Please wait a minute...
Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2021, Vol. 15 Issue (6) : 134    https://doi.org/10.1007/s11783-021-1427-1
RESEARCH ARTICLE
Effects of previous drying of sediment on root functional traits and rhizoperformance of emerged macrophytes
Farasat Ali1,2, Ghulam Jilani3, Leilei Bai1, Chunliu Wang1,2, Linqi Tian1,2, Helong Jiang1()
1. State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, Nanjing 210008, China
2. University of Chinese Academy of Sciences, Beijing 100049, China
3. Institute of Soil Science, PMAS Arid Agriculture University, Rawalpindi 46300, Pakistan
 Download: PDF(3227 KB)   HTML
 Export: BibTeX | EndNote | Reference Manager | ProCite | RefWorks
Abstract

• Sediment desiccation alters morphological characteristics of aquatic sediment.

• Alternation in morphological properties of sediment limiting root characteristics.

• Fibrous-rooted macrophytes root properties extra favor nutrients removal.

• Thick-rooted macrophytes exhibit higher life-span in two sediment types.

Purpose of the current study was to investigate the effects of constantly wet and dried-rewetted sediments on root functional traits of emerged macrophytes and their nutrients removal abilities. It is based on the hypothesis that root characteristics and nutrients removal abilities of plants will be altered in the course of sediment desiccation. Four emerged macrophytes including two fibrous-root plants (Canna indica and Acorus calamus) and two thick-root plants (Alocasia cucullata and Aglaonema commutatum) were investigated for their root functional traits and rhizoperformance in both wet and dried-rewetted sediments. Results showed that sediment desiccation followed by rewetting substantially altered the root functional traits (root surface area, radial oxygen loss, and root activity) of plants due to adverse changes in morphological characteristics (porosity, bulk density, particle density) of dried-rewetted sediments than by wet sediments. Consequently, limited plants growth and removal of nitrogen (N), phosphorus (P) and dissolved organic carbon (DOC) were recorded in dried-rewetted sediments and their pore water than in wet sediments. Radial oxygen loss from plant roots correlated positively with root functional traits, plants growth, and removal of N, P and DOC from pore water and sediment in both sediment types. Among the macrophyte species, the fibrous-root plants having advantages root functional traits, greatly influenced the rhizospheric conditions (pH, dissolved oxygen and redox potential), and demonstrated higher N, P and DOC reduction from both sediment types. While, the thick-rooted plants with thick diameter roots (D > 1 mm) and higher rhizome exhibited longer life-span in both sediment types.

Keywords Fibrous-root macrophytes      Thick-root macrophytes      Nutrients removal      Wet sediment      Dried-rewetted sediment     
Corresponding Author(s): Helong Jiang   
Issue Date: 13 April 2021
 Cite this article:   
Farasat Ali,Ghulam Jilani,Leilei Bai, et al. Effects of previous drying of sediment on root functional traits and rhizoperformance of emerged macrophytes[J]. Front. Environ. Sci. Eng., 2021, 15(6): 134.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-021-1427-1
https://academic.hep.com.cn/fese/EN/Y2021/V15/I6/134
Fig.1  Root functional traits of four wetland plant species in the wet and dried-rewetted sediments. A. ROL, B. root activity, C. root porosity, D. Fe-plaque formation on root surface, and E. root surface area (Mean±SE, n = 4; different letters on the bar under each treatment point to significant variations among species in the wet and dried-rewetted sediments at (P<0.05) according to one-way ANOVA. * indicates significant differences between wet sediment plants and dried-rewetted sediment plants or treatments according to Tukey’s pairwise comparisons and 95% confidence, except data over bars marked by the same letters for the same trait are not significantly different at P<0.05).
Fig.2  Relationships between rates of ROL, root activity, Fe-plaque formation, porosity, and root surface area of the four tested wetland plant species grown in wet and dried-rewetted sediments, R and R2 values of the simple correlation and regression analyses are exhibited and all are significant at P<0.05; ●, DSCE; ○, WSCE; ▲, DSCT; ?, WSCT; ♦, DSSF; ◊, WSSF; ■, DSIS; and □, WSIS; RWS and R2WS are represented simple correlation and regression values of root activity, root porosity, Fe plaque formation, and root surface area vs. ROL in wet sediments; and RDS and R2DS are represented simple correlation and regression values of root activity, root porosity, Fe plaque formation, and root surface area vs. ROL in dried-rewetted sediments.
