Changes
On May 16, 2022 at 12:36:22 PM +1000,
Link Digital:
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Removed the source URL from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Changed value of field
temporal_coverage_from
to2016-10-01
in Assessment of White Gum Moist Forest on NSW Crown Forest Estate -
Added resource Indicative Map for White Gum Moist Forest Threatened Ecological Community on NSW Crown Forest Estate to Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Added resource Native Forestry Map Viewer to Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Added resource Operational and Indicative Maps for the Assessment of Threatened Ecological Communities on NSW Crown Forest Estate to Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Added resource Data Quality Statement to Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Added resource Assessment of White Gum Moist Forest on NSW Crown Forest Estate to Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Deleted resource Assessment of White Gum Moist Forest on NSW Crown Forest Estate from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Deleted resource Indicative Map for White Gum Moist Forest Threatened Ecological Community on NSW Crown Forest Estate from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Deleted resource Operational and Indicative Maps for the Assessment of Threatened Ecological Communities on NSW Crown Forest Estate from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Deleted resource Data Quality Statement from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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Deleted resource Native Forestry Map Viewer from Assessment of White Gum Moist Forest on NSW Crown Forest Estate
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| 6 | "key": "harvest_portal", | 6 | "key": "harvest_portal", | ||
| 7 | "value": "SEED" | 7 | "value": "SEED" | ||
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| 12 | sets.seed.nsw.gov.au/dataset/assessment-of-white-gum-moist-forest-tec" | 12 | sets.seed.nsw.gov.au/dataset/assessment-of-white-gum-moist-forest-tec" | ||
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| 19 | "license_title": "Creative Commons Attribution", | 19 | "license_title": "Creative Commons Attribution", | ||
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| 24 | "metadata_created": "2018-06-15T08:52:58.489288", | 24 | "metadata_created": "2018-06-15T08:52:58.489288", | ||
| n | 25 | "metadata_modified": "2021-09-06T23:32:20.729163", | n | 25 | "metadata_modified": "2022-05-16T02:36:22.675445", |
| 26 | "name": "assessment-of-white-gum-moist-forest-tec", | 26 | "name": "assessment-of-white-gum-moist-forest-tec", | ||
| 27 | "notes": "An indicative map for White Gum Moist Forest (WGMF) was | 27 | "notes": "An indicative map for White Gum Moist Forest (WGMF) was | ||
| 28 | constructed to resolve long-standing issues surrounding its | 28 | constructed to resolve long-standing issues surrounding its | ||
| 29 | identification, location and extent within the NSW State Forest estate | 29 | identification, location and extent within the NSW State Forest estate | ||
| 30 | covered by the eastern Regional Forest Agreements. \r\nThe | 30 | covered by the eastern Regional Forest Agreements. \r\nThe | ||
| 31 | determination of WGMF was reviewed by the project\u2019s Threatened | 31 | determination of WGMF was reviewed by the project\u2019s Threatened | ||
| 32 | Ecological Community (TEC) Reference Panel (the Panel), and a set of | 32 | Ecological Community (TEC) Reference Panel (the Panel), and a set of | ||
| 33 | diagnostic parameters for identifying the WGMF TEC was agreed. \r\nOur | 33 | diagnostic parameters for identifying the WGMF TEC was agreed. \r\nOur | ||
| 34 | mapping process relied upon the occurrence of E.dunnii to diagnose the | 34 | mapping process relied upon the occurrence of E.dunnii to diagnose the | ||
| 35 | presence of WGMF. \r\n\r\nWe reviewed existing vegetation maps, | 35 | presence of WGMF. \r\n\r\nWe reviewed existing vegetation maps, | ||
| 36 | predictive models and observation records of E.dunnii to identify | 36 | predictive models and observation records of E.dunnii to identify | ||
| 37 | State Forests that are known or likely to include stands of the | 37 | State Forests that are known or likely to include stands of the | ||
| 38 | species. We then attempted several different approaches to sampling | 38 | species. We then attempted several different approaches to sampling | ||
| 39 | and mapping E.dunnii using ground based surveys, predictive modelling | 39 | and mapping E.dunnii using ground based surveys, predictive modelling | ||
| 40 | and aerial photograph interpretation (API). We used API assessment of | 40 | and aerial photograph interpretation (API). We used API assessment of | ||
| 41 | known E.dunnii stands to identify image patterns and signatures that | 41 | known E.dunnii stands to identify image patterns and signatures that | ||
| 42 | indicated the presence of E.dunnii. We used our findings to examine | 42 | indicated the presence of E.dunnii. We used our findings to examine | ||
| 43 | un-surveyed areas of relevant state forests via API, and then we | 43 | un-surveyed areas of relevant state forests via API, and then we | ||
| 44 | mapped any areas which appeared to be dominated or co-dominated by | 44 | mapped any areas which appeared to be dominated or co-dominated by | ||
| 45 | E.dunnii. We also developed a Random Forest presence-absence model and | 45 | E.dunnii. We also developed a Random Forest presence-absence model and | ||
| 46 | used it to predict the distribution of WGMF across its range.\r\nWe | 46 | used it to predict the distribution of WGMF across its range.\r\nWe | ||
