Rock lobsters can be exposed to poor water quality during all stages of handling and holding prior to going to market. Poor water quality reduces the time a lobster can be held alive and how many animals can be held in a system and thus may reduce profit. The quality of water can be assessed using many different measurements, with two of the most important being oxygen and ammonia (a form of nitrogen). An earlier FRDC funded study investigated oxygen and how it influenced the holding of rock lobsters. However, prior to the current study there was very limited understanding of the harmful effects of ammonia to rock lobsters. Ammonia can accumulate in holding and transport facilities via natural release of ammonia from lobsters, and from the bacterial decomposition of faeces, excess feed, and dead animals. Ammonia can be harmful to crustaceans in small amounts (or low concentrations) and even fatal if concentrations get too high. The toxicity of ammonia to aquatic animals becomes greater when other factors such as low dissolved oxygen, low salinity, and/or low pH (acidity of the water) also interact. In liquids, total ammonia comprises un-ionised ammonia (NH3), which is the more toxic component, and ionised ammonia (NH4 +; ammonium) in equilibrium. Lobsters can become stressed (having a higher demand upon their biological systems) during holding and handling but it is uncertain what effect this stress has on the ability of lobsters to tolerate ammonia. This project provided a better understanding of the effect of ammonia and other water quality measurements, on the health of stressed and unstressed lobsters.

Rock lobsters can be exposed to poor water quality during all stages of handling and holding prior to going to market. Poor water quality reduces the time a lobster can be held alive and how many animals can be held in a system and thus may reduce profit. The quality of water can be assessed using many different measurements, with two of the most important being oxygen and ammonia (a form of nitrogen). An earlier FRDC funded study investigated oxygen and how it influenced the holding of rock lobsters. However, prior to the current study there was very limited understanding of the harmful effects of ammonia to rock lobsters. Ammonia can accumulate in holding and transport facilities via natural release of ammonia from lobsters, and from the bacterial decomposition of faeces, excess feed, and dead animals. Ammonia can be harmful to crustaceans in small amounts (or low concentrations) and even fatal if concentrations get too high. The toxicity of ammonia to aquatic animals becomes greater when other factors such as low dissolved oxygen, low salinity, and/or low pH (acidity of the water) also interact. In liquids, total ammonia comprises un-ionised ammonia (NH3), which is the more toxic component, and ionised ammonia (NH4 +; ammonium) in equilibrium. Lobsters can become stressed (having a higher demand upon their biological systems) during holding and handling but it is uncertain what effect this stress has on the ability of lobsters to tolerate ammonia. This project provided a better understanding of the effect of ammonia and other water quality measurements, on the health of stressed and unstressed lobsters.

Rock lobsters can be exposed to poor water quality during all stages of handling and holding prior to going to market. Poor water quality reduces the time a lobster can be held alive and how many animals can be held in a system and thus may reduce profit. The quality of water can be assessed using many different measurements, with two of the most important being oxygen and ammonia (a form of nitrogen). An earlier FRDC funded study investigated oxygen and how it influenced the holding of rock lobsters. However, prior to the current study there was very limited understanding of the harmful effects of ammonia to rock lobsters. Ammonia can accumulate in holding and transport facilities via natural release of ammonia from lobsters, and from the bacterial decomposition of faeces, excess feed, and dead animals. Ammonia can be harmful to crustaceans in small amounts (or low concentrations) and even fatal if concentrations get too high. The toxicity of ammonia to aquatic animals becomes greater when other factors such as low dissolved oxygen, low salinity, and/or low pH (acidity of the water) also interact. In liquids, total ammonia comprises un-ionised ammonia (NH3), which is the more toxic component, and ionised ammonia (NH4 +; ammonium) in equilibrium. Lobsters can become stressed (having a higher demand upon their biological systems) during holding and handling but it is uncertain what effect this stress has on the ability of lobsters to tolerate ammonia. This project provided a better understanding of the effect of ammonia and other water quality measurements, on the health of stressed and unstressed lobsters.

