±3.77bc373.33±41.08a
    全株CK69.36±5.50b1459.86±39.96b36.56±7.61c43.86±5.05c
    Total plantF1.5110.03±1.22a1641.16±75.46a178.24±44.55a375.48±9.89a
    F3.044.61±8.20c751.69±10.13c77.39±5.11b162.94±26.08b
    F4.531.42±5.76c458.69±26.41d55.24±5.13bc401.90±40.26a
     1) 表中数据为平均值±标准误,相同部位同列数据后不同小写字母表示处理间差异显著(n=3,P<0.05,Duncan’s法)
     1) The data were mean±standard error, and different lowercase letters after data of the same plant part on the same column indicated significant differences among treatments (n=3, P<0.05, Duncan’s test)
    下载: 导出CSV
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出版历程
  • 收稿日期:  2022-10-07
  • 网络出版日期:  2023-09-03
  • 发布日期:  2023-03-30
  • 刊出日期:  2023-07-09

目录

    Corresponding author: ZENG Shucai, sczeng@scau.edu.cn

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