生态环境学报 ›› 2026, Vol. 35 ›› Issue (6): 843-855.DOI: 10.16258/j.cnki.1674-5906.2026.06.002
尹延鸽1,2(
), 曹广超1,2,3, 陈宗颜1,2,3, 袁杰1,2,3,*(
), 赵威1,2, 代嘉芳1,2
收稿日期:2025-11-06
修回日期:2026-03-31
接受日期:2026-04-09
出版日期:2026-06-18
发布日期:2026-06-08
通讯作者:
* 袁杰,E-mail: 作者简介:尹延鸽(1998年生),女,硕士研究生,研究方向为地表环境过程与生态响应。E-mail: 15036286399@163.com
基金资助:
YIN Yange1,2(
), CAO Guangchao1,2,3, CHEN Zongyan1,2,3, YUAN Jie1,2,3,*(
), ZHAO Wei1,2, DAI Jiafang1,2
Received:2025-11-06
Revised:2026-03-31
Accepted:2026-04-09
Online:2026-06-18
Published:2026-06-08
摘要:
祁连山是中国西北内陆干旱区重要的生态屏障,其优势树种青海云杉(Picea crassifolia Kom.)林下土壤总有机碳沿海拔梯度的空间分异规律及关键驱动因子尚不明确。该研究旨在揭示上述问题,以深化对区域土壤碳循环过程的理解,并为评估高寒森林土壤碳库对海拔变化的响应能力提供科学依据;以祁连山南坡青海云杉林为研究对象,采用梯度格局法,结合相关性分析与冗余分析,系统解析土壤总有机碳沿海拔及土层的分布特征及其与环境因子的关系。结果表明,青海云杉林土壤总有机碳含量总体随海拔升高呈先增后减趋势,均值变化范围为59.3-99.9 g∙kg−1。各海拔梯度内土壤总有机碳含量随土层加深而递减,0-10 cm土层总有机碳含量和密度均随海拔升高而增加,对海拔响应较显著,其余土层总有机碳含量则呈先增后减趋势。相关性分析和冗余分析表明,土壤总有机碳含量和全氮含量、饱和蓄水量及总孔隙度呈极显著正相关(p<0.01),与容重和土壤相对密度呈极显著负相关(p<0.01);土壤总有机碳密度与海拔呈正相关。研究得出结论:土壤总有机碳空间分异受土壤属性和地形因素的共同调控,土壤全氮、碳氮比、相对密度、海拔、坡度、pH和容重为主要影响因素,其中全氮贡献率最高,且不同土层驱动因子对土壤总有机碳的主导作用存在垂直分异性。
中图分类号:
尹延鸽, 曹广超, 陈宗颜, 袁杰, 赵威, 代嘉芳. 祁连山南坡青海云杉林土壤总有机碳对海拔梯度的响应[J]. 生态环境学报, 2026, 35(6): 843-855.
YIN Yange, CAO Guangchao, CHEN Zongyan, YUAN Jie, ZHAO Wei, DAI Jiafang. Responses of Soil Total Organic Carbon to Elevation Gradient in Pice crassifolia Kom. Forests on the Southern Slope of the Qilian Mountains[J]. Ecology and Environmental Sciences, 2026, 35(6): 843-855.
| 因子 | 土壤深度/cm | 海拔区间/m | |||
|---|---|---|---|---|---|
| 2900-3000(n=20) | 3000-3100(n=40) | 3100-3200(n=65) | 3200-3300(n=35) | ||
| STNC/(g∙kg−1) | 0-10 | 5.63±1.03Ba | 7.31±0.860ABa | 9.12±0.758Aa | 8.90±0.807Aa |
| 10-20 | 4.45±1.46Bab | 6.15±0.673ABab | 7.76±0.900Aab | 7.00±0.816ABab | |
| 20-30 | 3.43±0.553Bab | 5.05±0.622ABabc | 6.77±0.905Aab | 5.65±0.608ABbc | |
| 30-40 | 2.19±0.654Bb | 4.03±0.921ABbc | 5.98±0.981Ab | 4.84±0.922ABbc | |
| 40-50 | 1.85±0.310Ab | 3.67±0.738Ac | 5.27±1.07Ab | 4.06±1.021Ac | |
| SBD/(g∙cm−3) | 0-10 | 0.583±0.0427Ac | 0.452±0.0513Ab | 0.557±0.0389Ac | 0.561±0.0751Ab |
| 10-20 | 0.964±0.131Ab | 0.553±0.0632Bab | 0.700±0.0644ABbc | 0.868±0.0962Aa | |
| 20-30 | 0.923±0.0446Ab | 0.644±0.0783Bab | 0.820±0.0670ABab | 0.864±0.0687ABa | |
| 30-40 | 1.25±0.0782Aa | 0.835±0.149Aa | 0.920±0.109Aab | 1.01±0.0871Aa | |
| 40-50 | 1.33±0.0803Aa | 0.875±0.148Aa | 1.06±0.117Aa | 1.12±0.105Aa | |
| C/N | 0-10 | 15.3±0.576Ac | 16.0±0.625Ab | 14.9±0.364Ab | 15.3±0.800Aa |
| 10-20 | 16.8±2.09ABbc | 18.0±0.379Aab | 14.9±0.450Bb | 14.8±0.697Ba | |
| 20-30 | 17.8±0.699ABabc | 18.2±0.630Aab | 15.7±0.544BCb | 15.5±0.706Ca | |
| 30-40 | 20.8±1.99Aab | 19.9±1.59Aa | 16.2±0.656Aab | 16.5±1.62Aa | |
| 40-50 | 21.5±0.454Aa | 20.4±1.91Aa | 17.8±1.08Aa | 17.5±2.00Aa | |
| Cl/% | 0-10 | 11.4±3.24Aa | 7.29±0.612Ba | 7.10±0.553Ba | 6.19±0.945Ba |
