C1: Clean seas: marine litter

Short Description

This indicator of clean seas shows changes in the amount of litter in the marine environment, including litter on beaches, on the seafloor and floating litter. Beach litter surveys are completed annually or quarterly and cover a representative number of beaches. Data from benthic trawl surveys, typically carried out for fish stock assessments, are used to monitor the amount of litter on the seafloor. After each tow, all litter items are emptied from the net and counted and classified. Beached fulmars or individuals accidentally killed are collected as part of a monitoring programme in the Greater North Sea to assess the plastics found in their stomachs. Fulmars forage exclusively at sea, generally at the surface of the water. The amount of plastic they ingest can be used as a proxy for the abundance of floating litter in their environment and how this is changing. Indicators for seafloor litter, beach litter and plastic found in fulmar stomachs have been developed and expert groups are working to improve the data. Additional monitoring programmes are being developed to record the amount of microplastics in sediment and in biota.

Readiness and links to data

This indicator is not available for reporting in 2024 in a finalised form. An interim indicator is presented here that shows 3 aspects of litter in the marine environment: a) beach litter b) plastic in fulmar stomachs and c) seafloor litter.

The beach litter component of this interim indicator is drawn from an assessment of beach litter, developed by the Marine Conservation Society for Defra (project code ME5438) to support reporting under the Convention for the Protection of the Marine Environment of the North-East Atlantic (OSPAR) and UK Marine Strategy. This replaces an assessment previously presented here, reported under the UK Marine Strategy in 2019. The newer assessment is considered to be more statistically robust, as it is based on quarterly surveys of the same subset of beaches, as opposed to annual surveys of often differing beaches.

Data on the litter content of fulmar stomachs are published in the latest research report from Wageningen University to Defra (project code ME5227).

Assessments of marine litter were conducted as part of the OSPAR Quality Status Report 2023. The revised assessment of seafloor litter was incorporated into this indicator as part of the 2023 update.

The Centre for Environment, Fisheries and Aquaculture Science (Cefas) are currently developing indicator methods for microplastics in marine sediment and biota, which will be incorporated in a future update to the Outcome Indicator Framework.

