ENVIRONMENTAL PROTECTION River Teign Catchment River Water

ENVIRONMENTAL PROTECTION NRA

National Rivers Authority

South Wast Region

River Teign Catchment

River Water Quality

Classification 1990

NOVEMBER 1991 WQP/91/006 B L MILFORD

G O R D O N H BIELBY BSc Regional General Manager

C V M Davies Environmental Protection Manager ACKNOWLEDGEMENTS

The Water Quality Planner acknowledges the substantial contributions made by the following staff: R. Broome - Co-ordinator and Editor A. Burrows - Production of Maps and editorial support P. Grigorey - Production of Maps and editorial support B. Steele - Production of Forepage C. McCarthy - Administration and report compilation

Special thanks are extended to A. Burghes of Moonsoft, Exeter for computer support and the production of statistical schedules.

The following NBA sections also made valuable contributions: Pollution Control Field Control and Wardens Water Resources

Thanks also to R. Hamilton and J. Murray-Bligh for their contributions.

Suggestions for improvements that could be incorporated in the production of the next Classification report would be welcomed.

Further enquiries regarding the content of these reports should be addressed to: Freshwater Scientist, National Rivers Authority, Manley House, Kestrel Way, EXETER, Devon EX2 7LQ

ENVIRONMENT AGENCY

130037 RIVE21 WA3ER QUALITY IN THE RIVER TCIGN CATCHMENT LIST OF CONTOiTS Page No. 1 Introduction 1 2 River Teign Catchment 1 3 National Water Council's River Classification System 3 4 1990 River Water Quality Survey 4 5 1990 River Water Quality Classification 4 6 Non-compliance with Quality Objectives 5 7 Causes of Non-compliance 5 8 Glossary of Terms 6 9 References 6 10 Appendices: 10.1 River Quality Objectives including Monitoring points 10.2 Basic Determinand Analytical Suite 10.3 National Water Council (NWC) River Classification System 10.4 NWC Criteria for Nan-Metallic Determinands - Regional Variation 10.4.1 NWC Criteria for Metallic Determinands - Regional Variation 10.5 1990 River Water Quality Classification - tabular format 10.6 1990 River Water Quality Classification - map format 10.7 Calculated Determinand Statistics used for Quality Assessment 10.8 Compliant/Non-Conpliant River Reaches 10.9 Number of Samples Results exceeding quality standards 10.10 Percentage Exceedance of Determinand Statistics from Quality Standard 10.11 Identification of Possible Causes of Non-Compliance with River Quality Objectives National Rivers Authority South West Region

NRA Wessex Region NRA

National Rtvmrt Authority South Mfeit Rtgfon ie Tin Catchment TeignRiver

River Teign Catchment 1. INTRODUCTION Monitoring to assess the quality of river waters is undertaken in thirty- two catchments within the region. As part of this monitoring programme samples are collected routinely from selected monitoring points at a pre determined frequency per year, usually twelve spaced at monthly intervals. Each monitoring point provides data for the water quality of a river reach (in kilometres) upstream of the monitoring point. River lengths have been re-measured and variations exist over those recorded previously. Each water sample collected from each monitoring point is analysed for a range of chemical and physical constituents or properties known as determinands. Ihe analytical results for each sample are entered into a computer database called the Water Quality Archive. Selected data are accessed from the Archive so that the quality of each river reach can be determined based on a River Classification System developed by the National Water Council (NWC), (9.1). This report presents the river water quality classification for 1990 for monitored river reaches in the River Teign catchment.

2. RIVER TEIQ* CATCHMENT The River Teign flows over a distance of 50.8 km from its source to the tidal limit, (Appendix 10.1). Water quality was monitored at eight locations on the main river? seven sites were sampled at approximately monthly intervals and the site at Preston, which is a National Water Quality monitoring site, was sampled fortnightly. Blatchford Stream flows over a distance of 4.3 km from its source to the tidal limit, (Appendix 10.1) and was monitored at two locations at approximately monthly intervals. The River Lemon flows over a distance of 15.3 km from its source to the tidal limit, (Appendix 10.1) and was monitored at three locations at approximately monthly intervals. The Aller Brook flows over a distance of 7.9 km from its source to the tidal limit, (Appendix 10.1) and was monitored at four locations at approximatley monthly intervals. Throughout the Teign catchment twelve secondary tributaries and four tertiary tributaries of the River Teign were monitored. In addition Trenchford Reservoir was monitored at one location at approximately monthly intervals.

1 2.1 SECONDARY TRIBUTARIES The South Teign River, including Fernworthy Reservoir, flows over a distance of 6.3 km from its source to the confluence with the River Teign, (Appendix 10.1). Both the South Teign River and Fernworthy Reservoir were monitored at one location each at approximately monthly intervals. Fingle Brook (7 km), Sowton Brook (6.4 km), Bramble Brook (6.5 km), Reedy Brook (5.2 km), Scotley Brook (5.3 km), Rate Brook (3.8 km) and Liverton Brook (9.1 km) were all monitored at approximately monthly intervals at one location between their source and confluence with the River Teign, (Appendix 10.1). Rookery Brook (4.9 km) and Ugbrooke Stream (8.4 km) were both monitored at approximately monthly intervals at three locations between their source and confluence with the River Teign, (Appendix 10 .1 ). Beadon Brook flows over a distance of 8.3 km from its source to the confluence with the River Teign, (Appendix 10.1) and was monitored at three locations at approximately monthly intervals. The River Bovey flows over a distance of 26.7 km from its source to the confluence with the River Teign, (Appendix 10.1) and was monitored at four locations at approximately monthly intervals.

2.2 TERTIARY TRIBUTARIES Blackaton Brook flows over a distance of 9 km from its source to the confluence with the North Teign River, (Appendix 10.1) and was monitored at one site at approximately monthly intervals. Becka Brook flows over a distance of 6.3 km from its source to the confluence with the River Bovey, (Appendix 10.1) and was sampled at one location on twenty occasions during 1990 because of no recent water quality data. Wray Brook flows over a distance of 10.6 km from its source to the confluence with the River Bovey, (Appendix 10.1) and was sampled at two locations at approximately monthly intervals. Sandygate Stream flows over a distance of 7.6 km from its source to the confluence with the Ugbrooke Stream, (Appendix 10.1) and was monitored at three locations at approximately monthly intervals. Kennick and Tottiford Reservoirs were both monitored at one location at approximately monthly intervals.

2 I

Each sample was analysed for a minimum number of determinands (Appendix 10.2) plus additional determinands based on local knowledge of the catchment. In addition, at selected sites, certain metal analyses were carried out. The analytical results from all of these samples have been entered into the Water Quality Archive and can be accessed through the Water Act Register, (9.2).

3. NATIONAL WATER COUNCIL'S RTVER CLASSIFICATION SYSTBl 3.1 River Quality Objectives In 1978 river quality objectives (RQOs) were assigned to all river lengths that were part of the routine monitoring network and to those additional watercourses, which were not part of the routine network, but which received discharges of effluents. For the majority of watercourses long term objectives were identified based on existing and assumed adequate quality for the long term protection of the watercourse. In a few instances short term objectives were identified but no timetable for the achievement of the associated long term objective was set. The RQOs currently in use in the River Teign catchment are identified in Appendix 10.1. 3.2 River Quality Classification River water quality is classified using the National Water Council's (NWC) River Classification System (see Appendix 10.3), which identifies river water quality as being one of five quality classes as shown in Table 1 below: Table 1 - National Water Council - River Classification System Class Description 1A Good quality IB Lesser good quality 2 Fair quality 3 Poor quality 4 Bad quality Using the NWC system, the classification of river water quality is based on the values of certain determinands as arithmetic means or as 95 percentiles (5 percentiles are used for pH and dissolved oxygen) as indicated in Appendices 10.4.1 and 10.4.2.

3 The quality classification system incorporates some of the European Inland Fisheries Advisory Commission (EIFAC) criteria (Appendix 10.3) recommended for use by the NWC system.

4. 1990 RIVER WATER QUALITY SURVEY The 1990 regional classification of river water quality also includes the requirements of the Department of the Environment quinquennial national river quality survey. The objectives for the Department of the Environment 1990 River Quality Survey are given below: 1) To carry out a National Classification Survey based on procedures used in the 1985 National Classification Survey, including all regional differences. 2) To classify all rivers and canals included in the 1985 National Classification Survey. 3) To compare the 1990 Classification with those obtained in 1985. In addition, those watercourses, which were not part of the 1985 Survey and have been monitored since that date, are included in the 1990 regional classification of river water quality.

