Spatial changes in grey partridge (Perdix perdix) distribution in relation to 25 years of changing agriculture in Sussex, U.K
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Published source details
Aebischer N.J. & Potts G.R. (1998) Spatial changes in grey partridge (Perdix perdix) distribution in relation to 25 years of changing agriculture in Sussex, U.K. Gibier Faune Sauvage, Game Wildlife, 15, 293-308.
Published source details Aebischer N.J. & Potts G.R. (1998) Spatial changes in grey partridge (Perdix perdix) distribution in relation to 25 years of changing agriculture in Sussex, U.K. Gibier Faune Sauvage, Game Wildlife, 15, 293-308.
Actions
This study is summarised as evidence for the following.
Action | Category | |
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Revert arable land to permanent grassland Action Link |
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Reduce pesticide or herbicide use generally Action Link |
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Convert or revert arable land to permanent grassland Action Link |
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Reduce fertilizer, pesticide or herbicide use generally Action Link |
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Revert arable land to permanent grassland
A controlled before-and-after study in 1970-94 in a 28 km2 area of arable farmland in Sussex, England (Aebischer & Potts 1998), found that grey partridge Perdix perdix numbers declined rapidly on arable fields in 1987-94, following their reversion to grassland, beginning in 1987 (average of 6.5 coveys/km2 in 1970-86 vs. 1.1 coveys/km2 in 1987-94). There was a considerably smaller decline on arable fields that were not reverted to grassland (average of 4.9 coveys/km2 in 1970-86 vs. 2.5 coveys/km2 in 1987-94). The reversed fields went from being more favoured by partridges before reversion to less favoured afterwards, equating to a 23% per year decrease in relative habitat quality on the reversion fields.
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Reduce pesticide or herbicide use generally
A controlled before-and-after study in 1989-94 in a 28 km2 area of arable farmland in Sussex, England (Aebischer & Potts 1998), found significantly higher survival rates of grey partridge Perdix perdix chicks on 21 km2 with irregular insecticide applications, compared to a 7 km2 farm with insecticide applications four times a year (average of 34% survival on low application farms vs. 22% on high application farm). Before the start of intensive insecticide application (1970-88), there was no difference between areas (27% survival on low application farms vs. 30% on intensive application farm).
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Convert or revert arable land to permanent grassland
A controlled before-and-after study from 1970 to 1994 in Sussex, England (Aebischer & Potts 1998), found that grey partridge Perdix perdix numbers declined rapidly on arable fields following their reversion to grassland, which began in 1987 (average 6.5 coveys (flocks)/km2 in 1970-1986 vs 1.1 coveys/km2 in 1987-1994). There was a considerably smaller decline on arable fields that were not reverted to grassland (average 4.9 coveys/km2 in 1970-86 vs 2.5 coveys/km2 in 1987-1994). Fields that were reverted had been favoured by partridges prior to reversion, in comparison to arable fields, but were less favoured after reversion, equating to a 23% per year decrease in relative habitat quality. Fields in a 28 km2 area were surveyed for grey partridges in late August/early September after the autumn harvest by driving across fields at dawn and dusk and mapping the position of each observation.
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Reduce fertilizer, pesticide or herbicide use generally
A site comparison before-and-after study from 1989 to 1994 in Sussex, England (Aebischer & Potts 1998) found that survival rates of grey partridge Perdix perdix chicks were significantly higher on 21 km2 of arable farmland that received irregular insecticide applications, compared to a 7 km2 farm with insecticide applications four times a year (average 34% survival on low application farms vs 22% on high application farm). Before the start of intensive insecticide application (1970-1988), survival on the farm had been similar to, or higher than, that on the surrounding farms (27% survival on low application farms vs 30% on intensive application farm). Chick survival rates (up to the age of approximately six weeks) were calculated each year and compared between areas with intensive and irregular insecticide applications. A long-term data set (1970-1988) collected prior to this study was used to investigate chick survival prior to insecticide application on the intensive application farm.
Output references
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