Short Description
This indicator will use regularly collected data to track changes in relative abundance and/or distribution of species which are widespread and characteristic of different broad habitats in England including birds, bats, butterflies, moths, other invertebrates, and plants. The indicator will have 2 components: (a) changes in the relative abundance of those widespread species for which relevant data are available; and (b) changes in the distribution (the number of 1 km grid squares in which species are recorded in any given year) of widespread species for which relevant data are available.
Readiness and links to data
This indicator is not available for reporting in 2023 in a finalised form. An interim indicator is presented here that shows trends in the abundance of (a) breeding wild birds, (b) widespread butterflies and (c) widespread bats in England. The expectation is that this indicator will be expanded to include more species groups and habitat types in the future. Some data are already published annually elsewhere (wild birds, butterflies on farmland and in woodland, and bats), and methods for analysing trends in plants are being developed. Further work is required to combine and present trends for different species groups and habitat types within the abundance and distribution measures in this indicator.
Notes on indicator
While the overall trends for the composite indices presented in this indicator are clear from the charts, they mask the trends for individual species within each index – some farmland and woodland species trends have increased whereas others have either remained the same or decreased over time. Further details on these individual species trends are available in the source publications.
Due to COVID-19 restrictions in England, the Breeding Bird Survey report prepared by the British Trust for Ornithology, the RSPB and the Joint Nature Conservation Committee collected limited data in 2020 and therefore it was not possible to update the indicators for breeding wild birds in woodland and on farmland in England in the 2022 update of the Outcome Indicator Framework.
While the most recent Breeding Bird Survey was able to collect sufficient data in 2021 to update the woodland and farmland indicators in the source publication, the data were released too late to be included in the 2023 update of this indicator. Therefore, the latest data on farmland and woodland birds can be found in the Wild bird populations in England release.
Indicator components
Figure D4ai: Trends in abundance of breeding wild birds in woodland in England, 1970 to 2019
Table D4ai: Trends in abundance of breeding wild birds in woodland in England, 1970 to 2019
Year | 95% confidence interval lower bound | 95% confidence interval upper bound | Smoothed index | Unsmoothed index |
---|---|---|---|---|
1970 | 100.00 | 100.00 | 100.00 | 100.00 |
1971 | 102.07 | 104.52 | 103.20 | 106.10 |
1972 | 103.72 | 108.76 | 105.88 | 112.48 |
1973 | 104.11 | 110.94 | 107.10 | 110.99 |
1974 | 102.97 | 111.48 | 106.96 | 110.60 |
1975 | 101.48 | 111.37 | 105.86 | 110.89 |
1976 | 99.48 | 110.17 | 104.13 | 103.94 |
1977 | 97.49 | 108.41 | 102.06 | 110.21 |
1978 | 95.39 | 106.22 | 99.67 | 101.63 |
1979 | 94.02 | 104.54 | 98.06 | 93.59 |
1980 | 93.37 | 104.05 | 97.91 | 104.52 |
1981 | 93.73 | 104.15 | 98.08 | 105.70 |
1982 | 93.39 | 103.89 | 97.90 | 96.31 |
1983 | 92.69 | 103.94 | 97.67 | 102.86 |
1984 | 91.77 | 103.40 | 96.92 | 102.76 |
1985 | 90.19 | 102.14 | 95.41 | 101.53 |
1986 | 88.80 | 100.44 | 93.78 | 90.28 |