5. 1990 RIVER WATER QUALITY CLASSIFICATION Analytical data collected from monitoring during 1988, 1989 and 1990 were processed through a computerised river water quality classification programme. This resulted in a quality class being assigned to each monitored river reach as indicated in Appendix 10.5. The quality class for 1990 can be compared against the appropriate River Quality Objective and previous annual quality classes (1985-1989) also based on three years combined data, for each river reach in Appendix 10.5. The river water classification system used to classify each river length is identical to the system used in 1985 for the Department of the Environment's 1985 River Quality Survey. The determinand classification criteria used to determine the annual quality classes in 1985, subsequent years and for 1990 are indicated in Appendices 10.4 and 10.4.1. Improvements to this classification system could have been made, particularly in the use of a different suspended solids standard for Class 2 waters. As the National Rivers Authority will be proposing new classification systems to the Secretary of State in the near future, it was decided to classify river lengths in 1990 with the classification used for the 1985-1989 classification period.

4 The adoption of the revised criteria for suspended solids in Class 2 waters would have affected the classification of Aller Brook at Aller Orchard and Penninn, Newton Abbott. The river quality classes for 1990 of monitored river reaches in the catchment are shown in map form in Appendix 10.6. The calculated determinand statistics for pH, temperature, dissolved oxygen, biochemical oxygen demand (BOD), total ammonia, un-ionised ammonia, suspended solids, copper and zinc from which the quality class was determined for each river reach, are indicated in Appendix 10.7.

6. NON-COMPLIANCE WITH QUALITY OBJECTIVES Those monitored river reaches within the catchment, which do not comply with their assigned (RQO), are shown in map form in Appendix 10.8. Appendix 10.9 indicates the number of samples analysed for each determinand over the period 1988 to 1990 and the number of sample results per determinand, which exceed the determinand quality standard. For those non-compliant river reaches in the catchment, the extent of exceedance of the calculated determinand statistic with relevant quality standard (represented as a percentage), is indicated in Appendix 10.10.

7. CAUSES OF NON—COMPLIANCE For those river reaches, which did not comply with their assigned RQOs, the cause of non-compliance (where possible to identify) is indicated in Appendix 10.11.

5 8. GLOSSARY OF TERNS

RIVER REACH A segment of water, upstream from sampling point to the next sampling point. RIVER LENGTH River distance in kilometres. RIVER QUALITY OBJECTIVE That NWC class,which protects the most sensitive use of the water. 95 percentiles Maximum limits, which must be met for at least 95% of the time. 5 percentiles Minimum limits, which must be met for at least 95% of the time. BIOLOGICAL OXYGEN DEMAND A standard test measuring the microbial uptake of (5 day carbonaceous ATU) oxygen - an estimate of organic pollution. pH A scale of acid to alkali. UN—IONISED AMMONIA Fraction of ammonia poisonous to fish, NHJ. SUSPENDED SOLIDS Solids removed by filtration or centrifuge under specific conditions. USER REFERENCE NUMBER Reference number allocated to a sampling point. INFERRED STRETCH Segment of water, which is not monitored and whose water quality classification is assigned from the monitored reach upstream.

9. REFERENCES

Reference

9.1 National Water Council (1977). River Water Quality: The Next Stage. Review of Discharge Consent Conditions. London.

9.2 Water Act 1989 Section 117

9.3 Alabaster J. S. and Lloyd R. Water Quality Criteria for Freshwater Fish, 2nd edition, 1982. Butterworths.

6 Teign Catchment River Quality Objectives PEDX 10.1 APPENDIX

APPENDIX 10.2

BASIC DETERMINAND ANALYTICAL SUITE FOR ALL CLASSIFIH) RIVER SITES

pH as pH Units Conductivity at 20 C as uS/cm Water temperature (Cel) Oxygen dissolved % saturation Oxygen dissolved as mg/1 O Biochemical oxygen demand (5 day total ATO) as mg/1 0 Total organic carbon as mg/1 C Nitrogen ammoniacal as mg/1 N Ammonia un-ionised as mg/1 N Nitrate as mg/1 N Nitrite as mg/1 N Suspended solids at 105 C as mg/1 Total hardness as mg/1 CaC03 Chloride as mg/1 Cl Orthophosphate (total) as mg/1 P Silicate reactive dissolved as mg/1 Si02 Sulphate (dissolved) as mg/1 S04 Sodium (total) as mg/1 Na Potassium (total) as mg/1 K Magnesium (total) as mg/1 Mg Calcium (total) as mg/1 Ca Alkalinity as pH 4.5 as mg/1 CaC03 APPENDIX 10.3 NWC RIVER QUALITY CLASSIFICATION SYSTEM

River Class Quality criteria Remarks Current potential uses

Class limiting criteria (95 percentile)

1A Good (i) Dissolved oxygen saturation (i) Average 800 probably not (i) later of high quality Quality greater than 80* greater than 1.5 mg/1 suitable for potable supply (ii) Biochemical oxygen demand (ii) Visible evidence of pollution abstractions and for all not greater than 3 fig/1 should be absent abstractions (iii) Ammonia not greater than (ii) Game or other high class 0.4 mg/1 fisheries (iv) Where the water is abstracted (iii) High amenity value for drinking water, it coitplies with requirements for A2* water (v) Non-toxic to fish in EIFAC terms (or best estimates if EIFAC figures not available)

18 Good (i) DO greater than 60X saturation i) Average BOD probably not Mater of less high quality Quality (ii) BOD not greater thar 5 mg/1 greater than 2 mg/1 than Class U but usable for (iii) Ammonia not greater than ii) Average ammonia probably not substantially the sane 0.9 Big/1 greater than 0.5 mg/1 purposes (iv) Where water is abstracted for iii) Visible evidence of pollution drinking water, it complies with should be absent the requirements for A2* water iv) Maters of high quality which (v) Non-toxic to fish in EIFAC terns cannot be placed in Class 1A (or best estimates if EIFAC because of the high proportion figures not available) of high quality effluent present or because of the effect of physical factors such as canalisation, low gradient or eutrophication |v) Class 1A and Class 18 together are essentially the Class 1 of the River Pollution Survey (RPS)

2 Fair (i) DO greater than 40X saturation i) Average BOD probably not i) Waters suitable for potable Quality (ii) BOD not greater than 9 mg/1 greater than 5 mg/1 supply after advanced (iii) Where water is abstracted for ii) Similar to Class 2 of RPS treatment drinking water it complies with iii) Water not showing physical ii) Supporting reasonably good the requirements for A3* water signs of pollution other than coarse fisheries (iv) Non-toxic to fish in EIFAC terms humic colouration and a little iii} Moderate amenity value (or best estimates if EIFAC foaming below weirs figures not available) oor (i) DO greater than 10J saturation Sirilar to Class 3 of RPS Waters which are polluted to slity (ii) Not likely to be anaerobic an extent that fish are absent (iii) BOD not greater than 17 ng/1. only sporadically present. This nay not apply if there is a May be used for low grade high degree of re-aeration industrial abstraction purposes. Considerable potential for further use if cleaned up iad Maters which are inferior to Similar to Class 4 of RPS Waters which are grossly ility Class 3 in terns of dissolved polluted and are likely to oxygen and likely to be cause nuisance anaerobic at tines

DO greater than 10X saturation Insignificant watercourses and ditches not usable, where the objective is sinply to prevent nuisance developing

;es (a) Under extreme weather conditions (eg flood, drought, freeze-up), or when dominated by plant growth, or by aquatic plant decay, rivers usually in Class 1, 2, and 3 nay have BODs and dissolved oxygen levels, or annonia content outside the stated levels for those Classes. When this occurs the cause should be stated along with analytical results. (b) The BOD determinations refer to 5 day carbonaceous BOD (ATU). Ammonia figures are expressed as NIU . ** (c) In most instances the chemical classification given above will be suitable. However, the basis of the classification is restricted to a finite nunber of chemical deteroinands and there nay be a few cases where the presence of a chenical substance other than those used in the classification markedly reduces the quality of the water. In such cases, the quality classification of the water should be down-graded on the basis of biota actually present, and the reasons stated. (d) EIFAC (European Inland Fisheries Advisory Commission) limits should be expressed as 95 percentile limits.

EC category A2 and A3 requirements are those specified in the EEC Council directive of 16 June 1975 concerning the Quality of Surface fater intended for Abstraction of Drinking Water in the Member State.

