Water Sampling Results
Water Quality Monitoring of the River Cherwell: Sampling Results
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the NLS Screening database in combination with the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of >80%"
- "The following compounds were identified using the National Institute of Standards and Technology Library (NIST) and have a Spectral Fit of <80%"
Overview
We have been carrying out water quality sampling of the River Cherwell to check for potential impacts of run-off or leaching from the waste. This is additional to the routine sampling the Environment Agency carries out on the River Cherwell.
Until February 2026, the Environment Agency aimed to carry out weekly water quality monitoring subject to weather conditions and in response to any emerging evidence. Due to the high rainfall in January and February 2026, conditions on site meant that it was not possible to gain weekly water samples. This is because the locations where we need to take representative water samples were not accessible. We know that when water levels are high, we are not likely to gain meaningful data in relation to Kidlington due the high level of dilution.
From March 2026, our contractor Acumen Waste Services Limited became responsible for ongoing water quality sampling near to the illegal waste site. They we will continue to monitor for signs of pollution from the waste and we will update the information on this site as and when it becomes available.
The analysis is reviewed by specialists in toxicology. We know that there are many potential sources of substances found in water courses, including run off from roads, agriculture, the water industry, other industries and naturally occurring substances. We know that like many of our rivers the River Cherwell has its challenges with the water body classified as having a Moderate ecological status. Information is available here: Catchment Data Explorer: Cherwell (Bletchingdon to Ray) Water Body
Water quality samples includes an assessment using the gas chromatography-mass spectrometry (GCMS) screening technique: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen.
We will continue to monitor and we will make sample results available as and when the analysis is complete. https://environment.data.gov.uk/catchment-planning/WaterBody/GB106039037432
Analytical results from samples taken from 18 March 2026 onwards
Our contractors are carrying out water sampling of the Cherwell every two weeks, subject to weather and ground conditions. This will continue until all the waste has been removed.
All assessments of samples taken show that similar chemicals present in the upstream and downstream samples and includes chemicals that are found in other English waterways. These are in very low levels and any impacts on the environment are negligible. If this assessment changes we will update this page.
Please note that there has been a change in the sampling and analysis and the analytical methods have changed as a result. This is because the responsibility for the work has moved to the site operators, Acumen Waste Services Limited.
If you would like a pdf copy of the full chemical analysis for any of the samples, please email us: kidlington@environment-agency.gov.uk
Analytical results from samples taken 5 and 11 March 2026
Our assessment of samples taken on 5 March and 11 March 2026 shows that similar chemicals present in the upstream and downstream samples and includes chemicals that are found in other English waterways. These are in very low levels and any impacts on the environment are negligible.
Please note that there has been a change in the sampling and analysis and the analytical methods have changed as a result. This is because the responsibility for the work has moved to the site operators, Acumen Waste Services Limited.
If you would like a pdf copy of the full chemical analysis, please email us: kidlington@environment-agency.gov.uk
The sampling locations used are:
EA Sample Point (SP) Ref. | Acumen SP Ref. 5/3/26 | Acumen SP Ref. 11/3/26 | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP1 | SP1 | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP2 | SP2 | SP 50764 13829 |
Ingress (Sample 3) | SP3 | SP3 | SP 50791 13850 |
Waste (Sample 4) | SP5 | N/A – All wastewater on site now covered by aggregate | SP 50781 14096 |
D/S Cherwell 1 (Sample 5) | SP5 | SP5 | SP 50916 13798
|
D/S Cherwell 2 (Sample 6) | SP6 | SP6 | SP 50943 13253
|
Analytical results from samples taken 14 January 2026
Our assessment of samples taken on 14 January 2026 shows no significant increase in the range of chemicals in the ingress and downstream samples or in the concentrations downstream compared to upstream. They include chemicals that are found in other English waterways.
This data includes that obtained by using the GC-MS analytical technique: further guidance on this is available here: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen
Disclaimer for GCMS Results: All results are an approximate concentration. Where accreditation is claimed this is only for the identification of the substance and not the quantified amount.
The compounds identified in the GCMS results fit into one of four criteria, which can be pulled from the original dataset on MIDAS if required:
Samples were taken from the following locations:
Sample | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP 50764 13829 |
Ingress (Sample 3) | SP 50791 13850 |
D/S River Cherwell 1 (Sample 3) | SP 50916 13798 |
U/S = Upstream of the waste
D/S = Downstream of the waste
Waste = Sample taken from run-off/standing groundwater that has collated around the waste site boundary
NGR = National Grid Reference
Due to site flooding, samplers were unable to access the waste and D/S 2 sampling locations as they had done in previous weeks.
Determinand / Compound Name | U/S 1 (Sample 1) | U/S 2 (Sample 2) | Ingress (Sample 3) | D/S 1 (Sample 5) | Unit |
Ammonia un-ionised as N | <0.00018 | <0.00034 | <0.00029 | <0.00036 | mg/l |
Ammoniacal Nitrogen as N | <0.03 | <0.03 | <0.03 | <0.03 | mg/l |
BOD : 5 Day ATU | <3 | <3 | <3 | <3 | mg/l |
Chemical Oxygen Demand :- {COD} | 11 | 10 | 11 | 11 | mg/l |
Chloride | 39 | 34 | 38 | 35 | mg/l |
Conductivity at 25 C | 586 | 562 | 378 | 565 | uS/cm |
Nitrite as N | 0.014 | 0.014 | 0.013 | 0.014 | mg/l |
Nitrogen, Total Oxidised as N | 6.6 | 7.1 | 6.5 | 7.1 | mg/l |
Orthophosphate, reactive as P | 0.14 | 0.088 | 0.071 | 0.093 | mg/l |
Oxygen, Dissolved, % Saturation | 86.2 | 95.5 | 94.4 | 96.7 | % |
pH | 7.67 | 7.94 | 7.9 | 7.97 | PHUNITS |
Salinity : In Situ | 0.28 | 0.27 | 0.28 | 0.37 | ppt |
Solids, Suspended at 105 C | <6 | 11 | <6 | 12 | mg/l |
Temperature of Water | 5 | 5.2 | 4.5 | 5.3 | CEL |
Aluminium | 0.28 | 0.35 | 0.21 | 0.82 | mg/l |
Barium | 0.015 | 0.014 | 0.012 | 0.012 | mg/l |
Calcium | 84 | 82 | 84 | 83 | mg/l |
Copper |
|
|
| 0.01 | mg/l |
Iron | 0.41 | 0.62 | 0.33 | 0.64 | mg/l |
Magnesium | 4.9 | 4.8 | 4.8 | 5 | mg/l |
Manganese |
| 0.011 |
| 0.016 | mg/l |
Potassium | 4.1 | 3.6 | 3.8 | 3.6 | mg/l |
Sodium | 22 | 20 | 22 | 20 | mg/l |
Strontium | 0.23 | 0.21 | 0.22 | 0.21 | mg/l |
Zinc | 0.005 | 0.006 | 0.005 | 0.012 | mg/l |
1,1-Dimethyl-3-chloropropanol |
| 0.016 |
|
| ug/l |
1,3-Benzenediol, monobenzoate |
| 0.013 |
|
| ug/l |
13-Docosenamide, (Z)- |
|
| 1 |
| ug/l |
1-Butanol, 2,3-dimethyl- | 0.087 | 0.316 |
| 0.085 | ug/l |
1-Pentene, 4,4-dimethyl- | 0.016 |
|
|
| ug/l |
2-(4'-Methoxyphenyl)-2-(3'-methyl-4'methoxyphenyl)propane |
|
| 0.071 |
| ug/l |
2,2,4-Trimethyl-1,3-pentanediol diisobutyrate |
|
| 0.049 |
| ug/l |
2,4,6-Trimethyl-1-nonene |
|
| 0.081 |
| ug/l |
2,4,7,9-Tetramethyl-5-decyne-4,7-diol | 0.295 | 0.402 | 0.346 | 0.401 | ug/l |
2-Butanol, 2,3-dimethyl- |
| 0.188 |
|
| ug/l |
2-Ethylhexanoic acid |
| 0.172 |
|
| ug/l |
3-Buten-2-one, 3-methyl- |
|
|
| 0.063 | ug/l |
3-Hexanone, 2,5-dimethyl- | 0.014 |
|
|
| ug/l |
3-Pentanone | 0.018 | 0.02 | 0.027 |
| ug/l |
3-Penten-2-one | 0.045 |
|
|
| ug/l |
4-Cyanocyclohexene |
| 0.036 |
|
| ug/l |
4H-1,2,4-Triazol-4-amine |
|
| 0.045 |
| ug/l |
Butyl aldoxime, 3-methyl-, syn- |
| 0.062 |
|
| ug/l |
Caffeine | 0.057 | 0.053 | 0.061 | 0.071 | ug/l |
Caprolactam |
| 0.779 |
| 0.336 | ug/l |
Decane, 2,2,8-trimethyl- | 0.013 |
|
|
| ug/l |
Dimethyl phthalate |
|
|
| 0.07 | ug/l |
Diphenyl sulfone |
| 0.007 |
|
| ug/l |
Ethanone, 1,1'-(1,4-phenylene)bis- |
| 0.62 | 0.572 |
| ug/l |
Ethanone, 1-[4-(1-hydroxy-1-methylethyl)phenyl]- |
| 0.097 | 0.169 |
| ug/l |
Ethanone, 2,2-dimethoxy-1,2-diphenyl- |
|
| 0.069 | 0.054 | ug/l |
Fluoranthene |
| 0.003 |
|
| ug/l |
Hexamethoxymethylmelamine | 0.827 | 0.655 |
| 0.929 | ug/l |
Hexane, 3,3-dimethyl- | 0.015 |
|
|
| ug/l |
meso-3,4-Hexanediol |
| 0.062 |
|
| ug/l |
N,N-Diethyl-m-toluamide |
| 0.011 | 0.101 |
| ug/l |
n-Hexadecanoic acid | 0.091 |
| 0.404 | 0.269 | ug/l |
Octadecanoic acid | 0.03 | 0.094 | 0.17 | 0.096 | ug/l |
Octan-2-yl palmitate |
|
| 0.06 |
| ug/l |
Propyzamide | 0.032 | 0.04 | 0.046 | 0.036 | ug/l |
Sulfurous acid, 2-ethylhexyl hexyl ester |
| 0.024 | 0.026 |
| ug/l |
Supraene |
| 0.085 |
|
| ug/l |
Tri-(2-chloroethyl) phosphate |
| 0.076 | 0.078 | 0.124 | ug/l |
Tri-allate |
|
|
| 0.012 | ug/l |
Triethyl Citrate |
| 0.403 |
|
| ug/l |
Trifluoroacetic acid, 2-tetrahydrofurylmethyl ester |
|
|
| 0.045 | ug/l |
Undecane, 4,6-dimethyl- | 0.034 |
|
|
| ug/l |
Use limitation statement
There are no public access constraints to this data. Use of this data is subject to the licence identified.