1987 | 88.28 | 99.91 | 93.21 | 92.74 |
1988 | 88.01 | 100.08 | 93.33 | 98.22 |
1989 | 87.25 | 99.74 | 92.57 | 100.42 |
1990 | 85.11 | 97.45 | 90.14 | 94.78 |
1991 | 81.97 | 93.84 | 86.79 | 86.19 |
1992 | 79.09 | 90.48 | 83.88 | 83.70 |
1993 | 76.87 | 88.66 | 82.00 | 84.03 |
1994 | 75.68 | 87.37 | 80.90 | 84.30 |
1995 | 74.69 | 86.42 | 80.29 | 80.05 |
1996 | 73.93 | 85.72 | 79.86 | 84.26 |
1997 | 73.70 | 85.96 | 79.60 | 79.21 |
1998 | 74.07 | 86.61 | 79.79 | 81.61 |
1999 | 74.29 | 87.16 | 80.05 | 82.56 |
2000 | 74.02 | 87.38 | 79.73 | 83.95 |
2001 | 73.05 | 86.59 | 78.64 | 81.04 |
2002 | 71.25 | 85.11 | 77.38 | 77.32 |
2003 | 70.51 | 84.21 | 76.64 | 77.59 |
2004 | 70.50 | 83.81 | 76.59 | 77.88 |
2005 | 71.06 | 83.95 | 76.98 | 79.83 |
2006 | 71.49 | 84.59 | 77.32 | 80.47 |
2007 | 71.52 | 84.97 | 77.39 | 79.67 |
2008 | 71.25 | 85.25 | 77.46 | 79.30 |
2009 | 71.16 | 85.82 | 77.88 | 73.59 |
2010 | 71.80 | 87.07 | 78.79 | 79.67 |
2011 | 72.26 | 87.28 | 79.33 | 86.13 |
2012 | 71.82 | 86.60 | 78.58 | 81.47 |
2013 | 70.48 | 85.06 | 77.08 | 72.77 |
2014 | 69.62 | 84.35 | 75.96 | 78.00 |
2015 | 68.92 | 83.07 | 75.11 | 78.55 |
2016 | 68.09 | 81.93 | 74.24 | 76.51 |
2017 | 67.05 | 80.80 | 73.34 | 73.74 |
2018 | 66.13 | 79.24 | 72.45 | 72.77 |
2019 | 64.00 | 78.22 | 71.27 | 73.23 |
Trend description for D4ai
The indicator for breeding wild birds in woodland in England has declined by almost 30% between 1970 and 2019.
Assessment of change
Indicators for breeding wild birds in England are also reported in the England Biodiversity Indicators, which presents a short and long-term assessment for the same time periods used in this Outcome Indicator Framework assessment. These assessment results were reused here as the England Biodiversity Indicators method is tailored to the datasets of the specific taxonomic group (birds) and factors-in information on confidence. The assessment found a decrease (deterioration) in the abundance of breeding wild birds in woodland in England over the short and long-term periods. No medium-term assessment results are available for this indicator using the England Biodiversity Indicators methodology and it cannot be used to assess change since 2018.
Details on the England Biodiversity Indicators assessment methododology for this indicator can be found in sections 5 and 6 of the latest England Biodiversity Indicators report. Further information on the standard assessment used in the Outcome Indicator Framework, along with details on the methodology, is provided in the Assessment background page. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results pages.
Table D4ai: Assessment of change
Component | Subcomponent | Period | Date range | Percentage change | Smoothing function | Assessment of change |
---|---|---|---|---|---|---|
D4ai | Breeding wild birds in woodland | Short term | 2013 to 2018 | -6.01 | Smoothed data | Deterioration |
D4ai | Breeding wild birds in woodland | Medium term | N/A | N/A | N/A | Not assessed |
D4ai | Breeding wild birds in woodland | Long term | 1970 to 2018 | -27.55 | Smoothed data | Deterioration |
Note that smoothed data presented in Figure D4ai were used for percentage change calculations. The smoothing method is specific to this indicator and differs from the default Loess smoothing approach adopted for most indicators for the Outcome Indicator Framework assessment. Percentage change figures in Table D4ai may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen between the first and last years in the specified date range.
