 |

Science and Information Branch
WATER QUALITY
A
Compendium of Working Water Quality Guidelines for
British
Columbia
N. K. Nagpal Ph.D. P.Ag.
L. W. Pommen M.Sc. P.Eng.
L. G. Swain P.Eng.
Ministry of Environment
Updated:
August 2006
Table of
Contents
Introduction
Tables
References
Introduction
Compendium
of Working Guidelines for 2006.
The following
questions and answers will introduce you to the 2006 Compendium
of Working Water Quality Guidelines for British Columbia.
They will explain what the report is about and guide you
through its use. This report is revised periodically to incorporate
new information. The authors invite your comments and suggestion
on any errors or omissions in the guidelines cited here.
What are water quality guidelines and why are they important?
Water quality
guidelines are environmental benchmarks. They are safe levels
of substances for the protection of a given water use, including
drinking water, aquatic life, recreation and agriculture. They
are developed in order that water quality data can be assessed
and site-specific water quality objectives can be prepared.
The Ministry of Environment has recently published,
under a separate cover, a report on approved
water
quality
guidelines: British Columbia Approved Water Quality Guidelines, 2006 Edition. It lists water quality guidelines for certain priority substances and has been approved by the executive for use in B.C.
What are Working Guidelines and why do we have them?
The Working Guidelines Compendium brings together guidelines
that have not yet been approved by the Province-hence, called
the working guidelines. These guidelines were obtained from various
Canadian (primarily the Canadian Council of the Ministers of
the Environment or CCME), and other North American jurisdictions.
These working guidelines provide benchmarks for those subtances
that have not yet been fully assessed and formally endorsed
by the Ministry. They will be reviewed by the Ministry on a priority
basis for their formal approval and use in British Columbia.
When are Working Guidelines used?
Working guidelines are used when there have not been guidelines approved by the province for a substance of concern to protect a particular water use. The working guidelines provide the best guidance that the Ministry can provide, at the time of publication, about safe levels for different substances in the environment. Because these estimates can be based on historic information or different derivation protocols, and are obtained from a number of different agencies, one should use them with caution.
Who
can use this report?
Traditionally, water quality professionals such as consultants
have used this report. We are hoping that members of the public,
especially those associated with local stewardship groups, will
use this new user-friendly edition of the report to evaluate
water quality data that they collect.
What are sediment quality guidelines and how should they be used?
Sediment guidelines are generally stated in two ways:
- Safe levels of substances that will protect aquatic life from adverse
effects of toxic substance
- Levels which, if exceeded, will cause severe effects on
aquatic life.
These guidelines
are not based on cause-effect studies, but on levels of toxic
substances found in the sediment where biological effects have
been measured. Caution should be exercised in the application
of these guidelines.
What are site-specific water quality guidelines or objectives?
Site-specific
water quality guidelines (or objectives) are a refinement of
the province-wide guidelines. They are adapted to protect the
most sensitive water use at a specific location, taking local
circumstances into account. As suggested above, they have their
basis in the water quality guidelines plus the site characteristics
that may influence the toxic action of the substance of concern.
The Ministry recognizes that site-specific factors may necessitate
modification of the Approved or the Working guidelines and
suggests means to do this in a 1997 publication: Methods for
Deriving Site-Specific Water Quality Objectives in British
Columbia and Yukon.
What is the difference between the British Columbia water quality
guidelines and the Canadian Council of Ministers
of the Environment or CCME guidelines?
Care must
be exercised when numbers from B.C. and CCME are compared. In
some instances, B.C. guidelines for a substance may be specified
as two values: one to protect aquatic life from short-term,
lethal effects (i.e., the maximum value or the acute criterion)
and the other to protect it from long-term, sub-lethal effects
(the 30-day average value or the chronic criterion). On the
other hand, a CCME water quality guideline is always specified
as a single maximum value to protect aquatic life from all
adverse effects. CCME guidelines and B.C. chronic guidelines
are generally similar in value.
How do I find the guidelines for a substance in all these tables?
The substances
are arranged in alphabetical order in Table
1 and Table 2.
Substances in the water column are listed in Table
1 while
substances in the bottom sediments are listed in Table
2. The
last column in the Tables indicates the source of the guidelines.
Which water users are included in the tables?
There are
six uses of water that require protection: aquatic life, wildlife,
raw drinking water prior to treatment, recreation, irrigation
and livestock watering. Values to protect drinking water and
recreational water uses are mostly specified in the British
Columbia Water Quality Guidelines: 2006 Edition.
How do I use the tables of values?
You determine
for a waterbody the water uses that you want to ensure are
protected. Knowing this, you go to the table for a substance
and find the corresponding guideline for each use that you
want to protect. Usually the lowest guideline associated with
the uses that you want to protect will determine the level
that must be met to ensure that all the uses are protected.
CAUTION: The guidelines as specified in the References cited take precedence over the guidelines in this summary document, and should be consulted when using the guidelines to ensure accuracy and a full understanding of the guidelines.
I have seen other references to similar reports issued by the
Ministry in the past. Are those reports still valid?
As indicated
above, this report is revised periodically to incorporate new
information. Sections from the earlier versions that are still
useful have been included in this 2006 report. This 2006 version
and the British Columbia Water Quality Guidelines (Criteria):
2006 Edition supersede the following documents:
- Preliminary
Working Criteria for Water Quality, October 1982.
- Working
Criteria for Water Quality, April 1985.
- Approved
and Working Criteria for Water Quality, April 1987, March
1989, May 1991, February 1994 and April 1995.
- A Compendium of Working Water Quality Guidelines for British Columbia: 1998 Edition and updated August 23, 2001.
- British Columbia Approved Water Quality Guidelines (Criteria) 1998 Edition and updated August 24, 2001.
Which water quality guidelines have been developed by the Ministry?
Water quality
guidelines for the following substances have been approved:
Substance
_____________________________________________________________________________ |
-
Algae
- Aluminum
- Ammonia
- Arsenic
- Benthic
sedimentation
- Boron
- Carbon
(organic)
- Chlorate
- Chloride
- Chlorine
- Chlorophenols
- Cobalt
- Coliforms
- Colour
- Copper
- Cyanide
- Diisopropanolamine (DIPA)
- Dissolved
Oxygen
- Ethylbenzene
- Fluoride
- Lead
- Manganese
- Mercury
- Methyl
tertiary-butyl ether (MTBE)
- Microbiological
indicators
- Molybdenum
|
- MTBE (methyl tertiary-butyl ether
- Nitrate
- Nitrite
- Nitrogen (nitrate, nitrite and ammonia)
- Nutrients (phosphorus) and algae
- Organic Carbon
- Oxygen (dissolved)
- PAHs (polycyclic aromatic hydrocarbons)
- Particulate matter (suspended solids and turbidity)
- PCBs (polychlorinated biphenyls)
- pH
- Phosphorus
- Polychlorinated
biphenyls (PCBs)
- Polycyclic
aromatic hydrocarbons (PAHs)
- Pressure
(total gas pressure
- Selenium
- Silver
- Sulphate
- Sulpholane
- Suspended
solids
- Temperature
- Toluene
- Total
gas pressure
- Turbidity
- Zinc
|
|
Which water
quality guidelines are currently being developed by the Ministry?
Guidelines
for the following substances are being developed or reviewed
for possible formal approval by the ministry:
Substance
_____________________________ |
- Barium
- Benzene
- Beryllium
- Chromium
- Dioxins and Furans
- Iron
- Xylene
|
|
What guidelines have changed since the 1998 (updated in 2001) edition?
Guidelines have been added for:
- Beryllium - drinking water
- DDAC (didecyl dimethyl ammonium chloride) - freshwater aquatic life
- IPBC (3-lodo-2-propynl butyl carbamate) - freshwater aquatic life
- Nonyphenol and its ethoxylates - freshwater & marine aquatic life & sediment
- Polycyclic aromatic hydrocarbons - Quinoline - freshwater aquatic life
- Styrene - freshwater aquatic life
- Thallium - freshwater aquatic life
- Polychlorinated dibenzo-p-dioxins/dibenzo furans - freshwater & marine sediment
- Toxaphene - freshwater & marine sediment
Guidelines have been revised for:
- DDT (dichlorodiphenyl trichloroethane) - freshwater & marine sediment
- Endrin - marine sediment
- Lithium - freshwater aquatic life
- Diazinon - freshwater aquatic life
- Potassium - freshwater aquatic life
Guidelines have been deleted for:
- Acrolein - livestock
- Aldrin & Dieldrin - freshwater aquatic life
- Arsenic - approved B.C. guidelines adopted
- Beryllium - freshwater aquatic life
- Boron - approved B.C. guidelines adopted
- Calcium - food processing & industrial
- Chlordane - freshwater aquatic life & livestock
- Chloride - approved B.C. guidelines adopted
- Cobalt - freshwater aquatic life - approved B.C. guidelines adopted
- DDT (dichlorodiphenyl trichlorethane) - freshwater aquatic life & livestock
- Diazanon - livestock
- Endrin - freshwater aquatic life & livestock
- Heptachlor - freshwater aquatic life & livestock
- Methylene chloride - drinking water
- Phenols - aquatic life
- Toluene - approved B.C. guidelines adopted
What other tools does the Ministry have to help one assess water
quality?
