Sediment quality status of Lake Saint-Louis in 2015
Highlights
Status: Sediment quality in the northern sector of Lake Saint-Louis is good. Nearly 60% of samples have concentrations below the quality criteria thresholds. Sediment quality in the southern sector is classified as moderate-poor, primarily because of high concentrations of several contaminants measured near Beauharnois and in the Îles de la Paix basin (figure 1).
Trend: In both sectors of Lake Saint-Louis, the mean concentrations of the majority of substances decreased between 2003 and 2015.
Figure 1. Sediment sampling sites in Lake Saint-Louis between 2003 and 2015 and contamination index
Issue
Lake Saint-Louis was a major industrial hub for Quebec in the middle of the 20th century. With the opening of the St. Lawrence Seaway and construction of the Beauharnois hydroelectric dam, the upstream part of Lake Saint-Louis became heavily industrialized, and its aquatic environment has been severely impacted by discharges of toxic contaminants. The sediments of Lake Saint-Louis became increasingly contaminated with toxic substances, such as mercury and polychlorinated biphenyls (PCBs). However, since the 1970s, government action and control plans have reduced contaminant inputs to the St. Lawrence River and, consequently, into Lake Saint-Louis.
Lake Saint-Louis sediment quality monitoring took place in 2003 and in 2015, as changes in contaminant concentrations occur only very slowly and are perceptible on a 10-year time scale. The sediments of Lake Saint-Louis were sampled by Environment and Climate Change Canada (ECCC) and tested for numerous contaminants. The results presented in this factsheet refer to the northern and southern sectors of the lake as a function of sampling location relative to the St. Lawrence Seaway.
Key measuresSediment quality criteria and indicesThe sediment quality criteria used in this document (TEL: threshold effect level) are taken from Environment Canada and Ministère du Développement Durable, de l’Environnement et des Parcs du Québec [EC et MDDEP] (2007). They are defined on the basis of observed biological effects on benthic and pelagic organisms and contaminant concentrations measured in sediment.The quality indices are calculated by dividing the measured concentration of each substance (mercury, metals, PCBs and PAHs) in each sample by the TEL quality criterion for the substance in question. An index higher than 1 indicates that the concentration exceeds the criterion and biological effects may be observed, whereas an index lower than 1 indicates that sediment quality is good. Mean quality indices were calculated for metals (except mercury) and PAHs. The overall indicator status is based on the proportion of uncontaminated sites and contaminated sites relative to the total number of sites characterized. This proportion defines an overall status that ranges from good to poor. |
Sediment quality of Lake Saint-Louis
Northern sector of Lake Saint-Louis
Status in 2015: The overall sediment quality status of the northern sector of Lake Saint-Louis is considered good. Of a total of 53 samples collected north of the St. Lawrence Seaway, 60% showed concentrations below the threshold effect levels (TEL) used to assess sediment quality.
Mean concentrations of metals, mercury, PCBs, polybrominated diphenyl ethers (PBDEs), dioxins and furans, and polycyclic aromatic hydrocarbons (PAHs) are all below their respective TEL, with the exception of dibenzo(ah)anthracene which slightly exceeds its TEL (Table 1).
Table 1. Mean concentrations of the various substances measured in sediments (0 - 3 cm) from the northern sector of Lake Saint-Louis between 2003 and 2015
Substances measured | Quality criterion (1) | Sediment sampling year | Change in mean concentration (2) | |
---|---|---|---|---|
2003 | 2015 | Between 2003 and 2015 (%) | ||
Metals index | 1 | 0,85 | 0,73 | 14 |
Arsenic (µg/g) | 5,9 | 4,7 | 4,5 | 4 |
Cadmium (µg/g) | 0,6 | 0,63 | 0,50 | 19 |
Nickel (µg/g) | 47 | 25,3 | 21,7 | 14 |
Lead (µg/g) | 35 | 16,8 | 13,7 | 18 |
Chrominium (µg/g) | 37 | 36,1 | 32,1 | 11 |
Copper (µg/g) | 36 | 19,7 | 16,6 | 16 |
Zinc (µg/g) | 120 | 135,3 | 111,8 | 17 |
Mercury (µg/g) | 0,17 | 0,071 | 0,073 | -3 |
Polychlorinated biphenyls (PCBs) | ||||
Homologs (ng/g) | 34 | 27,3 | 17,9 | 34 |
Congeners (ng/g) | 34 | 18,4 | 11,9 | 35 |
Polybrominated diphenyl ethers (PBDEs) | ||||
BDE #99 (ng/g) | 0,4 | 0,43 | 0,38 | 12 |
BDE#100 (ng/g) | 0,4 | 0,13 | 0,11 | 16 |
Dioxins et furans | ||||
PCDD (pg tox. eq./g) | 0,85 | 0,120 | ||
PCDF (pg tox. eq./g) | 0,85 | 0,568 | ||
PAH index | 1 | 0,71 | 0,67 | 6 |
2-Methylnaphtalene (ng/g) | 20 | 5,4 | 6,1 | -13 |
Acenaphtene (ng/g) | 6,7 | 4,5 | 4,6 | -1 |
Acenaphthylene (ng/g) | 5,9 | 4,5 | 4,7 | -4 |
Anthracene (ng/g) | 47 | 5,4 | 8,4 | -56 |
Benzo(a)pyrene (ng/g) | 32 | 30,2 | 26,7 | 11 |
Benzo(a)anthracene (ng/g) | 32 | 20,3 | 26,1 | -29 |
Chrysene (ng/g) | 57 | 39,0 | 29,5 | 24 |
Dibenzo(ah)anthracene (ng/g) | 6,2 | 8,8 | 7,4 | 16 |
Fluoranthene (ng/g) | 110 | 53,1 | 52,4 | 1 |
Fluorene (ng/g) | 21 | 5,0 | 6,1 | -21 |
Naphtalene (ng/g) | 35 | 10,0 | 10,9 | -9 |
Phenanthrene (ng/g) | 42 | 28,5 | 26,4 | 7 |
Pyrene (ng/g) | 53 | 46,1 | 40,6 | 12 |
(1) EC and MDDEP. 2007; Exceedances of criteria are indicated in red.
