
Spatiotemporal variation and hotspots of climate change in the Yangtze River Watershed during 1958-2017
地理学报(英文版) ›› 2022, Vol. 32 ›› Issue (1) : 141-155.
Spatiotemporal variation and hotspots of climate change in the Yangtze River Watershed during 1958-2017
The Yangtze River Watershed in China is a climate change hotspot featuring strong spatial and temporal variability; hence, it poses a certain threat to social development. Identifying the characteristics of and regions vulnerable to climate change is significantly important for formulating adaptive countermeasures. However, with regard to the Yangtze River Watershed, there is currently a lack of research on these aspects from the perspective of natural and anthropogenic factors. To address this issue, in this study, based on the temperature and precipitation records from 717 meteorological stations, the RClimDex and random forest models were used to assess the spatiotemporal characteristics of climate change and identify mainly the natural and anthropogenic factors influencing climate change hotspots in the Yangtze River Watershed for the period 1958-2017. The results indicated a significant increasing trend in temperature, a trend of wet and dry polarization in the annual precipitation, and that the number of temperature indices with significant variations was 2.8 times greater than that of precipitation indices. Significant differences were also noted in the responses of the climate change characteristics of the sub-basins to anthropogenic and natural factors; the delta plain of the Yangtze River estuary exhibited the most significant climate changes, where 88.89% of the extreme climate indices varied considerably. Furthermore, the characteristics that were similar among the identified hotpots, including human activities (higher Gross Domestic Product and construction land proportions) and natural factors (high altitudes and large proportions of grassland and water bodies), were positively correlated with the rapid climate warming.
Yangtze River Watershed / climate change / RClimDex / Random Forest / anthropogenic and natural factors / hotspots {{custom_keyword}} /
Figure 1 Location of meteorological stations and sub-basins (a); SB1-45 denote the sub-basins. Land use and land cover change (LUCC) in 2015 (b); LUCC1 is cultivated land, LUCC2 is forest land, LUCC3 is grassland, LUCC4 is water body, LUCC5 is construction land, and LUCC6 is unused land. Study area elevation (c) |
Table S1 Definition of the extreme climate indices |
Index | Indicator name | Definition | Unit | ||
---|---|---|---|---|---|
FD0 | Frost days | Annual count when TN (daily minimum)<0ºC | Days | ||
SU25 | Summer days | Annual count when TX (daily maximum)>25ºC | Days | ||
ID0 | Ice days | Annual count when TX (daily maximum)<0ºC | Days | ||
TR20 | Tropical nights | Annual count when TN (daily minimum)>20ºC | Days | ||
GSL | Growing season Length | Annual count between the first span of at least 6 days with daily mean temperature >5℃ after winter and the first span after summer of 6 days with a daily mean temperature <5℃ | Days | ||
TXx | Max Tmax | Monthly maximum value of daily maximum temp | ºC | ||
TNx | Max Tmin | Monthly maximum value of daily minimum temp | ºC | ||
TXn | Min Tmax | Monthly minimum value of daily maximum temp | ºC | ||
TNn | Min Tmin | Monthly minimum value of daily minimum temp | ºC | ||
TN10p | Cool nights | Percentage of days when TN<10th percentile | Days | ||
TX10p | Cool days | Percentage of days when TX<10th percentile | Days | ||
TN90p | Warm nights | Percentage of days when TN>90th percentile | Days | ||
TX90p | Warm days | Percentage of days when TX>90th percentile | Days | ||
WSDI | Warm spell duration indicator | Annual count of days with at least 6 consecutive days when TX>90th percentile | Days | ||
CSDI | Cold spell duration indicator | Annual count of days with at least 6 consecutive days when TN<10th percentile | Days | ||
DTR | Diurnal temperature range | Monthly mean difference between TX and TN | ºC | ||
RX1day | Max 1-day precipitation amount | Monthly maximum 1-day precipitation | Mm | ||
RX5day | Max 5-day precipitation amount | Monthly maximum consecutive 5-day precipitation | Mm | ||
SDII | Simple daily intensity index | Annual total precipitation divided by the number of wet days (defined as PRCP≥1.0mm) in the year | Mm/day | ||
R10 | Number of heavy precipitation days | Annual count of days when PRCP≥10mm | Days | ||
Index | Indicator name | Definition | Unit | ||
R20 | Number of very heavy precipitation days | Annual count of days when PRCP≥20mm | Days | ||
R25 | Heavy precipitation days | Annual count of days when PRCP≥25mm | Days | ||
RR | Daily precipitation | A wet day is defined when RR ≥ 1 mm, and a dry day when RR < 1 mm | Days | ||
CDD | Consecutive dry days | Maximum number of consecutive days with RR<1mm | Days | ||
CWD | Consecutive wet days | Maximum number of consecutive days with RR≥1mm | Days | ||
R95p | Very wet days | Annual total PRCP when RR>95th percentile | Mm | ||
R99p | Extremely wet days | Annual total PRCP when RR>99th percentile | Mm | ||