In addition
to the Guidelines, the Ministry has developed several tools
that can be used to assess water quality. For instance, the
Principles document and the User's
Guide, (see below) outline
the process that can be used to develop site-specific water
quality objectives. The Status Report indicates the state of
water quality for waterbodies in BC where data are available.
The Ministry is also developing manuals that will help in designing
and implementing monitoring programs, and interpreting water
quality data. Titles of the completed reports are listed below:
Return
to the Table of Contents
Tables
Table 1.
Working Guidelines for the Water Column
Substance |
Working
Guidelines |
References |
Aldicarb
- freshwater aquatic life |
µg/L,
(aldicarb, aldicarb sulfoxide, aldicarb sulfone)
1, interim maximum |
1 |
Aldicarb
- marine aquatic life
|
µg/L,
(aldicarb, aldicarb sulfoxide, aldicarb sulfone)
0.15, interim maximum |
1
|
Aldicarb
- livestock |
µg/L,
(aldicarb, aldicarb sulfoxide, aldicarb sulfone)
11, interim maximum |
1
|
Aldicarb
- irrigation
|
µg/L,
(aldicarb, aldicarb sulfoxide, aldicarb sulfone)
54.9, interim maximum, other non-target crops |
1
|
Alkalinity
- food processing
|
mg/L,
total CaCO3
30 to 250 (process dependent) |
1 |
Alkalinity
- industrial (process dependent)
|
mg/L,
total CaCO3
0.5, iron and steel
125 to 150, chemical
130, tanning
50 to 75, textiles
1 to 1000, boilers
20 to 500, cooling
40 to 150, pulp and paper |
1 |
Alkalinity
- freshwater aquatic life
|
mg/L,
total CaCO3
up to 10, highly sensitive to acid inputs
10 to 20, moderately sensitive
over 20 low sensitivity
refer to calcium regarding sensitivity to
acid inputs, the more restrictive of calcium
or alkalinity is applicable |
2 |
Aniline
- freshwater aquatic life
|
µg/L,
total
2.2, maximum |
1 |
Antimony
- freshwater aquatic life
|
µg/L,
total
20, proposed Ontario guideline |
4 |
Antimony
- human health concerns |
µg/L,
total
14, human health protection
(consumption of water + organisms)
4300 human health protection
(consumption of organisms only) |
3 |
Atrazine
- freshwater aquatic life
|
µg/L,
Atrazine + metabolites
1.8 maximum |
1
|
Atrazine
- marine aquatic life |
µg/L,
Atrazine + metabolites
10 maximum |
7 |
Atrazine
- irrigation |
µg/L,
Atrazine + metabolites
10 interim maximum |
1
|
Atrazine
- livestock |
µg/L,
Atrazine + metabolites
5 interim maximum
|
1 |
Barium
- freshwater aquatic life
|
mg/L,
total (under Ministry review)
1, 30-/day average
5, maximum |
8
|
Barium
- marine aquatic life
|
mg/L, total (under Ministry review)
0.5, minimal risk
1, hazard |
5
(p. 244)
|
Barium
- marine aquatic life |
mg/L,
total (under Ministry review)
0.2, adverse effects on a bivalve |
9
|
Benzene
- freshwater aquatic life |
µg/L,
total (under Ministry review)
370, interim maximum |
1
|
Benzene
- marine aquatic life
|
µg/L,
total (under Ministry review)
110, interim maximum |
1
|
Beryllium
- drinking water |
µg/L, total 4.0, maximum contaminant level |
52 |
Beryllium
- freshwater aquatic life
|
µg/L,
total (under Ministry review)
5.3, chronic criterion |
10
|
Beryllium
- marine aquatic life
|
µg/L,
total (under Ministry review)
100, minimal risk
1500, hazard |
5
(p. 244)
|
Beryllium
- livestock
|
µg/L,
total (under Ministry review)
100, tentative maximum |
1
|
Beryllium
- irrigation
|
µg/L,
total (under Ministry review)
100, maximum, continuous use, all soils |
1
|
Beryllium
- irrigation |
µg/L,
total (under Ministry review)
500, maximum, up to 20 years on
fine-textured, neutral to alkaline soils |
11
(p. 21)
12 (p. 41)
5 (p. 341)
|
Bromide
- drinking water
|
µg/L
50, annual mean of monthly raw water samples
for systems using ozonation
less than 50 requires reduced bromate monitoring of treated
water
greater than 50 requires increased bromate monitoring of
treated water |
51
(1999)
|
Bromocil
- freshwater aquatic life
|
µg/L,
total
5, maximum |
1
|
Bromocil
- livestock
|
µg/L,
total
1100, interim maximum |
1 |
Bromocil
- irrigation
|
µg/L,
total
0.2, interim maximum
|
1 |
Bromoxynl
- freshwater aquatic life |
µg/L,
total
5, maximum |
1 |
Bromoxynl
- livestock |
µg/L, total
11, maximum for most sensitive animals |
1 |
Bromoxynl
- irrigation |
µg/L,
total
0.33, maximum for most sensitive legume species |
1 |
Cadmium
- freshwater aquatic life |
µg/L, total
cadmium = 10 exp (0.86[log{hardness}]-3.2)
0.01 at 30 mg/L CaCO3
0.02 at 60 mg/L CaCO3
0.03 at 90 mg/L CaCO3
0.04 at 120 mg/L CaCO3
0.05 at 150 mg/L CaCO3
0.06 at 210 mg/L CaCO3 |
1 |
Cadmium
- marine aquatic life
|
µg/L, total
0.12, maximum |
1
|
Cadmium
- livestock
|
µg/L, total (under Ministry review)
80, maximum |
1
|
Cadmium
- irrigation
|
µg/L, total (under Ministry review)
5.1, maximum |
1
|
Calcium
- freshwater aquatic life
|
mg/L, dissolved
up to 4, highly sensitive to acid inputs
4 to 8, moderately sensitive
over 8 low sensitivity
refer to alkalinity
the more restrictive of calcium or alkalinity applies |
2
|
Calcium
- livestock
|
mg/L, dissolved
1000, maximum
less if high levels of other major ions present |
1
|
Captan
- freshwater aquatic life
|
µg/L, total
1.3, interim maximum |
1
|
Captan
- livestock
|
µg/L, total
13, interim maximum |
1
|
Carbaryl
- freshwater aquatic life |
µg/L, total
0.20 maximum |
1
|
Carbaryl
- marine aquatic life |
µg/L, total
0.32, interim maximum |
1
|
Carbaryl
- livestock |
µg/L, total
1100, maximum |
1
|
Carbofuran
- freshwater aquatic life |
µg/L, total
1.8, maximum |
1 |
Carbofuran
- livestock |
µg/L, total
45, maximum |
1 |
Carbon tetrachloride
- freshwater aquatic life |
µg/L, total
13.3, interim maximum |
1
|
Carbon tetrachloride
- livestock |
µg/L, total
5, interim maximum |
1
|
Chlorobenzenes
- livestock
hexachlorobenzene |
µg/L,
total
0.52, interim maximum |
1
|
Chlorobenzenes
- marine aquatic life
monochlorobenzene |
µg/L,
total
25, interim maximum |
1
|
Chlorobenzenes
-marine aquatic life
1,2-dichlorobenzene |
µg/L,
total
42, interim maximum |
1
|
Chlorobenzenes
- marine aquatic life
1,2,4-trichlorobenzene |
µg/L,
total
5.4, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
monochlorobenzene |
µg/L,
total
1.3, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
1,2-dichlorobenzene |
µg/L, total
0.7, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
1,3-dichlorobenzene |
µg/L,
total
150, interim maximum |
1 |
Chlorobenzenes
- freshwater aquatic life
1,4-dichlorobenzene |
µg/L,
total
26, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
1,2,3-trichlorobenzene |
µg/L,
total
8, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
1,2,4-trichlorobenzene |
µg/L,
total
24, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
1,2,3,4-tetrachlorobenzene |
µg/L,
total
1.8, interim maximum |
1
|
Chlorobenzenes
