Table
30. Summary of Guidelines for Total Gas Pressure (TGP)
Water
Use |
Recommended
Guideline |
| Drinking
Water Supply |
None
proposed |
Freshwater
and Marine Aquatic Life
- local water depth greater than 1 m
|
maximum
DP is less than or equal to
76 mm Hg or less than
or equal to
110% at sea level |
Freshwater
and Marine Aquatic Life
- background levels exceed guidelines |
no
increase in DP or % TGP |
Freshwater
and Marine Aquatic Life
- hatchery environments
|
maximum
DP = 24 mm Hg or
103% at sea level
DP=0 mm Hg when pO2 is
less than or equal to 100 mm Hg |
| Wildlife |
None
proposed |
| Livestock
Water Supply |
None
proposed |
| Irrigation |
None
proposed |
| Primary
Contact Recreation |
None
proposed |
1. DP = excess gas pressure in mm Hg.
2. p02 = partial pressure of dissolved oxygen in mm of Hg.
References
20 and 20a |
Table
31. Summary of Water Quality Guidelines for Colour
Water
Use |
Colour
Units |
Recommended
Guidelines |
Drinking
Water Supply
(without treatment for
colour removal) |
True |
15
mg/L Pt |
Aquatic
Life
Fresh, Marine and Estuarine
|
Apparent |
30-day
average transmission of white light greater than or equal
to
80% of background. |
Aquatic
Life
Fresh, Marine and Estuarine |
True |
30-day
average true colour of filtered water samples shall not
exceed background levels by more than
5 mg/L Pt in clearwater
systems or 20% in coloured systems. |
Wildlife |
Apparent |
30-day
average transmission of white light greater than or equal
to
80% of background. |
Wildlife |
True |
30-day
average true colour of filtered water samples shall not
exceed background levels by more than
5 mg/L Pt in clearwater
systems
or 20% in coloured systems. |
Recreation
and Aesthetics
- fresh, marine and estuarine |
Apparent |
Secchi
disc sighting range
greater than or equal to 1.5 m
(30-day average). |
Recreation
and Aesthetics
- fresh, marine and estuarine
|
True |
15
mg/L Pt (30-day average) |
1.
A value of 15 mg/L platinum is the existing Ministry
of Health value.
Reference
29 |

Table 32. Summary of Water Quality Guidelines for Organic Carbon
Water
Use |
Organic
Carbon |
Recommended
Guidelines |
Drinking
Water Supply
- with chlorination |
TOC |
4
mg/L source water |
Drinking
Water Supply
- other disinfection |
— |
Not
recommended |
Aquatic
Life
- fresh water |
TOC |
30-day
median ± 20% of the
median background concentration. |
Aquatic
Life
- fresh water
|
DOC |
30-day
median ± 20% of the
median background concentration. |
Wildlife |
TOC |
30-day
median ± 20% of the
median background concentration. |
Wildlife |
DOC |
30-day
median ± 20% |
Industrial
Water Supply |
— |
None
recommended |
Irrigation |
— |
None
recommended |
Recreation
and Aesthetics |
— |
None
recommended |
Livestock
Watering |
— |
None
recommended |
TOC = Total organic carbon
DOC = Dissolved organic carbon
Reference
30 |
Table 33. Recommended Guidelines for Zinc
Water
Use |
Guideline
(µg/L Total Zinc)
|
Drinking Water |
5000
|
Recreation and Aesthetics |
5000
|
Marine Life |
10
|
Livestock Watering |
2000
|
Irrigation
- soil pH less than 6
|
1000
|
Irrigation
- soil pH equal to or greater than 6
and less than 7
|
2000
|
Irrigation
- soil pH greater than or equal to 7
|
5000
|
Freshwater Aquatic Life
- maximum concentration —
water hardness less than or equal to 90
water hardness equal to 100
water hardness equal to 200
water hardness equal to 300
water hardness equal to 400
|
use
the equation
33 + 0.75 x (hardness - 90)
—
33
40
115
190
265
|
Freshwater Aquatic Life
- 30-day average concentration —
water hardness less than or equal to 90
water hardness equal to 100
water hardness equal to 200
water hardness equal to 300
water hardness equal to 400
|
use
the equation
7.5
+ 0.75 x (hardness - 90)
—
7.5
15
90
165
240
|
1.
When the ambient zinc concentration in the environment
exceeds the guideline, then further degradation of
the ambient or existing water quality should be avoided.
2.
These are instantaneous maximums. 3.
Averages are of five weekly measurements taken
over a 30-day period.
4.
Water hardness is measured as mg/L of CaCO3.
Reference
31 |

