Park Grass

  • Experiment Code: R/PG/5
  • Experiment Site: Rothamsted
  • Objectives: Originally to study the effects of organic and inorganic amendments and lime on old grass for hay, latterly also for effects on botanical composition.
  • Description: Because of the earlier experiments had showed that different crops require different amounts and ratios of nitrogen (N), phosphorus (p) and potassium (K), Lawes and Gilbert extended their experiments in 1856 to include the mixed plant population of old grassland. The Park Grass experiment was established on c.2.8 ha of parkland that had been in permanent pasture for at least 100 years. Started by Lawes and Gilbert in 1856, its original purpose was to investigate ways of improving the yield of hay by the application of inorganic fertilisers or organic manures. Within 2-3 years it became clear that these treatments were having a dramatic effect on the species composition of what had been a uniform sward comprising about 50 species. Dramatically different swards have evolved as a result of the different pH and nutrient status of the soils. There are 35-45 species on the unfertilised plots but only 2 or 3 species on some of the fertilised plots. The continuing effects on species diversity and on soil function of the original treatments, together with later tests of liming and interactions with atmospheric inputs and climate change, has meant that Park Grass has become increasingly important to ecologists and soil scientists. A study published in the journal Nature shows that grassland diversity on the Park Grass experiment recovered once atmospheric nitrogen pollution reduced (Storkey et. al. 2015). The harvesting methods have changed as farming practices have modernised (see More). The plots are cut for hay in mid-June. The first cut for hay ensures seeds are returned each year. The management of the aftermath following the first hay cut varied in the early years, either being grazed by sheep or cut green. Since the 1890s the second crop has been cut green and removed. In some years a third cut has also been taken. Studies have also been made of the botanical composition of the plots both through visual surveys and by looking at the percentage contribution to the hay made by the various species (see More). Herbage yields are recorded each year. Physical samples of crops and soils have been preserved in the Rothamsted Sample Archive. The experiment also includes a small area used for micro-plot experiments. Since January 2020 twelve sub-plots have three soil moisture probes. The experiment has had three main phases (see Design Periods). Park Grass is a Genomic Observatory - a geographic site with a rich history of environmental/ecological data collection and a long-term commitment to future studies. The Park Grass soil metagenome from the untreated control plot 3d is now publicly available (see Related Documents). Park Grass is both an Environmental Change Network (ECN) data site and an Ecological Continuity Trust site (see Related Documents).
  • Date Start: 1856
  • Date End: Ongoing

Key Contacts

  • Sarah Perryman

  • Role: Data Manager
  • ORCID: https://orcid.org/0000-0002-0056-2754
  • Organisation: Rothamsted Research
  • Address: West Common, Harpenden, Hertfordshire, AL5 2JQ, United Kingdom
  • Jon Storkey

  • Role: Experiment Manager
  • ORCID: https://orcid.org/0000-0003-1094-8914
  • Organisation: Rothamsted Research
  • Address: West Common, Harpenden, Hertfordshire, AL5 2JQ, United Kingdom
  • Andy Gregory

  • Role: Principal Investigator
  • Organisation: Rothamsted Research
  • Address: West Common, Harpenden, Hertfordshire, AL5 2JQ, United Kingdom
  • Margaret Glendining

  • ORCID: https://orcid.org/0000-0002-6466-4629
  • Organisation: Rothamsted Research
  • Address: West Common, Harpenden, Hertfordshire, AL5 2JQ, United Kingdom

Funding

  • The e-RA database, including the published datasets generated from it, is part of the Rothamsted Long-Term Experiments - National Bioscience Research Infrastructure (RLTE-NBRI) , which also includes the Long-Term Experiments, the Sample Archive and Rothamsted's environmental monitoring activities including the weather stations and its role in the UK Environmental Change Network.
  • The RLTE-NBRI is supported by the Lawes Agricultural Trust and the Biotechnology and Biological Sciences Research Council (Grants BBS/E/C/00005189 (2012-2017); BBS/E/C/000J0300 (2017-2022); BBS/E/RH/23NB0007 (2023-2028)).

Experimental Design

Description

  • There were originally 20 plots, some split (see Plan 1865). Plot nomenclature in 1856-1902 is complex. Yields are given for the whole plot, eg plot 3, 1856-1885. From 1881-1902, yields from the small area chalked in 1881 are referred to as 'C' eg 3C, and from the much larger unchalked area as 'UC' eg 3UC. Separate yields were not recorded for the limed and unlimed Western and Eastern halves in 1883 and 1887, but in some years, eg 1887 and 1889, yields are shown for the Western (W) and Eastern (E) parts of the areas chalked (C) and unchalked (UC) in 1881, eg Plots 3EU, 3WC. Plots areas are shown in e-RA, which helps with understanding which parts of the plots are referred to.