Indicator components

Figure C1a: Items of litter per 100m of beach, England, 2017 to 2022

Table C1a: Items of litter per 100m of beach, England, 2017 to 2022

Date Location code Lower ci values Observed values Smoothed values Upper ci values
2016-12-03 UK049 539.01 36.00 1,256.66 1,974.32
2016-12-18 UK043 581.58 1,031.00 1,261.39 1,941.20
2017-01-14 UK050 652.97 3,903.00 1,268.87 1,884.76
2017-01-15 UK020 655.48 1,375.00 1,269.12 1,882.75
2017-01-20 UK048 667.88 51.00 1,270.34 1,872.79
2017-04-02 UK043 816.51 1,826.00 1,281.64 1,746.77
2017-04-03 UK048 818.15 211.00 1,281.71 1,745.27
2017-04-08 UK050 826.17 2,614.00 1,282.00 1,737.83
2017-04-09 UK020 827.74 1,854.00 1,282.05 1,736.36
2017-06-10 UK049 900.02 105.00 1,279.51 1,659.00
2017-06-12 UK048 901.52 35.00 1,279.23 1,656.93
2017-06-18 UK043 905.71 874.00 1,278.31 1,650.91
2017-07-08 UK050 916.42 2,500.00 1,274.44 1,632.47
2017-07-09 UK020 916.83 737.00 1,274.22 1,631.61
2017-09-16 UK020 918.60 1,150.00 1,252.18 1,585.75
2017-09-16 UK049 918.60 72.00 1,252.18 1,585.75
2017-09-16 UK050 918.60 734.00 1,252.18 1,585.75
2017-09-17 UK043 918.29 2,619.00 1,251.77 1,585.25
2017-10-13 UK048 907.60 9.00 1,240.49 1,573.39
2017-12-16 UK050 864.96 2,112.00 1,207.55 1,550.15
2017-12-17 UK043 864.16 1,129.00 1,206.99 1,549.82
2018-01-14 UK020 841.05 6,867.00 1,190.77 1,540.48
2018-01-15 UK048 840.20 23.00 1,190.17 1,540.14
2018-02-24 UK049 804.06 218.00 1,163.29 1,522.52
2018-04-13 UK048 757.11 0.00 1,125.08 1,493.04
2018-04-14 UK050 756.11 999.00 1,124.23 1,492.36
2018-04-15 UK020 755.11 1,518.00 1,123.39 1,491.67
2018-04-21 UK049 749.09 150.00 1,118.29 1,487.49
2018-04-22 UK043 748.09 3,387.00 1,117.43 1,486.78
2018-06-03 UK049 706.26 287.00 1,080.81 1,455.36
2018-06-17 UK043 692.80 1,916.00 1,068.51 1,444.22
2018-06-22 UK048 688.10 73.00 1,064.13 1,440.17
2018-06-26 UK020 684.38 336.00 1,060.64 1,436.91
2018-06-30 UK050 680.69 580.00 1,057.10 1,433.52
2018-09-15 UK020 606.38 630.00 972.45 1,338.51
2018-09-15 UK043 606.38 1,408.00 972.45 1,338.51
2018-09-15 UK049 606.38 654.00 972.45 1,338.51
2018-09-15 UK050 606.38 1,894.00 972.45 1,338.51
2018-12-16 UK043 486.57 1,930.00 848.70 1,210.83
2019-01-13 UK020 443.44 286.00 810.76 1,178.07
2019-01-26 UK049 423.37 369.00 793.59 1,163.81
2019-02-15 UK048 393.34 14.00 768.01 1,142.68
2019-04-07 UK020 328.77 538.00 709.48 1,090.18
2019-04-13 UK049 322.59 115.00 703.18 1,083.76
2019-04-15 UK048 320.49 14.00 701.02 1,081.55
2019-04-20 UK050 315.13 292.00 695.52 1,075.90
2019-06-22 UK049 233.46 1,281.00 617.53 1,001.59
2019-07-06 UK050 212.03 292.00 599.59 987.16
2019-07-07 UK043 210.47 1,310.00 598.32 986.18
2019-07-14 UK020 199.52 410.00 589.51 979.50
2019-09-18 UK048 108.01 1,376.00 518.61 929.20
2019-09-20 UK043 106.10 1,279.00 516.98 927.87
2019-09-21 UK020 105.17 981.00 516.19 927.20
2019-09-21 UK049 105.17 322.00 516.19 927.20
2019-09-21 UK050 105.17 620.00 516.19 927.20
2019-12-14 UK049 44.13 414.00 460.99 877.86
2019-12-15 UK043 43.58 374.00 460.46 877.35
2020-01-05 UK020 32.63 330.00 449.97 867.30
2020-01-25 UK050 23.38 288.00 441.05 858.72
2020-02-25 UK048 10.86 53.00 429.17 847.48
2020-09-19 UK020 -50.64 471.00 395.12 840.88
2020-09-20 UK043 -50.90 306.00 395.09 841.07
2020-09-20 UK050 -50.90 155.00 395.09 841.07
2020-12-11 UK049 -69.18 53.00 394.24 857.67
2021-06-28 UK049 -59.18 536.00 388.80 836.79
2021-07-11 UK020 -55.08 249.00 387.48 830.04
2021-09-18 UK020 -32.21 1,004.00 382.46 797.14
2021-09-18 UK050 -32.21 660.00 382.46 797.14
2021-09-21 UK048 -31.23 734.50 382.31 795.86
2021-09-23 UK049 -30.59 124.00 382.22 795.02
2021-12-12 UK043 -10.04 901.00 379.79 769.61
2022-01-07 UK049 -7.42 137.00 379.47 766.35
2022-01-09 UK020 -7.34 371.00 379.45 766.24
2022-04-02 UK050 -26.04 781.00 379.09 784.21
2022-04-03 UK043 -26.58 318.00 379.08 784.75
2022-04-03 UK048 -26.58 59.00 379.08 784.75
2022-04-06 UK049 -28.25 134.00 379.07 786.40
2022-04-10 UK020 -30.61 541.00 379.06 788.73
2022-06-19 UK048 -95.80 40.00 378.86 853.51
2022-07-08 UK049 -121.28 198.00 378.90 879.07
2022-07-10 UK020 -124.15 441.00 378.91 881.96
2022-09-17 UK020 -242.77 690.00 379.88 1,002.53
2022-09-18 UK043 -244.74 554.00 379.91 1,004.56
2022-09-18 UK048 -244.74 335.00 379.91 1,004.56
2022-09-24 UK050 -256.74 203.50 380.07 1,016.89
2022-10-06 UK049 -281.43 132.00 380.45 1,042.33