| 10-20 | 9.41±1.98Aa | 7.82±1.04Aa | 7.06±0.408Aa | 7.94±0.721Aa | |
| 20-30 | 9.67±1.40Aa | 7.35±0.812Aa | 7.17±0.543Aa | 7.20±0.368Aa | |
| 30-40 | 9.06±1.69Aa | 6.10±1.36Aa | 7.37±0.577Aa | 7.93±0.597Aa | |
| 40-50 | 9.64±2.45Aa | 7.38±1.20Aa | 7.21±0.430Aa | 7.56±0.632Aa | |
| Si/% | 0-10 | 70.0±4.67Aa | 74.0±2.51Aa | 66.6±3.86Aa | 64.3±5.71Aa |
| 10-20 | 71.6±8.53Aa | 73.6±3.26Aa | 73.8±3.78Aa | 68.7±5.50Aa | |
| 20-30 | 66.9±7.22Aa | 72.5±3.38Aa | 70.1±3.77Aa | 71.1±6.08Aa | |
| 30-40 | 55.5±10.8Aa | 63.2±6.59Aa | 69.8±3.75Aa | 67.8±4.98Aa | |
| 40-50 | 50.0±8.74Ba | 60.9±6.93ABa | 71.2±3.86Aa | 66.2±5.32ABa | |
| Sa/% | 0-10 | 18.6±2.35Aa | 18.7±2.67Aa | 26.3±4.24Aa | 29.5±6.34Aa |
| 10-20 | 18.9±6.73Aa | 18.6±3.47Aa | 19.1±4.05Aa | 23.3±5.60Aa | |
| 20-30 | 23.5±6.40Aa | 20.2±3.16Aa | 22.8±4.12Aa | 21.7±6.08Aa | |
| 30-40 | 35.4±11.0Aa | 30.7±7.00Aa | 22.9±3.92Aa | 24.3±5.15Aa | |
| 40-50 | 40.4±10.2Aa | 31.7±7.42Aa | 21.6±4.09Aa | 26.2±5.43Aa | |
| pH | 0-10 | 7.13±0.392Aa | 7.39±0.100Ab | 7.41±0.0703Aa | 7.00±0.255Aa |
| 10-20 | 7.11±0.575Aa | 7.57±0.159Aab | 7.20±0.244Aa | 7.28±0.297Aa | |
| 20-30 | 7.18±0.737Aa | 7.73±0.125Aab | 7.46±0.0546Aa | 7.29±0.330Aa | |
| 30-40 | 7.21±0.679Aa | 7.76±0.138Aab | 7.48±0.0443Aa | 7.32±0.332Aa | |
| 40-50 | 7.83±0.552Aa | 7.81±0.128Aa | 7.50±0.0781Aa | 7.41±0.326Aa | |
| TND/(kg∙m−2) | 0-10 | 0.320±0.0371Aa | 0.334±0.0660Aa | 0.454±0.0282Aa | 0.473±0.0410Aa |
| 10-20 | 0.391±0.0853Ba | 0.329±0.0529Ba | 0.454±0.0282ABa | 0.576±0.0330Aa | |
| 20-30 | 0.319±0.0573Ba | 0.303±0.0300Ba | 0.449±0.0282Aa | 0.474±0.0353Aa | |
| 30-40 | 0.264±0.0641Ba | 0.264±0.0407Ba | 0.433±0.0358Aa | 0.460±0.0616Aa | |
| 40-50 | 0.243±0.0342Ba | 0.269±0.0401ABa | 0.420±0.0350Aa | 0.416±0.0782Aa | |
| SWS/mm | 0-10 | 17.0±2.76Aa | 21.3±2.72Aa | 24.0±3.70Aa | 16.1±3.18Aa |
| 10-20 | 17.6±3.73Aa | 25.4±3.17Aa | 27.9±3.57Aa | 18.2±1.43Aa | |
| 20-30 | 18.3±1.06Aa | 25.1±2.76Aa | 26.9±3.04Aa | 17.5±1.85Aa | |
| 30-40 | 19.9±0.994Aa | 31.8±6.31Aa | 26.9±2.48Aa | 19.5±2.10Aa | |
| 40-50 | 18.6±2.24Aa | 25.5±4.29Aa | 28.4±2.66Aa | 20.3±2.87Aa | |
| SM/mm | 0-10 | 74.7±1.41Aa | 79.1±1.69Aa | 75.6±1.28Aa | 75.5±2.48Aa |
| 10-20 | 62.2±4.32Bb | 75.7±2.08Aab | 70.9±2.12ABab | 65.3±3.17Bb | |
| 20-30 | 63.5±1.47Bb | 72.7±2.58Aab | 66.9±2.21ABbc | 65.5±2.27ABb | |
| 30-40 | 52.6±2.58 Ac | 66.4±4.91Ab | 63.6±3.58Abc | 60.6±2.87Ab | |
| 40-50 | 50.1±2.65Ac | 65.1±4.89Ab | 59.5±3.78Ac | 56.9±3.47Ab | |
| SP/% | 0-10 | 74.7±1.41Aa | 79.0±1.69Aa | 75.6±1.28Aa | 75.5±2.48Aa |
| 10-20 | 62.2±4.32 Bb | 75.7±2.08Aab | 70.8±2.12ABab | 65.3±3.17Bb | |
| 20-30 | 63.5±1.47Bb | 72.7±2.58Aab | 66.9±2.21ABbc | 65.4±2.27ABb | |
| 30-40 | 52.6±2.58Ac | 66.4±4.92Ab | 63.6±3.58Abc | 60.6±2.87Ab | |
| 40-50 | 50.1±2.65Ac | 65.1±4.89Ab | 59.1±3.86Ac | 56.9±3.47Ab | |
| SG | 0-10 | 2.30±0.0379Ac | 2.11±0.0751Ac | 2.26±0.0409Ac | 2.24±0.0816Aa |
