Economic and Social Reports
Understanding factors shaping household environmental practices and behaviours in Canada
DOI: https://doi.org/10.25318/36280001202600900003-eng
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With Canada adopting the United Nations (UN) 2030 Agenda for Sustainable Development, reducing harm to the environment has been recognized as a key national priority (see Government of Canada [2023] and UN [n.d.] for more information on the Sustainable Development Goals). Previous research has shown that individuals with higher levels of education and income were more likely to engage in environmental practices and behaviours (Mustapha, 2013). Environmental practices and behaviours also vary by dwelling characteristics, such as housing type (e.g., detached dwellings may have greater environmental stewardship) and homeownership (Canuel et al., 2014; Huddart-Kennedy et al., 2009). However, few studies have examined how sociodemographic factors, dwelling characteristics and geographic context jointly shape environmental practices and interactions with nature in Canada.
Environmental behaviours may be influenced by intersecting social, housing and regional conditions; examining these factors together can provide a more comprehensive understanding of household environmental practices and behaviours. Using data from the 2021 Households and the Environment Survey, this study examines how kitchen waste composting and hazardous waste disposal vary among households. The study presents variations in these behaviours across sociodemographic, dwelling, interaction with nature and geographic characteristics (shown in charts). Multivariate analyses were also conducted to better isolate the relationships between behaviours and the various factors examined (these results are reported in the text, and the full data are available upon request).
Dwelling and contextual factors were more strongly associated than sociodemographic characteristics with kitchen waste composting practices
Overall, about 65% of households reported composting kitchen waste (data not shown). Contrary to prior research (e.g., Mustapha, 2013), income- and education-related differences were limited and inconsistent in the adjusted models, suggesting that dwelling and contextual factors may play a more substantial role than sociodemographic characteristics alone in composting kitchen waste (see Chart 1).

Data table for Chart 1
| Dwelling type | Participation |
|---|---|
| percent | |
|
|
| Single-detached | 71.9 Data table for Chart 1 Note * |
| Double | 74.4 Data table for Chart 1 Note * |
| Row or terrace | 66.3 Data table for Chart 1 Note * |
| Duplex | 67.5 Data table for Chart 1 Note * |
| Apartment or flat (reference category) | 48.5 |
| Tenure | |
| Rented | 50.8 Data table for Chart 1 Note * |
| Owned (reference category) | 70.2 |
| Time lived in dwelling | |
| Less than 5 years | 60.2 Data table for Chart 1 Note * |
| 5 to 9 years | 64.2 Data table for Chart 1 Note * |
| 10 years or more (reference category) | 68.5 |
| Visited parks or public greenspaces close to home Data table for Chart 1 Note 1 | |
| Visited parks or public greenspaces close to home (reference category) | 67.6 |
| Did not visit parks or public greenspaces close to home | 55.0 Data table for Chart 1 Note * |
| Did not have access to parks or public greenspaces close to home | 55.9 Data table for Chart 1 Note * |
| Grew vegetables, herbs, fruits, flowers or plants for personal use | |
| Yes | 72.6 Data table for Chart 1 Note * |
| No (reference category) | 53.0 |
| Participated in outdoor activities close to home | |
| Yes | 67.7 Data table for Chart 1 Note * |
| No (reference category) | 54.8 |
| Province | |
| Newfoundland and Labrador | 28.3 Data table for Chart 1 Note * |
| Prince Edward Island | 95.7 Data table for Chart 1 Note * |
| Nova Scotia | 91.5 Data table for Chart 1 Note * |
| Quebec | 60.1 Data table for Chart 1 Note * |
| Manitoba | 36.4 Data table for Chart 1 Note * |
| Saskatchewan | 31.2 Data table for Chart 1 Note * |
| British Columbia | 78.9 Data table for Chart 1 Note * |
| Ontario (reference category) | 66.9 |
| Census metropolitan areas (CMAs) | |
| Large CMAs (reference category) | 75.4 |
| Medium CMAs | 64.3 Data table for Chart 1 Note * |
| Small CMAs | 57.8 Data table for Chart 1 Note * |
| Small urban areas | 53.2 Data table for Chart 1 Note * |
| Non-urban areas | 60.0 Data table for Chart 1 Note * |
Dwelling characteristics
Households in apartments and flats (49%) had the lowest composting rate (see Chart 1), outpaced by those in single-detached houses (72%), doubles (74%), row and terrace houses (66%), and duplexes (68%). The differences (from 11 to 23 percentage points) largely remained when adjusting for other characteristics.Households that had lived in the same residence for less than 10 years (60% to 64%) were less likely to compost than those that had lived there for 10 years or more (69%). However, those that had lived in their current residence for 10 years or more were only 2 percentage points more likely than those that had lived there for a shorter period to compost, once all other factors were accounted for. In terms of housing tenure, renter households were less likely to compost (51%) compared with owner households (70%). Yet, once other factors were accounted for, the difference was reduced; renter households were 4 percentage points more likely to compost than owner households.
