| Literature DB >> 26965069 |
Junqiang Xia1, Shanshan Deng1, Jinyou Lu2, Quanxi Xu3, Quanli Zong1, Guangming Tan1.
Abstract
Significant channel adjustments have occurred in the Jingjiang Reach of the Middle Yangtze River, because of the operation of the Three Gorges Project (TGP). The Jingjiang Reach is selected as the study area, covering the Upper Jingjiang Reach (UJR) and Lower Jingjiang Reach (LJR). The reach-scale bankfull channel dimensions in the study reach were calculated annually from 2002 to 2013 by means of a reach-averaged approach and surveyed post-flood profiles at 171 sections. We find from the calculated results that: the reach-scale bankfull widths changed slightly in the UJR and LJR, with the corresponding depths increasing by 1.6 m and 1.0 m; the channel adjustments occurred mainly with respect to bankfull depth because of the construction of large-scale bank revetment works, although there were significant bank erosion processes in local regions without the bank protection engineering. The reach-scale bankfull dimensions in the UJR and LJR generally responded to the previous five-year average fluvial erosion intensity during flood seasons, with higher correlations being obtained for the depth and cross-sectional area. It is concluded that these dynamic adjustments of the channel geometry are a direct result of recent human activities such as the TGP operation.Entities:
Year: 2016 PMID: 26965069 PMCID: PMC4786812 DOI: 10.1038/srep22802
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.379
Figure 1(a) Yangtze River Basin. ①-Yichang; ②-Hukou; ③-Dongting Lake; ④- Poyang Lake; (b) Sketch of Jingjiang Reach with the locations of 171 cross sections and hydrometric sections. The Gezhouba Water Conservancy Project is located 38 km downstream of the TGD, and this project is the first large-scale run-of-river hydropower station on the Yangtze River with low-head and high flow. The cumulative volumes of channel scour in the sub-reaches I–IV were 0.41 × 108, 1.44 × 108, 3.9 × 108 and 3.1 × 108 m3 in 2002–2013; and (c) Cumulative channel evolution volume in the Jingjiang Reach since 2002, with the negative value meaning channel scour. With the TGP operation, the UJR and LJR generally underwent continuous channel degradation owing to the reduced sediment load, and slight channel aggradation occurred in a few years.
Figure 2Temporal variations in the flow and sediment regime entering the Jingjiang Reach of (a) Annual and flood-season water discharges; and (b) Annual and flood-season suspended-sediment discharges. All the hydrological data from the Bureau of Hydrology, Changjiang Water Resources Commission.
Figure 3Temporal changes of bed and bank profiles at two sections of (a) Jing53 in the UJR, which is located about 15.1 km downstream of Shashi; and (b) Jing98 in the LJR, which is located about 57.6 km upstream of Jianli. Changes in the bed and bank profiles at these sections were typical of the whole study reach, including stable and erodible banks. The variations in typical cross-sectional profiles were caused partly by the downstream movement of sand waves due to the transport of sand-bed load, and mainly by the non-equilibrium transport of suspended load. The intra-annual variability in the channel evolution shows an alternating process of erosion and deposition over a hydrological year, with a general trend in channel scour.
Figure 4Temporal variations in the reach-scale (heavy lines) and section-scale (thin lines with data marks) cross-sectional areas of (a) Upper Jingjiang Reach and (b) Lower Jingjiang Reach, showing the progression of channel scour in the Jingjiang Reach during the period from 2002 to 2013. In the UJR, Jing30 section is located 14.4 km upstream of Shashi, and Sha06 section is located 1.4 km downstream of Shashi; in the LJR, Jing108 and Jing122 sections are located 47.1 and 29.9 km upstream of Jianli, respectively. Jing30 is also located at the front of the central bar of Taipingkou. As shown in Table 1, the flood-season average discharge in 2006 was relatively low (11568 m3/s), with obvious sediment deposition occurring at Jing30, which led to a sharp reduction in the bankfull area in 2006. During the period from 2007 to 2009, this central bar was eroded significantly due to large discharges during flood seasons, which made a remarkable contribution to an increase in the bankfull area at Jing30.
