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Floating Aquatic Vegetation Impact on Farm Phosphorus Load:
FINAL REPORT DRAFT
Samira Daroub Timothy Lang
Jennifer Cooper Anne Sexton
Everglades Research and Education Center
BMP Training April 26, 2018
Table of Contents
• Chapter 1: Introduction
• Chapter 2: Discharge water summary of control and treatment farm phosphorus
and environmental parameters
• Chapter 3: Ambient water summary of control and treatment farm phosphorus
and environmental parameters
• Chapter 4: Paired-farm comparison of pre- and post-FAV controlled phosphorus
loads and other factors influencing phosphorus loads
• Chapter 5: Comparison of sediment phosphorus between control and treatment
farms during the treatment period
• Chapter 6: Seasonal impacts from suppressing floating aquatic vegetation on
canal water properties
Chapter 1: Introduction
• Everglades Agricultural
Area background
• Review of literature and
research justification
– Phosphorus Co-
precipitation with Calcium
Carbonate
– Phosphorus Storage in
Sediments
Objectives
1) Evaluate FAV management practices in the EAA farm canals for impact on
a) farm drainage water phosphorus (P) load
b) P speciation of farm drainage water
c) canal sediment properties
2) Use research results to develop a BMP for managing FAV in farm canals that further lowers farm P loads.
3) The goal is to provide growers an additional tool in their efforts to reduce off-farm P loading in the Everglades Agricultural Area.
Chapter 1: Introduction
• Methods
• Analyses
– 2-yr calibration and 4-yr treatment periods:
• Farm pairs 2501/0401, 1813/6117, and 3102/3103
– 3-yr calibration and 3-yr treatment periods:
• Farm pair 4701/4702
– Treatment accomplished through vigilant monitoring and spot spraying FAV
• Statistics and report structure
– Paired watershed design with repeated measures
– Boxplots, Correlations, Multiple Linear Regressions
– Compare calibration to treatment period and determine difference causes
Chapter 1: Introduction
Major Hypothesis
-Suppression of FAV will reduce off-farm P loads
-Suppression of FAV will increase production of denser Ca-
P precipitates
Chapter 1: Introduction
Table 6 - 1. Experimental farms identifying numbers, treatment-control designation, and size.
FarmID
(T/C)
0401
(T)
2501
(C)
6117
(T)
1813
(C)
3103
(T)
3102
(C)
4702
(T)
4701
(C)
Farm Pair 1 2 3 4
Size (acres) 908 824 781 594 609 1387 640 630
Dominant
Crop Sugarcane Sugarcane Sugarcane Sugarcane Sugarcane Sugarcane Sugarcane Sugarcane
Number of
Pumps 2 2 1 1 1 3 1 1
SFWMD
Receiving
Canal
West Palm
Beach Canal
West Palm
Beach Canal
West Palm
Beach Canal
West Palm
Beach Canal Ocean Canal Ocean Canal
Hillsboro
Canal
Hillsboro
Canal
T = treatment; C = control; SFWMD = South Florida Water Management District
Chapter 1: Introduction
S-5A Sub-basin
Farm 0401: 908 acres- cane w/corn
Farm 2501: 824 acres- cane w/corn → sod
Farm 1813: 594 acres- cane w/corn
Farm 6117: 784 acres- cane w/corn
S-6 Sub-basin
Farm 3102: 1387 acres- cane w/veg/corn/rice
Farm 3103: 609 acres- cane w/veg/corn/rice
Farm 4701: 630 acres- cane w/rice
Farm 4702: 640 acres- cane w/rice
Chapter 4: Paired-farm comparison of pre- and post-FAV
controlled phosphorus loads and other factors influencing
phosphorus loads
Chapter 4 objectives:
objectives:
– Identify which independent variables affect UAL, UAD, and
FWTP and the strength of the effect
– Forecast the degree of change a single independent
variable will have on UAL, UAD and FWTP
– Determine if multiple linear regression equations may be
used to predict future UAL, UAD and FWTP if independent
variables are known
Farm Paired Design: Methods
Chapter 4: Paired-Farm Comparison: Farm Pair 4 FAV
Chapter 4: Paired-Farm Comparison: Farm Pair 4
-0.10
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UALDiff
Calibration Period Treatment Period
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UADDiff
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FW
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-FW
TP
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4701 Minus 4702 FWTP Differences vs Time
FWTPDiff
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FA
V4
70
1-F
AV
47
02
(%
)
4701 Minus 4702 FAV Differences vs Time
FAVDiff
Chapter 4: Paired-Farm Comparison: Farm Pair 4
Chapter 4: Paired-Farm Comparison
Summary:
– Drainage is often the dominant variable for UAL rather than
FWTP – drainage volume is very important
– Reduction of UAL in two of the treatment farms were driven by
lower discharge volumes in the treatment period, there was no
change in the third pair, and the last farm pair (4701-4702) was
driven by reduction of FWTP
Final Conclusions
General Conclusions – Experimental Design
Conclusions: 1. Flaws in the experimental design, namely the lack of FAV cover control in
control farms and restrictions on seeding FAV in treatment farms, resulted in farm canal designations being unrepresentative of FAV effects on water properties.
2. In the future, the experimental design needs to be restructured so that control farms have no FAV cover and treatment farms are seeded to full coverage to analyze overall impacts of FAV suppression.
Conclusions – Objective 1
Objective 1: Evaluate two floating aquatic vegetation (FAV)
management practices in the Everglades Agricultural Area (EAA)
farm canals for impact on farm drainage water P load, along with
other factors that affect P loads
– Suppression of FAV below a threshold of 25% was not found to
be beneficial for reduction of farm drainage water P loads
because the FAV threshold was set too high
– Drainage is often the dominant variable for UAL rather than
FWTP – drainage volume is very important
Conclusions – Objective 2
Objective 2: Evaluate the effect of two FAV management practices
on P speciation of farm drainage water and on farm canal
sediment physical and chemical properties
– Suppression of FAV in treatment farms below a threshold of 25%
was found to lower sediment total P concentrations and increase
sediment bulk density
– Treatment farms experienced less deposition of lightweight
detrital material from aquatic plants that are easily transportable
during pumping events
– Increased sediment density may be due to the formation of
dense P containing Ca-P precipitates at higher pH levels found
in FAV-free canal water
Conclusions – Objective 3
Objective 3: Use the information from the research for the
development of a best management practice (BMP) for managing
FAV to produce denser
– Final conclusions are that suppression of FAV can be an effective tool
for reducing discharge total P at the farm scale
– Additional statistical analyses (BACI, PCA, storm impacts, seasonal
impacts) should be conducted to better understand the various factors
that affect P load discharge with and without FAV coverages
Potential New BMP Research
• Create updated BMP manual for growers
• Need to do more statistical analyses: – Storm impacts, Seasonal impacts
– BACI (before and after comparisons)
– PCA (principal component analysis) with all parameters
• Impact of sediment removal – Clean sediments from all farms
– Monitor discharge sediments after cleaning and long term
• Continue with drainage and ambient water sampling
• Other ideas from our Advisory Committee
Questions/Comments/Suggestions?