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Yousef AbdalAal & Ehsan Ghane
Biosystems and Agricultural Engineering Department
Michigan State University
Comparative analysis of newly proposed and
existing design criteria for saturated buffers
11th International Drainage Symposium
IDS 2022
August 30 to September 2, 2022
Des Moines, Iowa
INTRODUCTION
2
Saturated Buffers
 Treat the field drainage that, originally, is released directly to the open ditch
Without
saturated
buffer
With
saturated
buffer
Reported nitrate load removal
8% 84%
A Need for a design criterion ensuring adequate & consistent performance
3
Study Objectives:
1. Propose a new design criterion for saturated buffer that maximizes the total nitrate load removal.
2. Conduct a comparative analysis of all SB design criteria to identify the criterion with most potential
to maximize the nitrate load removal.
4
METHODS
5
Saturated Buffers Design Criteria
8
Illinois NRCS
Spread Sheet
Design 1
Optimum Width
Eq. by McEachran
et al. (2020)
Design 2
Newly proposed design(builds on Designs 1 & 2 )
Design 3
3 meters 30 meters
NR1 NR2 NR3 NRn
W1 W2 W3 ………...
Optimum width is at Maximum nitrate load removal
NRn : Nitrate load removal
 One point in time
 Saturated buffer
parameters:
 Width : Input
 Distribution pipe
length : Output
 No optimization
 One point in time
 Saturated buffer
parameters:
 Width : Output
 Distribution pipe
length : No need
 Maximize
effectiveness of
nitrate load removal
 Time period of any length (Captures flow variations)
 Saturated buffer parameters:
 Width : Output
 Distribution pipe length : Input
Wn
Comparative Analysis of Design Criteria:
•Width: 9.1 m
•Calculated length of
distribution pipe (L)
Design
1
•Calculated optimum
Width
•Design 1 length of
distribution pipe (L)
Design
2
•Calculated optimum
Width
• Design 1 length of
distribution pipe (L)
Design
3
Designed
hypothetical SB
systems
Estimate nitrate load
reduction
Identify the
optimum
design
Largest
nitrate load
removal
Main routine of
comparative analysis
&
Measured daily field
drainage data
- Used measured daily data from two field sites in Michigan
9
Main Routine of Comparative Analysis and Design 3
10
Hydrology Component
Nitrate Load Estimation
Component
and
 Estimates diverted flow & Bypass flow
 Accounts for exit head loss
 Process based - Two mass balances :
First mass balance
Location: Control structure
Mass balance:
𝑄𝐹𝑖𝑒𝑙𝑑 = 𝑄𝑑𝑖𝑣𝑒𝑟𝑡𝑒𝑑 + 𝑄𝐵𝑦𝑝𝑎𝑠𝑠
Main Routine: Hydrology Component (1)
𝑸𝒅𝒊𝒗𝒆𝒓𝒕𝒆𝒅
𝑸𝑩𝒚𝒑𝒂𝒔𝒔
11
𝐹𝑙𝑜𝑤 𝑡ℎ𝑟𝑜𝑢𝑔ℎ 𝑝𝑖𝑝𝑒
perforations
𝐹𝑙𝑜𝑤 𝑡ℎ𝑟𝑜𝑢𝑔ℎ buffer soil
Main Routine: Hydrology Component (2)
Exit head loss (h0 > h1)
Flow of water through perforations, same as subirrigation mode in (Skaggs, 1991)
Flow of water through the buffer soil to the open ditch, same as Design 1
Flow lines
Second mass balance - Location : Interface between distribution pipe & buffer soil
Mass balance :
𝐷𝑖𝑣𝑒𝑟𝑡𝑒𝑑 𝐹𝑙𝑜𝑤 = =
Flow lines
12
Main Routine: Nitrate Load Estimation Component
 First-order removal kinetics, same as Design 2
 Calculates the nitrate load from each flow component
Total Field load
Total load reaching ditch from SB
Load removal Total Field Load − Total Load reaching the open ditch from SB
=
13
RESULTS &
CONCLUSIONS
14
0
10000
20000
30000
40000
50000
60000
70000
80000
90000
2 6 10 14 18 22 26
Total
Flow
volume
over
3-yrs
(m
3
)
Saturated buffer width (m)
Total diverted volume Total bypass volume
Design 3: Impact of Buffer Width on Flow Components
Buffer width can greatly impact the amount of diverted flow
15
Design 3: Impact of Buffer width on Load Components
0
50
100
150
200
250
300
0
200
400
600
800
1000
1200
1400
1600
2 6 10 14 18 22 26
Total
Nitrate
load
removed
by
SB
over
3-
years
(Kg-N)
Total
Nitrate
load
reaching
ditch
over
3
years
(kg-N)
Saturated Buffer (SB) width [m]
Total diverted flow load Total bypass load Total saturated buffer load Total Load removed by SB
Zero nitrate load from diverted flow
Maximum diverted flow
Maximum nitrate load removal by the SB

