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Western Region - Drinking Water Inspectorate - Defra

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<strong>Drinking</strong> water<br />

2011<br />

Public water supplies in the<br />

<strong>Western</strong> region of England<br />

July 2012<br />

A report by the Chief Inspector of <strong>Drinking</strong> <strong>Water</strong>


W estern re gion<br />

<strong>Drinking</strong> water 2011<br />

<strong>Western</strong> region of England<br />

1


Dri nking water 20 11<br />

Published by<br />

<strong>Drinking</strong> W ater <strong>Inspectorate</strong><br />

Area 4a<br />

Ergon House<br />

Horseferry Road<br />

London<br />

SW 1P 2AL<br />

Tel: 0300 068 6400<br />

W ebsite: http://www.dwi.gov.uk<br />

© Crown Copyright 2012<br />

ISBN: 978-1-905852-64-2<br />

Copyright in the typographical arrangement and design rests with the Crown.<br />

This publication (excluding the logo) may be reproduced free of charge in any<br />

format or medium provided that it is reproduced accurately and not used in a<br />

misleading context. The material must be acknowledged as Crown copyright with<br />

the title and source of the publication specified.<br />

2


W estern re gion<br />

Contents<br />

Overview of drinking water quality in the region 4<br />

<strong>Water</strong> supply arrangements 9<br />

<strong>Drinking</strong> water quality testing 11<br />

<strong>Drinking</strong> water quality results 12<br />

Microbiological quality 12<br />

Chemical quality 21<br />

Maintaining water quality in distribution 32<br />

Maintaining water quality at the tap 36<br />

<strong>Drinking</strong> water quality events 41<br />

Technical audit activity 44<br />

Annex 1: Further sources of information 50<br />

Annex 2: Glossary and description of standards 51<br />

Annex 3: <strong>Drinking</strong> water quality events in the region 64<br />

Annex 4: Planned drinking water quality improvements 72<br />

Annex 5: Competition in the water industry 75<br />

Annex 6: <strong>Water</strong> company indices 77<br />

Annex 7: Information relating to public water supplies 84<br />

published by the <strong>Inspectorate</strong> in 2011<br />

Annex 8: Distribution of private water supplies 86<br />

<strong>Drinking</strong> <strong>Water</strong> 2011 is the annual report of the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong> and<br />

comprises reports covering public and private water supplies.<br />

Public supplies – This part describes drinking water quality in the <strong>Western</strong> region. The<br />

<strong>Inspectorate</strong> also publis hes a series of companion reports for othe r regions of England<br />

(Central and Eastern, Northern, and London and South East regions) and a separate<br />

report for Wales.<br />

Private supplies – A summary of information on private water supplies is reported for<br />

England and Wales.<br />

All parts are available on the <strong>Inspectorate</strong>’s websit e www.dwi.gov.uk<br />

3


Percentage of tests failing<br />

Dri nking water 20 11<br />

Overview of drinking water quality in the region<br />

<strong>Drinking</strong> <strong>Water</strong> 2011 is published as a series of seven reports, five of<br />

which cover public water supplies and two describe private water supplies.<br />

Each report presents information about drinking water quality for the<br />

calendar year of 2011.<br />

The improving national trend in the quality of public water supplies since<br />

1990 is shown in Figure 1. Compliance with the standards in the EU<br />

<strong>Drinking</strong> <strong>Water</strong> Directive now stands at 9 9.96% for public supplies in<br />

England, however, the results for private water supplies in England are of<br />

concern with 7.2% of tests failing to meet the standards in 2011.<br />

Figure 1: Percentage of tests from public and private supplies failing<br />

the drinking water standards (England and Wales combined)<br />

10<br />

9<br />

8<br />

7<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

0<br />

England and Wales public supplies England and Wales private supplies (data not available before 2010)<br />

Footnote:<br />

Public supp lies: Perc e ntag e of tests failing is calcul a ted for sam ples taken in zones .<br />

Private sup plies: Perc entage of tests failing is calcul ated for all sam ples .<br />

At the end of 2010, the regulations covering both public and private water<br />

supplies were changed to address deficiencies in the transposition of the<br />

<strong>Drinking</strong> <strong>Water</strong> Directive into national law . The infraction case by the<br />

European Commission was subsequently closed in September 2011. The<br />

purpose of the 2010 amendments to the regulations was twofold: to make<br />

enforcement mandatory for failures of standards in public buildings and to<br />

make clearer the duty to minimise disinfection by -products.<br />

4


W estern re gion<br />

In 2011, across 29 companies, over 43,000 tests were carried out at public<br />

buildings out of which 35 tests failed to comply with one or more of the<br />

standards or indicator parameter values (Coliform bacteria, E.coli, iron,<br />

lead, nitrite, taste, odour and turbidity). In the W estern region failures that<br />

arose due to arrangements in the public buildings are described in the<br />

Maintaining water quality at the tap section.<br />

In relation to how well companies are complying with the requirement to<br />

keep disinfection by-products as low as possible, in 2011 across England,<br />

the annual average figure for total trihalomethanes was 9.9µg/l in<br />

groundwater supplies and 27.9µg/l in surface water supplies compared to<br />

the standard of 100µg/l. For more information about trihalomethanes in the<br />

<strong>Western</strong> region see the Chemical quality – Disinfection by-products<br />

section.<br />

This report describes the key facts about the quality of public water in<br />

the <strong>Western</strong> region, which is served by seven water companies delivering<br />

water supplies to over four and a half million consumers. In addition local<br />

authorities have identified 14,858 private water supplies in the <strong>Western</strong><br />

region. Details of the quality of these private supplies can be found in the<br />

separate report <strong>Drinking</strong> <strong>Water</strong> 2011 – Private water supplies in England.<br />

Annex 8 of this report maps the location of private supplies reported to the<br />

EU under the <strong>Drinking</strong> <strong>Water</strong> Directive. It also shows small shared supplies<br />

used only for domestic purposes.<br />

5


Dri nking water 20 11<br />

The results of testing of public supplies in 2011 demonstrated that the<br />

overall quality of drinking water in the <strong>Western</strong> region was good. The<br />

figure for compliance with drinking water standards at consumers’ taps<br />

was 99.97%, the same as reported in 2010 and above the industry<br />

average. This figure is made up of the results of all the tests for 39<br />

parameters with European or national standards. Across the region , all<br />

tests for 29 out of 39 parameters gave satisfactory results. Failures were<br />

reported for E.coli, odour, taste, aluminium, iron, manganese, lead,<br />

turbidity, nickel, and one pesticide (Mecoprop (MCPP)).<br />

Table 2 puts the failures into context with respect t o the other regions of<br />

England and W ales.<br />

6


W estern re gion<br />

Table 2: Parameters exhibiting one or more failure of a standard<br />

England<br />

Parameters<br />

Wales<br />

Central<br />

and<br />

London<br />

and South<br />

Northern<br />

<strong>Western</strong><br />

Eastern<br />

East<br />

region<br />

region<br />

region<br />

region<br />

Microbiological parameters<br />

E.coli <br />

Enterococci<br />

<br />

Physical/chemical parameters<br />

Odour <br />

Taste <br />

Aluminium <br />

Iron <br />

Manganese <br />

Lead <br />

Turbidity <br />

Nickel <br />

Benzo(a)pyrene <br />

Copper <br />

Nitrite<br />

<br />

Bromate<br />

<br />

Chlortoluron 1 <br />

Clopyralid 1<br />

<br />

Glyphosate 1<br />

<br />

MCPA 1<br />

<br />

MCPP 1 <br />

Metaldehyde 1 <br />

Propyzam ide 1<br />

<br />

1 These parameters are pesticides.<br />

When the <strong>Western</strong> region is judged by the <strong>Inspectorate</strong>’s four indices of<br />

water quality performance, which look in turn at water treatment (covered<br />

by two indices, process control and disinfection), service reservoir integrity<br />

and network maintenance, the changes in 2011 were improvement in the<br />

figures for process control (>99.99%) and disinfection (99.99%). Figures<br />

for service reservoir integrity (99.97%) remained the same and the network<br />

maintenance figure (99.82%) was lower than last year. Nevertheless , in<br />

this region all indices were at or above the industry figure except for the<br />

7


Dri nking water 20 11<br />

network maintenance index. Individual water company figures are reported<br />

in Annex 6.<br />

Across the region, in 2011, there were slightly more events affecting water<br />

quality overall (46 compared to 42 in 2010). Only around one-quarter of<br />

these were of a type that necessitated a detailed investigation by an<br />

inspector and this compares favourably with the industry overall. The<br />

number of each event type can be found in the <strong>Drinking</strong> <strong>Water</strong> Quality<br />

Events section together with learning points from other event assessments<br />

by the <strong>Inspectorate</strong>. In 2011, there were no serious events affecting<br />

consumers in the <strong>Western</strong> region.<br />

Turning to planned improvements in drinking water quality in the region,<br />

in 2011 the <strong>Inspectorate</strong> confirmed the need for additional work at Empool<br />

works (WSX) and Thruxton and Compton boreholes (CHO). Companies in<br />

the region are committed to complete the work summarised in Annex 4<br />

during the AMP5 period (2010 –2015).<br />

In 2011, the <strong>Inspectorate</strong> provided the water industry with advice and<br />

guidance on nine topics to enable companies to comply with the drinking<br />

water regulations. In addition, nine research projects were published by<br />

the <strong>Inspectorate</strong> to support the industr y in carrying out regulatory risk<br />

assessments (see Annex 7).<br />

8


W estern re gion<br />

<strong>Water</strong> supply arrangements<br />

Seven water companies supply drinking water in the <strong>Western</strong> region:<br />

Bristol <strong>Water</strong> (BRL), Cholderton and District W ater (CHO), Se mbcorp<br />

Bournemouth <strong>Water</strong> (SBW), South West <strong>Water</strong> (SWT) and Wessex <strong>Water</strong><br />

(WSX). Two inset appointments, Veolia <strong>Water</strong> Projects (VWP) and<br />

SSE <strong>Water</strong> (SSE) supply consumers in the Tidworth area and Old Sarum,<br />

Salisbury respectively.<br />

Figure 3: Map illustrating sources of drinking water by zone across<br />

the region<br />

Much of the water in the region is derived from surface water (7 1%)<br />

abstracted from rivers such as the Severn, the Hampshire Avon, Dart, Exe,<br />

Fowey, Tamar and the Dorset Stour. There is a major transfer of water into<br />

the region via the river Severn from reservoirs in Wales that provide half<br />

the daily supply for English consumers in the Bristol <strong>Water</strong> area.<br />

Additionally, the upland areas of Bodmin Moor, Dartmoor, Exmoor and the<br />

Mendips are important catchments for water resources in the region.<br />

Surface water is drawn from many reservoirs, including Chew Valley Lake,<br />

Clatworthy, Colliford, Roadford and W imbleball. Groundwater provides a<br />

valuable resource (27%) in the region, with many boreholes drawing water<br />

from the chalk aquifer of the Wessex basin. The Permian a nd Triassic<br />

9


Dri nking water 20 11<br />

sandstone aquifer in the Otter Valley is also an important groundwater<br />

source for East Devon. Cholderton and District <strong>Water</strong>, relies exclusively<br />

on the chalk aquifer of the Wessex basin. Across the region, a small<br />

proportion of water supplies ( 2%) can be drawn from either surface or<br />

groundwater sources.<br />

Private water supplies in the region are widely distributed across the<br />

area with large concentrations in the Dartmoor and Exmoor regions .<br />

These private supplies are more reliant on groundwater (63%) than the<br />

public supplies in the area (27%).<br />

Summary facts about the drinking water supply infrastructure of<br />

the region are given in Table 4 with outline geographical and<br />

demographic information.<br />

Table 4: Key facts about public and private water supply arrangements<br />

in the <strong>Western</strong> region<br />

Public supplies<br />

Population supplied<br />

<strong>Water</strong> supplied (l/day)<br />

Abstraction points<br />

Treatment works<br />

Service reservoirs<br />

<strong>Water</strong> supply zones<br />

Length of mains pipe (km)<br />

4,529,770<br />

1,224 million<br />

348<br />

155<br />

809<br />

188<br />

36,110<br />

Private supplies<br />

Population supplied<br />

<strong>Water</strong> supplied (l/day)<br />

Approximate number of private<br />

water supplies<br />

Total number of local authorities<br />

66,317<br />

40 million<br />

14,858<br />

36<br />

<strong>Water</strong> composition<br />

Surface sources<br />

Groundwater sources<br />

Mixed sources<br />

71%<br />

27%<br />

2%<br />

<strong>Water</strong> composition<br />

Surface influenced supplies<br />

Groundwater sources<br />

Rainwater<br />

37%<br />

63%<br />


W estern re gion<br />

<strong>Drinking</strong> water quality testing<br />

Throughout 2011, water companies sampled drinking water across the<br />

region to test for compliance with the drinking water regulations. More than<br />

one-third (34%) of the tests were carried out on drinking water drawn from<br />

consumers’ taps selected at random. For monitoring purposes, company<br />

water supply areas are divided into zones . Sampling in zones at<br />

consumers’ taps is risk based with the number of tests being higher in<br />

zones with a large population (maximum 100,000). Other sample locations<br />

are water treatment works and treated water (service) reservoirs.<br />

Collectively, the seven water companies carried out a total of 614,422<br />

tests during 2011. Only 131 of these tests failed to meet the standards<br />

set down in the regulations or exceeded screening values.<br />

Table 5: Number of tests carried out by companies in the region<br />

Place of sampling<br />

Number<br />

Company<br />

<strong>Water</strong><br />

treatment<br />

works<br />

Service<br />

reservoirs<br />

Consumers’<br />

taps (zones)<br />

of tests<br />

per<br />

company<br />

Estimate of<br />

population<br />

Bristol W ater<br />

26,921<br />

(17)<br />

50,419<br />

(165)<br />

49,312<br />

(52)<br />

126,652 1,155,305<br />

Cholderton<br />

and District<br />

W ater<br />

737<br />

(2)<br />

312<br />

(1)<br />

370<br />

(1)<br />

1,419 2,100<br />

Sembcorp<br />

Bournemouth<br />

W ater<br />

14,170<br />

(7)<br />

6,182<br />

(20)<br />

17,851<br />

(10)<br />

38,203 430,000<br />

South W est<br />

W ater<br />

48,521<br />

(31)<br />

85,297<br />

(282)<br />

74,139<br />

(32)<br />

207,957 1,696,000<br />

SSE W ater<br />

0<br />

(0)<br />

0<br />

(0)<br />

389<br />

(1)<br />

389 685<br />

Veolia W ater<br />

Projects Ltd<br />

1,252<br />

(2)<br />

1,560<br />

(6)<br />

652<br />

(1)<br />

3,464 8,000<br />

W essex W ater<br />

75,315<br />

(85)<br />

92,907<br />

(299)<br />

68,116<br />

(91)<br />

236,338 1,237,680<br />

<strong>Region</strong><br />

overall<br />

166,916<br />

(144)<br />

236,677<br />

(773)<br />

210,829<br />

(188)<br />

614,422 4,529,770<br />

Num bers in brackets reflec t the num ber of wo rk s , reser voi rs or zo nes op er ated by that com pany in<br />

the re gion in 201 1. Som e com panies are perm itted to c arr y out som e tests on sam ples taken from<br />

s uppl y po ints rat he r than f r om consum ers ’ t aps.<br />

11


Dri nking water 20 11<br />

The regulations require companies to test for specified parameters at<br />

prescribed frequencies. Most of the testing is f or parameters with<br />

European or national standards, however, water companies are also<br />

required by the regulations to test for other parameters, such as<br />

ammonium, sulphate and colony counts.<br />

A summary of the results of testing by compan ies for each parameter can<br />

be found on the <strong>Inspectorate</strong>’s website (www.dwi.gov.uk) and on the CD<br />

accompanying this report. Additionally, the <strong>Inspectorate</strong> publishes<br />

annually, the performance indices for each company in Annex 6.<br />

<strong>Drinking</strong> water quality results<br />

The key water quality results for the <strong>Western</strong> region are presented in two<br />

tables, one showing the results for microbiological parameters (Table 6),<br />

the other dealing with chemical and physical parameters (Table 8). The<br />

microbiological quality of water is discussed first. Companies report all the<br />

results of the tests on a monthly basis to the <strong>Inspectorate</strong>. Also, tables in<br />

Annex 6 describe the drinking water quality performance indices of each<br />

company supplying in the region.<br />

Microbiological quality<br />

To protect public health, microbiological standards have to be met at each<br />

individual treatment works and service reservoir. The significance of the<br />

individual test results for each microbiological parameter at each location<br />

varies and a single positive result cannot be interpreted without other<br />

information. All companies are expected to follow best practice as set<br />

out in The Microbiology of <strong>Drinking</strong> <strong>Water</strong> published by the Standing<br />

Committee of Analysts (SCA) which can be found by visiting the<br />

Environment Agency’s website (www.environment -agency.gov.uk).<br />

12


W estern re gion<br />

Table 6: Microbiological tests<br />

The number of tests performed and the number of tests not m eeting<br />

the standard<br />

Parameter<br />

Current<br />

standard<br />

<strong>Water</strong> leaving water treatment works<br />

Total<br />

number<br />

of tests<br />

Number of<br />

tests not<br />

meeting<br />

the<br />

standard<br />

E.coli 0/100ml 23,464 2 SW T (2)<br />

Coliform bacteria 0/100ml 23,464 9<br />

Clostridium<br />

perfringens<br />

0/100ml 5,621 5<br />

Turbidity 1 1NTU 23,512 5<br />

<strong>Water</strong> leaving service reservoirs<br />

Additional<br />

information<br />

BRL (1), SBW (2),<br />

SW T (5), W SX (1)<br />

BRL (1), SBW (1),<br />

SW T (3),<br />

BRL (1), SBW (2),<br />

SW T (2),<br />

E.coli 0/100ml 39,522 3 SW T (2), W SX (1)<br />

Coliform bacteria<br />

0/100ml in<br />

95% of tests<br />

at each<br />

reservoir<br />

<strong>Water</strong> sampled at consumers’ taps<br />

39,522 20<br />

E.coli 0/100ml 12,582 6<br />

Enterococci 0/100ml 1,466 0<br />

BRL (4), SW T (6),<br />

W SX (10)<br />

All reservoirs in<br />

the region meet<br />

the 95%<br />

compliance rule<br />

BRL (1),SBW (3),<br />

SW T (1), W SX (1)<br />

1 Turbidity is a critical control parameter for water treatment and disinfection.<br />

E.coli at works and service reservoirs<br />

In 2011, out of a total of 23,464 tests at works, E.coli was detected in two<br />

samples (2 SWT) and there were just three E.coli failures (2 SWT, 1 WSX)<br />

out of a total of 39,522 tests at service reservoirs . This is an improvement<br />

compared to 2010 when there were three detections of E.coli at works and<br />

the same number in service reservoirs.<br />

On detecting E.coli, companies are required to act promptly to pro tect<br />

public health. Their immediate response when finding E.coli at a works or<br />

service reservoir is to sample again, and more widely, to confirm that<br />

water being received by consumers is safe. In 2011, these additional tests<br />

gave satisfactory results in all cases and there were no subsequent E.coli<br />

failures.<br />

E.coli was detected in a sample taken from Dotton works (near Sidmouth)<br />

in June and also in a sample taken on the same day from Blackhill service<br />

reservoir, a reservoir fed from Dotton works via Capel Lane service<br />

reservoir. In both cases the analyst recorded the presence of brown<br />

13


Dri nking water 20 11<br />

particulate matter in the samples. In response, South West <strong>Water</strong> checked<br />

treatment performance at the works, including disinfection, and externally<br />

inspected both reservoirs. Nothing untoward was found, but the residual<br />

chlorine level in water leaving Dotton works was increased. At that time<br />

the company believed that the failures were linked to contamination of the<br />

sample bottles, however, in September, after a further coliform failure at<br />

Dotton works, the company found a number of significant defects,<br />

including leaks in the roof of the treated water tank and this was removed<br />

from service until remedial works were completed. The <strong>Inspectorate</strong> was<br />

disappointed to note that the company failed to identify these defects when<br />

investigating the earlier E.coli failures and reminded the company of the<br />

need for investigations to be wide ranging and comprehensive. A new<br />

membrane was applied to the roof of the tank which was flood tested on<br />

5 December 2011 and the tank was subsequently returned to service.<br />

In December 2011, E.coli was detected in a sample collected from St Cleer<br />

works (near Liskeard) and also on the same day in a sample taken from<br />

Bodelva service reservoir. The reservoir is not hydraulically linked to St.<br />