Annonia Conversion Factors

(mg NH

Class 1A 0.4 ng NH

NWC RTVER CLASSIFICATION SYSTHl CRITERIA USED BY NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION FOR NGN- METALLIC DETERMINANDS

River Quality Criteria Class 1A Dissolved oxygen % saturation greater than 80% BOD (ATU) not greater than 3 mg/1 0 Total ammonia not greater than 0.31 mg/1 N Non-ionised ammonia not greater than 0.021 mg/1 N Temperature not greater than 21.5 C pH greater than 5.0 and less than 9.0 Suspended solids not greater than 25 mg/1 IB Dissolved oxygen % saturation greater than 60% BOD (ATU) not greater than 5 mg/1 O Total ammonia not greater than 0.70 mg/1 N Non-ionised ammonia not greater than 0.021 mg/1 N Temperature not greater than 21.5 C pH greater than 5.0 and less than 9.0 Suspended solids not greater than 25 mg/1 2 Dissolved oxygen & saturation greater than 40% BOD (ATU) not greater than 9 mg/1 0 Total ammonia not greater than 1.56 mg/1 N Non-ionised ammonia not greater than 0.021 mg/1 N Temperature not greater than 28 C pH greater than 5.0 and less than 9.0 Suspended solids not greater than 25 mg/1 3 Dissolved oxygen % saturation greater than 10% BOD (ATU) not greater than 17 mg/1 0 4 Dissolved oxygen % saturation not greater than 10% BOD (ATU) greater than 17 mg/1 0 STATISTICS USED BY NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION Determinand Statistic Dissolved oxygen 5 percentile BOD (ATU) 95 percentile Total ammonia 95 percentile Non-ionised ammonia 95 percentile Temperature 95 percentile pH 5 percentile 95 percentile Suspended solids arithmetic mean APPENDIX 10.4.1

NWC RIVER CLASSIFICATION SYSTOl CRITERIA USE) BY NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION TOR METALLIC DETERMINANDS

SOLUBLE COPPER

Total Hardness (mean) Statistic Soluble Copper* mg/1 CaC03 ug/1 Cu Class 1 Class 2 0-10 95 percentile < - 5 > 5 10 - 50 95 percentile < - 22 > 22 50 - 100 95 percentile < o 40 > 40 100 - 300 95 percentile < - 112 > 112

* Total copper is used for classification until sufficient data on soluble copper can be obtained.

T O T A L Z I N C

Total Hardness (mean) Statistic Total Zinc mg/1 CaC03 ug/1 Zn Class 1 Class 2 Class 3 0-10 95 percentile < = 30 < = 300 > 300 10 - 50 95 percentile < - 200 < « 700 > 700 50 - 100 95 percentile < = 300 < = 1000 > 1000 100 - 300 95 percentile < = 500 < = 2000 > 2000 NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION 1990 RIVER WATER QUALITY CLASSIFICATION CATCHMENT : TEIGN (06)

|1990 Map River (Reach upstream of | User National ( {Position 1 (Reference Grid | | Number 1 | Number Reference ( 1 1 1 1 1 1 1 1 SOUTH TEIGN RIVER |INFLOW, FERNWORTHY RES. (UOTCN. REACH) 1 | 1 SOUTH TEIGN RIVER |FERNWORTHY RESERVOIR | R06C051 SX 6670 8415| 1 2 SOUTH TEIGN RIVER |LEIGH BRIDGE | R06C001 sx 6831 8763| 1 1 1 3 NORTH TEIGN RIVER |GIDLEIGH PARK HOTEL | R06C002 sx 6775 8791| | 4 TEIGN |RUSHFORD | R06C003 sx 7048 8823| | 5 TEIGN |CLIFFORD BRIDGE | R06C004 sx 7809 8979| 1 6 TEIGN |BRIDFORD BRIDGE | R06C005 sx 8343 8723| | 7 TEIGN fSPARA BRIDGE | R06C037 sx 8435 8408| 1 8 TEIGN (CROCQMBE BRIDGE | R06C006 sx 8485 8115| 1 9 TEIGN | CHUDLEIGH BRIDGE j R06C007 sx 8575 7847| 1 io TEIGN |NEW BRIDGE | R06C008 sx 8490 7652[ 1 U TEIGN |PRESTON | R06B001 sx 8550 7452| TEIGN jNORMAL TIDAL LIMIT (INFERRED STRETCH) 1 1 1 1 12 ALLER BROOK |EDGINSWELL PUMPING STATION | R06A001 sx 8932 6625| | MANOR DRIVE KINGSKERSWELL | R06A002 sx 8801 6735| 1 13 A U £ R ( 14 ALLER BROOK |ALLER ORCHARD | R06A003 SX 8755 69001 1 15 ALLER BROOK |PENNINN NEWTON ABBOT | R06A004 sx 8705 70601 ALLER BROOK |NORMAL TIDAL LIMIT (INFERRED STRETCH) J 1 1 16 LEMON |BAGATOR MILL | R06B003 sx 7690 7556| 1 17 LQCN | BELOW CONFLUENCE WITH RIVER SIG ( R06B004 sx 7790 7355| 1 18 LEMON |BRADLEY PLAYING FIELDS NEWTON ABBOT | R06B005 sx 8532 7099| LEMON |NORMAL TIDAL LIMIT (INFERRED STRETCH) 1 1 1 1 19 BLATCHFORD STREAM |PERRY FARM | R06B006 sx 8360 7287| 1 20 BLATCHFORD STREAM |BLATCHFORD | R06B007 sx 8550 7301| BLATCHFORD STREAM |NORMAL TIDAL LIMIT (INFERRED STRETCH) \ 1 1 1 21 UGBROOKE STREAM |GAPPAH | R06B011 sx 8661 7729| | 22 UGBROOKE STREAM | HIGHER SANDYGATE | R06B012 sx 86 72 7513| 1 23 UGBROOKE STREAM (PRIOR TO RIVER TEIGN | R06B013 sx 8575 7375 j UGBROOKE STREAM (TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 1 1 24 SANDY GATE STREAM | PRIOR TO COLLEY BROOK | R06B008 sx 8917 7665| 1 25 SANDYGATE STREAM |COOMBE HOUBUDGE | R06B009 sx 8732 7580| 1 26 SANDYGATE STREAM (NEW CROSS KINGSTEIGNTON | R06B010 sx 8679 7483| SANDYGATE STREAM |UGBROOKE CONFLUENCE (INFERRED STRETCH) 1 ( 1 1 27 LIVERTON BROOK (VENTIFORD BRIDGE | R06B0S0 sx 8475 7475| LIVERTON BROOK (TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 1 1 28 BOVEY (BLACKALLER NORTH BOVEY | R06D001 sx 7376 8375| 1 29 BOVEY IDRAKEFORD BRIDGE | R06D002 sx 7893 8015| 1 30 BOVEY |LITTLE BOVEY | R06D003 sx 8320 7672| Reach |Distance River 85 86 61 88 89 90 [ Length j from Quality imc NWC NWC IMC NWC NWC | (kn) | source Objective Class Class Class Class Class Class| | (km) 1 1 1 1 1.5 1 1 5 1A 1A 2 1A 1A 1A 1 0.6 1 2 1 IA 1A 2 1A 1A 1A 1A | 4.2 | 6.3 1A 1A 2 1A 1A 1A 1A | 1 10.7 | 10.7 1A 1A 2 1A LA 2 2 1 4.1 | 14.a LA 1A 2 1A LA 1A 2 | 9.7 | 24.5 1A LA 2 1A 1A 1A 1A | 7.7 | 32.2 1A IB IB IB 18 1A 1A | 3.8 | 36.0 1A IB 2 2 1A LA IB | 3.5 | 39.5 1A IB 2 2 1A 1A 1A | 3.4 | 42.9 1A 1A IB 1A 1A IB IB | 2.7 | 45.6 1A 1A IB 1A 1A IB 2 | 2.5 | 48.1 1A 1A 1A 1A LA IB IB | 2.7 | 50.8 1A 1A 1A 1A 1A 18 IB (

1.2 1 12 2 3 3 2 3 3 3 | 1.9 1 3 1 2 2 3 IB 18 IB IB | 1.9 | 5.0 2 2 4 3 3 3 3 | l.B | 6.8 2 2 2 3 3 3 3 } 1.1 J 7.9 2 2 2 3 3 3 * 1 1 2.4 1 2.4 1A IA 1A 2 2 2 3 | 2.4 | 4.8 1A LA 1A 2 2 2 18 | 9.4 | 14.2 1A 1A 1A IB IB IB 2 I 1.1 | 15.3 1A 1A 1A IB IB IB 2 | 1 0.9 | 0.9 1A IB t 2.3 | 3.2 IB 3 | 1.1 | 4.3 IB 3 | 1 4.2 1 4.2 IB i 2 | 2.3 | 6.5 IB 3 2 | l.S | 8.3 2 3 3 | 0.1 | 8.4 2 3 3 |