Sediment type Treatment type Species Root, shoot, and total biomass (g/plant) Lateral roots
D≤1 mm D >1mm RB SB TB
WS WSIS IS 24.58±1.55A 11.93±2.19A 36.51±3.60A 127.23±4.23A 163.74±5.73A +
WSSF SF 16.76±1.20B 8.34±1.00B 25.10±2.10B 78.36±3.61B 103.21±3.16B +
WSCT CT 5.99±0.61C 12.50±1.65C 18.49±1.16C 49.61±3.12C 69.10±2.18C +
WSCE CE 1.81±0.80D 14.61±1.58C 16.42±1.89C 39.54±2.47D 55.96±2.90D
DS DSIS IS 21.26±2.86A* 10.40±1.54A* 31.66±3.51A* 123.67±4.40A* 155.33±5.91A* +
DSSF SF 13.56±1.18B* 7.75±1.32B* 21.31±2.28B* 64.19±3.24B* 85.50±4.42B* +
DSCT CT 3.67±0.10C* 12.82±1.15C* 16.60±1.15C* 40.78±2.90C* 57.38±2.98C* +
DSCE CE 1.21±0.30D* 13.37±1.12C* 14.85±1.14C* 35.42±2.25C* 50.27±2.29D*
Tab.1  Below- and above-ground biomass and total biomass of plant species in wet and dried-rewetted sediments (Mean±SE, n = 5; different letters in each treatment show significant differences among plants at (P<0.05) according to one-way ANOVA; * indicates significant differences between wet sediment plants and dried-rewetted sediment plants according to Tukey’s pairwise comparisons and 95% confidence, except data in table marked by the same letters for the same trait are not significantly different at P<0.05).
Sediment type Treatment type Species RL (cm/plant) SL (cm/plant) R/S ratio (d.w./plant) RGR (mg/g/d) PL (d)
WS WSIS IS 34.45±4.26A 83.57±4.48A 0.26±0.01A 1.23±0.02A 124±6.53A
WSSF SF 42.39±5.79B 93.37±6.71B 0.32±0.02B 0.71±0.07B 141±4.23B
WSCT CT 52.47±4.91C 28.23±3.18C 0.39±0.03C 0.42±0.03C 166±5.36C
WSCE CE 26.74±3.87D 31.01±4.23C 0.41±0.01C 0.32±0.01D 172±7.14C
DS DSIS IS 30.64±3.19A* 71.21±5.93A* 0.28±0.03A* 1.16±0.04A* 118±7.81A*
DSSF SF 39.26±4.05B* 86.05±6.70B* 0.33±0.04B* 0.59±0.01B* 129±7.52A*
DSCT CT 43.57±3.99B* 26.48±3.16C* 0.40±0.02C* 0.33±0.05C* 149±5.39B*
DSCE CE 22.67±3.17C* 24.97±5.13C* 0.42±0.04D* 0.28.±0.02D* 164±9.77C*
Tab.2  Growth attributes and longevity of plant species (Mean±SE, n = 5, different letters in each treatment show significant differences among plants at (P<0.05) according to one-way ANOVA; * indicates significant differences between wet sediment plants and dried-rewetted sediment plants according to Tukey’s pairwise comparisons and 95% confidence, except data in table marked by the same letters for the same trait are not significantly different at P<0.05).
Fig.3  Removal percentages of TN, TP, and DOC by four plant species from the sediment and interstitial water of wet and dried-rewetted sediments (Mean±SE, n = 4; smaller letters on the bar under each treatment indicates that the plants were significant differed in TN and TP removal percentages from the wet sediments according to one-way ANOVA at (P<0.05); the smaller letters with (*) represent that the plants were substantial diverse in TN, TP, and DOC removal percentages from the interstitial water of wet sediments according to one-way ANOVA at (P<0.05); large letters on the bar under each indicates that the plants were significant different in TN and TP removal percentages from the dried-rewetted sediments according to one-way ANOVA at (P<0.05), and the larger letters with (*) represent that the plant species were considerable different in TN, TP, and DOC removal percentages from the interstitial water of dried-rewetted sediments according to one-way ANOVA at (P<0.05). According to tukey pairwise comparisons and 95% confidence plant species/treatments were significant different, except data over bars marked by the same letters for the same nutrient are not significantly different at P<0.05.