Trend description for C1a

The individual survey results show that the number of litter items per 100 metres of beach in England varies considerably, from a maximum of 6,900 items in January 2018 to a minimum of zero items in April 2018. Therefore, a LOESS smoother has been applied to view trends in the data. The smoothed values peak in April 2017 at 1,280 items per 100 metres. The trend shows an overall decline between this date and September 2021 to 380 items per 100 metres, where it remains until the end of the series, October 2022.

Assessment of change

The assessment presented here is taken from the source publication for this indicator component. A Theil-Sen slope estimation was used, as this method is robust to outliers, which are common in beach litter data. It was not considered appropriate to assign a percentage change using this methodology. A statistically significant decrease (or improvement) of 103.6 litter items per 100 metres per year was observed over the short-term time period (2017 to 2022). This assessment does not consider whether any improvement is on a sufficient scale for meeting targets.

Change since 2018 has not been assessed, however this will be considered for future updates to this indicator.

The assessment results reported here may not be directly comparable with other analyses published elsewhere that use different methodologies to explore these indicators or are based on alternative datasets.

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.

Table C1a: Assessment of change

Component Subcomponent Period Date range Percentage change Smoothing function Assessment of change
C1a Observed values Short term 2017 to 2022 N/A Theil-Sen slope estimation Improvement
C1a Observed values Medium term N/A N/A N/A Not assessed
C1a Observed values Long term N/A N/A N/A Not assessed

Figure C1b: Percentage of sampled fulmars having more than 0.1g of plastic in their stomach, Greater North Sea, 2004-2008 to 2018-2022

Table C1b: Percentage of sampled fulmars having more than 0.1g of plastic in their stomach, Greater North Sea, 2004-2008 to 2018-2022

Time period Percentage
2004-2008 62
2005-2009 65
2006-2010 64
2007-2011 64
2008-2012 64
2009-2013 61
2010-2014 62
2011-2015 66
2012-2016 57
2013-2017 53
2014-2018 48
2015-2019 47
2016-2020 44
2017-2021 44
2018-2022 43

Trend description for C1b

From 2004 to 2014 approximately 60% of surveyed (beached) fulmars in the Greater North Sea region were found to have more than 0.1 grams of plastic (the threshold level used in the OSPAR target definition) in their stomachs. This reflects the abundance of floating litter in their environment. Since the period 2011 to 2015, there has been a decrease in the proportion of surveyed fulmars with more than 0.1g of plastic in their stomachs, to 43% in the period 2018 to 2022.

Assessment of change

A decrease (or improvement) in the percentage of sampled fulmars which have more than 0.1g of plastic in their stomach was observed over the short, medium, and long-term time periods. This assessment does not consider whether any improvement is on a sufficient scale for meeting targets.

Change since 2018 has also been assessed. A decrease (improvement) in the fulmar indicator was observed since 2018. However, this is based on only 5 data points so should be considered as indicative and not evidence of a clear trend.

The assessment results reported here are not directly comparable with other analyses published elsewhere that use different methodologies to explore these indicators or are based on alternative datasets.

Further information on this assessment, along with details on the methodology, is provided in the Assessment background. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results.