Cleer, but instead receives water from Restormel works via Charkhill<br />

service reservoir. Follow-up tests and enhanced monitoring by South West<br />

<strong>Water</strong> were all satisfactory. In early 2012 , the company took Bodelva<br />

service reservoir out of service for inspection and cleaning and similar<br />

action was scheduled for the treated water tank at St Cleer commencing<br />

mid April 2012 after essential enabling works (pump replacement at<br />

Bastreet works).<br />

During October, a sample collected by Wessex <strong>Water</strong> from Two Ash<br />

service reservoir (near Chard) contained E.coli and coliforms. Two Ash<br />

service reservoir had been inspected and cleaned in February 2010 when<br />

the structure was deemed satisfactory. The company implemented<br />

enhanced monitoring and detected coliforms again in November , triggering<br />

an external inspection which flagged concerns about the sampling facilities<br />

as the kiosk was sited next to a hedge with overhanging vegetation with out<br />

protection from the elements and passing cars using the road. Wessex<br />

<strong>Water</strong> upgraded the sampling facilities in December .<br />

Companies are reminded of their regulatory duty to ensure samples are<br />

representative of water in supply and the need to pay closer attention to<br />

all aspects of sampling (facilities and staff).<br />

14


W estern re gion<br />

Table 7: Detection of E.coli and Enterococci at treatment works,<br />

service reservoirs and consumers’ taps<br />

Company<br />

E.coli in<br />

water<br />

leaving<br />

treatment<br />

works<br />

E.coli in<br />

water<br />

leaving<br />

service<br />

reservoirs<br />

E.coli at<br />

consumers’<br />

taps<br />

Enterococci<br />

at<br />

consumers’<br />

taps<br />

Bristol W ater 0 – 3,823 0 – 8,402 1 – 3,120 0 – 387<br />

Cholderton and<br />

District W ater<br />

Sembcorp<br />

Bournemouth<br />

W ater<br />

0 – 103 0 – 52 0 – 12 0 – 4<br />

0 – 1,772 0 – 1,031 3 – 1,106 0 – 81<br />

South W est W ater 2 – 6,887 2 – 14,232 1 – 4,452 0 – 380<br />

SSE W ater 0 – 0 0 – 0 0 – 13 0 – 4<br />

Veolia W ater<br />

Projects Ltd<br />

0 – 206 0 – 312 0 – 24 0 – 8<br />

W essex W ater 0 – 10,673 1 – 15,493 1 – 3,855 0 – 602<br />

<strong>Region</strong> overall 2 – 23,464 3 – 39,522 6 – 12,582 0 – 1,466<br />

Note: Results ar e sho wn as the num ber of positive tests – the total num b er of tests.<br />

Coliform bacteria at works<br />

Testing for coliform bacteria gives reassurance that water entering the<br />

supply was treated adequately to remove bacterial and viral pathogens.<br />

Repeated occurrences of coliform bacteria in samples from the same<br />

works in one year are thus of concern and require action to be taken.<br />

In 2011, this situation occurred at three sites: Tottiford works, Dotton<br />

works (SWT) and Alderney works (SBW). Both sites failed the coliform<br />

standard on two occasions during 2011.<br />

There were two detections of coliforms at Dotton works (near Sidmouth),<br />

operated by South West <strong>Water</strong> during June and September (see the E. coli<br />

at works section).<br />

Coliforms were reported in samples from Tottiford works near Bovey<br />

Tracey in successive months (May and June). South West <strong>Water</strong> found and<br />

fixed a leaking sample tap and scheduled an internal inspection of the<br />

west cell of the treated water tank for early July. The inspection revealed<br />

15


Dri nking water 20 11<br />

ingress of rainwater in the northwest corner of the tank, pooling of wa ter in<br />

a drainage channel and the roof membrane was damaged. Repairs to the<br />

west cell of the treated water tank were completed on 26 July and the tank<br />

returned to supply a week later following cleaning and sampling. Due to<br />

work at the site to construct new rapid gravity filters, the east cell of the<br />

tank could not be taken out of supply immediately. The repairs to this cell,<br />

which included the application of a liquid membrane to the jointed areas of<br />

the roof slab, were carried out in February 2012 and the e ast cell was back<br />

in service in mid-March.<br />

During February 2012, there was an event at Tottiford works when a<br />

sample result of >100 E.coli was reported. The east cell of the treated<br />

water tank was out of use at this time and treatment was operating<br />

normally. South West <strong>Water</strong> found particulate matter in the sample bottle<br />

and concluded the sample was not representative of water entering supply.<br />

The <strong>Inspectorate</strong> has noted that it is not uncommon for failures to occur<br />

at sites where assets are being refurbishe d or modified and companies<br />

should take risks associated with such activities into account when<br />

investigating failures.<br />

In September, Wessex <strong>Water</strong> detected coliforms at Clarendon Park works<br />

(near Salisbury). The company found that the sample tap was corroded<br />

and there was a leak on the sample line . After replacement of the tap the<br />

non-return valve was found to be faulty and further repairs were carried<br />

out. The <strong>Inspectorate</strong> expects companies to have in place a proactive<br />

programme of maintenance of sampling facilities.<br />

During 2011 there were coliform failures at Alderney works operated by<br />

Sembcorp Bournemouth <strong>Water</strong>. Following the first failure in July the<br />

<strong>Inspectorate</strong> requested additional data and observed a rise in raw water<br />

coliform numbers in the preceding week. The company attributed the<br />

second failure to sample tap defects. The <strong>Inspectorate</strong> reported in 2010,<br />

on serious integrity issues at this site where the filters are situated above<br />

the contact tank. The company had failed to make a link between failure s<br />

in the downstream network with known integrity issues at the works. Again ,<br />

in 2011, there were coliform failures in consumer tap samples in zones fed<br />

by this works (see the Maintaining water quality at the tap section). The<br />

<strong>Inspectorate</strong> remains concerned about the company’s approach to the<br />

investigation of failures, which appears narrow in scope and lack s analysis<br />

of quality and asset condition data.<br />

During December, coliforms were detected at Banwell works (near W eston -<br />

Super-Mare). Bristol <strong>Water</strong> took follow-up samples from downstream<br />

reservoirs, but not from properties fed directly from the works. Companies<br />

are reminded that it is a regulatory duty to carry out comprehensive<br />

sampling and analysis in response to adverse results. Enforcement action<br />

16


W estern re gion<br />

will be taken if further evidence demonstrates that Bristol <strong>Water</strong> is not<br />

complying with Regulation 10.<br />

The <strong>Inspectorate</strong> has noted that coliform bacteria were found in nine<br />

(1 BRL, 2 SBW, 5 SWT, 1 WSX) samples from treatment works in the<br />

<strong>Western</strong> region during the year and this information will be taken into<br />

account during the <strong>Inspectorate</strong>’s risk -based programme of technical audit.<br />

Clostridium perfringens<br />

This organism is a spore-forming bacterium that is exceptionally resistant<br />

to unfavourable conditions in the water environment, such as extremes of<br />

temperature and pH, and disinfection processes such as chlorination and<br />

ultraviolet light. It is a normal component of the intestinal flora of up to<br />

35% of humans and other warm-blooded animals. These characteristics<br />

make it a useful indicator of either intermittent or historical faecal<br />

contamination of a groundwater source or the performance of a surface<br />

water filtration plant. The detection of any Clostridium perfringens should<br />

trigger an investigation by the water company.<br />

In 2011, out of 5,621 tests taken across the W estern region, five did not<br />

meet the specified value (1 BRL, 1 SBW, 3 SWT).<br />

South West <strong>Water</strong> detected Clostridium perfringens in samples collected<br />

from Allers works (February), Pynes works (June) and Drift works<br />

(October). The company implemented enhanced monitoring at each site.<br />

To date nothing untoward with treatment performance has been found.<br />

The <strong>Inspectorate</strong> expects the company to review and update the relevant<br />

regulatory risk assessments to record this information, particularly the use<br />

of monitoring as the control measure .<br />

In June, Bristol W ater identified Clostridium perfringens in a sample taken<br />

from Littleton works (near Bristol). Clostridium perfringens was recorded<br />

in raw water samples before its occurrence in the treated water sample;<br />

however, this did not result in a review of the regulatory risk assessment.<br />

This was not the only case in 2011 when the <strong>Inspectorate</strong> had reason to be<br />

critical of Bristol <strong>Water</strong>’s approach (see the Coliforms at works section).<br />

Sembcorp Bournemouth W ater reported Clostridium perfringens in a<br />

consumer tap sample collected from the Alderney North supply zone. This<br />

sample also contained E.coli and coliforms. A fittings inspection identified<br />

a number of irregularities at the property including an outside tap with an<br />

attached hose. The integrated non-return valve had failed allowing<br />

backflow and a sample taken from the hose contained high levels of<br />

coliforms, E.coli and Clostridium perfringens. A follow-up sample after<br />

these faults had been rectified was satisfactory. This is important evidence<br />

of the risk from hoses on outside taps where effective backflow protection<br />

17


Dri nking water 20 11<br />

is absent and the <strong>Inspectorate</strong> considers it should be shared more widely<br />

to assist the industry and the <strong>Water</strong> Regulations Advisory Service in<br />

dealing with certain groups of property owner who object to enforcement<br />

of the backflow protection element of the fittings regulations asserting that<br />

backflow risks are not proven and the remedies burdensome.<br />

Turbidity at works<br />

Turbidity is a measure of how much light can pass through water and<br />

indicates the condition or ‘cloudiness’ of water. Turbidity is caused by<br />

particles suspended in the water and is an important critical control<br />

measure of the performance of disinfection. Turbidity is measured at two<br />

points in the water supply chain, at treatment works where a value of<br />

1NTU applies and at consumers ’ taps where the standard of 4NTU applies.<br />

The following discussion focuses on the results of sa mples taken at<br />

treatment works.<br />

The number of turbidity failures across the region i n 2011 was five (1 BRL,<br />

2 SBW, 2 SWT) and this continues the improvement in previous years<br />

(17 in 2009, 6 in 2010).<br />

In June, a sample taken from Knapp Mill works (near Bournemouth)<br />

exhibited a value of >1NTU. Sembcorp Bournemouth W ater had taken<br />

duplicate samples and the other sample gave a satisfactory result of<br />

1NTU at Alderney works<br />

in December was limited to checks of on -site monitors and duplicate<br />

sampling (in this case the duplicate sampl e was lost so there was no<br />

validation evidence). Both of these situations lend further weight to the<br />

<strong>Inspectorate</strong>’s concerns about the narrow focus of investigations carried<br />

out by Sembcorp Bournemouth <strong>Water</strong> (see the Coliforms at works section).<br />

At Banwell works (near Weston-Super-Mare), Bristol W ater attributed a<br />

turbidity value of >1NTU in August to flow changes following maintenance<br />

activities on slow sand filters. Consequential changes in flow rate through<br />

the combined outlet chamber appear to have disturbed sediment at this<br />

location as there was no contemporaneous increase in turbidity at the<br />

outlet of each of the individual slow sand filters.<br />

Following a turbidity value of >1NTU in a sample from Stithians works<br />

(near Falmouth) in January, South West <strong>Water</strong> identified a link to issues<br />

with the control system settings on start up of the works following a power<br />

outage caused by a lightning strike. There was a loss of control of pH<br />

18


W estern re gion<br />

correction and the turbidity was caused by lime particles. Changes to<br />

control system settings since should prevent a recurrence.<br />

At Crownhill works (near Plymouth), South West <strong>Water</strong> linked a turbidity<br />

value of >1NTU in May to the closure of the outlet valve on the 36” outlet<br />

main of the treated water reservoir to facilitate drain down and cleaning<br />

of this asset. The sample had been taken when the reservoir was not in<br />

service, therefore it was not representative of water entering supply.<br />

Companies need to ensure that sampling staff are informed about the<br />

operational status of assets so that compliance samples are collected only<br />

when it is appropriate to do so.<br />

Coliform bacteria at service reservoirs<br />

Testing for coliform bacteria gives reassurance that the quality of water<br />

held at these strategic points in the distribution system is adequately<br />

maintained. The national standard requires that at least 95% of no less<br />

than 50 samples collected from each service reservoir throughout one year<br />

are free from all coliform bacteria. In 2011, all service reservoirs (including<br />

water towers) in the region met the standard.<br />

Coliform failures reported by South West <strong>Water</strong> at Bodelv a and Blackhill<br />

service reservoir and at Wessex <strong>Water</strong>’s Two Ash service reservoir are<br />

discussed in the section on E.coli at works and service reservoirs.<br />

In response to single coliform failures at Strete reservoir (December) and<br />

Stanborough reservoir (November) , South West <strong>Water</strong> drained and<br />

inspected these reservoirs. Nothing untoward was found , however,<br />

following a coliform failure at Yawl service reservoir (near Lyme Re gis)<br />

a flood test revealed the potential for ingress through roof hatches.<br />

Similarly, at Bindown reservoir (near Looe) in September , ingress as a<br />

consequence of roof ponding was identified as a risk requiring mitigation<br />

by a spray-on roof membrane. The company approach has involved<br />

keeping the reservoir out of service until all remedial works are complete.<br />

The <strong>Inspectorate</strong> is pleased to note this evidence of a proactive service<br />

reservoir risk management strategy by South W est <strong>Water</strong>.<br />

Wessex <strong>Water</strong> also displayed a proactive risk management approach to<br />

reservoir maintenance in 2011. During September , a sample taken by<br />

Wessex <strong>Water</strong> at Charlton Horethorne service reservoir (near Wincanton)<br />

failed for coliforms. A range of issues were found at the site: inadequat e<br />

sample facilities, low turnover and chlorine residual concentrations.<br />

Abandonment of this site was previously planned for January 2012 and<br />

this action was completed in February 2012. A coliform failure at Cockey<br />

Down service reservoir (near Salisbury) i n September led to an internal<br />

19


Dri nking water 20 11<br />

inspection in late October. No integrity issues were revealed. The sample<br />

line, tap and kiosk have been replaced.<br />

During 2011, Bristol <strong>Water</strong> reported coliform failures at the following<br />

reservoirs: Hutton (near Weston-Super-Mare), Tetbury, Tolldown (near<br />

Gloucester) and Marshfield (near Bath). The <strong>Inspectorate</strong> has noted the<br />

rise in coliform failures from one in 2010 to four in 2011 and further noted<br />

that no cause was found in any of the five investigations. The <strong>Inspectorate</strong><br />

will be closely scrutinising the effectiveness of Bristol <strong>Water</strong>’s service<br />

reservoir maintenance strategy.<br />

The <strong>Inspectorate</strong> has noted that coliform bacteria were found in 20<br />

(4 BRL, 6 SWT, 10 WSX) samples from service reservoirs in the <strong>Western</strong><br />

region during the year and this information will be taken into account in<br />

planning the <strong>Inspectorate</strong>’s risk-based forward programme of technical<br />

audit.<br />

E.coli and Enterococci at consumers’ taps<br />

A total of 12,582 consumers’ taps were tested in 2011 for E.coli and six<br />

were positive (1 BRL, 3 SBW, 1 SWT, 1 WSX). Like E.coli, the presence<br />

of Enterococci is indicative of faecal contamination and neither bacterium<br />

should be found in any sample. In 2011, Enterococci were not detected<br />

in any of the 1,466 samples collected acr oss the <strong>Western</strong> region from<br />

consumers’ taps. There was no indication, from information gathered by<br />

the four water companies, of a faecal contamination event affecting other<br />

properties in these zones.<br />

Samples from three properties in the Alderney North zon e contained E.coli<br />

(May, November and December). Sembcorp Bournemouth <strong>Water</strong> carried<br />

out fittings inspections and found irregularities in each case. These<br />

included a redundant length of pipework under the sink, a connection to<br />

a boiler filling loop, unhygienic anti-splash devices, lack of a non-return<br />

valve fitted to a washing machine (allowing foul water to come back up<br />

through the plug hole and into the sink) and an inoperable non -return valve<br />

on a hose attached to an outside tap. Despite the company’s ef fective use<br />

of fittings inspections to identify plumbing and backflow risks, the<br />

<strong>Inspectorate</strong> has a concern about the pattern of relatively frequent E.coli<br />

failures in this zone given the history of problems at the upstream works<br />

(see the E.coli at works section).<br />

A sample collected from a consumer’s tap in Wessex <strong>Water</strong>’s Allington<br />

zone in November contained E.coli and coliforms. Sequential follow-up<br />

water samples and a fittings inspection all yielded satisfactory results ,<br />

in contrast to the findings of Br istol W ater in relation to a property in the<br />

Filton and Northville zone in September where E.coli and coliforms were<br />

20


W estern re gion<br />

detected. In this case, re-samples on two separate occasions were positive<br />

before and after the tap was cleaned. The tap was loose fitting and<br />

unhygienic, and a fittings inspection found an unapproved hose connection<br />

at the property. Consumers were advised to boil water . South West <strong>Water</strong><br />

issued a notice for corrective action by a property owner following<br />

identification of fittings irregularit ies when investigating an E.coli and<br />

coliform failure in Restormel Central zone during November. The<br />

<strong>Inspectorate</strong> is pleased to note the involvement of fittings inspectors in the<br />

investigation of water quality failures by companies in the <strong>Western</strong> region.<br />

Chemical quality<br />

The drinking water regulations set out the minimum testing requirements<br />

for all chemical and physical parameters. A full summary of the results<br />

of testing by each company, including the results for indicator parameters ,<br />

is provided on the <strong>Inspectorate</strong>’s website and on the CD accompanying<br />

this report.<br />

The following text and Table 8 set out the results for those parameters<br />

where there has been a failure to meet a European or national standard<br />

(mandatory quality standards) and any other para meter of interest. In<br />

addition, at the request of local authorities, the results of testing for<br />

fluoride, iron, lead, manganese, nitrate, nitrite, pesticides and radioactivity<br />

are given. New this year, the <strong>Inspectorate</strong> has also included instances<br />

where residual chlorine results were reported at a level above that<br />

considered desirable on grounds of consumer acceptability (2mg/l).<br />

21


Dri nking water 20 11<br />

Table 8: Chemical and physical parameters<br />

The number of tests performed and the number of tests not meeting<br />

the standard or screening value<br />

Parameter<br />

Aesthetic parameters<br />

Current<br />

standard or<br />

specified<br />

concentration 1<br />

Total<br />

number<br />

of tests<br />

Number of<br />

tests not<br />

meeting<br />

the<br />

standard 4<br />

Additional information<br />

– odour<br />

4,126 5 SWT (1), WSX (4)<br />

No abnormal<br />

change<br />

BRL (1), SWT (1),<br />

– taste 4,098 7<br />

WSX (5)<br />

Aluminium 200μg/l 4,542 1 BRL (1)<br />

Chlorine – residual (free) 2 2mg/l 75,251 2 BRL (1), SWT (1)<br />

Chlorine – residual (total) 2 2mg/l 75,797 11 BRL (3), SWT (8)<br />

Fluoride 1.5mg/l 1,186 0<br />

Iron 200μg/l 4,275 22<br />

Lead (current standard) 25μg/l 1,476 2 WSX (2)<br />

Lead (future standard) 10μg/l 1,476 12<br />

Manganese 50μg/l 4,272 3<br />

Nickel 20μg/l 1,473 1 BRL (1)<br />

Nitrate 50mg/l 1,794 0<br />

Nitrite 0.5mg/l 1,796 0<br />

Pesticides – total 0.5μg/l 1,367 0<br />

Pesticide – individual 3 0.1μg/l 39,821 2<br />

pH (Hydrogen ion) 6.5 – 9.5 5,117 5<br />

Radioactivity<br />

Gross alpha 0.1Bq/l 688 2 SWT (2)<br />

Gross beta 1.0Bq/l 688 0<br />

Tritium 100Bq/l 111 0<br />

BRL (16), SBW (2),<br />

SWT (1), WSX (3)<br />

BRL (6), SWT (1),<br />

WSX (5)<br />

BRL (1), SWT (1),<br />

WSX (1)<br />

MCPP (Mecoprop)<br />

SWT (2)<br />

BRL (1), SWT (2),<br />

WSX (2)<br />

Turbidity (at consumers’<br />

taps)<br />

4NTU 5,056 1 BRL (1)<br />

Notes:<br />

1 For comparison, 1mg/l is one part in a million, 1μg/l is one part in a thousand million.<br />

2 The value of 2mg/l is a consumer acceptability value set by the <strong>Inspectorate</strong>.<br />

3 A further 3,925 tests were done for aldrin, dieldrin, heptachlor, heptachlor epoxide, all of which met the<br />

relevant standard.<br />

4 Standard or screening value.<br />

22


W estern re gion<br />

Aesthetic parameters<br />

Consumers expect their drinking water to be clear and bright in<br />

appearance and free from discer nible taste or odour. In recognition of this<br />

the regulations stipulate national standards for colour, odour and taste.<br />

Companies are required to investigate the cause of any adverse consumer<br />

taste or odour report and sample failures for aesthetic parameter s. Where,<br />

through investigation, the company established the cause to be<br />

arrangements or conditions within premises , these are described in the<br />

Maintaining water quality at the tap section.<br />

In the <strong>Western</strong> region overall, there were seven samples that faile d to<br />

meet standards for taste (1 BRL, 1 SWT, 5 WSX) out of a total of 4,098<br />

tests. In relation to these seven samples, five also failed for odour<br />

(1 SWT, 4 WSX). There were no failures of the colour standard. Most of<br />

the taste and odour failures recorded by Wessex <strong>Water</strong> are described in<br />

the section Chemical quality – Geosmin and the remainder are described<br />

below or in the Maintaining water quality at the tap section.<br />

Sweet<br />

This descriptor usually relates to samples where tap water is artificially<br />

softened within premises. However, South West <strong>Water</strong> did not identify<br />

a water softener or any other plumbing irregularities when carrying out<br />

a fittings inspection in response to a sample exhibiting a sweet taste and<br />

odour collected in September from a consumer’ s tap in the Prewely North<br />

zone. The <strong>Inspectorate</strong> expects companies to carry out enhanced<br />

monitoring in zones where unexplained taste or odour failures are<br />

recorded.<br />

Aluminium<br />

Aluminium can occur naturally in some water sources. Also, aluminium -<br />

based water treatment chemicals may be used at surface water works<br />

to aid the process of filtration.<br />

In 2011, a total of 4,542 samples were tested for aluminium in the <strong>Western</strong><br />

region. Cholderton and District <strong>Water</strong>, Semcorp Bournemouth <strong>Water</strong>, South<br />