3.4 1 3.4 IB 18 | 2.6 | 6.0 IB IB | 1.4 1 2 2 | 0.2 | 7.6 2 2 | 1 8.8 | 8.8 IA IB | 0.3 1 9.1 1A IB | 1 9.6 | 9.6 LA LA 1A LA LA LA IB | 8.1 1 17.7 LA l a 1A LA 1A LA LA | 6.5 | 24.2 1A LA IB 18 IB IB LB j NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION 1990 RIVER MATER QUALITY CLASSIFICATION CATCHMENT : TEIGN (06)

|1990 Hap River |Reach upstream of | Usee National | |Position 1 {Reference Grid | | Number 1 | Nunber Reference | 1 1 1 1 1 1 1 1 1 31 BOVEY | TWINYEO FARM | R06D004 SX 8447 7605| 1 BOVEY [TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 1 32 BECKA BROOK |NEW BRIDGE | R06D010 sx 7580 8006| 1 BECXA BROOK |BOVEY CONFLUENCE (INFERRED STRETCH) 1 1 1 33 WRAY BROOK |CASELY COURT | R06D008 SX 7858 8225| 1 34 WRAY BROOK IKNGWLG | R06D011 sx 7888 8024| 1 WRAY BROOK |BOVEY CONFLUENCE (INFERRED STRETCH) 1 1 1 35 KATE BROOK |CHUDLEIGH | R06C055 sx 8595 7853| 1 KATE BROOK |TEIGN CONFLUENCE (INTERRED STRETOl) 1 1 | 36 BRAMBLE BROOK |PRIOR TO RIVER TEIGN | R06C011 sx 8491 8124| 1 BRAMBLE BROOK |TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 1 BEACON BROOK | INFLOW, TRENCHFORD RES. (UHMON. REACH) | 37 BEADON BROOK |TR£NCHFORD RESERVOIR | RO6C050 sx 8064 8288| i 38 BEADON BROOK I To m FORD HOUSE | R06C009 sx 8084 8228| 1 39 BEADON BROOK |HYNER BRIDGE | R06C010 sx 8368 8170| | 40 BEADON BROOK |PRIOR TO RIVER TEIGN | R06C040 sx 8428 8170| 1 BEADON BROOK |TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 1 KENNICK STREAM | INFLOW, KENNICK RES. (UNMDN. STRETCH) 1 41 KENNICK STREAM |KENNICK RESERVOIR | R06C046 sx 8068 838B| 1 KEKNXCK STREAM | INFLOW, TOTTIFORD RES. (UNMON. STRETCH) 1 42 KENNICK STREAM |T0rrriFt>RD RESERVOIR | R06C049 sx 8106 8271| 1 1 1 43 ROOKERY BROOK |POOLE | R06C012 sx 6173 8610] 1 44 ROOKERY BROOK |ABOVE BARYTES MINE | R06C013 sx 6300 8632| 1 45 ROOKERY BROOK | PRIOR TO RIVER TEIGN | R06C014 sx 8376 8671| 1 ROOKERY BROOK |TEIGN CONFLUENCE (INFERRED STRETCH) 1 1 | 46 SOWTON BROOK | SOWTON BRIDGE | R06C015 sx 6338 8745| SOWTON BROOK |TEIGN CONFLUENCE (INTERRED STRETCH) 1 1 1 47 REEDY BROOK |REEDY BRIDGE | R06C054 sx 8199 6930) 1 REEDY BROOK |TEIGN CONFLUENCE (INTERRED STRETCH) 1 1 1 48 SCOTLEY BROOK |CLIFFORD BARTON | R06C0S7 sx 7772 9008| I 1 | 49 FINGLE BROOK |FINGLE BRIDGE | R06C053 sx 7433 9000| 1 FINGLE BROOK |TEIGN CONFLUENCE.

1.6 | 25.8 1A 1A IB IB IB IB 1A | 0.9 | 26.7 1A 1A IB IB IB IB LA |

3.9 1 3.9 1A 1A IB | 2.4 | 6.3 1A LA 18 | 1 7.5 1 7.5 1A Ia 2 j 2.7 r 1 0 .2 1A 1A IB | 0.4 | 10.6 1A 1A IB | \ 3.6 | 3.6 1A IB | 0.2 | 3.8 1A IB | 1 6.4 | 6.4 1A 1A 1A 1A 1A 1A IB | 0.1 | 6.5 1A 1A 1A 1A 1A LA IB | 1 3.0 | 3.0 1A IB 3 3 5 3 1 0.8 1 3.8 1A IB 3 3 3 3 2 I 0.2 | 4.0 1A IB 3 3 3 3 3 J 3.4 I 7.4 2 3 3 3 3 3 1A | 0.8 | 8.2 2 3 3 3 3 3 IB | 0.1 | 8.3 2 3 3 3 3 3 IB |

1.5 | 1.5 18 1 1.3 | 2.8 IB IB | 0.1 | 2.9 IB 1 1.1 | 4.0 IB LA | 1 2.4 1 2.4 IB i 3 i IB 1A 1A | 1.5 1 3.9 3 3 IB IB LA 1A 1A | 0.9 | 4.8 3 4 3 3 3 3 3 | 0.1 1 4.9 3 4 33 3 3 3 J 1 1 6.1 | 6.1 IB 18 IB IB IB 2 2 1 0.3 | 6.4 IBIBIB IB IB 2 2 1 \ 4.7 1 4.7 1A 3 | 0.5 | 5.2 1A 3 1 1 5.3 1 5.3 1A 3 1

7.0 1 7.0 IB 2 1 0.0 | 7.0 IB 2 1

7.5 1 7.5 LA IB | 1.5 | 9.0 LA IB | Teign Catchment Water Quality -1990

N O C fflL RIVERS /UTCKEIY - 3CUIH VEST FH2EN 1990 RIVH^ V K E F Q M J T i CLASSIFICHnEN cMiiiarn) EEigwpwp amnsn cs u s e d t o q l m j i y AssEsa-pg o a o t c n r : T E H U (06)

