Rhizomes are essential organs for growth and expansion of Phragmites australis. They function as an important source of organic matter and as a nutrient source, especially in the artificial land-water transitional zones (ALWTZs) of shallow lakes. In this study, decomposition experiments on 1- to 6-year-old P. australis rhizomes were conducted in the ALWTZ of Lake Baiyangdian to evaluate the contribution of the rhizomes to organic matter accumulation and nutrient release. Mass loss and changes in nutrient content were measured after 3, 7, 15, 30, 60, 90, 120, and 180 days. The decomposition process was modeled with a composite exponential model. The Pearson correlation analysis was used to analyze the relationships between mass loss and litter quality factors. A multiple stepwise regression model was utilized to determine the dominant factors that affect mass loss. Results showed that the decomposition rates in water were significantly higher than those in soil for 1- to 6-year-old rhizomes. However, the sequence of decomposition rates was identical in both water and soil. Significant relationships between mass loss and litter quality factors were observed at a later stage, and P-related factors proved to have a more significant impact than N-related factors on mass loss. According to multiple stepwise models, the C/P ratio was found to be the dominant factor affecting the mass loss in water, and the C/N and C/P ratios were the main factors affecting the mass loss in soil. The combined effects of harvesting, ditch broadening, and control of water depth should be considered for lake administrators.
Percentage of mass losses at different sampling times
3 days
7 days
15 days
30 days
60 days
90 days
120 days
180 days
In water
N%
0.009
0.167 c)
0.398
0.283 b)
-0.879 b)
0.905 b)
0.897 b)
0.57 a)
P%
0.211
0.264 c)
0.465
0.463a)
0.936 b)
0.955a)
0.926 b)
0.716 a)
C:N
0.313
0.14
0.001
0.311
-0.426 b)
-0.554
-0.466
0.022
C:P
-0.101
-0.101
-0.182
-0.063 b)
-0.677 b)
-0.820a)
-0.874a)
-0.919 b)
N:P
-0.792
-0.465
-0.359
-0.77
-0.275
-0.236
-0.197 b)
-0.624
In soil
N%
0.272
0.255 c)
0.451
0.913 c)
0.954 b)
-0.008 b)
0.938 b)
0.919 a)
P%
0.424
0.294 c)
0.563
0.950 c)
0.887a)
0.129 a)
0.941a)
0.958 a)
C:N
0.165
0.035
-0.047
-0.569
-0.850 c)
0.541
-0.625
-0.512
C:P
-0.226
-0.136
-0.431
-0.81
-0.851a)
0.202 b)
-0.719 b)
-0.742 a)
N:P
0.684
0.293
0.548
0.181
-0.276 b)
0.691a)
0.734 b)
0.875 a)
Tab.3
Environment
Equations
r2
p
In water
Mloss = 0.003t + 0.145
0.819
<0.0001
Mloss = 0.003t-0.0008C:P+ 0.074
0.933
<0.0001
In soil
Mloss = 0.003 t + 0.075
0.884
<0.0001
Mloss = 0.002t-0.136 C:N -0.0007C:P+ 0.167
0.924
<0.0001
Tab.4
Age categories
Mesh size/mm2
Incubation days/d
v/(d-1)
Environment
References
1- to 6- year-old
1 × 1
180
0.0040?0.0047
In water
This study
1- to 6- year-old
1 × 1
180
0.0033?0.0041
In soil
This study
1- to 2- year-old
1 × 1
953
0.0023
In water
ágoston-Szabó et al. (2006)
1-year-old
1 × 1
434
0.0014
In soil
Wrubleski et al. (1997)
1-year-old
1 × 1
434
0.0032
In water
Wrubleski et al. (1997)
1- to 4- year-old
1 × 1
369
0.0014?0.005
In soil
Asaeda and Nam (2002)
1- to 2- year-old
5 × 5
150
0.004
In water
Eid et al. (2014)
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