West <strong>Water</strong>, Wessex <strong>Water</strong>, Veolia <strong>Water</strong> Projects Ltd and SSE <strong>Water</strong><br />

achieved 100% compliance with the aluminium standard. Just one test<br />

exceeded the standard, in a sample collected in the Bristol <strong>Water</strong>’s<br />

Fishponds and Mangotsfield zone, and this was found not to be related<br />

to process control at the works.<br />

A level of 345ug/l of aluminium was recorded in a sample collected from<br />

a consumer’s tap in August, in the Fishponds and Mangotsfield zone on<br />

the outskirts of Bristol, operated by Bristol <strong>Water</strong>. The same sample also<br />

23


Dri nking water 20 11<br />

failed the standards for iron and manganese. The company identified a<br />

length of cast iron pipework at the end of the main in an area of low water<br />

flow. After flushing to remove deposits, further tests gave satisfactory<br />

results. The zone is subject to a legally binding program of mains<br />

rehabilitation and replacement, which is due for completion in March 2015 .<br />

The <strong>Inspectorate</strong> expects investigations of failures to be taken into<br />

account during the planning of this distribution maintenance work.<br />

Chlorine<br />

Chlorine is widely used in households as bleach. It is an important<br />

disinfectant with many applications in the home and workplace wherever<br />

the maintenance of good hygiene is necessary. It is the most common<br />

oxidative disinfectant used in swimming pools and there is a long history<br />

of its use in water supplies stretching back for a century. Typical levels<br />

of residual chlorine in public water supplies in the UK are in the range<br />

of 0.1 – 1.0mg/l, well below levels typically found in many other parts<br />

of the world. Human exposure to chlorine in drinking water has not been<br />

associated with any specific adverse health effects and the W orld Health<br />

Organisation’s (W HO) health-related guideline value for chlorine is set<br />

at 5mg/l.<br />

There is not a numerical standard for resid ual chlorine in drinking water<br />

in England, however, water companies are required to measure residual<br />

chlorine whenever they are collecting samples for microbiological analysis<br />

and any abnormal change in chlorine concentration must be investigated.<br />

In addition, water companies are expected to have regard to consumer<br />

acceptability by investigating chlorine -related taste and odour complaints<br />

from consumers. The <strong>Inspectorate</strong> has set a screening value of 2mg/l for<br />

the purpose of assessing the effectiveness of r esidual chlorine<br />

management by water companies.<br />

In October, South West <strong>Water</strong> recorded a total chlorin e level of 2.89mg/l<br />

when collecting a consumer tap sample in the Prewley North zone. The<br />

sampler discussed the on-site measurement with the customer who<br />

explained that the tap had been bleached prior to the sampler attending<br />

the property. The sampler spoke to his supervisor, flushed the tap and<br />

noted that a subsequent chlorine measurement was lower. He then carried<br />

out checks at a neighbour’s property and th e local service reservoir<br />

confirming there was not a problem with the wider supply.<br />

During September, at Drift works, South West <strong>Water</strong> recorded two high<br />

chlorine values (2.67 and 2.73mg/l). The company had previously<br />

increased the chlorine dose at the work s for a fortnight due to algal growth<br />

and elevated ammonia in the raw water. This action had resulted in higher<br />

than normal chlorine levels at a number of service reservoirs: Cryor, Ding<br />

24


W estern re gion<br />

Dong, Kerris (Chywoone), and Leha. During this same period there were<br />

25 consumer contacts about abnormal taste and odour. The company has<br />

since reviewed the operation of the works during periods when the<br />

characteristics of the raw water require action to optimise water treatment.<br />

The <strong>Inspectorate</strong> expects the company to upd ate its regulatory risk<br />

assessment documenting the learning in relation to both the risk and the<br />

control measures.<br />

During 2011, Bristol <strong>Water</strong> recorded three high chlorine values at Littleton<br />

works. The first of these was a total chlorine residual of 2.02mg/l in June<br />

and in October values of 2.09mg/l free chlorine and 2.25mg/l total chlorine<br />

were recorded. Ozone is the primary disinfectant at this site and at the<br />

time there was a known problem with the operation of the residual chlorine<br />

dosing pumps. The company plans to move the dosing point to prevent<br />

excess chlorine being dosed and to achieve a more stable residual<br />

chlorine concentration. The <strong>Inspectorate</strong> expects the company to update<br />

its risk assessment to reflect this risk and both the short and long -term<br />

mitigation measures.<br />

Disinfection by-products<br />

To ensure the microbiological safety of public water supplies , water<br />

companies are required to disinfect water at the treatment works before<br />

supplying it through the distribution system to consumers. Disinf ection<br />

may be achieved by any appropriate physical or chemical method, or<br />

a combination of the two. The choice of method will depend on a range<br />

of site-specific factors, but an important consideration is the requirement<br />

to keep disinfection by-products (DBPs) to a minimum. This 1998 EU<br />

<strong>Drinking</strong> <strong>Water</strong> Directive requirement was introduced formally into national<br />

law in January 2010.<br />

Chemical disinfectants are powerful oxidants that react with organic and<br />

inorganic matter in raw water to form other compounds known as DBPs.<br />

There are many different DBPs and the likelihood of any particular ones<br />

occurring in a given water supply can be predicted from the raw water<br />

quality and the method of disinfection. A summary of commonly<br />

encountered DBPs can be found in the WHO’s Guidelines for <strong>Drinking</strong><br />

<strong>Water</strong> Quality 2004 Section 8.5.4. Based on current global research it is<br />

felt that two groups of compounds, trihalomethanes (THMs) and<br />

haloaceticacids (HAAs), serve as adequate indicators for monitoring DBP<br />

performance overall. The most appropriate means of controlling DBPs is<br />

to remove organic precursors from the raw water before it is disinfected.<br />

The <strong>Inspectorate</strong> has made a preliminary assessment of how well<br />

companies in the <strong>Western</strong> region are meeting the DBP rule using water<br />

company THM data reported for 2011. For this initial evaluation, the<br />

25


Dri nking water 20 11<br />

<strong>Inspectorate</strong> has set a screening criterion of an an nual average value<br />

of 50µg/l<br />

Company<br />

Number of<br />

zones operated<br />

by company<br />

Number of zones<br />

exhibiting an annual<br />

average for<br />

trihalomethanes<br />

>50µg/l<br />

Bristol W ater 52 0 -<br />

Cholderton and<br />

District W ater<br />

1 0 -<br />

Name of zones<br />

exhibiting an<br />

annual average<br />

for<br />

trihalomethanes<br />

>50µg/l<br />

Sembcorp<br />

Bournemouth W ater<br />

10 0 -<br />

South W est W ater 32 12<br />

Drift<br />

W endron<br />

College<br />

Tamar<br />

Stithians<br />

Northcombe<br />

Prewley North<br />

Restormel W est<br />

Prewley W est<br />

Burrows<br />

Littlehempston,<br />

Tottiford and<br />

Bovey Cross<br />

Venford<br />

SSE W ater 11 0 -<br />

Veolia W ater<br />

Projects Ltd<br />

1 0 -<br />

W essex W ater 91 0 -<br />

Industry total 1,670 37 -<br />

Note: Figures are for whole company areas .<br />

Fluoride<br />

Traces of fluoride occur naturally in many water sources, particularly in<br />

groundwater. For example, fluoride occurs in water drawn from the great<br />

Oolite limestone in the area of North East Somerset and West Wiltshire<br />

26


W estern re gion<br />

(particularly around Lacock). Consumers can obtain specific information<br />

on the level of fluoride in the drinking water supply to their home or<br />

workplace from their water company.<br />

Fluoride is not removed by conventional water treatment. Some companies<br />

fluoridate water supplies when required to do so by the local public health<br />

authority as a protection against tooth decay. There are no fluoridation<br />

schemes in the <strong>Western</strong> region. In 2011, all 1,186 tests for fluoride taken<br />

across the region met the regulatory standard (1.5mg/l). Please refer to<br />

the <strong>Inspectorate</strong>’s website (www.dwi.gov.uk) for more information on<br />

fluoridation.<br />

On 11 February 2011, the judicial review brought against South Central<br />

Strategic Health Authority (SCSHA) by Geraldine Milner was concluded.<br />

The review was about whether the SCSHA followed the correct procedure<br />

when deciding to fluoridate the Southampton and South W est Hampshire<br />

area. The judge found in favour of the SCSHA and technical feasibility<br />

of the fluoridation arrangements are being finalised. No new fluoridation<br />

schemes were proposed in the <strong>Western</strong> region in 2011.<br />

Geosmin<br />

Geosmin is a natural substance produced by the seasonal growth of algae<br />

in slow moving surface water. It gives rise to a characteristic ‘earthy’ or<br />

‘musty’ taste and odour discern ible to consumers.<br />

In March/April and September/October , Wessex <strong>Water</strong> reported an<br />

earthy/musty taste and odour in nine cons umer tap samples (four odour,<br />

five taste) collected from Porlock zone near Minehead. The company had<br />

identified, through risk assessment, that the treatment at Porlock works<br />

was unable to cope adequately with the seasonal occurrences of geosmin<br />

in Nutscale raw water reservoir. Changes in catchment management, which<br />

have seen a return of the moorland to its natural state (in Exmoor National<br />

Park) has resulted in different run off patterns and nutrient levels in<br />

surface water. This has necessitated a more co mplex and sophisticated<br />

water supply management regime, whereby the works has to be taken out<br />

of supply and the area rezoned when raw water quality cannot be treated<br />

adequately. The raw water main between Nutscale reservoir and Porlock<br />

works is flushed and sampled twice weekly, and the works is only returned<br />

to supply following satisfactory samples. The <strong>Inspectorate</strong> expects the<br />

company to validate the control measure (water supply management<br />

regime) as being sufficiently robust to prevent taste and odour fa ilures<br />

at consumers’ taps at all times. If seasonal taste and odour events<br />

continue, then the risk assessment should be updated and the need for<br />

alternate control measures, such as additional treatment, identified.<br />

27


Dri nking water 20 11<br />

When consumers experience a persistent t aste or odour, they may contact<br />

their water company to report the problem. Records of these contacts in<br />

each zone are recorded by water companies and passed to the<br />

<strong>Inspectorate</strong> annually. Figure 10 shows the contact rate per thousand<br />

people across the <strong>Western</strong> region and the location of the taste or odour.<br />

Figure 10: Rate of taste and odour contacts per 1,000 population<br />

Figure 10 illustrates the location of taste and odour failures that were not<br />

attributed to premises and shows the background level of cons umer<br />

contacts reporting taste and odour problems. It can be seen that the<br />

highest rate of consumer contacts occurred in three zones ; Broadwood<br />

Direct zone adjacent to Porlock zone where sample failures were reported<br />

in 2011, Chute zone near Andover and Castleton zone (Sherborne). The<br />

<strong>Inspectorate</strong> expects companies to use mapping of consumer contacts as<br />

part of the process of risk assessment and risk management.<br />

Nitrate and nitrite<br />

Nitrate occurs naturally in all source waters due to the decay of vegetable<br />

material in soil. Nitrogenous fertilisers used on arable farmland are a<br />

significant source of nitrate in groundwater. Rainfall washes nitrate from<br />

the soil into lakes, rivers and streams. Nitrate levels can be reduced by<br />

water treatment or by blending wit h another low nitrate water source.<br />

In 2011, all 1,794 tests for nitrate met the standard (50mg/l).<br />

28


W estern re gion<br />

From extensive information gathered by the water companies, a likelihood<br />

of drinking water supplies in the region failing the nitrate standard in the<br />

longer term has been confirmed at some sites. As a consequence, a legally<br />

binding agreement is in place for catchment management and the<br />

construction of an integrated grid system to facilitate blending, if required,<br />

at several W essex <strong>Water</strong> sites: Bulbridge, Ch irton, Dunkerton, Fonthill<br />

Bishop, Hooke, Sturminster and W ylye which will benefit approximately<br />

22,000 consumers. The catchment management measures are due to be<br />

delivered by 2015 with the grid system in place by March 2018. Similarly,<br />

a blending scheme is to be progressed at Bristol W ater’s Frome works in<br />

Somerset by the end of September 2014.<br />

Nitrite may be formed when chloramine is used as the residual disinfectant<br />

to maintain the microbiological quality in the distribution network. The<br />

formation of nitrite is controlled by careful optimisation of the<br />

chloramination process. Sembcorp Bournemouth W ater uses chloramine as<br />

the residual at all its treatment works. Nitrite can also form in samples of<br />

water, after collection and before analysis, especially if the sample is not<br />

kept cool.<br />

In 2011, all 1,796 tests carried out across the region for nitrite met the<br />

standard.<br />

Pesticides and related products<br />

This group of substances, generically called pesticides, includes many<br />

organic chemicals ranging from wee d killers, to insecticides and<br />

fungicides. <strong>Water</strong> sources may contain traces of pesticide residues as a<br />

result of agricultural use (pest control on crops) and non -agricultural use<br />

(herbicides for weed control on highways, railways etc.). <strong>Water</strong> companies<br />

are required to assess the risk to drinking water supplies of pesticide use<br />

in source water catchments and then test for those that might be present.<br />

Companies have documented potential and actual pesticide hazards<br />

through their risk assessments as informed b y raw water monitoring. When<br />

pesticides are first detected, water companies will enhance the monitoring<br />

of raw water and notify the Environment Agency to facilitate appropriate<br />

action in the catchment to safeguard drinking water quality.<br />

In 2011, none of the tests in the region exceeded the standard for total<br />

pesticides. Likewise, there was 100% compliance (1,367 tests) for the four<br />

pesticides with a standard of 0.03μg/l. Out of a total of 39,821 tests for<br />

those individual pesticides with a standard of 0.1 μg/l just two exceeded<br />

the standard. The circumstances and substances involved are summarised<br />

below.<br />

29


Dri nking water 20 11<br />

Mecoprop (MCPP)<br />

Mecoprop is a herbicide frequently found with other herbicides such as<br />

2,4-D or dicamba. Its predominant use is for weed control in lawns ,<br />

amenity agriculture and cereals. The standard is 0.1μg/l.<br />

In December, Mecoprop was detected at a level of 0.482μg/l in a sample<br />

from Wendron works (near Helston in Cornwall). A follow-up sample also<br />

contained mecoprop at a level above the standard, but lower than seen in<br />

the original sample. South West <strong>Water</strong> increased the dose of powdered<br />

activated carbon (PAC) and implemented a strategic flushing programme<br />

to remove mecoprop from the distribution system. The Environment Agency<br />

were notified and visited farms within the catchment area, but failed to<br />

identify a point source. The company has since updated its risk<br />

assessment.<br />

pH (Hydrogen ion)<br />

The acidity of water is measured by pH. The standard for pH requires it to<br />

be above 6.5 and below 9.5. The most frequent problems arise in upland<br />

areas where water may pick up iron and humic acids from peaty soil,<br />

resulting in acidic raw water (low pH), which is commonly described as<br />

‘soft water’. Such water has an increased potential to corrode iron pipes.<br />

Where pH values above 9.5 occur this is usually due to leaching from<br />

cement mortar-lined mains.<br />

In the <strong>Western</strong> region, out of a total of 5,117 tests, the standard was<br />

exceeded on five occasions in 2011 (1 BRL, 2 SWT, 2 WSX).<br />

In January, Wessex <strong>Water</strong> reported a pH value of 6.4 in a sample from<br />

a concessionary raw water supply at two farms in the Nutscale Valley,<br />

Exmoor, where treatment is by ‘point of use’ devices. The company<br />

investigation found that the raw water main from Porlock had been used<br />

intermittently and pH in the raw water reservoir had dropped rapidly due<br />

to heavy rainfall and significant snowmelt. Subsequent samples from all<br />

properties using ‘point of use’ treatment devices were satisfactory. Since<br />

the Point of Use water treatment units were replaced in 2006, there have<br />

been no pH failures in relation to this supply, but following this event the<br />

company will be reviewing its risk assessment.<br />

During July, Bristol <strong>Water</strong> reported a pH of 6.28 from a consumer ’s tap<br />

sample in Filton and Northville zone. Fur ther samples were satisfactory<br />

ruling out a wider problem. From discussion with the customer the<br />

company concluded that there was a water softener or other treatment<br />

device installed at the property. The <strong>Inspectorate</strong> expects companies to<br />

30


W estern re gion<br />

carry out a fittings inspection when investigating unusual results from<br />

a tap in a property.<br />

South West <strong>Water</strong> recorded a pH of 9.6 in a consumer’s tap sample<br />

collected from the Bastreet and St Cleer zone in March. The company<br />

investigation attributed the cause to low flow in the asbestos cement-lined<br />

main and this was dealt with by flushing. The company identified a similar<br />

situation when investigating a pH value of 10.0 in the Lowermoor and<br />

Delank zone in July, which was linked to low flow in cement -lined ductile<br />

iron main and where the company plans to install a hydrant to facilitate<br />

flushing of the local system. Cement -lined mains are a feature of the<br />

distribution system in Cornwall and long -term remedial measures are being<br />

addressed through the company’s Distribution Ope ration and Maintenance<br />

Strategy. The <strong>Inspectorate</strong> expects the company to update regulatory risk<br />

assessments to formally document when a flushing regime is introduced as<br />

a short-term control measure.<br />

Radioactivity<br />

Gross alpha/gross beta/total indicative d ose<br />

Radioactivity in raw water can originate from natural substances or from<br />

a specific point emission. <strong>Water</strong> companies are required to screen for<br />

radionuclides that emit either alpha or beta particles. If such screening<br />

exceeds guide values (gross alpha 0.1Bq/l, gross beta 1.0Bq/l), then fuller<br />

analysis for specific radionuclides is carried out to determine the origin.<br />

Total indicative dose (TID) is a measure of the effective dose of radiation<br />

through consumption of the water. The guide value is 0.1mSv/ye ar.<br />

In 2011, out of 1,376 tests across the <strong>Western</strong> region there were two<br />

detections of gross alpha and no detections of gross beta above screening<br />

values (SWT).<br />

Gross alpha at levels above the screening value was recorded in samples<br />

collected from Wendron works (September and November) where<br />

screening is carried out monthly. South West <strong>Water</strong> has calculated TID and<br />

results were below the guide value. Naturally occurring radio nucleotides<br />

(radium and uranium) are a feature of the Wendron catchment and testin g<br />

for radon, radium and uranium has been carried out by South West <strong>Water</strong> .<br />