Design

  • Period: 1856 - 1902
  • Number of Plots: 20
  • Number of Sub-plots:

Crops

Crop Years Grown
Grass

Factors

Factors are the interventions or treatments which vary across the experiment.

Nitrogen Fertilizer Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
N1 52 kgN/ha - ammonium sulfate
N2 104 kgN/ha - ammonium sulfate
N3 156 kgN/ha - ammonium sulfate
N1* 52 kgN/ha - ammonium nitrate
N2* 104 kgN/ha - ammonium nitrate

Natural Fertilizer Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Farmyard Manure - once every 4 years
Fish Meal - once every 4 years To supply 68 kgN/ha.

Superphosphate Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
P 36 kgP/ha -

Potassium Fertilizer Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
K 242 kgK/ha - potassium sulphate

Sodium Nutrient Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Na 17 kgNa/ha - sodium sulphate

Magnesium Nutrient Exposure

Application: Whole Plot

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Mg 12 kgMg/ha - magnesium sulphate

Silicon Nutrient Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Si 28 - silicate of soda

Sawdust

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes

Measurements

Variable Unit Collection
Frequency
Material Description Crop
Yield Components t/ha Biannual SpecifiedCrop 1st and 2nd cuts, available from 1856-present. grass
Partial Botanical Separation Data Selected years. Biannual. Percentage composition of gramineae, leguminosae and other orders. Complete Botanical Separation Data. Selected years 1862-1976.
Complete Botanical Separation Data Selected years. Biannual. Percentage composition of species on plot. Selected years 1862-1976.
Soil Total Carbon variable data available for 1876, 1886, (1932, 1959, 1966, 1985, 1991)
Total Soil Nitrogen variable data available for 1876, 1886, (1913, 1932, 1959, 1966, 1985, 1991)
Soil pH variable data available for 1876, (1923, 1959, 1967, 1970, 1971, 1974, 1975, 1977, 1979, 1984, 1991, 1995, 1998, 2002, 2005, 2008, 2011, 2014)
Olsen P mg/kg variable From 1876 -
Total P mg/kg variable
Soil Weight t/ha variable From 1870 -
Root Mass t/ha variable From 1870 -

Description

  • Plots were divided into two in 1903 to test the effects of regular applications of lime.

Design

  • Period: 1903 - 1964

Crops

Crop Years Grown
Grass

Measurements

Variable Unit Collection
Frequency
Material Description Crop
Yield Components t/ha Biannual. 1st and 2nd cuts, available from 1856-present.
Partial Botanical Separation Data Selected years. Biannual. Percentage composition of gramineae, leguminosae and other orders. Complete Botanical Separation Data. Selected years 1862-1976.
Complete Botanical Separation Data Selected years. Biannual. Percentage composition of species on plot. Selected years 1862-1976.
Soil Total Carbon variable data available for 1876, 1886, 1932, 1959, 1966, 1985, 1991
Total Soil Nitrogen variable data available for (1876, 1886), 1913, 1932, 1959, (1966, 1985, 1991)
Soil pH variable data available for (1876), 1923, 1959, (1967, 1970, 1971, 1974, 1975, 1977, 1979, 1984, 1991, 1995, 1998, 2002, 2005, 2008, 2011, 2014)
Olsen P mg/kg variable From 1876 -
Total P mg/kg variable From 1876 -
Soil Weight t/ha variable From 1870 -
Root Mass t/ha variable From 1870 -

Description

  • In 1965 most plots were divided into four sub-plots, three of which receive chalk to maintain pHs of 7, 6 and 5 (sub-plots a, b and c respectively). The fourth sub-plot (sub-plot d) receives no chalk and the pH of these ranges from 3.5 to 5.7 depending on the fertilizer treatment. From 1965 plots 5/1, 5/2 and 6 were used for microplot experiments. Plots 6a and 6b were re-included in the main experiment in 1972 but the other half of plot 6 (6c and 6d) and plots 5/1 and 5/2 have remained outside the main experiment. Since 1990, nitrogen fertilizer has been withheld from half of all sub-plots formerly receiving 96 kg N ha-1 (plots 9 and 14) as either ammonium sulphate or sodium nitrate to study processes controlling soil acidification, heavy-metal mobilisation and botanical changes. Since 1995, plot 13 has been split into 13/1 and 13/2 and FYM/Fishmeal withheld from plot 13/1. Since 1996 plot 2 has been split into 2/1 and 2/2 with plot 2/1 receiving K as potassium sulphate. In 2013 plot 7 (PKNaMg) was divided into two equal sized plots, 7/1 and 7/2. This was to test whether P fertilizer was still required, because large reserves of P have built up in the soil. No P fertilizer was applied to Plot 7/1, but K, Na and Mg applications continued. Plot 7/2 continued as before (i.e. it received PKNaMg). In addition, N applications began on plot 15; 144kg N/ha as sodium nitrate to provide a comparison with plot 11/1 which receives the same amount of N as ammonium sulphate together with P, K, Na & Mg. From autumn 2016 all plots previously receiving 35 kg P ha-1 as triple superphosphate will receive 17 kg P ha-1 (until further notice) because of the high levels of available soil P from past P inputs. The P application to plot 20 will remain unchanged. Current K, Mg and Na rates on Park Grass remain unchanged. Yields are given for the four sub-plots, eg 3a, 3b, 3c and 3d.