(2) Mean: The mean values presented correspond to the geometric means of the measured values – the geometric mean is a good trend assessment tool.
Changes from 2003 until 2015: Over this period, the mean concentration of the metals index decreased by 14%, which indicates that the river system still has the capacity to recover from past disturbance. Taken individually, several metals are found at concentrations almost identical to their natural levels (see Table 3 in EC and MDDEP, 2007). Since the ban on PCBs in the late 1980s, their mean concentration has continued to decline at a rate of about 30% by decade. With the regulation of PBDEs in 2008, concentrations of these substances of emerging concern are now decreasing. Mean concentrations of various PAHs, with the exception of dibenzo(ah)anthracene, were all below their quality criteria in 2003, and the variations observed in 2015 are not significant. Based on the current trend, which decreased by 16% between 2003 and 2015, the mean concentration of dibenzo(ah)anthracene is expected to reach a level below its criterion within a decade.
Southern sector of Lake Saint-Louis
Status in 2015: The overall sediment quality status of the southern sector of Lake Saint-Louis in 2015 is rated as moderate-poor. Of the 42 sediment samples collected from the area south of the St. Lawrence Seaway, over 72% showed concentrations above the TEL. These exceedances are mainly related to the presence of mercury, PCBs, furans and PAHs (Table 2).
Changes since 2003: Between 2003 and 2015, mean concentrations of all substances decreased a significant 12% to 53%, except certain PAHs, which are present at very low concentrations and show non-significant variations. Mercury is the main contaminant, with a mean value 1.5 times above its quality criterion. It decreased by less than 15% between 2003 and 2015, compared to PCBs, which decreased by more than 40% over the same period. As with mercury, furans decreased by only 13% and remained well above their TEL. Finally, as shown by the 34% decrease recorded for the PAH index, several of these substances, including those that were present at the highest concentrations in 2003, decreased by at least 30%, indicating a good recovery of the aquatic environment for these contaminants.
Table 2. Mean concentrations of the various substances measured in sediments (0 – 3 cm) from the southern sector of Lake Saint-Louis between 2003 and 2015
Substances measured | Quality criterion (1) | Sediment sampling year | Change in mean concentration (2) | |
---|---|---|---|---|
2003 | 2015 | Between 2003 and 2015 (%) | ||
Metals index | 1 | 0,79 | 0,64 | 19 |
Arsenic (µg/g) | 5,9 | 4,4 | 3,9 | 12 |
Cadmium (µg/g) | 0,6 | 0,48 | 0,37 | 24 |
Nickel (µg/g) | 47 | 25,0 | 21,0 | 16 |
Lead (µg/g) | 35 | 16,6 | 11,7 | 30 |
Chromium (µg/g) | 37 | 34,9 | 29,1 | 17 |
Copper (µg/g) | 36 | 24,3 | 20,8 | 14 |
Zinc (µg/g) | 120 | 108,9 | 87,4 | 20 |
Mercury (µg/g) | 0,17 | 0,283 | 0,251 | 12 |
Polychlorinated biphenyls (PCBs) | ||||
Homologs (ng/g) | 34 | 65,8 | 38,1 | 42 |
Congeners (ng/g) | 34 | 43,1 | 24,6 | 43 |
Polybrominated diphenyl ethers (PBDEs) | ||||
BDE #99 (ng/g) | 0,4 | 0,10 | 0,09 | 13 |
BDE#100 (ng/g) | 0,4 | 0,04 | 0,02 | 44 |
Dioxins et furans | ||||
PCDD (pg tox. eq./g) | 0,85 | 0,183 | 0,161 | 12 |
PCDF (pg tox. eq./g) | 0,85 | 1,457 | 1,274 | 13 |
PAH index | 1 | 1,58 | 1,05 | 34 |
2-Methylnaphtalene (ng/g) | 20 | 7,6 | 8,7 | -15 |
Acenaphtene (ng/g) | 6,7 | 6,6 | 6,2 | 7 |
Acenaphthylene (ng/g) | 5,9 | 7,0 | 5,9 | 16 |
Anthracene (ng/g) | 47 | 13,8 | 12,2 | 12 |
Benzo(a)pyrene (ng/g) | 32 | 76,3 | 44,2 | 42 |
Benzo(a)anthracene (ng/g) | 32 | 66,5 | 41,7 | 37 |
Chrysene (ng/g) | 57 | 109,3 | 51,3 | 53 |
Dibenzo(ah)anthracene (ng/g) | 6,2 | 25,4 | 13,1 | 48 |
Fluoranthene (ng/g) | 110 | 116,7 | 80,0 | 31 |
Fluorene (ng/g) | 21 | 8,5 | 9,1 | -7 |
Naphtalene (ng/g) | 35 | 15,4 | 14,4 | 6 |
Phenanthrene (ng/g) | 42 | 48,0 | 38,3 | 20 |
Pyrene (ng/g) | 53 | 101,6 | 53,8 | 47 |
(1) EC and MDDEP. 2007; Exceedances of criteria are indicated in red.
