欢迎访问作物学报，今天是
作物学报

作物学报 ›› 2024, Vol. 50 ›› Issue (10): 2538-2549.doi: 10.3724/SP.J.1006.2024.44046

• 耕作栽培·生理生化 • 上一篇    下一篇

镉胁迫下复合菌剂对大豆的光合修复及其固定化效果的探究

刘宏缘(), 岑锎, 刘怡琳, 楼雪怡, 张雅婷, 吴嘉睿, 谭驭宇, 祝嘉丞, 方芳, 刘鹏*()   

  1. 浙江师范大学生命科学学院 / 植物学实验室, 浙江金华 321004
  • 收稿日期:2024-03-13 接受日期:2024-06-20 出版日期:2024-10-12 网络出版日期:2024-07-08
  • 通讯作者: *刘鹏, E-mail: sky79@zjnu.cn
  • 作者简介:E-mail: 2398008965@qq.com
  • 基金资助:
    国家自然科学基金项目(32001224);国家自然科学基金项目(41702181);金华市科技计划公益项目(2022-4-049)

Photosynthetic repair of Glycine max (Linn.) Merr. by compound fungus agents and immobilization effect under cadmium stress

LIU Hong-Yuan(), CEN Kai, LIU Yi-Lin, LOU Xue-Yi, ZHANG Ya-Ting, WU Jia-Rui, TAN Yu-Yu, ZHU Jia-Cheng, FANG Fang, LIU Peng*()   

  1. College of Life Science, Zhejiang Normal University / Botany Laboratory, Jinhua 321004, Zhejiang, China
  • Received:2024-03-13 Accepted:2024-06-20 Published:2024-10-12 Published online:2024-07-08
  • Contact: *E-mail: sky79@zjnu.cn
  • Supported by:
    National Natural Science Foundation of China(32001224);National Natural Science Foundation of China(41702181);Project of Jinhua Science and Technology Program(2022-4-049)

RichHTML

9

PDF

340

摘要：

镉(cadmium, Cd)作为对大豆等粮食类作物毒害最大的重金属之一, 不仅会抑制植物生长发育, 还会损害其光合系统致使光合速率下降。目前对于镉修复技术的探讨多集中于施加植物激素、改变种植模式等方向, 微生物与植物互作的研究仍有待探索。本研究为探究复合白腐真菌(White rot fungi)对镉污染的修复效果和固定化技术的实际应用价值, 以4种白腐真菌和大豆作为供试材料, 制备固态菌剂并对大豆设置土培处理, 且模拟镉污染土壤的浓度为0、50、100 mg L-1, 对应每个浓度分别进行3种处理(CK组-不做处理、EG1组-加入游离菌株、EG2组-加入固态菌剂), 研究混菌发酵与固定化技术对菌株吸附效能的影响, 同时探明镉毒害、固定化菌球以及大豆植株三者间的关联性。结果表明: (1) 除黄孢原毛平革菌外, 其余3种菌株兼容性良好。(2) 当混菌菌株组别为凤尾:云芝等于1∶1时, 处理浓度为50 mg L-1的镉溶液时可达到87.33%的吸附率。(3) 为延长混合菌株的使用时效, 提高吸附效果, 以海藻酸钠(SA)质量浓度为10 g L-1、生物炭(BC)质量浓度为15 g L-1、加菌量为2%制得的PVA固定化小球, 在加入适量添加剂后96 h吸附率可达(95.12±1.68)%。(4) 将固定化混菌菌剂施加入模拟镉污染土壤后, 大豆的各项生长和光合指标受到的抑制作用均得到缓释, 其中Fo的最大降幅为42.5%, Fv/Fm最大增幅为17.2%。(5) 大豆的抗氧化系统在菌剂处理14 d时得到增强, CK组中SOD、POD、CAT 3种酶最高活性均得以提升, 分别为27.34%、12.41%、13.58%; 此外, Pro及MDA含量分别呈上升和下降趋势, 共同表现出植物抗性的提高。综上, 镉胁迫下植株的PSII光化学反应中心受到抑制, 混合菌株固定化与单个或游离状态的菌株相比吸附效率更高, 施加固态菌剂后可有效开启大豆的光保护机制, 产生渗透调节物质, 同时激活抗氧化系统, 保证了大豆体内稳定的氧化还原环境以应对镉胁迫。

