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Marina Herrera-Pantoja Julio 2014

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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 20030

500

1000

1500

2000

2500

3000

3500

km

² o

f w

etl

an

d

year

History of East Anglia Fenlands

since 1600s

There has been a dramatic loss of wetlands

and now climate change are expected to disrupt

these fragile ecosystems

Smoothed figures based on 10 years moving averages

1-

0.75-

0.5-

0.25-

0-

-0.25-

-.5-

-0.75-

-1-

1772 1792 1812 1832 1852 1872 1892 1912 1932 1952 1972 1992

An

om

aly

(°C

) fr

om

1961

-90 a

vera

ge

Central England Global

Smoothed figures based on 10 years moving averages

1-

0.75-

0.5-

0.25-

0-

-0.25-

-.5-

-0.75-

-1-

1772 1792 1812 1832 1852 1872 1892 1912 1932 1952 1972 1992

An

om

aly

(°C

) fr

om

1961

-90 a

vera

ge

Central England Global

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

A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation

Community

ZoneOpen water area Swamp area Fen area

A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation

Community

ZoneOpen water area Swamp area Fen area

A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation

Community

ZoneOpen water area Swamp area Fen area

A1 - A4 S1 - S2 - S4 M9 - M13 - M22 - M24 Vegetation

Community

Zone

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

Predicted water table contours

Groundwater flow

Z

Fowlmere

boreholes

Predicted water table contours

Groundwater flow

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 drylandspecies.

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