Reach-scale bankfull widths and depths in different reaches with incoming discharges and suspended-sediment concentrations during flood seasons.
| Year | Upper Jingjiang Reach | Lower Jingjiang Reach | ||||||||
|---|---|---|---|---|---|---|---|---|---|---|
| (m3/s) | (kg/m3) | (m) | (m) | (m3/s) | (kg/m3) | (m) | (m) | |||
| 2002 | 17657 | 0.81 | 5.16 | 1384 | 14.20 | 16190 | 0.71 | 4.52 | 1292 | 13.45 |
| 2003 | 19185 | 0.42 | 12.34 | 1381 | 14.36 | 17619 | 0.42 | 9.91 | 1287 | 13.82 |
| 2004 | 17944 | 0.30 | 15.81 | 1382 | 14.55 | 17148 | 0.33 | 11.91 | 1303 | 13.97 |
| 2005 | 19919 | 0.40 | 16.53 | 1384 | 14.73 | 18951 | 0.43 | 11.99 | 1308 | 14.00 |
| 2006 | 11568 | 0.11 | 18.29 | 1388 | 14.62 | 11236 | 0.18 | 8.90 | 1306 | 14.18 |
| 2007 | 17940 | 0.25 | 25.75 | 1400 | 14.85 | 17298 | 0.31 | 12.71 | 1317 | 14.03 |
| 2008 | 17201 | 0.17 | 31.22 | 1402 | 14.84 | 16526 | 0.24 | 13.85 | 1321 | 13.93 |
| 2009 | 16660 | 0.18 | 32.91 | 1386 | 15.03 | 16293 | 0.24 | 15.20 | 1303 | 14.31 |
| 2010 | 17690 | 0.16 | 37.80 | 1388 | 15.19 | 16786 | 0.20 | 20.19 | 1306 | 14.36 |
| 2011 | 13371 | 0.07 | 38.16 | 1386 | 15.42 | 13101 | 0.15 | 12.68 | 1311 | 14.43 |
| 2012 | 19705 | 0.19 | 44.19 | 1387 | 15.58 | 18632 | 0.23 | 20.55 | 1307 | 14.50 |
| 2013 | 15738 | 0.15 | 45.88 | 1386 | 15.82 | 15235 | 0.21 | 17.86 | 1303 | 14.45 |
| Mean | 17048 | 0.28 | 27.00 | 1388 | 14.93 | 16251 | 0.31 | 13.36 | 1305 | 14.12 |
The suspended-sediment concentrations at Jianli were consistently greater that the values at Shashi after the TGP operation, and the increase of suspended load along the reach was caused by the recent channel scour of the reach below Shashi. There is a diversion branch at Ouchikou located in the reach between Shashi and Jianli, which led to the water discharges at Shashi being consistently greater than the values at Jianli. The ratio of the annual water discharge entering three diversion branches to the discharge at Zhicheng decreased gradually, with the average ratio reducing from 20.1% before 2002 to 11.7% in 2003–201327. A decrease in the diversion ratio of flow means that fewer flood-season discharges were diverted from the main stream of the Yangtze Reach into the Dongting Lake.
Q, S = mean discharge and suspended-sediment concentration at Shashi during a flood season from May to October.
Q, S = flood-season average discharge and suspended-sediment concentration at Jianli.
F, F = flood-season average fluvial erosion intensity at Shashi and Jianli.
, = reach-scale bankfull width and depth.
Figure 5Relationships between the reach-scale bankfull dimensions and the five-year average fluvial erosion intensity during flood seasons in the UJR and LJR: (a) Bankfull width; (b) Bankfull depth; and (c) Bankfull area. The average reach-scale bankfull width or depth in the UJR was greater than the corresponding value in the LJR, and such a distribution of hydraulic-geometry parameters in the Jingjiang Reach is caused by the particular geomorphological environment and hydrological characteristics.