Licence
Open Government Licence(External link)
Attribution statement
© Environment Agency copyright and/or database right 2025. All rights reserved.
Analytical results from samples taken 5 January 2026
Our assessment of samples taken on 5 January 2026 has identified some chemicals present in the River Cherwell at negligible levels downstream of the waste that are not found upstream. We cannot be certain if they are from the waste pile or another source and they include chemicals that are found in other English waterways. Any impacts on the environment are negligible.
This data includes that obtained by using the GC-MS analytical technique: further guidance on this is available here: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen
Disclaimer for GCMS Results: All results are an approximate concentration. Where accreditation is claimed this is only for the identification of the substance and not the quantified amount.
The compounds identified in the GCMS results fit into one of four criteria, which can be pulled from the original dataset if required:
Samples were taken from the following locations:
Sample | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP 50764 13829 |
D/S River Cherwell 1 (Sample 3) | SP 50916 13798 |
D/S River Cherwell 2 (Sample 4) | SP 50943 13253 |
U/S = Upstream of the waste
D/S = Downstream of the waste
Waste = Sample taken from run-off/standing groundwater that has collated around the waste site boundary
NGR = National Grid Reference
Determinand / Compound Name | U/S 1 | U/S 2 | D/S 1 | D/S 2 | Unit |
pH | 7.41 | 8.13 | 8.11 | 8.16 | PHUNITS |
Temperature of Water | 2.4 | 2.5 | 2.9 | 2.6 | CEL |
Conductivity at 25 C | 731 | 681 | 693 | 683 | uS/cm |
BOD : 5 Day ATU | <3 | <3 | <3 | <3 | mg/l |
Chemical Oxygen Demand :- {COD} | 15 | <10 | <10 | <10 | mg/l |
Ammoniacal Nitrogen as N | <0.03 | <0.03 | <0.03 | <0.03 | mg/l |
Nitrogen, Total Oxidised as N | 1.7 | 7.8 | 7.8 | 7.8 | mg/l |
Nitrite as N | 0.012 | 0.012 | 0.012 | 0.011 | mg/l |
Ammonia un-ionised as N | <0.00008 | <0.00032 | <0.00032 | <0.00032 | mg/l |
Solids, Suspended at 105 C | <6 | 6.5 | 6.7 | 6.5 | mg/l |
Chloride | 51 | 38 | 38 | 38 | mg/l |
Orthophosphate, reactive as P | 0.063 | 0.081 | 0.082 | 0.083 | mg/l |
Visible oil or grease, significant trace: Present/Not found (1/0) |
| Not found | Not found | Not found | N/A |
Salinity : In Situ |
| 0.33 | 0.34 | 0.33 | ppt |
Oxygen, Dissolved, % Saturation | 39.2 | 95.9 | 94.1 | 96.9 | % |
Sodium | 29 | 24 | 23 | 23 | mg/l |
Magnesium | 5.3 | 5.8 | 5.7 | 5.8 | mg/l |
Aluminium | 0.055 | 0.16 | 0.28 | 0.19 | mg/l |
Potassium | 4.2 | 4.3 | 4.4 | 4.2 | mg/l |
Calcium | 110 | 110 | 100 | 110 | mg/l |
Manganese | 0.059 | 0.013 | 0.016 | 0.017 | mg/l |
Iron | 0.10 | 0.26 | 0.32 | 0.34 | mg/l |
Copper |
|
| 0.0095 |
| mg/l |
Zinc |
|
| 0.0088 |
| mg/l |
Strontium | 0.36 | 0.25 | 0.25 | 0.25 | mg/l |
Barium | 0.019 | 0.011 | 0.012 | 0.012 | mg/l |
(E)-9-Octadecenoic acid ethyl ester |
|
|
| 3.2 | ug/l |
.beta.-Guanidinopropionic acid |
| 0.013 |
|
| ug/l |
1,1-Dimethyl-3-chloropropanol |
| 0.014 |
|
| ug/l |
1,2-Benzenediol, o-(3-bromobenzoyl)-o'-(2,3,4-trifluorobenzoyl)- |
|
| 0.039 |
| ug/l |
1,3-Dimethyl-5-pylazolyl-2,4-dichlorobenzoate | 0.031 | 0.033 | 0.02 |
| ug/l |
1H-Pyrazole, 4,5-dihydro-5-methyl- |
|
|
| 0.064 | ug/l |
1-Hydroxy-3-methoxy-6-methylanthraquinone, TMS derivative |
|
| 0.061 |
| ug/l |
1-Propene-1,2,3-tricarboxylic acid, tributyl ester | 0.012 |
| 0.016 |
| ug/l |
2,2,4-Trimethyl-1,3-pentanediol diisobutyrate | 0.02 |
| 0.023 | 0.058 | ug/l |
2,4,7,9-Tetramethyl-5-decyne-4,7-diol | 0.285 | 0.225 | 0.277 | 0.206 | ug/l |
2,5,8-Triphenyl benzotristriazole |
|
|
| 0.015 | ug/l |
2-{2-[2-(Acryloyloxy)-1-methylethoxy]-1-methylethoxy}-1-methylethyl acrylate |
|
|
| 0.074 | ug/l |
2-Ethylhexanal ethylene glycol acetal |
| 0.028 |
|
| ug/l |
2-Pentene, 4,4'-oxybis- | 0.215 | 0.266 |
|
| ug/l |
2-Propenoic acid, (1-methyl-1,2-ethanediyl)bis[oxy(methyl-2,1-ethanediyl)] ester |
|
|
| 0.014 | ug/l |
2-Propenoic acid, 2-methyl-, 1-methylbutyl ester | 0.259 | 0.307 | 0.131 | 0.158 | ug/l |
2-Pyrrolidinone, 1-butyl- |
|
|
| 0.065 | ug/l |
3,4-Dihydroxymandelic acid, 4TMS derivative |
| 0.016 |
|
| ug/l |
3,4-Hexanedione, 2,2,5-trimethyl- |
| 0.016 |
|
| ug/l |
3-Acetyl-2,5-dimethyl furan | 0.015 |
|
|
| ug/l |
3-Hexanol, 4-methyl- |
| 0.13 |
|
| ug/l |
3-Hexanone |
| 0.012 |
|
| ug/l |
3-Hexanone, 2,5-dimethyl- |
| 0.021 | 0.016 |
| ug/l |
3-Penten-2-one | 0.11 | 0.123 | 0.05 |
| ug/l |
3-Penten-2-one, (E)- |
|
|
| 0.107 | ug/l |
4-(7-Methyloctyl)phenol |
|
| 0.011 |
| ug/l |