Design

  • Period: 1965 - Now

Crops

Crop Years Grown
Grass

Factors

Factors are the interventions or treatments which vary across the experiment.

Nitrogen Fertilizer Exposure

Description: applied in spring

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
N1 48 kgN/ha - ammonium sulfate
N2 96 kgN/ha - ammonium sulfate
N3 144 kgN/ha - ammonium sulfate
N*1 48 kgN/ha - ammonium nitrate
N*2 96 kgN/ha - ammonium nitrate
N*3 144 kgN/ha - ammonium nitrate
(n2) 96 kgN/ha - 1989 ammonium sulfate
(n*2) 96 kgN/ha - 1989 ammonium nitrate

Natural Fertilizer Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Farmyard Manure 35 t/ha - applied every fourth year supplies c.240 kg N
Pelleted Poultry Manure - replaced fish meal in 2003; supplies c.65 kg N

Superphosphate Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
P 17 kgP/ha - applied in winter triple superphosphate

Potassium Fertilizer Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
K 17 kgK/ha - applied in winter potassium sulphate

Sodium Nutrient Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Na 15 kgNa/ha - applied in winter sodium sulphate

Magnesium Nutrient Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Mg 10 kgMg/ha - applied in winter magnesium sulphate

Silicon Nutrient Exposure

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Si 450 - applied in winter sodium silicate

Liming Exposure

Description: ground chalk applied as necessary to maintain soil at pH 7,6 and 5 on sub plots a, b and c

Levels
Level Name Amount Years Frequency Crop Method Chemical Form Notes
Lime - applied every third year since 1995, every 4 years before then calcium carbonate sub-plot d does not receive any chalk

Measurements

Variable Unit Collection
Frequency
Material Description Crop
Yield Components two cuts per year SpecifiedCrop every year from 1856 - present grass
Botanical Composition variable complete separations of hay selected years 1862-1976; partial separations of hay 1862-1976; complete species botanical surveys 1991-2000*below
Soil Total Carbon variable data available for 1876, 1886, 1932, 1959, 1966, 1985, 1991
Total Soil Nitrogen variable data available for (1876, 1886, 1913, 1932, 1959) 1966, 1985, 1991
Soil pH variable data available for (1876, 1923, 1959) 1967, 1970, 1971, 1974, 1975, 1977, 1979, 1984, 1991, 1995, 1998, 2002, 2005, 2008, 2011, 2014
Olsen P mg/kg variable
Total P variable From 1876
Soil Weight t/ha variable From 1870
Root Mass t/ha variable From 1870
Exchangeable Cations mg/kg variable K, Mg, Ca, Na in air-dried soil. From 1991-2011.
*botanical Survey Data Annual 1991-2000 by Imperial College. Weight of species in replicates > % compostition
Botanical Survey Data 2 years 1993-1994. Mass effects study by Imperial college, as described by Kunin, 1998
Leafhoppers 2 years Leafhoppers (Auchenorhyncha) on 13 plots sampled five time in the summers of 1977 and 1978, as described by Morris, 1992
Soil Moisture Since January 2020
Atmospheric Chemistry Dry deposition of NO2 (Atmospheric Chemistry, AN) measured on Park Grass by, and available through, the Environmental Change Network (ECN)
Precipitation Chemistry Wet deposition (precipitation chemistry, PC) measured on Park Grass by, and available through, the Environmental Change Network (ECN)

Site: Park Grass - Rothamsted

  • Experiment Site: Rothamsted
  • Description: The experiment was established on c. 2.8 ha of parkland that had been in permanent pasture for at least 100 years.
  • Visit Permitted?: Yes
  • Visiting Arrangments: By arrangement with Dr Andy Macdonald
  • Elevation: 133 Metres
  • Geolocation:    51.803812, -0.372097