| 47 | constructed an indicative map of WGMF using the combined results of | 47 | constructed an indicative map of WGMF using the combined results of | ||
| 48 | our API mapping and our predictive model. In total, we mapped | 48 | our API mapping and our predictive model. In total, we mapped | ||
| 49 | approximately 980 hectares of forest likely to be dominated or | 49 | approximately 980 hectares of forest likely to be dominated or | ||
| 50 | co-dominated by E.dunnii across 16 State Forests. Two thirds of the | 50 | co-dominated by E.dunnii across 16 State Forests. Two thirds of the | ||
| 51 | mapped area is associated with the northern populations of E.dunnii | 51 | mapped area is associated with the northern populations of E.dunnii | ||
| 52 | \u2013 the largest areas were in Beaury, Donaldson and Yabbra State | 52 | \u2013 the largest areas were in Beaury, Donaldson and Yabbra State | ||
| 53 | Forests. In the southern area, Kangaroo River State Forest includes | 53 | Forests. In the southern area, Kangaroo River State Forest includes | ||
| 54 | the largest representation of E.dunnii in State Forest. \r\nOur | 54 | the largest representation of E.dunnii in State Forest. \r\nOur | ||
| 55 | conclusions from this exercise is that our API interpretation is | 55 | conclusions from this exercise is that our API interpretation is | ||
| 56 | capable of separating E.dunnii from other related eucalypts but only | 56 | capable of separating E.dunnii from other related eucalypts but only | ||
| 57 | where it is supported by field reconnaissance. Therefore, further work | 57 | where it is supported by field reconnaissance. Therefore, further work | ||
| 58 | is required to increase API confidence throughout its range before our | 58 | is required to increase API confidence throughout its range before our | ||
| 59 | maps are suitable for operational applications. Nonetheless, our | 59 | maps are suitable for operational applications. Nonetheless, our | ||
| 60 | indicative map is still useful for providing a list of State Forests | 60 | indicative map is still useful for providing a list of State Forests | ||
| 61 | that include mapped areas of E.dunnii and identifying the areas that | 61 | that include mapped areas of E.dunnii and identifying the areas that | ||
| 62 | have corroborating field based evidence of E.dunnii.\r\nAs our | 62 | have corroborating field based evidence of E.dunnii.\r\nAs our | ||
| 63 | indicative map stands at present, we consider that it overestimates | 63 | indicative map stands at present, we consider that it overestimates | ||
| 64 | the extent of E.dunnii and its dominance, however, it is unlikely that | 64 | the extent of E.dunnii and its dominance, however, it is unlikely that | ||
| 65 | extensive stands exist outside our mapped areas. We also conclude that | 65 | extensive stands exist outside our mapped areas. We also conclude that | ||
| 66 | existing mapping (including both forest type mapping and OEH (2012) | 66 | existing mapping (including both forest type mapping and OEH (2012) | ||
| 67 | mapping) significantly underestimates the likely true | 67 | mapping) significantly underestimates the likely true | ||
| 68 | extent).\r\n\r\nIndicative TEC Mapping have been generated from best | 68 | extent).\r\n\r\nIndicative TEC Mapping have been generated from best | ||
| 69 | available composite environmental data layers - standardised to 30 m | 69 | available composite environmental data layers - standardised to 30 m | ||
| 70 | pixels.", | 70 | pixels.", | ||
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| 77 | South Wales. Its purpose is to improve environmental performance and | 77 | South Wales. Its purpose is to improve environmental performance and | ||
| 78 | waste management\r\n\r\nEPA works with the community, business, | 78 | waste management\r\n\r\nEPA works with the community, business, | ||
| 79 | industry and government to maintain a balance between protecting the | 79 | industry and government to maintain a balance between protecting the | ||
| 80 | environment, managing competing demands on the environment and | 80 | environment, managing competing demands on the environment and | ||
| 81 | supporting sustainable growth.\r\n\r\nEPA provides information and | 81 | supporting sustainable growth.\r\n\r\nEPA provides information and | ||
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| 84 | priorities, policies and programs. It publishes scientific research | 84 | priorities, policies and programs. It publishes scientific research | ||
| 85 | and monitors trends in the state of the environment, and offers advice | 85 | and monitors trends in the state of the environment, and offers advice | ||
| 86 | and incentives to help business and industry improve their | 86 | and incentives to help business and industry improve their | ||
| 87 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | 87 | environmental performance.\r\n\r\nSee: http://www.epa.nsw.gov.au\r\n", | ||
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| 225 | "state": "active", | 225 | "state": "active", | ||
| 226 | "tags": [], | 226 | "tags": [], | ||
| n | 227 | "temporal_coverage_from": "01/10/2016", | n | 227 | "temporal_coverage_from": "2016-10-01", |
| 228 | "temporal_coverage_to": "", | ||||
| 229 | "title": "Assessment of White Gum Moist Forest on NSW Crown Forest | 228 | "title": "Assessment of White Gum Moist Forest on NSW Crown Forest | ||
| 230 | Estate", | 229 | Estate", | ||
| 231 | "type": "dataset", | 230 | "type": "dataset", | ||
| 232 | "unpublished": "false", | 231 | "unpublished": "false", | ||
| 233 | "update_freq": "irregular", | 232 | "update_freq": "irregular", | ||
| t | 234 | "url": "", | t | 233 | "url": null, |
| 235 | "version": null | 234 | "version": null | ||
| 236 | } | 235 | } |