4-fluorophenyl 4-(4-pentylcyclohexyl)benzoate |
|
| 0.017 |
| ug/l |
4-Hydroxy-2-methylacetophenone |
|
|
| 0.018 | ug/l |
9,12-Octadecadienoic acid (Z,Z)- |
|
|
| 4 | ug/l |
9-Octadecenoic acid |
|
|
| 28 | ug/l |
Acetic acid, 3-acetoxy-1-ethyl-2-nitropentyl ester | 0.04 |
|
|
| ug/l |
Benzene, (trimethoxymethyl)- |
|
|
| 0.025 | ug/l |
Benzophenone |
|
|
| 0.11 | ug/l |
Bicyclo[4.1.0]heptane, 7-methylene- |
|
|
| 1.1 | ug/l |
Bisphenol A | 0.07 |
| 0.065 |
| ug/l |
Butane, 2-chloro-2-methyl- |
|
|
| 0.089 | ug/l |
Butanoic acid, 2,3-dimethyl-, methyl ester |
|
|
| 0.026 | ug/l |
Butanoic acid, 2-methyl- |
|
|
| 0.024 | ug/l |
Butanoic acid, 3-methyl- |
|
|
| 0.047 | ug/l |
Caffeine | 0.019 | 0.07 | 0.076 | 0.467 | ug/l |
Caprolactam | 0.195 |
|
|
| ug/l |
Carbamazepine |
| 0.039 | 0.056 | 0.031 | ug/l |
cis-9-Octadecenoic acid, propyl ester |
|
|
| 1.6 | ug/l |
Crotamiton |
| 0.024 | 0.031 |
| ug/l |
Cyclopenta[g]-2-benzopyran, 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethyl- |
| 0.015 | 0.018 | 0.015 | ug/l |
Decane, 2,4-dimethyl- |
|
| 0.017 | 0.017 | ug/l |
Diphenyl ether |
|
|
| 0.005 | ug/l |
Diphenyl sulfone | 0.03 | 0.013 | 0.015 |
| ug/l |
Dodecanoic acid |
|
|
| 0.146 | ug/l |
Ethanone, 1-(2-hydroxy-5-methylphenyl)- |
| 0.012 |
|
| ug/l |
Ethanone, 2,2-dimethoxy-1,2-diphenyl- | 0.069 | 0.058 | 0.151 |
| ug/l |
Fluoranthene |
| 0.003 |
|
| ug/l |
Formamide, N,N-dibutyl- |
|
|
| 0.034 | ug/l |
Hexadecanoic acid, ethyl ester |
|
|
| 0.334 | ug/l |
Hexadecanoic acid, methyl ester |
| 0.062 | 0.073 |
| ug/l |
Hexadecanoic acid, propyl ester |
|
|
| 0.105 | ug/l |
Hexanoic acid |
|
|
| 0.242 | ug/l |
Hexyl salicyclate |
|
|
| 0.034 | ug/l |
Isomaltol | 0.012 |
|
|
| ug/l |
Linoleic acid ethyl ester |
|
|
| 1.1 | ug/l |
Metacetamol | 0.04 |
|
|
| ug/l |
Methylal |
|
|
| 0.05 | ug/l |
N,N,N',N'-Tetraacetylethylenediamine |
| 0.108 | 0.124 | 0.073 | ug/l |
N,N-Diethyl-m-toluamide |
| 0.018 | 0.027 | 0.022 | ug/l |
N-Cyclohexyl-N'-methylurea, N'-methyl |
| 0.019 |
|
| ug/l |
n-Hexadecanoic acid | 0.108 | 0.188 |
| 17 | ug/l |
Nonanal |
|
|
| 0.083 | ug/l |
n-Propyl 9,12-octadecadienoate |
|
|
| 0.312 | ug/l |
n-Propyl acetate |
|
|
| 0.033 | ug/l |
Octadecanoic acid |
| 0.062 | 0.224 | 3 | ug/l |
Octadecanoic acid, ethyl ester |
|
|
| 0.103 | ug/l |
Octan-2-yl palmitate |
| 0.021 | 0.022 | 0.053 | ug/l |
p-Cresol (4-methylphenol) |
|
|
| 0.225 | ug/l |
Pentanoic acid |
|
|
| 0.441 | ug/l |
Pentanoic acid, 5-hydroxy-, 2,4-di-t-butylphenyl esters | 0.079 | 0.063 | 0.099 |
| ug/l |
Phenol, 2,4-bis(1,1-dimethylethyl)-, phosphite (3:1) |
|
| 0.243 |
| ug/l |
Phenol, 2,4-di-t-butyl-6-nitro- |
| 0.024 | 0.012 |
| ug/l |
Phosphoric acid, 2-chloroethenyl dimethyl ester |
| 0.024 |
| 0.026 | ug/l |
Propyzamide | 0.012 | 0.019 | 0.019 |
| ug/l |
Pyridine, 2,3,6-trimethyl- |
| 0.016 |
|
| ug/l |
Sulfurous acid, 2-ethylhexyl hexyl ester |
|
| 0.022 |
| ug/l |
Tetradecane |
|
|
| 0.023 | ug/l |
Tetradecanoic acid |
|
|
| 0.811 | ug/l |
Tri-(2-chloroethyl) phosphate |
|
| 0.045 |
| ug/l |
Tributyl phosphate |
|
|
| 0.027 | ug/l |
Triethyl Citrate |
| 0.831 | 1.2 | 1 | ug/l |
Use limitation statement
There are no public access constraints to this data. Use of this data is subject to the licence identified.
Licence
Open Government Licence(External link)
Attribution statement
© Environment Agency copyright and/or database right 2025. All rights reserved.
Analytical results from samples taken 16 December 2025
Our analysis has been reviewed by specialists in toxicology. Our latest assessment of samples taken on 16 December 2025 suggests there may be minimal seepage into the River Cherwell, however any impacts on the environment are negligible. The chemicals that we’ve found downstream of the site are similar to those already found in the watercourse.
Water quality samples include an assessment using the gas chromatography-mass spectrometry (GCMS) screening technique: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen
We will continue to monitor and we will make sample results available as and when the analysis is complete.
Samples were taken from the following locations:
Sample | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP 50764 13829 |
Ingress (Sample 3) | SP 50791 13850 |
Waste (Sample 4) | SP 50781 14094 |
D/S River Cherwell 1 (Sample 3) | SP 50916 13798 |
D/S River Cherwell 2 (Sample 4) | SP 50943 13253 |
U/S = Upstream of the waste
D/S = Downstream of the waste
Waste = Sample taken from run-off/standing groundwater that has collated around the waste site boundary
NGR = National Grid Reference
Biological Oxygen Demand (BOD) results are not yet available.