Figure D4aii: Trends in abundance of breeding wild birds on farmland in England, 1970 to 2019
Table D4aii: Trends in abundance of breeding wild birds on farmland in England, 1970 to 2019
Year | 95% confidence interval lower bound | 95% confidence interval upper bound | Smoothed index | Unsmoothed index |
---|---|---|---|---|
1970 | 100.00 | 100.00 | 100.00 | 100.00 |
1971 | 97.27 | 100.58 | 98.97 | 103.74 |
1972 | 95.33 | 101.55 | 98.59 | 104.32 |
1973 | 93.95 | 103.16 | 98.87 | 101.12 |
1974 | 94.18 | 105.30 | 100.16 | 101.93 |
1975 | 95.36 | 108.37 | 102.16 | 105.97 |
1976 | 96.18 | 110.56 | 103.60 | 109.95 |
1977 | 95.55 | 110.28 | 103.25 | 111.96 |
1978 | 92.26 | 107.60 | 100.70 | 103.75 |
1979 | 88.72 | 103.66 | 96.77 | 97.91 |
1980 | 84.14 | 98.85 | 92.26 | 97.18 |
1981 | 79.60 | 93.84 | 87.32 | 92.20 |
1982 | 74.26 | 88.91 | 82.29 | 81.66 |
1983 | 70.06 | 84.55 | 77.90 | 80.63 |
1984 | 66.42 | 80.53 | 73.97 | 80.03 |
1985 | 62.55 | 76.55 | 70.12 | 73.56 |
1986 | 59.04 | 73.35 | 66.69 | 67.58 |
1987 | 56.73 | 71.65 | 64.36 | 64.60 |
1988 | 55.31 | 70.42 | 63.25 | 64.59 |
1989 | 54.85 | 69.41 | 62.76 | 66.55 |
1990 | 53.91 | 68.04 | 61.93 | 68.23 |
1991 | 51.76 | 66.11 | 60.16 | 63.35 |
1992 | 49.67 | 63.91 | 57.81 | 59.14 |
1993 | 47.92 | 61.56 | 55.70 | 53.50 |
1994 | 47.01 | 60.23 | 54.51 | 56.18 |
1995 | 46.68 | 59.61 | 53.99 | 58.13 |
1996 | 45.97 | 58.65 | 53.44 | 56.84 |
1997 | 45.09 | 57.90 | 52.57 | 55.32 |
1998 | 44.45 | 56.95 | 51.59 | 52.58 |
1999 | 43.89 | 56.12 | 50.89 | 52.01 |
2000 | 43.74 | 55.55 | 50.63 | 52.85 |
2001 | 43.80 | 55.54 | 50.69 | 52.99 |
2002 | 43.95 | 55.77 | 50.88 | 53.02 |
2003 | 43.99 | 55.93 | 51.03 | 52.99 |
2004 | 43.87 | 56.18 | 50.97 | 53.29 |
2005 | 43.49 | 55.72 | 50.51 | 53.60 |
2006 | 42.72 | 54.62 | 49.56 | 52.83 |
2007 | 41.71 | 53.25 | 48.36 | 48.29 |
2008 | 40.92 | 52.08 | 47.38 | 49.72 |
2009 | 40.21 | 51.38 | 46.67 | 47.32 |
2010 | 39.66 | 50.70 | 46.18 | 47.78 |
2011 | 39.10 | 49.96 | 45.65 | 48.19 |
2012 | 38.34 | 49.05 | 44.82 | 48.65 |
2013 | 37.46 | 48.00 | 43.79 | 43.62 |
2014 | 36.79 | 47.29 | 43.00 | 43.91 |
2015 | 36.35 | 46.72 | 42.49 | 45.52 |
2016 | 36.09 | 46.29 | 42.02 | 42.95 |
2017 | 35.54 | 45.48 | 41.56 | 44.36 |
2018 | 34.98 | 44.78 | 40.98 | 41.94 |
2019 | 34.29 | 44.34 | 40.35 | 42.23 |
Trend description for D4aii
The indicator for breeding wild birds on farmland in England has declined by almost 60% between 1970 and 2019. Farmland birds experienced steeper declines during the late 1970’s and early 1980’s because of rapid changes in farmland management.
Assessment of change
Indicators for breeding wild birds in England are also reported in the England Biodiversity Indicators, which presents a short and long-term assessment for the same time periods used in this Outcome Indicator Framework assessment. These assessment results were reused here as the England Biodiversity Indicators method is tailored to the datasets of the specific taxonomic group (birds) and factors-in information on confidence. The assessment found a decrease (deterioration) in breeding wild birds on farmland in England over the short and long-term periods. No medium-term assessment results are available for this indicator using the England Biodiversity Indicators methodology and it cannot be used to assess change since 2018.
Details on the England Biodiversity Indicators assessment methodology for this indicator can be found in sections 5 and 6 of the latest England Biodiversity Indicators report. Further information on the standard assessment used in the Outcome Indicator Framework, along with details on the methodology, is provided in the Assessment background page. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results pages.
Table D4aii: Assessment of change
Component | Subcomponent | Period | Date range | Percentage change | Smoothing function | Assessment of change |
---|---|---|---|---|---|---|
D4aii | Breeding wild birds on farmland | Short term | 2013 to 2018 | -6.41 | Smoothed data | Deterioration |
D4aii | Breeding wild birds on farmland | Medium term | N/A | N/A | N/A | Not assessed |
D4aii | Breeding wild birds on farmland | Long term | 1970 to 2018 | -59.02 | Smoothed data | Deterioration |
Note that smoothed data presented in Figure D4aii were used for percentage change calculations. The smoothing method is specific to this indicator and differs from the default Loess smoothing approach adopted for most indicators for the Outcome Indicator Framework assessment. Percentage change figures in Table D4aii may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen between the first and last years in the specified date range.