To date all results have proved satisfactory.<br />

Tritium<br />

Monitoring for tritium is necessary only where a source of tritium is present<br />

within the catchment and it cannot be shown on t he basis of other<br />

surveillance programmes or investigations that the level of tritium is well<br />

below its parametric indicator value of 100Bq/l.<br />

31


Dri nking water 20 11<br />

South West <strong>Water</strong> has established, by risk assessment, that monitoring for<br />

tritium is not required. All tritium testing by the other companies in the<br />

<strong>Western</strong> region has given results well below 100Bq/l.<br />

Maintaining water quality in distribution<br />

Elevated levels of iron or manganese are objectionable to consumers<br />

because the water may appear turbid or discoloured due to unsightly<br />

deposits and may also stain laundry and water fittings. Since 2004 , the<br />

<strong>Inspectorate</strong> has been monitoring the progress of companies ’ distribution<br />

maintenance work using an index made up of three parameters (turbidity,<br />

iron and manganese). Figure 11 shows the long-term improvements in the<br />

<strong>Western</strong> region. In 2011, there was a deterioration largely due to mains<br />

renovation and replacement in the region.<br />

Figure 11: Percentage of tests meeting the standards for turbidity,<br />

iron and manganese.<br />

100.00<br />

99.90<br />

99.80<br />

99.70<br />

99.60<br />

99.50<br />

99.40<br />

99.30<br />

99.20<br />

99.10<br />

99.00<br />

2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011<br />

Bristol <strong>Water</strong><br />

Sembcorp Bournemouth <strong>Water</strong><br />

South West <strong>Water</strong> Wessex <strong>Water</strong><br />

Note: SSE W ater only beg an sup plying water in 200 8 . They ha ve achieved 10 0 % in each yea r<br />

s ince.<br />

Veolia W ater Proj ects onl y beg an sup pl ying wat er to Tidworth in 20 09. They ha v e achieve d 100%<br />

in each ye ar since.<br />

Chol de rton an d District W ater ha v e achieved 100% in each yea r exc ept 200 2 (9 5 .83%), 20 03<br />

(97. 62%) and 200 4 (97.22%).<br />

Discolouration of tap water often prompts consumers to contact their water<br />

company. The number of people contacting water companies about<br />

32


W estern re gion<br />

discoloured water are reported annually to the Inspe ctorate in accordance<br />

with Information Letter 1/2006. Looking at the trend since 2007 it can be<br />

seen from figure 12 that, across England and Wales, the numbers of<br />

consumers contacting their water company to complain about discoloured<br />

water has fallen from about 84,000 to below 54,000. In the <strong>Western</strong> region,<br />

the downward trend is more pronounced than that for the industry overall<br />

with the figure now standing at just below 11,000 , down by 45% since<br />

2007. These consumer contacts represent one-fifth of all consumer<br />

contacts to the industry regarding discolouration.<br />

Figure 12: Consumer contacts to companies for discolouration<br />

2007–2011<br />

90,000<br />

80,000<br />

70,000<br />

60,000<br />

50,000<br />

40,000<br />

30,000<br />

<strong>Western</strong> region<br />

Rest of Industry<br />

20,000<br />

10,000<br />

0<br />

2007 2008 2009 2010 2011<br />

Looking more closely at the <strong>Western</strong> region, mapping of the rate of<br />

consumer contacts by zone shows the changing picture from 2007 to 2011.<br />

Rates of consumer contacts to companies about discoloured water in 2007<br />

(Figure 13) illustrates the situation before the delivery of AMP4<br />

improvement work by companies. Figure 14 shows the comparable rate<br />

at the end of 2011 after completion of the AMP4 investment.<br />

These maps show the benefit of mains renovation work completed by<br />

South West <strong>Water</strong> in south west Cornwall and also areas around Bodmin<br />

Moor and Exeter, although in 2011 consumers were still experiencing<br />

discolouration problems in East Devon. The improvement in the area<br />

served by Bristol <strong>Water</strong> is less marked, with an increase in consumers<br />

reporting discolouration in areas near W ells and Midsomer Norton<br />

33


Dri nking water 20 11<br />

Figure 13: Rate of consumer contact per 1,000 population reporting<br />

black, brown or orange water in 2007<br />

Figure 14: Rate of consumer contact per 1,000 population reporting<br />

black, brown or orange water in 2011<br />

34


W estern re gion<br />

Across the <strong>Western</strong> region in 2011, out of a total of 8,547 tests for iron<br />

and manganese, there were 22 failures for iron (16 BRL, 2 SBW, 1 SWT, 3<br />

WSX) and 3 failures for manganese ( 1 BRL, 1 SWT, 1 WSX). In addition, there<br />

was one failure of the turbidity standard of 4NTU (1 BRL) and no failures<br />

of the polycyclic aromatic hydrocarbons ( PAH) standards. Most failures<br />

were treated as isolated occurrences of disturbances of mains deposits<br />

cleared by flushing. There were no failures of any of these standards in<br />

the areas served by Cholderton W ater, Veolia <strong>Water</strong> Projects and SSE<br />

<strong>Water</strong>.<br />

In 2011, Bristol <strong>Water</strong> recorded 16 failures of the standard for iron and one<br />

manganese failure, all in zones covered by a legally binding programme of<br />

AMP5 work to replace, rehabilitate and clean mains by 2015 : Sherston<br />

Marshfield Pucklechurch and W ick, Henleaze, Redland Cotham and<br />

Kingsdown, Stapleton St George and Conham, Stoke Bishop Coombe<br />

Dingle and Henbury, Eastville and Easton, Long Ashton Failands and<br />

Abbots Leigh, Avonmouth and Shirehampton, Bishopsworth Dundry and<br />

Stanton Drew. The manganese failure was in the Fishponds and<br />

Mangotsfield zone. In response to most failures, Bristol <strong>Water</strong> carried<br />

out only a limited investigation taking no action if the resample was<br />

satisfactory.<br />

In the Shirehampton area of Bristol, investigative samples exceeded the<br />

iron standard. The property was connected to t he supply towards the end<br />

of a three-inch cast iron main and the company carried out remedial<br />

flushing. Flushing was also carried out in another part of Bristol<br />

(Speedwell) when a sampling survey revealed that iron failures were more<br />

widespread. This area is included within the legally binding programme of<br />

work (Stapleton St. George and Conham zone) , however, the <strong>Inspectorate</strong><br />

has noted that the failure occurred in a public building therefore Bristol<br />

<strong>Water</strong> is under a duty to inform the building owner of the cause of the<br />

problem and the short- and long-term remedies. The <strong>Inspectorate</strong><br />

considers Bristol <strong>Water</strong> should be doing more in relation to short -term<br />

control measures and customer communications in areas where the<br />

company is not compliant with the iron stand ard and it is to be expected<br />

that customers will continue to experience discoloured water until delivery<br />

of longer-term improvements.<br />

In 2011, Sembcorp Bournemouth W ater reported only two failures of the<br />

iron standard, each in a different zone. The company investigation<br />

identified that the sample in Alderney South zone had been collected from<br />

a café which had just re-opened for business following closure over the<br />

winter period. The main was flushed and further tests gave satisfactory<br />

results. No cause was found for the other failure in a sample from a<br />

consumer’s tap in a property in St Catherines zone. The <strong>Inspectorate</strong><br />

expects this information to be taken into account in Sembcorp<br />

35


Dri nking water 20 11<br />

Bournemouth <strong>Water</strong>’s regulatory risk assessments and their Distribution<br />

Operation and Maintenance Strategy (DOMS).<br />

South West <strong>Water</strong> reported single failures of the standards for iron and<br />

manganese in 2011. The iron failure in the Drift zone occurred in a tap<br />

sample collected from a holiday let property situated at the end of the<br />

distribution system and flushing resolved the problem. The manganese<br />

failure in the Prewley West zone was a similar isolated occurrence with<br />

all re-samples being satisfactory.<br />

In 2011, there were three iron failures and one failure of the manganese<br />

standard in the area served by Wessex <strong>Water</strong>. Maundown North zone is<br />

covered by a legally binding programme of work to renovate the<br />

distribution system and a sample collected in May failed the standards for<br />

both iron and manganese. The <strong>Inspectorate</strong> expects that this information<br />

will be taken into account in the company’s risk assessment and DOMS.<br />

Wessex <strong>Water</strong> linked an iron failure in a sample from the Odcombe zone<br />

to a rezoning exercise to facilitate planned works. In the Dorchester zone,<br />

the company identified a long length of iron pipework to the building, which<br />

had not been used often during the Christmas and New Year period and<br />

the samples, after flushing, were satisfactory.<br />

Annex 4 details the legally binding programmes of distribution<br />

maintenance work schedule d to be completed between now and 2015<br />

to address distribution-related water quality problems in the region.<br />

Maintaining water quality at the tap<br />

Consumers expect their drinking water to be clear and bright in<br />

appearance and free from discernible taste, odour or contaminants.<br />

Several parameters are not routinely found in mains water , but instead<br />

they gain access to tap water close to the point of use. For example,<br />

certain plumbing metals (antimony, copper, lead and nickel) and sodium<br />

introduced by water softeners installed in premises. Accordingly,<br />

remediation of failures for these parameters requires action to be taken<br />

by property owners.<br />

36


Bristol <strong>Water</strong><br />

Cholderton and<br />

District <strong>Water</strong><br />

Sembcorp<br />

Bournemouth<br />

<strong>Water</strong><br />

South West <strong>Water</strong><br />

SSE <strong>Water</strong><br />

Veolia <strong>Water</strong><br />

Projects Ltd<br />

Wessex <strong>Water</strong><br />

W estern re gion<br />

Table 15: Failures in samples collected from taps where the cause was<br />

attributed to the premises<br />

Parameter<br />

Metals<br />

Antimony 0–388 0–4 0–81 0–379 0–4 0–8 0–757<br />

Copper 0–388 0–8 0–81 0–389 0–4 0–8 0–953<br />

Lead >10 6–388 0–4 0–81 1–390 0–4 0–8 5–601<br />

Nickel 1–388 0–6 0–81 0–389 0–4 0–8 0–597<br />

Colour 0–1,277 0–4 0–403 0–1,545 0–4 0–12 0–1,563<br />

Conductivity 0–1,408 0–4 0–411 0–2,130 0–12 0–12 0–1,870<br />

Odour 0–1,280 0–2 0–402 0–1,540 0–4 0–12 0–886<br />

pH 0–1,275 0–4 0–411 0–1,533 0–12 0–12 0–1,870<br />

Sodium 0–388 0–12 0–100 0–379 0–4 0–8 0–1,212<br />

Taste 1–1,279 0–2 0–400 0–1,522 0–4 0–12 0–879<br />

Total 8–8,459 0–50 0–2,451 1–10,196 0–56 0–100 5–11,188<br />

Note: Failures count ed in this table ar e those caused by con ditions or ar ran g em ents in the<br />

prem ises .<br />

Table 15 illustrates the distribution of failures for the parameters arising<br />

within all types of premises across the region. Overall, across the <strong>Western</strong><br />

region in 2011, there were 13 failures of the standards for metals ( 7 BRL,<br />

1 SWT, 5 WSX), and one positive detection for taste (1 BRL).<br />

In all such cases, the company must advise consumers of the failure and<br />

its cause with information about the actions needed t o safeguard health in<br />

the short term, as well as what is needed to effec t a remedy in the longer<br />

term. If the failure occurs in a public building, the company must go further<br />

and, either alone, or acting in collaboration with the local authority,<br />

enforce action by the relevant persons.<br />

37


Dri nking water 20 11<br />

Table 16 shows the number of investigations in public buildings resulting<br />

from a failure of a standard or exceedance of an indicator parameter<br />

value.<br />

Table 16: Investigations in public buildings where action is required<br />

by building owners<br />

Company<br />

Total tests at<br />

consumers’ taps<br />

Total tests<br />

at public<br />

buildings<br />

Investigations in public<br />

buildings<br />

Bristol W ater 49,312 2,654 3<br />

Cholderton<br />

and District<br />

W ater<br />

Sembcorp<br />

Bournemouth<br />

W ater<br />

South W est<br />

W ater<br />

370 0 0<br />

17,851 109 1<br />

74,139 2,780 3<br />

SSE W ater 389 0 0<br />

Veolia W ater<br />

Projects Ltd<br />

652 0 0<br />

W essex W ater 68,116 2,935 0<br />

Total 210,829 8,478 7<br />

Lead<br />

The most common source of lead in tap water is pipework installed before<br />

the 1970s or the use of non-approved solder on cold water systems. Lead<br />

may also leach from brass fittings. The standard of 10µg/l c omes into force<br />

at the end of 2013, but the <strong>Inspectorate</strong> has strongly recommended that<br />

companies take action ahead of the new standard coming into force<br />

(Guidance on the Implementation of the <strong>Water</strong> Supply (<strong>Water</strong> Quality)<br />

Regulations 2000 – Regulation 30).<br />

In 2011, companies in the region identified 12 failures (6 BRL, 1 SWT,<br />

5 WSX) of the future standard of 10µg/l out of a total of 1,476 tests,<br />

a slight increase compared to the nine failures recorded in 2010.<br />

As shown in figure 17, the situation regarding lead in the <strong>Western</strong> region<br />

is now similar to that of the industry overall.<br />

38


Percentage meeting standard<br />

W estern re gion<br />

Figure 17: Percentage of tests meeting the future standard of 10µg/l<br />

for lead between 2001 and 2011<br />

100<br />

99<br />

98<br />

97<br />

96<br />

95<br />

94<br />

2002 2003 2004 2005 2006 2007 2008 2009 2010 2011<br />

10ug/l Industry<br />

10ug/l <strong>Region</strong>al<br />

Most (9 out of 12) zones, where lead results greater than 10µg/l were<br />

reported in 2011, receive phosphate dosing which results in a protective<br />

layer inside pipework minimising the release of lead into tap water.<br />

Two companies in the region, W essex <strong>Water</strong> and South West W ater, have<br />

identified, in regulatory risk assessments, the likelihood of failing the<br />

10µg/l lead standard and have put action plans in place. Wessex W ater<br />

offers its consumers free replacement of lead service pipes (the part of the<br />

pipe owned by the consumer) and is working closely with local authorities<br />

and housing associations to identify properties where lead pipes can be<br />

replaced. South West <strong>Water</strong> has implemented enhanced monitoring with<br />

pipework identification to identify hot spot areas. The company is<br />

investigating mechanisms available for discounting the cos t to customers<br />

to encourage pipe replacement and is developing a lead awareness<br />

communications campaign with local authorities.<br />

In 2011, there was one occurrence in June of a failure of the 10µg/l lead<br />

standard reported at a public building. On investigation, it was determined<br />

that the property was a shop selling and repairing sewing machines. Such<br />

premises are not classed as public buildings ( Information letter<br />

10/2004). In light of this error the company has briefed staff on the<br />

classification of public buildings. The supply pipe and customer side<br />

pipework was replaced with medium-density polyethylene pipe in<br />

December.<br />

In 2011, the <strong>Inspectorate</strong> commissioned research with the water industry<br />

research organisation (UKWIR) to look beyond the current water trea tment<br />

measures now in place to reduce exposure to lead from tap water. The<br />

study looked at a wide range of quantitative and qualitative data including<br />

39


Dri nking water 20 11<br />

the estimated number of properties with lead pipes in the UK, lead in tap<br />

water measurements, and the costs and benefits of measures such as<br />

water treatment and supply pipe and service pipe replacement. One output<br />

of the project is an economic tool that enables users to estimate the costs<br />

and benefits of baseline phosphate dosing alongside the alternatives of<br />

lead pipe replacement or rehabilitation. Wider impacts were also<br />

considered, including consequential wastewater treatment costs, carbon<br />

emissions, health and other benefits , such as reductions in copper<br />

concentrations in tap water.<br />

The published UKWIR report, Alternatives to phosphate for<br />

plumbosolvency control (12/DW/04/12), concluded there is no practical ,<br />

alternative water treatment measure to the phosphate dosing regime<br />

already in place and this was confirmed as being effective in reducing lead<br />

concentrations in tap water substantially. The report also makes clear how<br />

replacement of a water company supply pipe will not result in a significant<br />

reduction in risk of exposure to lead unless the customer service pipe is<br />

also replaced at the same time. The r esearch has identified additional<br />

benefits attributable to phosphate dosing in the form of reduced amounts<br />

of copper leaching from plumbing and a similar effect in relation to iron<br />

concentrations. Pipe relining as an alternative to lead pipe replacement<br />

is also discussed in the UKWIR report. Early testing of this approach did<br />

not result in relining being widely applied by the industry, however, a new<br />

relining method has been developed which is potentially more cost<br />

beneficial and this is currently undergoi ng trials. The findings of this<br />

research will be taken into account in water company strategies for<br />

minimising exposure to lead in the long term.<br />

Aesthetic parameters<br />

Consumers expect their drinking water to be clear and bright in<br />

appearance and free from discernible taste or odour. In recognition of this<br />

the regulations stipulate national standards for colour, odour and taste.<br />

Companies are required to investigate the cause of any failures for the<br />

aesthetic parameters: taste, odour and colour.<br />

In 2011, one sample collected by Bristol <strong>Water</strong> from a consumer’s tap in<br />

the Clevedon zone in November exhibited a sweet taste that was<br />

attributed, on investigation, to the installation of a water softener. There<br />

was no separate mains fed drinking water tap and the h ouseholder was<br />

given advice.<br />

Wessex <strong>Water</strong> currently has two legally binding programmes of work to<br />

improve taste and odour. One of these, at Blashford works, is delayed as<br />

the works is being replaced with the Grid scheme and Blashford works will<br />

40


W estern re gion<br />

remain out of service, the other, at Sutton Bingham works is on target for<br />

completion in 2014 when over 62,000 consumers will benefit from<br />

improved water quality (see Annex 4).<br />

During 2011, South West <strong>Water</strong> completed a programme of work to<br />

improve taste and odour in the area served by Stithians works.<br />

<strong>Drinking</strong> water quality events<br />

<strong>Water</strong> quality events are classified into five broad categories based on the<br />

initial company report. The categories are:<br />

Not significant: no further information required by an inspector to assess<br />

the event.<br />

Minor: it is unlikely that further information would be required by an<br />

inspector to assess the event.<br />

Significant: a full company report is usually required to enable an<br />

inspector to assess the event.<br />

Serious: in addition to a full compa ny report, the assessment may involve<br />

more than one inspector in the investigation.<br />

Major: in addition to a full company report, will require an investigation led<br />

by senior inspectors involving extensive information gathering and usually<br />

site visits.<br />

In 2011, companies in the W estern region notified the <strong>Inspectorate</strong> of<br />

46 events. Table 18 shows how these events were classified.<br />

Table 18: <strong>Water</strong> quality events in the region in 2011<br />

Nature of event<br />

Risk assessment category (DWI)<br />

Minor/notsignificant<br />

Significant Major/serious<br />

2010 2011 2010 2011 2010 2011<br />

Air in water - - - - - -<br />

Chemical 3 3 1 1 - -<br />

Discoloured water 3 5 5 4 - -<br />

Inadequate treatment - - 1 - - -<br />

Loss of supplies/poor pressure 7 5 1 2 - -<br />

Microbiological 1 8 5 3 1 -<br />

Taste/Odour - 6 - 2 - -<br />

Health concern 1 - 1 - - -<br />

Public concern 8 7 1 - - -<br />

Other 2 - 1 - - -<br />

<strong>Region</strong> overall 25 34 16 12 1 -<br />

England and Wales 222 251 160 135 9 2<br />

41


Dri nking water 20 11<br />

A summary of the nature, cause and duration of each event categorised as<br />

significant, serious or major, along with details of the <strong>Inspectorate</strong> findings<br />

are set out in Annex 3. Most events were of relatively short duration and<br />

the company took appropriate action to inform and safeguard consumers<br />

and other stakeholders. A comparison of 2010 events with those of 2011<br />

shows a decrease in the numbers of significant, serious and major events<br />

in the <strong>Western</strong> region (12 compared to 17 in 2010).<br />

Wider learning points from event assessments in the region in 2011 are<br />

highlighted by the following cases:<br />

Loss of supply and discolouration following planned work<br />

In August, more than 3,000 consumers experienced discoloured water and<br />

loss of supply when planned work by Bristol W ater went wrong. The work<br />

to be carried out was the cleaning of a 24-inch main in the Long Ashton<br />

area of North Somerset. This strategic main had been identified by the<br />

company as the highest priority trunk main for renovation during the AMP5<br />

period (2010–2015). To carry out the cleaning work, the company first<br />

needed to change the supply arrangem ents by making a cross-connection<br />

between another 600mm main at Barrow Treatment works and the 24 -inch<br />

Long Ashton trunk main. This connection was to be made via a 500mm<br />

main and to maintain supplies while making this connection, the company<br />

had laid a short length of 180mm main with a pressure control valve<br />

(PCV). A series of three valve operations was involved in making the<br />

connection and the planning included a risk assessment, network<br />

modelling and preparation of valve instructions. Shortly after the 18 0mm<br />

connection had been made at the works, localised flooding was observed<br />

on-site and consumers began to report no water. Part of the 24-inch main<br />

had been abandoned in 2008 and the 180mm connection was to be made<br />

at a point downstream of the valve separa ting the live and abandoned<br />

section. However, because the Geographic Information System (GIS)<br />

records were incorrect the connection was actually made into the<br />

abandoned section resulting in no water entering the Long Ashton main.<br />

<strong>Water</strong> instead flowed from the open ended section of the abandoned main<br />

causing the localised flooding. The company were able to halt the planned<br />

work and restore the system to its normal operation. However , the loss of<br />

flow through the Long Ashton main mobilised deposits resulting in<br />

discolouration of the downstream supply. The discolouration was<br />

exacerbated by the automatic operation of a pumping station which<br />

extended the area affected.<br />

The <strong>Inspectorate</strong> was critical of the risk assessment for the planned work.<br />