| 10-20 | 2.53±0.0593Ab | 2.24±0.0658Bbc | 2.36±0.0520ABbc | 2.48±0.0451Ab | |
| 20-30 | 2.53±0.0203Ab | 2.31±0.0689Babc | 2.44±0.0497ABab | 2.49±0.0373ABb | |
| 30-40 | 2.64±0.0208Aab | 2.42±0.0617Bab | 2.47±0.0565ABab | 2.55±0.0401ABb | |
| 40-50 | 2.66±0.0200Aa | 2.45±0.0610Ba | 2.55±0.0421ABa | 2.59±0.0308ABb | |
表1 不同海拔梯度不同土层土壤环境因子相关指标
Table 1 Relevant indicators of soil environmental factors at different altitude gradients and different soil layers
| 因子 | 土壤深度/cm | 海拔区间/m | |||
|---|---|---|---|---|---|
| 2900-3000(n=20) | 3000-3100(n=40) | 3100-3200(n=65) | 3200-3300(n=35) | ||
| STNC/(g∙kg−1) | 0-10 | 5.63±1.03Ba | 7.31±0.860ABa | 9.12±0.758Aa | 8.90±0.807Aa |
| 10-20 | 4.45±1.46Bab | 6.15±0.673ABab | 7.76±0.900Aab | 7.00±0.816ABab | |
| 20-30 | 3.43±0.553Bab | 5.05±0.622ABabc | 6.77±0.905Aab | 5.65±0.608ABbc | |
| 30-40 | 2.19±0.654Bb | 4.03±0.921ABbc | 5.98±0.981Ab | 4.84±0.922ABbc | |
| 40-50 | 1.85±0.310Ab | 3.67±0.738Ac | 5.27±1.07Ab | 4.06±1.021Ac | |
| SBD/(g∙cm−3) | 0-10 | 0.583±0.0427Ac | 0.452±0.0513Ab | 0.557±0.0389Ac | 0.561±0.0751Ab |
| 10-20 | 0.964±0.131Ab | 0.553±0.0632Bab | 0.700±0.0644ABbc | 0.868±0.0962Aa | |
| 20-30 | 0.923±0.0446Ab | 0.644±0.0783Bab | 0.820±0.0670ABab | 0.864±0.0687ABa | |
| 30-40 | 1.25±0.0782Aa | 0.835±0.149Aa | 0.920±0.109Aab | 1.01±0.0871Aa | |
| 40-50 | 1.33±0.0803Aa | 0.875±0.148Aa | 1.06±0.117Aa | 1.12±0.105Aa | |
| C/N | 0-10 | 15.3±0.576Ac | 16.0±0.625Ab | 14.9±0.364Ab | 15.3±0.800Aa |
| 10-20 | 16.8±2.09ABbc | 18.0±0.379Aab | 14.9±0.450Bb | 14.8±0.697Ba | |
| 20-30 | 17.8±0.699ABabc | 18.2±0.630Aab | 15.7±0.544BCb | 15.5±0.706Ca | |
| 30-40 | 20.8±1.99Aab | 19.9±1.59Aa | 16.2±0.656Aab | 16.5±1.62Aa | |
| 40-50 | 21.5±0.454Aa | 20.4±1.91Aa | 17.8±1.08Aa | 17.5±2.00Aa | |
| Cl/% | 0-10 | 11.4±3.24Aa | 7.29±0.612Ba | 7.10±0.553Ba | 6.19±0.945Ba |
| 10-20 | 9.41±1.98Aa | 7.82±1.04Aa | 7.06±0.408Aa | 7.94±0.721Aa | |
| 20-30 | 9.67±1.40Aa | 7.35±0.812Aa | 7.17±0.543Aa | 7.20±0.368Aa | |
| 30-40 | 9.06±1.69Aa | 6.10±1.36Aa | 7.37±0.577Aa | 7.93±0.597Aa | |
| 40-50 | 9.64±2.45Aa | 7.38±1.20Aa | 7.21±0.430Aa | 7.56±0.632Aa | |
| Si/% | 0-10 | 70.0±4.67Aa | 74.0±2.51Aa | 66.6±3.86Aa | 64.3±5.71Aa |
| 10-20 | 71.6±8.53Aa | 73.6±3.26Aa | 73.8±3.78Aa | 68.7±5.50Aa | |
| 20-30 | 66.9±7.22Aa | 72.5±3.38Aa | 70.1±3.77Aa | 71.1±6.08Aa | |
| 30-40 | 55.5±10.8Aa | 63.2±6.59Aa | 69.8±3.75Aa | 67.8±4.98Aa | |
| 40-50 | 50.0±8.74Ba | 60.9±6.93ABa | 71.2±3.86Aa | 66.2±5.32ABa | |
| Sa/% | 0-10 | 18.6±2.35Aa | 18.7±2.67Aa | 26.3±4.24Aa | 29.5±6.34Aa |
| 10-20 | 18.9±6.73Aa | 18.6±3.47Aa | 19.1±4.05Aa | 23.3±5.60Aa | |
| 20-30 | 23.5±6.40Aa | 20.2±3.16Aa | 22.8±4.12Aa | 21.7±6.08Aa | |
| 30-40 | 35.4±11.0Aa | 30.7±7.00Aa | 22.9±3.92Aa | 24.3±5.15Aa | |
| 40-50 | 40.4±10.2Aa | 31.7±7.42Aa | 21.6±4.09Aa | 26.2±5.43Aa | |