|River |nsach ifstneu of | Ubar 90 Oilailatod DBtanuimd statistics U9ed for Quality Assessment I 1 | fef. »C 1 1 1 1 1 1 I 1 j Nu b e r Class pH Lower | pH L£per | Tteperatue } DO (%) | BOD (MU) flbtal Jtmania JUrim. Anoxia S.Salicfe Tbtal Qf p v "total Zinc j I 1 1 Class 5*H» j Class 95%ilo | Class 95%ile | Class 5%ile j Class 95%ile j Class 95\ile j Class 95%Hb Class n m (lass 95U1* Class 9% l e j I 1 1 1 1 1 1 1 1 I 1 1 I 1 1 1 1 1 1 1 1 |30Um lEK W KWEH IVUNCKIlff JEHW3IR IB06CXSL LA 1A 5-3 1 1A 6.9 LA 19.0 1A 86.0 1A 2.0 1 1A 0.080 1A 22.3 |3DUm TED39 RIVER |i£D»aasos jpoecooi 1A 1A 6.0 1 u 7.1 1A 1£.8 lA 82.0 1A 2.1 i 1A 0.029 1 1A 0.010 1A 3.2 LA 10.4 1A 67.2 | 1 1 I IKKIH TEttJJ RIVtK lamoni w « tern* PC6C002 2 LA 5.6 I I* 6.6 1A 17.5 1A 88.6 LA 2.1 1 1A 0.039 1 1A 0.010 lA 1.1 2 10.6 LA 27.6 | |TE3X39 jnraac |F06G003 2 LA 5.9 t 7.0 LA 16.5 1A 83.2 2 7.7 1 1A 0.100 1 lA 0.010 lA 2.4 LA 5.0 1A 12.0 | ITEHU laJPKXD SCOBS |BDGG004 1A 1A 6.6 1 u 7.4 LA 18.1 1A 82.3 1A 2.6 1 !A 0.067 1 1A 0.010 lA 3.0 - -- - j \t e b 3h isarrao aran |HQ6C005 1A 1A 6.6 1 1* 7.4 1A 18.3 LA 86.6 1A 3.0 t 1A 0.052 1 1A 0.010 LA 3.4 1A 7.8 1A 29.0 | 1*03X11 | S M A B 0 n X |B06C037 IB 1A 6.7 1 7.4 LA 17.2 IB 74.6 1A 2.6 1 1A 0.061 1 JA 0.010 1A 4.3 1A 9.4 LA 91.0 | {tESS ICKXXME OO Q E {F06C006 1A 1A 6.8 1 1A 7.4 1A 16.6 1A 85.2 1A 2.6 1 !A 0.051 1 1A 0.010 LA 4.0 1A 6.1 1A 95.1 | |iEiat [OUXEElf W11U5 |fl06C007 IB 1A 6.6 I 1A 8.0 1A 18.3 IB T5.3 LA 2.5 1 1A 0.070 1 1A 0.010 1A 6.4 1A 8.6 1A 106.6 | | 1 o » |tlW BODGE |BDGG008 2 1A 7.0 1 !A 7.8 1A 17.9 2 56.8 1A 2.2 1 1A 0.080 1 1A 0.010 LA 5.8 1A 11.4 1A U1.0 | |1ED3V IHG3IEN iPDfflOOl IB 1A 6.9 1 1A 7.7 LA 17.0 LA 80.4 IB 3.2 1 1A 0.107 1 1A 0.010 lA 19.0 lA 14.0 1A 78.9 | 1 1 1 pÛRBOCK lo x m s e u u h w q g s m n a i |J€6*ML 3 1A 7.6 1 Â 8.1 LA 17.0 2 48.5 3 13.9 | 3 1.700 1 3 0.029 1A 8.9 - - - - | |AU£RBC0K |j«nR cfxve K i H s a a c L |P06W»2 IB LA 7.6 1 1A 8.3 1A 16.5 LA 81.0 IB 3.3 1 IB 0.550 1 1A 0.010 1A 16.9 1A 7.0 LA 25.0 j |AIIfR 8RXF ptflflKKJMD |B06NX)3 3 1A 7.7 1 8.2 1A 17.0 IB 66.0 3 14.0 | 3 2.981 1 3 0.060 3 30.9 - - - - j jtf lS tB C C K IHIWDW (©OCR/TOT IF06A004 3 1A 7-8 | 1A 8.2 1A 17.1 IB 76.0 2 7.3 1 2 1.221 1 3 0.030 3 41.8 “ ” | 1 I 1 |I£KW {a o a z n m i . |RD6H»3 3 1A 6.5 1 JA 7.0 LA 14-5 3 30.9 LA 1.7 1 lA 0.059 1 1A 0.010 1A 3.0 1A 8.8 1A 12.8 | | U K H jEEXCW ( H f Q E R E H Q H RIVER SB3 |ttffl004 IB 1A 6.6 1 1A 7.4 LA 15.0 IB 79.9 1A 2.0 I 1A 0.060 1 1A 0.010 LA 3.7 1A 11.1 1A 46.3 | |U K M ismxcr euxhc puue rcwm t a n s |H36B005 2 1A 7.3 1 1A 8.3 1A 17.0 2 55.5 1A 2.6 1 I* O.lfiO 1 1A 0.010 1A 7.0 LA 12.6 1A 18.5 | 1 1 1 lamoroDawjw | R H V P7W1 |FD6B006 IB LA 7.2 1 Â 8.2 LA 15.0 IB 79.5 1A 2.4 1 !A 0.146 1 1A 0.010 1A 22.8 LA 6.9 1A 19.4 | 10/00100 SBOM (O id a F X D (FD6B007 3 LA 7.6 1 !A 8.3 1A 15.5 IB 67.0 LA 2.8 1 1A 0.110 1 1A 0.010 3 35.8 1A 50.0 1A 50 .0 1 1 1 1 i m m i |UHCC*E SZEDH lu nraTl |B06BQ11 2 1A 7-5 1 1A 8.4 LA 18.4 IB 67.5 2 7.5 1 IB 0.460 1 1A 0.019 LA 14.6 LA 5.0 1A 13.1 | jix a a x e s s o h IHnXP StEBSOE |S06B012 2 1A 7.6 1 l a 8.2 LA 16.9 IB 77.8 2 5.5 1 2 0.838 1 lA 0.010 1A 18.5 1A 10.3 LA 32.3 | |US*X*E SUCH |Hmil ID RIVER 1ED3I |F06B013 3 LA 7.3 1 1A 8.0 1A 17.3 LA 88.5 1A 2-5 | 1A 0-215 1 JA 0.010 3 122.5 2 50.0 1A 107.6 | 1 1 1 |SMCKHE SDCm |n a n t t d a x i m s o c k |PDffl008 IB LA 7.6 1 1A 8-2 1A 15.9 IB 67.0 LA 2-6 1 l a 0.162 1 1A 0.010 1A 6.2 LA 12.2 1A 13.2 | |SNDR3QE SBBM |CEOfE HXIKIDZ JRD6B009 IB LA 7.8 1 !A 8.5 1A 15.4 IB 79.1 lA 2.3 1 !A 0.096 1 1A 0.010 1A 7.7 1A 5.0 1A 13.0 | ISNlXQgS STPDH }lfW QCSS WWJbUOMm |fl*B010 2 1A 7.7 1 1A 8.2 LA 16.4 2 44.6 2 5.1 1 1A 0.L19 1 1A 0.010 1A 8.5 LA 5.0 1A 21.9 j i 1 1 75.6 | l U V H O B C C K IVQ03PCH3 a a n z |F06B050 IB IA 7.5 1 ^ 7.8 1A 17.0 IB 73.2 LA 2.4 i 1A 0.127 1 1A 0.010 1A 7.1 1A 6.9 LA 1 1 1 |B0UK lOAXMLER tQOH BCWEf jpoaooi IB 1A 6.6 i !A 7.3 1A 15.4 IB 75.8 lA 2.3 1 1A 0.040 1 1A 0.010 LA 4.8 - - - - | (IEVEX (rratoKH) am z z |B06C0Q2 1A lA 6.7 1 Â 7.2 LA 15.9 1A 89.3 1A 2-8 1 iA 0.065 1 !A 0.010 1A 5.1 - - - - | pedx 10.< Appendix |b o w |Lrm£ acvEif |B06DOO3 IB 1A 6.7 1 !A 7.4 1A 17.2 1A 86.4 IB 3.4 1 1A 0.061 1 1A 0.010 LA 7.4 LA 7.0 1A 21.2 | |0CW2f j TW INS) FMH |PD6C004 1A 1A 6.8 1 1A 7.4 1A 18.1 1A 81.7 1A 2.6 1 1A 0.120 1 1A 0.010 1A 12.9 1A 7.3 1A 20.0 | 1 1 1 |EEUA BCCK JtfW 9HDGE IKD6C010 IB LA 6.3 1 1A 7.1 1A L6.0 IB 65.1 LA 2.5 1 1A 0.185 1 1A 0.010 1A 5.2 1A 6.9 1A 11.0 | 1 1 1 ivtiw a r a c lotaiy axis1 FD6E008 2 LA 7.0 1 1A 7.4 1A L6.9 IB 79.2 IB 4.4 | 2 0.743 I I* 0.010 1A LO.O 1A 6.9 1A 0 . 7 | |VRAY H O * | N E H £ IB06C0U IB 1A 7.0 1 1A 7.4 1A L6.9 1A 80.3 IB 3.9 1 IB 0.319 1 1A 0.010 1A 8.9 1A 8.8 LA L9.0 | 1 1 1 NflHL*M> HHVE8S jgJDCRny - 3DUIH VEST FEdEN 1990 RIWEaVRnRqWIIK OJeSlFKSnCK (xomnp gantmwi) smnsncs ihd c t q k jn kses&bb CTOOffNT : TECTJ (06)