- freshwater aquatic life
pentachlorobenzene |
µg/L,
total
6, interim maximum |
1
|
Chloroethanes
- freshwater aquatic life
1,2-dichloroethane
|
µg/L, total
100, interim maximum |
1 |
Chloroethanes
- freshwater aquatic life
1,2-dichloroethane |
µg/L, total
5, interim maximum |
1 |
Chloroethenes
- freshwater aquatic life
1,1,2-trichloroethene
(trichloroethylene, TCE) |
µg/L, total
21, interim maximum |
1 |
Chloroethenes
- livestock
1,1,2-trichloroethene
(trichloroethylene, TCE) |
µg/L, total
50, interim maximum |
1 |
Chloroethenes
- freshwater aquatic life
1,1,2,2-tetrachloroethene
(tetrachloroethylene, PCE) |
µg/L, total
111, interim maximum |
1 |
Chloromethanes
- freshwater aquatic life
dichloromethane
(Methylene chloride)
|
µg/L, total
98.1, interim maximum
|
1 |
Chloromethanes
- livestock
dichloromethane
(Methylene chloride) |
µg/L, total
50, interim maximum |
1 |
Chloromethanes
Chloroform
-freshwater aquatic life (trichloromethane) |
µg/L,
total trichloromethane
1.8, interim maximum |
1
|
Chloromethanes
Chloroform
- livestock
(trichloromethane) |
µg/L, total
100, interim maximum |
1 |
Chloromethanes
- freshwater aquatic life
tetrachloromethane
(carbon tetrachloride)
|
µg/L, total
13.3, interim maximum |
1 |
Chloromethanes
- livestock
tetrachloromethane
(carbon tetrachloride) |
µg/L, total
5, interim maximum |
1 |
4-chloro-2-methylphenoxy
acetic acid
(MCPA)
- drinking water |
µg/L,
total
10, lifetime health advisory |
15 |
4-chloro-2-methylphenoxy
acetic acid
(MCPA)
- freshwater aquatic life |
µg/L,
total
2.6, interim maximum |
1
|
4-chloro-2-methylphenoxy
acetic acid
(MCPA)
- marine aquatic life |
µg/L,
total
4.2, interim maximum |
1
|
4-chloro-2-methylphenoxy
acetic acid
(MCPA)
- livestock |
µg/L,
total
25, interim maximum |
1
|
4-chloro-2-methylphenoxy
acetic acid
(MCPA)
- irrigation |
µg/L,
total
0.025, maximum |
1
|
Chlorothalonil
- drinking water
2,4,5,6-tetrachloro-1,3
benzenedicarbonitrile |
µg/L,
total
200, health advisory |
15 |
Chlorothalonil
- freshwater aquatic life
2,4,5,6-tetrachloro-1,3
benzenedicarbonitrile |
µg/L,
total
0.18, interim maximum, chlorothalonil + 4-hydroxy
transformation product |
1
|
Chlorothalonil
- marine aquatic life
2,4,5,6-tetrachloro-1,3
benzenedicarbonitrile |
µg/L,
total
0.36, interim maximum, chlorothalonil + 4-hydroxy
transformation product |
1
|
Chlorothalonil
- livestock
2,4,5,6-tetrachloro-1,3
benzenedicarbonitrile |
µg/L,
total
170, interim maximum |
1 |
Chlorothalonil
- irrigation
2,4,5,6-tetrachloro-1,3
benzenedicarbonitrile |
µg/L,
total
5.8, interim maximum |
1
|
Chlorpyrifos
- freshwater aquatic life |
µg/L,
total
0.0035, maximum |
1 |
Chlorpyrifos
- marine aquatic life |
µg/L,
total
0.002, interim maximum |
1
|
Chlorpyrifos
- livestock |
µg/L,
total
24, interim maximum |
1
|
Chromium
- freshwater aquatic life
|
µg/L,
total (under Ministry review)
1, maximum, Cr(VI)
8.9, interim maximum, Cr(III) |
1
|
Chromium
- marine aquatic life |
µg/L,
total (under Ministry review)
1.5, maximum, Cr(VI)
56, interim maximum, Cr(III) |
1
|
Chromium
- livestock
|
µg/L,
total (under Ministry review)
50, maximum Cr(VI)
50, interim maximum Cr(III) |
1 |
Chromium
- irrigation |
µg/L,
total (under Ministry review)
8, maximum Cr(VI)
4.9, interim maximum Cr(III) |
1 |
Cobalt
- livestock
|
µg/L,
total
1000, maximum |
1 |
Cobalt
- irrigation
|
µg/L, total
50, maximum (continuous use on all soils)
5000, maximum (for up to 20-year use
on fine-textured neutral to alkaline soils) |
1 |
Colour
- industrial
|
true
colour, process dependent
5, textiles and tanning
5 to 20, chemicals
25 to 100, pulp and paper |
1 |
Conductivity
(specific)
- livestock |
µS/cm,
(see also filterable residue and salinity)
1400 to 4200, maximum, species dependent |
1 |
Conductivity
(specific)
- irrigation |
µS/cm,
(see also filterable residue and salinity)
700 to 5000, soil and crop dependent |
1 |
Conductivity
(specific)
- industrial |
µS/cm,
(see also filterable residue and salinity)
0.7 to 8000, boilers, process dependent
140 to 4000, cooling, process dependent |
1 |
Cyanazine
- freshwater aquatic life
|
µg/L,
total
2, interim maximum |
1
|
Cyanazine
- irrigation |
µg/L,
total
0.5, interim maximum |
1
|
Cyanazine
- livestock
|
µg/L,
total
10, interim maximum (same as drinking water) |
1 |
2,4-D
- freshwater aquatic life
|
µg/L,
total (2,4-dichlorophenoxyacetic acid)
4, maximum (ester formulation) |
1 |
2,4-D
- livestock |
µg/L,
total (2,4-dichlorophenoxyacetic acid)
100, maximum |
1 |
DDAC (didecyl dimethyl ammonium chloride)
- freshwater aquatic life |
µg/L, total
1.5, maximum |
1 |
Dehydroabietic
Acid
- freshwater aquatic life |
See Resin Acids |
38 |
Deltamethrin
-freshwater aquatic life |
µg/L,
total
0.0004, maximum |
1
|
Deltamethrin
-livestock |
µg/L,
total
2.5, maximum |
1
|
Diazinon
- freshwater aquatic life
|
µg/L,
total
0.08, Ontario’s objective
0.043, secondary chronic value |
24
14
|
Dibutylphthalate
(DBP) Phthalate ester
- freshwater aquatic life |
µg/L,
total
19, interim maximum |
1
|
Dicamba
- freshwater aquatic life
|
µg/L,
total
10, interim maximum |
1
|
Dicamba
- livestock
|
µg/L,
total
122, maximum |
1
|
Dicamba
- irrigation
|
µg/L,
total
0.006, maximum |
1
|
1,2-dichloroethane
- freshwater aquatic life |
µg/L,
total
100, interim maximum, protection and maintenance |
1
|
1,2-dichloroethane
- livestock
|
µg/L,
total
5, interim maximum (same as drinking water) |
1
|
2,4-dichlorophenoxy acetic
acid
- freshwater aquatic life |
µg/L,
total 2,4-D acid
4, maximum (ester formulation) |
1 |
2,4-dichlorophenoxy acetic
acid
- livestock |
µg/L,
total 2,4-D acid
100, maximum |
1 |
Diclofop-methyl
- freshwater aquatic life |
µg/L,
total
6.1, maximum |
1
|
Diclofop-methyl
- livestock
|
µg/L,
total
9, interim maximum |
1
|
Diclofop-methyl
- irrigation |
µg/L,
total
0.18, maximum |
1
|
Di-(2-ethylhexyl)phthalate
(DEHP) Phthalate ester
- freshwater aquatic life |
µg/L,
total
16, interim maximum |
1
|
Dimethoate
- freshwater aquatic life
|
µg/L,
total
6.2, interim maximum |
1
|
Dimethoate
- livestock
|
µg/L,
total
3, interim maximum |
1
|
Di-n-butyl
tin
- freshwater aquatic life |
µg/L,
total
0.08, Ontario objective |
25 |
Dinoseb
- freshwater aquatic life
|
µg/L,
total
0.05, maximum |
1
|
Dinoseb
- livestock
|
µg/L,
total
150, maximum, protects lactating dairy cows |
1
|
Dinoseb
- irrigation
|
µg/L,
total
93, maximum for legumes
46, maximum for cereals and hay
16, maximum for all other crops |
1 |
Dissolved
Solids
(residue, filterable)
- food processing |
mg/L, total dissolved
50 to 850, process dependent |
1 |
Dissolved
Solids
(residue, filterable)
- livestock
|
mg/L,
total dissolved
1000, maximum, sensitive species
3000, maximum, other species |
1 |
Dissolved
Solids
(residue, filterable)