| pH | 0-10 | 7.13±0.392Aa | 7.39±0.100Ab | 7.41±0.0703Aa | 7.00±0.255Aa |
| 10-20 | 7.11±0.575Aa | 7.57±0.159Aab | 7.20±0.244Aa | 7.28±0.297Aa | |
| 20-30 | 7.18±0.737Aa | 7.73±0.125Aab | 7.46±0.0546Aa | 7.29±0.330Aa | |
| 30-40 | 7.21±0.679Aa | 7.76±0.138Aab | 7.48±0.0443Aa | 7.32±0.332Aa | |
| 40-50 | 7.83±0.552Aa | 7.81±0.128Aa | 7.50±0.0781Aa | 7.41±0.326Aa | |
| TND/(kg∙m−2) | 0-10 | 0.320±0.0371Aa | 0.334±0.0660Aa | 0.454±0.0282Aa | 0.473±0.0410Aa |
| 10-20 | 0.391±0.0853Ba | 0.329±0.0529Ba | 0.454±0.0282ABa | 0.576±0.0330Aa | |
| 20-30 | 0.319±0.0573Ba | 0.303±0.0300Ba | 0.449±0.0282Aa | 0.474±0.0353Aa | |
| 30-40 | 0.264±0.0641Ba | 0.264±0.0407Ba | 0.433±0.0358Aa | 0.460±0.0616Aa | |
| 40-50 | 0.243±0.0342Ba | 0.269±0.0401ABa | 0.420±0.0350Aa | 0.416±0.0782Aa | |
| SWS/mm | 0-10 | 17.0±2.76Aa | 21.3±2.72Aa | 24.0±3.70Aa | 16.1±3.18Aa |
| 10-20 | 17.6±3.73Aa | 25.4±3.17Aa | 27.9±3.57Aa | 18.2±1.43Aa | |
| 20-30 | 18.3±1.06Aa | 25.1±2.76Aa | 26.9±3.04Aa | 17.5±1.85Aa | |
| 30-40 | 19.9±0.994Aa | 31.8±6.31Aa | 26.9±2.48Aa | 19.5±2.10Aa | |
| 40-50 | 18.6±2.24Aa | 25.5±4.29Aa | 28.4±2.66Aa | 20.3±2.87Aa | |
| SM/mm | 0-10 | 74.7±1.41Aa | 79.1±1.69Aa | 75.6±1.28Aa | 75.5±2.48Aa |
| 10-20 | 62.2±4.32Bb | 75.7±2.08Aab | 70.9±2.12ABab | 65.3±3.17Bb | |
| 20-30 | 63.5±1.47Bb | 72.7±2.58Aab | 66.9±2.21ABbc | 65.5±2.27ABb | |
| 30-40 | 52.6±2.58 Ac | 66.4±4.91Ab | 63.6±3.58Abc | 60.6±2.87Ab | |
| 40-50 | 50.1±2.65Ac | 65.1±4.89Ab | 59.5±3.78Ac | 56.9±3.47Ab | |
| SP/% | 0-10 | 74.7±1.41Aa | 79.0±1.69Aa | 75.6±1.28Aa | 75.5±2.48Aa |
| 10-20 | 62.2±4.32 Bb | 75.7±2.08Aab | 70.8±2.12ABab | 65.3±3.17Bb | |
| 20-30 | 63.5±1.47Bb | 72.7±2.58Aab | 66.9±2.21ABbc | 65.4±2.27ABb | |
| 30-40 | 52.6±2.58Ac | 66.4±4.92Ab | 63.6±3.58Abc | 60.6±2.87Ab | |
| 40-50 | 50.1±2.65Ac | 65.1±4.89Ab | 59.1±3.86Ac | 56.9±3.47Ab | |
| SG | 0-10 | 2.30±0.0379Ac | 2.11±0.0751Ac | 2.26±0.0409Ac | 2.24±0.0816Aa |
| 10-20 | 2.53±0.0593Ab | 2.24±0.0658Bbc | 2.36±0.0520ABbc | 2.48±0.0451Ab | |
| 20-30 | 2.53±0.0203Ab | 2.31±0.0689Babc | 2.44±0.0497ABab | 2.49±0.0373ABb | |
| 30-40 | 2.64±0.0208Aab | 2.42±0.0617Bab | 2.47±0.0565ABab | 2.55±0.0401ABb | |
| 40-50 | 2.66±0.0200Aa | 2.45±0.0610Ba | 2.55±0.0421ABa | 2.59±0.0308ABb | |
| 土壤深度/ cm | 海拔区间/m | ||||
|---|---|---|---|---|---|
| 2900- 3000 (n=20) | 3000-3100(n=40) | 3100-3200(n=65) | 3200- 3300 (n=35) | ||
| 土壤总有机碳质量分数/ (g∙kg−1) | 0-10 | 85.3±22.5a | 114±27.9a | 129±31.9a | 143±41.4a |
| 10-20 | 69.2±29.8ab | 109±31.1a | 105±31.5ab | 103±32.1b | |
| 20-30 | 60.7±15.5ab | 89.5±26.2ab | 93.6±29.9b | 84.1±21.9bc | |
| 30-40 | 42.8±15.9b | 73.6±41.3b | 84.8±27.1b | 72.8±31.4bc | |
| 40-50 | 39.8±12.5b | 70.1±36.9b | 83.3±27.6b | 61.9±35.7c | |
| 土壤总有机碳密度/ (kg∙m−2) | 0-10 | 4.87±0.730a | 5.07±2.13a | 6.64±1.22a | 7.02±0.810a |
| 10-20 | 6.22±1.34a | 5.84±2.43a | 6.70±1.67a | 8.40±1.66a | |
