Chin J Plan Ecolo ›› 2016, Vol. 40 ›› Issue (9): 893-901.doi: 10.17521/cjpe.2016.0163

• Research Articles • Previous Articles     Next Articles

Effects of streams on lignin degradation during foliar litter decomposition in an alpine forest

Kai YUE1, Wan-Qin YANG1,2, Yan PENG1, Chun-Ping HUANG1,3, Chuan ZHANG1, Fu-Zhong WU1,2,*()   

  1. 1Long-term Research Station of Alpine Forest Ecosystems, Provincial Key Laboratory of Ecological Forestry Engineering, Institute of Ecology and Forestry, Sichuan Agricultural University, Chengdu 611130, China

    2Collaborative Innovation Center for Ecological Security in the Upper Reaches of the Yangtze River, Chengdu 611130 ,China
    3College of Life Science, Sichuan Normal University, Chengdu 610101, China
  • Received:2016-05-09 Accepted:2016-07-23 Online:2016-09-29 Published:2016-09-10
  • Contact: Fu-Zhong WU


AimsStreams are widely distributed in alpine forests, and litter decomposition in which is an important component of material cycling across the forest landscape. The leaching and fragmenting effects as well as the unique environmental factors in streams may have significant impacts on lignin degradation during litter decomposition, but studies on this are lacking.
Methods Using litterbag methods, we investigated the dynamics of lignin mass remaining and concentration (percent litter mass, %) during the decomposition of four foliar litters, which varied significantly in the initial litter chemical traits, from the dominant species of Salix paraplesia, Rhododendron lapponicum, Sabina saltuaria, and Larix mastersiana under different habitats (forest floor, stream, and riparian zone) in the upper reaches of the Minjiang River.
Important findings After two year’s incubation, litter lignin mass remaining for a specific litter species varied significantly (p < 0.05) among habitats, with an order of stream < riparian zone < forest floor. Lignin was degraded substantially in the early stage of litter decomposition process, and the lignin concentration first decreased and then increased with the proceeding of litter decomposition, but varied significantly (p < 0.05) among different litter species. Lignin mass showed a general trend of decrease across the 2-year decomposition course. In addition, habitat type, decomposition period and microenvironmental factors (e.g., temperature, pH value and nutrient availability) showed substantial influences on lignin degradation rate. These results suggest that the traditional view that lignin was relatively recalcitrant with an increase of concentration in the early stage of litter decomposition is challenged, but the loss of lignin in the early phrase is in line with recent findings about the fate of lignin during litter decomposition. Moreover, the significant differences of lignin degradation rates among different decomposition period and habitat types indicated that local-scale environmental factors can play a significant role in litter decomposition and lignin degradation processes.

Key words: carbon cycling, forest floor, stream, riparian zone, degradation rate, species, environmental factor

Table 1

Characteristics of environmental conditions of different habitats during the process of foliar litter decomposition (mean ± SD, n = 90)"

生境 Habitat AT (℃) C (g·kg-1) N (g·kg-1) P (g·kg-1) pH
林下 Forest floor 2.0 ± 5.2 126 ± 26 5.8 ± 1.1 1.2 ± 0.2 6.6 ± 0.02
生境 Habitat AT (°C) HCO3- (mg·L-1) NH4+ (mg·L-1) NO3-(mg·L-1) PO43- (μg·L-1) pH FV (m·s-1)
溪流 Stream 5.1 ± 2.6 13.9 ± 1.96 0.10 ± 0.05 0.29 ± 0.07 7.85 ± 0.38 6.6 ± 0.4 0.53 ± 0.15
河岸带 Riparian zone 4.8 ± 3.4 19.7 ± 1.33 0.04 ± 0.02 0.34 ± 0.08 7.84 ± 0.41 6.9 ± 0.3 0.05 ± 0.01

Table 2

Initial chemical properties of Salix paraplesia, Rhododendron lapponicum, Sabina saltuaria, and Larix mastersiana foliar litters (mean ± SD, n = 9)"

物种 Species C (%) N (%) P (%) 木质素 Lignin (%) C:N C:P N:P Lignin:N
康定柳 S. paraplesia 34.8 ± 0.9c 2.64 ± 0.15a 0.17 ± 0.01a 24.7 ± 1.3d 13.2 ± 0.8d 207 ± 19.7c 15.7 ± 1.7a 9.38 ± 0.8c
高山杜鹃 R. lapponicum 38.6 ± 1.1b 0.69 ± 0.10d 0.10 ± 0.02d 29.8 ± 0.8b 57.2 ± 10.2a 375 ± 53.6a 6.75 ± 1.5c 44.3 ± 8.3a
方枝柏 S. saltuaria 46.9 ± 1.8a 1.05 ± 0.06c 0.15 ± 0.01b 28.1 ± 0.8c 45.1 ± 3.9b 304 ± 12.6b 6.79 ± 0.7c 26.9 ± 1.8b
四川红杉 L. mastersiana 37.5 ± 0.5b 1.59 ± 0.11b 0.12 ± 0.01c 37.8 ± 1.0a 23.6 ± 1.8c 320 ± 24.6b 13.6 ± 0.8b 30.1 ± 2.1b