Soil

  • Type: Luvisol
    Silty clay loam over clay-with-flints overlying chalk. The site is normally well drained (Hook series) or moderately well drained (Batcombe series)

Soil Properties

Variable Value Reference Year Is Estimated Is Baseline
Sand content 11.6% (Percent) NO NO
Silt content 66.3% (Percent) NO NO
Clay content 22.1% (Percent) NO NO
Soil density 1.1g/cm3 (gram per cubic centimetre) 2011 NO NO

Datasets available

Title (hover for a longer description) Year of Publication Identifier Version

Crop yield data - Annual

Dataset: Park Grass Hay Yields, Fertilizer and Lime Treatments 1903-1964 2022 10.23637/rpg5-yields1903-1964-01
01
Dataset: Park Grass Hay Yields, Fertilizer and Lime Treatments 1965-2018 2021 10.23637/rpg5-yields1965-2018-01
01

Soil data

Park Grass Soil pH 1856-2011 2016 10.23637/KeyRefOAPGsoilpH
01
Park Grass Metaproteome 2022 10.6019/PXD017392
01

Species observation data

Park Grass Changes in Mean Species Numbers 1864-2011 2016 10.23637/KeyRefOAPGspecies
01
Dataset: Park Grass Species, Fertilizer and Lime Treatments 2010-2012 2022 10.23637/rpg5-species_2010-2012-01
01
Dataset: Park Grass Species, Fertilizer and Lime Treatments 1991-2000 2021 10.23637/rpg5-species_1991-2000-01
01
Park Grass Plot Photos 2022 10.23637/rpg5-plotphotos-01
01
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Videos

Video on the Park Grass Experiment
A visually engaging short film on the Park Grass experiment presented by Dr Johnathan Storkey.

Images

Plans, fertilizer treatments and liming details for the Park Grass experiment

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Plans and treatments

  • Park Grass today Park Grass experiment plan since 1965, updated 2018, showing plot layout, treatment codes and lime, fertilizer and manure treatments. doi: 10.23637/rpg5-plan1965-01
  • Park Grass plan 1903-1964 Park Grass experiment plan showing plot layout, treatment codes and lime, fertilizer and manure treatments 1903-1964. doi: 10.23637/rpg5-plan1903-1964-01
  • Park Grass plan 1856-1902 Park Grass experiment plan showing plot layout, treatment codes and lime, fertilizer and manure treatments 1856-1902. doi: 10.23637/rpg5-plan1856-1902-01
  • Park Grass lime treatments 1856-2021 Details of lime or chalk applied to the Park Grass experiment since the start of the experiment in 1856. doi: 10.23637/rpg5-LimeTreats-01

Information about the botanical surveys

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Park Grass Botanical Compostion

Studies have also been made of the botanical composition of the plots both through visual surveys and by looking at the percentage contribution to the hay made by the various species. The most recent comprehensive surveys of botanical composition, PARKCOMPIC, made just before the first cut, were done annually between 1991 and 2000. See 150th Anniversary Publication for soil pH and a summary of those species comprising at least 10% of herbage, and the total number of species identified on each plot (after Crawley et al, 2005). There are many interactions between fertilizer, manure treatment and pH. Without exception, all the original treatments imposed in 1856 have caused a decline in species number compared to the original sward. In most cases, this is due to changes in soil fertility and annual nutrient inputs and perhaps also the way in which the sward was managed. Numbers of species have decreased, even on the plots given no fertilizers or manures, due to acid deposition. Applying nitrogen as sodium nitrate or ammonion sulphate reduces diversity further, and in the ammonium form also rapidly acidifies the soil, reducing the number of species to one or two, Holcus lanatus (Yorkshire Fog) and Anthoxanthum odoratum (Sweet Vernal Grass).

Survey method: From 1991 to 2000, six randomly located quadrats measuring 50cm x 25cm were located within each of the plots in early June, immediately before the first cut. The herbage was cut with scissors to ground level and plant material taken back to the laboratory where it was sorted into species. Samples were oven-dried at 80 °C for 24 hours, after which dry mass was determined for each species. Data in PARKCOMPIC is shown as gm/0.125 m2 for each quadrat and as gm/0.75m2 for the total (ie 6 quadrats).

Further information is given in the Rothamsted Guide to the Classical Experiments 2018 pages 20-30, in Crawley et. al. (2005) and in the Key References listed below.

The dataset PKMASSEFF is a survey of plant diversity carried out by Kunin (1998) in 1993 and 1994. He measured plant diversity in 54 transects across the plot boundaries of all plots, except 5, 9-1, 14-1, 18-20, mainly sub-plots 'a' (pH = 7) and 'd' (unlimed). Transects were surveyed in May and June 1993 and May 1994, before the first cut of each year. In each surveyed transect the number of reproductive plants of each species was recorded. See Kunin (1998) in Key References below for full details of survey method and description of transects.