关键词: 白腐真菌, 混菌发酵, 固定化技术, 镉污染土壤

Abstract:

Cadmium, a highly toxic heavy metal affecting food crops like soybean, not only inhibits plant growth and development but also damages the photosynthetic system, leading to reduced photosynthesis rates. Current cadmium remediation technologies primarily focus on the application of plant hormones and alteration of planting patterns, while the interaction between microorganisms and plants remains underexplored. This study aims to explore the remediation potential of compound white rot fungi in addressing cadmium pollution and the practical application value of immobilization technology. Four types of white rot fungi and Glycine max (Linn.) Merr. were used to prepare solid bacterial agents and set up a soil cultivation method for soybeans. We simulated cadmium-contaminated soil concentrations of 0, 50, and 100 mg L-1. Three treatments were conducted for each concentration: a control group (CK) with no treatment, an experimental group with free strains (EG1), and an experimental group with solid agents (EG2). We examined the effects of mixed fermentation and immobilization technology on the strains’ adsorption efficiency and established the correlation between cadmium toxicity, immobilized microspheres, and soybean plants. The results indicate that, except for Phanerochaete chrysosporium, the other three strains demonstrated good compatibility. A mixed group of bacterial strains containing Pleurotus sajor-caju and Coriolus versicolor in a 1:1 ratio achieved an adsorption rate of 87.33% in cadmium-contaminated solutions at a concentration of 50 mg L-1. To prolong the duration and improve the adsorption effect of the mixed strain, PVA mixed pellets with a sodium alginate (SA) concentration of 10 g L-1, biochar mass concentration of 15 g L-1, and bacterial content of 2% achieved a degradation rate of (95.12 ± 1.68)% within 96 hours after adding appropriate additives. Introducing immobilized mixed bacteria into simulated cadmium-contaminated soil inhibited the growth and photosynthetic indices of soybeans. The maximum decrease in Fo was 42.5%, and the maximum increase in Fv/Fm was 17.2%. After 14 days, the soybean antioxidant system was enhanced, with the highest activities of SOD, POD, and CAT being 27.34%, 12.41%, and 13.58%, respectively, in the CK group. Additionally, there was an increase in proline content and a decrease in malondialdehyde content, indicating enhanced plant resistance. In conclusion, cadmium stress suppresses the photochemical reaction center II in plants’ photosystems. The immobilization of mixed strains results in higher adsorption efficiency compared to single or free states. Applying a reliable bacterial agent enables soybeans to effectively trigger their light protection mechanism, produce osmoregulatory substances, and activate the antioxidant system, thus maintaining a stable redox environment and coping with cadmium stress.

Key words: white rot fungi, mixed fermentation, immobilization technology, cadmium-contaminated soil

图1

不同浓度Cd2+下4种白腐真菌降解率 误差线表示标准差。不同小写字母表示同一时间段内不同菌种间差异显著(P < 0.05)。"

表1

不同时间下白腐真菌混合菌株各组别对Cd2+的吸附效果"