Fig.4  Relationships between rates of ROL and removal percentages of TN, TP, and DOC by four wetland plants grown in wet and dried-rewetted sediments; R and R2 values of the simple correlation and regression analyses are exhibited and all are significant at P<0.05; ○ represent TN and TP removal by CE from pore water of WSCE or DSCE, and DOC removal by CE from pore water of DSCE; ● represent TN and TP removal by CE from sediment of WSCE or DSCE, and DOC removal by CE from pore water of WSCE; ? represent TN and TP removal by CT from interstitial water of WSCT or DSCT, and DOC removal by CT from pore water of DSCT; ▲ represent TN and TP removal by SF from sediment of WSSF or DSSF, and DOC removal by CT from pore water of WSCT; ◊ represent TN and TP removal by SF from interstitial water of WSSF or DSSF, DOC removal by SF from pore water of DSSF; ♦ represent TN and TP removal by SF from sediment of WSSF or DSSF, and DOC removal by SF from pore water of WSSF; □ represent TN and TP removal by IS from interstitial water of WSIS or DSIS, and DOC removal from pore water of DSIS; ■ represent TN TP removal by IS from sediment of WSIS or DSIS, and DOC removal from pore water of WSIS; RS and R2S represent simple correlation and regression values of TN and TP removal percentages from sediment vs. ROL; RW and R2W represent simple correlation and regression values of TN, TP, and DOC removal percentages from interstitial water vs. ROL; RWS and R2WS indicate simple correlation and regression values of DOC removal percentages from pore water of wet sediments vs. ROL, RDS and R2DS represent simple correlation and regression values of DOC removal percentages from pore water of dried-rewetted sediments vs. ROL.
Fig.5  DO, pH, EC, and ORP in interstitial water of plant species grown in wet and dried-rewetted sediments (Mean±SE, n = 4; different letters on top of the bar under each treatments point to significant differences among plant species in wet and dried-rewetted sediments/treatments according to one-way ANOVA at P<0.05; * indicates significant differences between wet sediment plants and dried-rewetted sediment plants or treatments according to Tukey’s pairwise comparisons and 95% confidence, except data over bars marked by the same letters for the same trait are not significantly different at P<0.05).
Fig.6  PCA biplot of mean factor loadings of each treatment on PCA-1 and PCA-2, un-rotated eigenvectors for each root functional trait, nutrient removal percentage, and biogeochemical factor are represented by different color arrows, different color circles are indicated dried-rewetted sediment treatments, and different color triangles are represented wet sediment treatments.
1 R Al-Saedi, K Smettem, K H M Siddique (2018). Nitrogen removal efficiencies and pathways from unsaturated and saturated zones in a laboratory-scale vertical flow constructed wetland. Journal of Environmental Management, 228: 466–474
https://doi.org/10.1016/j.jenvman.2018.09.048
2 F Ali, G Jilani, R Fahim, L Bai, C Wang, L Tian, H Jiang (2019). Functional and structural roles of wiry and sturdy rooted emerged macrophytes root functional traits in the abatement of nutrients and metals. Journal of Environmental Management, 249: 109330
https://doi.org/10.1016/j.jenvman.2019.109330
3 J K Apple, E M Smith, T J Boyd (2008). Temperature, salinity, nutrients, and the covariation of bacterial production and chlorophyll-a in estuarine ecosystems. Journal of Coastal Research, 55(10055): 59–75
https://doi.org/10.2112/SI55-005.1