| 20-30 | 5.63±1.58a | 5.41±1.45a | 7.89±2.35a | 7.40±0.830a | |
| 30-40 | 5.24±1.45a | 4.98±1.75a | 7.48±2.14a | 7.29±1.52a | |
| 40-50 | 5.25±1.42a | 5.19±1.83a | 7.95±2.29a | 6.65±2.44a | |
表2 土壤总有机碳质量分数和总有机碳密度不同土层分布特征
Table 2 Vertical distribution patterns of soil total organic carbon content and density across soil layers
| 土壤深度/ cm | 海拔区间/m | ||||
|---|---|---|---|---|---|
| 2900- 3000 (n=20) | 3000-3100(n=40) | 3100-3200(n=65) | 3200- 3300 (n=35) | ||
| 土壤总有机碳质量分数/ (g∙kg−1) | 0-10 | 85.3±22.5a | 114±27.9a | 129±31.9a | 143±41.4a |
| 10-20 | 69.2±29.8ab | 109±31.1a | 105±31.5ab | 103±32.1b | |
| 20-30 | 60.7±15.5ab | 89.5±26.2ab | 93.6±29.9b | 84.1±21.9bc | |
| 30-40 | 42.8±15.9b | 73.6±41.3b | 84.8±27.1b | 72.8±31.4bc | |
| 40-50 | 39.8±12.5b | 70.1±36.9b | 83.3±27.6b | 61.9±35.7c | |
| 土壤总有机碳密度/ (kg∙m−2) | 0-10 | 4.87±0.730a | 5.07±2.13a | 6.64±1.22a | 7.02±0.810a |
| 10-20 | 6.22±1.34a | 5.84±2.43a | 6.70±1.67a | 8.40±1.66a | |
| 20-30 | 5.63±1.58a | 5.41±1.45a | 7.89±2.35a | 7.40±0.830a | |
| 30-40 | 5.24±1.45a | 4.98±1.75a | 7.48±2.14a | 7.29±1.52a | |
| 40-50 | 5.25±1.42a | 5.19±1.83a | 7.95±2.29a | 6.65±2.44a | |
图1 土壤总有机碳质量分数及密度沿海拔梯度分布特征 箱体表示四分位距(IQR),箱内横线表示中位数,■和▲表示均值;须线延伸至1.5倍IQR范围内的最远数据点,线帽标记须线的端点;点(◆)表示异常值。不同小写字母表示不同海拔梯度间差异显著(p<0.05)。图2、图3的图注同上
Figure 1 Variation in soil total organic carbon mass fraction and density along the altitudinal gradient
图2 不同土层土壤总有机碳质量分数沿海拔梯度分布特征
Figure 2 Distribution characteristics of soil total organic carbon mass fraction in different soil layers along the altitudinal gradient
图4 青海云杉林土壤总有机碳与环境因子的相关性 *表示在0.05水平呈显著相关性(p<0.05);**表示在0.01水平呈极显著相关性(p<0.01);***表示在0.001水平呈极显著相关性(p<0.001);STOC:土壤总有机碳含量,STOCD:土壤总有机碳密度
Figure 4 Correlation between soil total organic carbon and environmental factors of P. crassifolia forests
图5 不同土层深度土壤总有机碳含量及密度与影响因子的冗余分析(RDA) 黑色箭头表示响应变量;绿色箭头表示解释变量
Figure 5 Redundancy analysis (RDA) of soil total organic carbon content and density with influencing factors at different soil depths
| [1] |
DIXON R K, SOLOMON A M, BROWN S, et al., 1994. Carbon pools and flux of global forest ecosystems[J]. Science, 263(5144): 185-190.
DOI PMID |
| [2] |
FU C, CHEN Z, WANG G Q, et al., 2021. A comprehensive framework for evaluating the impact of land use change and management on soil organic carbon stocks in global drylands[J]. Current Opinion in Environmental Sustainability, 48: 103-109.
DOI URL |
| [3] |
GAO G L, FENG Q, XU E W, et al., 2025. Carbon dioxide and water exchanges of a Qinghai spruce forest ecosystem in the Qilian Mountains in Northwestern China[J]. Journal of Hydrology, 662(Part B): 133987.
DOI URL |
| [4] |
MA H H, PENG M, YANG Z, et al., 2024. Spatial distribution and driving factors of soil organic carbon in the Northeast China Plain: Insights from latest monitoring data[J]. Science of the Total Environment, 911: 168602.