分组Group 24 h 48 h 72 h 96 h
1/2 黄孢+1/2 云芝
1/2 P. chrysosporium + 1/2 C. versicolor		 69.60±0.12 d 71.20±0.76 e 72.63±0.22 d 73.54±0.33 f
1/2 黃孢+1/2 平菇
1/2 P. chrysosporium + 1/2 P. ostreatus		 65.03±0.44 e 65.62±0.57 f 72.88±0.11 d 73.36±0.45 f
1/2 黃孢+1/2 凤尾
1/2 P. chrysosporium + 1/2 P. sajor-caju		 75.29±0.86 c 77.91±0.54 c 78.48±0.95 c 79.75±0.18 d
1/2 云芝+1/2 黃孢
1/2 C. versicolor + 1/2 P. chrysosporium		 70.02±0.58 d 70.19±0.87 e 74.34±0.32 c 74.37±0.15 e
1/2 云芝+1/2 平菇
1/2 C. versicolor + 1/2 P. ostreatus		 84.31±0.71 a 84.20±0.94 a 84.91±0.87 a 85.13±0.67 b
1/2 云芝+1/2 凤尾
1/2 C. versicolor + 1/2 P. sajor-caju		 85.15±0.24 a 85.94±0.91 a 86.63±0.93 a 86.79±0.54 a
1/2 平菇+1/2 黃孢
1/2 P. ostreatus + 1/2 P. chrysosporium		 68.92±0.91 d 73.00±0.12 d 74.08±0.12 c 73.92±0.27 ef
1/2 平菇+1/2 云芝
1/2 P. ostreatus + 1/2 C. versicolor		 65.11±0.23 e 70.48±0.65 e 74.66±0.78 c 74.79±0.78 e
1/2 平菇+1/2 凤尾
1/2 P. ostreatus + 1/2 P. sajor-caju		 58.73±0.78 g 67.25±0.76 f 68.18±0.87 e 69.10±0.45 g
1/2 凤尾+1/2 黃孢
1/2 P. sajor-caju + 1/2 P. chrysosporium		 59.13±0.21 g 66.06±0.69 f 67.23±0.78 e 67.81±0.54 h
1/2 凤尾+1/2 云芝
1/2 P. sajor-caju + 1/2 C. versicolor		 75.88±0.87 c 76.00±0.86 c 80.23±0.21 b 81.27±0.67 c
1/2 凤尾+1/2 平菇
1/2 P. sajor-caju + 1/2 P. ostreatus		 78.51±0.97 b 82.39±0.24 b 84.28±0.67 a 84.58±0.45 b
1/3 黃孢+1/3 云芝+1/3 平菇
1/3 P. chrysosporium + 1/3 C. versicolor + 1/3 P. ostreatus		 73.51±0.95 c 75.29±0.81 c 80.17±0.43 b 81.91±0.78 c
1/3 黃孢+1/3 平菇+1/3 凤尾
1/3 P. chrysosporium + 1/3 P. ostreatus + 1/3 P. sajor-caju		 62.54±0.57 f 64.72±0.88 f 65.46±0.12 f 66.31±0.34 i
1/3 云芝+1/3 平菇+1/3 凤尾
1/3 C. versicolor + 1/3 P. ostreatus + 1/3 P. sajor-caju		 79.21±0.41 b 76.50±0.61 c 84.24±0.57 a 85.14±0.78 b

表2

固定化白腐真菌混菌的正交实验(33)因素水平"

试验号
Test number		 A B C 96 h Cd吸附率
96 h Cd adsorption rate (%)
SA质量浓度
SA mass concentration
(g L-1)		 BC质量浓度
BC mass concentration
(g L-1)		 加菌量
Amount of mixed fungi
(%)
1 1(5) 1(15) 1(1) 86.65±0.16 b
2 1 2(20) 2(2) 91.62±1.85 a
3 1 3(25) 3(3) 83.07±0.01 c
4 2(10) 1 2 93.88±0.74 a
5 2 2 3 92.56±2.07 c
6 2 3 1 90.59±0.21 b
7 3(15) 1 3 84.99±0.83 b
8 3 2 1 86.99±0.83 b
9 3 3 2 87.29±0.82 a

表3

其余制作配方及制作条件的选择"

