在高度城市化的河流系统中管理河流温度对于维持水生生态系统和相关的有益用途至关重要。在这项工作中,我们更新并利用了机械的河流温度模型,I-TreeCoolRiver,评估两种生态恢复方案的降温影响:(1)替代河床材料边缘和(2)河岸地区植树的遮阳效应。i-TreeCoolRiver模型进行了修改,以考虑河床温度的日波动,这与浅层城市溪流有关,在浅层城市溪流中,缺乏自然遮荫加上水柱的低热容量会使昼夜波动相对极端。该模型在洛杉矶河流域ComptonCreek的4.2公里范围内进行了校准和验证,加州两条本地鱼,arroyochub(Gilaorcuttii)和未装甲的三叶松棘鱼(Gasterosteusaculeatuswilliamsoni),被认为是评估热生境适宜性的目标物种。主要发现包括:(1)考虑到床温度的日波动(R2从0.43增加到0.68),模型性能得到了改善;(2)基质修复和植树可能会将夏季温度降低到有记录的重点鱼类产卵温度阈值之内。使用liecrete作为混凝土底部的替代材料降低了中值河流温度指标:最大每周最大值,每周最大平均值,每周最低最低温度平均为3°C(13%)至20.4°C,19.7°C,和17.8°C,分别。河岸走廊的植树使平均河流温度指标平均降低了0.9°C(4%)至22.7°C,22°C,19°C,分别。结合这两种情况,将河流温度指标平均降低了4°C(18%)至18.2°C。因此,如果实施恢复,水温不会成为将重点鱼类重新引入康普顿溪的限制因素。城市森林和水管理人员可以利用这项工作的含义来恢复其他城市地区的热污染河流。
Managing river temperature in highly urbanized stream systems is critical for maintaining aquatic ecosystems and associated beneficial uses. In this work, we updated and utilized a mechanistic river temperature model, i-Tree Cool River, to evaluate the cooling impacts of two ecological restoration scenarios: (1) an alternative streambed material limecrete and (2) shading effects of tree planting in riparian areas. The i-Tree Cool River model was modified to account for diurnal fluctuations of streambed temperature, which is relevant in shallow urban streams where lack of natural shading combined with low heat capacity of the water column can make diurnal fluctuations relatively extreme. The model was calibrated and validated on a 4.2 km reach of Compton Creek in the Los Angeles River watershed, California. Two native fish, arroyo chub (Gila orcuttii) and unarmored threespine stickleback (Gasterosteus aculeatus williamsoni), were considered the target species for assessing thermal habitat suitability. Key findings include: (1) model performance was improved when accounting for diurnal fluctuations in bed temperature (R2 increased from 0.43 to 0.68); and (2) substrate rehabilitation and tree planting can potentially reduce summertime temperatures to within the documented spawning temperature thresholds for the focal fish species. Using limecrete as an alternative material for the concrete bottom decreased the median river temperature metrics: maximum weekly maximum, maximum weekly average, and minimum weekly minimum temperatures by an average of 3 °C (13%) to 20.4 °C, 19.7 °C, and 17.8 °C, respectively. Tree planting in the riparian corridor decreased the average river temperature metrics by an average of 0.9 °C (4%) to 22.7 °C, 22 °C, and 19 °C, respectively. Combining the two scenarios decreased the river temperature metrics by an average of 4 °C (18%) to 18.2 °C. Therefore, water temperature would not be a limiting factor in potential reintroduction of the focal fish species to Compton Creek if restoration were implemented. Implications of this work could be used by urban forest and water managers for restoring thermally polluted rivers in other urban areas.