(River | Reach vgBtraan of 1 Iter | 90 | rhimiatfrari Datemrinand Statistics used for QaUty jteMsunait 1 1 1 1 Rsf- 1m e | 1 1 1 1 1 | m±er[ Oass| £fi Lower | EHlfeer TbipexsturB DO (%) | BCD UOU) (Tbtal Anuria fUucn. A uuiilb| S.Solicb Total Zinc | 1 1 1 I Class 5%ils | Gass 95tile (lass 95%ile Stile | Class 95tile | Class 95tile | Class 95til» | Class M u | Class 95%ile Cass 95%ii* | I 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 « 1 \ m z bo x lauracs |E0GG055| IB | 1A 7.8 1 8.5 1A 17.9 lfi 79.2 1 IB 3.1 1 1A 0.280 1 1A 0.010 1 1A 6.3 1 1A 5.0 1A 19.1 | 1 1 1 1 1 1 |BV»B£ BOCK |HULK ID HTVSt TEB3i |nxoau| IB | 1A 7.5 1 8.1 1A 15.4 1A 82.5 1 u 3.4 1 1A 0.037 1 1A 0.010 1 1A 7.7 1 1A 5.0 1A 16.7 | 1 1 1 1 1 1 l a w m a n * ITMZUKM) USSSCOR |R£CGE0| 2 I 1A 6.2 1 6.7 1A 19.0 2 54.0 1 1A 2.1 1 !A 0.120 1 1A 0.010 1 1A 2.1 | - - - - | [BENXnSDGK iromRH) m s |HKC0Q9| 3 | 3 4.7 1 I* 8.0 1A 18.0 lfi 79.0 1 1A 2.6 1 1A 0.212 1 3 0.026 | 1A 12.1 | - - - - | |SXXR 9£XX |H9ER SO R E |H36CD10| 1A | 1A 6.5 1 1A 7.1 1A 15.7 1A 86.6 | 1A 2.1 j 1A 0.034 1 1A 0.010 1 1A 3.8 j - - - - J |EDDCN BOCK |TOERTD raVTOTEHU |HKGM0| IB | 1A 6.8 1 1A 7.8 1A 16.2 lfi 77.3 1 1A 2.3 1 1A 0.032 1 1A 0.010 1 1A 4.1 | " - | 1 1 1 1 1 1 [Ftranx ssc3H (KZ9HEX ICEOBXSR (B06G0481 lfi | 1A 6.4 1 1A 7.2 1A 20.0 lfi 64.0 1 13 3.1 1 1A 0.050 1 1A 0.010 1 1A 2.7 J - - - ^ | (FOTDEK SB B M fromKH) ra z u m |BDGCD49| 1A | 1A 6.4 1 7.0 1A 20.0 1A ai.o 1 1A 2.1 1 1A 0.140 1 1A 0.010 1 1A 1.9 | * ” ^ | 1 1 1 1 1 1 iRUHCf SOCK |KTU |FD6GQ12j 1A | 1A 6.7 1 1A 7.1 1A 14.5 1A 84.9 1 1A 2.0 1 1A 0.151 1 1A o.mo | 1A 4.9 1 1A s.o 1A 15.7 | I H X M W BOCK |MXMB EKRQE5 MDE |H36G013| 1A | 1A 6.9 1 1A 7.4 1A 15.6 1A 82.0 1 1A 2.2 1 1A 0.141 1 *A 0.010 1 1A 5.7 1 lA u.o 1A 144.5 | j m w w HU K |H0m TO RTWR in ® |J0GGQ14| 3 1 1A 6.5 1 !A 7.0 1A 15.1 1A 83.7 1 IB 3.1 1 1A 0.130 1 1A 0.010 1 1A 6.3 1 1A 33.2 3 4020.0 | 1 1 1 1 1 1 (30001 BOOK |s m b h bo i z x |BDGCQ15| 2 1 1A 7.0 1 1A 7.8 1A 18.3 2 44.6 1 1A 2.1 1 1A 0.165 1 !A 0.010 1 1A 5.3 1 ^A S.O 1A 21.2 | 1 1 1 1 1 1 (MILK BOCK \vsnx butue |E06GQ54| 3 1 1A 6.9 1 7.8 1A 15.0 3 15.0 1 2 5.4 1 1A 0.170 1 1A 0.010 | 1A 9.5 1 — — • “ { 1 1 1 1 1 1 \ s a m x x bock IOU7KZD BR B H |B06C057| 3 | 1A 6.9 1 JA 7.7 1A 15.0 3 32.0 1 12 3.3 1 1A 0.230 1 !A 0.010 | 1A 9.2 | ““ " | 1 1 1 1 1 1 IP3HZE BOCK |pmz£ Ba n x |£DGG063| 2 I 1A 6.9 1 1A 7.8 IA 15.4 1A 81.0 | 2 8.7 1 IB 0.396 1 1A 0.010 | 1A 1.A | - * * 1 1 1 1 1 1 1 (s/cmrcN b o c k |QMfI£ |ID6G052| lfi | 1A 6.6 1 1A 7.0 1A 15.5 lfi 75.1 1 1A 2.9 1 IB 0.537 1 1A 0.010 | 1A 3.9 1 !A 6.9 1A 18.8 | 1 1 1 1 1 1 Teign Catchment Compliance -1990

iwnDN, k x v b s wntxtnr - s u h tear pbsscn 1990 FUVQlWSR 9 IU T T Q JS 3 PTCXQEN r u m rum cr sm e awm sircno (P) O O O f O T : DESK (06)

|Rlwr jRndi tywtp—n of 1 Utar 1 fH lamx E«lfc*r | itepKatun DO (%) BCD (AXU) |D£al /Bsxxiii |Udm. Aaaxua| S-9olicfc ibtol Cbfytr I Tbt&l Zinc | 1 I Brf. 1 1 1 1 1 | Nsfaarl n p N P 1 I* P N P NP 1 N P 1 R F 1 HF N P | N P | 1 1 1 J 1 1 1 1 1 1 1 1 1 I 1 1 1 1 1 , 1 1 1 1 |SUH 1SSM RMS inRNKDff nsnxro |flxa»i| u - U - 1 12 - 11 - 11 - 1 11 - 1 8 - | U 1 12 ( 12 | |XUR m n RMS Item b o o s |P06CD01| 30 “ » — 1 31 - 30 1 30 — 1 30 - 1 20 30 1 31 ~ | 31 - | 1 1 1 1 1 1. liaan m m ravm Kanant rat razx. JPMC002I 30 - 30 - 1 u - 30 - 36 - I 30 - 1 22 - | » - ii 1 | ii I fimi IIUHOD IIC6CD03I 20 - 20 - 1 20 - 20 - 20 1 1 20 - 1 20 | X - 20 i 20 j p m i Icunoo BBSS |FD6C0M| 25 - 25 - 1 25 - 25 - 25 - 1 25 - 1 23 - | 25 - 0 - i 0 - | finai iwniuv amxz \w6aas\ 36 - 36 - I 36 - 36 - 36 1 1 36 - 1 30 - | 36 - 36 - j 36 - J iram j s m a Bt m z |F06C037| 38 - 38 - 1 38 - 38 2 37 1 1 37 - 1 32 - j 38 - 38 i t 38 | rxoai | a c a n Ba n s \S060D6\ 38 - 38 - 1 38 - 38 1 38 - 1 38 - 1 31 - | 38 - 38 i 38 j flZJUl lauuani so n s |tOGCOQ7| Z3 - 23 - 1 ZL - 21 2 21 - t 21 - 1 21 | 23 1 21 i 21 i (roar liwaanz irasoei 23 - 23 - 1 a - 21 1 21 - 1 21 - 1 21 - | 23 1 21 - i 21 - j Iran Ir o o r |PDGB0Q1| 68 ~ 68 1 £7 — 66 2 66 3 1 66 1 ® 68 13 a i i a —■ i 1 1 1 1 1 1 1 pmjssaccK lEzxaieMzx. r i v d c a m n m |BDGW0I| 39 - 39 - 1 38 - 38 1 39 2 1 39 2 1 30 1 | 39 3 0 i 0 - i [ALLQt SOCK [ m t x crtvg n n o * a o g i > |HJ6MQ2| 39 - 39 - I 39 - 39 - 39 - 1 39 - 1 37 - | 39 7 39 i 39 - i |*Ui» BOOK i M i s t a o n c |R06M»3| 39 - 39 - 1 39 - » - 39 5 1 38 8 1 » 12 | 39 14 0 - i 0 - I IKUERBOX i m a m m e a t Ne a r |RXM04| 38 — 38 — 1 38 — 38 “ 38 1 1 38 1 I 38 2 | 38 14 0 *■ i 0 - i 1 I t 1 1 1 1 i mcM iBNjNnn mdll |NX£003| 20 - 20 - 1 20 - 20 1 20 - 1 20 - 1 16 | 20 - 20 i 20 - j {IDOI [BEzar a m m z w m ravro sic |H06B004| 26 - 26 - I 26 - 26 1 26 - 1 26 - 1 26 - | 26 - 2 - i 25 - j | i w » iBvafir m a o c n m s nxrcn abbot |H06B005| 34 — 34 — 1 34 ~ 34 2 34 1 1 34 — 1 32 34 1 33 - i 33 “ i 1 1 1 1 1 1 1 IKAKMCK) SSBM | n m n m |B06B006| 20 - 20 - 1 20 - 20 L 19 - t 20 - 1 20 | 20 4 20 i 20 j |gjttutm> s m m [B/aarac (BD6B007) 20 ** 20 — 1 l^ — 19 — 19 — 1 19 — 1 19 20 10 19 ■ i 19 ■ I 1 1 1 1 1 1 I IUBCCNCSEMDN KJMWM |S0GBQU| 22 - 22 - 1 » - 22 - 22 2 1 22 - 1 21 - | 22 2 22 i 22 - i l uscaz s x x m |HDMS SVEKSQE |P0ffl0L2| 22 - 22 - t 22 - Z2 - 22 1 1 22 2 1 22 - | 22 3 22 ( 22 i lucBoac s a w inazu ID tuvvM m x |B06B0U| 24 24 1 24 24 ■* 24 1 24 — 1 24 24 21 22 ■ i 22 — i 1 1 1 1 1 1 _ 1 ISKOOOK SDON {nan to o u s t hook |P06B006| 23 - 23 - 1 22 - 21 - 23 - 1 23 - i 22 | 23 I 23 i 23 i l a m o a g a n w |ax»«K n n n n x (W6S009| 23 - 23 - 1 23 - 22 - 23 - 1 23 - t 23 - | 2) 1 23 i 23 i j s n o o e s s o R |tiw Qu s iccunxnout |FD6BD10| 22 22 1 n a 1 22 I U ” 1 22 22 1 22 * i 22 — | 1 1 1 1 1 I 1 |LXVEHm BOCK rVDQSKR) BOXXZ |RDffl050| 21 — 21 — 1 20 — 20 2 21 1 21 ~ 1 20 21 1 21 * i 21 - i 1 1 I 1 1 1 1 |BCM3r iBjaMin ram syjct |ftiffi001| 24 - 24 - 1 24 - 24 1 24 - 1 24 - I 23 - | 24 1 0 j 0 j 10.9 Appendix |BMSr lOMBCBO Btmz |R06C002| 24 - 24 - 1 24 - 24 24 1 1 24 - 1 19 - | 24 1 0 i 0 I |Boocr |U31X£ B3UQT (B06C003I 38 - 38 - 1 37 - 37 37 3 1 37 - 1 » - | 38 3 37 - i 37 - 1 lacwer { w n c ® rw* |nxcoo4| 39 ~ 39 — 1 38 ~ 3T7 1 37 1 1 37 - 1 36 39 S 37 - i 17 l 1 1 1 1 1 1 | n o & m x K |MN Bt m z IPMOiOj u — U ~ 1 *2 - 22 2 22 ~ ( 22 - 1 21 22 1 22 - i 22 i 1 1 1 1 1 1 1 pHMtf B O X l o a m o x r t |K*nXM| 21 - n - 1 21 - 20 1 21 } 1 21 t 1 li a 1 }i i il I \ m x n o * | K O U 11 ■ 21 “ t 21 - 21 - 21 1 1 21 1 1 21 21 1 21 i 21 i 1 1 1 1 1 1 1 iVSSML RXVBtS XUHXtHT - SXHH tCST HGH3I 1990 RIVER tfOER Q K I T t dASSffTCJTOK fUfER cr 9 N U S (TO XC> I W X CF 3KUS UKSiLNj gWJIY SR1KI) (F) onatfHr : issai (06)