项目
Item		 处理组
Processing group		 机械强度
Mechanical strength
(mN)		 Cd吸附率
Cd adsorption rate (%)
交联时间
Cross-linking time		 1 h 1531±47.49 e 86.45±1.59 c
4 h 1944±64.40 d 90.42±0.55 b
8 h 2024±44.92 cd 82.91±1.47 d
12 h 2103±85.02 c 75.55±1.62 f
24 h 2388±41.54 b 73.33±2.15 f
36 h 2767±63.98 a 69.56±0.99 g
保存方法
Method of saving		 冷冻保存
Cryopreservation		 2054±64.23 d 80.67±0.51 e
0.2 mol L-1 NaH2PO4的饱和硼酸溶液
0.2 mol L-1 NaH2PO4 of a saturated boric acid solution		 2411±45.41 b 83.54±1.03 d
湿体冷藏环境
Moisture cold storage environment		 2326±06.43 c 84.34±1.27 cd
5 mg L-1 Cd模拟废水中冷藏
5 mg L-1 Cd simulated wastewater		 2453±56.65 a 91.44±1.35 b
二氧化硅和
沸石添加情况
SiO2 and zeolite addition condition		 加入10 g二氧化硅, 未加入沸石
10 g of silica was added, and no modified zeolite was added		 2508±42.68 b 91.65±0.47 b
加入5 g沸石, 未加入二氧化硅
5 g of modified zeolite was added, without silica being added		 2487±26.32 bc 92.39±0.79 b
加入10 g二氧化硅, 5 g沸石
10 g of silica was added and 5 g of modified zeolite		 2523±12.54 b 95.12±1.68 a

图2

固定化混菌小球表观图和电镜扫描图"

表4

PVA固定化小球表观测定"

小球各指标
Small ball indicators		 载菌量
Loage
(cfu mL-1)		 真密度
True density
(g L-1)		 堆积密度
Accumulacking density (g L-1)		 含水倍率
Water content (%)		 含水率
Rate of water content (%)		 比表面积
Specific surface area (m2 g-1)
测定结果
Determination results		 (4.13±0.01)×106 1.231±0.014 0.734±0.001 55.20±2.21 1.147±0.04 318.69±4.27

图3

不同处理下镉对大豆株高和叶面积的影响 误差线表示标准差。不同小写字母表示同一生育期内处理间差异显著(P < 0.05)。CK: 不做处理; EG1: 加入游离菌株; EG2: 加入固态菌剂; Cd0: 0 mg L-1 Cd; Cd50: 50 mg L-1 Cd; Cd100: 100 mg L-1 Cd。"

图4

不同处理下镉对大豆各项荧光参数的影响 误差线表示标准差。不同小写字母表示同一胁迫时期内处理间差异显著(P < 0.05)。处理同图3。"

图5

不同处理下镉对大豆SOD、POD、CAT活性的影响 误差线表示标准差。不同小写字母表示同一胁迫时期内处理间差异显著(P < 0.05)。处理同图3。"

图6

不同镉处理下大豆Pro含量和MDA含量变化情况 误差线表示标准差。不同小写字母表示同一胁迫时期内处理间差异显著(P < 0.05)。处理同图3。"

