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Table 2

Summary table identifying consideration when employing each macrophyte monitoring methodology.

  Method       
Consideration Trimble mapping − On site digitizing Hydroacoustic 200 khz sonar Hydroacoustic 800 khz downscan Hydroacoustic 800 kHz side scan Duel-frequency identification sonar (DIDSON) Aireborn remote sensing (satelite imagery) Optical videography
Turbidity Turbidity dependent Turbidity independent Turbidity independent Turbidity independent Turbidity independent Turbidity dependent Turbidity dependent
Identifies species Can identify species Cannot distinguish between species Cannot distinguish between species Cannot distinguish between species Cannot distinguish between species Cannot distinguish between species; grond truthing data required Can identify species
Macrophytes mapped Submerged, emergent, floating Submerged Submerged Submerged Submerged Submerged, emergent, floating Submerged
Provides spatial distribution maps Yes Provides georeferenced transect data Provides georeferenced transect data Yes Provides georeferenced transect data Yes Provides georeferenced transect data
Consistency of data collection between field operators High variation Minimal variation Minimal variation Minimal variation Minimal variation N/A Minimal variation
Consistency of data processing between interpretors N/A Minimal variation Minimal variation High variation Minimal variation Minimal variation Minimal variation
Data collection time Highly dependent upon macrophyte abundance Independent of macrophyte abundance Independent of macrophyte abundance Independent of macrophyte abundance Independent of macrophyte abundance No field data collection required Independent of macrophyte abundance
Post-data collection processing Minimal Moderate Moderate High High Moderate High
Equipment expenses High Moderate Moderate Modeate Very high Nill Low
Identifies depth of macrophyte growth No Yes Yes No No No No
Identifies percentage of water column occupied by macrophytes No Yes Yes No No No No
Other Visibility of macrophytes during on site digitising is highly dependent upon turbidity and surface conditions at the time of sampling Sonar may not penetrate through dense macrophytes resulting in lost
Can be difficult to run boat transects through dense macrophyte due to fouling of boat propellor
False macrophyte detections can result from submerged tree branches and other debris
Sonar may not penetrate through dense macrophytes resulting in lost
Can be difficult to run boat transects through dense macrophyte due to fouling of boat propellor
Identiyfing macrophyte beds from sidescan imagery can be difficult without ground truting data
Sidescan sonar in some instances may not penetrate through dense surface-to-substrate macrophyte beds, therefore only indicating near edge macrophytes boundaries, not full spatial extents
Can be difficult to run boat transects through dense macrophyte due to fouling of boat propellor Temporal availability of cloud free satelite imagery may be restrictive Can be difficult to run boat transects through dense macrophyte due to fouling of boat propellor

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