Open Access
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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