[1] Shi W G, Zhang Y H, Chen S L, Polle A, Rennenberg H, Luo Z B. Physiological and molecular mechanisms of heavy metal accumulation in nonmycorrhizal versus mycorrhizal plants. Plant Cell Environ, 2019, 42: 1087-1103.
[2] 尚晓静, 张富美, 程伟, 苏莉, 侯瑞. 裂褶菌菌株G18对孔雀石绿染料的脱色优化. 菌物学报, 2020, 39: 1580-1592.
doi: 10.13346/j.mycosystema.200055
Shang X J, Zhang F M, Cheng W, Su L, Hou R. Decolorization optimization of malachite green dye by Schizomycete strain G18. J Microbiol, 2020, 39: 1580-1592 (in Chinese with English abstract).
[3] Sharma S, Pandey L M. Hydrophobic surface induced biosorption and microbial ex situ remediation of oil-contaminated sites. Ind Eng Chem Res, 2021, 60: 9378-9388.
[4] Takahashi M, Nakamura H. Toothpick method to evaluate soil antagonism against the white root rot fungus, Rosellinia necatrix. J Gen Plant Pathol, 2020, 86: 55-59.
doi: 10.1007/s10327-019-00887-1
[5] 杨珍, 戴传超, 王兴祥, 李孝刚. 作物土传真菌病害发生的根际微生物机制研究进展. 土壤学报, 2019, 56: 12-22.
Yang Z, Dai C C, Wang X X, Li X G. Advance in research on rhizosphere microbial mechanisms of crop soil-borne fungal diseases. Acta Pedol Sin, 2019, 56: 12-22 (in Chinese with English abstract).
[6] Ben Ayed A, Akrout I, Albert Q, Greff S, Simmler C, Armengaud J, Kielbasa M, Turbé-Doan A, Chaduli D, Navarro D, Bertrand E, Faulds C B, Chamkha M, Maalej A, Zouari-Mechichi H, Sciara G, Mechichi T, Record E. Biotransformation of the fluoroquinolone, levofloxacin, by the white-rot fungus Coriolopsis gallica. J Fungi, 2022, 8: 965.
[7] 许飘. 白腐真菌对重金属的吸附富集特性及其重金属耐受性和抗性机制研究. 湖南大学博士学位论文, 湖南长沙, 2016.
Xu P. Mechanism of Heavy Metal Tolerance and Resistance of White Rot Fungi. PhD Dissertation of Hunan University, Changsha, Hunan, China, 2016 (in Chinese with English abstract).
[8] Liang J, Gong S X, Sun Y H, Zhang J J, Zhang J F. Enhanced degradation of phenol by a novel biomaterial through the immobilization of bacteria on cationic straw. Water Sci Technol, 2021, 84: 3791-3798.
doi: 10.2166/wst.2021.498 pmid: 34928844
[9] 朱晓丽, 张婵娟, 张星, 寇志健, 王军强, 尚小清. 生物炭固定化硫酸盐还原菌对镉污染土壤的钝化修复. 环境科学学报, 2023, 43: 421-429.
Zhu X L, Zhang C J, Zhang X, Kou Z J, Wang J Q, Shang X Q. Passivation and remediation of cadmium-contaminated soil by biochar-immobilized sulfate-reducing bacteria. J Environ Sci, 2023, 43: 421-429 (in Chinese with English abstract).
[10] 吴正可, 刘国华, 李阳, 郑爱娟, 常文环, 陈志敏, 蔡辉益. 混菌固态发酵菜籽粕工艺优化. 中国农业科学, 2019, 52: 4603-4612.
doi: 10.3864/j.issn.0578-1752.2019.24.014
Wu Z K, Liu G H, Li Y, Zheng A J, Chang W Q, Chen Z M, Cai H Y. Optimization of solid fermentation of rapeseed meal with mixed bacteria. Sci Agric Sin, 2019, 52: 4603-4612 (in Chinese with English abstract).
[11] Duan-Mu H Z, Wang Y, Bai X, Cheng S F, Deyholos M K, Wong G K S, Li D, Zhu D, Li R, Yu Y, Cao L, Chen C, Zhu Y M. Wild soybean roots depend on specific transcription factors and oxidation reduction related genesin response to alkaline stress. Funct Integr Genomics, 2015, 15: 651-660.
[12] Ji H S, Bang S G, Ahn M-A, Kim G, Kim E, Eom S H, Hyun T K. Molecular cloning and functional characterization of heat stress-responsive superoxide dismutases in garlic (Allium sativum L.). Antioxidants (Bsael), 2021, 10: 815.
[13] Tulsiyan K D, Mahalik A, Dandekar B R, Mondal J, Biswal H S. Enhancement of peroxidase activity in magnetic ionic liquids. ACS Sustainable Chem Eng, 2023, 23: 8487-8494.