Fig. 1

Dynamics of lignin mass remaining (g) in the decomposing foliar litter of Salix paraplesia (A), Rhododendron lapponicum (B), Sabina saltuaria (C), and Larix mastersiana (D) under different habitat conditions (mean ± SD, n = 9). Different lowercase letters indicate significant (p < 0.05) differences of lignin mass remaining for a given litter species in a specific decomposition period under different habitat conditions."

Fig. 2

Dynamics of lignin concentration (percent litter mass, %) during Salix paraplesia (A), Rhododendron lapponicum (B), Sabina saltuaria (C), and Larix mastersiana (D) foliar litter decomposition (p < 0.05) under different habitat conditions (mean ± SD, n = 9). Different lowercase letters indicate significant (p < 0.05) differences of lignin concentration among different decomposition periods for a given litter species incubated in a specific type of habitat. FP, freezing period; GS, growing season; IV, initial value; LGS, late growing season; PP, pre-freezing period; TP, thawing period; 1, first year; 2, second year."

Fig. 3

Dynamics of lignin degradation rate (%/month) during Salix paraplesia (A), Rhododendron lapponicum (B), Sabina saltuaria (C), and Larix mastersiana (D) foliar litter decomposition (p < 0.05) under different habitat conditions (mean ± SD, n = 9). Different lowercase letters indicate significant (p < 0.05) differences of lignin degradation rate among different decomposition periods for a given litter species incubated in a specific type of habitat. FP, freezing period; GS, growing season; IV, initial value; LGS, late growing season; PP, pre-freezing period; TP, thawing period; 1, first year; 2, second year."

Table 3

Repeated-measure ANOVA analysis on the effects of litter species, habitat type, and decomposition period on lignin degradation rate during litter decomposition process"

Influence factor
Degree of freedom
F p
物种 Species 3 165.753 < 0.001
生境 Habitat 2 75.197 < 0.001
时期 Period 9 504.141 < 0.001
物种×生境 Species × habitat 6 40.353 < 0.001
物种×时期 Species × period 27 17.003 < 0.001
生境×时期 Habitat × period 18 18.317 < 0.001
Species × habitat × period
54 12.020 < 0.001

Table 4

Stepwise regression analysis between lignin degradation rate (%/month) of the 2 years and foliar litter initial chemical properties"

生境 Habitat 回归式 Regression model
a0 a1X1 a2X2 a3X3 a4X4
林下 Forest floor ŷ = 0.424 -0.017 C:N (0.353) +0.042 C (0.607)
溪流 Stream ŷ = 1.602 -0.031 Lignin:N (0.785) +13.231 P (0.874)
河岸带 Riparian zone ŷ = -7.311 +0.032 Lignin (0.783) +20.108 P (0.888) +0.164 N:P (0.932) +0.090 C (0.940)

Table 5

F-value for the regression analysis between lignin degradation rate (%/month) and environmental factors under different habitats during foliar litter decomposition"

林下 Forest floor AT C N P pH
康定柳 Salix paraplesia 26.925*** 35.094*** 1.987 0.340 6.194*
高山杜鹃 Rhododendron lapponicum 16.022*** 0.064 5.700* 17.816*** 2.431
方枝柏 Sabina saltuaria 10.134** 1.037 23.348*** 23.681*** 8.314**
四川红杉 Larix mastersiana 30.336*** 7.748** 32.560*** 10.076** 13.489***
溪流 Stream AT HCO3- NH4+ NO3- PO43- pH FV
康定柳 Salix paraplesia 0.001 0.572 2.692 13.248*** 0.522 6.208* 0.385
高山杜鹃 Rhododendron lapponicum 1.286 1.722 6.088* 8.832** 1.612 1.652 1.590
方枝柏 Sabinasaltuaria 1.245 4.809* 7.579** 8.964** 0.001 6.454* 0.103
四川红杉 Larix mastersiana 2.815 2.179 4.681* 11.866** 0.063 5.594* 0.053
河岸带 Riparian zone AT HCO3- NH4+ NO3- PO43- pH FV
康定柳 Salix paraplesia 35.148*** 5.748* 12.267** 0.256 1.305 16.431*** 2.540
高山杜鹃 Rhododendron lapponicum 3.702 2.822 2.029 1.369 0.001 7.300** 5.752*
方枝柏 Sabina saltuaria 1.564 4.024* 6.775* 4.609* 0.115 3.545 6.232*
四川红杉 Larix mastersiana 36.978*** 15.189*** 19.985*** 4.305* 0.055 0.371 11.602**
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