This did not cover the entire activity and used incorrect population<br />

predictions (


W estern re gion<br />

3,000) leading to the conclusion that the discolouration risk was minimal<br />

when in fact the asset had already been identified as exhibi ting a high<br />

discolouration risk. This event once again highlights for companies the<br />

importance of verification of risk assessments and checks on the accuracy<br />

of GIS records prior to commencement of planned work.<br />

Unusual taste due to temporary loss of trea tment control<br />

In August, 31 consumers living in the New Forest area of Hampshire<br />

reported an unusual taste in their tap water (with up to 2 ,150 people<br />

potentially affected). The supply to the area comes from Knapp Mill works<br />

via Adlams works. After treatment at Knapp Mill, water with free residual<br />

chlorine is transferred to Adlams works where the residual chorine is<br />

converted to chloramine. Investigations carried out by Sembcorp<br />

Bournemouth <strong>Water</strong> identified a chlorine control issue at Knapp Mill.<br />

The online chlorine monitors were falsely reading zero causing the control<br />

system to increase the dose to compensate. The works shutdown<br />

automatically in response to the zero chlorine signal from the monitors,<br />

however, when the pumps started at Adlams Lane, the bis ulphite dosing<br />

at Knapp Mill was at a high level and , for a short period, water with a lower<br />

than normal level of chlorine went forward to Adlams Lane. In<br />

compensation, the system automatically increased the chlorine dose and,<br />

as a consequence, water with a higher than expected level of chlorine left<br />

Knapp Mill. Due to the slow reaction of the bisulphite dosing pumps at<br />

Adlams works this chlorinated water went on to the next stage of treatment<br />

(ammoniation) where the level of chlorine was further increased.<br />

Essentially the works was operating in a manner contrary to its design,<br />

causing changes to the characteristics of the water that were discernible<br />

to consumers. The <strong>Inspectorate</strong> was critical of the design and<br />

configuration of the chlorine control system (particularly its slow response<br />

to changes in water quality). The company investigation was<br />

unsatisfactory, especially in relation to the number, nature and timeliness<br />

of samples from the distribution network. It is a breach of Regulation 10<br />

not to carry out appropriate monitoring when there is reason to believe<br />

water is not wholesome and compliance with Regulation 26 requires both<br />

the design and continuous operation of water treatment to be fit for<br />

purpose.<br />

Unusual taste and odours following heavy rainfall<br />

During October, 37 consumers in the Wadebridge, Bodmin and Padstow<br />

areas of Cornwall contacted South West <strong>Water</strong> reporting an unusual earthy<br />

taste and odour in tap water. After an increase in taste and odour<br />

consumer contacts over two days the company beg an to dose powdered<br />

43


Dri nking water 20 11<br />

carbon at its Restormel works. Investigations confirmed an earthy taste<br />

and odour in samples from consumers’ taps and also at Restormel works.<br />

There had been recent heavy rainfall and this followed on from a<br />

prolonged summer dry spell. Methyl-isoborneol (MIB) and geosmin, two<br />

naturally occurring taste and odour causing compounds , were present at<br />

levels only marginally above the taste threshold for the se compounds, but<br />

the sensitivity of consumers was verified by the quick reporting of the<br />

problem to the company. Advice to consumers was provided by the<br />

company’s call centre and website, and South W est <strong>Water</strong> liaised with<br />

local health professionals to maintain public confidence regarding there<br />

being no potential impact on health. The Inspect orate was pleased to note<br />

the proactive handling of this event. The company enhanced treatment<br />

following the first consumer contacts working quickly to identify the root<br />

cause and providing consumers with information. Companies are reminded<br />

of the importance of developing skills and resources in event recognition<br />

through rapid diagnosis of consumer water quality contacts.<br />

During 2011, Wessex <strong>Water</strong> was cautioned for the misconnection of a<br />

property to a sewer in 2010. The company admitted the offence of<br />

supplying water unfit for human consumption and was formally cautioned.<br />

No offences are currently under consideration by the <strong>Inspectorate</strong> in<br />

connection with any of the events that occurred in the <strong>Western</strong> region<br />

during 2011.<br />

Technical audit activity<br />

The <strong>Inspectorate</strong> has operated a risk -based approach to technical audit<br />

since 2005 and no technical audit takes place without a reason.<br />

On 14 December 2011, and in line with the Government’s Better<br />

Regulation policy, Parliament gave the Chief Inspector powers in th e<br />

Public Bodies Bill to recover the costs of its regulatory activities from the<br />

industry from January 2013 onwards. During 2012, the <strong>Inspectorate</strong> has<br />

consulted the industry and other stakeholders on the proposed charging<br />

regime, the detail of which will be set out in Orders laid under the Bill in<br />

autumn 2012. W hereas the work of inspectors in assessing companies’<br />

compliance with the drinking water monitoring requirements as set out in<br />

the drinking water regulations can be predetermined, the technical audit<br />

activities of inspectors is less predictable, however, the nature and volume<br />

of technical audit activity over the past s even years is illustrated in Figure<br />

19 as an indication of the scope and extent of the new charging<br />

arrangements going forward.<br />

44


Number of audits<br />

W estern re gion<br />

Figure 19: Audit activity in the region 2005–2011<br />

35<br />

30<br />

Abstraction and treatment<br />

25<br />

Service reservoir integrity and<br />

management<br />

Distribution operational maintenance<br />

20<br />

Sampling and analysis<br />

15<br />

Response to recommendations<br />

10<br />

Compliance with requirements for<br />

Legal Instruments<br />

Other<br />

5<br />

Consumer complaint handling<br />

0<br />

2005 2006 2007 2008 2009 2010 2011<br />

Table 20 sets out all the risk-based technical audits, which took place in<br />

the <strong>Western</strong> region during 2011 together with summary findings. This is<br />

followed by information about industry wide themes assessed duri ng the<br />

year and the particulars of consumer complaint investigations by<br />

Inspectors, including a case study.<br />

Table 20: Summary of the technical audit findings in the <strong>Western</strong><br />

region in 2011<br />

Location and<br />

Company<br />

Main findings from audit<br />

reason<br />

Audit focus: Abstraction and treatment<br />

South W est<br />

W ater<br />

Crownhill<br />

works depot –<br />

water supply<br />

hygiene<br />

Unsatisfactory.<br />

Uncapped pipes and uncapped fittings ,<br />

evidence of some used/dirty fittings in stores<br />

available for reuse.<br />

45


Dri nking water 20 11<br />

Location and<br />

Company<br />

Main findings from audit<br />

reason<br />

W essex Rodbourne Generally satisfactory.<br />

W ater works –<br />

Critical of inadequate arrangements for the<br />

microbiological chlorination, but noted plan to upgrade the<br />

and turbidity disinfection s ystem .<br />

failures<br />

Recommended all monitors have visible<br />

calibration status .<br />

Noted two boreholes overflowing due to<br />

malfunctioning air valves on top of the<br />

headplates, raw water sample taps in poor<br />

condition with a heavy layer of scale, lack of<br />

sample point on supply to Rodbourne tower<br />

despite this supply being capable of<br />

independent use to supply Allington service<br />

reservoir.<br />

Audit focus: service reservoir integrity and management<br />

W essex Hardenhuish Generally satisfactory.<br />

W ater service<br />

Noted inadequate drainage at sample<br />

reservoir –<br />

facilities, subsidence of reservoir banks,<br />

microbiological mature tree growth on the banks, fencing<br />

failures<br />

around reservoir No.1 in poor condition.<br />

Audit focus: Distribution operational maintenance<br />

South W est Hole in the Unsatisfactory.<br />

W ater ground – water Critical that contractors used dirty pipes and<br />

supply hygiene fittings and could not make chloros up onsite<br />

as the gangs did not carry Instachlor chlorine<br />

tablets.<br />

W essex<br />

W ater<br />

Depot and<br />

hole in the<br />

ground – water<br />

supply hygiene<br />

Mains relining,<br />

Bridgwater –<br />

procedures<br />

Satisfactory.<br />

Good practices observed in the field and the<br />

depot was tidy and well managed.<br />

W essex<br />

Satisfactory.<br />

W ater<br />

W orking practices and procedures adhered to<br />

in accordance with the Operational<br />

Requirements and Code of Practice for the in -<br />

situ Resin Lining of W ater Mains.<br />

Audit focus: consumer complaint handling<br />

South W est<br />

All satisfactory.<br />

W ater<br />

Taste and<br />

odour (1)<br />

Other (1)<br />

Discolouration<br />

(1)<br />

Audit focus: Compliance with requirements for Legal Instruments<br />

South W est<br />

W ater<br />

Closure of<br />

legal<br />

Instruments –<br />

general<br />

<br />

Company was advised that insuffici ent<br />

information was being provided to the<br />

<strong>Inspectorate</strong> for sign off of Legal Instruments;<br />

requirements explained and company has<br />

since complied.<br />

46


W estern re gion<br />

During 2011, the <strong>Inspectorate</strong> audited the water supply hygiene<br />

procedures of 11 companies across England and W ales following receipt of<br />

information which increased the <strong>Inspectorate</strong>’s overall assessment of risk<br />

associated with the way companies carried out work in their distribution<br />

systems. These audits covered equipment storage conditions in depots<br />

and vans, as well as mains repairs and meter installations. The outcome of<br />

a majority of the audits were generally satisfactory, but examples of poor<br />

practice were identified where contamination of drinking water might have,<br />

or did, occur as a consequence of unsuitabl e storage of fittings, pipes and<br />

other materials, insufficient clearance of soil from around open pipes<br />

or connections, inadequate flushing or disinfection and a lack of good<br />

hygiene within vans. The findings were summarised and published in an<br />

Information Letter (IL 04/2012) to promote industry-wide learning and<br />

improvement in this critically important aspect of day -to-day operations.<br />

Figure 21: An example of unsuitable storage of pipes prior to<br />

installation<br />

47


Dri nking water 20 11<br />

Complaints to the <strong>Inspectorate</strong><br />

The number of consumers who had cause to complain to the <strong>Inspectorate</strong><br />

because the company failed to resolve a water quality concern has fallen<br />

from six in 2010 to three in 2011. Consumers also contact water<br />

companies when they are dissatisfied with their water quali ty and<br />

complaints regarding appearance, taste and odour and incidence of illness<br />

has remained static between 2010 and 2011 at just below 18,000. By far<br />

the largest component of these figures are the contacts for appearance<br />

and 2011 has seen a levelling out of the previous encouraging reduction<br />

in these contacts.<br />

Table 22 shows the number of complaints about water quality received by<br />

the <strong>Inspectorate</strong> in 2011 alongside the annual rate of consumer contacts to<br />

water companies about water quality issues. Genera lly, complaints made<br />

directly to the <strong>Inspectorate</strong> arise when a company’s handling of a<br />

consumer contact has fallen short of best practice and this only comes to<br />

light as a result of intervention by an inspector. For this reason, there is<br />

no direct relationship between the figures set out in Table 22 and it is not<br />

uncommon for complaints to the <strong>Inspectorate</strong> to be from customers of<br />

companies exhibiting a low rate of consumer contact generally.<br />

Table 22: Complaint rates to industry and to the <strong>Inspectorate</strong><br />

Company<br />

Rate of consumer contacts<br />

per 1,000 people 1 to water<br />

companies in 2011<br />

Number of complaints<br />

received by the<br />

<strong>Inspectorate</strong> in 2011<br />

Bristol W ater 2.2 -<br />

Cholderton and<br />

District W ater<br />

Sembcorp<br />

Bournemouth<br />

W ater<br />

South W est<br />

W ater<br />

- -<br />

1.1 -<br />

6.9 3<br />

SSE W ater 0.4 -<br />

Veolia W ater<br />

Projects Ltd<br />

0.5 -<br />

W essex W ater 2.4 -<br />

Industry rate 1.9 34<br />

1 Rat e of contacts for app e ara nce, taste an d odou r and illness .<br />

48


W estern re gion<br />

During 2011, the following complaint case illustrate s why the <strong>Inspectorate</strong><br />

considers it important that companies have in place effective arrangements<br />

for diagnosing consumer contacts.<br />

Case example<br />

In April, a consumer contacted Ofwat to report tap water in Truro, Cornwall<br />

with an unusually strong chlorine taste and odour and occasional<br />

discolouration. The consumer who was referred correctly by Ofwat to the<br />

<strong>Inspectorate</strong>, was aware of past work by South West <strong>Water</strong> replacing water<br />

mains in the area in 2003 and this knowledge in part prompted the<br />

complaint. The property in question was a holiday home. The consumer<br />

was not a permanent resident and personal occupation of the property was<br />

for only a few months each year. On being told of the complaint by the<br />

<strong>Inspectorate</strong>, South West <strong>Water</strong> contacted the consumer and arranged to<br />

meet with them when they were next in res idence. A water quality report<br />

for the zone was provided. W hen the visit to the property took place the<br />

company offered a fittings inspection and gave advice on backflow<br />

prevention. Free check valves to fit to white goods were provided after<br />

explaining how these can often be the cause of unusual tastes and odours.<br />

By meeting with the consumer personally and by giving useful and<br />

accurate information South West <strong>Water</strong> successfully reassured the<br />

consumer.<br />

Published research has shown how gaps in knowledge resu lt in heuristic<br />

judgements whereby a person falls back on unrelated information from the<br />

past (in this case mains renovation) to make sense of a current situation<br />

thereby creating misperceptions and distrust, triggering complaining<br />

behaviour (in this case the call to Ofwat rather than the water company).<br />

The <strong>Inspectorate</strong> expects companies to invest in providing factual<br />

information about water quality proactively to consumers recognising how<br />

water quality contacts, when well handled, are the most effective w ay of<br />

positively influencing consumer perceptions of drinking water quality .<br />

For further information on the <strong>Water</strong> Supply (<strong>Water</strong> Quality) Regulations<br />

2000, or the microbiological and chemical parameters covered by the<br />

regulations please refer to the DWI website (www.dwi.gov.uk).<br />

If you have a need for more specific information than that on our website,<br />

please contact us on the DWI enquiry line: 0300 068 6400.<br />

49


Dri nking water 20 11<br />

Annex 1<br />

Further sources of information<br />

The publication <strong>Drinking</strong> water 2011 comprises the regional reports for<br />

England and a report covering Wales. There are f our regional reports for<br />

England (Central and Eastern, London and South East, Northern, and<br />

<strong>Western</strong>) and one for Wales (in two languages). Each report presents<br />

information from 2011 under the f ollowing headings:<br />

<br />

<br />

<br />

<br />

<br />

<br />

Overview of drinking water quality in the region.<br />

<strong>Water</strong> supply arrangements.<br />

<strong>Drinking</strong> water quality testing.<br />

<strong>Drinking</strong> water quality results.<br />

Technical audit activity.<br />

<strong>Drinking</strong> water quality events.<br />

There are also separate reports covering private water supplies, one<br />

covering England and one covering Wales.<br />

The reports and other content are published on the DWI website<br />

(www.dwi.gov.uk).<br />

Content of the CD<br />

The CD supplied with the printed report holds all of the above content and<br />

additionally it contains:<br />

<strong>Water</strong> company look-up tables<br />

These summarise all the results of water company monitoring in 2011.<br />

They provide information on:<br />

<br />

<br />

<br />

<br />

what was tested;<br />

how many tests were performed;<br />

the range of the results of testing; and<br />

how many tests failed to meet the standards.<br />

Significant drinking water quality events in England and<br />

Wales 2011<br />

To promote shared learning, the <strong>Inspectorate</strong> has compiled a list of all<br />