4 J Armstrong, W Armstrong, P M Beckett (1992). Phragmites australis: Venturi- and humidity-induced pressure flows enhance rhizome aeration and rhizosphere oxidation. New Phytologist, 120(2): 197–207
https://doi.org/10.1111/j.1469-8137.1992.tb05655.x
5 W Armstrong (1971). Radial oxygen losses from intact rice roots as affected by distance from the apex, respiration and waterlogging. Plant Physiology, 25(2): 192–197
https://doi.org/10.1111/j.1399-3054.1971.tb01427.x
6 W Armstrong (1980). Aeration in higher plants. Advances in Botanical Research, 7: 225–234
https://doi.org/10.1016/S0065-2296(08)60089-0
7 X Bai, K Chen, K Ren, W Huang, X Chen (2012). Impacts of four emergent macrophytes on sediment nutrient loading. Journal of Freshwater Ecology, 27(4): 481–493
https://doi.org/10.1080/02705060.2012.675524
8 L Bao, X Li, P Cheng (2018). Phosphorus retention along a typical urban landscape river with a series of rubber dams. Journal of Environmental Management, 228: 55–64
https://doi.org/10.1016/j.jenvman.2018.09.019
9 J W Barko, R M Smart (1986). Sediment‐related mechanisms of growth limitation in submersed macrophytes. Ecology, 67(5): 1328–1340
https://doi.org/10.2307/1938689
10 L C Batty, A J Baker, B D Wheeler (2002). Aluminium and phosphate uptake by Phragmites australis: The role of Fe, Mn and Al root plaques. Annals of Botany, 89(4): 443–449
https://doi.org/10.1093/aob/mcf067
11 W Battye, V P Aneja, W H Schlesinger (2017). Is nitrogen the next carbon? Earth’s Future, 5(9): 894–904
https://doi.org/10.1002/2017EF000592
12 M A O Bustamante, M V Mier, J A E Estrada, C D Domíguez (2011). Nitrogen and potassium variation on contaminant removal for a vertical subsurface flow lab scale constructed wetland. Bioresource Technology, 102(17): 7745–7754
https://doi.org/10.1016/j.biortech.2011.06.005
13 J R Carmignani, A H Roy (2017). Ecological impacts of winter water level drawdowns on lake littoral zones: A review. Aquatic Sciences, 79(4): 803–824
https://doi.org/10.1007/s00027-017-0549-9
14 W Chen, Z Chen, Q He, X Wang, C Wang, D Chen, Z Lai (2007). Root growth of wetland plants with different root types. Acta Ecologica Sinica, 27(2): 450–457
https://doi.org/10.1016/S1872-2032(07)60017-1
15 X C Chen, L Huang, T H A Chang, B L Ong, S L Ong, J Hu (2019). Plant traits for phytoremediation in the tropics. Engineering (Beijing), 5(5): 841–848
https://doi.org/10.1016/j.eng.2019.07.019
16 Z H Chen, F Chen, X Y Cheng, X C Liu, X Y Zhou (2004). Researches on macrophyte roots in the constructed wetlands: A review. Plant Biology, 5: 131–142
17 X Y Cheng, W Y Chen, B H Gu, X C Liu, F Chen, Z H Chen, X Y Zhou, Y X Li, H Huang, Y J Chen (2009a). Morphology, ecology, and contaminant removal efficiency of eight wetland plants with differing root systems. Hydrobiologia, 623(1): 77–85
https://doi.org/10.1007/s10750-008-9649-9
18 X Y Cheng, M Q Liang, W Y Chen, X C Liu, Z H Chen (2009b). Growth and contaminant removal effect of several plants in constructed wetlands. Journal of Integrative Plant Biology, 51(3): 325–335
https://doi.org/10.1111/j.1744-7909.2008.00804.x
19 S Daneshgar, A Callegari, A Capodaglio, D Vaccari (2018). The potential phosphorus crisis: resource conservation and possible escape technologies: A review. Resources, 7(37): 1-22
https://doi.org/10.3390/resources7020037
20 W J Fitz, W W Wenzel (2002). Arsenic transformations in the soil–rhizosphere–plant system: fundamentals and potential application to phytoremediation. Journal of Biotechnology, 99(3): 259–278
https://doi.org/10.1016/S0168-1656(02)00218-3
21 X Fu, X He (2015). Nitrogen and phosphorus removal from contaminated water by five aquatic plants. In: international conference on mechatronics, electronic, industrial and control engineering. Singapore: Atlantis Press