Figure D4bi: Trends in abundance of widespread butterflies in woodland in England, 1990 to 2021
Table D4bi: Trends in abundance of widespread butterflies in woodland in England, 1990 to 2021
Year | 95% confidence interval lower bound | 95% confidence interval upper bound | Smoothed index | Unsmoothed index |
---|---|---|---|---|
1990 | 81.61 | 106.03 | 93.82 | 100.00 |
1991 | 79.93 | 100.76 | 90.34 | 90.36 |
1992 | 77.86 | 95.92 | 86.89 | 110.40 |
1993 | 75.42 | 91.52 | 83.47 | 55.72 |
1994 | 72.75 | 87.59 | 80.17 | 65.16 |
1995 | 69.95 | 84.07 | 77.01 | 86.90 |
1996 | 67.04 | 80.82 | 73.93 | 85.11 |
1997 | 64.12 | 77.76 | 70.94 | 94.62 |
1998 | 61.25 | 74.86 | 68.06 | 58.21 |
1999 | 58.57 | 72.17 | 65.37 | 49.89 |
2000 | 56.14 | 69.75 | 62.94 | 50.00 |
2001 | 54.00 | 67.60 | 60.80 | 48.19 |
2002 | 52.13 | 65.71 | 58.92 | 56.23 |
2003 | 50.46 | 64.03 | 57.25 | 70.79 |
2004 | 48.94 | 62.49 | 55.71 | 73.45 |
2005 | 47.53 | 61.07 | 54.30 | 55.72 |
2006 | 46.26 | 59.80 | 53.03 | 56.23 |
2007 | 45.16 | 58.72 | 51.94 | 36.81 |
2008 | 44.28 | 57.85 | 51.07 | 35.16 |
2009 | 43.62 | 57.21 | 50.41 | 55.21 |
2010 | 43.12 | 56.72 | 49.92 | 62.95 |
2011 | 42.76 | 56.36 | 49.56 | 55.72 |
2012 | 42.53 | 56.13 | 49.33 | 29.24 |
2013 | 42.46 | 56.06 | 49.26 | 57.54 |
2014 | 42.48 | 56.12 | 49.30 | 50.81 |
2015 | 42.55 | 56.33 | 49.44 | 49.20 |
2016 | 42.60 | 56.74 | 49.67 | 35.56 |
2017 | 42.55 | 57.41 | 49.98 | 46.77 |
2018 | 42.25 | 58.39 | 50.32 | 66.99 |
2019 | 41.57 | 59.69 | 50.63 | 58.48 |
2020 | 40.44 | 61.35 | 50.90 | 58.61 |
2021 | 38.86 | 63.39 | 51.13 | 39.72 |
Trend description for D4bi
The indicator for widespread butterflies in woodland in England declined between 1990 and 2010, more steeply than the decline seen in the farmland butterflies indicator. However, in recent years, the woodland butterfly indicator has shown little change.
Assessment of change
Indicators for widespread butterflies in England are also reported in the England Biodiversity Indicators, which presents a short, medium and long-term assessment for the same time periods used in this Outcome Indicator Framework assessment. These assessment results were reused here as the England Biodiversity Indicators method is tailored to the datasets of the specific taxonomic group (butterflies) and factors-in information on confidence. There was little or no change in the abundance of widespread butterflies in woodland over the short and medium-term assessment periods. Over the long-term period, decreases in widespread butterflies in woodland were recorded.
Change since 2018 has also been assessed using the England Biodiversity Indicators methodology. Little or no change was seen since 2018 for woodland butterflies. However, this is based on 4 data points so should be considered as indicative and not evidence of a clear trend.
Details on the England Biodiversity Indicators assessment methodology for this indicator can be found in sections 5 and 6 of the latest England Biodiversity Indicators report. Further information on the standard assessment used in the Outcome Indicator Framework, along with details on the methodology, is provided in the Assessment background page. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results pages.
