This is an archive of the Countryside Survey 2000 website. It is not being updated.
Click here for the current Countryside Survey website.

Accounting for Nature: Assessing habitats in the UK countryside
2.   The National Picture
















 

Conclusions

2.39 In this chapter, some of the key national trends that emerge from the analyses of CS2000 and NICS2000 information have been presented. Some of the changes we have seen in Great Britain between 1990 and 1998 differ markedly from those observed prior to 1990.

2.40 In England and Wales, the area of the Broadleaved Woodland and Built-up Broad Habitats both increased by 4% and 5%, respectively, reflecting policies for woodland planting and the impact of urban growth. Less expected was the 17% decline in the semi-natural Acid Grassland Broad Habitat. In Scotland, Broadleaved Woodland showed an even bigger increase of 9%, along with a 19% increase in the semi-natural Fen, Marsh and Swamp Broad Habitat. For Great Britain as a whole there was an 18% loss of Calcareous Grassland, a habitat of conservation importance.

Box 2.2: Year-to-year variations in vegetation

A total of 158 vegetation plots were recorded at ten of the Environmental Change Network (ECN) sites, 107 of which had been monitored for at least four consecutive years up to, and including 1999.

The range of vegetation conditions found at the ECN sites is narrower than that recorded in the CS2000 field survey because the sample is much smaller. However, these data are valuable because they help us understand how variable these measures are from year to year, and whether these differences are as large as the changes recorded by successive Countryside Surveys.

[Click on the graph to reveal the underlying data]

[Note: In the printed version of this report, the values on the x-axis are incorrect. The correct values are shown above].

Each of the condition measures described in Box 2.1 can be calculated using the data from ECN sites. The largest differences between years were found in species richness (see graph opposite); other condition measures were more stable. As would be expected, the highest variability was seen in arable fields and agricultural grasslands, where weed species can come and go from one year to the next. Some of this variability is likely to have been caused by climatic factors.

Some changes between years reflected longer term trends seen in CS2000. In particular, in infertile grasslands there was a relative increase in species adapted to high nutrient levels between 1997 and 1999, consistent with on-going eutrophication.

Year to year variation cannot by itself account for most of the long-term changes in CS2000 between 1990 and 1998. It is, however, an important issue, on which further work is required over longer time spans. In the context of CS2000, the ECN Study will provide valuable background information that can help with the more detailed interpretation of the results of the Survey.

Visit the ECN web site:www.ecn.ac.uk

2.41 In Northern Ireland there have been decreases of the Arable and Horticultural and Calcareous Grassland, and gains in Broadleaved Woodland Broad Habitats. Improved Grassland has increased largely by the more intensive agricultural use of formerly Neutral Grassland. Given the high conservation status of some hay meadows included in Neutral Grassland, the process of decline deserves investigation.

2.42 One of the most significant results of CS2000 concerns landscape features, such as hedges, walls and lowland ponds, used in the Government’s Quality of Life Counts indicator. Overall, the indicator for landscape features shows that in Great Britain the decline in length of hedges and walls reported for the 1980s has been halted. In the case of hedges in England and Wales, there is some evidence that losses in the early 1990s have been reversed. Lowland ponds show a small net increase. However, in Northern Ireland the stock of hedges and earth banks declined.

2.43 The overall analysis of vegetation condition in Great Britain shows very marked trends towards increasing levels of nutrient availability – or eutrophication – and conditions, which favour tall, competitive plants especially on linear features. These trends were evident in the majority of vegetation types and especially in the semi-natural vegetation types important for biodiversity – infertile grassland, upland wooded, moorland grass and heath and bog vegetation. A different trend towards lower nutrient levels and more competitive plants was shown in the vegetation of crops and weeds, perhaps showing the effects of set-aside and arable-ley rotations.

2.44 The Government’s Quality of Life Counts indicator for plant diversity shows that changes in plant diversity have reduced in magnitude since the 1980s, but during the 1990s losses have been mostly associated with the vegetation found in managed agricultural grasslands, field boundaries and verges. Perhaps of greatest concern is the continuing decline in plant diversity in infertile grassland – the vegetation typical of wildflower meadows and species-rich banks and verges. A more detailed analysis of these changes is presented for each of the Broad Habitats in the Chapters that follow.

[ Previous ] [ Contents ] [ Chapter 2 contents ] [ Next ]


Latest information on Countryside Survey (2007)

HOME | WEB SITE OVERVIEW | SEARCH | CONTACT | WHAT'S NEW  | REPORT | RESULTS & DATA
THE SURVEY
| RESEARCHNEWSLETTER | SPONSORS | LINKS | COPYRIGHT

E-mail:
countrysidesurvey@ceh.ac.uk   

© Crown/NERC                      This page was last updated on 30 March 2007