- irrigation |
mg/L,
total dissolved
500 to 3500, maximum, crop and soil dependent |
1 |
Dissolved
Solids
(residue, filterable)
- industrial |
mg/L,
total dissolved, process dependent
0.5, boilers
100, textiles
750, petroleum
1000, iron and steel
200, chemical
200 to 500, pulp and paper
500 to 35000, cooling |
1 |
Endosulfan
- freshwater aquatic life |
µ/L, total
0.02, maximum |
1 |
Ethylene
glycol
- freshwater aquatic life |
mg/L,
total
192, interim maximum |
1
|
Floatable
Solids
- industrial
|
mg/L,
total
0, iron and steel |
1 |
Glyphosate
- freshwater aquatic life
|
µg/L,
total
65, interim maximum |
1
|
Glyphosate
- livestock
|
µg/L,
total
280, maximum, same as drinking water |
1
|
Halogenated methanes (see also Choloromethanes) tribromomethane (Bromoform)
- livestock |
µg/L, total
100, maximum |
1 |
Halogenated methanes
dichlorobromomethane
- livestock |
µg/L, total
100, maximum |
1 |
Halogenated methanes
dibromochloromethane
- livestock |
µg/L, total
100, maximum |
1 |
Hardness
- food processing
|
µg/L,
total dissolved
10 to 250, process dependent |
1 |
Hardness
- industrial process dependent
|
µg/L,
total dissolved
0.07 to 1, boilers
0 to 150, tanning
8 to 55, textiles
0.1 to 100, iron and steel
130 to 6250, cooling
low to 350, chemical
350, petroleum
100, pulp and paper |
1 |
Hexachloro-1,3-butadiene (HCBD)
- freshwater aquatic life |
µg/L,
total
1.3, interim maximum |
1 |
| Hexachlorocyclohexane |
see
Lindane |
— |
IPBC (3-lodo-2-propynl butyl carbamate)
- freshwater aquatic life |
|
µg/L, total
1.9, interim maximum |
1 |
Lead
- freshwater aquatic life
tetra-ethyl lead |
µg/L,
total organic
0.0007, maximum, Ontario objective |
18 |
Lead
- freshwater aquatic life
tri-ethyl lead |
µg/L,
total organic
0.4, maximum, Ontario objective |
18 |
Lead
- freshwater aquatic life
tetra-methyl lead |
µg/L,
total organic
0.006, maximum, Ontario objective |
18 |
Lindane
- freshwater aquatic life
hexachlorocyclohexane
|
µg/L,
total
0.01, maximum |
1 |
Lindane
- livestock
hexachlorocyclohexane |
µg/L,
total
4, maximum |
1 |
Linuron
- freshwater aquatic life
|
µg/L,
total
7, interim maximum |
1
|
Linuron
- irrigation
|
µg/L, total
3.3, maximum, cereals, hay, pastures
0.071, interim maximum, other crops |
1
|
Lithium
- freshwater aquatic life
|
mg/L,
total
0.014, secondary chronic value
0.096 Final chronic value
0.870 Aquatic maximum value |
14
16
16
|
Lithium
- irrigation
|
mg/L,
total
2.5, maximum, continuous use on all soils
(this may be too high for cereals since
1 mg/L suppressed barley growth) |
1,
5 |
Magnesium
- food processing
|
mg/L,
total
10 to 30, process dependent |
1 |
Magnesium
- industrial
|
mg/L,
total, process dependent
0.01, boilers
2 to 35, chemicals
12, pulp and paper
25, petroleum |
1 |
Malathion
- freshwater aquatic life
- marine aquatic life |
µg/L,
total
0.1, maximum |
10 |
Manganese
- food processing |
µg/L,
total
30 to 200, process dependent |
1 |
Manganese
- marine aquatic life |
µg/L,
total
100, to protect consumers of shellfish |
10 |
Manganese
- irrigation
|
µg/L, total
200, maximum, continuous use on all soils
10000, maximum for up to 20 years on
neutral to alkaline fine-textured soils |
1 |
Manganese
- industrial |
µg/L
10, boilers
10 to 50, textiles
100 to 500, pulp and paper
10 to 200, tanning
20 to 100, chemical
20 to 50, cooling water |
1 |
MCPA (4-chloro-2-methyl phenoxy acetic acid; 2-methyl-4-chloro phenoxy acetic acid)
- drinking water |
µg/L,
total
10, lifetime health advisory |
15 |
MCPA (4-chloro-2-methyl phenoxy acetic acid; 2-methyl-4-chloro phenoxy acetic acid)
- freshwater aquatic life |
µg/L, total
2.6, interim maximum |
1 |
MCPA (4-chloro-2-methyl phenoxy acetic acid; 2-methyl-4-chloro phenoxy acetic acid)
- marine aquatic life |
µg/L, total
4.2, interim maximum |
1
|
MCPA (4-chloro-2-methyl phenoxy acetic acid; 2-methyl-4-chloro phenoxy acetic acid)
- livestock |
µg/L, total
25, interim maximum |
1
|
MCPA (4-chloro-2-methyl phenoxy acetic acid; 2-methyl-4-chloro phenoxy acetic acid)
- irrigation |
µg/L, total
0.16, cereals, hay and pastures
0.025, other crops |
1
|
Methylene Chloride
- freshwater aquatic life |
µg/L, total
98.1, interim maximum |
1
|
Methylene Chloride
- livestock
|
µg/L, total
50, interim maximum |
1
|
Metolachlor
- freshwater aquatic life |
µg/L, total
7.8, interim maximum |
1
|
Metolachlor
- irrigation |
µg/L, total
28, interim maximum, crops |
1
|
Metolachlor
- livestock
|
µg/L, total
50, interim maximum, same as drinking water |
1
|
Metribuzin
- freshwater aquatic life |
µg/L, total
1, interim maximum |
1
|
Metribuzin
- irrigation |
µg/L, total
0.5, interim maximum, non-target crop species |
1
|
Metribuzin
- livestock |
µg/L, total
80, interim maximum, same as drinking water |
1
|
Nickel
- freshwater aquatic life
|
µg/L, total
25, maximum at hardness of 0 to 60
mg/L as CaCO3
65, maximum at hardness of 60 to 120
mg/L as CaCO3
110, maximum at hardness of 120 to 180
mg/L as CaCO3
150, maximum at hardness greater than 180
mg/L as CaCO3 |
1 |
Nickel
- marine aquatic life
|
µg/L, total
8.3, 4-day average
75, 1-hour average |
10 |
Nickel
- livestock
|
µg/L, total
1000, maximum |
1 |
Nickel
- irrigation
|
µg/L, total
200, maximum, continuous use on all soils
2000 maximum, 20-year use on
neutral to alkaline fine-textured soils |
1 |
Nonylphenol (NP) and its ethoxylates
- freshwater aquatic life
|
µg/L, total
1.0, interim maximum, expressed on a toxic equivalency (TEQ) basis using NP toxic equivalency factors (TEFs). See reference.
|
1 |
Nonylphenol (NP) and its ethoxylates
- marine aquatic life |
µg/L, total
0.7, interim maximum, expressed on a toxic equivalency (TEQ) basis using NP toxic equivalency factors (TEFs). See reference. |
1 |
Oil
and Grease
- freshwater aquatic life
|
mg/L,
total
the surface water should be virtually free
of petroleum, animal or vegetable oils |
22 |
Oil
and Grease
- industrial
|
mg/L,
total, process dependent
0, iron and steel
0.2 to 1, boilers |
1 |
| Organotins |
See Tin. |
|
pH
- industrial
|
pH,
process dependent
2.5 to 10.5, textiles
7 to 10.5, boilers
6 to 9, petroleum
6 to 8, tanning
5 to 8.3, cooling
5 to 8.7, chemical
5 to 9, iron and steel
6 to 8, pulp and paper |
1 |
Phthalate
esters (DBP)
Dibutylphthalate
- freshwater aquatic life |
µg/L,
total
19, interim maximum |
1
|
Phthalate
esters (DEHP)
Di-(2-ethylhexyl)phthalate
- freshwater aquatic life |
µg/L,
total
16, interim maximum |
1
|
Picloram
- freshwater aquatic life |
µg/L,
total
29, interim maximum |
1
|
Picloram
- livestock |
µg/L, total
190, interim maximum, same as drinking water |
1
|
Polycyclic aromatic hydrocarbons (PAHs)
Quinoline
- freshwater aquatic life
|
µg/L, total
3.4 , interim maximum
(See Approved B.C. guidelines for other PAHs.)
