Australian Natural Resources Atlas

Monitoring the Rangelands - Photographic Sequences for Broken Hill Complex

Location map of Broken Hill Complex bioregion

The Rangelands Information System Photographic Sequences is a tool which allows the user to view a photographic record of particular areas in the Rangelands. The photographs for Broken Hill Complex has been provided by the Department of Land and Water Conservation, NSW.

The following photographic sequence products are available for the Broken Hill Complex bioregion:

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Location 1

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January 1954

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1955

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1956

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1957

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1977

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1978

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1979

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1984

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

Location 2

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January 1954

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1955

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1956

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1957

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1977

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1978

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1979

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

January 1984

Dominated by Maireana astrotricha with a few M.pyramidata and Atriplex vesicaria. The main pasture species is Enneapogon which can be seen coming and going over the time.

Location 3

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January 1955

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1956

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1975

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1976

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1978

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1979

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1984

The woody shrub encroachment at location 3 is mainly Senna artemisiodes nothosubsp. Coriacea with with a few S.artemisiodes subsp. Petiolaris.

January 1997

Some very heavy rabbit damage in exclosurec -19 some shredding of lower branches

Location 4

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January 1990

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1991

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1992

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1993

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1994

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1996

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1997

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1998

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

January 1999

Images show a saltbush site near Broken Hill. The site is dominated by Mitchell grass (Astrebla sp) and a mix of other perennial grasses such as Panicum and Eragrostis sp. A low density (average of 225 plants per hectare) of perennial chenopods such as cotton bush (Maireana sp) and bladder saltbush (Atriplex sp) are present. Biomass ranges from 250 kg/ha in 1999 at the end of the drought to almost 2500 kg/ha in 1994. The site is considered stable and highly productive.

Location 5

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January 1991

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1992

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1993

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1994

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1996

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1997

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1998

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 1999

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

January 2000

Images show a bluebush site located in a National Park in the Menindee area. Pasture at the site is dominated by bottlewashers (Enneapogon sp) and speargrass (Stipa sp). These butts can be seen persisting throughout the dry years in 1992 and 1996-191999. The shrub layer is dominated by black bluebush (M.pyramidata) with scattered pearl bluebush (M.sedifolia) in an average density of around 1800 plants per hectare. Perennial chenopod density ranges from 3000 in 1991 to a low of 1440 in 1998. Biomass ranged from 1250 kg/ha in 1993 to less than 100 kg/ha in 1999 after a prolonged dry period from 1996. The site is generally stable.

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