The historic Veale Gardens, part of the Adelaide Parklands surrounding the city, has been in a state of severe decline for a decade. A substantial amount of tree mortality has occurred over many years leading to a major loss of canopy cover throughout the park. The north-west corner of the gardens was identified as a key area of tree decline and G.U.F was commissioned to determine the cause and identify a rehabilitation program to save the trees including a number of significant species.
G.U.F conducted a detailed assessment of tree decline and collected a considerable amount of soil sampling and plant and soil function measures on 30 trees in the most affected areas.
Baseline plant and soil measurements and visual assessments were used to determine a Plant Health Care (PHC) program based on scientific validation to address the issues and restore tree and soil health. This data collection included:
Plant Health Care Programs: Tree protection zones (TPZ) were calculated and mulch beds negotiated.
The 350mm + thick root zone material was then inoculated with microscope qualitative assessed microbial concentrate of
The mulch material rapidly decomposed over a two-month intensive liquid PHC application period. The microbial activity went through multiple microbial flushes from bacterial bloom – Slime mold (Fuligo septica) – Saprophytic species (Mushrooms). The material decomposed to about 100 mm and became a mycelium blanket over the root zone.
During a 3-month period following treatment, MultispeQ photosynthesis data was collected to track tree health and compared to visual tree assessments taken at the same time. For each tree, 10-20 MultispeQ measurements were taken from random positions within the tree canopy.
The purpose of this summary is to show preliminary validation of the ability of MultispeQ parameters to distinguish between tree’s of different health conditions and to provide proof-of-concept data supporting the use of the MultispeQ to diagnose tree health. As such, the two primary objectives of this analysis are to determine:
1. Which MultispeQ measurements, if any, correspond to visual tree health assessments?
2. If the MultispeQ can be used to develop a sensor based tree health calculator to diagnose tree health?
The first goal of this analysis was to determine which, if any, MultispeQ parameters have potential to serve as early indicators of tree stress. In order to accomplish this goal, we compared tree’s that were visually assessed to be of poor health to trees that were assessed to have either fair or good health for each sampling date. Multivariate analysis was used to account for light intensity and time of measurement, both of which can affect photosynthesis measurements.
The difference between fair or good trees and poor trees are shown in Figure 1. The quantum yields of photosystem II (Phi2) and other energy losses (PhiNO) were significantly increased in fair/good trees at every sampling date except for November 10 (Phi2) and December 2 (PhiNO) (p < 0.05). Conversely, the quantum yield of nonphotochemical quenching (PhiNPQ) was significantly reduced in fair/good trees at every sampling date. Relative chlorophyll content was not significantly changed between fair/good and poor trees on November 4 and 10, but was significantly reduced in fair/good trees every sampling date starting November 25.
These results suggest that healthier trees (i.e. tree’s visually assessed as fair or good) were actively regulating away less energy from photosynthesis (PhiNPQ) than trees of poor health, increasing the photosynthetic efficiency of these trees (Phi2).
Having successfully validated that MultispeQ measurements relate to visual tree assessments, the long-term goal is to develop a real-time tree health calculator to diagnose tree health status using objective, MultispeQ based data. In the absence of a large dataset of MultispeQ tree health data, this can only be accomplished by comparing unknown test trees to known reference trees that are measured under the same light intensity, temperature, growth stage and tree age conditions as the test trees.
In this study, we identified four trees that failed to respond to the PHC program and were assessed as poor for the duration of the study; we used these trees as a lower tree health baseline. Additionally, we identified five trees that were in good health prior to the establishment of this study and used these trees as an upper baseline for tree health at the study site. We then compared these baseline trees to other trees in the study area. Again, we use multivariate analysis to account for light intensity and time of measurement.
The change in each MultispeQ parameter over time for each category of the tree, upper baseline, lower baseline, and test trees are shown in Figure 2. The relative chlorophyll content of the upper baseline trees was significantly lower than the lower baseline and test trees at all but the first sampling date (Fig. 2A), while the lower baseline and test trees had significantly different SPAD at all but the 1st and last sampling dates (p < 0.05). The separation in Phi2 between the test trees and the upper and lower baseline trees were generally very small (Fig 2B). On the other hand, the test trees tended to have significantly lower PhiNPQ than the lower baseline and significantly higher PhiNPQ than the upper baseline (Fig 2C). The opposite was true for PhiNO, where the lower baseline was below the test trees and the upper baseline was above the test trees (Fig 2D).
SPAD, PhiNPQ and PhiNO all appear to be potentially useful indicators to diagnose tree health status. Furthermore, these preliminary results support our belief that the MultispeQ can be a useful tool in developing real-time, sensor-based tools to diagnose tree health.
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