[14] Ren H, Li J, Liu P, Ren X Y, Song T, Gao G S, Li D W, Liu S T. Cloning of catalase gene and antioxidant genes in Scophthalmus maximus response to metalloprotease of Vibrio anguillarum stress. J Oceanol Limnol, 2022, 40: 322-335.
[15] Gao Q, Xu L, Li X, Yang W W, Mi Q L, Lu L M, Liu X, Wang K, Lu Y F, Chen Z Y, Li X M, Li L Q. Proteome and physiological analyses reveal tobacco (Nicotiana tabacum) peroxidase 7 (POD 7) functions in responses to copper stress. Transgenic Res, 2022, 31: 431-444.
doi: 10.1007/s11248-022-00310-0 pmid: 35793054
[16] Lee M R, Kim C S, Park T, Choi Y S, Lee K H. Optimization of the ninhydrin reaction and development of a multiwell plate- based high-throughput proline detection assay. Anal Biochem, 2018, 556: 57-62.
[17] Stenholm A, Hedeland M, Pettersson C E. Neomycin removal using the white rot fungus Trametes versicolor. J Environ Sci Health A Tox Hazard Subst Environ Eng, 2022, 57: 436-447.
[18] 黄仕元, 李胜, 王振宇, 林森焕, 邓简. 固定化白腐真菌对复合污染废水的处理. 应用化工, 2022, 51: 103-106.
Huang S Y, Li S, Wang Z Y, Lin S H, Deng J. Treatment of compound-contaminated wastewater by immobilized white-rot fungi. Appl Chem Ind, 2022, 51: 103-106 (in Chinese with English abstract).
[19] Liu W T, Li J T, Zheng Z Q, Li F Y. Microbial immobilization technology for remediation of petroleum hydrocarbon contaminated soil. J Eng Technol, 2021, 21: 339-347.
[20] 渠心静, 陈铭, 廖皎, 张宸辉, 陈隆升, 袁军. 磷缓解油茶铝胁迫的叶片生理响应. 中南林业科技大学学报, 2021, 41(7): 62-71.
Qu X J, Chen M, Liao J, Zhang C H, Chen L S, Yuan J. Phosphorus alleviates leaf physiological responses of Camellia oleifera aluminum stress. J Central South Univ For Technol, 2021, 41(7): 62-71 (in Chinese with English abstract).
[21] 张星雨, 叶志彪, 张余洋. 植物响应镉胁迫的生理与分子机制研究进展. 植物生理学报, 2021, 57: 1437-1450.
Zhang X Y, Ye Z B, Zhang Y Y. Progress on the physiological and molecular mechanisms of plant response to cadmium stress. Plant Physiol J, 2021, 57: 1437-1450 (in Chinese with English abstract).
[22] 谢德志, 魏子璐, 朱峻熠, 杜莹, 金水虎, 岳春雷. 水禾对镉胁迫的生理响应. 浙江农林大学学报, 2020, 37: 683-692.
Xie D Z, Wei Z L, Zhu J Y, Du Y, Jin S H, Yue C L. Physiological response of water weed to cadmium stress. J Zhejiang A&F Univ, 2020, 37: 683-692 (in Chinese with English abstract).
[23] Cao D Q, Wang X, Wang Q H, Fang X M, Jin J Y, Hao X D, Iritani E, Katagiri N. Removal of heavy metal ions by ultrafiltration with recovery of extracellular polymer substances from excess sludge. J Membr Sci, 2020, 606: 118103.
[24] Zuchowski J, Pecio L, Jaszek M, Stochmal A. Solid-state fermentation of rapeseed meal with the white-rot fungi Trametes versicolor and Pleurotus ostreatus. Appl Biochem Biotechnol, 2013, 171: 2075-2081.
[25] Tomm H A, Ucciferri L, Ross A C. Advances in microbial culturing conditions to activate silent biosynthetic gene clusters for novel metabolite production. J Ind Microbiol Biotechnol, 2019, 46: 1381-1400.
[26] Opong-Danouanh E, Blime M Srapato S, Mangoni A, Tasdemir D. Induction of isochromanones by co-cultivation of the marine fungus Cosmospora sp. and the phytopathogen Magnaporthe oryzae. Int J Mol Sci, 2022, 23: 782.
[27] Birhanli E, Erdogan S, Yesilada O, Onal Y. Laccase production by newly isolated white rot fungus Funalia trogii: effect of immobilization matrix on laccase production. Biochem Eng J, 2013, 71: 134-139.