Determinand / Compound Name | U/S 1 (Sample 1) | U/S 2 (Sample 2) | Ingress (Sample 3) | Waste (Sample 4) | D/S 1 (Sample 5) | D/S 2 | Unit |
Temperature of Water | 9.1 | 8.6 | 8.5 | 8.7 | 8.5 | 8.6 | CEL |
Conductivity at 25 C | 697 | 610 | 677 | 1271 | 604 | 604 | uS/cm |
BOD : 5 Day ATU |
|
|
|
|
|
| mg/l |
Chemical Oxygen Demand :- {COD} | 29 | 12 | 24 | 95 | 13 | 13 | mg/l |
Ammoniacal Nitrogen as N | <0.03 | <0.03 | <0.03 | 3.2 | <0.03 | <0.03 | mg/l |
Nitrogen, Total Oxidised as N | 1.9 | 6.8 | 2.2 | <0.2 | 6.8 | 6.7 | mg/l |
Nitrite as N | 0.032 | 0.011 | 0.04 | <0.004 | 0.011 | 0.01 | mg/l |
Ammonia un-ionised as N | <0.00013 | <0.00039 | <0.00015 | 0.00935 | <0.00038 | <0.00038 | mg/l |
Solids, Suspended at 105 C | 9.4 | 10 | 29 | 22 | 12 | 13 | mg/l |
Chloride | 56 | 27 | 44 | 52 | 28 | 27 | mg/l |
Orthophosphate, reactive as P | 0.11 | 0.079 | 0.072 | 0.03 | 0.078 | 0.08 | mg/l |
Visible oil or grease, significant trace: Present/Not found (1/0) | Not found | Not found | Not found | Not found | Not found | Not found | N/A |
Salinity : In Situ | 0.34 | 0.3 | 0.33 | 0.64 | 0.29 | 0.29 | ppt |
Oxygen, Dissolved, % Saturation | 43.8 | 86.1 | 49.4 | 30.7 | 87 | 87.1 | % |
Aluminium | 0.2 | 0.33 | 0.47 | 0.29 | 0.51 | 0.42 | mg/l |
Barium | 0.023 | 0.013 | 0.02 | 0.053 | 0.014 | 0.014 | mg/l |
Calcium | 99 | 96 | 110 | 220 | 97 | 97 | mg/l |
Iron | 0.31 | 0.48 | 0.94 | 0.61 | 0.79 | 0.64 | mg/l |
Magnesium | 5.1 | 5.2 | 5.4 | 9.7 | 5.3 | 5.3 | mg/l |
Manganese | 0.041 | 0.017 | 0.034 | 1.2 | 0.026 | 0.021 | mg/l |
Potassium | 6.2 | 3.8 | 5.2 | 5.6 | 3.8 | 3.8 | mg/l |
Sodium | 31 | 17 | 24 | 36 | 17 | 17 | mg/l |
Strontium | 0.33 | 0.24 | 0.33 | 0.76 | 0.24 | 0.24 | mg/l |
Zinc | 0.0078 |
| 0.0084 | 0.047 | 0.0056 | 0.006 | mg/l |
Nickel |
|
|
| 0.0064 |
|
| mg/l |
Copper |
|
|
| 0.024 |
|
| mg/l |
Lead |
|
|
| 0.0071 |
|
| mg/l |
(-)-Pinane-3-carboxylic acid |
|
|
| 0.329 |
|
| ug/l |
(Propan-2-yloxy)carbohydrazide | 0.035 |
|
|
| 0.012 |
| ug/l |
.alpha.,.alpha.'-Dihydroxy-m-diisopropylbenzene |
|
|
| 0.194 |
|
| ug/l |
1-((1S,3aR,4R,7S,7aS)-4-Hydroxy-7-isopropyl-4-methyloctahydro-1H-inden-1-yl)ethanone |
|
|
| 0.268 |
|
| ug/l |
1-(2-Thienyl)-1-propanone |
|
|
| 0.041 |
|
| ug/l |
1(3H)-Isobenzofuranone |
|
|
| 0.156 |
|
| ug/l |
1-(Ethylsulfonyl)piperazine |
|
|
| 0.013 |
|
| ug/l |
1,3,5,7-Tetroxane |
|
|
| 0.173 |
|
| ug/l |
1,3,5-Trially-1,3,5-triazine-2,4,6-trione |
|
|
| 0.143 |
|
| ug/l |
1,3,5-Triazine-2,4,6(1H,3H,5H)-trione, 1,3,5-trimethyl- |
|
|
| 0.038 |
|
| ug/l |
1,3-Benzenediol, monobenzoate |
| 0.017 |
|
|
|
| ug/l |
1,3-Cyclohexadiene-1-carboxaldehyde, 2,6,6-trimethyl- |
|
|
| 0.13 |
|
| ug/l |
1,3-Cyclohexanedione, 2,2,5,5-tetramethyl- |
|
|
| 0.052 |
|
| ug/l |
1,3-Dimethyl-5-pylazolyl-2,4-dichlorobenzoate |
| 0.034 |
|
|
|
| ug/l |
1,4-Dioxane |
|
|
| 0.269 |
|
| ug/l |
1,8-Diazacyclotetradecane-2,7-dione |
|
|
| 0.133 |
|
| ug/l |
1-Butanol, 2,3-dimethyl- | 0.084 | 0.054 | 0.125 | 0.062 | 0.189 | 0.083 | ug/l |
1-Butanol, 4-(1-methylethoxy)- |
|
|
| 0.089 |
|
| ug/l |
1-Butanone, 1-(2,4,5-trihydroxyphenyl)- |
|
|
| 0.015 |
|
| ug/l |
1-Ethyl-2-pyrrolidone |
|
|
| 0.595 |
|
| ug/l |
1H-Pyrazole, 5-methoxy-1,3-dimethyl- |
| 0.012 | 0.013 |
|
|
| ug/l |
1-Pentanone, 1-(4-methylphenyl)- |
|
|
| 0.023 |
|
| ug/l |
1-Propanol, 2-(2-hydroxypropoxy)- |
|
|
| 0.183 |
|
| ug/l |
2-(2-(2-Butoxyethoxy)ethoxy)acetic acid |
|
|
| 0.277 |
|
| ug/l |
2-(2-Butoxyethoxy)acetic acid |
|
|
| 0.341 |
|
| ug/l |
2-(2-Chloroethoxy)-1,3,2-dioxaphospholan-2-one |
|
|
| 0.014 |
|
| ug/l |
2-(2-Chloroethoxy)ethyl bis(2-chloroethyl) phosphate |
|
|
| 0.221 |
|
| ug/l |
2(3H)-Benzothiazolone |
|
|
| 2 |
|
| ug/l |
2(5H)-Furanone, 5-(acetyloxy)- |
| 0.015 |
|
|
|
| ug/l |
2,2,4,4,5,5,7,7-Octamethyloctane | 0.039 |
|
|
| 0.046 |
| ug/l |
2,2,5,5-Tetramethyl-3-hexanone |
| 0.012 | 0.019 |
|
|
| ug/l |
2,3-Dimethylpentanoic acid |
|
|
| 0.14 |
|
| ug/l |
2,4,7,9-Tetramethyl-5-decyne-4,7-diol |
| 0.131 | 0.12 | 4.6 | 0.157 | 0.164 | ug/l |
2,4-Imidazolidinedione, 5-ethyl-5-methyl- |
|
|
| 0.02 |
|
| ug/l |
2,6-Dimethoxyhydroquinone |
|
|
| 0.018 |
|
| ug/l |
2-Chloroethyl benzoate |
|
| 0.047 | 0.094 |
|
| ug/l |
2H-Pyran-2-one, tetrahydro-4-methyl- |
|
|
| 0.015 |
|
| ug/l |
2-Pentanol, 2-methyl- |
|
|
|
| 0.012 | 0.027 | ug/l |
2-Propanol, 1-(2-butoxy-1-methylethoxy)- |
|
|
| 0.201 |
|
| ug/l |
2-Propanol, 1-(2-methoxy-1-methylethoxy)- |
|
|
| 0.031 |
|
| ug/l |
2-Propanol, 1,3-dichloro- |
|
| 0.013 | 0.226 |
|
| ug/l |
2-Propanol, 1-butoxy- |
|
|
| 0.027 |
|
| ug/l |
2-Propanol, 1-chloro- |
|
|
| 0.569 |
|
| ug/l |
2-Propanol, 1-chloro-, phosphate (3:1) |
|
| 1.9 | 38 |
|
| ug/l |
2-Pyrrolidinone, 1-butyl- |
|
|
| 0.056 |
|
| ug/l |
2-Pyrrolidinone, 1-methyl- |
|
|
| 0.065 |
|
| ug/l |
2-Thio-2,4-oxazolidinedione |
|
|
| 0.017 |
|
| ug/l |
2-Thiopheneacetamide, N,N-dibutyl- |
|
|
| 0.074 |
|
| ug/l |
2-Thiophenecarboxylic acid, 4-nitrophenyl ester |
|
|
| 0.035 |
|
| ug/l |
3,5-di-tert-Butyl-4-hydroxyphenylpropionic acid |
