生物多样性 ›› 2022, Vol. 30 ›› Issue (11): 22093. DOI: 10.17520/biods.2022093
高洁1, 李德浩1, 姜海波1,*(), 邓光怡1, 张超凡2, 何春光1,*(), 孙鹏3
收稿日期:
2022-02-26
接受日期:
2022-06-16
出版日期:
2022-11-20
发布日期:
2022-09-29
通讯作者:
姜海波,何春光
作者简介:
he-cg@nenu.edu.cn基金资助:
Jie Gao1, Dehao Li1, Haibo Jiang1,*(), Guangyi Deng1, Chaofan Zhang2, Chunguang He1,*(), Peng Sun3
Received:
2022-02-26
Accepted:
2022-06-16
Online:
2022-11-20
Published:
2022-09-29
Contact:
Haibo Jiang,Chunguang He
摘要:
白鹤(Grus leucogeranus)为IUCN红色名录极危物种, 在中转停歇地松嫩平原的停歇生境为湿地, 近年来却出现多数个体迁离湿地转移到玉米(Zea mays)地取食停歇的现象。为探究迁徙白鹤在中转停歇地取食生境利用变化的原因, 我们于2020年9月至2021年11月对该区域白鹤种群数量和取食生境等进行观测, 并对食物资源量进行了分析。结果表明: (1)在农田生境取食的白鹤个体数量占比达72.7%, 是湿地生境的2.66倍。农田已成为迁徙白鹤在中转停歇地的主要取食生境之一。(2)根据不同的收割方式, 农田可提供的总能量是湿地的1.24-2.79倍; 白鹤在农田的日摄入能量约为湿地的1.56倍。(3)在农田白鹤的每日取食时间约占总活动时长的53.5%, 是湿地的1.67倍, 取食成功率是湿地的1.56倍。白鹤取食生境利用变化的主要原因可能是由于水位变化、食物资源变化、取食难易度不同和人为干扰等综合作用导致。为有效保护和管理白鹤生境, 建议合理进行湿地生态补水调控并恢复白鹤主要食源植物, 开展农业用地保护计划并设置自然保护小区。
高洁, 李德浩, 姜海波, 邓光怡, 张超凡, 何春光, 孙鹏 (2022) 白鹤利用农田作为中转取食生境的原因. 生物多样性, 30, 22093. DOI: 10.17520/biods.2022093.
Jie Gao, Dehao Li, Haibo Jiang, Guangyi Deng, Chaofan Zhang, Chunguang He, Peng Sun (2022) Analyzing the relative habitat use by Siberian cranes on migratory stopover sites: A traditional wetland species switching to croplands for food resources. Biodiversity Science, 30, 22093. DOI: 10.17520/biods.2022093.
水深 Water depth (cm) | 平均数量 Average quantity (yield/m2) | 平均生物量 Average biomass (g) | 群落面积 Community area (×105 m2) | 总数量 Total quantity (×106 ) | 总生物量 Total biomass (×107 g) |
---|---|---|---|---|---|
0 | 117 ± 24 | 0.58 ± 0.05 | 0.49 | 5.74 | 0.33 |
5 | 131 ± 47 | 1.25 ± 0.09 | 0.73 | 9.60 | 1.20 |
10 | 355 ± 127 | 1.42 ± 0.10 | 2.91 | 103.42 | 14.69 |
15 | 157 ± 22 | 1.17 ± 0.14 | 9.05 | 142.09 | 16.62 |
20 | 115 ± 29 | 1.18 ± 0.07 | 0.81 | 9.26 | 1.09 |
25 | 118 ± 43 | 0.94 ± 0.06 | 4.55 | 53.68 | 5.05 |
30 | 83 ± 34 | 0.92 ± 0.06 | 5.75 | 47.75 | 43.93 |
总计 Total | - | 24.29 | 371.54 | 43.37 |
表1 研究区内湿地生境可提供扁秆荆三棱球茎资源量
Table 1 The resources of Bolboschoenus planiculmis corn provided by wetland habitats in the study area
水深 Water depth (cm) | 平均数量 Average quantity (yield/m2) | 平均生物量 Average biomass (g) | 群落面积 Community area (×105 m2) | 总数量 Total quantity (×106 ) | 总生物量 Total biomass (×107 g) |
---|---|---|---|---|---|
0 | 117 ± 24 | 0.58 ± 0.05 | 0.49 | 5.74 | 0.33 |
5 | 131 ± 47 | 1.25 ± 0.09 | 0.73 | 9.60 | 1.20 |
10 | 355 ± 127 | 1.42 ± 0.10 | 2.91 | 103.42 | 14.69 |
15 | 157 ± 22 | 1.17 ± 0.14 | 9.05 | 142.09 | 16.62 |
20 | 115 ± 29 | 1.18 ± 0.07 | 0.81 | 9.26 | 1.09 |
25 | 118 ± 43 | 0.94 ± 0.06 | 4.55 | 53.68 | 5.05 |
30 | 83 ± 34 | 0.92 ± 0.06 | 5.75 | 47.75 | 43.93 |
总计 Total | - | 24.29 | 371.54 | 43.37 |
秸秆处理方式 Straw treatment mode | 平均数量 Average quantity (yield/m2) | 平均生物量 Average biomass (g/m2) | 总数量 Total quantity (×109) | 总生物量 Total biomass (×109 g) |
---|---|---|---|---|
秸秆离田 Straw leaving field | 12 ± 2 | 9.14 ± 0.03 | 1.07 | 0.80 |
秸秆还田 Straw returning to field | 27 ± 15 | 20.49 ± 0.03 | 2.39 | 1.80 |
表2 研究区内农田生境可提供食物资源量
Table 2 The amount of food resources provided by farmland habitats in the study area
秸秆处理方式 Straw treatment mode | 平均数量 Average quantity (yield/m2) | 平均生物量 Average biomass (g/m2) | 总数量 Total quantity (×109) | 总生物量 Total biomass (×109 g) |
---|---|---|---|---|
秸秆离田 Straw leaving field | 12 ± 2 | 9.14 ± 0.03 | 1.07 | 0.80 |
秸秆还田 Straw returning to field | 27 ± 15 | 20.49 ± 0.03 | 2.39 | 1.80 |
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