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Twenty-eighth Report Adapting Institutions to Climate Change Cm ...

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2.52<br />

2.53<br />

2.54<br />

2.55<br />

2.56<br />

2.57<br />

oxygen demand), dilution and temperature. These relationships were recognised at the beginning<br />

of the 20th century by the Royal Commission on Sewage Disposal. Warmer waters brought on by<br />

climate change will have a lower capacity for dissolved oxygen, and biochemical activity will be<br />

greater. This means that more restrictions will have <strong>to</strong> be placed on the organic material present<br />

in discharges.<br />

Warmer lowland waters, enriched with nitrate and phosphate, are more prone in sunny conditions<br />

<strong>to</strong> algal blooms, which have potential health and aesthetic implications, and can cause problems<br />

for aquatic ecosystems. Water supply reservoirs are particularly prone <strong>to</strong> this phenomenon, which<br />

is likely <strong>to</strong> become a more frequent event in the future. Treatment costs <strong>to</strong> produce drinking water<br />

may rise as a result.<br />

Another important fac<strong>to</strong>r is the presence of nitrogen compounds. Ammonia in untreated sewage<br />

and from farm waste run-off is noxious, particularly <strong>to</strong> fish, and affects the dissolved oxygen<br />

regime through nitrification. Again, changes <strong>to</strong> temperature and flow, and the sudden discharge<br />

of untreated sewage during s<strong>to</strong>rms, will need even greater attention as climate changes.<br />

Nitrates present in, or produced from, discharges of untreated sewage and farm waste add <strong>to</strong> that<br />

present in the diffuse run-off from agricultural land and in discharges of treated sewage effluent<br />

from sewage works. Agricultural nitrate arises from nitrification of organic nitrogen in the soil<br />

and from fertiliser application; it will be washed in<strong>to</strong> water bodies by rainfall and some will find<br />

its way in<strong>to</strong> groundwater as well as rivers. The interface between soil and water is a major fac<strong>to</strong>r in<br />

water quality control, and climate change will affect this complex interface. Biochemical processes<br />

of denitrification, in which nitrates can be reduced <strong>to</strong> nitrogen in anoxic environments, will be<br />

just one of the processes affected. The Commission was provided with evidence of the operational<br />

challenges of nitrate in groundwater in North Norfolk.<br />

Reduced aquifer levels and freshwater flows, coupled with rising sea levels, may allow the ingress<br />

of salt water upstream in estuaries, potentially affecting freshwater environments where excess salt<br />

concentrations can affect the usability of water for irrigation and for potable water supplies. Rising<br />

salt concentrations will also impact on the biodiversity of affected freshwater ecosystems.<br />

Sediment can also be a major problem; it may be washed off land during intense rainfall. It can<br />

reduce the clarity of water, blanket organisms that live in the bot<strong>to</strong>m of water bodies, smother<br />

plants, congest the gills of fish and smother the gravel-based spawning grounds of fish such as<br />

salmon and trout. The Commission saw efforts in the River Glaven catchment sensitive farming<br />

management project <strong>to</strong> reduce the sediment burden (Box 3D).<br />

If agricultural practices change as a result of climate change, the types and amounts of fertilisers<br />

or pesticides which find their way in<strong>to</strong> water through run-off could also change, with implications<br />

for river chemistry and biology.<br />

Drought<br />

2.58 The climate projections suggest drier summers, and so droughts may become more prevalent. The<br />

implications for water supply for the natural environment and for domestic, agricultural, industrial<br />

and recreational use will be significant.<br />

21<br />

Chapter 2

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