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Organic nitrogen in UK rainfall (495Kb)

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<strong>Organic</strong> <strong>nitrogen</strong> <strong>in</strong> <strong>UK</strong> ra<strong>in</strong>fall<br />

Researchers usually measure the <strong>nitrogen</strong> content of<br />

ra<strong>in</strong> <strong>in</strong> terms of the concentrations of ammonium or<br />

nitrate ions. Plants can use this ‘<strong>in</strong>organic’ <strong>nitrogen</strong><br />

as a fertiliser, and soil microbes convert it <strong>in</strong>to gases<br />

such as <strong>nitrogen</strong>, nitrous oxide and nitric oxide. Too<br />

much <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong> can lead to some plant<br />

species, such as grasses, outgrow<strong>in</strong>g others, such<br />

as wild flowers. It can lead to higher nitrate levels <strong>in</strong><br />

streams and lakes, and more nitrous oxide, a<br />

greenhouse gas, be<strong>in</strong>g released <strong>in</strong>to the atmosphere.<br />

Until this GANE project started, we did not know<br />

how much organic <strong>nitrogen</strong> there was <strong>in</strong> ra<strong>in</strong>,<br />

although reports from other parts of the world, and<br />

occasional measurements <strong>in</strong> the <strong>UK</strong>, suggested that<br />

concentrations might be important.<br />

Over two years we took careful measurements,<br />

mak<strong>in</strong>g sure that microbes did not degrade the ra<strong>in</strong><br />

samples and birds did not contam<strong>in</strong>ate them. The<br />

measurements showed that around one third of the<br />

<strong>nitrogen</strong> <strong>in</strong> <strong>UK</strong> ra<strong>in</strong>fall is organic (see map). There is<br />

more organic <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong> <strong>in</strong> the west. This<br />

correlates with higher concentrations of ammonium<br />

<strong>in</strong> the atmosphere, suggest<strong>in</strong>g a biological source,<br />

such as agriculture.<br />

We do not yet know whether plants or soil microbes<br />

can use organic <strong>nitrogen</strong> <strong>in</strong> the same way as<br />

<strong>in</strong>organic <strong>nitrogen</strong>. However, researchers cannot<br />

ignore it when estimat<strong>in</strong>g the total deposition of<br />

<strong>nitrogen</strong> from the atmosphere.<br />

Ace Stock Ltd/Alamy


<strong>Organic</strong> <strong>nitrogen</strong> <strong>in</strong> <strong>UK</strong> ra<strong>in</strong>fall<br />

Neil Cape (Pr<strong>in</strong>cipal Investigator) and Margaret Anderson, Centre for Ecology & Hydrology Ed<strong>in</strong>burgh.<br />

Philip Rowland and David Wilson, Centre for Ecology & Hydrology Lancaster.<br />

What we found out<br />

<strong>Organic</strong> <strong>nitrogen</strong> makes up 24-40% of the<br />

total amount of dissolved <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong><br />

and snow across the <strong>UK</strong>. The fraction of<br />

water-soluble organic <strong>nitrogen</strong> was greatest<br />

at western sites, where ammonium<br />

concentrations <strong>in</strong> ra<strong>in</strong> were also higher.<br />

However, the seasonal pattern across all<br />

sites showed maximum concentrations of<br />

ammonium and nitrate <strong>in</strong> late spr<strong>in</strong>g, but<br />

maximum concentrations of water-soluble<br />

organic <strong>nitrogen</strong> <strong>in</strong> late summer (see graph<br />

on right). The processes lead<strong>in</strong>g to watersoluble<br />

organic <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong> are<br />

therefore different from those that emit<br />

ammonia <strong>in</strong>to the atmosphere.<br />

Why these results are important<br />

Policy-makers sett<strong>in</strong>g and assess<strong>in</strong>g critical<br />

loads for <strong>nitrogen</strong> deposition need to take<br />

<strong>in</strong>to account the high levels of watersoluble<br />

organic <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong> and snow.<br />

How we did it<br />

We measured the concentration of watersoluble<br />

organic <strong>nitrogen</strong> <strong>in</strong> ra<strong>in</strong> at seven<br />

sites across the <strong>UK</strong>, over a period of 1-2<br />

years. We collected ra<strong>in</strong>water <strong>in</strong><br />

cont<strong>in</strong>uously open sta<strong>in</strong>less steel funnels<br />

dra<strong>in</strong><strong>in</strong>g to a glass bottle over one to two<br />

weeks. We added thymol to preserve the<br />

ra<strong>in</strong>water dur<strong>in</strong>g and after collection. After<br />

chemical analysis, we excluded samples<br />

show<strong>in</strong>g signs of contam<strong>in</strong>ation (significant<br />

concentrations of potassium or phosphate<br />

ions). We used two methods to measure<br />

the total dissolved <strong>nitrogen</strong>: heat<strong>in</strong>g the<br />

sample with a strong oxidis<strong>in</strong>g agent<br />

(persulphate) to convert organic <strong>nitrogen</strong><br />

<strong>in</strong>to nitrate ions, which we then measured<br />

by conventional methods; and heat<strong>in</strong>g the<br />

sample to over 1000°C <strong>in</strong> oxygen, to<br />

convert all <strong>nitrogen</strong> compounds to nitric<br />

oxide (gas) which we then detected by the<br />

light it generates when it reacts with ozone<br />

– high temperature chemilum<strong>in</strong>escence.<br />

The latter generally gave the larger values,<br />

and we used it to assess the organic<br />

component of dissolved <strong>nitrogen</strong>.<br />

Weighted mean concentrations (_M) of <strong>in</strong>organic and total N <strong>in</strong><br />

precipitation (2000-2002)<br />

Data for total N are presented for both analytical methods:<br />

high temperature chemilum<strong>in</strong>escence and persulphate digestion/colorimetry<br />

Site Nitrate Ammonium total N organic N %organic persulph. organic N %<br />

total N (persulp.) organic<br />

Cairngorm<br />

North-east Scotland 30 14 58 14 24% 47 2 5%<br />

Bush<br />

East Scotland 15 16 46 15 33% 46 15 33%<br />

Merlewood<br />

North-west England 17 27 87 35 40% 64 12 18%<br />

Moor House<br />

North-west England 20 32 84 31 37% 69 16 23%<br />

Climoor<br />

North Wales 22 33 73 29 39% 61 16 27%<br />

Norwich University<br />

South-east England 38 58 129 33 26% 126 30 24%<br />

W<strong>in</strong>frith<br />

South-west England 23 26 75 23 31% 58 7 11%<br />

For more <strong>in</strong>formation contact:<br />

Neil Cape<br />

Centre for Ecology & Hydrology, Bush Estate<br />

Penicuik EH26 0QB.<br />

Tel: 0131 445 8533, email: jnc@ceh.ac.uk<br />

Shaded areas show organic fraction<br />

of N <strong>in</strong> ra<strong>in</strong>.Total area is proportional<br />

to total N concentration.<br />

Publications<br />

Water, Air and Soil Pollution: Focus (2004).<br />

See also: Cape et al., The Scientific World, 1,<br />

230-237 (2001)

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