DOI URL |
| [5] | MUKHTAR H, YANG Y, XU M, et al., 2025. Elevation‐dependent vegetation greening and its responses to climate changes in the south slope of the Himalayas[J]. Geophysical Research Letters, 52(4): e2024GL113276. |
| [6] |
SCHLESINGER W H, 1990. Evidence from chronosequence studies for a low carbon-storage potential of soils[J]. Nature, 348(6298): 232-234.
DOI |
| [7] |
SHANGGUAN Y Y, ZHAO H, ZHANG Z Z, et al., 2025. Carbon storage and sequestration of five planting patterns of Picea crassifolia plantations in Qilian Mountains[J]. Frontiers in Earth Science, 13: 1560899.
DOI URL |
| [8] |
WU J J, JIAO L, ZHU X L, et al., 2024. Different resource allocation strategies of two dominant conifer species to the heterogeneous environments in the Qinghai-Tibet Plateau[J]. Forest Ecology and Management, 563: 121986.
DOI URL |
| [9] |
蔡文良, 谢艳云, 唐雯, 2019. 海南尖峰岭热带山地雨林土壤有机碳储量和垂直分布特征[J]. 生态环境学报, 28(8): 1514-1521.
DOI |
| CAI W L, XIE Y Y, TANG W, 2019. Vertical distribution of soil organic carbon storage of tropical mountain rainforest in Jianfengling, Hainan[J]. Ecology and Environmental Sciences, 28(8): 1514-1521. | |
| [10] | 曹小玉, 李际平, 闫文德, 2014. 不同龄组杉木林土壤有机碳与氮磷钾分布特征及耦合关系[J]. 土壤通报, 45(5): 1137-1143. |
| CAO X Y, LI J P, YAN W D, 2014. Variation of contents of Soil Organic Carbon, N, P and K and their coupling relationships in different age groups of Chinese fir plantations[J]. Chinese Journal of Soil Science, 45(5): 1137-1143. | |
| [11] |
车宗玺, 高承兵, 车宗桓, 等, 2025. 祁连山青海云杉 (Picea crassifolia) 林水源涵养功能空间特征[J]. 中国沙漠, 45(5): 301-307.
DOI |
| CHE Z X, GAO C B, CHE Z H, et al., 2025. Characteristics of water conservation function of Picea crassifolia forest in the Qilian Mountains[J]. Journal of Desert Research, 45(5): 301-307. | |
| [12] | 冯金元, 蒋志成, 蒋志仁, 等, 2025. 祁连山中段青海云杉林土壤有机碳分布特征及影响因素[J]. 水土保持通报, 45(3): 261-267, 277. |
| FENG J Y, JIANG Z C, JIANG Z R, et al., 2025. Characteristics and influencing factors of soil organic carbon at Picea crassifolia forests in middle part of Qilian Mountains[J]. Bulletin of Soil and Water Conservation, 45(3): 261-267, 277. | |
| [13] |
冯宜明, 吕春燕, 王零, 等, 2023. 不同林分密度青海云杉林碳氮储量及其分配格局[J]. 干旱区地理, 46(7): 1133-1144.
DOI |
| FENG Y M, LÜ C Y, WANG L, et al., 2023. Carbon and nitrogen storage and allocation patterns of Picea crassifolia forest with different stand density[J]. Arid Land Geography, 46(7): 1133-1144. | |
| [14] |
付建新, 曹广超, 郭文炯, 2021. 祁连山国家公园青海片区山水林田湖草的时空分异[J]. 应用生态学报, 32(8): 2866-2874.
DOI |
| FU J X, CAO G C, GUO W J, et al., 2021. Spatial-temporal differentiation of mountain-water-forest-farmland-lake-grass system in Qinghai area of the Qilian Mountain National Park, China[J]. Chinese Journal of Applied Ecology, 32(8): 2866-2874. | |
| [15] |
高海宁, 李彩霞, 孙小妹, 等, 2021. 祁连山北麓不同海拔土壤化学计量特征[J]. 中国沙漠, 41(1): 219-227.
DOI |
|
GAO H N, LI C X, SUN X M, et al., 2021. Stoichiometry characteristics of soil at different altitudes in the Qilian Mountains[J]. Journal of Desert Research, 41(1): 219-227.