|
1 |
Potassium
- freshwater aquatic life |
mg/L, as KCl
373 - 432, threshold for Daphnia magna immobilization |
17 |
1,2-propylene
glycol
- freshwater aquatic life |
mg/L,
total
500, interim maximum |
1
|
Residue,
filterable (dissolved solids)
- food processing |
mg/L,
total dissolved
50 to 850, process dependent |
1 |
Residue,
filterable (dissolved solids)
- livestock
|
mg/L,
total dissolved
1000, maximum, sensitive species
3000, maximum, other species |
1 |
Residue,
filterable (dissolved solids)
- irrigation
|
mg/L,
total dissolved
500 to 3500, maximum, crop and soil dependent |
1 |
Residue,
filterable (dissolved solids)
- industrial |
mg/L,
total dissolved, process dependent
0.5, boilers
100, textiles
750, petroleum
1000, iron and steel
200, chemical
200 to 500, pulp and paper
500 to 35000, cooling |
1 |
Residue,
filterable (suspended solids)
- food processing |
mg/L,
total
0 to 500 |
1 |
Residue,
filterable (suspended solids)
- industrial
|
mg/L,
total, process dependent
0.05, boilers
5, textiles
10, petroleum
0 to 25, iron and steel
5 to 10, chemical
10, pulp and paper
100 to 5000, cooling |
1 |
Resin
Acids
dehydroabietic acid (DHA)
- freshwater aquatic life
|
µg/L,
total
1 at pH 5.0
2 at pH 5.5
2 at pH 6.0
4 at pH 6.5
8 at pH 7.0
12 at pH 7.5
13 at pH 8.0
14 at pH 8.5
14 at pH 9.0 |
38 |
Resin
Acids (total)
abietic acid
neoabietic acid
pimaric acid
isopimaric acid
sandaracopimaric acid
- freshwater aquatic life |
µg/L, total
1 at pH 5.0
3 at pH 5.5
4 at pH 6.0
9 at pH 6.5
25 at pH 7.0
45 at pH 7.5
52 at pH 8.0
60 at pH 8.5
62 at pH 9.0 |
38 |
Salinity
- freshwater aquatic life
- terrestrial wildlife
|
g/L of NaCl or equivalent
(the sea is about 35 g/L or 3.5%)
1.5, maximum |
24
(p.32) |
Salinity
- marine aquatic life
- estuarine aquatic life |
g/L of NaCl or equivalent
(the sea is about 35 g/L or 3.5%)
+ or - 10%, maximum change |
24
(p.68) |
Salinity
- marine aquatic life
- estuarine aquatic life
- estuarine wildlife
|
g/L of NaCl or equivalent
(the sea is about 35 g/L or 3.5%)
6, maximum for waterfowl marshes to protect vegetation
For natural communities the maximum
24-hour change should not exceed
1 if natural salinity is 0 to 3.5
2 if natural salinity is 3.5 to 13.5
4 if natural salinity is 13.5 to 35 |
24
(p.53) |
Salinity
- recreation
|
g/L of NaCl or equivalent
(the sea is about 35 g/L or 3.5%)
9, ideal
5 to 20, acceptable range
this is isotonic to blood and tears |
24
(p.18) |
Settleable
Solids
- industrial
|
mg/L, total
0 to 100, iron and steel |
1 |
Silica
- food processing
|
mg/L, total
0 to 50, process dependent |
1 |
Silica
- industrial
|
mg/L, total, process dependent
0.01 to 150, boilers
25 to 200, cooling
20 to 100, pulp and paper
25, textiles |
1 |
Simazine
- freshwater aquatic life |
µg/L, total
10, interim maximum |
1
|
Simazine
- irrigation |
µg/L, total
0.5, interim maximum
protection of non-target crops |
1
|
Simazine
- livestock
|
µg/L,
total
10, interim maximum
same as drinking water |
1
|
Sodium
- irrigation
|
mg/L, dissolved
crop, soil and water regime dependent |
1 |
Solids,
Floatable
- industrial
|
mg/L,
total
0, iron and steel |
1 |
Solids,
Settleable
- industrial |
mg/L,
total
0 to 100, iron and steel |
1 |
Solids,
Suspended (residue,
non-filterable)
- food processing |
mg/L,
total
0 to 500 |
1 |
Solids,
Suspended (residue,
non-filterable)
- industrial |
mg/L,
total, process dependent
0.05, boilers
5, textiles
10, petroleum
0 to 25, iron and steel
5 to 10, chemical
10, pulp and paper
100 to 5000, cooling |
1 |
Styrene
- freshwater aquatic life |
µg/L, total
72, interim maximum |
1 |
Sulphate
- livestock
|
mg/L,
dissolved
1000, maximum |
1 |
Sulphate
- industrial |
mg/L,
dissolved
process dependent
175 to 200, iron and steel
250, tanning
200 to 2700, cooling |
1 |
Sulphide
- food processing
|
µg/L,
as H2S
200, detected by smell in air at 2 ppb
and in water at 0.025 to 0.25 µg/L |
1 |
Sulphide
- industrial |
µg/L,
as total sulphide
5000, cooling water |
1 |
Sulphide
- freshwater aquatic life
- marine aquatic life
|
µg/L,
as H2S
2, detected by smell in air at 2 ppb
and in water at 0.025 to 0.25 µg/L |
11
(p. 213)
12, 15 |
Surfactant,
LAS
- drinking water |
µg/L,
total
500 |
5
(p. 67) |
Surfactant
- freshwater aquatic life |
µg/L, total
200 Linear alkylbenzene sulphonates (LAS); 65 LAS -99% level of protection
340 Alcohol ethoxylated sulphate (AES) - 99% level of protection;
50 Alcohol ethoxylated surfactants (AE) - 99% level of protection
|
5
(p. 191)
19 (p. 3.4-10) |
Suspended
Solids
(residue, non-filterable)
- food processing |
mg/L,
total
0 to 500 |
1 |
Suspended
Solids
(residue, non-filterable)
- industrial |
mg/L,
total, process dependent
0.05, boilers
5, textiles
10, petroleum
0 to 25, iron and steel
5 to 10, chemical
10, pulp and paper
100 to 5000, cooling |
1 |
Tannins
and Lignins
- drinking water |
µg/L,
total
400, taste and odour threshold |
22 |
Tebuthiuron
1-(5-tert-butyl-1,3,4-
thiadiazol-2-yl)-1,3-dimethylurea
- drinking water |
µg/L,
total
490, lifetime health advisory |
15 |
Tebuthiuron
1-(5-tert-butyl-1,3,4-
thiadiazol-2-yl)-1,3-dimethylurea
- freshwater aquatic life |
µg/L,
total
1.6, interim maximum |
1
|
Tebuthiuron
1-(5-tert-butyl-1,3,4-
thiadiazol-2-yl)-1,3-dimethylurea
- livestock |
µg/L,
total
130, interim maximum |
1
|
Tebuthiuron
1-(5-tert-butyl-1,3,4-
thiadiazol-2-yl)-1,3-dimethylurea
- irrigation |
µg/L,
total
0.27, interim maximum for cereals, hay and pasture |
1
|
Tetrachloroethylene
- freshwater aquatic life |
µg/L,
total
111, interim maximum |
1
|
Thallium
- drinking water
|
µg/L,
total
2, maximum
0.5, maximum contaminant level goal |
23 |
Thallium
- freshwater aquatic life |
µg/L,
total
1.7, human health, consumption of
water + organism
6.3, human health, consumption of
organism only |
23 |
Thallium
- freshwater aquatic life |
µg/L, total
0.8, 30-day average, site-specific objective for the lower Columbia River, B.C.
|
13 |
Thallium
- freshwater aquatic life |
µg/L,
total
0.3, water quality objective for Ontario |
24 |
Tin,
Organic
Di-n-butyl tin
- freshwater aquatic life |
µg/L,
total
0.08, Ontario objective |
25 |
Tin,
Organic
Tributyl tin
- freshwater aquatic life |
µg/L,
total
0.008, interim maximum |
1
|
Tin,
Organic
Tributyl tin
- marine aquatic life |
µg/L,
total
0.001, interim maximum |
1
|
Tin,
Organic
Tributyl tin
- livestock
|
µg/L,
total
250, maximum, especially dairy cattle |
1
|
Tin,
Organic
Tricyclohexyl tin
- livestock |
µg/L,
total
250, interim maximum, especially dairy cattle |
1 |
Tin,
Organic
Triethyl tin
- freshwater aquatic life |
µg/L,
total
0.4, Ontario objective |
25 |
Tin,
Organic
Triphenyl tin
- freshwater aquatic life |
µg/L,
total
0.022, interim maximum |
1
|
Tin,
Organic
Triphenyl tin
- marine aquatic life |
µg/L,
total
96-hour LC50 = 34 to 48.9 |
1
|
Tin,
Organic
Triphenyl tin
- livestock
|
µg/L,
total
820, maximum, especially dairy cattle |
1 |
Titanium
- freshwater aquatic life
|
µg/L, total
2000,median threshold level: Scenedesmus
4600,median threshold level : Daphnia
|
17 (page 286) |
Triallate
- freshwater aquatic life |
µg/L,
total
0.24, interim maximum |
1 |
Triallate
- livestock
|
µg/L,
total
230, interim maximum, same as drinking water |
1
|
Tributyl
tin
-
freshwater aquatic life
|
µg/L,
total
0.008, interim maximum |
1
|
Tributyl
tin
-
marine aquatic life |
µg/L,
total
0.001, interim maximum |
1
|
Tributyl
tin
- livestock |
µg/L,
total
250, maximum, especially dairy cattle |
1
|
1,1,1-trichloroethane
- drinking water |
µg/L,
total
200, maximum acceptable concentration |
10,
26 |
1,1,1-trichloroethane
- freshwater aquatic life |
mg/L,
total
11.1, 96-hour EC50 for P. promelas
(loss of equilibrium, narcosis, etc.) |
1
|
Trichloroethylene
- freshwater aquatic life |
µg/L,
total
21, interim maximum |
1
|
Trichloroethylene
- livestock
|
µg/L,
total
50, interim maximum |
1
|
Trichloromethane
- aquatic life (chloroform) |
µg/L,
total
1.8, interim maximum |
1
|
Tricyclohexyl
tin
- livestock |
µg/L,
total
250, interim maximum, especially dairy cattle |
1
|
Triethyl
tin
- freshwater aquatic life |
µg/L,
total
0.4, Ontario objective |
25 |
Trifluralin
- freshwater aquatic life |
µg/L,
total
0.2, maximum |
1
|
Trifluralin
- livestock |
µg/L,
total
45, interim, same as drinking water |
1
|
Triphenyl
tin
- freshwater aquatic life |
µg/L,
total
0.022, interim maximum |
1
|
Triphenyl
tin
- marine aquatic life
|
µg/L,
total
96-hour LC50 = 34 to 48.9 |
1 |
Triphenyl
tin
- livestock |
µg/L,
total
820, interim maximum, especially dairy cattle |
1 |
Turbidity
- food processing
|
NTU,
process dependent
1 to 10 |
1 |
Turbidity
- industrial |
NTU,
process dependent
0, tanning
0.3 to 15, textiles
10 to 100, pulp and paper
1 to 2, chemical |
1 |
Uranium
- freshwater aquatic life |
µg/L,
total
300, maximum
500, Ontario’s water quality objectives |
27
24
|
Uranium
- marine aquatic life |
µg/L,
total
100, minimal risk
500, hazardous |
5
(p. 257) |
Uranium
- livestock
|
µg/L,
total
200, maximum |
1 |
Uranium
- irrigation
|
µg/L,
total
10, interim maximum, continuous or intermittent use on all soils
100, maximum for up to 20-years use
on fine-textured soils
with pH greater than or equal to 7 |
1 |
Vanadium
- freshwater aquatic life |
µg/L, total
6, Ontario’s water quality objective
20, secondary chronic value
|
24
14
|
Vanadium
- marine aquatic life |
µg/L, total
50, trigger value for 99% level of protection
|
|
19 |
Vanadium
- livestock |
µg/L, total
100, maximum |
1 |
Vanadium
- irrigation |
µg/L, total
100, maximum, continuous use on all soils
1000, maximum for 20-year use
on fine-textured soils
with pH less than or equal to 7 |
|
1 |
Zinc
- industrial |
mg/L,
total
0.01, boilers |
1 |
1.