events that occurred in 2011 which illustrate the nature and cause of each<br />

event, the main actions by the company and findings from the inspectors’<br />

assessments. Relevant content from this overall list is contained in an<br />

annex to each regional report.<br />

50


W estern re gion<br />

Annex 2<br />

Glossary and description of standards<br />

These definitions will assist the underst anding of the report where<br />

technical terms have been used.<br />

µg/l<br />

1,2-Dichloroethane<br />

Acrylamide<br />

Aesthetic<br />

Aggressive<br />

Alkali<br />

Aluminium<br />

Ammonium<br />

microgram per litre (one millionth of a gram<br />

per litre).<br />

is a solvent that may be found in groundwater in<br />

the vicinity of industrial sites. W here necessary<br />

it can be removed by special water treatment.<br />

A European health-based standard of<br />

3μg/l applies.<br />

European health-based standard. A monomer<br />

is not normally found in drinking water. It is<br />

produced in the manufacture of polyacrylamides<br />

occasionally used in water treatment.<br />

Its presence in drinking water is limited by<br />

control of the product specification. Standard<br />

is 0.1µg/l.<br />

associated with the senses of taste, smell<br />

and sight.<br />

a term used to indicate that the water has a<br />

tendenc y to dissolve copper (and other metals)<br />

from the inner surface of a pipe or water fitting<br />

such as a tap.<br />

a solution containing an excess of free hydroxyl<br />

ions, with a pH greater than seven.<br />

occurs naturally in some source water s. It is<br />

removed from drinking water by conventional<br />

water treatment (coagulation and filtration).<br />

Aluminium sulphate and polyaluminium chloride<br />

may be used as water treatment chemicals at<br />

some water treatment works. A national standard<br />

of 200μg/l applies.<br />

salts are naturally present in trace amounts in<br />

most waters. Their presence might indicate<br />

contamination of sanitary significance and they<br />

interfere with the operation of the disinfection<br />

process. An indicator parameter with a guide<br />

value of 0.5mg/l.<br />

51


Dri nking water 20 11<br />

Analytical quality control<br />

(AQC)<br />

Antimony<br />

Aquifer<br />

Arsenic<br />

Authorised departure<br />

Benzene<br />

Benzo(a)pyrene<br />

Boron<br />

Bromate<br />

the method used to ensure that laboratory<br />

analysis methods are performing correctly.<br />

is rarely found in drinking water.<br />

Trace amounts can be derived from brass tap<br />

fittings and solders. A European heal th-based<br />

standard of 5μg/l applies.<br />

water-containing underground strata.<br />

occurs naturally in only a few sources of<br />

groundwater. Specific water treatment is required<br />

to remove it. A European health-based standard<br />

of 10μg/l applies.<br />

authorisation for a water company to temporarily<br />

supply water exceeding a drinking water<br />

standard, granted by the authorities only when<br />

there is no risk to human health.<br />

is present in petrol. It is not found in drinking<br />

water, but it can migrate through underground<br />

plastic water pipes if petrol is spilt in the vicinity.<br />

A European health-based standard of 1μg/l<br />

applies. Some bottled waters and soft drinks<br />

which include sodium benzoate as an ingredient<br />

have been reported as containing benzene.<br />

is one of several compounds known as polycyclic<br />

aromatic hydrocarbons (PAHs). Their source in<br />

drinking water is as a result of deterioration of<br />

coal tar, which many years ago was used to line<br />

water pipes. Due to extensive water mains<br />

refurbishment and renewal it is now rare to<br />

detect this substance in drinking water.<br />

A European health-based standard of<br />

0.01μg/l applies.<br />

in surface water sources comes from industrial<br />

discharges or from detergents in treated sewage<br />

effluents. The very low concentrations found in<br />

some drinking waters are not a concern to<br />

public health. A European health-based standard<br />

of 1mg/l applies.<br />

can be formed during disinfection of drinking<br />

water through a reaction between naturally<br />

occurring bromide and strong oxidants (usually<br />

ozone). It may be generated in the manufacture<br />

of sodium hypochlorite disinfectant.<br />

Exceptionally, groundwater can be contaminated<br />

with bromate, released from industrial sites .<br />

A European health-based standard of<br />

10μg/l applies.<br />

52


W estern re gion<br />

Bulk supply<br />

Cadmium<br />

Catchment<br />

Chloramination<br />

Chloramine<br />

Chloride<br />

Chlorine residual<br />

Chromium<br />

Clostridium perfringens<br />

Coagulation<br />

Coliform bacteria<br />

water supplied in bulk, usually in treated form,<br />

from one water company to another.<br />

is rarely detected in drinking water and trace<br />

amounts are usually due to dissolution of<br />

impurities from plumbing fittings. A Europea n<br />

health-based standard of 5μg/l applies.<br />

when used in connection with water, the<br />

catchment is the area drained by a river or<br />

water body.<br />

the process of generating a chloramine<br />

disinfectant residual in water leaving a<br />

treatment works.<br />

a substance formed by a reaction between<br />

chlorine and ammonia, used as a disinfectant in<br />

distribution s ystems because of its long -lasting<br />

properties compared to chlorine.<br />

is a component of common salt. It may occur in<br />

water naturally, but it may also be present due<br />

to local use of de-icing salt or saline intrusion.<br />

An indicator parameter with a guide value<br />

of 250mg/l.<br />

the small amount of chlorine or chloramines<br />

present in drinking water to maintain i ts quality<br />

as it passes through the water company’s<br />

network of pipes and household plumbing.<br />

is not present in drinking water. A European<br />

health-based standard of 50μg/l applies.<br />

is a spore-forming bacterium that is pr esent in<br />

the gut of warm -blooded animals. The spores can<br />

survive disinfection. The presence of spores in<br />

drinking water indicates historic contamination<br />

that requires investigation. The standard is<br />

0 per 100ml.<br />

a process employed during drinking water<br />

treatment to assist with the removal of<br />

particulate matter.<br />

are widely distributed in the environment often<br />

as a result of human or animal activity, but some<br />

grow on plant matter. Their presence in a water<br />

supply indicates a need to investigate the<br />

integrity of the water supply s ystem.<br />

The standard is 0 per 100ml.<br />

53


Dri nking water 20 11<br />

Colony counts<br />

Colour<br />

Communication pipe<br />

Compliance assessment<br />

Compound<br />

Concessionary supplies<br />

Conductivity<br />

Contact tank<br />

Contravention<br />

Copper<br />

are general techniques for detecting a wide<br />

range of bacteria, the types and numbers being<br />

dependent on the conditions of the test.<br />

These counts, if done regularly, can help to<br />

inform water management, but they have no<br />

direct health significance. The standard is ‘no<br />

abnormal change’.<br />

occurs naturally in upland water sources.<br />

It is removed by conventional water treatment.<br />

A national standard of 20mg/l on the<br />

Platinum/Cobalt (Pt/Co) scale applies.<br />

the connection from the water main to the<br />

consumer’s property boundary.<br />

a comparison made by the <strong>Inspectorate</strong> of data<br />

gathered by water companies against standards<br />

and other regulatory requirements.<br />

a compound consists of two or more elements<br />

in chemical combination.<br />

historical free supplies of water for a<br />

householder, established when a company<br />

wanted to lay mains across land and the<br />

landowner might agree, subject to a permission,<br />

to take a supply of water from the main.<br />

is a non-specific measure of the amount of<br />

natural dissolved inorganic substances in<br />

source waters. An indicator parameter with<br />

a guide value of 2,500µS/cm.<br />

a tank, normally situated on a treatment works<br />

site, which forms part of the disinfection process.<br />

A disinfectant chemical (normally chlorine) is<br />

dosed into the water as it flows into the tank.<br />

The period of time that the water takes to flow<br />

through the tank allows sufficient ‘contact’ time<br />

for the chemical to kill, or deactivate, any<br />

viruses or pathogenic organisms that may be<br />

present in the water.<br />

a breach of a regulatory requirement.<br />

in drinking water comes mostly from copper<br />

pipes and fittings in households. In general,<br />

water sources are not aggressive towards<br />

copper, but problems very occasionally occur on<br />

new housing estates. These ‘blue water’ events<br />

can be avoided by good plumbing practices.<br />

A European health-based standard of<br />

2mg/l applies.<br />

54


W estern re gion<br />

Cryptosporidium<br />

Cyanide<br />

Dead leg<br />

Distribution systems<br />

<strong>Drinking</strong> water standards<br />

is a parasite that causes severe gastroenteritis<br />

and can survive disinfection. In the UK,<br />

continuous monitoring is undertaken at works<br />

classified by the company as being at<br />

significant risk.<br />

is not present in drinking water. A European<br />

health-based standard of 50μg/l applies.<br />

refers to a piece of piping which is stopped off at<br />

one end, but is connected to the supply at the<br />

other end and can result in stagnant water in<br />

the pipework.<br />

a water company’s network of mains, pipes,<br />

pumping stations and service reservoirs through<br />

which treated water is conveyed to consumers.<br />

the prescribed concentrations or values listed<br />

in regulations.<br />

EC <strong>Drinking</strong> <strong>Water</strong> Directive Council Directive 98/83/EC December 1998 –<br />

setting out drinking water standards to be<br />

applied in member states.<br />

Enforcement action the means, as set out in the W ater Act 1989<br />

and consolidated into the W ater Industry Act<br />

1991, by which the Secretary of State requires<br />

a water company to comply with certain<br />

regulatory requirements.<br />

Enterococci<br />

Environment Agency<br />

Epichlorohydrin<br />

Epidemiology<br />

see Escherichia coli.<br />

the Environment Agency is responsible for<br />

maintaining or improving the quality of fresh,<br />

marine, surface and underground water in<br />

England and W ales.<br />

can be found in trace amounts in polyamine<br />

water treatment chemicals. Its presence in<br />

drinking water is limited by control of the product<br />

specification. A European health-based standard<br />

of 0.1μg/l applies.<br />

a process of studying the distribution of cases of<br />

disease within a population in relation to<br />

exposure to possible sources of the infection,<br />

with a view to establishing the actual source of<br />

the infection.<br />

55


Dri nking water 20 11<br />

Escherichia coli and<br />

Enterococci<br />

Event<br />

are bacteria present in the gut of warm -blooded<br />

animals. They should not be present in drinking<br />

water and, if present, immediate action is<br />

required to identify and remove any source of<br />

faecal contamination that is found. The standard<br />

is 0 per 100ml.<br />

water companies have to inform the <strong>Inspectorate</strong><br />

about occasions when water quality or<br />

sufficienc y is affected or when public confidence<br />

in drinking water quality may be impacted. The<br />

<strong>Inspectorate</strong> refer to these instances as ‘Events’ .<br />

Filtration<br />

Fluoride<br />

Geosmin<br />

Granular activated carbon<br />

Gross alpha/gross beta<br />

Groundwater<br />

the separation of suspended particulate matter<br />

from a fluid.<br />

occurs naturally in many water sources,<br />

especially groundwater. It cannot be removed by<br />

conventional water treatment so high levels must<br />

be reduced by blending with anoth er low fluoride<br />

water source. Some water companies are<br />

required by the local health authority to<br />

fluoridate water supplies as a protection against<br />

tooth decay. The drinking water standard<br />

ensures levels are safe in either circumstance.<br />

Fluoridation of water is a Department of Health<br />

polic y. A European health-based standard of<br />

1.5mg/l applies.<br />

a substance produced by the growth of algae,<br />

normally in surface waters which gives rise to a<br />

characteristic ‘earthy’ or ‘musty’ taste or odour.<br />

an adsorbent filtration media used to remove<br />

trace organic compounds from water.<br />

radioactivity in raw water can originate from<br />

natural substances or from a specific point<br />

emission. W ater companies are required to<br />

screen for radionuclides that emit either alpha or<br />

beta particles. If such screening exceeds guide<br />

values (gross alpha 0.1Bq/l, gross beta 1.0Bq/l)<br />

then fuller analysis for specific radionuclides is<br />

carried out to determine the origin.<br />

water from aquifers or other underground<br />

sources.<br />

56


W estern re gion<br />

Hydrogen Ion<br />

(pH)<br />

Improvement programmes<br />

Indicator organism<br />

Indicator parameter<br />

Information Letter<br />

<strong>Inspectorate</strong><br />

Iron<br />

Lead<br />

m 3 /d<br />

Manganese<br />

gives an indication of the degree of acidity of the<br />

water. A pH of 7 is neutral; values below 7 are<br />

acidic and values above 7 are alkaline.<br />

A low pH water may result in pipe corrosion.<br />

This is corrected by adding an alkali during<br />

water treatment. A specification of between<br />

6.5 and 9.5 applies.<br />

water company improvement works, these are<br />

legally binding on the company and each<br />

programme will remedy an actual or pote ntial<br />

breach of a drinking water standard within a<br />

specified time period.<br />

an organism which indicates the presence of<br />

contamination and hence the possible presence<br />

of pathogens.<br />

something that is measured to che ck that<br />

control measures, such as water treatment,<br />

are working effectively.<br />

formal guidance to water companies given<br />

by the <strong>Inspectorate</strong> and published on the<br />

<strong>Inspectorate</strong>’s website at www.dwi.gov.uk<br />

The <strong>Drinking</strong> W ater <strong>Inspectorate</strong>.<br />

is present naturally in many water sources.<br />

It is removed by water treatment. Some iron<br />

compounds are used as water treatment<br />

chemicals. However, the commonest source<br />

of iron in drinking water is corrosion of iron<br />

water mains. A national standard of<br />

200μg/l applies.<br />

very occasionally occurs naturally in raw waters,<br />

but the usual reason for its presence in drinking<br />

water is plumbing in older properties. If the water<br />

supply has a tendenc y to dissolve lead then<br />

water companies treat the water to reduce<br />

consumer exposure. The permanent remedy is<br />

for householders to remove lead pipes and<br />

fittings. A European health-based standard of<br />

25μg/l applies, but 10μg/l will apply from 25<br />

December 2013 onwards.<br />

cubic metre per day.<br />

is present naturally in many sources and is<br />

usually removed during treatment. A national<br />

standard of 50μg/l applies.<br />

57


Dri nking water 20 11<br />

Mean zonal compliance<br />

percentage<br />

Mercury<br />

Methyl-isoborneol (MIB)<br />

mg/l<br />

Microbiological<br />

Ml/d<br />

Nickel<br />

Nitrate<br />

Nitrite<br />

Notice<br />

a measure of compliance with drinking water<br />

standards introduced by the <strong>Inspectorate</strong> in<br />

2004.<br />

is not found in sources of drinking water.<br />

A European health-based standard of<br />

1μg/l applies.<br />

a natural substance produced by the growth of<br />

algae, normally in surface waters which gives<br />

rise to a characteristic ‘eart hy’ or ‘musty’ taste or<br />

odour. It is detected by the method for assessing<br />

taste and odour.<br />

milligram per litre (one thousandth of a gram<br />

per litre).<br />

associated with the study of microbes.<br />

megalitre per day (one Ml/d is eq uivalent to<br />

1,000 m 3 /d, or to 220,000 gallons/d).<br />

occurs naturally in some groundwater and where<br />

necessary special treatment can be installed to<br />

remove it. Another source of nickel in drinking<br />

water is the coatings on modern taps and other<br />

plumbing fittings. A European health-based<br />

standard of 20μg/l applies.<br />

occurs naturally in all source waters although<br />

higher concentrations tend to occur where<br />

fertilisers are used on the land. Nitrate can be<br />

removed by ion exchange water treatment or<br />

through blending with other low nitrate sources.<br />

A European health-based standard of<br />

50mg/l applies.<br />

is sometimes produced as a by-product when<br />

chloramine is used as the essential residual<br />

disinfectant in a public water supply.<br />

Chloramine is the residual disinfectant of choice<br />

in large distributions systems because it is more<br />

stable and long-lasting. Careful operation of the<br />

disinfection process ensures levels of nitrite are<br />

kept below the standard. A European health -<br />

based standard of 0.5mg/l applies.<br />

an instruction served by the Secretary of State<br />

(in the case of water supplies, the Chief<br />

Inspector of W ater) requiring specific actions to<br />

be taken by the recipient within a specified<br />

timescale.<br />

58


W estern re gion<br />

Odour<br />

Ofwat<br />

Oocyst<br />

Organoleptic<br />

Ozone process (ozonation)<br />

Parameters<br />

Pathogen<br />

PCV<br />

Periodic review<br />

Pesticides<br />

Pesticides – organochlorine<br />

compounds (aldrin, dieldrin,<br />

heptachlor, heptachlor<br />

epoxide)<br />

can arise as a consequence of natur al processes<br />

in surface waters, particularly between late<br />

spring and early autumn. W ater treatment with<br />

activated carbon or ozone will remove natural<br />

substances causing taste. The standard relates<br />

to the evaluations of a panel of people assessing<br />

samples in the laboratory.<br />

the water industry’s economic regulator.<br />

the resistant form in which Cryptosporidium<br />

occurs in the environment, and which is capable<br />

of causing infection.<br />

characteristics of a substance as detected by ou r<br />

senses, for example taste, odour or colour.<br />

the application of ozone gas in drinking<br />

water treatment.<br />

the substances, organisms and properties listed<br />

in Schedule 2 and Regulation 3 of the<br />

regulations. Parameter definitions can be found<br />

in this annex.<br />

an organism which can infect humans and<br />

cause disease.<br />

see ‘Prescribed concentration or value’.<br />

the economic regulator’s process of setting<br />

water prices.<br />

any fungicide, herbicide, insecticide or related<br />

product (excluding medicines) used for the<br />

control of pests or diseases.<br />

are no longer used in the UK because they are<br />

persistent in the environment. They are not found<br />

in drinking water. A European chemical standard<br />

of 0.03μg/l for each compound applies.<br />

59


Dri nking water 20 11<br />

Pesticides – other than<br />

organochlorine compounds<br />

Phosphate dosing<br />

Plumbosolvency<br />

Polycyclic aromatic<br />

hydrocarbons<br />

(PAHs)<br />

Powdered activated carbon<br />

(PAC)<br />

Pre- and post-renovation<br />

assessment (PPRA)<br />

Prescribed concentration or<br />

value (PCV)<br />

Private supplies<br />

Protozoan parasites<br />

Public Register<br />

is a diverse and large group of organic<br />

compounds used as weed killers, in secticides<br />

and fungicides. Many water sources contain<br />

traces of one or more pesticides as a result of<br />

both agricultural and non-agricultural uses,<br />

mainly on crops and for weed control on<br />

highways and in gardens. W here needed, water<br />

companies have installed water treatment<br />

(activated carbon and ozone) so that pesticides<br />

are not found in drinking water. W ater companies<br />

must test for those pesticides used widely in<br />

their area of supply. Pesticide monitoring thus<br />

varies according to risk. A European chemical<br />

standard of 0.1μg/l for each individual substance<br />

and 0.5μg/l for the total of all pesticides applies.<br />

treatment of water that results in a protective<br />

film building up on the inside of pipes minimising<br />

the likelihood of lead being present in drinking<br />

water supplied through lead pipes.<br />

the tendenc y for lead to dissolve in water.<br />

is a group name for several substances present<br />

in petroleum -based products such as coal tar.<br />

(see Benzo(a)pyrene listed above for more<br />

information). A European health-based<br />

standard of 0.1μg/l for the sum of all the<br />

substances applies.<br />

powdered activated carbon is employed in<br />

treatment processes to remove pollutants.<br />

a programme of assessment before and after<br />

mains renovation to demonstrate justification<br />

for the work, and the improvements achieved<br />

by the renovation.<br />

the numerical value assigned to drinking water<br />

standards defining the maximal or minimal legal<br />

concentration or value of a parameter.<br />

water supplied for human consumption or food<br />

production which is not provided by a water<br />

undertaker or licensed water supplier.<br />

a single cell organism that can only survive<br />

by infecting a host.<br />

drinking water quality information made available<br />

to the public by water companies as required<br />

by regulations.<br />

60


W estern re gion<br />

Public supplies<br />

Raw water<br />

Regulations<br />

Remedial action<br />

Residual disinfectant<br />

Risk assessment<br />

Secretary of State<br />

Selenium<br />

Service connection<br />

Service pipe<br />

Service reservoir<br />

Sodium<br />

Springs<br />

water supplied by a company licensed for<br />

that purpose.<br />

water prior to receiving treatment for the purpose<br />

of drinking.<br />

The W ater Supply (W ater Quality) Regulations<br />

2000 (England), 2010 (W ales).<br />

action taken to improve a situation.<br />

the small amount of chlorine or chloramines<br />

present in drinking water to maintain its quality<br />

as it passes through the water company’s<br />

network of pipes and household plumbing.<br />

a review undertaken to identif y actual or<br />

potential hazards to human health in a water<br />

treatment works and associated supply s ystem.<br />

Prioritisation of risk is based on consideration of<br />

likelihood and consequence of the risk occurring.<br />

Secretary of State for Environment, Food<br />

and Rural Affairs.<br />

is an essential element and a neces sary dietary<br />

component. Amounts in drinking water are<br />

usually well below the standard. A European<br />

health-based standard of 10μg/l applies.<br />

connection between the water company's main<br />

to a consumer’s property.<br />

any pipe subject to mains water pressure or<br />

subject to mains pressure but for the closing<br />

of some valve.<br />

a water tower, tank or other reservoir used<br />

for the storage of treated water within the<br />

distribution s ystem.<br />

is a component of common salt. It is present<br />

in seawater and brackish groundwater.<br />

Some treatment chemicals contain sodium.<br />

Concentrations in drinking water are extremely<br />

low, but some water softeners can add<br />

significant amounts to drinking water where they<br />

are installed in homes or factories. A national<br />

standard of 200mg/l applies.<br />

groundwater appearing at the surface at the<br />

outcrop of the junction of a permeable stratum<br />

with an impermeable stratum.<br />

61


Dri nking water 20 11<br />

Sulphate<br />

Supply pipe<br />

Supply point<br />

Surface water<br />

Taste<br />

Technical audit<br />

Tetrachloroethane and<br />

Trichloroethene<br />

Tetrachloromethane<br />

Time of supply<br />

Total indicative dose<br />

Total organic carbon<br />

Toxicology<br />

Treated water<br />

occurs naturally in all waters and is difficult to<br />

remove by treatment. An indicator parameter with<br />

a guide value of 250mg/l.<br />

see service pipe.<br />

a point other than a consumer’s tap authorised<br />

for the taking of samples for compliance with<br />

the regulations.<br />

untreated water from rivers, impounding<br />

reservoirs or other surface water source.<br />

can arise as a consequence of natural processes<br />

in surface waters, particularly between late<br />

spring and early autumn. W ater treatment with<br />

activated carbon or ozone wil l remove natural<br />

substances causing taste. The standard relates<br />

to the evaluations of a panel of people assessing<br />

samples in the laboratory.<br />

the means of checking that water companies are<br />

complying with their statutory obligations.<br />

are solvents that may occur in groundwater in<br />

the vicinity of industrial sites. W here necessary<br />

they are removed by specialist treatment.<br />

A European health-based standard of 10μg/l<br />

for the sum of both substances applie s.<br />

is a solvent that may occur in groundwater in the<br />

vicinity of industrial sites. W here necessary it is<br />

removed by specialist water treatment.<br />

A national standard of 3 μg/l applies.<br />

the moment when water passes from the water<br />

company’s pipework into a consumer’s pipework.<br />

is a measure of the effective dose of radiation<br />

the body will receive from consumption of the<br />

water. It is calculated only when screening<br />

values for gross alpha or gross beta (radiation)<br />

are exceeded. An indicator parameter with a<br />

guide value of 0.10mSv/year.<br />

represents the total amount of organic matter<br />

present in water. An indicator parameter with<br />

a guide value of ‘no abnormal change’.<br />

the study of the health effects of substances.<br />

water treated for use for domestic purposes as<br />

defined in the regulations.<br />

62


W estern re gion<br />

Trihalomethanes<br />

Tritium<br />

Turbidity<br />

Undertakings<br />

Vinyl chloride<br />

<strong>Water</strong> supply zone<br />

WHO<br />

Wholesome/wholesomeness<br />

are formed during disinfection of water by a<br />

reaction between chlorine and naturally occurring<br />

organic substances. Their production is<br />

minimised by good operational practice.<br />

A European health-based standard of 100μg/l<br />

applies.<br />

is a radioactive isotope of hydrogen.<br />

Discharges to the environment are strictly<br />

controlled and there is a national programme<br />

of monitoring surface waters. An indicator<br />

parameter with a guide value of 100Bq/l.<br />

is a measure of the cloudiness of water. At<br />

treatment works, measurement is an important<br />

non-specific water quality control parameter<br />

because it can be monitored continuously on line<br />

and alarms set to alert operators to deterioration<br />

in raw water quality or the ne ed to optimise<br />

water treatment. An indicator parameter with a<br />

guide value of 1NTU. W hen detected at the<br />

consumer’s tap it can arise from disturbance of<br />

sediment within water mains. A national standard<br />

of 4NTU applies in this case.<br />

legally binding programmes of work agreed<br />

between a water company and the Chief<br />

Inspector of <strong>Drinking</strong> W ater to address actual<br />

or potential water quality issues.<br />

may be present in plastic pipes as a residual of<br />

the manufacturing process of polyvinyl chloride<br />

(PVC) water pipes. Its presence in drinking water<br />

is controlled by product specification.<br />

A European health-based standard of 0.5μg/l<br />

applies.<br />

a pre-defined area of supply for establishing<br />

sampling frequencies, compliance with standards<br />

and information to be made publicly available.<br />

W orld Health Organisation.<br />

a legal concept of water quality which is defined<br />

by reference to standards and other<br />

requirements set out in the regulations.<br />

63


Dri nking water 20 11<br />

Annex 3<br />

Not significant and minor drinking water quality events<br />

Nature Number of not significant and minor events Area affected (estimate of pop ulation affected)<br />

