干旱区研究 ›› 2022, Vol. 39 ›› Issue (3): 820-828.doi: 10.13866/j.azr.2022.03.15
何启欣1,2,3(),曹广超2,3,4(),曹生奎1,2,3,程梦园1,2,3,刁二龙1,2,3,高斯远1,2,3,邱巡巡1,2,3,赵美亮1,2,3,程国1,2,3
收稿日期:
2021-09-03
修回日期:
2022-02-22
出版日期:
2022-05-15
发布日期:
2022-05-30
通讯作者:
曹广超
作者简介:
何启欣(1995-),女,硕士研究生,研究方向为自然地理与生态环境过程. E-mail: 基金资助:
HE Qixin1,2,3(),CAO Guangchao2,3,4(),CAO Shengkui1,2,3,CHENG Mengyuan1,2,3,DIAO Erlong1,2,3,GAO Siyuan1,2,3,QIU Xunxun1,2,3,ZHAO Meiliang1,2,3,CHENG Guo1,2,3
Received:
2021-09-03
Revised:
2022-02-22
Online:
2022-05-15
Published:
2022-05-30
Contact:
Guangchao CAO
摘要:
利用香日德-柴达木河流域的湖水、河水、地下水、井水、雪等不同水体59组样品,室内测试样品δ2H和δ18O值并对其特征进行分析,探讨其影响因素、氘盈余值(d-excess)及河水沿程变化等。结果表明:(1) 香日德-柴达木河流域各水体氢氧同位素特征有差异,水循环过程中δ18O的富集程度为:湖水>冰>地下水>河水>井水>雪,河水和地下水水力联系紧密,流域各水体中河水和湖水的蒸发作用最强。(2) 湖水δ2H和δ18O的最大值均在盆地底部的霍布逊湖,最小值均在上游东支河源冬给措纳湖,表明青藏高原北部湖水δ2H和δ18O比南部偏正,存在明显的高程效应。(3) 河水δ2H和δ18O之间存在较显著的线性关系δ2H=4.93δ18O-29.6(R2=0.97),氢氧同位素组分的富集主要受控于河流蒸发的影响,河水上游蒸发作用最强,d-excess值偏大的原因可能为海拔高,气温低,空气湿度小。(4) 同一位置冰的氢氧稳定同位素较水贫化,是局部水汽反复蒸发凝结的结果。
何启欣,曹广超,曹生奎,程梦园,刁二龙,高斯远,邱巡巡,赵美亮,程国. 香日德-柴达木河流域水体氢氧稳定同位素特征及影响因素研究[J]. 干旱区研究, 2022, 39(3): 820-828.
HE Qixin,CAO Guangchao,CAO Shengkui,CHENG Mengyuan,DIAO Erlong,GAO Siyuan,QIU Xunxun,ZHAO Meiliang,CHENG Guo. Hydrogen-oxygen isotope characteristics of water bodies in the Xiangride-Qaidam River Basin and its influencing factors[J]. Arid Zone Research, 2022, 39(3): 820-828.
表1
香日德-柴达木河流域氢氧稳定同位素比值"
类型 | 样品个数 | δ2H/‰ | δ18O/‰ | d-excess/‰ | |||||
---|---|---|---|---|---|---|---|---|---|
均值±标准差 | 变化范围 | 均值±标准差 | 变化范围 | 均值±标准差 | 变化范围 | ||||
湖水 | 8 | -116.98±21.10 | -139.63~-83.58 | -18.19±3.38 | -21.63~-11.99 | 28.57±6.84 | 12.34~33.43 | ||
冰 | 13 | -119.23±12.04 | -102.10~-148.90 | -17.84±2.02 | -22.64~-15.22 | 23.50±5.16 | 16.37~32.19 | ||
河水 | 31 | -107.87±8.50 | -131.78~-91.88 | -15.89±1.70 | -20.78~-12.92 | 19.14±5.40 | 9.88~34.44 | ||
地下水 | 3 | -109.32±5.58 | -101.57~-114.53 | -16.34±0.93 | -15.05~-17.20 | 21.32±1.85 | 18.83~23.10 | ||
井水 | 3 | -99.36±7.17 | -104.96~-89.24 | -13.90±1.23 | -14.86~-12.17 | 11.81±2.64 | 8.10~13.96 | ||
雪 | 1 | -73.48 | - | -7.80 | - | -11.12 | - |
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