APPENDIX C - Examples of Conceptual Models
Table C-1 Example of a Conceptual Model Applicable to the Dredging Site during the Work
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
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During the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Sediment dredging | Physical | Dredged sediments | Resuspension | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The sediments resuspended in the water column during dredging will reach the spawning sites of some fish species located downstream from the dredging site in sufficient quantity to significantly affect its potential. |
Noise | Diffusion | Ambient air | Fauna Human | The noise generated by dredging activities will affect the well-being of on-site workers and nearby residents. | ||||
Chemical | Contaminants (adsorbés aux sédiments dragués) | Resuspension | Water column | Hydrodynamic and hydrosedimento-logical conditions | Human Fauna Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The contaminants resuspended in the water column during dredging (adsorbed to the particles or dissolved) will be adsorbed by the organisms in the environment in sufficient quantity to trigger acute effects. | |
Contaminants (désorption du sédiment et diffusion) | Complexation Readsorption Release of potentially toxic natural substances | Water column | Hydrodynamic and hydrosedimento-logical conditions | Human Fauna Flora Particularity | The contaminants resuspended in the water column during dredging (adsorbed to the particles or dissolved) and absorbed by the organisms in the environment will be bioaccumulated by a harvested species (particularity) so as to render it unfit for human consumption. | |||
Volatilization | Ambient air | Dispertion | Human Fauna Flora Particularity | The contaminants associated with the dredged sediments will be volatilized in the ambient air in sufficient concentration to affect the health of on-site workers. |
Table C-2 Example of a Conceptual Model Applicable to the Dredging Site after Completion of the Work
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
After the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Dredging sediments | Physical | Suspended dredged sediments | Dispersion and sedimentation | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The sediments resuspended in the water column during dredging will reach the spawning sites of some fish species located downstream from the dredging site in sufficient quantity to affect its potential significantly. |
Undredged sediments | Sediment exposure | Sediments Interstitial water | Hydrosedimento-logical conditions | Fauna Flora Particularity | The grain-size distribution of the on-site sediments exposed after dredging precludes recolonization of the environment by a diversified benthic community. | |||
Chemical | Contaminants (adsorbed to the dredged sediments) | Dispersion and sedimentation | Water column | Transport by current | Human Fauna Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The contaminants resuspended in the water column during dredging (adsorbed to the particles or dissolved) will be absorbed by the organisms in the environment in sufficient quantity to trigger chronic effects. | |
Contaminants (desorption from the sediment and diffusion) | Complexation Readsorption Other | Water column | Hydrodynamic and hydrosedimento-logical conditions Environmental physicochemistry | |||||
Volatilization | Ambiant Air | Dispersion | ||||||
Contaminants (undredged sediments) | Sediment exposure | Sediments Interstitial water | Hydrosedimento-logical conditions Environmental physicochemistry | The chemical nature of the sediments exposed after dredging will allow recolonization of the environment and result in harmful effects for the organisms that will return to it. |
Table C-3 Example of a Conceptual Model Applicable to the Disposal Site during Disposal of Sediments in Open Water
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
During the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Disposal or containment of contaminated sediments in open water | Physical | Sediment disposal at sea | Dispertion | Water column | Hydrodynamic conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The sediments resuspended in the water column during disposal will reach concentrations that can clog the gills of fish located downstream from the ocean disposal site, triggering their acute mortality. |
Sedimentation | SSediments receptors | Hydrosedimento-logical conditions | Fauna Human Flora Particularity | The sediments will be deposited in part on a spawning site, leading to significantly reduced productivity. | ||||
Noise | Diffusioon | Ambient air | Topography | Fauna Human | The noise generated by the disposal activities will affect the well-being of nearby residents. | |||
Chemical | Contaminants (adsorbed to the dredged sediments) | Dispersion | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Flora Human Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The contaminants resuspended in the water column during disposal at sea (adsorbed to the particles or dissolved) will be absorbed by the organisms in the environment in sufficient quantity to trigger acute effects. | |
Contaminants (desorption from the sediment and diffusion) | Complexation Readsorption Release of potentially toxic natural substances | Water column | Hydrodynamic and hydrosedimento-logical conditions Environmental physicochemistry | Fauna Flora Human Particularity | ||||
Volatilization | Ambient air | Dispersion | Fauna Flora Human Particularity | The contaminants associated with the dredged sediments will be volatilized in the ambient air in sufficient concentration to affect the health of on-site workers. |
Table C-4 Example of a Conceptual Model Applicable to the Disposal Site after Sediment Disposal in Open Water
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
After the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Disposal in open water | Physical | Deposited sediments | Transport | Water column | Hydrodynamic conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The grain-size distribution of the sediments at the disposal site precludes recolonization of the environment by a diversified benthic community. |