DOI |
|
| [16] | 韩春兰, 付小梅, 余无忌, 等, 2016. 火山喷出物发育土壤的比重及颗粒组成测定[J]. 土壤通报, 47(5): 1097-1101. |
| HAN C L, FU X M, YU W J, et al., 2016. Determination on specific gravity and particle composition of soil developed from volcanic ejecta[J]. Chinese Journal of Soil Science, 47(5): 1097-1101. | |
| [17] | 李铭杰, 牛保亮, 陈志成, 等, 2025. 树种多样性对宝天曼天然栎林土壤有机碳的影响[J]. 生态学报, 45(21): 1-11. |
| LI M J, NIU B L, CHEN Z C, et al., 2025. Effects of tree species diversity on soil organic carbon in natural forests of Quercus aliena var. acuteserrata in Baotianman[J]. Acta Ecologica Sinica, 45(21): 1-11. | |
| [18] | 李霞, 朱万泽, 舒树淼, 等, 2021. 基于主成分分析的大渡河中游干暖河谷草地土壤质量评价[J]. 生态学报, 41(10): 3891-3900. |
| LI X, ZHU W Z, SHU S M, et al., 2021. Soil quality assessment of grassland in dry and warm valley of Dadu River based on principal component analysis[J]. Acta Ecologica Sinica, 41(10): 3891-3900. | |
| [19] | 李晓燕, 2025. 2000-2022年祁连山南坡蒸散量时空分异特征及驱动力研究[D]. 西宁: 青海师范大学. |
| LI X Y, 2025. Spatiotemporal differentiation characteristics and driving forces of evapotranspiration on the southern slope of the Qilian Mountains from 2000 to 2022[D]. Xining: Qinghai Normal University. | |
| [20] | 刘宝迪, 白其格那, 赵利清, 等, 2025. 昆仑山不同海拔土壤养分及生态化学计量特征[J]. 生态学报, 45(16): 1-12. |
| LIU B D, BAI Q G N, ZHAO L Q, et al., 2025. Soil nutrients and ecological stoichiometric characteristics at different altitudes in the Kunlun Mountains[J]. Acta Ecologica Sinica, 45(16): 7995-8006. | |
| [21] | 刘建泉, 李进军, 邸华, 2017. 祁连山森林植被净生产量、碳储量和碳汇功能估算[J]. 西北林学院学报, 32(2): 1-7. |
| LIU J Q, LI J J, DI H, 2017. Estimation of forest vegetation net production, carbon storage and carbon sink function in Qilian Mountations[J]. Journal of Northwest Forestry University, 32(2): 1-7. | |
| [22] | 刘潘伟, 高鹏, 刘晓华, 等, 2018. 大岗山流域土壤碳氮要素空间分布特征及影响因素[J]. 中国水土保持科学, 16(2): 73-79. |
| LIU P W, GAO P, LIU X H, et al., 2018. Spatial distribution and influential factors of soil carbon and nitrogen in Dagangshan Watershed[J]. Science of Soil and Water Conservation, 16(2): 73-79. | |
| [23] | 牛赟, 刘贤德, 王立, 等, 2014. 祁连山大野口流域青海云杉林分结构及其土壤水热特征分析[J]. 生态环境学报, 23(3): 385-391. |
| NIU Y, LIU X D, WANG L, et al., 2014. Feature analysis on stand structure of Picea crassifolia and its water and temperature of soil in Dayekou basin of Qilian Mountains[J]. Ecology and Environmental Sciences, 23(3): 385-391. | |
| [24] | 裴薇薇, 杨喆, 王云英, 等, 2024. 祁连山区青海云杉林碳汇特征及调控因子[J]. 中国农业科技导报, 26(1): 226-233. |
| PEI W W, YANG Z, WANG Y Y, et al., 2024. Carbon sink characteristics and regulatory factors of Picea crassifolia forests in the Qilian Mountains[J]. Journal of Agricultural Science and Technology, 26(1): 226-233. | |
| [25] | 王会利, 王绍能, 宋贤冲, 等, 2018. 广西猫儿山水青冈林土壤剖面有机碳垂直分布特征及影响因素[J]. 中南林业科技大学学报, 38(11): 89-94, 122. |
| WANG H L, WANG S N, SONG X C, et al., 2018. Vertical distribution of soil organic carbon and its influence factors of Fagus longipetiolata forest in Mao’ermountain, Guangxi[J]. Journal of Central South University of Forestry & Technology, 38(11): 89-94, 122. | |
| [26] | 王健祺, 李发东, 李俊峰, 等, 2025. 天山北坡玛纳斯河流域土壤有机碳分布特征与影响因素[J]. 中国生态农业学报, 33(3): 449-461. |
| WANG J Q, LI F D, LI J F, et al., 2025. Distribution characteristics and influencing factors of soil organic carbon in the Manas River Basin on the northern slope of Tianshan Mountain[J]. Chinese Journal of Eco-Agriculture, 33(3): 449-461. | |
| [27] | 王艳丽, 字洪标, 程瑞希, 等, 2019. 青海省森林土壤有机碳氮储量及其垂直分布特征[J]. 生态学报, 39(11): 4096-4105. |
| WANG Y L, ZI H B, CHENG R X, et al., 2019. Forest soil organic carbon and nitrogen storage and characteristics of vertical distribution in Qinghai Province[J]. Acta Ecologica Sinica, 39(11): 4096-4105. | |
| [28] | 吴振云, 李进军, 李娜, 等, 2020. 祁连山青海云杉林生长状况及固碳潜力空间分异研究[J]. 兰州大学学报(自然科学版), 56(6): 749-754. |
| WU Z Y, LI J J, LI N, et al., 2020. Growth status of Picea crassifolia forest and its potential distribution of biomass C stock in Qilian Mountains, northwestern China[J]. Journal of Lanzhou University: Natural Sciences, 56(6): 749-754. | |
| [29] | 咸庆玲, 曹广超, 袁杰, 等, 2025. 祁连山南坡典型流域坡面尺度土壤有机碳变化特征及影响因素研究[J]. 水土保持研究, 32(6): 29-37. |
| XIAN Q L, CAO G C, YUAN J, et al., 2025. Study on variation characteristics and influencing factors of soil organic carbon at slope scale in typical watersheds on southern slope of Qilian Mountains[J]. Research of Soil and Water Conservation, 32(6): 29-37. | |
| [30] | 杨荣荣, 曹广超, 曹生奎, 等, 2020. 祁连山南坡表层土壤有机质含量反演[J]. 生态科学, 39(5): 57-63. |
| YANG R R, CAO G C, CAO S K, et al., 2020. The surface soil organic matter content inversion on the south slope of Qilian Mountains[J]. Ecological Science, 39(5): 57-63. | |
| [31] |
尤海舟, 毕君, 王超, 等, 2018. 河北小五台山不同海拔白桦林土壤有机碳密度分布特征及影响因素[J]. 生态环境学报, 27(3): 432-437.