Earlier surveys of the botanical composition of Park Grass were carried out from 1862 to 1976. The dataset PARKCOMP consists of complete botanical analyses, carried out in 1862, 1867, 1872 and 1877, and several more times between 1903 and 1948. No analyses were carried out between 1949 and 1972. Further full botanical analyses were carried out on limited plots between 1973 and 1976. Full details are given by Williams 1978. Samples of plant material were taken from each plot, separated into the different species and weighed. The Open University two letter species codes are also included.

The dataset PARKPARTCOMP contains a much simpler partial analysis of the three main groups of plants - grasses, legumes and other species. These were carried out between 1862 and 1976. Again samples were taken from each plot, separated and then weighed to determine the percentage composition.

Except during 1895-1902, either complete or partial analyses were done in all years between 1874 and 1948 for plots 3 (unmanured), 7 (PKNaMg) and 9 (N2PKNaMg). Full details are given by Williams 1978.

Williams (1978) analysed selected plots between 1973 and 1976, after the sub-division of the Limed (L) and Unlimed (U) plots into a, b, c and d sub-plots. Results for 1975 and 1976 in PARKPARTCOMP still refer to L and U half-plots. The L half-plot is equivalent to the a and b sub-plots, the U half-plot is equivalent to the c and d subplots.

Between 1920 and 1990 visual surveys were made twice a year, before the hay was cut in June and again in the autumn (PARKVISUAL).

Galium tricornutum Section 8 Broadbalk
Grass sorting 1930s

Non-herbicide plot section 8 Broadbalk
Plots 11-2d and 12d, June 2005

Broadbalk elevated view
Plots 14.1 and 14.2, May 1990

Key References

2015

  • Storkey, J. , Macdonald, A.J. , Poulton, P.R. , Scott, T. , Kohler, I.H. , Schnyder, H. , Goulding, K.W.T. and Crawley, M.J. (2015) "Grassland biodiversity bounces back from long-term nitrogen addition", Nature , 528, 401-4
    DOI: 10.1038/nature16444

2006

  • Silvertown, J. , Poulton, P.R. , Johnston, A., E. , Edwards, G. , Heard, M. and Biss, P.M. (2006) "The Park Grass Experiment 1856-2006: Its contribution to ecology", Journal of Ecology, 94, 801-814
    DOI: 10.1111/j.1365-2745.2006.01145.x
  • Rothamsted_Research (2006) "A celebration of 150 years of the Park Grass Experiment", Harpenden, UK, 1-6
    DOI: 10.23637/ERADOC-1-253

2005

  • Crawley, M.J. , Johnston, A.E. , Silvertown, J. , Dodd, M. , de Mazancourt, C. , Heard, M.S. , Henman, D.F. and Edwards, G.R. (2005) "Determinants of species richness in the Park Grass experiment", American Naturalist, 165, 179-192
    DOI: 10.1086/427270

1998

  • Kunin, W.E. (1998) "Biodiversity at the edge: A test, of the importance of spatial "mass effects" in the Rothamsted Park Grass experiments", Proceedings of the National Academy of Sciences of the United States of America, 95, 207-212
    DOI: 10.1073/pnas.95.1.207

1995

  • Dodd, M. , Silvertown, J. , McConway, K. , Potts, J. and Crawley, M. (1995) "Community Stability - a 60-Year Record of Trends and Outbreaks in the Occurrence of Species in the Park Grass Experiment", Journal of Ecology, 83, 277-285
    DOI: 10.2307/2261566

1994

  • Jenkinson, D.S. , Potts, J.M. , Perry, J.N. , Barnett, V. , Coleman, K. and Johnston, A.E. (1994) "Trends in Herbage Yields over the Last Century on the Rothamsted Long-Term Continuous Hay Experiment", Journal of Agricultural Science, 122, 365-374
    DOI: 10.1017/S0021859600067290

1978

1976

  • Thurston, J.M. , Williams, E.D. and Johnston, A.E. (1976) "Modern developments in an experiment on permanent grassland started in 1856: effects of fertilizers and lime on botanical composition and crop and soil analyses", Annales Agronomiques, 27, 1043-1082

how yield has been measured and important changes in harvesting methods over the years, including yield correction factor

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Harvesting methods

The plots were originally cut by scythe, then by horse-drawn and then tractor-drawn mowers. The mowing maching was first used for the first cut in 1901, though it had been used for the second cut since 1881. The plots were cut each year for hay, usually in June, and a second cut taken in the autumn since 1875. A second cut was not taken every year, and not from every plot each year, if there was insufficient herbage to sample. No second cut taken 1856-1874, 1876, 1884, 1885, 1887, 1899, 1911, 1914, 1921, 1924, 1933 or 2003. In 1903-1917, the second cut was taken from the whole plot, not the Limed and Unlimed halves. The regrowth after the first cut was grazed by sheep 1856-1872, except for 1866, 1870, and 1873 and 1874, when the regrowth was mown but not removed from the plots.

