Ecology and Environment ›› 2021, Vol. 30 ›› Issue (8): 1695-1705.DOI: 10.16258/j.cnki.1674-5906.2021.08.016
• Research Articles • Previous Articles Next Articles
PAN Guoying1,2(), LIN Fenglian1,2, YUAN Feng1,2, LUO Qian1,2, GAO Qianqian1,2, LI Jian1,2, WU Chengzhen3, CHEN Can1,2,*(
)
Received:
2021-03-07
Online:
2021-08-18
Published:
2021-11-03
Contact:
CHEN Can
潘国营1,2(), 林凤莲1,2, 袁锋1,2, 罗倩1,2, 高倩倩1,2, 李键1,2, 吴承祯3, 陈灿1,2,*(
)
通讯作者:
陈灿
作者简介:
潘国营(1996年生),女,硕士研究生,主要研究方向城市林业。E-mail: panguoying1119@163.com
基金资助:
CLC Number:
PAN Guoying, LIN Fenglian, YUAN Feng, LUO Qian, GAO Qianqian, LI Jian, WU Chengzhen, CHEN Can. Study on Purification Ability of 10 Highly Efficient Strains in Artificial Wastewater[J]. Ecology and Environment, 2021, 30(8): 1695-1705.
潘国营, 林凤莲, 袁锋, 罗倩, 高倩倩, 李键, 吴承祯, 陈灿. 10株高效菌株对人工污水净化能力研究[J]. 生态环境学报, 2021, 30(8): 1695-1705.
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URL: https://www.jeesci.com/EN/10.16258/j.cnki.1674-5906.2021.08.016
湿地类型 Wetland type | w(有机质 Organic matter)/ (g∙kg-1) | w(全氮 TN)/ (g∙kg-1) | w(全磷 TP)/ (g∙kg-1) | w(全钾 TK)/ (g∙kg-1) | w(水解氮 Hydrolyzed Nitrogen)/ (mg∙kg-1) | w(速效磷 Available Phosphorus)/ (mg∙kg-1) | w(速效钾 Available potassium)/ (mg∙kg-1) |
---|---|---|---|---|---|---|---|
再力花 Thalia dealbata Link | 71.32 | 4.15 | 5.63 | 0.52 | 125.32 | 377.02 | 76.80 |
香根草 Vetiveria zizanioides L. | 74.87 | 2.93 | 6.02 | 0.75 | 260.55 | 412.79 | 91.48 |
花叶芦荻 A. donax var.versicolor | 67.77 | 4.06 | 5.10 | 0.39 | 115.05 | 395.00 | 62.24 |
Table 1 Soil fertility of wetland system
湿地类型 Wetland type | w(有机质 Organic matter)/ (g∙kg-1) | w(全氮 TN)/ (g∙kg-1) | w(全磷 TP)/ (g∙kg-1) | w(全钾 TK)/ (g∙kg-1) | w(水解氮 Hydrolyzed Nitrogen)/ (mg∙kg-1) | w(速效磷 Available Phosphorus)/ (mg∙kg-1) | w(速效钾 Available potassium)/ (mg∙kg-1) |
---|---|---|---|---|---|---|---|
再力花 Thalia dealbata Link | 71.32 | 4.15 | 5.63 | 0.52 | 125.32 | 377.02 | 76.80 |
香根草 Vetiveria zizanioides L. | 74.87 | 2.93 | 6.02 | 0.75 | 260.55 | 412.79 | 91.48 |
花叶芦荻 A. donax var.versicolor | 67.77 | 4.06 | 5.10 | 0.39 | 115.05 | 395.00 | 62.24 |
污水质量浓度 Mass concentration in sewage | 全氮 TN | 氨氮 NH4+-N | 全磷 TP | 化学需氧量COD | 镉 Cd2+ | 铅 Pb2+ | 锌 Zn2+ | 铜 Cu2+ |
---|---|---|---|---|---|---|---|---|
高质量浓度 High mass concentration (H) | 40 | 24 | 3 | 400 | 10 | 10 | 10 | 10 |
中质量浓度 Medium mass concentration (M) | 30 | 18 | 2 | 300 | 5 | 5 | 5 | 5 |
低质量浓度 Low mass concentration (L) | 20 | 12 | 1 | 200 | 1 | 1 | 1 | 1 |
Table 2 The mass concentrations of indicators of different mass concentration wastewater mg∙L-1
污水质量浓度 Mass concentration in sewage | 全氮 TN | 氨氮 NH4+-N | 全磷 TP | 化学需氧量COD | 镉 Cd2+ | 铅 Pb2+ | 锌 Zn2+ | 铜 Cu2+ |
---|---|---|---|---|---|---|---|---|
高质量浓度 High mass concentration (H) | 40 | 24 | 3 | 400 | 10 | 10 | 10 | 10 |
中质量浓度 Medium mass concentration (M) | 30 | 18 | 2 | 300 | 5 | 5 | 5 | 5 |
低质量浓度 Low mass concentration (L) | 20 | 12 | 1 | 200 | 1 | 1 | 1 | 1 |