22 R E Haling, L K Brown, A G Bengough, I M Young, P D Hallett, P J White, T S George (2013). Root hairs improve root penetration, root–soil contact, and phosphorus acquisition in soils of different strength. Journal of Experimental Botany, 64(12): 3711–3721
https://doi.org/10.1093/jxb/ert200
23 M R Hasan, C Rina (2009). Use of algae and aquatic macrophytes as feed in small-scale aquaculture: A review, Technical Paper, 531 FAO: 112–123
24 L Hermann, F Kraus, R Hermann (2018). Phosphorus processing: Potentials for higher efficiency. Sustainability, 10(5): 1–19
https://doi.org/doi.org/10.3390/su10051482
25 C W Hickey, M M Gibbs (2009). Lake sediment phosphorus release management: Decision support and risk assessment framework. New Zealand Journal of Marine and Freshwater Research, 43(3): 819–856
https://doi.org/10.1080/00288330909510043
26 H Huang, Y Zhu, Z Chen, X Yin, G Sun (2012). Arsenic mobilization and speciation during iron plaque decomposition in a paddy soil. Journal of Soils and Sediments, 12(3): 402–410
https://doi.org/10.1007/s11368-011-0461-1
27 X Ji, L Xu, Y Xie, Z Wang, F Chen, W Chen, Z Luo (2015). Effects of hydrophytes on removal of nitrogen and phosphorus in different levels of eutrophic water. Southwest China Journal of Agricultural Sciences, 28: 809–814 (in Chinese)
28 D Jing, H y Hu (2010). Chemical oxygen demand, nitrogen, and phosphorus removal by vegetation of different species in pilot-scale subsurface wetlands. Environmental Engineering Science, 27(3): 247–253
https://doi.org/10.1089/ees.2009.0440
29 H Kludze, R DeLaune, W Patrick Jr (1994). A colorimetric method for assaying dissolved oxygen loss from container-grown rice roots. Agronomy Journal, 86(3): 483–487
https://doi.org/10.2134/agronj1994.00021962008600030005x
30 J Kyambadde, F Kansiime, L Gumaelius, G Dalhammar (2004). A comparative study of Cyperus papyrus and Miscanthidium violaceum-based constructed wetlands for wastewater treatment in a tropical climate. Water Research, 38(2): 475–485
https://doi.org/10.1016/j.watres.2003.10.008
31 W L Lai, S Q Wang, C L Peng, Z H Chen (2011). Root features related to plant growth and nutrient removal of 35 wetland plants. Water Research, 45(13): 3941–3950
https://doi.org/10.1016/j.watres.2011.05.002
32 W L Lai, Y Zhang, Z H Chen (2012). Radial oxygen loss, photosynthesis, and nutrient removal of 35 wetland plants. Ecological Engineering, 39: 24–30
https://doi.org/10.1016/j.ecoleng.2011.11.010
33 D Liu (2017). Estimation of riverine organic carbon flux based on remote sensing and in-situ data. Hangzhou: Zhejiang University
34 J Lu, S E Bunn, M A Burford (2018a). Effects of water level fluctuations on nitrogen dynamics in littoral macrophytes. Limnology and Oceanography, 63(2): 833–845
https://doi.org/10.1002/lno.10673
35 J Lu, S E Bunn, M A Burford (2018b). Nutrient release and uptake by littoral macrophytes during water level fluctuations. Science of the Total Environment, 622–623: 29–40
https://doi.org/10.1016/j.scitotenv.2017.11.199
36 Y Lu, Y Zhou, S Nakai, M Hosomi, H Zhang, H J Kronzucker, W Shi (2014). Stimulation of nitrogen removal in the rhizosphere of aquatic duckweed by root exudate components. Planta, 239(3): 591–603
https://doi.org/10.1007/s00425-013-1998-6
37 X Mei, Z Ye, M Wong (2009). The relationship of root porosity and radial oxygen loss on arsenic tolerance and uptake in rice grains and straw. Environmental Pollution, 157(8-9): 2550–2557
https://doi.org/10.1016/j.envpol.2009.02.037