Colour — One TCU (true colour unit) is theoretically
equal to 2 TAC (total absorbance colour) unit, but correlation
between the two methods is poor.
2.
Conductivity — Livestock
and Irrigation values are derived from reference #1 assuming
1 mg/L filterable residue
is about
equal to 1.4 µS/cm.
3.
Iron — Dissolved iron and
iron precipitates are the important forms to consider.
Total iron is often high due to
iron content
of suspended sediment and this is not important.
4.
Manganese — Dissolved
manganese and manganese precipitates are the important
forms to consider. Total manganese is often
high due to manganese content of suspended sediment and
thus is not important.
5.
Nickel — For freshwater
aquatic life nickel was lethal (7-day test) to C. dubia
at
7 µg/L (hardness = 40 mg/L CaCO3)
and 15 µg/L
(hardness = 177 mg/L CaCO3). See reference
21.
6.
Resin Acids — Total resin
acids include abietic acid, neoabietic acid, pimaric
acid, isopimaric acid, and sandaracopimaric acid but
not dehydroabietic acid.
7.
Sulphide — Total sulphide
= dissolved H2S + HS + acid-soluble metal
sulphides present in suspended matter. Dissolved sulphide
is that remaining
after suspended solids have been removed after flocculation
or settling. In aquatic environments, H2S
and HS are in equilibrium as H2S = H+ + HS-.
The un-ionized H2S can be calculated from dissolved sulphide,
the sample
pH and the ionization constant (which is dependent on
the sample water temperature) of H2S.
8.
X. (app. y) in the references refers to appendix y in
reference X.
|
Return to the Table of Contents
Table 2. Working Guidelines for the Sediments
| Substance |
Working
Guidelines (dry-weight basis) |
References |
Aldrin
- freshwater
|
µg/g,
(when sediment contains 1% organic carbon)
0.002 lowest effect level based on SLC
0.08 severe effect level based on SLC |
28 |
Aldrin
- marine
|
µg/g
0.005 EPA chronic marine EqP threshold
0.0001 significantly toxic to R. abronius based on CoA |
30 |
Arsenic
(total)
- freshwater |
µg/g
5.9 ISQG
17 PEL |
1 |
Arsenic
(total
- marine
|
µg/g
7.24 ISQG
42 PEL |
1 |
| Benzene
hexachloride |
This
is a conserved misleading name for
Hexachlorocyclohexane, it is not an aromatic compound. This
is not the same compound as Hexachlorobenzene. |
— |
Benzene
hexachloride-total
BHC-total
Hexachlorocyclohexane
see also Lindane (gamma isomer)
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
0.003 lowest effect level based on SLC
0.12 severe effect level based on SLC |
28 |
Benzene
hexachloride-alpha
BHC-alpha
Hexachlorocyclohexane
see also Lindane (gamma isomer)
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
0.006 lowest effect level based on SLC
0.10 severe effect level based on SLC |
28 |
Benzene
hexachloride-beta
BHC-beta
Hexachlorocyclohexane
see also Lindane (gamma isomer)
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
0.005 lowest effect level based on SLC
0.21 severe effect level based on SLC |
28 |
Bis
(2-ethylhexyl) phthalate
- marine |
µg/g,
(when sediment contains 1% organic carbon)
0.47 no adverse effect on biota
0.78 minor adverse effects |
29 |
Butyl
benzyl phthalate
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.049 no adverse effect on biota
0.64 minor adverse effects |
29 |
Cadmium
(total)
- freshwater
|
µg/g
0.6, ISQG
3.5 PEL |
1 |
Cadmium
(total)
- marine |
|
1 |
Chlordane
(total)
- freshwater
|
µg/g
0.0045 ISQG
0.00887 PEL |
1 |
Chlordane
(total)
- marine
|
µg/g
0.00226 ISQG
0.00479 PEL |
1 |
Chromium
(total)
- freshwater
|
µg/g
37.3 ISQG
90 PEL |
1 |
Chromium
(total)
- marine
|
µg/g
52.3 ISQG
160 PEL |
1 |
Copper
(total)
- freshwater
|
µg/g
35.7 ISQG
197 PEL |
1 |
Copper
(total)
- marine
|
µg/g
18.7 ISQG
108 PEL |
1 |
Dibenzofuran
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.15 no adverse effect on biota
0.58 minor adverse effects |
29 |
| 1,2-Dichlorobenzene |
µg/g,
(sediment containing 1% organic carbon)
0.023 no adverse effects on biota |
29 |
| 1,4-Dichlorobenzene |
µg/g,
(when sediment contains 1% organic carbon)
0.031 no adverse effects on biota
0.09 minor adverse effects |
29 |
Dichloro
diphenyl dichloroethane
1,1-Dichloro 2,2-bis
(p-chloro-phenyl) ethane
- freshwater
p,p'-DDD |
µg/g
0.00354 ISQG
0.00851 PEL |
1 |
Dichloro
diphenyl dichloroethane
1,1-Dichloro 2,2-bis
(p-chloro-phenyl) ethane
- marine
p,p'-DDD |
µg/g
0.00122 ISQG
0.00781 PEL |
1 |
Dichloro
diphenyl dichloroethene
1,1-Dichloro 2,2-bis
(p-chloro-phenyl) ethene
- freshwater
p,p'-DDE |
µg/g
0.00142 ISQG
0.00675 PEL |
1 |
Dichloro
diphenyl dichloroethene
1,1-Dichloro 2,2-bis
(p-chloro-phenyl) ethene
- marine
p,p'-DDE |
µg/g
0.00207 ISQG
0.374 PEL |
1 |
Dichloro
diphenyl trichloroethane
1,1,1-Trichloro 2,2-bis
(p-chloro-phenyl) ethane
- freshwater & marine
total DDT |
µg/g
0.00119 ISQG
0.00477 PEL |
1 |
Dieldrin
- freshwater
|
µg/g
0.00285 ISQG
0.00667 PEL |
1 |
Dieldrin
- marine |
µg/g
0.00071 ISQG
0.0043 PEL |
1 |
Diethyl
phthalate
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.61 no adverse effect on biota
1.10 minor adverse effects |
29 |
Diethyl
phthalate
- marine |
µg/g,
(when sediment contains 1% organic carbon)
0.61 lowest AET benthic community composition |
31 |
Dimetyl
phthalate
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.53 no adverse effects on biota |
29 |
Di-n-butyl
phthalate
- marine |
µg/g,
(when sediment contains 1% organic carbon)
2.2 no adverse effect on biota
17 minor adverse effects |
29 |
Di-N-octyl
phthalate
- marine |
µg/g,
(when sediment contains 1% organic carbon)
0.58 no adverse effects on biota
45 minor adverse effects |
29 |
Endrin
- freshwater & marine |
µg/g
0.00267 ISQG
0.0624 PEL |
|
1 |
Heptachlor (Heptachlor
epoxide)
- freshwater & marine |
µg/g
0.0006 ISQG
0.00274 PEL |
1 |
Hexachlorobenzene
- freshwater
|
µg/g, (when sediment contains 1% organic carbon)
0.01 no effect level based on EqP
0.02 lowest effect level based on SLC
0.24 severe effect level |
28 |
Hexachlorobenzene
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.0038 no adverse effects on biota
0.023 minor adverse effects |
29 |
Hexachlorobenzene
- marine |
µg/g
0.23 maximum level for drege disposal based on AET |
33 |
Hexachlorobutadiene
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.039 no adverse effects on biota
0.062 minor adverse effects |
29 |
| Hexachlorocyclohexane |
see
Benzene hexachloride (a conserved misleading name)
see Lindane (gamma isomer only)
|
— |
Iron
(total)
- freshwater
|
µg/g
21,200 (about 2%) lowest effect level based on SLC
43,766 (about 4%) severe effects level based on SLC |
34 |
Lead
(total)
- freshwater
|
µg/g
35 ISQG
91 PEL |
1 |
Lead
(total)
- marine
|
µg/g
30 ISQG
112 PEL |
1 |
Lindane-gamma
BHC
(Hexachlorocyclohexane)
- freshwater
|
µg/g
0.00094 ISQG
0.00138 PEL |
1 |
Lindane-gamma
BHC
(Hexachlorocyclohexane)
- marine |
µg/g
0.00032 ISQG
0.00099 PEL |
1 |
Mercury
(total)
- freshwater
|
µg/g
0.170 ISQG
0.486 PEL |
1 |
Mercury
(total)
- marine
|
µg/g
0.130 ISQG
0.70 PEL |
1 |
Mirex
- freshwater
|
µg/g, (when sediment contains 1% organic carbon)
0.007 lowest effect level based on SLC
1.30 severe effect level based on SLC |
28 |
Nickel
(total)
- freshwater
|
µg/g
16 lowest effect level based on SLC
75 severe effect level based on SLC |
34 |
Nickel
(total)
- marine |
µg/g
30 effects range low based on NSTPA
50 effects range median based on NSTPA |
30 |
N-Nitrosodiphenylamine
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.11 no adverse effect on biota |
29 |
Nonylphenol (NP) and its ethoxylates
- freshwater
|
µg/g dry weight, assuming 1% total organic carbon
1.4, provisional maximum using equilibrium partitioning approach, expressed on a toxic equivalency basis using NP toxic equivalency factors. See reference.