Fig. 1 Changes of TN mass concentration in swage with and without bacteria treatments Different lowercase letters indicate significant differences between different strains at the same treatment time; different capital letters indicate significant differences between different treatment times of the same strain, n=3;the same below
变异来源 Source of variation | df | F | |||
---|---|---|---|---|---|
全氮 TN | 氨氮 NH4+-N | 化学需氧量 COD | 全磷 TP | ||
校正模型 Calibration model | 131 | 433.485** | 176.183** | 393.199** | 1311.757** |
截距 Intercept | 1 | 271060.287** | 141796.804** | 294054.424** | 1942.975** |
质量浓度 Mass concentration | 2 | 8831.66** | 5094.498** | 14295.696** | 294.235** |
菌株 Strains | 10 | 893.397** | 202.431** | 748.072** | 101.183** |
时间 Time | 3 | 7469.366** | 2340.11** | 3756.656** | 35.719** |
质量浓度×菌株 Mass concentration×strains | 20 | 58.118** | 50.092** | 27.968** | 200.199** |
质量浓度×时间 Mass concentration×time | 6 | 281.593** | 95.853** | 200.51** | 60.442** |
菌株×时间 Strains×time | 30 | 137.928** | 29.986** | 67.645** | 300.128** |
质量浓度×菌株×时间 Mass concentration×strains×time | 60 | 13.189** | 22.831** | 6.254** | 600.037** |
Table 3 Multi-factor Analysis of the dynamic changes of TN, NH4+-N, COD, TP mass concentration in different strains
变异来源 Source of variation | df | F | |||
---|---|---|---|---|---|
全氮 TN | 氨氮 NH4+-N | 化学需氧量 COD | 全磷 TP | ||
校正模型 Calibration model | 131 | 433.485** | 176.183** | 393.199** | 1311.757** |
截距 Intercept | 1 | 271060.287** | 141796.804** | 294054.424** | 1942.975** |
质量浓度 Mass concentration | 2 | 8831.66** | 5094.498** | 14295.696** | 294.235** |
菌株 Strains | 10 | 893.397** | 202.431** | 748.072** | 101.183** |
时间 Time | 3 | 7469.366** | 2340.11** | 3756.656** | 35.719** |
质量浓度×菌株 Mass concentration×strains | 20 | 58.118** | 50.092** | 27.968** | 200.199** |
质量浓度×时间 Mass concentration×time | 6 | 281.593** | 95.853** | 200.51** | 60.442** |
菌株×时间 Strains×time | 30 | 137.928** | 29.986** | 67.645** | 300.128** |
质量浓度×菌株×时间 Mass concentration×strains×time | 60 | 13.189** | 22.831** | 6.254** | 600.037** |
测定指标 Measurement index | 细菌 Bacterial | 真菌 Fungi | |||
---|---|---|---|---|---|
拟合模型 Fit model | R2 | 拟合模型 Fit model | R2 | ||
全氮 TN | y=0.037x2-0.0049x+0.092 | 0.9881 | y=0.1334x1.185 | 0.9999 | |
氨氮 NH4+-N | y= -0.0059x2+0.1688x-0.0374 | 0.9976 | y=0.1151x1.0814 | 0.9883 | |
化学需氧量 COD | y= -0.0016x2+0.1379x-0.0184 | 0.9927 | y=0.1572x0.9493 | 0.9914 | |
全磷 TP | y= -0.029x2+0.2517x-0.173 | 0.9881 | y=0.1121x1.0105 | 0.9748 | |
平均去除率 Average adsorption rate | y=0.0002x2+0.1382x-0.034 | 1 | y=0.1292x1.0615 | 0.9885 |
Table 4 Fitting model table of bacteria and fungi
测定指标 Measurement index | 细菌 Bacterial | 真菌 Fungi | |||
---|---|---|---|---|---|
拟合模型 Fit model | R2 | 拟合模型 Fit model | R2 | ||
全氮 TN | y=0.037x2-0.0049x+0.092 | 0.9881 | y=0.1334x1.185 | 0.9999 | |
氨氮 NH4+-N | y= -0.0059x2+0.1688x-0.0374 | 0.9976 | y=0.1151x1.0814 | 0.9883 | |
化学需氧量 COD | y= -0.0016x2+0.1379x-0.0184 | 0.9927 | y=0.1572x0.9493 | 0.9914 | |
全磷 TP | y= -0.029x2+0.2517x-0.173 | 0.9881 | y=0.1121x1.0105 | 0.9748 | |
平均去除率 Average adsorption rate | y=0.0002x2+0.1382x-0.034 | 1 | y=0.1292x1.0615 | 0.9885 |
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