Table C1b: Assessment of change

Component Period Date range Percentage change Smoothing function Assessment of change
C1b Short term 2013-2017 to 2018-2022 -18.87 Rolling average Improvement
C1b Medium term 2008-2012 to 2018-2022 -32.81 Rolling average Improvement
C1b Long term 2004-2008 to 2018-2022 -30.65 Rolling average Improvement

Percentage change refers to the difference seen from the first to last 5-year moving average in the specified date range.

Figure C1ci: Mean probability that benthic trawl surveys contain a litter item, expressed as a percentage, Greater North Sea and Celtic Seas, 2012 to 2019

Table C1ci: Mean probability that benthic trawl surveys contain a litter item, expressed as a percentage, Greater North Sea and Celtic Seas, 2012 to 2019

Year Celtic Seas Greater North Sea
2012 47.00 57.00
2013 49.00 67.00
2014 53.00 69.00
2015 43.00 59.00
2016 38.00 69.00
2017 40.00 76.00
2018 45.00 73.00
2019 43.00 75.00

Trend description for C1ci

In the Greater North Sea, there has been a gradual increase in the mean probability of a benthic survey containing litter, from 57% in 2012 to 75% in 2019. In the Celtic Seas, the mean probability of a survey containing litter has fluctuated around 45%, with a peak of 53% in 2014. More granular data is available for the latest year in the series (2019, C1cii), with the greatest probability of a benthic trawl survey containing litter being in the south and south-east Greater North Sea and the south-west Celtic Seas. Benthic trawl surveys in the north-west Greater North Sea and Celtic Seas have the lowest probability of containing a litter item.

Assessment of change

The time series for C1ci, mean probability that benthic trawl surveys contain a litter item, is from 2012 to 2019 which is not yet long enough to produce an assessment for the medium and long-term time periods.

An increase (or deterioration) was observed in the Greater North Sea region, but a decrease (or improvement) was observed in the Celtic Seas region over the most recent 5 years for which trends can be assessed (2013 to 2018). However, it is important to note that assessment results reported here are not directly comparable with other analyses published elsewhere that use different methodologies to explore these indicators or are based on alternative datasets.

Further information on this assessment, along with details on the methodology, is provided in the Assessment background. Summaries by 25 Year Environment Plan goal and information on indicator links are presented in the Assessment results.

Table C1ci: Assessment of change

Component Subcomponent Period Date range Percentage change Smoothing function Assessment of change
C1ci Celtic Seas Short term 2013 to 2018 -16.30 Loess Improvement
C1ci Celtic Seas Medium term N/A N/A N/A Not assessed
C1ci Celtic Seas Long term N/A N/A N/A Not assessed
C1ci Greater North Sea Short term 2013 to 2018 16.47 Loess Deterioration
C1ci Greater North Sea Medium term N/A N/A N/A Not assessed
C1ci Greater North Sea Long term N/A N/A N/A Not assessed

Assessment categories for indicator C1ci were assigned based on smoothed data, so percent change figures in Table C1ci may differ from unsmoothed values quoted elsewhere. Percentage change refers to the difference seen from the first to last year.

Image C1cii: Probability that benthic trawl surveys contain a litter item, expressed as a percentage, UK, 2019 (smoothed)

Trend description for C1cii

In the Greater North Sea, there has been a gradual increase in the mean probability of a benthic survey containing litter, from 57% in 2012 to 75% in 2019. In the Celtic Seas, the mean probability of a survey containing litter has fluctuated around 45%, with a peak of 53% in 2014. More granular data is available for the latest year in the series (2019, C1cii), with the greatest probability of a benthic trawl survey containing litter being in the south and south-east Greater North Sea and the south-west Celtic Seas. Benthic trawl surveys in the north-west Greater North Sea and Celtic Seas have the lowest probability of containing a litter item.

Assessment of change

No assessment of change is available for C1cii as this is a spatial representation of the most recent year's data presented in C1ci, which has been assessed.

Indicator Metadata