|
|
| 1.5 |
|
| ug/l |
3,5-Heptanedione, 2,2,4,6,6-pentamethyl- |
|
| 0.017 |
|
|
| ug/l |
3-Cyclohexen-1-ol, 4-methyl-1-(1-methylethyl)-, (R)- |
|
|
| 0.079 |
|
| ug/l |
3-Ethyl-4-hydroxy-dihydro-furan-2-one |
|
|
| 0.051 |
|
| ug/l |
3-Ethylheptanoic acid |
|
|
| 0.065 |
|
| ug/l |
3-Heptanone, 2,4-dimethyl- |
|
|
|
| 0.018 |
| ug/l |
3-Heptyne-2,6-dione, 5-methyl-5-(1-methylethyl)- |
|
|
| 0.049 |
|
| ug/l |
3-Hexanol, 4-methyl- |
|
| 0.027 |
|
|
| ug/l |
3-Hexen-1-ol, propanoate, (Z)- |
|
|
| 0.027 |
|
| ug/l |
3-Pentanol, 3-methyl- |
|
|
| 0.071 |
|
| ug/l |
3-Piperidinol, 1-ethyl- |
|
|
| 0.054 |
|
| ug/l |
4,4-Dimethyl-1,2,3,4-tetrahydro-.gamma.-carboline |
|
|
| 0.024 |
|
| ug/l |
4,5-Dimethoxy-2-hydroxyacetophenone |
|
|
| 0.136 |
|
| ug/l |
4,6-Octadiyn-3-one, 2-methyl- |
|
|
|
| 0.01 |
| ug/l |
4-Chlorobutyric acid, 4-isopropylphenyl ester |
|
|
| 0.021 |
|
| ug/l |
4-Ethyl-2,6-dimethoxyphenol |
|
|
| 0.062 |
|
| ug/l |
4-Octene-2,7-diol, 2,7-dimethyl-, Z- |
|
|
| 0.054 |
|
| ug/l |
4-Piperidinone, 2,2,6,6-tetramethyl- |
|
|
| 0.044 |
|
| ug/l |
4'-Propoxy-2-methylpropiophenone |
|
|
| 0.124 |
|
| ug/l |
4-Propoxybenzoic acid trimethylsilyl ester |
|
|
| 0.018 |
|
| ug/l |
5'-Hydroxy-2',3',4'-trimethylacetophenone |
|
|
| 0.19 |
|
| ug/l |
5-Hydroxymethylfurfural |
|
|
| 0.279 |
|
| ug/l |
7-Chloro-1-(4-fluorophenyl)heptan-1-one |
|
|
| 0.035 |
|
| ug/l |
8-Hydroxycarvotanacetone |
|
|
| 0.055 |
|
| ug/l |
Acetic acid ethenyl ester |
|
|
|
| 0.019 |
| ug/l |
Acetic acid, (2,4-xylyl)- |
|
|
| 0.148 |
|
| ug/l |
Acetyl valeryl |
|
|
| 0.021 |
|
| ug/l |
Atrazine |
|
|
| 2.9 |
|
| ug/l |
Atrazine desethyl |
|
|
| 1.4 |
|
| ug/l |
Aziridinone, 1,3-bis(1,1-dimethylethyl)- |
|
|
| 0.026 |
|
| ug/l |
Benzenamine, 4-methyl-N,N-bis(4-methylphenyl)- |
|
|
| 0.022 |
|
| ug/l |
Benzeneacetic acid |
|
|
| 0.529 |
|
| ug/l |
Benzenebutanoic acid, 2,5-dimethyl- |
|
|
| 0.345 |
|
| ug/l |
Benzenemethanol, .alpha.,.alpha.,4-trimethyl- |
|
|
| 0.228 |
|
| ug/l |
Benzenemethanol, .alpha.,.alpha.-dimethyl- |
|
|
| 0.116 |
|
| ug/l |
Benzenemethanol, .alpha.-methyl- |
|
|
| 0.027 |
|
| ug/l |
Benzenesulfonamide, 2-methyl- |
|
|
| 0.256 |
|
| ug/l |
Benzenesulfonamide, 4-methyl- |
|
| 0.251 | 7.2 |
|
| ug/l |
Benzenesulfonamide, N-butyl | 0.222 |
| 0.565 | 3.8 |
|
| ug/l |
Benzenesulfonanilide |
|
|
| 0.059 |
|
| ug/l |
Benzoic acid, 2,4,6-trimethyl- |
|
|
| 0.435 |
|
| ug/l |
Benzoic acid, 2,6-dichloro- |
|
|
| 0.029 |
|
| ug/l |
Benzoic acid, 3,5-bis(1,1-dimethylethyl)-4-hydroxy- |
|
|
| 0.077 |
|
| ug/l |
Benzoic acid, 4-(1-methylethyl)- |
|
|
| 0.095 |
|
| ug/l |
Benzoic acid, 4-methyl- |
|
|
| 0.017 |
|
| ug/l |
Bicyclo[2.2.1]heptane-2,5-dione, 1,7,7-trimethyl- |
|
|
| 0.035 |
|
| ug/l |
Bicyclo[3.1.1]heptan-2-one, 3,6,6-trimethyl- |
|
|
| 0.34 |
|
| ug/l |
Bis(1-chloro-2-propyl)(3-chloro-1-propyl)phosphate |
|
| 0.281 | 13 |
|
| ug/l |
Bis(1-chloro-2-propyl)-3-(3-chloropropoxy)propyl phosphate |
|
|
| 0.487 |
|
| ug/l |
Bis(2-methoxyethoxy)methane |
|
|
| 1.6 |
|
| ug/l |
Bis(3-chloro-1-propyl)(1-chloro-2-propyl)phosphate |
|
| 0.018 | 1 |
|
| ug/l |
Bisphenol A |
| 0.015 | 0.102 | 0.576 |
| 0.017 | ug/l |
Bromoform | 0.017 | 0.017 | 0.011 |
| 0.014 | 0.012 | ug/l |
Butane, 2-methoxy-2-methyl- |
|
|
| 0.074 |
|
| ug/l |
Butanoic acid, 2-ethyl-, methyl ester |
|
|
| 0.115 |
|
| ug/l |
Butanoic acid, 2-methyl- |
|
|
| 0.02 |
|
| ug/l |
Butanoic acid, 3-methyl- |
|
|
| 0.142 |
|
| ug/l |
Butanoic acid, methyl ester |
|
| 0.016 |
|
|
| ug/l |
Caffeine | 0.026 | 0.053 | 0.19 |
| 0.065 | 0.063 | ug/l |
Caprolactam |
|
|
| 19 |
|
| ug/l |
Carbamazepine |
| 0.016 |
|
| 0.023 | 0.019 | ug/l |
Carbonic acid, 2-ethoxyethyl 2-methoxyethyl ester |
|
|
| 0.038 |
|
| ug/l |
Coumarin |
|
|
| 0.177 |
|
| ug/l |
Cyclobutanone, 2,3,3-trimethyl- |
|
|
| 0.014 |
|
| ug/l |
Cyclohexanecarboxylic acid, 4-(1,5-dimethyl-3-oxohexyl)-, methyl ester, cis- |
|
|
| 0.454 |
|
| ug/l |
Cyclohexanemethanol, 4-hydroxy-.alpha.,.alpha.,4-trimethyl- |
|
|
| 0.41 |
|
| ug/l |
Cyclohexanol |
|
|
| 0.033 |
|
| ug/l |
Cyclopenta[g]-2-benzopyran, 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethyl- |
|
|
|
| 0.009 |
| ug/l |
Decyl acrylate |
| 0.029 | 0.059 |
|
|
| ug/l |
Dehydroabietic acid |
|
|
| 0.291 |
|
| ug/l |
Didesmethyldiphenhydramine |
|
|
| 0.024 |
|
| ug/l |
Diethyl carbitol |
|
|
| 0.055 |
|
| ug/l |
Diethyl ethylphosphonate |
|
|
| 0.049 |
|
| ug/l |
Dimethyl sulfone |
|
|
| 0.061 |
|
| ug/l |
Diphenyl sulfone |
|
| 0.08 | 0.363 |
| 0.005 | ug/l |
Disulfide, diheptyl |
|
|
| 0.095 |
|
| ug/l |
DL-4,5-Octanediol |
|
|
| 0.033 |
|
| ug/l |
Ethanol, 2-butoxy-, phosphate (3:1) |
|
|
| 0.285 |
|
| ug/l |
Ethanol, 2-ethoxy- |
|
|
| 0.046 |
|
| ug/l |
Ethanone, 1-(3-hydroxy-4-methoxyphenyl)- |
|
|
| 0.019 |
|
| ug/l |
Ethiolate |
|
|
| 0.167 |
|
| ug/l |
Ethyl 4-(ethyloxy)-2-oxobut-3-enoate |
|
|
| 0.057 |
|
| ug/l |
Eucalyptol |
|
|
| 0.027 |
|
| ug/l |
Fenchone |
|
|
| 0.028 |
|
| ug/l |
Fluoranthene | 0.007 | 0.004 | 0.005 |