Table
34. Recommended Guidelines for Ethylbenzene
Water
Use |
Guideline
(mg/L Ethylbenzene)
|
Raw Drinking Water (aesthetics) |
0.0024 mg/L
|
Fresh Water Aquatic Life |
0.20*
mg/L
|
Marine Aquatic Life |
0.25*
mg/L
|
Recreation |
0.0024
mg/L
|
Crop Irrigation |
insufficient
data
|
Livestock Watering |
insufficient
data
|
*1.
Revised B.C. guidelines based on review of
CCME Water Quality Guidelines for Ethylbenzene
2.
All guidelines are maximum values.
Reference
28 |

Table
35. Summary of Water Quality Guidelines for Toluene
Water
Use
|
Guideline
(mg/L Toluene)
|
Raw Drinking Water (aesthetics)
|
0.024 mg/L
|
Fresh Water Aquatic Life
|
0.039
mg/L
|
Marine Estuarine Aquatic Life
|
0.33
mg/L
|
Recreation
|
none
proposed
|
Crop Irrigation
|
none
proposed
|
Livestock Watering
|
0.024
mg/L
|
1.
All guidelines are maximum total values.
Reference
33 |
Table 36. Summary of Water Quality Guidelines for Sulphate
Water
Use |
Guideline
(mg/L sulphate) |
Raw
Drinking Water (aesthetics) |
500
mg/L |
Fresh
Water Aquatic Life (maximum) |
100
mg/L |
Fresh
Water Aquatic Life (alert level) |
50
mg/L |
1.
Maximum concentration: not to be exceeded at any
time.
2.
Alert level: monitor the health of aquatic moss populations
occasionally.
Reference
34
|

Table
37. Examples of the Recommended Acute Guidelines to Protect
Freshwater Aquatic Life from the Toxic Effects of Manganese
Maximum at Specified
CaCO3 Hardness
|
Guideline
(mg/L total Manganese)
|
25 mg/L
|
0.8 mg/L
|
50 mg/L
|
1.1
mg/L
|
100 mg/L
|
1.6
mg/L
|
150 mg/L
|
2.2
mg/L
|
300 mg/L
|
3.8
mg/L
|
1.
When the ambient manganese concentration in the environment
exceeds the guideline then further degradation of
the ambient or existing water quality should be avoided.
2.
The instantaneous maximum is calculated from
less than or equal to 0.01102 hardness + 0.54.
Reference
35 |
Table
38. Examples of the Recommended Chronic Guidelines to Protect
Freshwater Aquatic Life from the Toxic Effects of Manganese
30-Day Mean at
Specified
CaCO3 Hardness
|
Guideline
(mg/L total Manganese)
|
25 mg/L
|
0.7mg/L
|
50 mg/L
|
0.8 mg/L
|
100 mg/L
|
1.0
mg/L
|
150 mg/L
|
1.3
mg/L
|
300 mg/L
|
1.9 mg/L
|
1.
When the ambient manganese concentration in the environment
exceeds the guideline then further degradation of
the ambient or existing water quality should be avoided.
2.
The mean of 5 weekly measurements over a 30-day
period is calculated from less than or equal to
0.0044 hardness + 0.605.
Reference
35 |

Table
39. Recommended Guidelines for Methyl Tertiary-Butyl Ether
(MTBE)
Water Use
|
Recommended
Guidelines
|
Raw Drinking Water (aesthetics)
|
0.02 mg/L maximum
|
Recreation and Aesthetics
|
0.02 mg/L maximum
|
Livestock Watering
|
11.0
mg/L maximum
|
Wildlife, Irrigation
|
Insufficient
Data
|
Aquatic Life (freshwater)
|
3.4 mg/L maximum
|
Aquatic
Life (marine, estuarine) |
0.44
mg/L maximum |
For livestock watering, concentrations
above the taste and odour thresholds that are below the
livestock guideline may result in certain livestock avoiding
water, reducing consumption and suffering associated adverse
effects.
Reference 36 |
Table
40. Recommended Guideline for Selenium
Water Use
|
Guideline
for Total Selenium
|
Drinking Water
|
10 µg/L maximum
|
Aquatic Life (freshwater)
|
2.0 µg/L mean
|
Aquatic Life (marine)
|
2.0 µg/L
mean
|
Aquatic Life (sediments
|
2.0 µg/g
(dry weight) mean
|
Aquatic Life (tissue)
|
1.0 µg/g body weight
(wet weight)
mean
|
Wildlife
|
4.0 µg/L
mean
|
Irrigation |
10 µg/L
mean |
Livestock Watering |
30.0 µg/L
mean |
1.
For the aquatic life sediment guideline the total
organic carbon in the sediment is assumed to be 5%.
2.
The aquatic life sediment and tissue values are
interim guidelines and apply to both freshwater and
marine environments.
3.
The mean concentrations in the water column are based
on at least 5 weekly samples taken over a 30-day
period; in tissue or sediment samples they are based
on 5 independent samples.
Reference 37
|

