Summary {-}

st <- read.csv("../data/data-metadata/metadata_stresseurs.csv")
cv <- read.csv("../data/data-metadata/metadata_composantes_valorisees.csv")
st$stresseur <- gsub("_","",st$stresseur)
cv$comp_val <- gsub("_","",cv$comp_val)

src <- function(dat) {
    paste(dat$source, collapse = ",") %>%
    str_split(",") %>%
    unlist() %>%
    unique() %>%
    length()
}

ct1 <- function(dat) {
  dat %>%
  group_by(title, stresseur) %>%
  summarize(tot = n()) %>%
  apply(., 1., function(x) glue("[{x[1]}](#{x[2]}) ({x[3]})")) %>%
  gsub("\\( ", "\\(", .) %>%
  paste(collapse = "; ") %>%
  tolower()
}

ct2 <- function(dat) {
  dat %>%
  group_by(title, comp_val) %>%
  summarize(tot = n()) %>%
  apply(., 1., function(x) glue("[{x[1]}](#{x[2]}) ({x[3]})")) %>%
  gsub("\\( ", "\\(", .) %>%
  paste(collapse = "; ") %>%
  tolower()
}

Through the St. Lawrence action plan, the Government of Canada and the Government of Quebec have been collaborating since 2018 on a common framework for the assessment of the cumulative effects of marine vessel activities on the St. Lawrence and Saguenay River, working closely with First Nations, various stakeholders and coastal communities. A team from Laval University was mandated for a pilot assessment of cumulative effects. The objective of the pilot project was to propose and test a cumulative effects assessment approach in a study area that covers the St. Lawrence (fluvial section and estuary) and the Saguenay River (deep water section). This pilot project is centered on the assessment of the cumulative effects of 7 environmental stressors originating from marine vessel activities on 5 valued components identified beforehand through consultation workshops with relevant experts, collaborators, and stakeholders.

The method selected to assess the cumulative effects of marine vessel activities in the study area comes from @halpern2008a and requires three types of data: 1) the spatial presence or absence of valued components, 2) the spatial distribution and relative intensity of environmental stressors, and 3) the relative vulnerability of each valued component to each stressor. The proposed method combines those three elements to obtain a cumulative effects score that is relative and spatially explicit.

The process of gathering the necessary data to apply this cumulative effects approach is referred to, in this report, as the portrait of the study area. The characterization of environmental stressors was done through the integration of r src(st) datasets and results in the description of r length(unique(st$title)) stressors divided in r nrow(st) subcategories: r ct1(st). The characterization of valued components, meanwhile, was done through the integration of r src(cv) datasets and resulted in the description of r length(unique(cv$title)) valued components divided in r nrow(cv) subcategories: r ct2(cv). Finally, an approach combining metrics of exposure and sensitivity -- e.g. stressor frequency, trophic impact, resistance, resilience, legal status -- was used to assess the relative vulnerability of subcategories of valued components to subcategories of environmental stressors.

Here, we detail the general observations that arise from the cumulative effects assessment as bullet points. Additional observations are presented in the report and can also be done by exploring the results of the assessment; we invite the reader to explore section \@ref(resultats) of the report for more information, and in particular to explore the figures provided. All the data evaluated and used for this assessment are available in appendix 1 and updates to the assessment are detailed in appendix 10.









EffetsCumulatifsNavigation/ceanav documentation built on April 17, 2023, 1:02 p.m.