Yields were originally estimated by weighing the produce from the whole plot, either as hay (1st harvest) or green crop (2nd harvest), and dry matter determined. Since 1960, yields of dry matter have been estimated from strips cut with a forage harvester. However, for the first cut the remainder of each plot is still mown and made into hay, continuing earlier management and ensuring return of seed. For the second cut, the whole of each plot is cut with a forage harvester. Consequently recorded yields of dry matter are now larger than previously as fewer losses occur. The following correction factor should be used for post-1960 data for cut 1 to give yield values equivalent to pre-1960 values:

Ycut 1 = 0.2743 x (YF 1.662 ) (Bowley et al, 2017)

where YF = yield collected by forage harvester, t/ha. The correction factor was obtained from the relationship between yields for hay and forage harvested cuts (r2 = 0.90) for a selection of plots for 1959 and 1992-1994. For more details, refer to Bowley et al, 2017 (see Key References below).

Since 2021, a new machine has been in use, the 'Amazone Forage Harvester'. It cuts a width of 1.5m rather than the previous 1.1m. The machine is fitted with a bespoke weighing balance which weighs the cut as it goes. Subsequent analyses take this into account and a conversion is already calculated.

Galium tricornutum Section 8 Broadbalk
Harvesting 1941

Non-herbicide plot section 8 Broadbalk
Harvesting 1st cut 2005

Broadbalk elevated view
Harvesting 1st cut 2005

Galium tricornutum Section 8 Broadbalk
Cutting 2nd cut 2015

Non-herbicide plot section 8 Broadbalk
Raking 2nd cut 2015

Broadbalk elevated view
Weighing 2nd cut 2015

Galium tricornutum Section 8 Broadbalk
Weighing sub-samples for % moisture 2nd cut 2015

Non-herbicide plot section 8 Broadbalk
Dried samples 2nd cut 2015

Broadbalk elevated view
Labelled sample tins 2nd cut 2015

Galium tricornutum Section 8 Broadbalk
Amazone Forage Harvester June 2022 at south side of Park Grass

Non-herbicide plot section 8 Broadbalk
Park Grass 2022 mowing east end

Broadbalk elevated view
Mowing Park Grass June 2022

Key References

2017

  • Bowley, H.E. , Mathers, A.W. , Young, S.D. , Macdonald, A.J. , Ander, E.L. , Watts, M.J. , Zhao, F.J. , McGrath, S.P. , Crout, N.M.J. and Bailey, E.H. (2017) "Historical trends in iodine and selenium in soil and herbage at the Park Grass Experiment, Rothamsted Research, UK", Soil Use and Management, 33, 252-262
    DOI: 10.1111/sum.12343

Information about soil chemical and physical properties

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Park Grass Soils

The Park Grass experiment was started by Lawes and Gilbert in 1856 to look at the effects of applying fertilizers and manures on the yield of hay from permanent grassland. The field had been in permanent pasture for at least 100 years before the experiment began. It is never ploughed or sown. Here, details are given of the site and soil.

Site details

  • Location: Rothamsted Research, Harpenden, Herts, AL5 2JQ, UK
  • Latitude: 51.804
  • Longitude: -0.373
  • GB Grid Reference: TL122 129
  • Gradient: The site is level
  • Irrigation: There is no irrigation

Soil details

  • FAO Classification: Chromic Luvisol (or Alisol)
  • U.S. Soil Taxonomy: Aquic (or Typic) Paleudalf
  • Soil Survey of England & Wales Group: Gleyic argillic brown earths (Hook) and Stagnogleyic paleo-argillic brown earth (batcombe) (Avery, 1980)
  • Soil Survey of England & Wales Series: Predominately Hook Series, some also typical Batcombe (Avery & Catt, 1995 - see Soil Map link on the left hand side).

For more details of the Hook and Batcombe soil series, see Cranfield University 2018 Soils Guide.

Soil texture class: Silty clay loam over clay-with-flints overlying chalk. The site is normally well drained (Hook series) or moderately well drained (Batcombe series) (Avery & Catt, 1995).

