Chin J Plant Ecol ›› 2005, Vol. 29 ›› Issue (6): 878-883.DOI: 10.17521/cjpe.2005.0116 cstr: 32100.14.cjpe.2005.0116
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WEI Xiao-Ping1, ZHAO Chang-Ming1, WANG Gen-Xuan2,1,*(
), CHEN Bao-Ming1, CHENG Dong-Liang1
Received:2005-02-02
Accepted:2005-05-27
Online:2005-02-02
Published:2005-09-30
Contact:
WANG Gen-Xuan
Supported by:WEI Xiao-Ping, ZHAO Chang-Ming, WANG Gen-Xuan, CHEN Bao-Ming, CHENG Dong-Liang. ESTIMATION OF ABOVE- AND BELOW-GROUND BIOMASS OF DOMINANT DESERT PLANT SPECIES IN AN OASIS-DESERT ECOTONE OF MINQIN, CHINA[J]. Chin J Plant Ecol, 2005, 29(6): 878-883.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2005.0116
| Plant species | Species number per sample (Mean±SD) | Frequency (%) | Coverage (%) | Importance value | ||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Agriophyllum squarrosum | 7 | 30 | 0 | 70 | ||||||||||||||||||
| Nitraria tangutorum | 1 | 7 | 9 | 69 | ||||||||||||||||||
| Calligonum mongolicum | 5 | 26 | 2 | 66 | ||||||||||||||||||
| Haloxylon ammodendron | 1 | 7 | 2 | 29 | ||||||||||||||||||
| Halogeton arachnoideus | 2 | 10 | 0 | 23 | ||||||||||||||||||
| Phragmites communis | 1 | 5 | 0 | 10 | ||||||||||||||||||
| Sophora alopecuroides | 0 | 3 | 0 | 6 | ||||||||||||||||||
| Limonium aureum | 8 | 2 | 0 | 4 | ||||||||||||||||||
| Artemisia arenaria | 0 | 2 | 0 | 4 | ||||||||||||||||||
| Thermopsis schischkinii | 0 | 2 | 0 | 4 | ||||||||||||||||||
| Elaeagnus angustifolia | 0 | 0 | 0 | 3 | ||||||||||||||||||
| Suaeda glauca | 0 | 1 | 0 | 2 | ||||||||||||||||||
| Hedysarum scoparium | 0 | 0 | 0 | 1 | ||||||||||||||||||
| Bassia dasyphylla | 0 | 0 | 0 | 0 | ||||||||||||||||||
| Caragana microphylla | 0 | 0 | 0 | 0 | ||||||||||||||||||
| Cirsium setosum | 0.05±0.27 | 0.24 | 0.001 | 0.466 | ||||||||||||||||||
Table 1 Analysis of dominant species in study area
| Plant species | Species number per sample (Mean±SD) | Frequency (%) | Coverage (%) | Importance value | ||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Agriophyllum squarrosum | 7 | 30 | 0 | 70 | ||||||||||||||||||
| Nitraria tangutorum | 1 | 7 | 9 | 69 | ||||||||||||||||||
| Calligonum mongolicum | 5 | 26 | 2 | 66 | ||||||||||||||||||
| Haloxylon ammodendron | 1 | 7 | 2 | 29 | ||||||||||||||||||
| Halogeton arachnoideus | 2 | 10 | 0 | 23 | ||||||||||||||||||
| Phragmites communis | 1 | 5 | 0 | 10 | ||||||||||||||||||
| Sophora alopecuroides | 0 | 3 | 0 | 6 | ||||||||||||||||||
| Limonium aureum | 8 | 2 | 0 | 4 | ||||||||||||||||||
| Artemisia arenaria | 0 | 2 | 0 | 4 | ||||||||||||||||||
| Thermopsis schischkinii | 0 | 2 | 0 | 4 | ||||||||||||||||||
| Elaeagnus angustifolia | 0 | 0 | 0 | 3 | ||||||||||||||||||
| Suaeda glauca | 0 | 1 | 0 | 2 | ||||||||||||||||||
| Hedysarum scoparium | 0 | 0 | 0 | 1 | ||||||||||||||||||
| Bassia dasyphylla | 0 | 0 | 0 | 0 | ||||||||||||||||||
| Caragana microphylla | 0 | 0 | 0 | 0 | ||||||||||||||||||
| Cirsium setosum | 0.05±0.27 | 0.24 | 0.001 | 0.466 | ||||||||||||||||||
| Species | Weight (g·plant-1) | Height of sand mounds (cm·plant-1) | Basal diameter (cm·plant-1) | Total height (cm·plant-1) | Canopy cover (m2·plant-1) | |