| 0.009 | 0.009 | ug/l |
Formamide, N,N-dimethyl- |
|
|
| 0.025 |
|
| ug/l |
Fumaric acid, 4-cyanophenyl pentyl ester |
|
|
| 0.098 |
|
| ug/l |
Fumaronitrile |
|
|
|
|
| 0.012 | ug/l |
hexadecyl acrylate |
|
|
| 0.418 |
|
| ug/l |
Hexamethoxymethylmelamine |
|
|
|
| 0.388 | 0.265 | ug/l |
Hexane, 3,3-dimethyl- |
|
|
| 0.028 |
|
| ug/l |
Hexanoic acid, 3,5,5-trimethyl- |
|
|
| 0.229 |
|
| ug/l |
Hexathiane |
|
|
| 0.431 |
|
| ug/l |
Ibuprofen |
|
|
| 0.174 |
|
| ug/l |
l-Alanine, N-(2,3,4-trifluorobenzoyl)-, methyl ester |
|
|
| 0.056 |
|
| ug/l |
L-Fenchone |
|
|
| 0.028 |
|
| ug/l |
m-Aminophenylacetylene |
|
|
| 0.523 |
|
| ug/l |
Mecoprop |
|
|
| 5.3 |
|
| ug/l |
N,N,N',N'-Tetraacetylethylenediamine |
|
|
|
| 0.042 | 0.051 | ug/l |
N,N-Diethyl-m-toluamide |
| 0.016 | 0.014 | 0.388 | 0.013 | 0.016 | ug/l |
N-Cyclohexyl-N'-methylurea, N'-methyl |
|
|
| 0.024 |
|
| ug/l |
Neodecanoic acid |
|
|
| 0.612 |
|
| ug/l |
n-Hexadecanoic acid | 0.156 |
|
|
|
|
| ug/l |
Octadecanoic acid |
|
|
| 0.523 |
|
| ug/l |
Pentanoic acid, 5-hydroxy-, p-t-butylphenyl ester |
| 0.011 | 0.014 |
|
|
| ug/l |
Phenylacetamide, 4-fluoro-N-propyl- |
|
|
| 0.014 |
|
| ug/l |
Phosphoramidous difluoride |
|
|
| 0.021 |
|
| ug/l |
Phosphoric acid, 2-chloroethenyl dimethyl ester |
|
| 0.016 |
|
|
| ug/l |
Phthalic anhydride |
|
|
| 0.022 |
|
| ug/l |
Propanoic acid, 2-methyl- |
|
|
| 0.039 |
|
| ug/l |
Propanol, [(butoxymethylethoxy)methylethoxy]- |
|
|
| 0.032 |
|
| ug/l |
Propyzamide |
| 0.018 | 0.016 |
| 0.017 | 0.021 | ug/l |
Pyrazine |
|
|
| 0.08 |
|
| ug/l |
Pyrene |
|
| 0.004 |
| 0.006 | 0.007 | ug/l |
Pyridine, 2,3,6-trimethyl- |
| 0.021 | 0.011 |
|
| 0.011 | ug/l |
Sal Ethyl carbonate |
|
|
| 0.024 |
|
| ug/l |
Sulfone, methyl phenyl |
|
|
| 0.048 |
|
| ug/l |
Sulfur (S8) |
|
|
| 9.5 |
|
| ug/l |
Terpineol |
|
|
| 1.4 |
|
| ug/l |
Tetramethylfuran |
|
|
| 0.04 |
|
| ug/l |
Tri-(2-chloroethyl) phosphate |
|
| 0.095 | 14 | 0.023 |
| ug/l |
Tributyl phosphate |
|
|
| 0.055 |
|
| ug/l |
Tricyclo[2.2.1.0(2,6)]heptane, 1,3,3-trimethyl- | 0.162 |
|
|
|
|
| ug/l |
Triethyl Citrate |
| 0.327 |
|
| 0.422 | 0.358 | ug/l |
Triethyl phosphate |
|
|
| 1.6 |
|
| ug/l |
Triisopropylphosphate |
|
|
| 0.071 |
|
| ug/l |
Tris-(1,3-dichloroisopropyl) phosphate |
|
| 0.42 | 2.9 |
|
| ug/l |
Tris(3-chloropropyl) phosphate |
|
|
| 0.031 |
|
| ug/l |
Valproic Acid |
|
|
| 0.03 |
|
| ug/l |
Analytical results from samples taken 4 December 2025
Samples were taken from the following locations:
Sample | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP 50764 13829 |
Ingress (Sample 3) | SP 50791 13850 |
Waste (Sample 4) | SP 50781 14094 |
D/S River Cherwell 1 (Sample 3) | SP 50916 13798 |
D/S River Cherwell 2 (Sample 4) | SP 50943 13253 |
U/S = Upstream of the waste
D/S = Downstream of the waste
Waste = Sample taken from run-off/standing groundwater that has collated around the waste site boundary
NGR = National Grid Reference
Determinand / Compound Name | U/S 1 (Sample 1) | U/S 2 (Sample 2) | Ingress (Sample 3) | Waste (Sample 4) | D/S 1 (Sample 5) | D/S 2 (Sample 6) | Unit |
Ammonia un-ionised as N | <0.00014 | <0.00035 | <0.00035 | 0.00548 | <0.00035 | <0.00037 | mg/l |
Ammoniacal Nitrogen as N | <0.03 | <0.03 | <0.03 | 0.78 | <0.03 | <0.03 | mg/l |
BOD : 5 Day ATU | <3 |
|
|
| <3 |
| mg/l |
Chemical Oxygen Demand :- {COD} | 21 | 17 | 16 | 25 | 18 | 14 | mg/l |
Chloride | 80 | 30 | 30 | 54 | 30 | 30 | mg/l |
Conductivity at 25 C | 806 | 570 | 571 | 870 | 566 | 563 | uS/cm |
Nitrite as N | 0.026 | 0.009 | 0.0083 | 0.29 | 0.0087 | 0.0091 | mg/l |
Nitrogen, Total Oxidised as N | 0.71 | 7.6 | 7.5 | 3.3 | 7.6 | 7.6 | mg/l |
Orthophosphate, reactive as P | 0.094 | 0.11 | 0.11 | <0.01 | 0.11 | 0.11 | mg/l |
Oxygen, Dissolved, % Saturation | 52.5 | 87.6 | 87.6 | 79.1 | 87.4 | 88.3 | % |
pH | 7.48 | 7.88 | 7.88 | 7.71 | 7.89 | 7.91 | PHUNITS |
Salinity : In Situ | 0.4 | 0.28 | 0.28 | 0.43 | 0.28 | 0.27 | ppt |
Solids, Suspended at 105 C | <6 | 30 | 31 | 8.3 | 27 | 28 | mg/l |
Temperature of Water | 7.4 | 7.7 | 7.5 | 6 | 7.4 | 7.4 | CEL |
Visible oil or grease, significant trace: Present/Not found (1/0) | Not found | Not found | Not found | Not found | Not found | Not found | N/A |
Aluminium | 0.091 | 1.3 | 1.4 | 0.081 | 1.1 | 1.1 | mg/l |
Barium | 0.022 | 0.015 | 0.016 | 0.029 | 0.014 | 0.014 | mg/l |
Calcium | 120 | 87 | 87 | 160 | 88 | 85 | mg/l |
Iron | 0.18 | 2.1 | 2.4 | 0.14 | 1.8 | 1.9 | mg/l |
Magnesium | 5.4 | 5.4 | 5.5 | 5.9 | 5.5 | 5.4 | mg/l |
Manganese | 0.11 | 0.043 | 0.038 | 0.1 | 0.032 | 0.035 | mg/l |
Potassium | 3.5 | 4.5 | 4.4 | 1.4 | 4.3 | 4.1 | mg/l |
Sodium | 38 | 19 | 19 | 36 | 19 | 18 | mg/l |
Strontium | 0.42 | 0.2 | 0.23 | 0.51 | 0.23 | 0.23 | mg/l |
Zinc |
| 0.015 | 0.013 | 0.0053 | 0.01 | 0.01 | mg/l |
1,2:5,6-Di-O-isopropylidene-a-d-ribohexafurnos-3-ulose |
|
|
|
| 0.01 |
| ug/l |
1,3-Benzenediol, monobenzoate | 0.01 |
|
|
|
|
| ug/l |
1,3-Dimethyl-5-pylazolyl-2,4-dichlorobenzoate | 0.027 | 0.02 | 0.02 |