Soil texture, 0-23cm, 2002 from six sub-plots (Poulton, pers comm):

  • Sand (2000 - 63 µm) : 11.6 %
  • Silt (63 - 2 µm) : 66.3 %
  • Clay (<2 µm) : 22.1 %

Soil structure: The structure of the topsoils are clearly influenced by organic matter content and base status. The calcareous plots have very dark coloured surface horizons, characterized by strongly developed granular or fine subangluar blocky peds. In contrast, the acid plots are more weakly structured and in extreme cases, typified by the unlimed plots which have received regular applications of ammonium sulphate (eg plots 4/2d, 9/2d and 11/2d), organic matter has accumulated at the surface to form a discrete mat or mor layer, and the immediately underlying mineral soil is massive and structureless (Avery & Catt, 1995).

Soil pH: In 1965 most plots were divided into four sub-plots. Three subplots receive different amounts of lime as required to maintain pH at 7, 6 and 5 (sub-plots a, b and c, respectively). Sub-plot d receives no lime and pH of these ranges from 3.5 to 5.7, depending on the fertilizer treatment. See Park Grass Open Access soil pH for selected plots, for more details.

Soil sampling: A few plots were sampled in 1870 but the first major soil sampling was in 1876, 20 years after the experiment started. Soils were taken with an open-ended iron box, 30.5cm x 30.5cm x 22.9cm deep. Just three samples were taken from each plot, as this method was disruptive on grassland. Since 1932, samples have been taken by straight-sided semi-cylindrical auger, bulking a large number of cores for each plot or sub-plot. All samples except in 1932 have been taken to a depth of 23cm, and in some years, deeper samples were also taken (Poulton, 1996).

Soil bulk density: A standard value of 1.1 g cm3 (2500 t ha-1) should be used as a general indication of soil bulk density. This is the mean of all plots, sampled in 2011, 0-23cm only. Note that if detailed plot calculations are required, eg nutrient content, individual plot data should be used - please contact the e-RA Curators for this. Also, in some plots bulk density varies greatly within the 23cm depth particularly on acidic sub-plots with a 'mat' of semi decomposed organic matter on the surface.

With thanks to Andy Macdonald and Paul Poulton for help with compiling the information and text.

Key References

2009

  • Tye, A.M. , Kemp, S.J. and Poulton, P.R. (2009) "Responses of soil clay mineralogy in the Rothamsted Classical Experiments in relation to management practice and changing land use", Geoderma, 153, 136-146
    DOI: 10.1016/j.geoderma.2009.07.019

1996

  • Poulton, P.R. (1996) "Park Grass. ", Global Change and Terrestrial Ecosystems, Report No. 7, GCTE Task 3.3.1, Soil Organic Matter Network (SOMNET), 1996 Model and Experimental Metadata (Smith P. , Smith J.U. and Powlson D.S. (eds) - GCTE Focus 3 Office, Wallingford, UK), 129-132

1995

1980

  • Avery, B.W. (1980) "Soil classification for England and Wales (higher categories). ", ,

1969

  • Salter, P.J. and Williams, J.B. (1969) "The moisture characteristics of some Rothamsted, Woburn and Saxmundham soils", Journal of Agricultural Science, 73, 155-156
    DOI: 10.1017/S0021859600024242

Key References

2022

  • Addy, J. (2022) "Reproduction of Figures for: A heteroskedastic model of Park Grass spring hay yields in response to weather suggests continuing yield decline with climate change in future decades", Rothamsted Research, 01
    DOI: 10.23637/rothamsted.988x5
  • Addy, J.W.G. , Ellis, R.H. , MacLaren, C. , Macdonald, A.J. , Semenov, M.A. and Mead, A. (2022) "A heteroskedastic model of Park Grass spring hay yields in response to weather suggests continuing yield decline with climate change in future decades", Journal of the Royal Society Interface, 19
    DOI: 10.1098/rsif.2022.0361

2021

  • Cabrera, J.C.B. , Hirl, R.T. , Schaufele, R. , Macdonald, A. and Schnyder, H. (2021) "Stomatal conductance limited the CO2 response of grassland in the last century", BMC Biology, 19, 50
    DOI: 10.1186/s12915-021-00988-4
  • Addy, J.W.G. , Ellis, R.H. , Macdonald, A.J. , Semenov, M.A. and Mead, A. (2021) "Changes in agricultural climate in South-Eastern England from 1892 to 2016 and differences in cereal and permanent grassland yield", Agricultural and Forest Meteorology, 308-309, 108560
    DOI: 10.1016/j.agrformet.2021.108560
  • Glendining, M.J. , Poulton, P.R. , Macdonald, A.J. and Gregory, A.S. (2021) "Park Grass Experiment lime treatments, 1856-2021"
    DOI: 10.23637/rpg5-LimeTreats-01
  • Rothamsted_Research (2021) "Park Grass experiment plan and treatments since 1965, updated 2018"
    DOI: 10.23637/rpg5-plan1965-01