PRCPTOT | Annual total wet-day precipitation | Annual total PRCP in wet days (RR≥1mm) | Mm |
Table 1 Temporal changes in extreme climate indices in the Yangtze River Watershed from 1958-2017 |
Temperature indices | Changing rate per decade | Precipitation indices | Changing rate per decade |
---|---|---|---|
TXx (℃) | 0.19 | RX1day (mm) | 0.36 |
TXn (℃) | 0.28 | RX5day (mm) | 1.74 |
TNx (℃) | 0.15 | SDII (mm/day) | 0.06 |
TNn (℃) | 0.32 | R95p (mm) | 13.14 |
DTR (℃) | -0.06 | R99p (mm) | 6.17 |
SU25 (days) | 2.63 | PRCPTOT (mm) | 8.45 |
ID0 (days) | -0.02 | R10 (days) | 1.04 |
TR20 (days) | 2.57 | R20 (days) | 0.13 |
FD0 (days) | -3.04 | R25 (days) | 0.02 |
TX10p (days) | -1.5 | CDD (days) | -0.65 |
TX90p (days) | 2.71 | CWD (days) | 0.87 |
TN10p (days) | -3.65 | ||
TN90p (day) | 4.29 | ||
WSDI (days) | 1.77 | ||
CSDI (days) | -1.56 | ||
GSL (days) | 1.34 |
Notes: Trends marked in bold are statistically significant at the 0.05 level. |
Figure 6 Analysis of the related factors of climate change in the Yangtze River Watershed from 1958-2017 (a denotes significance at the 0.05 level; b denotes significance at the 0.01 level; blank value means no significant correlation) |
Table 2 The importance of factors affecting climate change (after normalization) |
DTR | TXx | TXn | TNx | TNn | TN10p | TN90p | TX90p | FD0 | TR20 | SU25 | |
---|---|---|---|---|---|---|---|---|---|---|---|
Elevation | 0.74 | 0.63 | 1 | 1 | 0.78 | 1 | 1 | 0.83 | 0.77 | 0.44 | 0.74 |
Slope | 0.36 | 0.49 | 0.60 | 0.19 | 0.45 | 0.24 | 0.06 | 0.81 | 0.48 | 0.61 | 0.09 |
Population | 0.03 | 0.53 | 0.50 | 0.38 | 0.04 | 0.43 | 0.56 | 0.58 | 0.54 | 0.82 | 0.41 |
GDP | 0.73 | 1 | 0.67 | 0 | 0.06 | 0 | 0 | 0.61 | 0.20 | 0.96 | 1 |
Cultivated land | 0.47 | 0.17 | 0.36 | 0.21 | 0 | 0.11 | 0.21 | 0.15 | 0.63 | 0.21 | 0.53 |
Forest land | 0.35 | 0.75 | 0.19 | 0.30 | 0.09 | 0.31 | 0.52 | 0.14 | 0.37 | 0.48 | 0 |
Grassland | 0.06 | 0.74 | 0.05 | 0.77 | 0.24 | 0.38 | 0.65 | 1 | 0.34 | 0.37 | 0.04 |
Water body | 0.06 | 0 | 0.28 | 0.14 | 1 | 0.74 | 0.11 | 0 | 1 | 0 | 0.42 |
Construction land | 1 | 0.84 | 0.80 | 0.19 | 0.52 | 0.18 | 0.22 | 0.61 | 0.75 | 1 | 0.25 |
Unused land | 0 | 0.51 | 0 | 0.37 | 0.34 | 0.33 | 0.09 | 0.01 | 0 | 0.16 | 0.31 |
Figure S2 Changing rate of the rest extreme temperature indices in the Yangtze River sub-basins from 1958-2017 |
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Variations in long-term precipitation trends due to climate forcings have been observed in many parts of the world, exacerbating hydrological uncertainties to predicting droughts, floods, water resource availability, and ecosystem services. The Lower Mississippi River Alluvial Valley (LMRAV) is an important economic region of the midsouth USA, which is prone to natural disasters from extreme climate events and is known historically for cyclic flooding events and, within the last 20 years, for groundwater level declines. However, our knowledge of long-term precipitation trends in this region is fragmented. Using 100-year historic daily precipitation data from six stations of forest lands along with multivariate statistical analysis, we found that there were significant increasing trends (p ≤ 0.05) in annual precipitation near the south coastal area of the LMRAV and only marginally increasing trends in the northern area. Spatial variation in seasonality was observed at the decadal scale with increasing trends in fall near the coastal area and in spring around the north area. In addition to becoming wetter, the coastal area also experienced higher precipitation intensity with shorter return period over the past 100 years. These findings are useful to water resource managers for adapting to changing climate conditions in the LMRAV.
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Climate change and urbanization are key factors affecting the future of water quality in urbanized catchments. The work reported in this paper is an evaluation of the combined and relative impact of climate change and urbanization on the water quality of receiving water bodies in the context of a highly urbanized watershed served by a combined sewer system (CSS) in northern Italy. The impact is determined by an integrated modelling study involving two years of field campaigns. The results obtained from the case study show that impervious urban surfaces and rainfall intensity are significant predictors of combined sewer overflows (CSOs) and consequently of the water quality of the receiving water body. Scenarios for the year 2100 demonstrate that climate change combined with increasing urbanization is likely to lead to severe worsening of river water quality due to a doubling of the total phosphorus load from CSOs compared to the current load. Reduction in imperviousness was found to be a suitable strategy to adapt to these scenarios by limiting the construction of new impervious areas and decreasing the existing areas by only 15%. This information can be further utilized to develop future designs, which in turn should make these systems more resilient to future changes in climate and urbanization.Copyright © 2018 Elsevier Ltd. All rights reserved.
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