Table D4bi: Assessment of change
Component | Subcomponent | Period | Date range | Percentage change | Smoothing function | Assessment of change |
---|---|---|---|---|---|---|
D4bi | Widespread butterflies in woodland | Short term | 2016 to 2021 | 2.94 | Smoothed data | Little or no change |
D4bi | Widespread butterflies in woodland | Medium term | 2011 to 2021 | 3.16 | Smoothed data | Little or no change |
D4bi | Widespread butterflies in woodland | Long term | 1990 to 2021 | -45.51 | Smoothed data | Deterioration |
Note that smoothed data presented in Figure D4bi were used for percentage change calculations. The smoothing method is specific to this indicator and differs from the default Loess smoothing approach adopted for most indicators for the Outcome Indicator Framework assessment. Percentage change figures in Table D4bi may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen between the first and last years in the specified date range.
Figure D4bii: Trends in abundance of widespread butterflies on farmland in England, 1990 to 2021
Table D4bii: Trends in abundance of widespread butterflies on farmland in England, 1990 to 2021
Year | 95% confidence interval lower bound | 95% confidence interval upper bound | Smoothed index | Unsmoothed index |
---|---|---|---|---|
1990 | 95.21 | 123.05 | 109.13 | 100.00 |
1991 | 95.82 | 120.04 | 107.93 | 119.94 |
1992 | 96.06 | 117.37 | 106.72 | 125.31 |
1993 | 95.94 | 115.04 | 105.49 | 75.33 |
1994 | 95.53 | 113.04 | 104.29 | 89.74 |
1995 | 94.85 | 111.33 | 103.09 | 104.95 |
1996 | 93.94 | 109.80 | 101.87 | 116.41 |
1997 | 92.81 | 108.35 | 100.58 | 132.73 |
1998 | 91.52 | 106.92 | 99.22 | 99.77 |
1999 | 90.14 | 105.50 | 97.82 | 89.54 |
2000 | 88.75 | 104.11 | 96.43 | 94.41 |
2001 | 87.38 | 102.76 | 95.07 | 87.30 |
2002 | 86.07 | 101.48 | 93.77 | 85.90 |
2003 | 84.83 | 100.26 | 92.55 | 105.92 |
2004 | 83.67 | 99.11 | 91.39 | 103.99 |
2005 | 82.61 | 98.05 | 90.33 | 91.41 |
2006 | 81.68 | 97.12 | 89.40 | 92.26 |
2007 | 80.93 | 96.37 | 88.65 | 68.55 |
2008 | 80.41 | 95.84 | 88.12 | 64.86 |
2009 | 80.13 | 95.54 | 87.84 | 93.11 |
2010 | 80.08 | 95.47 | 87.77 | 95.72 |
2011 | 80.23 | 95.59 | 87.91 | 87.30 |
2012 | 80.57 | 95.93 | 88.25 | 53.70 |
2013 | 81.10 | 96.50 | 88.80 | 104.23 |
2014 | 81.71 | 97.26 | 89.48 | 101.15 |
2015 | 82.35 | 98.22 | 90.28 | 93.33 |
2016 | 82.93 | 99.43 | 91.18 | 70.63 |
2017 | 83.39 | 100.94 | 92.17 | 89.33 |
2018 | 83.63 | 102.77 | 93.20 | 109.90 |
2019 | 83.54 | 104.92 | 94.23 | 109.90 |
2020 | 83.08 | 107.39 | 95.24 | 101.15 |
2021 | 82.27 | 110.20 | 96.23 | 86.90 |
Trend description for D4bii
The indicator for widespread butterflies on farmland in England declined between 1990 and 2010. However, in recent years, the farmland butterfly indicator has increased to a figure similar to its 1990 baseline value.
Assessment of change
Indicators for widespread butterflies in England are also reported in the England Biodiversity Indicators, which presents a short, medium and long-term assessment for the same time periods used in this Outcome Indicator Framework assessment. These assessment results were reused here as the England Biodiversity Indicators method is tailored to the datasets of the specific taxonomic group (butterflies) and factors-in information on confidence. The assessment found little or no change in the abundance of widespread butterflies on farmland over the short, medium term and long term.
Change since 2018 has also been assessed using the England Biodiversity Indicators methodology. Little or no change was seen since 2018 for farmland butterflies. However, this is based on 4 data points so should be considered as indicative and not evidence of a clear trend.
Details on the England Biodiversity Indicators assessment methodology for this indicator can be found in sections 5 and 6 of the latest England Biodiversity Indicators report. Further information on this assessment, along with details on the methodology, is provided in the Assessment background page. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results pages.