2017

  • Bowley, H.E. , Mathers, A.W. , Young, S.D. , Macdonald, A.J. , Ander, E.L. , Watts, M.J. , Zhao, F.J. , McGrath, S.P. , Crout, N.M.J. and Bailey, E.H. (2017) "Historical trends in iodine and selenium in soil and herbage at the Park Grass Experiment, Rothamsted Research, UK", Soil Use and Management, 33, 252-262
    DOI: 10.1111/sum.12343

2016

  • J. Storkey , A.J. Macdonald , J.R. Bell , I.M. Clark , A.S. Gregory , N.J. Hawkins , P.R. Hirsch , L.C. Todman and Whitmore, A.P. (2016) "The Unique Contribution of Rothamsted to Ecological Research at Large Temporal Scales.", Advances in Ecological Research (eds: A.J. Dumbrell , R.L. Kordas and G. Woodward - Academic Press), Vol 55, Chapter 1, pp. 3-42
    DOI: 10.1016/bs.aecr.2016.08.002

2015

  • Storkey, J. , Macdonald, A.J. , Poulton, P.R. , Scott, T. , Kohler, I.H. , Schnyder, H. , Goulding, K.W.T. and Crawley, M.J. (2015) "Grassland biodiversity bounces back from long-term nitrogen addition", Nature , 528, 401-4
    DOI: 10.1038/nature16444

2010

2009

  • Johnston, A.E. , Poulton, P.R. and Coleman, K. (2009) "Soil organic matter: its importance in sustainable agriculture and carbon dioxide fluxes", Advances in Agronomy, 101, 1-57
    DOI: 10.1016/s0065-2113(08)00801-8

2006

  • Silvertown, J. , Poulton, P.R. , Johnston, A., E. , Edwards, G. , Heard, M. and Biss, P.M. (2006) "The Park Grass Experiment 1856-2006: Its contribution to ecology", Journal of Ecology, 94, 801-814
    DOI: 10.1111/j.1365-2745.2006.01145.x

2005

  • Crawley, M.J. , Johnston, A.E. , Silvertown, J. , Dodd, M. , de Mazancourt, C. , Heard, M.S. , Henman, D.F. and Edwards, G.R. (2005) "Determinants of species richness in the Park Grass experiment", American Naturalist, 165, 179-192
    DOI: 10.1086/427270

1998

  • Kunin, W.E. (1998) "Biodiversity at the edge: A test, of the importance of spatial "mass effects" in the Rothamsted Park Grass experiments", Proceedings of the National Academy of Sciences of the United States of America, 95, 207-212
    DOI: 10.1073/pnas.95.1.207

1996

  • Poulton, P.R. (1996) "The Park Grass Experiment, 1856-1995", NATO advanced research workshop, Evaluation of soil organic matter models using existing long-term datasets, NATO ASI Series I: Global Environmental Change, (Powlson D. S. , Smith P. and Smith J.U. (eds) - Springer-Verlag, Berlin), Vol 38, 377-384
  • Poulton, P.R. (1996) "Park Grass. ", Global Change and Terrestrial Ecosystems, Report No. 7, GCTE Task 3.3.1, Soil Organic Matter Network (SOMNET), 1996 Model and Experimental Metadata (Smith P. , Smith J.U. and Powlson D.S. (eds) - GCTE Focus 3 Office, Wallingford, UK), 129-132

1994

  • Jenkinson, D.S. , Potts, J.M. , Perry, J.N. , Barnett, V. , Coleman, K. and Johnston, A.E. (1994) "Trends in Herbage Yields over the Last Century on the Rothamsted Long-Term Continuous Hay Experiment", Journal of Agricultural Science, 122, 365-374
    DOI: 10.1017/S0021859600067290

1992

  • Morris, M.G. (1992) "Responses of Auchenorhyncha (Homoptera) to Fertilizer and Liming Treatments at Park Grass, Rothamsted", Agriculture, Ecosystems & Environment, 41, 263-283
    DOI: 10.1016/0167-8809(92)90115-R

1976

  • Thurston, J.M. , Williams, E.D. and Johnston, A.E. (1976) "Modern developments in an experiment on permanent grassland started in 1856: effects of fertilizers and lime on botanical composition and crop and soil analyses", Annales Agronomiques, 27, 1043-1082

1964

For further information and assistance, please contact the e-RA curators, Sarah Perryman and Margaret Glendining using the e-RA email address: era@rothamsted.ac.uk