38 X Q Mei, M H Wong, Y Yang, H Y Dong, R L Qiu, Z H Ye (2012). The effects of radial oxygen loss on arsenic tolerance and uptake in rice and on its rhizosphere. Environmental Pollution, 165: 109–117
https://doi.org/10.1016/j.envpol.2012.02.018
39 X-Q Mei, Y Yang, NF-Y Tam, Y-W Wang, L Li (2014). Roles of root porosity, radial oxygen loss, Fe plaque formation on nutrient removal and tolerance of wetland plants to domestic wastewater. Water Resarch, 50:147–159
40 M M Montiel-Rozas, E Madejón, P Madejón (2016). Effect of heavy metals and organic matter on root exudates (low molecular weight organic acids) of herbaceous species: An assessment in sand and soil conditions under different levels of contamination. Environmental Pollution, 216: 273–281
https://doi.org/10.1016/j.envpol.2016.05.080
41 M Nikolakopoulou, A Argerich, J D Drummond, E Gacia, E Martí, A Sorolla, F Sabater (2018). Emergent macrophyte root architecture controls subsurface solute transport. Water Resources Research, 54(9): 5958–5972
https://doi.org/10.1029/2017WR022381
42 S Pezeshki, R DeLaune (2012). Soil oxidation-reduction in wetlands and its impact on plant functioning. Biology (Basel), 1(2): 196–221
https://doi.org/10.3390/biology1020196
43 N Pi, N Tam, MH Wong (2011). Formation of iron plaque on mangrove roots receiving wastewater and its role in immobilization of wastewater-borne pollutants. Marine pollution bulletin, 63(5–12): 402–411
44 V Poirier, C Roumet, A D Munson (2018). The root of the matter: Linking root traits and soil organic matter stabilization processes. Soil Biology & Biochemistry, 120: 246–259
https://doi.org/10.1016/j.soilbio.2018.02.016
45 H Poorter, J Bühler, D van Dusschoten, J Climent, J A Postma (2012). Pot size matters: A meta-analysis of the effects of rooting volume on plant growth. Functional Plant Biology, 39(11): 839–850
https://doi.org/10.1071/FP12049
46 E Rejmánková (2011). The role of macrophytes in wetland ecosystems. Journal of Ecology and Environment, 34(4): 333–345
https://doi.org/10.5141/JEFB.2011.044
47 V Ruban, J López-Sánchez, P Pardo, G Rauret, H Muntau, P Quevauviller (1999). Selection and evaluation of sequential extraction procedures for the determination of phosphorus forms in lake sediment. Journal of Environmental Monitoring, 1(1): 51–56
https://doi.org/10.1039/a807778i
48 B C Sekadende, J F Machiwa, F F Mwanuzi (2014). Processes governing the retention of phosphorus and nitrogen in nyashishi wetland. Open Journal of Ecology, 04(03): 124–134
https://doi.org/10.4236/oje.2014.43014
49 P A Siver, A M Coleman, G A Benson, J T Simpson (1986). The effects of winter drawdown on macrophytes in candlewood lake, connecticut. Lake and Reservoir Management, 2(1): 69–73
https://doi.org/10.1080/07438148609354604
50 State Environmental Protection Administration of China (2002). Methods for Water Analysis. 4 ed. Beijing: Environment Science Press, 200–285 (in Chinese)
51 U Stottmeister, A Wießner, P Kuschk, U Kappelmeyer, M Kästner, O Bederski, R A Müller, H Moormann (2003). Effects of plants and microorganisms in constructed wetlands for wastewater treatment. Biotechnology Advances, 22(1–2): 93–117
https://doi.org/10.1016/j.biotechadv.2003.08.010
52 X Sun, Y Chen (1994). Research on root systems of Ceratoides arboresorens. Grassland of China, 4: 39–44 (in Chinese)
53 C H Syu, C H Lee, P Y Jiang, M K Chen, D Y Lee (2014). Comparison of As sequestration in iron plaque and uptake by different genotypes of rice plants grown in As-contaminated paddy soils. Plant and Soil, 374(1–2): 411–422
https://doi.org/10.1007/s11104-013-1893-8
54 G J Taylor, A A Crowder (1983). Use of the DCB technique for extraction of hydrous iron oxides from roots of wetland plants. American Journal of Botany, 70(8): 1254–1257