DOI |
| YOU H Z, BI J, WANG C, et al., 2018. Altitudinal distribution rule of Betula platyphylla forest’s soil organic carbon density and its influencing factors in Xiaowutai Mountain in Hebei[J]. Ecology and Environmental Sciences, 27(3): 432-437. | |
| [32] | 袁杰, 曹广超, 曹生奎, 等, 2017. 祁连山南坡不同植被类型枯落物及其土壤持水特性分析[J]. 生态科学, 37(5): 180-190. |
| YUAN J, CAO G C, CAO S K, et al., 2017. Analysis on litterfall and soil water retention properties of different vegetation types on the south slope of Qilian Mountains[J]. Ecological Science, 37(5): 180-190. | |
| [33] | 曾立雄, 雷蕾, 王晓荣, 等, 2018. 海拔梯度对祁连山青海云杉林乔木层和土壤层碳密度的影响[J]. 生态学报, 38(20): 7168-7177. |
| ZENG L X, LEI L, WANG X R, et al., 2018. Effect of altitudinal variation on carbon density in arbor layer and soil layer of Picea crassifolia forest in Qilian Mountains[J]. Acta Ecologica Sinica, 38(20): 7168-7177. | |
| [34] | 赵盼盼, 周嘉聪, 林开淼, 等, 2019. 不同海拔对福建戴云山黄山松林土壤微生物生物量和土壤酶活性的影响[J]. 生态学报, 39(8): 2676-2686. |
| ZHAO P P, ZHOU J C, LIN K M, et al., 2019. Effects of different altitudes on soil microbial biomass and enzyme activities in Pinus taiwanensis forests on Daiyun Mountain, Fujian Province[J]. Acta Ecologica Sinica, 39(8): 2676-2686. | |
| [35] | 赵青, 刘爽, 陈凯, 等, 2021. 武夷山自然保护区不同海拔甜槠天然林土壤有机碳变化特征及影响因素[J]. 生态学报, 41(13): 5328-5339. |
| ZHAO Q, LIU S, CHEN K, et al., 2021. Change characteristics and influencing factors of soil organic carbon in Castanopsis eyrei natural forests at different altitudes in Wuyishan Nature Reserve[J]. Acta Ecologica Sinica, 41(13): 5328-5339. | |
| [36] | 赵维俊, 许尔文, 牛赟, 等, 2025. 祁连山典型流域青海云杉林林分空间结构对林下更新的影响[J]. 中南林业科技大学学报, 45(1): 1-7. |
| ZHAO W J, XU E W, NIU Y, et al., 2025. Effects of spatial structure of Picea crassifolia stand on undergrowth regeneration of a typical watershed in the Qilian mountains, China[J]. Journal of Central South University of Forestry & Technology, 45(1): 1-7. |
| [1] | 徐茂宏. 暖温带森林土壤微生物α多样性海拔梯度格局及其影响因素[J]. 生态环境学报, 2025, 34(5): 678-687. |
| [2] | 唐建亭, 袁杰, 陈宗颜, 李晓燕, 孙子婷. 祁连山南坡土地利用变化及碳储量研究[J]. 生态环境学报, 2024, 33(9): 1353-1361. |
| [3] | 关玉亮, 甘先华, 殷祚云, 黄钰辉, 陶玉柱, 李宽, 张卫强, 邓彩琼, 曾祥尧, 黄芳芳. 南岭自然保护区不同海拔梯度植物多样性分布格局[J]. 生态环境学报, 2024, 33(6): 877-887. |
| [4] | 李佳婧, 梁咏亮, 李静尧, 李小伟, 杨君珑. 基于叶片功能性状的贺兰山西坡植物生态策略分析[J]. 生态环境学报, 2024, 33(1): 45-53. |
| [5] | 房园, 梁中, 张毓涛, 师庆东, 孙雪娇, 李吉玫, 李翔, 董振涛. 天山云杉森林生态系统的水源涵养能力海拔梯度变化特征[J]. 生态环境学报, 2023, 32(9): 1574-1584. |
| [6] | 秦浩, 李蒙爱, 高劲, 陈凯龙, 张殷波, 张峰. 芦芽山不同海拔灌丛土壤细菌群落组成和多样性研究[J]. 生态环境学报, 2023, 32(3): 459-468. |
| [7] | 王小娜, 徐当会, 王谢军, 方向文. 祁连山灌丛群落结构特征随海拔梯度和经度的变化[J]. 生态环境学报, 2022, 31(2): 231-238. |
| [8] | 蔡锡安, 黄娟, 吴彤, 刘菊秀, 蒋芬, 王森浩. 植物叶片排放甲烷的初步研究[J]. 生态环境学报, 2021, 30(9): 1842-1847. |
| [9] | 闫东锋, 张妍妍, 吕康婷, 周梦丽, 王婷, 赵宁. 太行山南麓不同海拔梯度天然林优势树种生态位特征[J]. 生态环境学报, 2021, 30(8): 1571-1580. |
| [10] | 何斌, 李青, 陈群利, 李望军, 游萍. 黔西北黄杉群落物种多样性的海拔梯度格局[J]. 生态环境学报, 2021, 30(6): 1111-1120. |
| [11] | 张莎莎, 李爱琴, 王会荣, 王晶晶, 徐小牛. 不同海拔杉木人工林土壤碳氮磷生态化学计量特征[J]. 生态环境学报, 2020, 29(1): 97-104. |
| 阅读次数 | ||||||
|
全文 |
|
|||||
|
摘要 |
|
|||||