|---|---|---|---|---|---|---|
| Above-ground | Below-ground | |||||
| Nitraria tangutorum Calligonum mongolicum Haloxylon ammodendron Agriophyllum squarrosum Halogeton arachnoideus | 288.91±320.66 34.69±17.37 1 876.36±836.31 4.69±2.29 6.24±4.26 | 721.55±779.67 32.51±17.08 - 0.59±0.35 0.70±0.49 | 27.72±21.29 - - - - | - 0.99±0.47 2.93±1.04 0.32±0.08 0.35±0.17 | 28.32±6.75 45.10±16.41 221.59±75.26 18.78±6.81 11.72±3.75 | 3.71±4.69 0.24±0.13 0.35±0.21 0.11±0.06 0.09±0.06 |
Table 2 Plant species and average morphological characteristics of dominant species
| Species | Weight (g·plant-1) | Height of sand mounds (cm·plant-1) | Basal diameter (cm·plant-1) | Total height (cm·plant-1) | Canopy cover (m2·plant-1) | |
|---|---|---|---|---|---|---|
| Above-ground | Below-ground | |||||
| Nitraria tangutorum Calligonum mongolicum Haloxylon ammodendron Agriophyllum squarrosum Halogeton arachnoideus | 288.91±320.66 34.69±17.37 1 876.36±836.31 4.69±2.29 6.24±4.26 | 721.55±779.67 32.51±17.08 - 0.59±0.35 0.70±0.49 | 27.72±21.29 - - - - | - 0.99±0.47 2.93±1.04 0.32±0.08 0.35±0.17 | 28.32±6.75 45.10±16.41 221.59±75.26 18.78±6.81 11.72±3.75 | 3.71±4.69 0.24±0.13 0.35±0.21 0.11±0.06 0.09±0.06 |
| Species biomass | Correlation coefficients | |||
|---|---|---|---|---|
| Sand mounds at height (cm) | Basal diameter (cm) | Total height (cm) | Canopy cover (cm2) | |
| Nitraria tangutorum Above-ground dry biomass, ADB (g) Below-ground fresh biomass, BFB (g) Total fresh biomass, TFB (g) Total dry biomass, TDB (g) | 0.711a 0.810a 0.780a 0.786a | - - - - | -0.002 -0.099 -0.065 -0.071 | 0.868a 0.918a 0.907a 0.909a |
| Calligonuum mongolicum Above-ground dry biomass(g) Below-ground fresh biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - - | 0.492c 0.488c 0.437c 0.507c | 0.033 0.131 0.078 0.051 | 0.949a 0.910a 0.967a 0.922a |
| Haloxylon ammodendron | ||||
| Above-ground dry biomass(g) | - | 0.790a | 0.405 | 0.878a |
| Agriophyllum squarrosum Above-ground dry biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - | 0.851a 0.849a 0.853a | 0.377c 0.291 0.368c | 0.704a 0.639a 0.694a |
| Halogeton arachnoideus Above-ground dry biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - | 0.791a 0.807b 0.809a | 0.336c 0.339c 0.315 | 0.883a 0.785a 0.888a |
Table 3 Correlation coefficients between basal diameter, total height, canopy cover and height of sand mounds with Nitraria tangutorum and biomass of species
| Species biomass | Correlation coefficients | |||
|---|---|---|---|---|
| Sand mounds at height (cm) | Basal diameter (cm) | Total height (cm) | Canopy cover (cm2) | |
| Nitraria tangutorum Above-ground dry biomass, ADB (g) Below-ground fresh biomass, BFB (g) Total fresh biomass, TFB (g) Total dry biomass, TDB (g) | 0.711a 0.810a 0.780a 0.786a | - - - - | -0.002 -0.099 -0.065 -0.071 | 0.868a 0.918a 0.907a 0.909a |
| Calligonuum mongolicum Above-ground dry biomass(g) Below-ground fresh biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - - | 0.492c 0.488c 0.437c 0.507c | 0.033 0.131 0.078 0.051 | 0.949a 0.910a 0.967a 0.922a |
| Haloxylon ammodendron | ||||
| Above-ground dry biomass(g) | - | 0.790a | 0.405 | 0.878a |