Chemical 4 – BRL (1), SW T (1), W SX (1) Milborne St Andrew, Dorset (3)<br />

Penzance, Cornwall (3)<br />

W eston-Super-Mare and surrounding area<br />

(108,652)<br />

Discolouration 5 – SW T (2), W SX (3) Bridgwater, Somerset (2,870)<br />

Exeter, Devon (1,200)<br />

Taunton, Somerset (1,250)<br />

Melksham, W iltshire (3,400)<br />

Chasewater, Cornwall (4,125)<br />

Loss of supplies/<br />

poor pressure<br />

5 – BRL (1), SW T (1), W SX (3) Fovant, W iltshire (90)<br />

Minehead, Somerset (3,250)<br />

St Ives, Cornwall (5,152)<br />

W arminster, W iltshire (4,500)<br />

Lympsham, Somerset (1,250)<br />

Microbiological 8 – BRL (2), SW T (3), W SX (3) Bristol and W eston -Super-Mare (200,000)<br />

Dorchester, Dorset (78)<br />

Plymouth, Devon (3)<br />

Bristol (3)<br />

St Austell, Cornwall (5)<br />

Taunton, Somerset (3)<br />

Truro, Cornwall (3)<br />

Hullavington, W iltshire (3)<br />

Public concern 7 – BRL (1), SW T (3), W SX (3) Chittlehamholt, Devon (3)<br />

Plympton, Devon (50)<br />

Stock wood, Bristol (3)<br />

Loxbeare, Devon (8)<br />

Cherhill, W iltshire (3)<br />

Shaftesbury, Dorset (5)<br />

Litton Cheney (3)<br />

64


W estern re gion<br />

Nature Number of not significant and minor events Area affected (estimate of pop ulation affected)<br />

Taste or odour 6 – BRL (1), SW T (3), W SX (2) Crantock, Cornwall (3)<br />

Bath (3)<br />

Exeter, Devon (3)<br />

W est Lulworth, Dorset (3)<br />

W esterleigh, South Gloucestershire (100)<br />

Truro, Cornwall (3)<br />

Total 34 –BRL (6), SWT (13), WSX (15 ) 336,033<br />

Significant, serious and major drinking water quality events<br />

Date and<br />

duration<br />

25 May 2011<br />

For 36 hours<br />

(SW T)<br />

Area<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

City of Truro 11,250 Discolouration due to<br />

planned work.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

South West <strong>Water</strong> Ltd action :<br />

Repaired main.<br />

Replaced faulty equipment.<br />

Sampled affected area.<br />

Flushed mains.<br />

DWI comments and findings:<br />

Suggested that the com pany annotates its mains records<br />

to ensure that appropriate warning flag put on the key<br />

valve.<br />

Suggested that to meet the r equirements of the<br />

Information Direction , where an event has a clear<br />

second phase, the company continues to keep<br />

stakeholders informed and acts in a proactive m anner.<br />

Company did not forewarn customers.<br />

Recommended advance notification of consumers in<br />

planned work situations where risk of discolouration has<br />

been identified.<br />

The company was reminded of the contents of<br />

Information Letter 16/2000 relating to warning<br />

consumers and carrying out work on the network<br />

resulting in discolouration to supplies.<br />

Risk classification: Significant.<br />

65


Dri nking water 20 11<br />

Date and<br />

duration<br />

05 Jun 2011<br />

For 38 hours<br />

(BRL)<br />

Area<br />

Burnham on<br />

Sea, Somerset<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

17,500 Loss of supplies with<br />

media interest.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

Bristol <strong>Water</strong> Plc action:<br />

Repaired main.<br />

Sampled affected area.<br />

Provided bottled water on request.<br />

Flushed mains.<br />

The company made a repair to a strategic main following<br />

large scale burst with m edia interest causing public<br />

concern.<br />

DWI comments and findings:<br />

Did not notify <strong>Inspectorate</strong> – the company chose to email<br />

the <strong>Inspectorate</strong> rather than use the cascade sys tem.<br />

Reminded company of telephone cascade system which<br />

must be used for first notification, e -mail is appropriate<br />

only for follow-on comm unications.<br />

Risk classification: Significant.<br />

17 Jun 2011<br />

For 24 hours<br />

(SW T)<br />

Exmouth and<br />

East Devon<br />

coastal area<br />

93,085 Microbiological<br />

contamination.<br />

South West <strong>Water</strong> Ltd action:<br />

Increased chlorine residuals in the distribution s ystem.<br />

Sampled affected area.<br />

Carried out a laboratory audit to verify the analytical<br />

procedure and staff com petence.<br />

Carried out sampler checks .<br />

Inspections of treated water storage tanks.<br />

DWI comments and findings:<br />

Checks by company found nothing untoward.<br />

The <strong>Inspectorate</strong> is content with th e actions taken by the<br />

company.<br />

No recommendations or suggestions made.<br />

Risk classification: Significant.<br />

66


W estern re gion<br />

Date and<br />

duration<br />

21 Aug 2011<br />

For 4 days<br />

(SBW )<br />

Area<br />

East End,<br />

Bucklers Hard<br />

and East<br />

Bolder<br />

Villages, New<br />

Forest,<br />

Hampshire<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

2,150 Failure of the<br />

disinfection s ystem.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

Sembcorp Bournemouth <strong>Water</strong> Ltd action:<br />

Flushed mains.<br />

Sampled affected area.<br />

Modified the system logic for th e forward predictive<br />

dosing of sodium bisulphite to prevent further problems<br />

with chloramination.<br />

DWI comments and findings:<br />

Unacceptable delay in notifying local/health authorities.<br />

Unacceptable delay in notifying <strong>Inspectorate</strong>.<br />

Samples not analysed for a ppropriate parameters.<br />

Sampling was not timely enough.<br />

Inadequate risk assessment.<br />

Recommended adequate and timely samples are<br />

collected as required by Regulation 10.<br />

Recommended review and staff briefing about<br />

responding to a rapidly changing situation cr eating a<br />

large number of alarms, and putting in place a clear set<br />

of escalation procedures .<br />

Critical of failure to notify appropriate stakeholders.<br />

Critical of failure to provide accurate documentation to<br />

the <strong>Inspectorate</strong>.<br />

Recommended that the company carr y out a risk<br />

assessment including contingency measures, when<br />

control critical equipment is removed for maintenance .<br />

Critical that such a key part of the process was so slow<br />

to react to changing conditions and that the company<br />

had failed to recognise this p rior to the event.<br />

Suggested that the com pany investigate any similar set -<br />

ups at other sites and m ake corrections as required.<br />

Risk classification: Significant.<br />

67


Dri nking water 20 11<br />

Date and<br />

duration<br />

01 Sep 2011<br />

For 3 days<br />

(BRL)<br />

Area<br />

Long Ashton,<br />

North<br />

Somerset<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

3,292 Discolouration due to<br />

planned work.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

Bristol <strong>Water</strong> Plc action:<br />

Flushed mains.<br />

Review of procedures.<br />

Sampled affected area.<br />

Improved procedures for updating GIS.<br />

DWI comments and findings:<br />

Inadequate contingenc y planning.<br />

Samples not analysed for appropriate parameters in<br />

contravention of Regulation 10.<br />

Inadequate risk assessment.<br />

Inadequate procedures.<br />

Critical that the risk ass essment carried out in advance<br />

of the work was based on a short section of main and<br />

did not take into account the properties fed by the 24"<br />

trunk main downstream of the new pipework. The new<br />

pipework had been connected to an abandoned section<br />

of main, geographic information system ( GIS) records<br />

were incorrect and the main had been inadequately<br />

capped off.<br />

Recommendations were made in respect of risk<br />

assessment procedures, GIS records, main capping.<br />

25 Oct 2011<br />

For 4 days<br />

(SW T)<br />

Cornwall , west<br />

of Bodmin<br />

Moor, supplied<br />

by Restormel<br />

works<br />

3,773 Musty taste or odour<br />

due to low levels of<br />

methyl-isoborneol and<br />

geosmin.<br />

Risk classification: Significant.<br />

South West <strong>Water</strong> Ltd action:<br />

Sampled affected area.<br />

Implemented/optimised powdered activated carbon<br />

dosing at both works.<br />

DWI comments and findings:<br />

No recommendations or suggestions made.<br />

Restormel works was subject to enforcement<br />

(undertaking) for pesticides prior to this event. The<br />

company has been evaluating the use of advanced<br />

oxidation processes in c ombination with granular<br />

activated carbon to provide a more robust barrier before<br />

making a decision on the final solution. The work is due<br />

to be completed b y 31 March 2014.<br />

Risk classification: Significant.<br />

68


W estern re gion<br />

Date and<br />

duration<br />

04 Nov 2011<br />

For 16 hours<br />

(BRL)<br />

Area<br />

Broom Hill<br />

Brislington,<br />

Bristol<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

6,163 Discolouration due to<br />

a burst main.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

Bristol <strong>Water</strong> Plc action:<br />

Repaired main.<br />

Sampled affected area.<br />

DWI comments and findings:<br />

The <strong>Inspectorate</strong> sugges ted that the company make a<br />

full risk assessment of any activity carried out by a third<br />

party to assess the risks posed to water quality by<br />

planned works and that these risks are fully documented<br />

and mitigated against.<br />

Risk classificatio n: Significant.<br />

02 Dec 2011<br />

For 3 weeks<br />

(SW T)<br />

Areas of<br />

Helston and<br />

the Lizard<br />

Peninsula<br />

supplied by<br />

W endron<br />

works<br />

22,500 Evidence of chemical<br />

contamination<br />

(mecoprop).<br />

South West <strong>Water</strong> Ltd action:<br />

By-passed service reservoir.<br />

Flushed mains.<br />

Sampled affected area.<br />

DWI Comments and findings:<br />

Inadequate treatment process ; no dedicated organic<br />

micro-pollutant barrier.<br />

Powdered activated carbon dosing is in place as short -<br />

term mitigation.<br />

Catchment investigation and enhanced monitoring being<br />

used to identify point sources of pollution and the<br />

company has enhanced water quality monitoring in place<br />

to identify any increases in pesticide levels at an early<br />

stage.<br />

Risk classification: Significant.<br />

69


Dri nking water 20 11<br />

Date and<br />

duration<br />

05 Dec 2011<br />

For 3 days<br />

(W SX)<br />

Area<br />

Trowbridge,<br />

W iltshire<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

5,700 Loss of supplies due<br />

to a burst main.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

Wessex <strong>Water</strong> Services Ltd action:<br />

Repaired main.<br />

Sampled affected area.<br />

Provided an alternative supply by tanker /bowser.<br />

The company rezoned the area and repaired the main<br />

that was damaged by a third party.<br />

Alternative supply arrangements were provide d and<br />

bottled water on request to those areas that could not be<br />

fed reliably during the repair operation.<br />

Flushing operations cleared the discolouration within 48<br />

hours.<br />

DWI comments and findings:<br />

No recommendations o r suggestions made .<br />

Risk classification: Significant.<br />

13 Dec 2011<br />

For 16 hours<br />

(BRL)<br />

Churchill,<br />

Langford &<br />

W rington,<br />

Bristol<br />

4,250 Discolouration due to<br />

planned work.<br />

Bristol <strong>Water</strong> Plc action:<br />

Repaired main.<br />

Sampled affected area.<br />

Flushing operation cl eared the discolouration within<br />

48 hours.<br />

DWI comments and findings:<br />

Suggestion that the com pany considers making a full<br />

assessment of any activity involving third parties not<br />

under the direct control of the company and appraises<br />

the extent of potential risks to the planned operation and<br />

water quality, and that the company subsequently<br />

documents contingency and control measures arising<br />

from any identified risks.<br />

Risk classification: Significant.<br />

70


W estern re gion<br />

Date and<br />

duration<br />

20 Dec 2011<br />

For 1 day<br />

(SW T)<br />

Area<br />

Looe, St.<br />

Blazey,<br />

Liskeard and<br />

surrounding<br />

areas,<br />

Cornwall<br />

Estimate of<br />

population<br />

affected<br />

Nature and cause of<br />

the event<br />

10,000 Microbiological<br />

contamination.<br />

Main actions and findings from the <strong>Inspectorate</strong><br />

investigation<br />

South West <strong>Water</strong> Ltd action:<br />

Sampled affected area.<br />

Company removed Bodelver service reservoir from<br />

service for cleaning and inspection. No issues were<br />

identified at the service reservoir. The company have<br />

started enabling works to allow the treated water tank at<br />

St Cleer to be removed from supply and inspected.<br />

DWI comments and findings:<br />

No cause was identified for the microbiological failures.<br />

Suggestion made that company should collect more<br />

frequent, larger volume samples in response to any<br />

future faecal coliform contamination detected at works.<br />

Risk classification: Significant.<br />

22 Dec 2011<br />

For 3 days<br />

(BRL)<br />

Congyre Grove<br />

near Bristol<br />

30 Microbiological<br />

contamination.<br />

Bristol <strong>Water</strong> Plc action:<br />

Repaired main.<br />

Sampled affected area.<br />

Made changes to company procedures.<br />

DWI comments and findings:<br />

No recommendations or suggestions made .<br />

Risk classification: Significant.<br />

71


Dri nking water 20 11<br />

Annex 4<br />

Planned drinking water quality improvements<br />

Compan y<br />

Parameter,<br />

hazard or driver<br />

Site<br />

Due for<br />

completion *<br />

Status *<br />

Legal<br />

Instrument<br />

BRL Cryptosporidium Cheddar 31-Dec-13 Ongoing Notice<br />

BRL Cryptosporidium Littleton 31-Dec-12 Ongoing Notice<br />

BRL Cryptosporidium Purton 31-Dec-11<br />

Completed<br />

05-Jan-12<br />

Notice<br />

BRL Cryptosporidium Shipton Moyne 31-Dec-12 Ongoing Notice<br />

BRL Cryptosporidium Stowey 31-Dec-13 Ongoing Notice<br />

BRL<br />

Iron<br />

Trunk mains<br />

rehabilitation<br />

31-Mar-15 Ongoing Undertaking<br />

BRL Lead Sherborne 31-Jul-13 Ongoing Notice<br />

BRL Metaldehyde Banwell catchment 31-Mar-15 Ongoing Undertaking<br />

BRL<br />

Metaldehyde<br />

Littleton and<br />

Purton catchments<br />

31-Mar-15 Ongoing Undertaking<br />

BRL Metaldehyde Stowey catchment 31-Mar-15 Ongoing Undertaking<br />

BRL Nitrate Frome 04-Sep-14 Ongoing Undertaking<br />

BRL<br />

Total<br />

Trihalomethanes<br />

Littleton<br />

31-Dec-11<br />

Completed<br />

15-Dec-12<br />

Undertaking<br />

CHO Nitrate Cholderton 31-Mar-13 Ongoing Undertaking<br />

SBW<br />

Coliform bacteria,<br />

E.coli<br />

Alderney<br />

14-Feb-11<br />

SBW Cryptosporidium W oodgreen 31-Dec-11<br />

SBW<br />

SW T<br />

Iron, Turbidity<br />

and Polycyclic<br />

aromatic<br />

hydrocarbons<br />

Cryptosporidium,<br />

Colour and<br />

Turbidity<br />

Completed<br />

14-Feb-11<br />

Completed<br />

31-Dec-11<br />

Undertaking<br />

Notice<br />

Distribution s ystem 31-Mar-15 Ongoing Undertaking<br />

Bovey Cross<br />

31-Mar-12<br />

Completed<br />

07-Jan-11<br />

Notice<br />

SW T Iron and Turbidity Greatwell 31-Dec-11 Delayed Undertaking<br />

SW T<br />

Lead<br />

Drift, Restormel<br />

Central, Dotton<br />

and Pynes Central<br />

SW T Manganese Tottiford 31-Mar-12<br />

SW T Pesticides Drift 31-Mar-12<br />

31-Mar-15 Ongoing Undertaking<br />

Completed<br />

12-Mar-12<br />

Completed<br />

30-Mar-12<br />

Undertaking<br />

Undertaking<br />

SW T Pesticides Restormel 31-Mar-14 Ongoing Undertaking<br />

SW T<br />

SW T<br />

Taste, Odour and<br />

Manganese<br />

Total<br />

Trihalomethanes<br />

Stithians<br />

31-Mar-10<br />

Completed<br />

25-Jan-11<br />

Undertaking<br />

W endron 31-Dec-14 Ongoing Undertaking<br />

W SX 2,4-D (pesticide) Fovant TBC Pending TBC<br />

72


W estern re gion<br />

Compan y<br />

W SX<br />

Parameter,<br />

hazard or driver<br />

Chlortoluron,<br />

Isoproturon,<br />

MCPA, MCPB,<br />

2,4-D and<br />

Metazachlor<br />

Site<br />

Friar W addon<br />

Due for<br />

completion *<br />

31-Jan-11<br />

Status *<br />

Completed<br />

01-Jan-12<br />

Legal<br />

Instrument<br />

Undertaking<br />

W SX Coliform bacteria Moorbrake Camp 31-Mar-13 Ongoing Notice<br />

W SX<br />

W SX<br />

Contamination<br />

from catchment<br />

Contamination<br />

from catchment<br />

Brixton Deverill<br />

Portesham<br />

31-Mar-10<br />

30-Sep-10<br />

W SX Cryptosporidium Dewlish 31-Mar-12<br />

Completed<br />

23-Mar-12<br />

Completed<br />

07-Mar-11<br />

Completed<br />

07-Nov-11<br />

Notice<br />

Notice<br />

Notice<br />

W SX Cryptosporidium Dunkerton 31-Mar-13 Ongoing Notice<br />

W SX Cryptosporidium Tatworth 31-Mar-13 Ongoing Notice<br />

W SX Cryptosporidium Tollerdown 31-Mar-14 Ongoing Notice<br />

W SX<br />

Cryptosporidium<br />

Upton Scudamore<br />

Comb<br />

31-Mar-12<br />

Completed<br />

11-Aug-11<br />

Notice<br />

W SX Cryptosporidium W iddenham 31-Mar-14 Ongoing Notice<br />

W SX E.coli Grange 31-Mar-12<br />

W SX E.coli Grove New 31-Mar-13<br />

Completed<br />

30-Mar-12<br />

Completed<br />

05-May-11<br />

Notice<br />

Notice<br />

W SX E.coli Tucking Mill N/A Ongoing Notice<br />

W SX Iron Danesborough 30-Jun-11<br />

W SX<br />

W SX<br />

Iron, Manganese<br />

and Turbidity<br />

Isoproturon,<br />

Pesticides,<br />

Mecoprop,<br />

Chlortoluron and<br />

Taste and Odour<br />

Trunk mains<br />

renovation<br />

Completed<br />

30-Dec-11<br />

Undertaking<br />

31-Mar-15 Ongoing Undertaking<br />

Sutton Bingham 31-Mar-14 Ongoing Undertaking<br />

W SX Lead Distribution s ystem 31-Mar-15 Ongoing Undertaking<br />

W SX<br />

W SX<br />

Metaldehyde<br />

(pesticide)<br />

Nitrate<br />

Durleigh catchment 31-Mar-15 Ongoing Undertaking<br />

Dunkerton,<br />

Chirton, Fonthill<br />

Bishop,<br />

Sturminster<br />

Marshall/Shapwick ,<br />

Hooke, Bulbridge<br />

and W ylye<br />

31-Mar-18 Ongoing Undertaking<br />

W SX Taste and Odour Blashford 31-Mar-14 Delayed Undertaking<br />

*Dates used are those for the completio n of the agreed programme of work. There is a<br />

further period of 12 months before a programme is officially closed to as certain the<br />

benefits of the work to consumers.<br />

73


Dri nking water 20 11<br />

Delayed programmes<br />

Compan y<br />

Parameter, hazard<br />

or driver<br />

Site<br />

Reason for dela y<br />

SW T Iron and Turbidity Greatwell Commissioning issues<br />

W SX Taste and Odour Blashford Change of solution<br />

Acknowledged actions to sustain safe, clean drinking<br />

water<br />

Additional<br />

acknowledged<br />

actions to mitigate<br />

risk<br />

(as at Dec 2008)<br />

Acknowledged actions<br />

completed (as at Dec<br />

2010)<br />

Acknowledged actions<br />

completed (as at Dec 2011)<br />

38 25 26<br />

74


W estern re gion<br />

Annex 5<br />

Competition in the water industry<br />

The following table indicates the extent of competition in the water<br />

industry in England and Wales.<br />

Inset appointments in place in 2011<br />

Site Appointee Incumbent and region Status<br />

Shotton Paper,<br />

Shotton<br />

Albion W ater<br />

Dŵr Cymru W elsh W ater,<br />

W ales<br />

Supplying<br />

water<br />

Buxted Chicken,<br />

Flixton<br />

Anglian W ater Essex and Suffolk W ater,<br />

Central and Eastern region<br />

Supplying<br />

water<br />

W ynyard, near<br />

W olviston<br />

Berryfields,<br />

Aylesbury<br />

Brooklands, Milton<br />

Keynes<br />

Great Billing W ay,<br />

Northampton<br />

Kings Cross,<br />

London<br />

Long Croft Road,<br />

Corby<br />

Priors Hall, Corby<br />

The Bridge,<br />

Dartford<br />

Media City,<br />

Salford Quays<br />

Bromley Common,<br />

Bromley<br />

Farndon Road,<br />

Market<br />

Harborough<br />

Graylingwell,<br />

Chichester<br />

Great W estern<br />

Park, Didcot<br />

Hale Village,<br />

Tottenham<br />

Kennet Island,<br />

Reading<br />

Kingsmere,<br />

Bicester<br />

Llanilid Park,<br />

South W ales<br />

New South<br />

Quarter, Croydon<br />

Park Views,<br />

Epsom<br />

Hartlepool W ater<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Independent W ater<br />

Networks Ltd<br />

Peel W ater<br />

Networks Ltd<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

SSE W ater<br />

Northumbrian W ater,<br />

Northern region<br />

Thames W ater, London and<br />

South East region<br />

Anglian W ater,<br />

Central and Eastern region<br />

Anglian W ater,<br />

Central and Eastern region<br />

Thames W ater, London and<br />

South East region<br />

Anglian W ater,<br />

Central and Eastern region<br />

Anglian W ater,<br />

Central and Eastern region<br />

Thames W ater, London and<br />

South East region<br />

United Utilities, Northern<br />

region<br />

Thames W ater, London and<br />

South East region<br />

Severn Trent W ater/ Anglian<br />

W ater, Central and Eastern<br />

region<br />

Portsmouth W ater/Southern<br />

W ater, London and South<br />

East region<br />

Thames W ater, London and<br />

South East region<br />

Thames W ater, London and<br />

South East region<br />

Thames W ater, London and<br />

South East region<br />

Thames W ater, London and<br />

South East region<br />

Dŵr Cymru W elsh W ater,<br />

W ales<br />

Thames W ater, London and<br />

South East region<br />

Thames W ater, London and<br />

South East region<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

75


Dri nking water 20 11<br />

Site Appointee Incumbent and region Status<br />

Riverside, Barking SSE W ater Essex and Suffolk<br />

W ater/Thames W ater,<br />

Central and Eastern region<br />

The Portway, near<br />

Salisbury<br />

Fairfield Park and<br />

Lower W ilbury<br />

Farm, Arlesey<br />

MoD Tidworth<br />

near Andover<br />

SSE W ater<br />

Veolia W ater<br />

Central<br />

Veolia W ater<br />

Projects<br />

W essex W ater,<br />

W estern region<br />

Anglian W ater, Central and<br />

Eastern region<br />

W essex W ater,<br />

W estern region<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

Supplying<br />

water<br />

New inset appointments in 2011<br />

Site Appointee Incumbent and<br />

region<br />

Kennet Island<br />

(Phase 7), Reading<br />

SSE W ater<br />

Thames W ater,<br />

London and South<br />

East region<br />

Status<br />

Appointment<br />

granted<br />

76


W estern re gion<br />

Annex 6<br />

<strong>Water</strong> company indices<br />

Bristol <strong>Water</strong> plc<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 17<br />

Number of service reservoirs 169<br />

Number of water supply zones 52<br />

Length of mains pipe (km) 6,670<br />

Population served<br />

Population supplied 1,155,305<br />

Number of local authorities 9<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

301<br />

(Ml/day)<br />

Percentage from<br />

81<br />

surface sources<br />

Percentage from<br />

12<br />

ground sources<br />

Percentage from<br />

7<br />

mixed sources<br />

Area of supply<br />

Gloucestershire, Wiltshire, Bristol,<br />

Somerset<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 99.97% 99.96% 99.96% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 100% 99.86% 99.99% 99.99%<br />

Disinfection Index 100% 99.97% 99.99% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 99.88% 99.89% 99.59% 99.88%<br />

Reservoir Integrity Index 99.97% 99.99% 99.98% 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

99.85% 99.96% 99.92% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 1,048 1,028 888 N/A<br />

Rate per 1,000 population 0.94 0.90 0.77 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 2,917 2,935 2,567 N/A<br />

Rate per 1,000 population 2.63 2.58 2.22 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong><br />

A total of 1 consumer of Bristol W ater plc directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi .gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean zon al com pliance for 39<br />

par am eters .<br />

77


Dri nking water 20 11<br />

Cholderton and District <strong>Water</strong> Company Ltd<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 2<br />

Number of service reservoirs 1<br />

Number of water supply zones 1<br />

Length of mains pipe (km) 30<br />

Population served<br />

Population supplied 2,100<br />

Number of local authorities 2<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

(Ml/day)<br />

0.685<br />

Percentage from<br />

surface sources<br />

0<br />

Percentage from<br />

ground sources<br />

100<br />

Percentage from<br />

mixed sources<br />

0<br />

Area of supply<br />

Small parts of Wiltshir e & Hampshire<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 100% 100% 100% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 100% 100% 100% 99.99%<br />

Disinfection Index 100% 99.36% 100% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 100% 100% 100% 99.88%<br />

Reservoir Integrity Index 100% 100% 100% 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

100% 100% 100% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 0 0 0 N/A<br />

Rate per 1,000 population 0 0 0 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 0 0 0 N/A<br />

Rate per 1,000 population 0 0 0 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong><br />

No consumers of Cholderton and District W ater Company Ltd directly contacted DW I<br />

in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vid ual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean zon al com pliance for 39<br />

par am eters .<br />

78


W estern re gion<br />

Semcorp Bournemouth <strong>Water</strong> Ltd<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 8<br />

Number of service reservoirs 20<br />

Number of water supply zones 10<br />

Length of mains pipe (km) 2,808<br />

Population served<br />

Population supplied 430,000<br />

Number of local authorities 6<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

148<br />

(Ml/day)<br />

Percentage from<br />

85<br />

surface sources<br />

Percentage from<br />

15<br />

ground sources<br />

Percentage from<br />

0<br />

mixed sources<br />

Area of supply<br />

Parts of Dorset, Hampshire and<br />

Wiltshire<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 99.99% 99.94% 99.98% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 99.99% 100% 100% 99.99%<br />

Disinfection Index 99.90% 99.87% 99.95% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 100% 100% 99.82% 99.88%<br />

Reservoir Integrity Index 99.95% 100% 100% 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

99.96% 99.73% 99.95% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 263 292 380 N/A<br />

Rate per 1,000 population 0.62 0.68 0.89 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 570 505 477 N/A<br />

Rate per 1,000 population 1.34 1.18 1.12 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> Inspectorat e<br />

No consumers of Semcorp Bournemouth W ater Ltd directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean zon al com pliance for 39 par am eters .<br />

79


Dri nking water 20 11<br />

South West <strong>Water</strong> Ltd<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 31<br />

Number of service reservoir s 312<br />

Number of water supply zones 32<br />

Length of mains pipe (km) 15,000<br />

Population served<br />

Population supplied 1,696,000<br />

Number of local authorities 17<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

433<br />

(Ml/day)<br />

Percentage from<br />

93<br />

surface sources<br />

Percentage from<br />

6<br />

ground sources<br />

Percentage from<br />

1<br />

mixed sources<br />

Area of supply<br />

Devon, Cornwall, Somerset (part),<br />

Dorset (part)<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 99.98% 99.97% 99.99% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 100% 100% 100% 99.99%<br />

Disinfection Index 99.98% 99.97% 99.97% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 99.91% 99.89% 99.94% 99.88%<br />

Reservoir Integrity Index 99.93% 99.93% 99.97% 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

99.97% 99.91% 99.97% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 1,951 1,812 1,113 N/A<br />

Rate per 1,000 population 1.16 1.08 0.66 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 14,675 11,085 11,653 N/A<br />

Rate per 1,000 population 8.72 6.59 6.87 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong><br />

A total of 3 consumers of South W est W ater Ltd directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean zon al com pliance for 39 par am eters .<br />

80


W estern re gion<br />

SSE <strong>Water</strong><br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 0<br />

Number of service reservoirs 0<br />

Number of water supply zones 11<br />

Length of mains pipe (km) 22<br />

Population served<br />

Population supplied 5,000<br />

Number of local authorities 12<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

0.661<br />

(l/day)<br />

Percentage from<br />

39<br />

surface sources<br />

Percentage from<br />

48<br />

ground sourc es<br />

Percentage from<br />

13<br />

mixed sources<br />

Area of supply<br />

Old Sarum, near Salisbury;<br />

Hale Village, Tottenham; Graylingwell,<br />

Chichester; Bromley Common,<br />

Bromley; Kennet Island, Reading; Park<br />

Views, Epsom; Llanilid Park, South<br />

Wales; Kingsmere, Bicester; Great<br />

<strong>Western</strong> Park, Didcot; Barking<br />

Riverside, Barking; Farndon Road,<br />

Market Harborough<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 100% 100% 100% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index N/A N/A N/A 99.99%<br />

Disinfection Index N/A N/A N/A 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 100% 100% 100% 99.88%<br />

Reservoir Integrity Index N/A N/A N/A 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

100% 100% 100% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 1 1 2 N/A<br />

Rate per 1,000 population 0.74 0.5 0.39 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 0 2 2 N/A<br />

Rate per 1,000 population 0 0.99 0.39 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong><br />

No consumers of SSE W ater directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean z on al com pliance for 39 par am eters .<br />

81


Dri nking water 20 11<br />

Veolia <strong>Water</strong> Projects Ltd<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 2<br />

Number of service reservoirs 6<br />

Number of water supply zones 1<br />

Length of mains pipe (km) 98<br />

Population served<br />

Population supplied 8,000<br />

Number of local authorities 1<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

(Ml/day)<br />

Percentage from<br />

surface sources<br />

Percentage from<br />

ground sources<br />

Percentage from<br />

mixed sources<br />

Area of supply<br />

Tidworth, Wiltshire<br />

4<br />

0<br />

100<br />

0<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water quality* 100% 100% 100% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 100% 100% 100% 99.99%<br />

Disinfection Index 100% 100% 100% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 100% 100% 100% 99.88%<br />

Reservoir Integrity Index 100% 100% 100% 99.96%<br />

Building water systems<br />

Parameters influenced by domestic<br />

water s ystems<br />

100% 100% 100% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 16 1 0 N/A<br />

Rate per 1,000 population 1.74 0.12 0 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 3 6 4 N/A<br />

Rate per 1,000 population 0.33 0.73 0.48 1.91<br />

Complaints to the <strong>Drinking</strong> W ater <strong>Inspectorate</strong><br />

No consumers of Veolia W ater Projects Ltd directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.g ov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep resented by mean zon al com pliance for 39 par am eters .<br />

82


W estern re gion<br />

Wessex <strong>Water</strong> Services Ltd<br />

<strong>Water</strong> supply arrangements<br />

Company assets<br />

Number of treatment works 95<br />

Number of service reservoirs 301<br />

Number of water supply zones 91<br />

Length of mains pipe (km) 11,500<br />

Population served<br />

Population supplied 1,237,680<br />

Number of local authorities 15<br />

<strong>Water</strong> supplied<br />

W ater supplied<br />

337<br />

(Ml/day)<br />

Percentage from<br />

27<br />

surface sources<br />

Percentage from<br />

71<br />

ground sources<br />

Percentage from<br />

2<br />

mixed sources<br />

Area of supply<br />

Large parts of Somerset, Dorset and<br />

Wiltshire, small areas of<br />

Gloucestershire and Devon<br />

<strong>Drinking</strong> water quality summary data<br />

Company figure<br />

Industry average<br />

2009 2010 2011 2011<br />

Overall drinking water<br />

quality*<br />

99.95% 99.98% 99.98% 99.96%<br />

<strong>Water</strong> treatment<br />

Process Control Index 100% >99.99% 100% 99.99%<br />

Disinfection Index 99.90% 99.95% >99.99% 99.97%<br />

Distribution systems<br />

Distribution Maintenance Index 99.97% 99.97% 99.91% 99.88%<br />

Reservoir Integrity Index 99.97% 99.98% 99.96% 99.96%<br />

Building water systems<br />

Parameters influenced by<br />

domestic water s ystems<br />

99.80% 99.94% 99.92% 99.87%<br />

Consumer contacts<br />

Company figure Industry average<br />

2009 2010 2011 2011<br />

Informing consumers<br />

Total number 1,157 1,051 1,066 N/A<br />

Rate per 1,000 population 0.98 0.81 0.86 1.21<br />

Acceptability of water to<br />

consumers<br />

Total number 3,845 3,224 2,988 N/A<br />

Rate per 1,000 population 3.26 2.47 2.41 1.91<br />

Complaints to the <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong><br />

No consumers of W essex W ater Services Ltd directly contacted DW I in 2011.<br />

Note: Sum m ary results for each com pan y of tests for indi vidual par am eters ar e suppl ied on<br />

the DW I website at http:// www.dwi.gov.uk<br />

* Ove ra ll dr inking wat er qu ality as rep r esented by mean zon al com pliance for 39 par am eters .<br />

83


Dri nking water 20 11<br />

Annex 7<br />

Information relating to public water supplies published by the<br />

<strong>Inspectorate</strong> in 2011<br />

Information Letters<br />

Ref<br />

Title<br />

01/2011 Amendment to The <strong>Water</strong> Supply (<strong>Water</strong> Quality) Regulations<br />

2010 (Wales)<br />

02/2011 DWI Enforcement Policy<br />

03/2011 Publication of World Health Organisation (WHO) document<br />

entitled '<strong>Water</strong> safety in buildings'<br />

04/2011 Guidance on the general provisions for monitoring of parameters<br />

relevant to radioactivity<br />

05/2011 Production, delivery, receipt and control of water treatment<br />

chemicals<br />

06/2011 Technical Audit of <strong>Water</strong> Companies under Section 86 of the<br />

<strong>Water</strong> Industry Act 1991: Publication of the report following the<br />

audit of STS Analytical Services at Bridgend<br />

07/2011 Implementation of the new SCA blue book 233: The<br />

determination of taste and odour in drinking waters (2010)<br />

08/2011 Publication of report: Objectionable taste and odour in water<br />

supplies in North-East London between January and March 2010<br />

The letters , an d thei r asso c iated anne xes, can be found on the Inspector ate’s website at<br />

http://dwi.defra.go v.uk/stakeholders /inform ation -l etters /inde x.htm<br />

Technical guidance<br />

<br />

DWI Approval of Enterolert-DW® Quanti-Tray® method for the<br />

determination of Enterococci in drinking water s<br />

Copi es of the abo ve gui da nce can be foun d on the Inspectorat e’s we bsite at<br />

http://dwi.defra.go v.uk/stakeholders /guidance -a nd -codes -of-p ractice/<br />

84


W estern re gion<br />

Research<br />

Ref<br />

DWI 70/2/260<br />

DWI 70/2/245<br />

DWI 70/2/224<br />

DWI 70/2/242<br />

DWI 70/2/253<br />

DWI 70/2/255<br />

DWI 70/2/208<br />

WRF 4006<br />

DWI 70/2/225<br />

DWI 70/2/189<br />

Title<br />

Alternatives to phosphate for plumbosolvency control<br />

Investigation of instances of low or negative pressures in<br />

UK drinking water systems<br />

Analytical methods for predicted disinfection by -products<br />

of probable toxicological significance<br />

Evaluation of haloacetic acid concentrations in trea ted<br />

drinking water (Cranfield University)<br />

Evaluation of haloacetic acid concentrations in treated<br />

drinking water (WRc plc)<br />

A review of fungi in drinking water and the implications for<br />

human health<br />

Critical assessment of implementing desalination<br />

technology<br />

An investigation of leaching from flexible rising mains<br />

leading from borehole pumps<br />

<strong>Water</strong> Safety in Buildings<br />

Copi es of res ea rc h re po rts and exec utive summ aries can be foun d o n the Inspec torate’s websit e<br />

at http://dwi. defra.go v.uk/researc h/com pleted -res ea rc h/20 00todate. htm<br />

85


Dri nking water 20 11<br />

Annex 8<br />

Distribution of private water supplies<br />

South West<br />

86


W estern re gion<br />

Local authorities<br />

Key<br />

Forest of Dean District Council 1<br />

Gloucester City Council 2<br />

Tewkesbury Borough Council 3<br />

Cheltenham Borough Council 4<br />

Stroud District Council 5<br />

Cots wold District Council 6<br />

South Gloucestershire Council 7<br />

W iltshire Council 8<br />

Swindon Borough Counc il 9<br />

North Somerset District Council 10<br />

Bristol City Council 11<br />

Bath and North East Somerset District Council 12<br />

North Devon District Council 13<br />

W est Somerset District Council 14<br />

Sedgmoor District Council 15<br />

Mendip District Council 16<br />

Torridge District Council 17<br />

Mid Devon District Council 18<br />

Taunton Deane Borough Council 19<br />

South Somerset District Council 20<br />

North Dorset District Council 21<br />

East Dorset District Council 22<br />

Cornwall Council 23<br />

W est Devon Borough Council 24<br />

Teignbridge District Council 25<br />

Exeter City Council 26<br />

East Devon District Council 27<br />

W est Dorset District Council 28<br />

W eymouth and Portland Borough Council 29<br />

Purbeck District Council 30<br />

Poole Borough Council 31<br />

Bournemouth Borough Council 32<br />

Christchurch Borough Council 33<br />

Plymouth City Council 34<br />

South Hams District Cou ncil 35<br />

Torbay Council 36<br />

87


<strong>Drinking</strong> <strong>Drinking</strong> <strong>Water</strong> <strong>Inspectorate</strong> <strong>Water</strong> <strong>Inspectorate</strong> | Ergon House, | 55, Whitehall Horseferry | London Road | | London SW1A 2EY | SW1P | Tel: 2AL 020 | Tel: 7270300 337068 6400<br />

http://www.dwi.gov.uk<br />

PB 13777

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