|
1 |
Nonylphenol (NP) and its ethoxylates
- marine
|
µg/g dry weight, assuming 1% total organic carbon
1.0, provisional maximum using equilibrium partitioning approach, expressed on a toxic equivalency basis using NP toxic equivalency factors. See reference.
|
1 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
total PCBs |
µg/g,
(when sediment contains 1% organic carbon)
0.02 no effect level, approved provincial guideline |
35 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
total PCBs
|
µg/g
0.0341 ISQG
0.277 PEL |
1 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
Arochlor 1254 |
µg/g
0.060 ISQG
0.340 PEL
Provisional, assuming 1% total organic carbon
|
1 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
Arochlor 1254 |
µg/g,
(when sediment contains 1% organic carbon)
0.34 severe effect level based on SLC 90th percentile |
28 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
Arochlor 1016 |
µg/g,
(when sediment contains 1% organic carbon)
0.007 lowest effect level based on SLC 10th percentile
0.53 severe effect level based on SLC 90th percentile |
28 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
Arochlor 1248 |
µg/g,
(when sediment contains 1% organic carbon)
0.03 lowest effect level based on SLC 10th percentile
1.50 severe effect level based on SLC 90th percentile |
28 |
Polychlorinated
Biphenyls (PCBs)
- freshwater
Arochlor 1260 |
µg/g,
(when sediment contains 1% organic carbon)
0.005 lowest effect level based on SLC 10th percentile
0.24 severe effect level based on SLC 90th percentile |
28 |
Polychlorinated
Biphenyls (PCBs)
- marine
total PCBs
|
µg/g,
(when sediment contains 1% organic carbon)
0.02 no effect level, approved provincial guideline |
35 |
Polychlorinated
Biphenyls (PCBs)
- marine
total PCBs |
µg/g
0.0215 ISQG
0.189 PEL |
1 |
Polychlorinated
Biphenyls (PCBs)
- marine
Arochlor 1254 |
µg/g
0.06333 ISQG
0.709 PEL
Provisional, assuming 1% total organic carbon |
1 |
Polychlorinated dibenzo-p-dioxins/dibenzo furans (PCDD/Fs)
- freshwater & marine
|
µg/g dry weight
0.85 ISQG
21.5 PEL
Provisional maximum expressed on a toxic equivalency basis using toxic equivalent factors for fish. See reference.
|
1 |
Polycyclic
Aromatic Hydrocarbons (PAHs) total
- freshwater
|
µg/g
4 effects range low based on NSTPA
35 effects range medium |
30 |
Polycyclic
Aromatic Hydrocarbons (PAHs) total
- freshwater
|
µg/g,
(when sediment contains 1% organic carbon)
100 severe effect level |
39 |
Polycyclic
Aromatic Hydrocarbons (PAHs) LPAH
lower molecular weight
- freshwater
|
µg/g
0.1 no effects threshold based on BA |
32 |
Polycyclic
Aromatic Hydrocarbons (PAHs) HPAH
higher molecular weight
- freshwater
|
µg/g
1.0 no effects threshold based on BA |
32 |
Polycyclic
Aromatic Hydrocarbon (PAH) Acenaphthene
- freshwater |
µg/g
0.00671 ISQG
0.0889 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Acenaphthylene
- freshwater |
µg/g
0.00587 ISQG
0.128 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Anthracene
- freshwater |
µg/g
0.0469 ISQG
0.245 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(a)anthracene
- freshwater |
µg/g
0.0317 ISQG
0.385 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzofluoranthene
- freshwater
|
µg/g
0.3 no effect threshold based on BA |
32 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(k)fluoranthene
- freshwater |
µg/g
0.24 lowest effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(k)fluoranthene
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
13.4 severe effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- freshwater |
µg/g
0.1 no effect threshold based on BA |
32 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- freshwater |
µg/g
0.17 lowest effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
3.2 severe effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH)
Benzo(a)pyrene
- freshwater |
µg/g
0.0319 ISQG
0.782 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Chrysene
- freshwater |
µg/g
0.0571 ISQG
0.862 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Dibenzo(a,h) anthracene
- freshwater |
µg/g
0.00622 ISQG
0.135 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Fluoranthene
- freshwater
|
µg/g
0.111 ISQG
2.355 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Fluorene
- freshwater |
µg/g
0.0212 ISQG
0.144 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Indeno (1,2,3,c,d) pyrene
- freshwater |
µg/g
0.07 no effect threshold based on BA |
32 |
Polycyclic
Aromatic Hydrocarbon (PAH) Indeno (1,2,3,c,d) pyrene
- freshwater |
µg/g
0.2 lowest effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Indeno (1,2,3,c,d) pyrene
- freshwater |
µg/g,
(when sediment contains 1% organic carbon)
3.2 severe effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH)
2-methylnaphthalene
- freshwater
|
µg/g
0.0202 ISQG
0.201 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Naphthalene
- freshwater
|
µg/g
0.0346 ISQG
0.391 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Phenanthrene
- freshwater |
µg/g
0.0419 ISQG
0.515 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Pyrene
- freshwater |
µg/g
0.053 ISQG
0.875 PEL |
1 |
Polycyclic
Aromatic Hydrocarbons (PAHs) LPAH lower molecular weight
- marine |
µg/g,
(when sediment contains 1% organic carbon)
3.7 no adverse effects on biota
7.8 minor adverse effects on biota |
29 |
Polycyclic
Aromatic Hydrocarbons (PAHs) HPAH higher molecular weight
- marine |
µg/g,
(when sediment contains 1% organic carbon)
9.6 no adverse effects on biota
53 minor adverse effects on biota |
29 |
Polycyclic
Aromatic Hydrocarbon (PAH) Acenaphthene
- marine |
µg/g
0.00671 ISQG
0.0889 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Acenaphthylene
- marine |
µg/g
0.00587 ISQG
0.128 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH)
Anthracene
- marine |
µg/g
0.0469 ISQG
0.245 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(a)anthracene
- marine |
µg/g
0.0748 ISQG
0.693 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzofluroanthenes (all)
- marine |
µg/g,
(when sediment contains 1% organic carbon)
2.3 no adverse effect on biota
4.5 minor adverse effects on biota |
29 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.31 no adverse effect on biota
0.78 minor adverse effects on biota |
29 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- marine |
µg/g
0.17 lowest effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(g,h,i)perylene
- marine |
µg/g, (when sediment contains 1% organic carbon)
3.2 severe effect level based on SLC |
39 |
Polycyclic
Aromatic Hydrocarbon (PAH) Benzo(a)pyrene
- marine |
µg/g
0.0888 ISQG
0.763 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Chrysene
- marine
|
µg/g
0.108 ISQG
0.846 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Dibenzo(a,h) anthracene
- marine |
µg/g
0.00622 ISQG
0.135 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Fluoranthene
- marine
|
µg/g
0.113 ISQG
1.494 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Fluorene
- marine
|
µg/g
0.0212 ISQG
0.144 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Indeno (1,2,3,c,d) pyrene
- marine |
µg/g,
(when sediment contains 1% organic carbon)
0.34 no adverse effect on biota
0.88 minor adverse effect on biota |
29 |
Polycyclic
Aromatic Hydrocarbon (PAH)
2-methylnaphthalene
- marine
|
µg/g
0.020 ISQG
0.202 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Naphthalene
- marine |
µg/g
0.0346 ISQG
0.391 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Phenanthrene
- marine
|
µg/g
0.0867 ISQG
0.544 PEL |
1 |
Polycyclic
Aromatic Hydrocarbon (PAH) Pyrene
- marine
|
µg/g
0.153 ISQG
1.398 PEL |
1 |
Selenium
(total)
-freshwater
|
µg/g
5 |
37
(p. 3) |
Silver
(total
- freshwater
|
µg/g
0.5 Ontario sediment quality guideline |
36 |
Silver
(total)
- marine
|
µg/g
1.0 effects range low based on NSTPA
2.2 effects range median based on NSTPA |
30 |
1,2,4-Trichlorobenzene
- marine
|
µg/g,
(when sediment contains 1% organic carbon)
0.0081 no adverse effects on biota
0.018 minor adverse effects
0.064 maximum level for dredge disposal |
29 |
Toxaphpene
- freshwater & marine |
µg/g, (when sediment contains 1% organic carbon)
0.0001, provisional maximum |
1 |
Zinc
(total)
- freshwater |
µg/g
123 ISQG
315 PEL |
1 |
Zinc
(total)
- marine
|
µg/g
124 ISQG
271 PEL |
1 |
1.
