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Marina Herrera-Pantoja 
Julio 2014
Wetlands provide valuable 
hydrological, biochemical 
and climatic functions that 
are essential for supporting 
the world’s biodiversity 
In Britain, the high species 
richness of wetlands in 
East Anglia, support 20% 
of all nationally rare and 
40% of nationally scarce 
vascular plants
1637 1825 1934 2003 
3500 
3000 
2500 
2000 
1500 
1000 
500 
0 
km² of wetland 
year 
History of East Anglia Fenlands 
since 1600s 
1- 
0.75- 
0.5- 
0.25- 
0- 
-0.25- 
-.5- 
-0.75- 
Central England Global 
-1- 
1772 1792 1812 1832 1852 1872 1892 1912 1932 1952 1972 1992 
Smoothed figures based on 10 years moving averages 
Anomaly (°C ) from 1961-90 average 
There has been a dramatic loss of wetlands 
and now climate change are expected to disrupt 
these fragile ecosystems
N 
Breckland 
Breckland is a natural habitat which 
comprises a group of fluctuating meres 
fed by groundwater from the underlying 
Chalk aquifer 
These meres have unique 
hydrogeological characteristics which 
advantage a number of rare species 
that require low competition and low 
nutrient levels
Open water area Swamp area Fen area 
Zone 
A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation 
Community 
Generalised zonation of wetland vegetation in a typical habitat in 
East Anglia indicating the National Vegetation Classification plant 
communities (Rodwell, 1991; Fojt, 1994; 1995; Wheeler and 
Proctor, 2000)
Soil AWC & FAW 
Groundwater Recharge 
Model 
Daily data from a nearby 
meteorological station 
Potential groundwater recharge 
(Hxr) 
Actual evapotranspiration 
(AE) 
Groundwater Flow 
Model 
Water levels for the baseline and 
future scenarios 
Ecohydrological Guidelines 
Possible impacts of climate change 
on wetland communities
Fowlmere 
boreholes 
Groundwater flow 
Predicted water table contours 
Z 
During the 2080s the mean water table is almost 0.9 m lower 
than the baseline mean value and the lowest of the three 
modelled scenarios 
The persistence of future dry periods could lead to a loss of 
wetland communities and increased representation of dryland 
species.
Mean 
water table 
(m AOD ) 
Minimum 
water table 
(m AOD) 
Duration of 
low water table 
(months) 
Maximum 
water table 
(m AOD) 
Duration of 
hight water 
table (months) 
Likely impact on 
wetland communities 
Baseline 30.74 28.68 12 33.85 3 
2020s 31.06 27.98 24 33.76 2 Changes towards swamp-like stands 
2050s 30.79 29.35 9 36.85 6 Recovery of rare and local plant species 
2080s 29.84 27.91 61 32.03 0 Loss of wetlands communities 
Simulated water levels in a wetland fed by an unconfined Chalk 
aquifer during the baseline period (1961-1990) and the 2020s, 
2050s and 2080s future periods of the ‘high’ gas emissions 
scenario and their likely impacts on groundwater dependent 
wetland communities in East Anglia
Climate change may alter groundwater recharge provoking 
changes in the elevation of the water table in unconfined 
Chalk aquifers in East Anglia. 
The persistence of future dry periods with associated low 
groundwater recharge during the latter part of this century 
will potentially increase pressures on groundwater 
dependent wetlands. 
The predicted fall in wetland water level by the end of this 
century may have a greater impact on those mere species 
with a small tolerance to dry conditions. 
Although species may adapt themselves to climate change 
planned adaptation can provide opportunities for protection 
of endanger species
ACKNOWLEDGEMENTS 
Mexican National Council for 
Science and Technology 
(CONACYT) 
Climatic Research Unit, 
University of East Anglia

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Effects cc gwd wetlands mhp

  • 2. Wetlands provide valuable hydrological, biochemical and climatic functions that are essential for supporting the world’s biodiversity In Britain, the high species richness of wetlands in East Anglia, support 20% of all nationally rare and 40% of nationally scarce vascular plants
  • 3. 1637 1825 1934 2003 3500 3000 2500 2000 1500 1000 500 0 km² of wetland year History of East Anglia Fenlands since 1600s 1- 0.75- 0.5- 0.25- 0- -0.25- -.5- -0.75- Central England Global -1- 1772 1792 1812 1832 1852 1872 1892 1912 1932 1952 1972 1992 Smoothed figures based on 10 years moving averages Anomaly (°C ) from 1961-90 average There has been a dramatic loss of wetlands and now climate change are expected to disrupt these fragile ecosystems
  • 4. N Breckland Breckland is a natural habitat which comprises a group of fluctuating meres fed by groundwater from the underlying Chalk aquifer These meres have unique hydrogeological characteristics which advantage a number of rare species that require low competition and low nutrient levels
  • 5. Open water area Swamp area Fen area Zone A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation Community Generalised zonation of wetland vegetation in a typical habitat in East Anglia indicating the National Vegetation Classification plant communities (Rodwell, 1991; Fojt, 1994; 1995; Wheeler and Proctor, 2000)
  • 6. Soil AWC & FAW Groundwater Recharge Model Daily data from a nearby meteorological station Potential groundwater recharge (Hxr) Actual evapotranspiration (AE) Groundwater Flow Model Water levels for the baseline and future scenarios Ecohydrological Guidelines Possible impacts of climate change on wetland communities
  • 7. Fowlmere boreholes Groundwater flow Predicted water table contours Z During the 2080s the mean water table is almost 0.9 m lower than the baseline mean value and the lowest of the three modelled scenarios The persistence of future dry periods could lead to a loss of wetland communities and increased representation of dryland species.
  • 8. Mean water table (m AOD ) Minimum water table (m AOD) Duration of low water table (months) Maximum water table (m AOD) Duration of hight water table (months) Likely impact on wetland communities Baseline 30.74 28.68 12 33.85 3 2020s 31.06 27.98 24 33.76 2 Changes towards swamp-like stands 2050s 30.79 29.35 9 36.85 6 Recovery of rare and local plant species 2080s 29.84 27.91 61 32.03 0 Loss of wetlands communities Simulated water levels in a wetland fed by an unconfined Chalk aquifer during the baseline period (1961-1990) and the 2020s, 2050s and 2080s future periods of the ‘high’ gas emissions scenario and their likely impacts on groundwater dependent wetland communities in East Anglia
  • 9. Climate change may alter groundwater recharge provoking changes in the elevation of the water table in unconfined Chalk aquifers in East Anglia. The persistence of future dry periods with associated low groundwater recharge during the latter part of this century will potentially increase pressures on groundwater dependent wetlands. The predicted fall in wetland water level by the end of this century may have a greater impact on those mere species with a small tolerance to dry conditions. Although species may adapt themselves to climate change planned adaptation can provide opportunities for protection of endanger species
  • 10. ACKNOWLEDGEMENTS Mexican National Council for Science and Technology (CONACYT) Climatic Research Unit, University of East Anglia