Households’ interactions with nature
Households that interacted with nature and participated in activities related to greenspaces and the outdoors were also more likely to compost. Those that reported not residing near parks or public greenspaces, and those that had access to these areas but did not visit them, were less likely to compost (55% to 56%) than those that had access to parks or public green spaces and visited them (68%). Meanwhile, households that grew vegetables, herbs, fruits, flowers or plants for personal use or had participated in outdoor activities were more likely to compost (68% to 73%) than those that did not participate in either activity (53%). This pattern of difference remained once other factors were accounted for.
Geographical variation
Composting rates were highest in Prince Edward Island (96%), Nova Scotia (91%) and British Columbia (79%). Compared with Ontario (67%), fewer households in Newfoundland and Labrador, Quebec, Manitoba, and Saskatchewan (28% to 60%) composted their kitchen waste. Compared with households in large census metropolitan areas (CMAs) (75%), households in all other population areas reported lower composting rates, ranging from 53% to 64%. Adjusted models showed a similar pattern of geographic differences.
Controlled hazardous waste disposal was associated with selected sociodemographic, dwelling and geographic characteristics
About 80% of households had hazardous waste to dispose of over the past 12 months (43% had pharmaceutical or medical waste; 38% had pesticides, chemical waste or e-waste; and 59% had textiles or fabric waste; data not shown). While three in four households disposed of it in a controlled way, the use of controlled disposal methods varied across groups (see Chart 2).

Data table for Chart 2
| Household composition | Pharmaceutical and medical waste | Pesticides and chemical waste | E-waste | Textiles and fabric waste |
|---|---|---|---|---|
| percent | ||||
Source: Statistics Canada, Households and the Environment Survey, 2021. |
||||
| Adults only | 67.2 Data table for Chart 2 Note * | 78.0 Data table for Chart 2 Note * | 54.1 Data table for Chart 2 Note * | 25.1 Data table for Chart 2 Note * |
| Adults with children | 61.2 Data table for Chart 2 Note * | 74.5 Data table for Chart 2 Note * | 49.2 Data table for Chart 2 Note * | 24.2 Data table for Chart 2 Note * |
| Seniors only (reference category) | 84.2 | 81.8 | 66.8 | 28.8 |
| Highest level of education | ||||
| College, CEGEP or other non-university certificate or diploma | 77.3 Data table for Chart 2 Note * | 81.3 Data table for Chart 2 Note * | 60.7 Data table for Chart 2 Note * | 27.9 Data table for Chart 2 Note * |
| Bachelor's degree (reference category) | 67.1 | 77.2 | 52.4 | 24.2 |
| Dwelling type | ||||
| Single-detached | 75.0 Data table for Chart 2 Note * | 80.8 Data table for Chart 2 Note * | 61.6 Data table for Chart 2 Note * | 26.5 Data table for Chart 2 Note * |
| Apartment or flat (reference category) | 65.2 | 68.2 | 48.9 | 23.1 |
| Time lived in dwelling | ||||
| Less than 5 years | 62.0 Data table for Chart 2 Note * | 73.3 Data table for Chart 2 Note * | 46.8 Data table for Chart 2 Note * | 22.4 Data table for Chart 2 Note * |
| 10 years or more (reference category) | 79.4 | 81.5 | 63.9 | 28.3 |
| Province | ||||
| Quebec | 77.3 Data table for Chart 2 Note * | 81.9 Data table for Chart 2 Note * | 58.2 Data table for Chart 2 Note * | 35.8 Data table for Chart 2 Note * |
| British Columbia | 72.4 Data table for Chart 2 Note * | 83.8 Data table for Chart 2 Note * | 70.7 Data table for Chart 2 Note * | 26.1 Data table for Chart 2 Note * |
| Ontario (reference category) | 69.8 | 72.9 | 48.7 | 21.0 |
| Census metropolitan areas (CMAs) | ||||
| Large CMAs (reference category) | 65.7 | 75.1 | 52.1 | 27.8 |
| Medium CMAs | 69.8 Data table for Chart 2 Note * | 80.3 Data table for Chart 2 Note * | 59.1 Data table for Chart 2 Note * | 23.6 |
| Small CMAs | 74.9 Data table for Chart 2 Note * | 77.8 Data table for Chart 2 Note * | 55.9 Data table for Chart 2 Note * | 21.4 |
| Small urban areas | 77.3 Data table for Chart 2 Note * | 81.6 Data table for Chart 2 Note * | 61.1 Data table for Chart 2 Note * | 27.2 |
| Non-urban areas | 80.0 Data table for Chart 2 Note * | 81.0 Data table for Chart 2 Note * | 63.1 Data table for Chart 2 Note * | 27.3 |
Sociodemographic characteristics
Households with adultsNote 1 only and adults with children were less likely to dispose of hazardous waste in a controlled way (61% to 67% for pharmaceutical and medical waste, 75% to 78% for pesticides and chemical waste, 49% to 54% for e-waste, and 24% to 25% for textiles and fabric waste) compared with senior-only households (84%, 82%, 67% and 29%, respectively). These patterns remained after adjusting for all other characteristics.