| 0.023 |
| ug/l |
1-Butanol, 2,3-dimethyl- | 0.023 |
| 0.12 | 0.032 | 0.087 | 0.142 | ug/l |
1-Dodecanamine, N,N-dimethyl- | 0.024 |
|
|
|
|
| ug/l |
1-Hexene, 4,5-dimethyl- |
| 0.042 |
|
|
|
| ug/l |
1H-Pyrazolo[3,4-d]pyrimidin-4-amine | 0.011 |
|
|
|
|
| ug/l |
1-Pentanone, 1-(4-methylphenyl)- |
|
| 0.012 | 0.022 |
|
| ug/l |
2,4,7,9-Tetramethyl-5-decyne-4,7-diol | 0.011 | 0.065 | 0.099 | 0.097 | 0.082 | 0.081 | ug/l |
2,4-Azetidinedione, 3,3-diethyl-1-methyl- |
|
|
|
| 0.012 |
| ug/l |
2-Butanol, 2,3-dimethyl- |
|
|
| 0.049 |
|
| ug/l |
2-Cyanoethyl acrylate |
|
|
| 0.037 |
|
| ug/l |
2-Ethylhexanoic acid |
|
|
|
| 0.026 |
| ug/l |
2-Propanol, 1-chloro-, phosphate (3:1) | 0.055 |
| 0.067 | 5.6 | 0.084 | 0.055 | ug/l |
2-Propenoic acid, 2-methyl-, (tetrahydro-2-furanyl)methyl ester |
| 0.027 |
|
|
|
| ug/l |
2-Thiobarbituric acid, tris(tert-butyldimethylsilyl) deriv. |
|
| 0.012 |
|
|
| ug/l |
3-Buten-2-one, 3-methyl- |
|
| 0.021 |
|
| 0.081 | ug/l |
3-Hexanol, 5-methyl- | 0.037 |
|
|
| 0.023 |
| ug/l |
3H-pyrazol-3-one, 2,4-dihydro-2-phenyl-5-(phenylamino)- | 0.048 |
|
|
|
|
| ug/l |
3-Penten-2-one |
|
|
|
| 0.017 | 0.049 | ug/l |
acenaphthene |
|
|
|
| 0.002 |
| ug/l |
Anthracene |
|
|
|
| 0.003 |
| ug/l |
Atrazine |
|
|
| 0.138 |
|
| ug/l |
Atrazine desethyl |
|
|
| 0.094 |
|
| ug/l |
Benz[a]anthracene |
|
|
|
| 0.01 |
| ug/l |
Benzaldehyde, 4-benzyloxy-3-methoxy-2-nitro- |
|
|
| 0.02 |
|
| ug/l |
Benzene, 1-ethyl-2,4-dimethyl- | 0.013 |
|
|
|
|
| ug/l |
Benzenesulfonamide, 4-methyl- |
|
|
| 0.372 |
|
| ug/l |
Benzenesulfonamide, N-butyl |
|
|
| 0.612 |
|
| ug/l |
Benzo[a]pyrene |
|
|
|
| 0.006 |
| ug/l |
Bis(1-chloro-2-propyl)(3-chloro-1-propyl)phosphate |
|
|
| 0.978 |
|
| ug/l |
Bis(2-methoxyethoxy)methane |
|
|
| 0.098 |
|
| ug/l |
Bis(3-chloro-1-propyl)(1-chloro-2-propyl)phosphate |
|
|
| 0.064 |
|
| ug/l |
Butane, 2-chloro-2-methyl- |
| 0.097 |
|
|
|
| ug/l |
Butane, 2-methoxy-2-methyl- | 0.014 |
| 0.012 |
| 0.012 |
| ug/l |
Caffeine | 0.006 | 0.048 | 0.065 | 0.614 | 0.051 | 0.041 | ug/l |
Chrysene |
|
| 0.007 |
| 0.011 |
| ug/l |
Coumarin |
|
|
| 0.024 |
|
| ug/l |
Cyclopenta(cd)pyrene, 3,4-dihydro- |
|
|
|
| 0.01 |
| ug/l |
Diphenyl sulfone |
| 0.005 |
| 0.195 | 0.006 |
| ug/l |
Ethanol, 2-(trimethylsilyl)- | 0.011 |
|
|
|
|
| ug/l |
Ethanone, 1-[4-(1-hydroxy-1-methylethyl)phenyl]- |
|
|
| 0.032 |
|
| ug/l |
Ethanone, 2,2-dimethoxy-1,2-diphenyl- |
|
|
| 0.089 |
|
| ug/l |
Flufenacet |
|
| 0.015 |
| 0.014 |
| ug/l |
Fluoranthene | 0.004 | 0.006 | 0.017 | 0.003 | 0.027 | 0.025 | ug/l |
Furan, 2-methoxy- |
|
| 0.012 |
|
|
| ug/l |
Hexadecanoic acid, methyl ester | 0.018 |
|
|
|
|
| ug/l |
Hexane, 3,3-dimethyl- |
| 0.019 |
|
|
|
| ug/l |
Isonicotinic acid, 2-phenylethyl ester |
| 0.028 |
|
|
|
| ug/l |
Methyl Isobutyl Ketone | 0.012 |
|
|
|
|
| ug/l |
Methyl stearate | 0.01 |
|
|
|
|
| ug/l |
N,N,N',N'-Tetraacetylethylenediamine |
|
|
|
| 0.043 |
| ug/l |
N,N-Diethyl-m-toluamide |
|
| 0.012 |
|
|
| ug/l |
n-Decanoic acid |
| 0.017 |
|
|
|
| ug/l |
n-Hexadecanoic acid |
| 0.031 |
|
|
|
| ug/l |
Nitrous acid, cyclohexyl ester |
|
|
|
| 0.01 |
| ug/l |
Nonanal | 0.015 |
| 0.016 |
|
|
| ug/l |
Octadecanoic acid | 0.219 | 0.023 | 0.176 | 0.089 | 0.112 | 0.031 | ug/l |
Pentanal, 2-methyl- | 0.028 |
|
|
|
|
| ug/l |
Pentanoic acid, 5-hydroxy-, 2,4-di-t-butylphenyl esters | 0.024 |
|
|
|
|
| ug/l |
Phenol, 2,4-bis(1,1-dimethylethyl)-, phosphite (3:1) |
| 0.053 |
|
| 0.513 |
| ug/l |
Phthalimide | 0.012 |
|
|
|
|
| ug/l |
Propane, 1,1-dimethoxy- |
|
| 0.012 |
|
|
| ug/l |
Propanoic acid | 0.013 |
|
|
|
|
| ug/l |
Propyzamide |
| 0.026 | 0.042 |
| 0.043 | 0.037 | ug/l |
Pyrene |
| 0.004 | 0.013 |
| 0.017 | 0.017 | ug/l |
Pyridine, 2,3,6-trimethyl- | 0.01 |
|
|
|
|
| ug/l |
Sulfur (S8) |
|
| 0.006 |
| 0.006 |
| ug/l |
trans-3-Penten-2-ol |
|
| 0.11 |
| 0.079 | 0.118 | ug/l |
Tri-(2-chloroethyl) phosphate |
|
|
| 1.1 |
|
| ug/l |
Tri-allate |
| 0.011 | 0.012 |
| 0.014 | 0.014 | ug/l |
Tricyclo[2.2.1.0(2,6)]heptane, 1,3,3-trimethyl |
| 0.101 |
|
|
|
| ug/l |
Triethyl Citrate |
|
| 0.285 |
| 0.241 |
| ug/l |
Triethyl phosphate |
|
|
| 0.041 |
|
| ug/l |
Triphenylphosphine oxide |
|
|
| 0.077 |
|
| ug/l |
Tris-(1,3-dichloroisopropyl) phosphate |
|
|
| 0.149 |
|
| ug/l |
*This data includes that obtained by using the GC-MS analytical technique: further guidance on this is available here: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen
Disclaimer for GCMS Results: All results are an approximate concentration. Where accreditation is claimed this is only for the identification of the substance and not the quantified amount.
The compounds identified in the GCMS results fit into one of four criteria, which can be pulled from the original dataset on MIDAS if required:
Use limitation statement
There are no public access constraints to this data. Use of this data is subject to the licence identified.
Licence
Attribution statement
© Environment Agency copyright and/or database right 2025. All rights reserved.