Table 41. Recommended Guidelines for Temperature
Water Use |
Recommended
Guideline
|
Drinking Water Supply |
15 degrees Celsius maximum
|
Freshwater Aquatic Life
- streams with bull trout and/or
Dolly Varden
|
maximum 10 degrees Celsius-spawning
maximum 15 degrees Celsius-rearing
maximum 10 degrees Celsius-incubation
minimum 2 degrees Celsius-incubation
|
Freshwater Aquatic Life
- streams with known fish distribution
|
+ or - 1 degree Celsius change beyond
optimum temperature range as shown in
Table 42 for each
life history phase of the
most sensitive salmonid species
present
Hourly rate of change not to exceed
1 degree Celsius
|
Freshwater Aquatic Life
- streams with unknown fish distribution
|
Mean Weekly Maximum Temperature (MWMT) = 18 degrees Celsius
(maximum daily temperature = 19 degrees Celsius)
Hourly rate of change not to exceed 1 degree Celsius
maximum incubation temperature = 12 degrees Celsius
(in the Spring and the Fall)
|
Freshwater Aquatic Life
- lakes and impoundments
|
+ or - 1 degree Celsius change
from natural ambient background
|
Marine
and Estuarine Aquatic Life |
+
or - 1 degree Celsius change
from natural ambient background
hourly rate of change up to 0.5 degrees Celsius
|
Wildlife
and Livestock Watering
Irrigation and Industrial Water Supplies
|
+ or - 1 degree Celsius change
from natural ambient background
|
Recreation
and Aesthetics |
30
degrees Celsius maximum
The thermal characteristics of waters used for bathing and swimming should not cause an appreciable increase or decrease in the deep body temperature of bathers and swimmers.
|

Table
42. Optimum Temperature Ranges of Specific Life History Stages
of Salmonids and Other Cold water species for Guideline Application
| Species |
Incubation |
Rearing |
Migration |
Spawning |
Salmon |
| Chinook |
5.0-14.0 |
10.0-15.5 |
3.3-19.0 |
5.6-13.9 |
| Chum |
4.0-13.0 |
12.0-14.0 |
8.3-15.6 |
7.2-11.8 |
| Coho |
4.0-13.0 |
9.0-16.0 |
7.2-15.6 |
4.4-12.8 |
| Pink |
4.0-13.0 |
9.3-15.5 |
7.2-15.6 |
7.2-12.8 |
| Sockeye |
4.0-13.0 |
10.0-15.0 |
7.2-15.6 |
10.6-12.8 |
Trout
|
| Brown |
1.0-10.0 |
6.0-17.6 |
— |
7.2-12.8 |
| Cutthroat |
9.0-12.0 |
7.0-16.0 |
— |
9.0-12.0 |
| Rainbow |
10.0-12.0 |
16.0-18.0 |
— |
10.0-15.5 |
Char
|
| Arctic
char |
1.5-5.0 |
5.0-16.0 |
— |
4.0 |
| Brook
Trout |
1.5-9.0 |
12.0-18.0 |
— |
7.1-12.8 |
| Bull
Trout |
2.0-6.0 |
6.0-14.0 |
— |
5.0-9.0 |
| Dolly
Varden |
— |
8.0-16.0 |
— |
— |
| Lake
Trout |
5.0 |
6.0-17.0 |
— |
10.0 |
Grayling
|
| Arctic
grayling |
7.0-11.0 |
10.0-12.0 |
— |
4.0-9.0 |
Whitefish
|
| Lake
Whitefish |
4.0-6.0 |
12.0-16.0 |
— |
greater
than 8.0 |
| Mountain
Whitefish |
less
than 6.0 |
9.0-12.0 |
— |
less than 6.0 |
Other Species |
| Burbot |
4.0-7.0 |
15.6-18.3 |
— |
0.6-1.7 |
White
Sturgeon |
14.0-17.0 |
— |
— |
14.0 |
Table 43. Summary of Water Quality Guidelines for Arsenic
Water Use |
Recommended Guideline (µg/L
of Total Arsenic) |
Source Drinking Water |
25 (interim guideline) |
| Aquatic Life
Freshwater
Marine and Estuarine
|
5
12.5 (interim guidelines) |
Agriculture
Irrigation
Livestock Watering
|
100 (interim guideline)
25 (interim guideline) |
Wildlife |
25 (interim guideline)
|
Recreation and Aesthetics |
None recommended |