[28] 陈金媛, 沈洋洋, 李烜桢. 白腐真菌Ganoderma sinense对镉和蒽的去除能力. 环境工程学报, 2016, 10: 787-791.
Chen J Y, Shen Y Y, Li X Z. Removal capacity of cadmium and anthracene by the white rot fungus Ganoderma sinense. Chin J Environ Eng, 2016, 10: 787-791 (in Chinese with English abstract).
[29] 余泽海, 胡云霜, 张晏菘, 邱慧敏, 李志霞, 林宏飞. 聚乙烯醇/海藻酸钠/水性聚氨酯复合载体制备及固定化硝化菌降解氨氮废水的研究. 水处理技术, 2022, 48(11): 94-97.
Yu Z H, Hu Y S, Zhang Y S, Qiu H M, Li Z X, Lin H F. Study on preparation of polyvinyl alcohol / sodium alginate / waterborne polyurethane composite carrier and degradation of ammonia nitrogen wastewater by immobilized nitrifiers. Technol Water Treatment, 2022, 48(11): 94-97 (in Chinese with English abstract).
[30] 毛轩雯, 李逸雯, 姜小羽, 王颜和, 吴楠, 蒋云杰, 刘粤, 游薇, 王婷舒, 肖茵翠, 方芳, 刘鹏. 混合白腐真菌的固定化及其在治理铅污染废水中的应用. 微生物学报, 2024, 64: 283-302.
Mao X W, Li Y W, Jiang X Y, Wang Y H, Wu N, Jiang Y J, Liu Y, You W, Wang T S, Xiao Y C, Fang F, Liu P. Immobilization of mixed white-rot fungi and its application in the treatment of lead-contaminated wastewater. Acta Microbiol Sin, 2024, 64: 283-302 (in Chinese with English abstract).
[31] 张靖雯, 肖盈, 陈佳志. 复合固定化菌株L5降解高效氯氰菊酯的特性研究. 广东化工, 2021, 48(22): 116-118.
Zhang J W, Xiao Y, Chen J Z. Characterization of efficient cypermethrin degradation in compound immobilized strain L5. Guangdong Chem Ind, 2021, 48(22): 116-118 (in Chinese with English abstract).
[32] Jiang Y, Yu G B, Zhou Y, Liu Y Y, Feng Y H, Li J C. Effects of sodium alginate on microstructural and properties of bacterial cellulose nanocrystal stabilized emulsions. Colloid Surf A Physicochem Eng Aspects, 2020, 607: 125474.
[33] 戴海根, 吴宏伟, 吴尚卫, 崔莹, 杨冰, 第乙林, 赵春旭. 干旱胁迫对鹰嘴紫云英种子萌发及幼苗叶绿素荧光特性的影响. 草原与草坪, 2022, 42(5): 95-105.
Dai H G, Wu H W, Wu S W, Cui Y, Yang B, Di Y L, Zhao C X. Effect of drought stress on seed germination and chlorophyll fluorescence characteristics of young seedlings. Grassl & Turf, 2022, 42(5): 95-105 (in Chinese with English abstract).
[34] Cao Y N, Tan Q, Zhang F, Ma C X, Xiao J, Chen G C. Phytoremediation potential evaluation of multiple Salix clones for heavy metals (Cd, Zn and Pb) in flooded soils. Sci Total Environ, 2022, 813: 152482.
[35] Cui Y Y, Zhang Q Y, Liu P, Zhang Y C. Effects of polyethylene and heavy metal cadmium on the growth and development of Brassica chinensis var. chinensis. Water Air Soil Pollut, 2022, 233: 426.
[36] Pan T W, Dong Q Y, Cai Y X, Cai K Z. Silicon-mediated regulation of cadmium transport and activation of antioxidant defense system enhances Pennisetum glaucum resistance to cadmium stress. Plant Physiol Biochem, 2023, 195: 206-213.
[37] 张琼, 陆銮眉, 戴清霞, 朱丽霞, 郑海燕. 镉胁迫对水仙根系抗氧化系统的影响. 福建农业学报, 2016, 31: 591-595.
Zhang Q, Lu L M, Dai Q X, Zhu L X, Zheng H Y. Effect of cadmium stress on the antioxidant system of Narcissus roots. Fujian J Agric Sci, 2016, 31: 591-595 (in Chinese with English abstract).
[38] Georgieva K, Mihailova G, Fernández-Marín B, Bertazza G, Govoni A, Arzac M I, Laza J M, Vilas J L, García-Plazaola J I, Rapparini F. Protective strategies of Haberlea rhodopensis for acquisition of freezing tolerance: interaction between dehydration and low temperature. Int J Mol Sci, 2022, 23: 15050.
No related articles found!
Viewed
Full text


