Lifecycle stage
Uncollected waste — pathways to environment
Modelled direct discard to water, direct discard to land and open burning.
Trend
Uncollected waste entering the environment
Breakdown
Household environmental pathways
Raw data
Public observations only. Provisional estimates are labelled; internal records and empty placeholders are excluded.
| Block | Year | Category | Value | Units | Evidence | Source |
|---|---|---|---|---|---|---|
| Uncollected waste entering the environment | 2015 | Direct Discard to Land | 590.95 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2015 | Direct Discard to Water | 331.19 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2015 | Open Burning | 1,785.64 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2015 | Total | 2,707.78 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2016 | Direct Discard to Land | 604.7 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2016 | Direct Discard to Water | 338.89 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2016 | Open Burning | 1,827.21 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2016 | Total | 2,770.81 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2017 | Direct Discard to Land | 618.18 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2017 | Direct Discard to Water | 346.45 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2017 | Open Burning | 1,867.93 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2017 | Total | 2,832.55 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2018 | Direct Discard to Land | 631.14 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2018 | Direct Discard to Water | 353.71 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2018 | Open Burning | 1,907.11 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2018 | Total | 2,891.97 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2019 | Direct Discard to Land | 643.89 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2019 | Direct Discard to Water | 360.86 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2019 | Open Burning | 1,945.62 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2019 | Total | 2,950.36 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2020 | Direct Discard to Land | 673.55 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2020 | Direct Discard to Water | 377.48 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2020 | Open Burning | 2,035.23 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2020 | Total | 3,086.25 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2021 | Direct Discard to Land | 690.18 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2021 | Direct Discard to Water | 386.8 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2021 | Open Burning | 2,085.48 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2021 | Total | 3,162.45 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2022 | Direct Discard to Land | 707.95 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2022 | Direct Discard to Water | 396.76 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2022 | Open Burning | 2,139.2 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2022 | Total | 3,243.91 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2023 | Direct Discard to Land | 727.77 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2023 | Direct Discard to Water | 407.86 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2023 | Open Burning | 2,199.07 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2023 | Total | 3,334.71 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2024 | Direct Discard to Land | 748.05 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2024 | Direct Discard to Water | 419.23 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2024 | Open Burning | 2,260.36 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Uncollected waste entering the environment | 2024 | Total | 3,427.64 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2015 | Direct Discard to Land | 421.39 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2015 | Direct Discard to Water | 13.26 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2015 | Open Burning | 1,616.08 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2015 | Total | 2,050.73 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2016 | Direct Discard to Land | 431.19 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2016 | Direct Discard to Water | 13.57 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2016 | Open Burning | 1,653.7 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2016 | Total | 2,098.46 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2017 | Direct Discard to Land | 440.8 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2017 | Direct Discard to Water | 13.87 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2017 | Open Burning | 1,690.55 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2017 | Total | 2,145.22 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2018 | Direct Discard to Land | 450.05 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2018 | Direct Discard to Water | 14.16 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2018 | Open Burning | 1,726.01 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2018 | Total | 2,190.22 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2019 | Direct Discard to Land | 459.14 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2019 | Direct Discard to Water | 14.44 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2019 | Open Burning | 1,760.86 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2019 | Total | 2,234.45 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2020 | Direct Discard to Land | 480.28 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2020 | Direct Discard to Water | 15.11 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2020 | Open Burning | 1,841.97 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2020 | Total | 2,337.36 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2021 | Direct Discard to Land | 492.14 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2021 | Direct Discard to Water | 15.48 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2021 | Open Burning | 1,887.45 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2021 | Total | 2,395.07 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2022 | Direct Discard to Land | 504.82 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2022 | Direct Discard to Water | 15.88 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2022 | Open Burning | 1,936.07 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2022 | Total | 2,456.77 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2023 | Direct Discard to Land | 518.95 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2023 | Direct Discard to Water | 16.33 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2023 | Open Burning | 1,990.25 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2023 | Total | 2,525.53 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2024 | Direct Discard to Land | 533.41 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2024 | Direct Discard to Water | 16.78 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2024 | Open Burning | 2,045.72 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
| Household environmental pathways | 2024 | Total | 2,595.91 | tonnes | modelled | Inventory mass-balance calculation MECC / UNSW Centre for Sustainable Development Reform Provenance notesDerived from upstream inventory flows and documented assumptions. |
Method and limitations
Uncollected waste — pathways to environment
This page estimates plastic directly discarded to water, discarded on land or openly burned.
How it is produced
Household pathway rates come from the 2017 FBOS Census; other sector rates come from APWC/IUCN. Rates are multiplied by modelled plastic waste generated and checked against total uncollected waste.
Read with care
Multiple Census answers are treated as if each described all household waste, so overlap is possible. The figures are modelled and should not be added together with accidental leakage estimates as though they were independent measurements.