(2) Mean: The mean values presented correspond to the geometric means of the measured values – the geometric mean is a good trend assessment tool.
Long-term trend
The results show that the majority of the contaminants measured in Lake Saint-Louis sediments in the northern and southern sectors have decreased over 12 years between 2003 and 2015. The temporal profiles performed on a sediment core taken in the Îles de la Paix basin confirm this downward trend for all contaminants (Figure 2). The decrease in concentrations began with the implementation of the various environmental controls and regulations. Current concentrations are similar to those measured in the 1940s and 1950s and, over the coming decades, they could reach the minimum concentrations recorded at the start of the last century.
Figure 2. Temporal profiles of a sediment core taken in the Îles de la Paix basin
Spatial analysis of contamination
Spatial analysis oThe spatial distribution maps presented in figures 3 to 5 show the main areas contaminated with PCBs, furans and mercury, respectively. Again, in 2015, these three contaminants are the most abundant and still pose a risk to aquatic life in Lake Saint-Louis.
Figure 3. PCB concentrations in Lake Saint-Louis sediments in 2015
Figure 4. Furan concentrations in Lake Saint-Louis sediments in 2015
Figure 5. Mercury concentrations in Lake Saint-Louis sediments in 2015
The area between the Beauharnois dam and the outlet of the Îles de la Paix basin is still significantly affected, although mean concentrations of PCBs, furans and mercury decreased by 12% to 42%. The complete recovery of this sedimentary area could take several more decades, as the section of the river near Beauharnois is dynamic with strong currents and frequent sediment resuspension.
Moreover, the land along the southern part of the area was heavily industrialized in the mid-20th century, and the rainwater that drains this territory is likely still contaminated when it flows into the river. The sedimentary basin located in the northern sector of Lake Saint-Louis still contains concentrations exceeding the sediment quality criteria, although the means are now below the criteria. This area should recover completely in the coming decades, given that contaminant inputs, mainly from the Ottawa River, have decreased significantly.
Outlook
Concentrations of toxic substances resulting from the industrial boom in the middle of the 20th century, such as PCBs, mercury and other metals, PAHs, and dioxins and furans, have significantly declined in the surface sediments of Lake Saint-Louis. In the northern sector, concentrations are below the values of the quality criteria for the protection of aquatic life, while in the southern sector, exceedances are still observed, particularly for PCBs, furans and mercury, and certain PAHs.
Sediment quality in the northern sector of Lake Saint-Louis can be considered good, even though there are still some local criterion exceedances. The southern sector remains highly contaminated, despite the various remediation measures taken since the 1980s. Environmental monitoring remains necessary in order to measure the trend towards recovery over the coming decades.
References
Environment Canada and Ministère du Développement Durable, de l’Environnement et des Parcs du Québec. 2007. Criteria for the Assessment of Sediment Quality in Quebec and Application Frameworks: Prevention, Dredging and Remediation. 39 pages. Criteria_sediment_2007E.pdf
Pelletier M. 2008. Toxic Contamination in Sediments — Lake Saint-Louis: Where Two Rivers Meet. Monitoring the State of the St. Lawrence River, Environment Canada. 8 pages.
Prepared by
Magella Pelletier
Fresh Water Quality Monitoring and Surveillance
Environment and Climate Change Canada
My thanks to Michel Arseneau, Germain Brault, Claude Lessard and Simon Blais of Environment and Climate Change Canada for their contributions to the fieldwork.
Thanks also to Simon Blais for the financial contribution from the Environmental Protection Operations Directorate under the St. Lawrence Action Plan.