Table D4bii: Assessment of change
Component | Subcomponent | Period | Date range | Percentage change | Smoothing function | Assessment of change |
---|---|---|---|---|---|---|
D4bii | Widespread butterflies on farmland | Short term | 2016 to 2021 | 5.54 | Smoothed data | Little or no change |
D4bii | Widespread butterflies on farmland | Medium term | 2011 to 2021 | 9.47 | Smoothed data | Little or no change |
D4bii | Widespread butterflies on farmland | Long term | 1990 to 2021 | -11.82 | Smoothed data | Little or no change |
Note that smoothed data presented in Figure D4bii were used for percentage change calculations. The smoothing method is specific to this indicator and differs from the default Loess smoothing approach adopted for most indicators for the Outcome Indicator Framework assessment. Percentage change figures in Table D4bii may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen between the first and last years in the specified date range.
Figure D4c: Trends in abundance of bats in England, 1999 to 2020
Table D4c: Trends in abundance of bats in England, 1999 to 2020
Year | 95% confidence interval lower bound | 95% confidence interval upper bound | Smoothed index | Unsmoothed index |
---|---|---|---|---|
1999 | 100.00 | 100.00 | 100.00 | 100.00 |
2000 | 99.98 | 104.51 | 102.62 | 97.19 |
2001 | 100.50 | 108.90 | 105.18 | 103.91 |
2002 | 101.01 | 112.60 | 107.20 | 96.01 |
2003 | 102.49 | 116.78 | 110.03 | 105.29 |
2004 | 104.80 | 121.96 | 113.65 | 106.60 |
2005 | 108.11 | 126.82 | 117.69 | 113.31 |
2006 | 110.75 | 130.87 | 121.32 | 115.47 |
2007 | 113.53 | 134.00 | 124.11 | 116.57 |
2008 | 115.32 | 136.48 | 125.91 | 122.60 |
2009 | 116.16 | 137.07 | 126.48 | 121.18 |
2010 | 116.51 | 137.33 | 126.41 | 116.55 |
2011 | 117.22 | 137.43 | 126.65 | 122.08 |
2012 | 117.71 | 138.74 | 127.40 | 115.74 |
2013 | 119.02 | 140.65 | 129.28 | 126.32 |
2014 | 120.85 | 143.51 | 131.90 | 118.73 |
2015 | 123.57 | 147.16 | 135.18 | 134.10 |
2016 | 125.74 | 150.24 | 137.69 | 129.79 |
2017 | 127.43 | 153.24 | 139.61 | 131.57 |
2018 | 129.09 | 155.37 | 141.60 | 134.10 |
2019 | 129.98 | 159.02 | 143.88 | 137.07 |
2020 | 131.08 | 162.88 | 146.48 | 139.64 |
Trend description for D4c
The indicator for widespread bats in England has increased by approximately 40% since the turn of the century. The bat species within this index vary in their habitat requirements, but all occur in farmland and woodland landscapes.
Assessment of change
Indicators for breeding wild birds in England are also reported in the England Biodiversity Indicators, which presents a short and long-term assessment for the same time periods used in this Outcome Indicator Framework assessment. These assessment results were reused here as the England Biodiversity Indicators method is tailored to the datasets of the specific taxonomic group (bats) and factors-in information on confidence. There was an increase (improvement) in the abundance of widespread bats over the short and long-term assessment periods. No medium-term assessment results are available for this indicator using the England Biodiversity Indicators methodology and it cannot be used to assess change since 2018.
Details on the England Biodiversity Indicators assessment methodology for this indicator can be found in sections 5 and 6 of the latest England Biodiversity Indicators report. Further information on the standard assessment used in the Outcome Indicator Framework, along with details on the methodology, is provided in the Assessment background page. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results pages.
Table D4c: Assessment of change
Component | Subcomponent | Period | Date range | Percentage change | Smoothing function | Assessment of change |
---|---|---|---|---|---|---|
D4c | Abundance of widespread bats | Short term | 2014 to 2019 | 9.08 | Smoothed data | Improvement |
D4c | Abundance of widespread bats | Medium term | N/A | N/A | N/A | Not assessed |
D4c | Abundance of widespread bats | Long term | 1999 to 2019 | 43.88 | Smoothed data | Improvement |
Note that smoothed data presented in Figure D4c were used for percentage change calculations. The smoothing method is specific to this indicator and differs from the default Loess smoothing approach adopted for most indicators for the Outcome Indicator Framework assessment. Percentage change figures in Table D4c may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen between the first and last years in the specified date range.