https://doi.org/10.1002/j.1537-2197.1983.tb12474.x
55 C Tian, C Wang, Y Tian, X Wu, B Xiao (2015). Root radial oxygen loss and the effects on rhizosphere microarea of two submerged plants. Polish Journal of Environmental Studies, 24: 1795–1802
https://doi.org/10.15244/pjoes/38971
56 L Tu, K A Jarosch, T Schneider, M Grosjean (2019). Phosphorus fractions in sediments and their relevance for historical lake eutrophication in the Ponte Tresa Basin (Lake Lugano, Switzerland) since 1959. Science of the Total Environment, 685: 806–817
https://doi.org/10.1016/j.scitotenv.2019.06.243
57 USEPA (1983). Methods for Chemical Analysis of Water and Wastes. Madison: ASA and SSSA & Cincinnati: Environmental Monitoring and Support Laboratory
58 E J W Visser, G M Bögemann (2003). Measurement of porosity in very small samples of plant tissue. Plant and Soil, 253(1): 81–90
https://doi.org/10.1023/A:1024560322835
59 Q Wang, Y Hu, H Xie, Z Yang (2018). Constructed wetlands: A review on the role of radial oxygen loss in the rhizosphere by macrophytes. Water (Basel), 10(6): 1-11
https://doi.org/10.3390/w10060678
60 M West, N Fenner, R Gough, C Freeman (2017). Evaluation of algal bloom mitigation and nutrient removal in floating constructed wetlands with different macrophyte species. Ecological Engineering, 108: 581–588
https://doi.org/10.1016/j.ecoleng.2017.07.033
61 C Wu, Z Ye, H Li, S Wu, D Deng, Y Zhu, M Wong (2012). Do radial oxygen loss and external aeration affect iron plaque formation and arsenic accumulation and speciation in rice? Journal of Experimental Botany, 63(8): 2961–2970
https://doi.org/10.1093/jxb/ers017
62 X L Xu, X X Lu, X D Lei, L K Cao (2012). Effects of hydrophytes on removal of nitrogen and phosphorus in eutrophic water. Journal of Shanghai Jiao Tong University, 30(1): 8–14
63 Z Xu, Y Ban, Y Jiang, X Zhang, X Liu (2016). Arbuscular mycorrhizal fungi in wetland habitats and their application in constructed wetland: A review. Pedosphere, 26(5): 592–617
https://doi.org/10.1016/S1002-0160(15)60067-4
64 C Yang, L Yang, Y Yang, Z Ouyang (2004). Rice root growth and nutrient uptake as influenced by organic manure in continuously and alternately flooded paddy soils. Agricultural Water Management, 70(1): 67–81
https://doi.org/10.1016/j.agwat.2004.05.003
65 J Yang, G Zheng, J Yang, X Wan, B Song, W Cai, J Guo (2017). Phytoaccumulation of heavy metals (Pb, Zn, and Cd) by 10 wetland plant species under different hydrological regimes. Ecological Engineering, 107: 56–64
https://doi.org/10.1016/j.ecoleng.2017.06.052
66 Z Ye, A Baker, M H Wong, A Willis (1997). Copper and nickel uptake, accumulation and tolerance in Typha latifolia with and without iron plaque on the root surface. New Phytologist, 136(3): 481–488
https://doi.org/10.1046/j.1469-8137.1997.00758.x
67 Y Zhan, Y Yu, J Lin, X Wu, Y Wang, Y Zhao (2019). Simultaneous control of nitrogen and phosphorus release from sediments using iron-modified zeolite as capping and amendment materials. Journal of Environmental Management, 249: 109369
https://doi.org/10.1016/j.jenvman.2019.109369
68 X Zhang, F Zhang, D Mao (1999). Effect of iron plaque outside roots on nutrient uptake by rice (Oryza sativa L.): phosphorus uptake. Plant and Soil, 209(2): 187–192
https://doi.org/10.1023/A:1004505431879
[1] FSE-21020-OF-AF_suppl_1 Download
[1] Guangrong Sun, Chuanyi Zhang, Wei Li, Limei Yuan, Shilong He, Liping Wang. Effect of chemical dose on phosphorus removal and membrane fouling control in a UCT-MBR[J]. Front. Environ. Sci. Eng., 2019, 13(1): 1-.
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed