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Water
Public Water Supplies, Yield and Demand:
1981/1982 to 2003/2004

Average volume of water
(Megalitres/day)
| 1981/82 | 1990/91 | 1995/96 | 2000/01 | 2001/02 | 2002/03 | 2003/04 |
|---|
Yield from developed water
resources | 3,246 | 3,486 | 3,501 | 3,564 | 3,563 | 3,564 | 3,359 |
|---|
Daily demand from public
supplies | 2,262 | 2,301 | 2,322 | 2,401 | 2,408 | 2,387 | 2,397 |
|---|
For sustainable management of water resources, it is
essential to meet consumers' demand and standards, whilst
maintaining aquatic ecosystem health. Abstraction of water
has impacts on geology, habitats, wildlife, biodiversity,
and recreational use of water resources. To prevent low
flow levels downstream, minimum compensation flows need to
be discharged at all times. Compensation flows are
specified in the Water Orders made under the Water
(Scotland) Act 1980.
Demand for water in Scotland has increased by 6% since
1981/1982, although yield from developed resources
(representing the potential water available) is still
greater than demand. The fall in yield between 2002/2003
and 2003/2004 is principally due to including only those
sources that are currently operational. For 2003/2004,
daily demand includes an estimated 48% lost through
leakage.
1
Water demand comes from unmetered and metered potable
water, and small amounts of non-potable water. Unmetered
demand (domestic use, small industries, public use,
etc.) accounted for 80% of daily demand in
2003/2004, compared with 70% in 1981/1982. In contrast,
metered demand decreased from 28% to 20% of daily
demand.
SOURCE: SCOTTISH WATER
1
Drinking Water Quality:
1991-2003

| 1991 | 1995 | 1999 | 2000 | 2001 | 2002 | 2003 |
|---|
Number of samples taken
(000's) | 227 | 231 | 143 | 152 | 173 | 148 | 155 |
|---|
Percentage failure for total
coliforms | 7.0 | 2.6 | 1.5 | 1.1 | 0.9 | 1.3 | 0.9 |
|---|
Percentage failure for faecal
coliforms | 3.0 | 1.0 | 0.3 | 0.2 | 0.1 | 0.2 | 0.1 |
|---|
The coliform group of organisms is present in large
numbers in the gut of all warm-blooded animals and
therefore widely distributed in the environment. Their
presence in tap water indicates a breach in the integrity
of the water supply system.
The 1990 Water Supply (Water Quality) (Scotland)
Regulations set strict standards for compliance and the
success rate varies across Scotland. The major centres of
population are served by water treatment works, which are
generally well equipped to achieve the standards set.
Infrequent minor and low level failures with little
implication occur at these works. Rural areas not served by
treatment works can have water of variable quality.
Between 1991 and 2003 the percentage failure for total
coliforms fell from 7% to 0.9% and the percentage failure
for faecal coliforms fell from 3% to 0.1%.
The standard set by the Water Supply Regulations, for
95% of samples to be free of all coliforms, has been met
every year since 1992. However, the strict standard of zero
faecal coliforms in all samples has not yet been achieved,
with 0.1% of samples failing this test in 2003.
SOURCE: SCOTTISH EXECUTIVE DRINKING WATER QUALITY
DIVISION
2
River Water Quality:
1999-2004

Length (kilometres)
Classification
3 | 1999 | 2000 | 2001 | 2002 | 2003 | 2004 |
|---|
Poor | 1,077
R | 854
R | 929 | 903 | 751 | 717 |
|---|
Seriously polluted | 91 | 73
R | 83 | 56 | 53 | 51 |
|---|
Unclassified | - | 12,816
R | 11,960 | 7,999 | 5,903 | 3,807 |
|---|
Total length of network | 25,382 | 25,455
R | 25,511 | 25,445 | 25,436 | 25,434 |
|---|
Low standards of river water quality may threaten the
aquatic environment, drinking water quality and
recreational water use. Sewage, industry, urban development
and agriculture are some of the factors that may affect
river water quality.
The Scottish Environment Protection Agency (
SEPA) has established a Digitised River
Network (
DRN) to classify about 25,000km of the
approximately 100,000km of rivers and burns in Scotland.
The
DRN comprises those watercourses
draining a catchment of 10km
2 or more. Rivers are classified as
excellent, good, fair, poor or seriously polluted
according to measures of chemical, biological, nutrient and
aesthetic quality. Between 2000 and 2004 the length of
'unclassified' river fell by 70% to 3,807 km.
Between 1999 and 2004, the length of poor and seriously
polluted rivers in Scotland fell by 400km.
SEPA has set a target of a reduction of
351km in poor and seriously polluted rivers for the period
1999-2006.
4 Poor biological and nutrient quality are the most
frequent reasons for classifying rivers as poor or
seriously polluted.
SOURCE: SCOTTISH ENVIRONMENT PROTECTION AGENCY
Nitrate Concentrations in Rivers:51993-2004

Percentage of sites within band6
Band | 1993 | 1995 | 2000 | 2002 | 2003 | 2004 |
|---|
=7.5 mg N/l | 5.7 | 6.3 | 5.7 | 4.7 | 2.6 | 3.5 |
|---|
2.5 to <7.5 mg N/l | 14.1 | 13.5 | 14.1 | 14.6 | 16.7 | 14.1 |
|---|
0.75 to <2.5 mg N/l | 33.3 | 35.4 | 32.3 | 34.4 | 31.8 | 31.3 |
|---|
0.3 to <0.75 mg N/l | 13.5 | 13.0 | 16.7 | 12.5 | 14.1 | 14.1 |
|---|
<0.3 mg N/l | 33.3 | 31.8 | 31.3 | 33.9 | 34.9 | 37.0 |
|---|
The enrichment of waters by nutrients, such as nitrates
and phosphates, can damage the aquatic environment through
the accelerated growth of algae and other plant life. The
rapid growth and subsequent decay of plant organisms
depletes oxygen levels, and this can have harmful effects
upon fish and other aquatic, life a process known as
eutrophication.
High nitrate levels have a greater impact on marine and
coastal waters than freshwater, although nitrates in
freshwater will eventually reach the sea. The main source
of nitrates in freshwater is run-off from agricultural
land.
Concentrations of nitrate below 0.3 mg N/l are
considered to be natural or background levels;
7 over one-third of the sites met this classification in
2004. Between 1993 and 2004 the percentage of sites with
average nitrate concentrations =2.5 mg N/l rose to a peak
of 25.5% in 1997, before falling to 17.6% in 2004.
Regulations have been made designating 14% of the area
of Scotland
8 as Nitrate Vulnerable Zones (
NVZs).
9 In
NVZs mandatory rules on farming
practices aim to reduce nitrate water pollution from
agricultural sources.
SOURCE: SCOTTISH ENVIRONMENT PROTECTION AGENCY
Orthophosphate Concentrations in
Rivers:
10 1993-2004

Percentage of sites within band6,11
Band | 1993 | 1995 | 2000 | 2002 | 2003 | 2004 |
|---|
=250 µg P/l | 5.2 | 8.3 | 4.1 | 2.1 | 3.6 | 1.3 |
|---|
125 to <250 µg P/l | 7.3 | 8.9 | 10.4 | 5.7 | 5.7 | 6.2 |
|---|
50 to <125 µg P/l | 23.6 | 21.4 | 19.8 | 17.7 | 16.7 | 19.4 |
|---|
25 to <50 µg P/l | 20.4 | 18.2 | 19.3 | 19.8 | 18.2 | 15.0 |
|---|
<25 µg P/l | 43.5 | 43.2 | 46.4 | 54.7 | 55.7 | 58.1 |
|---|
Excess orthophosphate in freshwaters can lead to
eutrophication. The main sources of orthophosphate are
outputs from sewage treatment works and diffuse pollution
from agriculture.
Between 1993 and 2001 there was some fluctuation in the
distribution of mean orthophosphate concentrations, with
reduced precipitation in 1996 and 1997 increasing the
percentage of sites with mean concentrations =250 µg P/l.
Over this period the percentage of sites with mean
concentrations <25 µg P/l and =125 µg P/l averaged 45%
and 16% respectively. By 2004, the percentage of sites with
mean concentrations <25 µg P/l had increased to 58% and
the percentage of sites =125 µg P/l had fallen to 7.5%.
This reduction in orthophosphate concentrations is in part
due to the installation of orthophosphate removal
facilities in sewage treatment works.
Under the Urban Waste Water Treatment Directive (
UWWTD) (91/271/
EEC), the Ythan Estuary, Dean Water,
South Calder Water, River Almond, the lower part of the
River Don and their respective catchments are all
designated sensitive areas. Discharges into waters that
have been designated as sensitive require additional
treatment to remove nutrients.
SOURCE: SCOTTISH ENVIRONMENT PROTECTION AGENCY
Effluent Compliance with
Discharge Consents: 1996/1997 to 2003

Samples complying with relevant standards
(Percentage)
Type of discharge consent | 96/97 | 97/98 | 98/99 | 99/00 | 00/01 | 01/02 | 2002
12 | 2003
12 |
|---|
Trade effluent | 74 | 83 | 78 | 80 | 85 | 81 | 84 | 84 |
|---|
Public sewage | 78 | 82 | 86 | 86 | 89 | 88 | 89 | 88 |
|---|
Private sewage | 51 | 64 | 75 | 70 | 78 | 81 | 72 | 74 |
|---|
Other discharges
13 | 87 | 89 | 91 | 93 | 93 | 87 | 92 | 98 |
|---|
All discharges | 73 | 80 | 82 | 82 | 86 | 85 | 85 | 86 |
|---|
Under the Control of Pollution Act (1974) it is an
offence to cause or knowingly permit discharge of
poisonous, noxious or polluting substances to controlled
waters in Scotland. Discharges of sewage and trade effluent
into controlled waters, including all coastal and inland
waters may, however, be made under a discharge consent
authorised by the Scottish Environment Protection Agency (
SEPA). Authorisations contain conditions
on both the quality and quantity of effluent permitted.
SEPA control these discharges through
licensing and monitoring.
Point source sewage effluent is currently the most
important source of pollution affecting tidal waters in
Scotland.
The overall compliance rate increased from 73% in
1996-1997 to 86% in 2003. Compliance rates for trade
effluent and public sewage discharges have both risen by
10% since 1996-1997. Private sewage discharges show a 23%
increase in compliance rates since 1996/1997 but have
fallen from a peak of 81% in 2001/2002.
SEPA has set a target of 95% compliance
for licences issued under the Control of Pollution Act by
2003/2004.
14
SOURCE: SCOTTISH ENVIRONMENT PROTECTION AGENCY
Compliance with the
EC Bathing Water Directive (76/160/
EEC): 1988-2004

| 1988 | 1995 | 2000 | 2001 | 2002 | 2003 | 2004 |
|---|
Mandatory standard compliance
(%) | 52 | 83 | 84 | 84 | 91 | 95 | 93 |
|---|
Guideline standard (%) | 9 | 22 | 41 | 41 | 41 | 67 | 55 |
|---|
Failure to comply (%) | 48 | 17 | 16 | 16 | 9 | 5 | 7 |
|---|
Number of identified coastal bathing waters
15,16 | 23 | 23 | 58 | 58 | 58 | 58 | 58 |
|---|
High quality bathing waters are important for a wide
variety of interests and support Scotland's tourism
industry. Monitoring the quality of these waters provides
an indication of the health risks of bathing from both
direct and diffuse discharges of effluents containing
faecal contaminants.
EC Bathing Water Directive (76/160/
EEC) sets out two quality standards -
the 'mandatory' standard, and the stricter 'guideline'
standard. Member states should comply with the mandatory
standard and aim to comply with the guideline standard.
In 2004, 93% of identified coastal bathing waters
achieved the mandatory standard, and 55% also complied with
the guideline standard.
It is important to note that the weather is thought to
affect compliance, with wet weather often contributing to
poorer results and, conversely, drier, hotter weather
associated with better results. The fall in compliance
rates between 2003 and 2004 may have been a result of the
extremely wet weather of 2004.
SOURCE: SCOTTISH ENVIRONMENT PROTECTION AGENCY
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