Rock lobsters can be exposed to poor water quality during all stages of handling and holding prior to going to market. Poor water quality reduces the time a lobster can be held alive and how many animals can be held in a system and thus may reduce profit. The quality of water can be assessed using many different measurements, with two of the most important being oxygen and ammonia (a form of nitrogen). An earlier FRDC funded study investigated oxygen and how it influenced the holding of rock lobsters. However, prior to the current study there was very limited understanding of the harmful effects of ammonia to rock lobsters. Ammonia can accumulate in holding and transport facilities via natural release of ammonia from lobsters, and from the bacterial decomposition of faeces, excess feed, and dead animals. Ammonia can be harmful to crustaceans in small amounts (or low concentrations) and even fatal if concentrations get too high. The toxicity of ammonia to aquatic animals becomes greater when other factors such as low dissolved oxygen, low salinity, and/or low pH (acidity of the water) also interact. In liquids, total ammonia comprises un-ionised ammonia (NH3), which is the more toxic component, and ionised ammonia (NH4 +; ammonium) in equilibrium. Lobsters can become stressed (having a higher demand upon their biological systems) during holding and handling but it is uncertain what effect this stress has on the ability of lobsters to tolerate ammonia. This project provided a better understanding of the effect of ammonia and other water quality measurements, on the health of stressed and unstressed lobsters.

Rock lobsters can be exposed to poor water quality during all stages of handling and holding prior to going to market. Poor water quality reduces the time a lobster can be held alive and how many animals can be held in a system and thus may reduce profit. The quality of water can be assessed using many different measurements, with two of the most important being oxygen and ammonia (a form of nitrogen). An earlier FRDC funded study investigated oxygen and how it influenced the holding of rock lobsters. However, prior to the current study there was very limited understanding of the harmful effects of ammonia to rock lobsters. Ammonia can accumulate in holding and transport facilities via natural release of ammonia from lobsters, and from the bacterial decomposition of faeces, excess feed, and dead animals. Ammonia can be harmful to crustaceans in small amounts (or low concentrations) and even fatal if concentrations get too high. The toxicity of ammonia to aquatic animals becomes greater when other factors such as low dissolved oxygen, low salinity, and/or low pH (acidity of the water) also interact. In liquids, total ammonia comprises un-ionised ammonia (NH3), which is the more toxic component, and ionised ammonia (NH4 +; ammonium) in equilibrium. Lobsters can become stressed (having a higher demand upon their biological systems) during holding and handling but it is uncertain what effect this stress has on the ability of lobsters to tolerate ammonia. This project provided a better understanding of the effect of ammonia and other water quality measurements, on the health of stressed and unstressed lobsters.

Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest.  Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes.  Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective.  The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data. 

The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance.  However, the relationship between catch and effort data and abundance is not always constant or linear.  Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass.  Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass.  Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort.  Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.

Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour.  If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds.  Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.

This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.

Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.

Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest.  Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes.  Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective.  The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data. 

The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance.  However, the relationship between catch and effort data and abundance is not always constant or linear.  Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass.  Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass.  Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort.  Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.

Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour.  If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds.  Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.

This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.

Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.

Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest.  Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes.  Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective.  The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data. 

The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance.  However, the relationship between catch and effort data and abundance is not always constant or linear.  Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass.  Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass.  Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort.  Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.

Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour.  If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds.  Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.

This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.

Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.

Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest.  Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes.  Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective.  The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data. 

The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance.  However, the relationship between catch and effort data and abundance is not always constant or linear.  Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass.  Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass.  Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort.  Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.

Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour.  If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds.  Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.

This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.

Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.

Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest.  Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes.  Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective.  The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data. 

The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance.  However, the relationship between catch and effort data and abundance is not always constant or linear.  Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass.  Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass.  Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort.  Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.

Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour.  If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds.  Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.

This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.

Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.