Abstract

Cited
  Shared   
  Discussed   
[1] 杜永;王艳;王学红;孙乃立;杨建昌. 黄淮地区不同粳稻品种株型、产量与品质的比较分析[J]. 作物学报, 2007, 33(07): 1079 -1085 .
[2] 贺立源;徐尚忠;李建生. 玉米自交系苗期耐酸的生物学和营养学特性[J]. 作物学报, 2000, 26(02): 205 -209 .
[3] 宋开山;张柏;李方;段洪涛;王宗明. 玉米叶绿素含量的高光谱估算模型研究[J]. 作物学报, 2005, 31(08): 1095 -1097 .
[4] 潘庆民;于振文;王月福;田奇卓. 公顷产9000 kg小麦氮素吸收分配的研究[J]. 作物学报, 1999, 25(05): 541 -547 .
[5] 王爱云;田煦. 螯合稀土——硼在苎麻上的应用研究[J]. 作物学报, 1997, 23(05): 597 -602 .
[6] 张磊;张宝石;周荣华;高丽峰;赵光耀;宋彦霞;贾继增. 小麦细胞分裂素氧化/脱氢酶基因(TaCKX2)的克隆及其遗传作图[J]. 作物学报, 2007, 33(09): 1419 -1425 .
[7] 庄克章;郭新宇;王纪华;王空军;吴正锋;刘鹏;董树亭;张吉旺. 高油115籽粒灌浆期光能利用效率[J]. 作物学报, 2007, 33(02): 230 -235 .
[8] 程颖;宋伟;刘志勇;解超杰;倪中福;彭惠茹;聂秀玲;杨作民;孙其信. 小麦品种贵农21抗条锈病基因的SSR标记[J]. 作物学报, 2006, 32(12): 1867 -1872 .
[9] 杨典洱;张承亮;陈翠霞;王岳光; 王斌;张超良;陈绍江. 禾谷镰刀菌引起玉米青枯病的抗性基因遗传分析[J]. 作物学报, 2002, 28(03): 389 -393 .
[10] 郑克武;邹江石;吕川根. N肥和栽插密度对杂交稻“两优培九”产量及N素吸收利用的影响[J]. 作物学报, 2006, 32(06): 885 -893 .
京ICP备15008789号-2