干旱区研究 ›› 2023, Vol. 40 ›› Issue (12): 2043-2052.doi: 10.13866/j.azr.2023.12.16 cstr: 32277.14.j.azr.2023.12.16
• 生态与环境 • 上一篇
张建华1(),张琨1,刘勇2,张红2,张凯权1,周晓阳3,徐龙超3()
收稿日期:
2023-04-14
修回日期:
2023-08-30
出版日期:
2023-12-15
发布日期:
2023-12-18
作者简介:
张建华(1978-),女,博士,副教授,主要从事植物生态学、生态系统物质循环研究. E-mail: 基金资助:
ZHANG Jianhua1(),ZHANG Kun1,LIU Yong2,ZHANG Hong2,ZHANG Kaiquan1,ZHOU Xiaoyang3,XU Longchao3()
Received:
2023-04-14
Revised:
2023-08-30
Published:
2023-12-15
Online:
2023-12-18
摘要:
为了探究煤矿排土场人工林凋落物持水性能对矿区水土保持及生态系统恢复的重要作用,本研究采用野外调查和室内浸提相结合的方法,测定了山西省安太堡露天煤矿排土场4种典型人工林(小叶杨、榆树、油松和刺槐)不同分解阶段凋落物蓄积量、持水率、持水量、吸水速率等持水特性。结果表明:小叶杨和油松凋落物蓄积量显著高于刺槐和榆树(P<0.05);4种人工林不同分解阶段凋落物持水率和持水量与浸水时间均呈极显著对数关系(P<0.01);凋落物吸水速率呈现刺槐>榆树>小叶杨>油松,且吸水速率与浸水时间均存在极显著幂函数关系(P<0.01)。凋落物最大持水量和有效拦蓄量分别为:4.59~8.94 t·hm-2和3.42~7.31 t·hm-2,顺序均为:小叶杨>油松>刺槐>榆树。小叶杨凋落物的持水能力最强,而刺槐凋落物吸水速率最快。因此,优先栽植小叶杨,并与刺槐适当混交,对山西省露天煤矿复垦区水源涵养有积极作用。
张建华, 张琨, 刘勇, 张红, 张凯权, 周晓阳, 徐龙超. 山西省露天煤矿复垦区典型人工林凋落物持水性能研究[J]. 干旱区研究, 2023, 40(12): 2043-2052.
ZHANG Jianhua, ZHANG Kun, LIU Yong, ZHANG Hong, ZHANG Kaiquan, ZHOU Xiaoyang, XU Longchao. Study on water-holding capacity of litters from typical artificial forests in reclaimed regions of the opencast coal mine in Shanxi Province[J]. Arid Zone Research, 2023, 40(12): 2043-2052.
表1
不同类型人工林概况"
林型 | 纬度 | 经度 | 海拔 /m | 人工林类型 | 林龄 /a | 林下优势种 | 平均胸径/cm | 平均树高/m | 密度 /(株·hm-2) | 郁闭度 /% |
---|---|---|---|---|---|---|---|---|---|---|
小叶杨 | 39°29′26.15″N | 112°18′55.30″E | 1469 | 纯林 | 25 | 赖草、早熟禾、阿尔泰狗娃花 | 10.90 | 5.50 | 2133 | 40 |
榆树 | 39°29′28.64″N | 112°18′44.41″E | 1474 | 纯林 | 25 | 兴安胡枝子、早熟禾、阿尔泰狗娃花 | 12.90 | 5.50 | 1100 | 56 |
油松 | 39°29′29.80″N | 112°18′46.49″E | 1471 | 纯林 | 25 | 兴安胡枝子、早熟禾、阿尔泰狗娃花 | 10.70 | 4.70 | 1500 | 75 |
刺槐 | 39°29′33.35″N | 112°18′44.08″E | 1474 | 纯林 | 25 | 角蒿、铁杆蒿、早熟禾 | 9.80 | 4.80 | 2033 | 70 |
表2
不同人工林凋落物厚度与蓄积量"
林型 | 总厚度 /cm | 总蓄积量/(t·hm-2) | 未分解层(U) | 半分解层(S) | |||
---|---|---|---|---|---|---|---|
蓄积量/(t·hm-2) | 比例/% | 蓄积量/(t·hm-2) | 比例/% | ||||
小叶杨 | 2.33±0.44b | 3.53±0.72a | 1.78±0.23a | 53.25±8.13ab | 1.76±0.58ab | 46.75±8.13ab | |
榆树 | 2.60±0.31b | 1.38±0.02b | 0.93±0.03b | 67.26±2.79a | 0.45±0.05b | 32.74±2.79a | |
油松 | 3.60±0.06a | 3.14±0.81ab | 1.07±0.11b | 36.53±4.88b | 2.07±0.09a | 63.47±4.88b | |
刺槐 | 2.70±0.15ab | 1.73±0.24ab | 0.90±0.03b | 53.35±5.63ab | 0.83±0.21ab | 46.65±5.63ab |
表3
凋落物持水量与浸水时间的关系"
人工林类型 | 凋落物层 | 方程 | R2 |
---|---|---|---|
小叶杨 | 半分解层 | W=3.5359+0.2899lnt | 0.9507** |
未分解层 | W=1.3222+0.1070lnt | 0.9564** | |
榆树 | 半分解层 | W=3.6787+0.3759lnt | 0.9739** |
未分解层 | W=2.5010+0.1179lnt | 0.9955** | |
油松 | 半分解层 | W=3.0141+0.4581lnt | 0.9229** |
未分解层 | W=1.8658+0.1959lnt | 0.9691** | |
刺槐 | 半分解层 | W=1.1334+0.2441lnt | 0.9814** |
未分解层 | W=2.0821+0.1668lnt | 0.9650** |
表4
凋落物持水率与浸水时间的关系"
人工林类型 | 凋落物层 | 方程 | R2 |
---|---|---|---|
小叶杨 | 半分解层 | R=210.21+16.506lnt | 0.9760** |
未分解层 | R=290.25+24.142lnt | 0.9959** | |
榆树 | 半分解层 | R=181.71+18.376lnt | 0.9845** |
未分解层 | R=301.38+13.745lnt | 0.9933** | |
油松 | 半分解层 | R=169.70+25.719lnt | 0.9199** |
未分解层 | R=200.68+21.030lnt | 0.9693** | |
刺槐 | 半分解层 | R=106.10+23.170lnt | 0.9812** |
未分解层 | R=231.85+18.470lnt | 0.9689** |
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