Table 44. Summary of Chlorate Guidelines
Water Use |
Guidelines
|
Raw Drinking Water |
2.4 mg/L |
Wildlife and Livestock
|
3 mg/L
|
| Freshwater Aquatic Life |
30 mg/L |
Marine Aquatic Life |
5 µg/L |
Table 45. Summary of Recommended Water Quality Guidelines for Diisopropanolamine (DIPA)
Water Use |
Guideline (mg DIPA/L)
|
Freshwater Aquatic Life |
1.6 mg/L maximum |
Marine Aquatic Life |
Insufficient data |
| Irrigation |
3.9 mg/L maximum |
Livestock Watering |
38 mg/L maximum |
Table 46. Summary of Recommended Guidelines for Sulpholane
Water Use |
Guideline (mg Sulpholane/L)
|
Freshwater Aquatic Life |
50 maximum |
Marine Aquatic Life |
Insufficient data |
| Irrigation |
8.4 maximum |
Livestock Watering |
14 maximum |

Table 47. Recommended Guidelines for Chloride
Water Use |
Guideline (mg Chloride/L
|
Drinking Water |
250 |
Recreation and Aesthetics |
None |
| Freshwater Aquatic Life1
Instantaneous Maximum Concentration
30-d Average Concentration (5 weekly measurements)
|
600
150
|
Marine Aquatic Life |
Human activities should not cause the chloride of marine and estuarine waters to fluctuate by more than 10% of the natural chloride expected at that time or depth. |
| Irrigation |
100 |
| Livestock Watering |
600 |
| Wildlife |
600 |
1. When ambient chloride concentration in the environment exceeds the guideline, then further degradation of the ambient or existing water quality should be avoided.
Reference 43 |
Table 48. Recommended Guidelines for Cobalt
Water Use |
Guideline (µg/L Total Cobalt)
|
Aquatic Life: Freshwater
Maximum
30-d Average (5 weekly measurements)
|
|
Aquatic Life: Marine |
Not recommended |
Wildlife |
Not recommended |
Irrigation |
Not recommended |
| Livestock watering |
Not recommended |

Table 49. Recommended Guidelines for Boron
Water Use |
Guideline (mg/L Total Boron)
|
|
|
Aquatic Life
Freshwater
Marine
|
1.2
1.2 |
Wildlife |
5 |
Irrigation |
0.5 to 6 (depends on crop; see Table 50) |
| Livestock watering |
5 |
Table 50. Recommended Irrigation Water Guidelines for Boron
| Tolerance |
Boron in Irrigation Water (mg/L) |
Agricultural Crop |
| Very Sensitive |
<0.5 |
Blackberry |
| Sensitive |
0.5 to 1 |
Peach, cherry, plum grape, cowpea, onion, garlic, sweet potato, wheat, barley sunflower, mung bean, sesame, lupin, strawberry, Jerusalem artichoke, kidney bean, lima bean |
| Moderately Sensitive |
1 to 2 |
Red pepper, pea, carrot, radish, potato, cucumber |
| Moderately Tolerant |
2 to 4 |
Lettuce, cabbage, celery, turnip, Kentucky bluegrass, oat, corn, artichoke, tobacco, mustard, clover, squash, muskmelon |
| Tolerant |
4 to 6 |
Sorghum, tomato, alfalfa, purple vetch, parsley, red beet, sugar beet |
| Very Tolerant |
6 to 15 |
Asparagus |

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45. Moss, S.A. and N.K. Nagpal. 2003. Ambient Water Quality Guidelines for Boron. Ministry of Water, Land and Air Protection, Victoria, B.C.
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