Concentrations are expressed as µg/g or µg/g
sediment containing 1% organic carbon. A guideline
expressed as µg/g is based on the sediment
as a whole and does not require adjustment for organic
carbon content. Adjustments to guidelines are required
when they are expressed in terms of the sediment
containing
1% organic carbon. For sediments with organic carbon
other than 1%, an adjustment in guidelines should
be made by multiplying the guideline by the % organic
carbon content of the sediment.
2.
SLC = Screening Level Concentration
3.
CoA = Co-Occurrence analyses
4.
AET = Apparent Effects Threshold
5.
EqP = Equilibrium Partitioning
6.
NSTPA = National Status and Trends Program Approach
7.
BA = Background Approach
8.
PEL = Probable Effect Level
9.
ISQG = Interim Sediment Quality Guideline
10.
EPA = United States Environmental Protection Agency
|
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to the Table of Contents
References
1.
Canadian Council of Ministers of the Environment, October 2005. Canadian Environmental Quality Guidelines.
2. Swain, L. G. 1987.
Second report on chemical sensitivity of BC lakes to acidic
inputs. Water Management Branch, Ministry
of Environment, Victoria, BC. 31p.
3. National Recommended Water
Quality Guidelines; Notice; Republication. Federal Register
Vol 63, No. 237, Part IV. EPA. December 10,
1998.
4. Fletcher, T., G. L. Stephenson, J. Wang, C. D. Wren
and B. W. Muncaster. 1996. Scientific criteria document for
the development
of a provincial water quality guideline for antimony. Ontario
Ministry of Environment and Energy. ISBN 0-7778-4619-5. 32p.
5.
National Academy of Sciences. 1972. Water Quality Criteria
1972, Washington, DC., 1972. (The Blue Book).
6.
US Environmental Protection Agency. 2002.
7. Plumley, F. G. and D. E. Davis. 1980.
The effects of a photosynthetic inhibitor, atrazine, on salt
marsh adaphic algae in culture,
microcosms, and in the field. Estuaries 3: 217-223.
8. Haywood,
G. P. and R. W. Drinnan (Dobrocky Seatech Ltd.). 1983. A Literature
Review and Report on Barium Toxicity in freshwater, In Relation to the Monkman Coal Project, February, 1983,
49 p. (Prepared for: Petro-Canada Exploration Ltd.).
9. Spangenberg,
J. V., and G. N. Cherr. 1996. Developmental effects of barium
exposure in a marine (Mytilus californianus).
Environ. Toxicol. Chem. 15: 1769-1774.
10. 20460. EPA 440/5-86-001.
(The Gold Book).
11. US EPA. 1976. Quality Criteria for Water,
July 1976. (The Red Book).
12. American Fisheries Society. 1979.
A Review of the EPA Red Book: Quality Criteria for Water, April
1979.
13.
Ministry of Environment, Lands and Parks. 2000. Water Quality Assessment and Objectives for the Lower Columbia River: Birchbank to the International Border. Overview Report..
14.
Efroymson, R.A., G.W. Suter II, B.E. Sample, and D.S. Jones. 1997. Preliminary Remediation Goals for Ecological Endpoints. ES/ER/TM-162/R2. Prepared for the U.S. Department of Energy, Office of Environmental Management under budget and reporting code EW 20. Web site: http://www.hsrd.ornl.gov/ecorisk/tm162r2.pdf.
15. US
Environmental Protection Agency. 1989. Drinking water health
advisory: Pesticides. Office of Drinking Water Advisories,
Washington, D.C.
16.
Michigan Department of Environmental Quality (MDEQ). 2006 Rule 57. Guideline Levels, Great Lakes and Environmental Assessment Section, Surface Water Quality Division, Department of Environmental Quality, Michigan p3.
17.
Water Quality Criteria Second Edition. Publication 3-A (Reprint, June 1, 1974). Edited by J.E. McKee and H.W. Wolf. The Resource Agency of California State Water Resources Control Board. P. 244.
18. Andrews, D. and C. Neville. 1994. Scientific criteria document for the development of provincial water quality guidelines for alkylleads. Ontario Ministry of Environment and Energy. ISBN 0-7778-2856-1. 42p.
19. Australian and New Zealand Guidelines for Fresh and Marine Water Quality. Volume 1. October 2000. National Water Quality Management Strategy, Paper No. 4.
20. Sigma Environmental Consultants Ltd. 1983. Summary of Water Quality Criteria For Salmonid Hatcheries (SECL 8067, Revised Edition, October 1983) (Prepared for Dept. of Fisheries and Oceans).
21. Department of Environment, Inland Waters Branch. 1972. Guidelines for Water Quality Objectives and Standards, Technical Bulletin No. 67, Ottawa, Canada.
22. Sweet, H. R. and R. H. Fetrow. 1975. Ground-Water Pollution By Wood Waste Disposal. Ground Water. 13(12):227-231.
23. Pontius, F.W. 1996. An update of the federal regs. Jour. Amer. Water Works Ass. Arch 1996: 36-46.
24. Water Management Policies, Guidelines, and Provincial Water Quality Objectives of the Ministry of Environment and Energy, Ontario. July 1994. Reprinted February 1999. ISBN 0-7778-8473-9 rev.
25. Andrews, D., K. Reid, and C. Neville. 1995. Scientific criteria document for the development of provincial water quality guidelines for organotins. Ontario Ministry of Environment and Energy. ISBN 0-7778-3068-X. 93p.
26. Ontario Ministry of Environment. 1989. Parameters Listing System (PALIS). Drinking Water Section, Water Resources Branch, Toronto.
27. Environment Canada. Guidelines for surface water quality, Vol. 1, Inorganic chemical substances. (Series of reports 1979 to 1983).
28. Jaagumagi, R. 1992. Development of the Ontario Provincial Sediment Quality Guidelines for PCBs and the Organochlorine Pesticides. Water Resources Branch, Ontario Ministry of the Environment.
29. Sediment Management Standards, Washington State Department of Ecology, April 1991.
30. Long, E. R., and Morgan, L. G. 1990. The Potential for Biological Effects of Sediment Sorbed Contaminants Tested in the National Status and Tends Program, National Oceanic and Atmospheric Administration, Seattle, Washington.
31. Barrick, R., S. Becker, L. Brown, H. Beller and R. Pastorok. 1988. Sediment Quality Values Refinement: 1988 Update and Evaluation of Puget Sound AET. Vol.1 Prepared for the Puget Sound Estuary Program. PTI Environmental Services, Bellevue, Wash. (Cited from: D. D. MacDonald, S. L Smith, M. P. Wong and P. Murdoch. 1992. The development of Canadian Marine Environmental Quality Guidelines. Marine)
32. Environment Canada and Ministry of the Environment of Quebec. July 1992. Interim criteria for quality assessment of St. Lawrence River Sediment. Environment Canada, St. Lawrence Centre, and Ministry of the Environment of Quebec.
33. Puget Sound Dredged Disposal Analysis. 1989. Management Plan Report: Unconfined Openwater Disposal of Dredged Material Phase II (north and south Puget Sound). Washington State Department of Natural Resources, Olympia, Wash. Cited from D. D. MacDonald, S. L. Smith, M. P. Wong and P. Murdoch. 1992. The development of Canadian marine environmental quality guidelines. Marine Environmental Quality Series No.1. Ecosystem Sciences and Evaluation Directorate, EcoHealth Branch, Ottawa, Ont.
34. Jaagumagi, R. 1992. Development of the Ontario Provincial Sediment Quality Guidelines for Arsenic, Cadmium, Chromium, Copper, Iron, Lead, Manganese, Mercury, Nickel, and Zinc. Water Resources Branch, Ontario Ministry of the Environment.
35. Nagpal, N. K. 1992. Water quality criteria for polychlorinated biphenyls. Water Quality Branch, Water Management Division, Ministry of Environment, Lands and Parks, Victoria, BC.
36. Persaud, D., R. Jaagumagi, and A. Hayton. 1992. Guidelines for the protection and management of aquatic sediment quality in Ontario. Report No. ISBN 0772992487. Ontario Ministry of Environment, Water Resources Branch.
37. International Joint Commission. 1981. Report to the Great Lakes Science Advisory Board. Report of the Aquatic Ecosystem Objectives Committee, Nov. 1981.
38. Environment Ontario. 1988. Scientific Criteria Document For Development of Provincial Water Quality Objectives and Guidelines, Resin Acids. ISBN 0-7729-4347-8.
39. Persaud, D., R. Jaagumagi, and A. Hayton. 1993 (March). Guidelines for the protection and management of aquatic sediment quality in Ontario. Report No. ISBN 0772992487. Ontario Ministry of Environment, Water Resources Branch.
40. Anon. 1999 (March).Complying with the Stage 1 D/DEP Rule. JAWWA, 91(3): 16-32.
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