Analytical results from samples taken 28 November 2025
Samples were taken from the following locations:
Sample | Location (NGR) |
U/S Tributary 1 (Sample 1) | SP 50747 14126 |
U/S Tributary 2 (Sample 2) | SP 50764 13829 |
D/S River Cherwell 1 (Sample 3) | SP 50916 13798 |
D/S River Cherwell 2 (Sample 4) | SP 50943 13253 |
U/S = Upstream of the waste
D/S = Downstream of the waste
NGR = National Grid Reference
Determinand / Compound Name | U/S 1 (Sample 1) | U/S 2 (Sample 2) | D/S 1 (Sample 3) | D/S 2 (Sample 4) | Unit |
Ammonia un-ionised as N | 0.00015 | <0.00038 | <0.0004 | <0.0004 | mg/l |
Ammoniacal Nitrogen as N | 0.032 | <0.03 | <0.03 | <0.03 | mg/l |
BOD : 5 Day ATU | <3 | <3 | <3 | <3 | mg/l |
Chemical Oxygen Demand :- {COD} | 32 | 11 | 10 | 10 | mg/l |
Chloride | 47 | 35 | 35 | 34 | mg/l |
Conductivity at 25 C | 647 | 659 | 654 | 654 | uS/cm |
Nitrite as N | <0.004 | 0.0087 | 0.0079 | 0.0077 | mg/l |
Nitrogen, Total Oxidised as N | 0.22 | 6.9 | 7 | 6.9 | mg/l |
Orthophosphate, reactive as P | 0.081 | 0.11 | 0.1 | 0.1 | mg/l |
Oxygen, Dissolved, % Saturation | 53.1 | 90 | 90.2 | 89.2 | % |
pH | 7.47 | 7.92 | 7.92 | 7.95 | PHUNITS |
Salinity : In Situ | 0.32 | 0.32 | 0.32 | 0.32 | ppt |
Solids, Suspended at 105 C | <6 | 12 | 11 | 12 | mg/l |
Temperature of Water | 8.4 | 7.5 | 8.1 | 7.4 | CEL |
Visible oil or grease, significant trace: Present/Not found (1/0) | Not found | Not found | Not found | Not found | N/A |
Aluminium | 0.031 | 0.22 | 0.31 | 0.27 | mg/l |
Barium | 0.016 | 0.012 | 0.013 | 0.013 | mg/l |
Calcium | 100 | 99 | 100 | 100 | mg/l |
Iron | 0.086 | 0.48 | 0.67 | 0.59 | mg/l |
Magnesium | 4.6 | 5.8 | 5.9 | 5.9 | mg/l |
Manganese | 0.08 | 0.015 | 0.022 | 0.019 | mg/l |
Potassium | 2.8 | 4.3 | 4.4 | 4.4 | mg/l |
Sodium | 22 | 22 | 22 | 22 | mg/l |
Strontium | 0.34 | 0.25 | 0.26 | 0.26 | mg/l |
Zinc |
|
| 0.005 | 0.0051 | mg/l |
1(3H)-Isobenzofuranone, 3,3-dimethyl- | 0.011 | 0.015 |
| 0.011 | ug/l |
1,2-Benzenedicarboxylic acid | 0.014 |
|
|
| ug/l |
1,2-Bis(3,5,5-trimethyl-2-cyclohexenylidene)hydrazine |
| 0.012 |
| 0.011 | ug/l |
1,3-Dimethyl-5-pylazolyl-2,4-dichlorobenzoate | 0.016 | 0.018 | 0.016 | 0.028 | ug/l |
1-Decanamine, N-decyl-N-methyl- | 0.018 |
|
|
| ug/l |
1-Dodecanamine, N,N-dimethyl- | 0.705 | 0.024 |
|
| ug/l |
1-Hexene, 4,5-dimethyl- |
| 0.031 |
|
| ug/l |
1-Pentanol, 4-methyl-2-propyl- |
|
| 0.034 | 0.036 | ug/l |
1-Pentene, 2,4,4-trimethyl- | 0.011 |
|
|
| ug/l |
1-Tetradecanamine, N,N-dimethyl- | 0.142 |
|
|
| ug/l |
2,2,4-Trimethyl-1,3-pentanediol diisobutyrate |
|
|
| 0.013 | ug/l |
2,2-Dimethylpropionic acid, 4-methylpentyl ester |
| 0.016 |
|
| ug/l |
2,3,4,5-Tetrafluorobenzyl alcohol, 2-methylpropyl ether |
|
|
| 0.009 | ug/l |
2,3-Dihydro-2-methyl-5-ethylfuran | 0.02 |
|
|
| ug/l |
2,4,7,9-Tetramethyl-5-decyne-4,7-diol |
| 0.067 | 0.082 | 0.077 | ug/l |
2,4-Dichlorobenzamide |
|
|
| 0.044 | ug/l |
2-Chloroethyl benzoate |
|
|
| 0.021 | ug/l |
2-Ethyl-1-butanol, trifluoroacetate |
|
| 0.012 | 0.013 | ug/l |
2-Fluoro-6-trifluoromethylbenzoic acid, 4-nitrophenyl ester |
|
|
| 0.324 | ug/l |
2-Propanol, 1-chloro-, phosphate (3:1) | 0.043 | 0.06 | 0.083 | 0.087 | ug/l |
3,7-Dimethyl-1-phenylsulfonyl-2,6-octadiene |
|
|
| 0.011 | ug/l |
3-Buten-2-one, 3-methyl- |
|
|
| 0.009 | ug/l |
3-Penten-2-one |
| 0.009 |
|
| ug/l |
4-fluorophenyl 4-(4-pentylcyclohexyl)benzoate |
| 0.009 |
|
| ug/l |
4-Methyl-3-heptanol, trifluoroacetate | 0.03 |
|
|
| ug/l |
5-(4-Hexyloxybenzoyloxy)-2-(4-nitrophenyl)pyrimidine |
| 0.022 |
|
| ug/l |
Benzoic acid, (4-benzoyloxy-2-chlorophenyl) ester |
|
|
| 0.01 | ug/l |
Butane, 2-chloro-2-methyl- |
| 0.12 | 0.109 | 0.095 | ug/l |
Butane, 2-methoxy-2-methyl- | 0.011 | 0.011 | 0.014 | 0.011 | ug/l |
Butanoic acid, 2-pentenyl ester, (Z)- |
|
| 0.009 |
| ug/l |
Caffeine | 0.009 | 0.075 | 0.099 | 0.075 | ug/l |
Carbamazepine |
| 0.022 | 0.029 | 0.028 | ug/l |
Coumarin |
|
|
| 0.003 | ug/l |
Crotamiton |
| 0.023 |
|
| ug/l |
Cyclohexane, (1,1-dimethylethyl)- | 0.012 |
|
|
| ug/l |
Cyclopenta[g]-2-benzopyran, 1,3,4,6,7,8-hexahydro-4,6,6,7,8,8-hexamethyl- |
|
| 0.015 | 0.009 | ug/l |
Diethylcyanamide | 0.011 |
|
|
| ug/l |
Diphenyl sulfone |
| 0.007 | 0.008 | 0.007 | ug/l |
Dodecylmethylbenzylamine | 0.079 |
|
|
| ug/l |
Ethanedioic acid, dibutyl ester |
|
| 0.01 |
| ug/l |
Ethanol, 2-(trimethylsilyl)- |
|
| 0.011 |
| ug/l |
Ethanone, 1,1'-(1,4-phenylene)bis- |
|
| 0.013 |
| ug/l |
Ethanone, 1-[4-(1-hydroxy-1-methylethyl)phenyl]- |
| 0.012 | 0.015 |
| ug/l |
Flufenacet |
| 0.018 | 0.023 |
| ug/l |
Fluoranthene | 0.004 | 0.003 | 0.003 | 0.003 | ug/l |
Furan, 2-methoxy- |
|
|
| 0.008 | ug/l |
Furan, 2-methoxy-ug/l |
| 0.01 |
|
| ug/l |
Isopropyl palmitate |
|
|
| 0.813 | ug/l |
Metacetamol |
| 0.01 | 0.012 | 0.011 | ug/l |
Methyl stearate |
|
| 0.015 | 0.013 | ug/l |
Methyl stearate 0.018 Nonanal | 0.014 |
|
|
| ug/l |
N,N,N',N'-Tetraacetylethylenediamine |
| 0.056 | 0.066 | 0.047 | ug/l |
N,N-Diethyl-m-toluamide |
| 0.015 | 0.017 | 0.016 | ug/l |
Neopentane |
|
|
| 0.009 | ug/l |
n-Hexadecanoic acid | 0.354 |
|
|
| ug/l |
Nonanal |
| 0.014 | 0.018 | 0.015 | ug/l |
Octadecanoic acid | 0.365 | 0.242 | 0.262 | 0.265 | ug/l |
Pentanoic acid, 5-hydroxy-, 2,4-di-t-butylphenyl esters | 0.025 | 0.024 | 0.031 | 0.019 | ug/l |
Pentanoic acid, 5-hydroxy-, p-t-butylphenyl ester |
|
|
| 0.013 | ug/l |
Phenol, 2,4-bis(1,1-dimethylethyl)-, phosphite (3:1) | 0.262 | 0.725 | 1.3 | 0.837 | ug/l |
Propanoic acid | 0.014 |
|
|
| ug/l |
Propyzamide |
| 0.041 | 0.046 | 0.046 | ug/l |
Pyrene |
|
| 0.003 | 0.002 | ug/l |
Pyridine, 2,3,6-trimethyl- |
|
| 0.011 |
| ug/l |
Succinic acid, di(4-trifluoromethoxybenzyl) ester |
|
| 0.48 |
| ug/l |
Sulfurous acid, 2-ethylhexyl hexyl ester |
| 0.046 |
|
| ug/l |
TATP |
|
| 0.012 |
| ug/l |
Tetradecanoic acid, 10,13-dimethyl-, methyl ester | 0.016 |
|
| 0.015 | ug/l |
Thiophene, 2,5-di(benzoylthio)- |
| 0.009 |
|
| ug/l |
Tri-allate |
| 0.008 | 0.006 | 0.012 | ug/l |
Triethyl Citrate |
| 0.208 | 0.325 | 0.366 | ug/l |
Trifluoroacetic acid, 2-tetrahydrofurylmethyl ester | 0.012 | 0.018 |
| 0.008 | ug/l |
*This data includes that obtained by using the GC-MS analytical technique: further guidance on this is available here: Water quality monitoring data GC-MS and LC-MS semi-quantitative screen
Disclaimer for GCMS Results: All results are an approximate concentration. Where accreditation is claimed this is only for the identification of the substance and not the quantified amount.
The compounds identified in the GCMS results fit into one of four criteria, which can be pulled from the original dataset on MIDAS if required:
Use limitation statement
There are no public access constraints to this data. Use of this data is subject to the licence identified.
Licence
Attribution statement
© Environment Agency copyright and/or database right 2025. All rights reserved.