Households whose highest level of educational attainment was a college, CEGEP or other non-university certificate or diploma were more likely to dispose of e-waste in a controlled manner (61%), compared with those with a bachelor’s degree (52%) and were about 8 percentage points more likely to use this method when accounting for all other factors. When accounting for other factors, those with a college, CEGEP or other non-university certificate or diploma were consistently more likely than those with a bachelor’s degree to dispose of hazardous waste in a controlled way.
Dwelling characteristics
Households in single-detached dwellings were more likely to dispose of hazardous waste in a controlled manner across all waste types (27% to 81%) compared with those in apartments and flats (23% to 68%). These differences remained after accounting for other covariates (except for textiles and fabric waste), with households in single-detached dwellings being 6 to 9 percentage points more likely to use controlled disposal methods compared with those in apartments and flats. Households that had lived in their current dwelling for less than 10 years (including those that had lived there for less than 5 years and for 5 to 9 years) were less likely to report controlled disposal across all hazardous waste types (62% for pharmaceutical and medical waste, 73% for pesticides and chemical waste, 47% for e-waste, and 22% for textiles and fabric waste) compared with those that had lived in their dwelling for 10 years or more (79%, 82%, 64% and 28%, respectively). However, after accounting for other factors, differences remained only for those that had lived in their dwelling for less than five years.
Households’ interaction with nature
Households that did not have access to a nearby park or public greenspace and those that had access but did not visit such spaces were less likely to report controlled disposal of pesticides and chemical waste (71% to 76%) compared with those that had visited a nearby park or public greenspace (80%, not shown in the chart). Adjusted models indicated a similar pattern of difference for pesticide and chemical controlled waste disposal.
Geographical variation
Across the most populated provinces, households in British Columbia and Quebec were more likely to use controlled disposal methods (82% to 84% for pesticides and chemical waste, 58% to 71% for e-waste, and 26% to 36% for textiles and fabric waste) compared with Ontario (73%, 49% and 21%, respectively). Households outside large CMAs were more likely to use controlled disposal methods for pharmaceuticals and medical waste (70% to 80%), pesticides and chemical waste (80% to 82%, except for small CMAs), and e-waste (56% to 63%), compared with households in large CMAs (66%, 75% and 52%, respectively).
Conclusion
By jointly examining sociodemographic, dwelling, interaction with nature, and geographic characteristics, this study demonstrates that different household and contextual factors shape different environmental practices and behaviours. Composting kitchen waste was most strongly associated with the residential context, with variations by dwelling type, length of residence, geographic setting and interaction with nature. Variation in controlled hazardous waste disposal was shown for selected groups, notably households with adults only and adults with children, those in single-detached dwellings, and those that had lived in their dwelling for less than five years.
Acknowledgments
This study was funded by the Analytical Project Initiative at Statistics Canada. The authors would like to thank the reviewers Tanya Christidis and Rubab Arim at Statistics Canada and Elizabeth Baxter, Rana Salem and Susan Fraser at Environment and Climate Change Canada for their comments on an earlier version of this paper.
Authors
Allison Leanage is with the Health Analysis and Modelling Division, Samuel MacIsaac and Max Stick are with the Economic and Social Analysis and Modelling Division, and Gordon Dewis is with the Environment Accounts and Statistics Division, at Statistics Canada.
Appendices
Appendices available upon request.
References
Canuel, M., Abdous, B., Bélanger, D., & Gosselin, P. (2014). Development of composite indices to measure the adoption of pro-environmental behaviours across Canadian provinces. PLOS One, 9(7), e101569. https://doi.org/10.1371/journal.pone.0101569
Government of Canada. (2023). Canada and the Sustainable Development Goals. https://www.canada.ca/en/employment-social-development/programs/agenda-2030.html
Huddart-Kennedy, E., Beckley, T. M., McFarlane, B. L., & Nadeau, S. (2009). Rural-urban differences in environmental concern in Canada. Rural Sociology, 74(3), 309–329. https://doi.org/10.1526/003601109789037268
Mustapha, I. (2013). Composting by households in Canada (Catalogue No. 16-002-X). EnviroStats. /n1/pub/16-002-x/2013001/article/11848-eng.htm
United Nations. (n.d.). The 17 goals. https://sdgs.un.org/goals
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