1 1 1 n t f . 1 1 1 i i

1 1 1 1 1 1 1 1

1 1 1 1 1 1 1 1 | w r a B O C K j a u u n r a 2 0 J H ) 6 C 0 6 5 | 2 1 2 1 “ 1 2 0 “ 1 2 1 1 1 2 1 1 1 9 2 1 1 1 2 1 2 1 - |

1 1 1 1 1 L . 1 .... a - - a ™ - ” | | B N O £ B O C K (HOCR ID RIVtS 1X301 ( K E O Q U l 2 5 2 5 1 2 5 “ 2 5 ■“ 2 5 1 1 2 5 “ 1 4 « 5 “

1 1 1 I 1 1 - J fppm qcucpwm J f C 6 C 0 5 0 | 1 2 1 2 iiii i m X Z H B O O K 1 1 2 1 1 1 1 2 1 1 2 1 i i 1 2 1 1 2 pF0 6 C D < » | j s M Q I E R T K (ramicHo m s 3 7 3 3 7 1 I 3 7 " 3 7 3 3 7 - j 3 7 1 3 5 1 | 3 7 2 1 3 7 |P0 6 0 Q 1 0 | 3 7 3 7 3 7 3 7 l E m x n a o o K (HBCR BOJXZ 3 7 1 3 7 1 3 7 1 3 0 1 1 * |H0 6 C D 4 0 | 3 6 3 6 1 3 6 {ascot BOOK | n m TD RIVES IS U I 1 3 6 1 3 6 1 3 6 1 2 0 3 6 1 1 % -

1 1 1 1 1 1 1 (ranaat asraam | F D 6 C D 4 6 | 1 2 1 2 iram nx sncm 1 u 1 1 1 2 1 1 2 1 i o 1 2 1 1 2 u - j [ratcac SQ SK n u r a w i ) m s B u m p C 6 C 0 « | 1 2 - 1 2 - 1 2 - 1 1 2 - 1 2 - t 1 2 - 1 u 1 2 - 1 1 2 - 1 2 - |

1 1 1 1 1 j s c c m r b o x I r a x i n d t f d O l ^ i a 1 3 7 1 3 9 1 1 2 8 f t 1 1 3 7 H | jnxraRr BRXK |f0 6 C 0 1 3 | p a n e m s a s m e 3 7 3 7 1 3 7 - 3 7 3 7 - 1 3 7 t 3 3 3 7 1 3 7 3 7 - | p a m r b o x |m m ID RIVER 1031 I f l K C D M l 3 7 - 3 7 - 1 3 7 3 7 3 7 1 3 7 1 3 6 3 7 1 3 7 - 3 7 - | 1 - L - . . . 1 1 1 1 1 | S M O I B O C K \3 a a m m a | P O f c t l S | 2 S ~ 2 5 — 1 2 5 “ 2 5 5 2 5 ~ 1 2 5 1 U 2 4 *" 1 2 4 2 5 - |

1 i 1 .. 1 - 1 1 1 p a n b d c k p o o r BR1UGZ 1 1 0 6 0 * 4 1 1 7 1 7 — 1 1 7 “ 1 7 6 1 7 1 1 1 7 1 1 * 1 7 2 1 1 7 “ 1 7 - |

1 1 1 1 1 1 _ _ L [snrmrr a a x l a i T O D g n o c r 11 0 6 0 0 5 7 1 1 3 ■— 1 3 “ 1 1 3 “ 1 3 6 1 3 2 i u 1 u 1 3 2 1 1 3 ■“ 1 3 - I

1 1 1 1 1 1 1 i n x x E b o c k i r o n s e k q x z |F0 6 C 0 5 3 | 2 0 2 0 * i 2 0 2 0 ~~ 2 0 1 1 2 0 “ 1 1 9 2 0 - I 2 0 "" 2 0 - 1

1 1 1 1 1 I 1 (8 X 39001 BOCK | a m u |F D 6 C Q S 2 | 2 0 2 0 1 2 0 2 0 2 2 0 1 2 0 1 1 2 0 2 0 1 2 0 2 0 - |

1 1 1 1 “ 1 “ 1 1 NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION 1990 RIVER WATER QUALITY CLASSIFICATION PERCENTAGE EXCEEDENCE OF DETERMINAND STATISTICS FROM QUALITY STANDARDS CATCHMENT : TEIGN (06)

[River |Reach upstream of User | 1 Ref. j 1 Number| pH Lower 1

I - - | | - 1 - 1 I 1 1 1 1 1 2 I 1 158 | - I 1 - 1 | : ! 7

6 I | 29 | 1 - 1 - - 1 6 1 1 t 1 1 | - 1 S* 1 9 1 36 I - 1 - 1 i 1 56 | 91 | 186 23 | - j 45 67 | - 1 - 1 1 1 1 1 61 i - | I - 31 1 - 1 1 1 1 1 1 i - | 43 j - 1 - 1 1 1 1 1

- 20 1 - i O o 1 390 | 1 - 1 1 1 i - j - | - 1 “ 1 I 1 1 1 i - 9 | “ ** 1 “ 1 1 1 1 5 i - - 1 ~ 1 1 13 1 II