Physical and chemical | Deposited sediments | Sediment exposure | Sediments Interstitial water | Hydrosedimento-logical conditions | Fauna Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The chemical and physical nature of the dredged materials deposited will allow for the recolonization of the environment and have harmful effects on the returning organisms. The sediments transported downstream during ocean disposal will be deposited on a spawning ground, which will significantly reduce its productivity (clogging and toxicity for sensitive life stages). The sediments transported downstream during ocean disposal will be deposited on a nursery site of a valued (for whatever reason) fish species in sufficient quantity to chronically affect the population (reduced survival and breeding success). |
Table C-5 Example of a Conceptual Model Applicable to On-site Sediment Capping Activities
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
During the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Capping contaminated sediments in open water | Physical | Capped sediments | Resuspension and transport during placement of materials | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The sediments resuspended in the water column during disposal will reach concentrations that can clog the gills of fish located downstream from the ocean disposal site, triggering their acute mortality. The grain-size distribution of the sediments at the disposal site precludes recolonization of the environment by a diversified benthic community. |
Other mechanisms related to the technology used | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | |||||
Chemical | Contaminants (adsorbed to the deposited sediments) | Resuspension and transport during placement of materials | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The contaminants resuspended in the water column during the work (adsorbed to the particles or dissolved) will be absorbed by the organisms in the environment in sufficient quantity to trigger acute effects. | |
Contaminants (desorption from the sediment and diffusion) | Complexation Readsorption | Water column | Hydrodynamic and hydrosedimento-logical conditions Environmental physicochemistry | Fauna Human Flora Particularity |
Table C-6 Example of a Conceptual Model Applicable to the Site after Completion of Sediment Capping Work
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
After the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Capping contaminated sediments in open water | Physical | Capped sediments | Bioturbation and erosion triggering failure of capping material and a leak | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The materials used to cap contaminated sediments do not provide protection against the hydrodynamic conditions of the watercourse, to the point of observing medium-term dispersion and downstream accumulation of contaminated sediments. |
Chemical | Contaminants (desorption from covered sediments) | Diffusion | Water column | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The contaminants dispersed downstream (adsorbed to the particles or dissolved) due to erosion of the capping site will be absorbed by the organisms in the environment in sufficient quantity to trigger acute effects. |
Table C-7 Example of Additional Conceptual Models Proposed during On-shore Disposal or Containment
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
---|---|---|---|---|---|---|---|---|
During the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
On-shore disposal or containment | Physical | Sédiments déposés | Loss | Surface water | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The quantity of fine particles released into the watercourse by the outflow of the sediment settling tank, which serves as a containment enclosure for the contaminated sediments, exceeds the recommended level for protection of aquatic life. |
Chemical | Contaminants (adsorbed to the dredged sediments) | Loss | Surface water | Hydrodynamic and hydrosedimento-logical conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | Contaminants considered to be bioaccumulative and persistent percolate through the containment enclosure of the contaminated sediments, thus presenting an unacceptable risk for the aquatic environment. |
Table C-8 Example of Additional Conceptual Models during Disposal in a Terrestrial Environment
Source | Stressor | Ecosystem | Apprehended response | Example of impact hypothesis | ||||
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During the work | Mechanism | Abiotic component | Mechanism | Receptor | ||||
Terrestrial disposal and containment | Physical | Deposited sediments | Air transportation | Atmosphere | Weather conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The residential population near the work site is inconvenienced by the dust generated and transported into the air by the winds from the sediment dewatering site. |
Noise | Diffusion | Ambient air | Topography | Fauna Human | The machinery and vehicles used for dredging and transport of sediments generate noise that disrupts a tourist area during the high season. | |||
Chemical | Contaminants (adsorbed to the deposited sediments) | Air transportation | Ambient air | Weather conditions | Fauna Human Flora Particularity | Consideration of the apprehended responses determined in the literature for each of the target receptors | The quantity of contaminants (adsorbed to the dust) breathed by the population of the nearby residential area exceeds the level considered acceptable for human health. | |
Contaminants | Desorption from the sediment and diffusion or percolation/td> | Groundwater | Hydrodynamic and hydrosedimento-logical conditions Environmental physicochemistry | Human Fauna Flora Particularity | The quantity of contaminants found in the water of a sampling well installed nearby, after transport of contaminants in the soil, exceeds the acceptable criterion for human health. | |||
Runoff water (from the dike or spillway) | Weather conditions | Human Fauna Flora Particularity | ||||||
Adjacent soil | Geochemical conditions | Human Fauna Flora Particularity |