| Agriophyllum squarrosum Above-ground dry biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - | 0.851a 0.849a 0.853a | 0.377c 0.291 0.368c | 0.704a 0.639a 0.694a |
| Halogeton arachnoideus Above-ground dry biomass(g) Total fresh biomass(g) Total dry biomass(g) | - - - | 0.791a 0.807b 0.809a | 0.336c 0.339c 0.315 | 0.883a 0.785a 0.888a |
| Species | Equations | Data statistics | |||||
|---|---|---|---|---|---|---|---|
| Estimation | Prediction | ||||||
| R | N | F | P | R | P | ||
| Nitraria tangutorum ADB BFB TFB TDB | Y1=68.878+0.005 932 X2 Y2=328.636+0.033 781X2 Y3=546.033+0.053 14 X2 Y4=224.909+0.021 18 X2 | 0.868 0.918 0.907 0.909 | 22 22 22 22 | 61.029 107.271 92.606 95.382 | 0.000 0.000 0.000 0.000 | 0.923 0.952 0.983 0.978 | 0.000 0.000 0.000 0.000 |
| Calligonum mongolicum ADB BFB TFB TDB | Y1=-0.371+6.946X1+0.011 95X2 Y2=-11.355+14.768X1+0.022 84X2 Y3=-14.218+19.116X1+0.053 91X2 Y4=-0.865+15.524X1+0.022 34X2 | 0.966 0.929 0.974 0.944 | 21 21 21 21 | 125.341 56.956 164.913 73.749 | 0.000 0.000 0.000 0.000 | 0.993 0.985 0.976 0.994 | 0.000 0.000 0.000 0.000 |
| Haloxylon ammodendron | |||||||
| ADB | Y=501.709+284.065X1+0.24X2 | 0.903 | 22 | 41.885 | 0.000 | 0.917 | 0.000 |
| Agriophyllum squarrosum ADB TFB TDB | Y1= -3.348+20.230X1+0.001 453X2 Y2= -8.422+69.941X1+0.003 591X2 Y3= -3.870+23.298X1+0.001 571X2 | 0.906 0.881 0.904 | 33 33 33 | 69.004 52.199 67.045 | 0.000 0.000 0.000 | 0.954 0.947 0.968 | 0.000 0.000 0.000 |
| Halogeton arachnoideus ADB TFB TDB | Y1= -0.485+3.455X1+0.006 1X2 Y2= -14.031+118.501X1+0.025 6X2 Y3= -0.653+5.179X1+0.006 36X2 | 0.885 0.827 0.893 | 35 35 35 | 57.983 34.693 63.227 | 0.000 0.000 0.000 | 0.936 0.949 0.953 | 0.000 0.000 0.000 |
Table 4 Regression equations of biomass and results of analysis
| Species | Equations | Data statistics | |||||
|---|---|---|---|---|---|---|---|
| Estimation | Prediction | ||||||
| R | N | F | P | R | P | ||
| Nitraria tangutorum ADB BFB TFB TDB | Y1=68.878+0.005 932 X2 Y2=328.636+0.033 781X2 Y3=546.033+0.053 14 X2 Y4=224.909+0.021 18 X2 | 0.868 0.918 0.907 0.909 | 22 22 22 22 | 61.029 107.271 92.606 95.382 | 0.000 0.000 0.000 0.000 | 0.923 0.952 0.983 0.978 | 0.000 0.000 0.000 0.000 |
| Calligonum mongolicum ADB BFB TFB TDB | Y1=-0.371+6.946X1+0.011 95X2 Y2=-11.355+14.768X1+0.022 84X2 Y3=-14.218+19.116X1+0.053 91X2 Y4=-0.865+15.524X1+0.022 34X2 | 0.966 0.929 0.974 0.944 | 21 21 21 21 | 125.341 56.956 164.913 73.749 | 0.000 0.000 0.000 0.000 | 0.993 0.985 0.976 0.994 | 0.000 0.000 0.000 0.000 |
| Haloxylon ammodendron | |||||||
| ADB | Y=501.709+284.065X1+0.24X2 | 0.903 | 22 | 41.885 | 0.000 | 0.917 | 0.000 |
| Agriophyllum squarrosum ADB TFB TDB | Y1= -3.348+20.230X1+0.001 453X2 Y2= -8.422+69.941X1+0.003 591X2 Y3= -3.870+23.298X1+0.001 571X2 | 0.906 0.881 0.904 | 33 33 33 | 69.004 52.199 67.045 | 0.000 0.000 0.000 | 0.954 0.947 0.968 | 0.000 0.000 0.000 |
| Halogeton arachnoideus ADB TFB TDB | Y1= -0.485+3.455X1+0.006 1X2 Y2= -14.031+118.501X1+0.025 6X2 Y3= -0.653+5.179X1+0.006 36X2 | 0.885 0.827 0.893 | 35 35 35 | 57.983 34.693 63.227 | 0.000 0.000 0.000 | 0.936 0.949 0.953 | 0.000 0.000 0.000 |
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