The Ringlet is widespread and common in Britain, and continuing to extend its range although it is still absent in north-west England
and the highlands of Scotland. There is some evidence of a decline in the 19th century from the industrial areas like London which may suggest that pollution
was a factor and that cleaner air had enabled the butterfly to re-expand in the last century (Asher et al.). Although
many colonies have been lost through over-zealous cutting of vegetation, new areas are being colonised probably through climate change. Since the 1970s its
distribution has expanded coupled with more than a triple increase in abundance. This butterfly is one of our most successful in Hertfordshire and Middlesex in its distribution and population
with numbers increasing at a good rate (Wood, 2016) although abundance has declined to about half of that in the 2015-19 period perhaps due to the
drier summers.
This species is found on tall, lush grassland near hedgerows, edges of woodland and woodland rides. It is scarcer in the drier areas and on arable land.
Earliest records suggest that the butterfly was common and widespread. Matthews noted it in the 1890s at Stevenage (Gibbs)
and Palmer found many in the Knebworth woods in the 1920s. It was described as 'fairly common and widespread' by Waterton in his
1970-81 report.
Local Distribution and Abundance
As indicated on the map, the Ringlet is widespread in the Stevenage area with the highest populations in the Knebworth woods complex, Fairlands Valley Park
and Great Ashby Park. An estimated 400 individuals were seen at Norton Green Common on 13 July 2001 by Trevor Chapman. On 1 July 2009, Ken King counted 241
specimens at Knebworth Park on his transect. There could be an association between early summer weather and the abundance of the Ringlet in the
following year: higher temperatures and less rainfall in early summer tends to adversely affect the butterfly in some way, e.g. reduced reproductive
potential of emerging females and laying fewer healthy eggs for the following year's generation. The drought in 2022 appears to have had a detrimental effect
on this species because there were far fewer specimens reported in 2023 and a shorter flight period than normal.
Stevenage (South Fairlands Valley Park) transect 1993-2025
This species is now taking a turn for the worse since the heights of 2017 before when
abundance was increasing. The butterfly also endured significant downturns in 2004, 2007 and 2015. The summers of 2003 and
2006 were hot and dry which may have had an effect on numbers in the following year but the declines were not so apparent elsewhere in the county. The early
summers of 2014, 2017, 2018 and the spring of 2020 were warm and dry which may have withered the larval foodplants but I suspect that changes in the grass
cutting regime in the park and lack of management in the woods are factors too. The long drought in 2022 appeared not to have impacted in terms of numbers
flying in the summer unlike the closely related Meadow Brown. However, the season in 2023 turned out to be the worst this century.
Weekly totals
Knebworth Park transect 1996-2010 and 2017-2025
Clearly, numbers were increasing as shown on the graph for 1996 until 2010. Some of the warmer
summers in the 2000s had a negative impact on numbers in the following year, most significantly so in 2009 to 2010. Perhaps the abundance in 2009 was so high
that the carrying capacity in the habitat was exceeded. The fact there was a slight increase in abundance in both 2018 and 2019 compared to the previous year
seems to suggest that the habitat and the ecosystem therein, in which the Ringlet is mostly seen, in the north-western section of the park, was not affected
by the warm and dry early summers in 2017 and 2018 in the same way as on the Stevenage transect. In 2020, numbers fell dramatically not only probably because
of the impact of the spring drought on the larval foodplants but also the excessive grazing by deer (presence of many deer droppings) leaving fewer tall
tussocks of grass which the butterfly seem to prefer. There was a good pick up in numbers in 2022 in spite of the drought like what occurred in the Stevenage
transect.
Weekly totals
Knebworth Woods transect 2017-2025
This is common and seen in all sections although most plentiful in Norton Green Common. The significant rise
in numbers in 2019 is probably partly due to the cutting regime in the meadow during the previous winter when many scrubs and small trees were cut. 2022 saw
a record year for this butterfly in terms of abundance with 101 counted on 3 July. On the other hand, 2023 was the worst year in terms of
numbers probably because of the long drought in the previous year impacting the development of larvae on desiccated grasses - also see notes for the
Stevenage transect above.
Weekly totals
Pryor's Wood transect 2000-2022
It is common at this site. 2019 was the best year with 145 specimens counted including 41 on 8 July.
Life History
Earliest date: 6 June 2015 at GlaxoSmithKline, Stevenage Latest date: 31 August 2014 at Walkern
One generation is produced
each year with the first adults usually emerging in the last week of June. The peak period is in the middle of July and very few specimens are on the wing
after the first week of August. Females drop their eggs among the tall vegetation. By the end of July, larvae emerge and feed on the grass leaves before
entering hibernation for the winter. Feeding resumes in the spring. Pupae are formed in a cocoon at the base of a grass tussock in June.
One of the few butterflies which flies in the rain. Its dark colouring and bobbling flight over the vegetation are diagnostic for the Ringlet although
a faded specimen might be confused with a male Meadow Brown. When fresh, the white fringe on the wings is clearly visible. It regularly rests and feeds on
flowers and taking photographs of the butterfly should be straightforward. Early morning is the best time for upperside shots.
Variations/Aberrations
The number and patterns of the eyespots, especially on the undersides, vary for this butterfly. The 'ringlets' may become elongated
and appear pear-shaped which is classified as ab. lanceolata. I found a specimen where three white-centred ocelli were present on
the forewing at Norton Green on 29 June 2025 known as aberration hyperophthalma
Asher, J., Warren, M., Fox, R., Harding, P., Jeffcoate, G. and Jeffcoate, S. (2001). The Millennium Atlas of Butterflies in Britain and Ireland, Oxford University Press, Oxford
Brereton et al. (2019)
Brereton, T.M., Botham, M.S., Middlebrook, I., Randle, Z., Noble D., Harris, S., Dennis, E.B., Robinson, A.E., Peck, K. &
Roy, D.B. (2019). United Kingdom Butterfly Monitoring Scheme report for 2018. Centre for Ecology & Hydrology & Butterfly Conservation, British Trust
for Ornithology and Joint Nature Conservation Committee. UKBMS Annual Report 2018
Fox et al. (2023)
Fox R, Dennis EB, Purdy KM, Middlebrook I, Roy DB, Noble DG, Botham MS & Bourn NAD (2023). The State of the UK's
Butterflies 2022, Butterfly Conservation, Wareham, UK. Butterfly Conservation website
Gibbs (1902)
Gibbs, A.E. (1902) edited by Page,W. in 'Lepidoptera'. The Victoria History of the County of Hertford, Vol 1 pp. 148-153, Archibald Constable, London
UKBMS (2024)
UKBMS (2024). 2024 Summary of Changes table for the UK, Butterfly Conservation, the UK Centre for Ecology and Hydrology, British Trust for Ornithology,
and the Joint Nature Conservation Committee UKBMS 2024 Summary of Changes
Waterton (1982)
Waterton, P. (1982). The Status and Distribution of Butterflies in Hertfordshire 1970-81, Transactions of the Hertfordshire Natural History Society Vol 29 pp. 111-119
Wood (2016)
Wood, A. (2016). Butterflies of Hertfordshire and Middlesex, Hertfordshire Natural History Society, St. Albans
Wood (2025)
Wood, Andrew (2025). Hertfordshire and Middlesex Butterflies 2024, Hertfordshire and Middlesex Branch of Butterfly Conservation February 2025