1 1 1 1 i 19 I - 1 - | ~ — | 1 1 ! " | I 1 ^ 1 140 i 1 « 1 3 | I - i - i 1 1 1 1 NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION 1990 RIVER WATER QUALITY CLASSIFICATION PERCENTAGE EXCEEDENCE OF DETERMINAND STATISTICS FROM QUALITY STANDARDS CATCHMENT : TEIGN (06)

|River (Roach upstream of | User | PERCENTAGE EXCEEDENCE OF STATISTIC FROM QUALITY STANDARD 1 | Ref. | i 1 1 1 1 1 ( Number( pH Lower | pH Upper | Teinperature| DO (%) BOD (ATU)| Total Un-ionised Suspended j Total | Total 1 1 I 1 1 1 | Ammonia Ammonia Solids ( Copper ( Zinc I t 1 1 1 1 1 1 1 i 1 1 1 1 1 1 1 1 1 1 1 1 1 |KATE BROOK (CHUDLEIGH |R06C055| 1 4 ( - — - | - 1 1 1 1 1 1 1 1 |BRAMBLE BROOK (PRIOR TO RIVER TEIGN |R06C011| “ “ 14 ( - - ( - 1 1 1 1 1 1 1 1 |BEADON BROOK (TRENCHFORD RESERVOIR |RO6C050| -[ 1 ~ 1 32 | - - _ | _ {BEADON BROOK (icrriFORD HOUSE |R06C009( 6 ( 1 - 1 1 | - 33 ( - | |BEADON BROOK |HYNER BRIDGE |R06c010( - | 1 - ( - 1 - -( _ ( - |BEADON BROOK |PRIOR TO RIVER TEIGN (R06C040( — - - - - ( - 1 1 1 I 1 1 1 1 |KEKNICK STREAM |KENNICK RESERVOIR (R06C048| - ( t - | - | - - ( - |KENNICK STREAM ITOTTIFORD RESERVOIR |R06C049| - - - - - j - I 1 1 1 1 1 1 1 |ROOKERY BROOK |POOLE |R06C012| * | 1 - | - | - ~ - | - (ROOKERY BROOK (ABOVE BARYTES MINE |R06C013| - | 1 - | - - | -_ - ] _ 1 — (ROOKERY BROOK (PRIOR TO RIVER TEIGN |R06C014| * - - - - ( - 1 1 1 1 1 1 1 1 (SOWTON BROOK |SOWTON BRIDGE |R06C015| 26 - - - ( - 1 1 1 1 1 ( 1 1 |REEDY BROOK (REEDY BRIDGE |R06C054| 16 80 | ~ — -* I — 1 1 1 1 1 1 1 1 ISCOTLEY BROOK (CLIFFORD BARTON |R06C057| 60 10 | — — ” 1 1 1 1 1 1 1 1 |FINGLE BROOK (FINGLE BRIDGE |R06C053| ~ 74 ( — — | — 1 1 1 1 1 1 1 1 (BLACKATON BROOK (CHAPPLE (R06C052| — 6 73 — " | 1 1 1 1 1 1 1 1 NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION IDENTIFICATION OF POSSIBLE CAUSES OF NON-COMPLIANCE WITH RQO CATCHMENT : TEIGN (06)

* a WORK ALREADY IN HAND

|1990 Map River | Reach upstream of User Reach |Possible causes of non-compliance T (Position 1 Reference Length 1 | Number 1 Number (km) 1 1 1 1 1 1 1 1 1 1 1 1 1

1 3 NORTH TEIGN RIVER | GIDLEIGH PARK HOTEL R06C002 10.7 |CATCHMENT GEOLOGY, UP-STREAMS ABSTRACTIONS, MOORIAND 1 1 4 TEIGN | RUSHFORD R06C003 4.1 | SEWAGE TREATMENT WORKS, UP-STREAM ABSTRACTIONS 1 | 7 TEIGN | SPARA BRIDGE R06C037 3.8 |DROUGHT 1 I 9 TEIGN | CHUDLEIGH BRIDGE R06C007 3.4 1 1 io TEIGN | NEW BRIDGE R06C008 2.7 (SEWAGE TREATMENT WORKS, U W VELOCITY 1 1 11 TEIGN | PRESTON R06B001 2-5 (INDUSTRIAL DISCHARGE 1 1 1 1 1 12 ALLER BROOK | EDGINSWELL PUMPING STATION R06A001 1.2 (URBANISATION, CULVERTING, SEKAGE TREATMENT WORKS, LOW FLOWS | 1 14 ALLER BROOK | ALLER ORCHARD R06A003 1.9 |URBANISATION, SEWAGE TREATEMENT WORKS, DEVELOPMENT AT BARTON | 1 15 ALLER BROOK | PENNINN NEWTON ABBOTT R06A004 1.8 |URBANISATION, CULVERTING 1 1 1 1 1 16 LDCN | BAGATOR MILL R06B003 2.4 (DROUGHT 1 1 17 LEMON | BELOW CONFLUENCE WITH RIVER SI R06B004 2.4 (DROUGHT 1 1 18 LEMON | BRADLEY PLAYING FIELDS NEWTON R06B00S 9.4 (URBANISATION, CULVERTING 1 1 1 1 1 19 BLATCHFORD STREAM | PERRY FARM R06B006 0.9 1 | 20 BIATCHFORD STREAM | BLATCHFORD R06B007 2.3 | CHINA CLAY DISCHARGE 1 1 1 1 1 21 UGBROOKE STREAM | GAPPAH R06B011 4.2 1 | 22 UGBROOKE STREAM | HIGHER SANDYGATE R06B012 2.3 | CHINA CLAY DISCHARGE 1 1 23 UGBROOKE STREAM | * PRIOR TO RIVER TEIGN R06B013 1.8 | CHINA CLAY DISCHARGE 1 1 1 1 1 27 LTVERTON BROOK | VENTIFORD BRIDGE R06B050 8.8 IPISH FARM EFFLUENT 1 1 1 1 1 28 BOVEY | BLACKALLER NORTH BOVEY R06D001 9.6 | SEWAGE TREATMENT WORKS 1 1 30 BOVEY | LITTLE BOVEY R06D003 6.5 1 1 1 1 | 32 BECKA BROOK | NEW BRIDGE R06D010 3.9 (ROAD RUN-OFF, DROUGHT 1 1 1 1 1 33 WRAY BROOK | CASELY COURT R06D008 7.5 |SEPTIC TANKS, DROUGHT 1 1 34 WRAY BROOK | KNOWLE R06D011 2.7 | SEWAGE TREATEMENT WORKS 1 1 1 1 KATE BROOK | CHUDLEIGH R06C055 3.6 1 35 |FISH FARM DISCHARGE 1 1 1 10.11 Appendix BRAMBLE BROOK 1 36 | PRIOR TO RIVER TEIGN R06C011 6.4 (DROUGHT 1 1 1 1 1 37 BEADON BROOK | TRENCHFORD RESERVOIR R06C050 0.8 I 1 36 BEADON BROOK | T e r m FORD HOUSE R06C009 0.2 | IMPOUNDMENT, UP-STREAM ABSTRACTIONS 1 1 1 1 1 46 SOWTON BROOK | SOWTON BRIDGE R06C015 6.1 |DROUGHT, UP-STREAM ABSTRACTIONS 1 1 1 1 1 47 REEDY BROOK | REEDY BRIDGE R06C054 4.7 (DROUGHT 1 1 1 1 NATIONAL RIVERS AUTHORITY - SOUTH WEST REGION IDENTIFICATION OF POSSIBLE CAUSES OF NON-COMPLIANCE WITH RQO CATCHMENT : TEIGN (06)

* = WORK ALREADY IN RAND

|1990 Map{River | Reach upstream of | User | Reach |Possible causes of non-compliance j |Position| 1 j Referencej Length 1 1 | Number | 1 | Number j Oca) 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 | 48 |SC0TLEY BROOK | CLIFFORD BARTON | R06C057 | 5.3 (DROUGHT, ENGINEERING WORKS, CATCHMENT GEOLOGY | 1 1 1 1 1 1 . 1 | 49 |FINGLE BROOK | FINGLE BRIDGE | R06C053 | 7.0 |SEWAGE TREATMENT WORKS, ENGINEERING WORKS, CATCHMENT GEOLOGY | 1 1 1 1 1 1 1 | 50 |BLACKATON BROOK | CHAPPLE | R06C052 | 7.5 (PRIVATE DISCHARGES | 1 1 1 1 1 1 1 pedx 10.11 Appendix