SB Design criteria should maximize nitrate load removal
16
Comparative Analysis of Design Criteria
CL site BL site
Design 1 Design 2 Design 3 Design 1 Design 2 Design 3
Buffer length (m) 433 643
Buffer width (m) 9.1 17.9 18.6 9.1 11.8 11.6
Total diverted flow (𝒎𝟑
)
71366
(36.1%)
45397
(23.0%)
44062
(22.3%)
25204
(28.3%)
21170
(23.7%)
21416
(24.0%)
Total nitrate-N load removed (kg)
258.4
(12.7%)
341.6
(16.8%)
342.0
(16.8%)
257.6
(17.2%)
266.8
(17.8%)
266.9
(17.8%)
Average annual diverted flow (𝒎𝟑
𝒚𝒆𝒂𝒓−𝟏
) 23879 15132 14687 8401 7057 7139
Average annual nitrate-N removed
(𝒌𝒈 𝒚𝒆𝒂𝒓−𝟏
)
86.2 113.86 114.0 85.9 88.9 89.0
Maximum diverted flow ≠ maximum nitrate load removal
Designs 2 & 3: Consistent maximum load removal regardless of site conditions
   

17
Design 3 Data Analysis & Potential
0
2
4
6
8
10
12
14
16
18
0
10
20
30
40
50
60
70
2 6 10 14 18 22 26 30 34
Percentage
nitrate
load
removal
(%)
Percentage
diverted
flow
(%)
Buffer width (m)
Diverted flow
Nitrate load removal
• Range of buffer width values with optimal nitrate load removal
• User-specified objective functions can be applied
• Estimated annual nitrate load removal can be used to give an estimate of nitrate credit values
Design
1
buffer
width
(9.1
m)
Buffer
width
at
98%
max
removal
(15.5
m)
Design
2
buffer
width
(17.8
m)
Design
3
buffer
width
(18.6
m)
Design 3 shows potential for use in SB decision-support tools
18
Future Work
 An online GIS tool linked to DRAINMOD to estimate daily drainage discharge
Required inputs to Design 3:
Further enhancement to Design 3:
 Incorporate more sophisticated hydrology and nitrate load estimation modules
20
Take-Home Messages:
 Increasing diverted flow to the buffer does not necessarily lead to more nitrate load removal.
 Designs 2 & 3 consistently provided maximum nitrate load removal regardless of sites
conditions, while this was not the case for Design 1.
 Design 3 has potential for use in decision-support tools related to SB.
21
Acknowledgements:
23
Email: Abdalaal@msu.edu
24

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August 31 - 1030 - Yousef AbdalAal

  • 1. Yousef AbdalAal & Ehsan Ghane Biosystems and Agricultural Engineering Department Michigan State University Comparative analysis of newly proposed and existing design criteria for saturated buffers 11th International Drainage Symposium IDS 2022 August 30 to September 2, 2022 Des Moines, Iowa
  • 3. Saturated Buffers  Treat the field drainage that, originally, is released directly to the open ditch Without saturated buffer With saturated buffer Reported nitrate load removal 8% 84% A Need for a design criterion ensuring adequate & consistent performance 3
  • 4. Study Objectives: 1. Propose a new design criterion for saturated buffer that maximizes the total nitrate load removal. 2. Conduct a comparative analysis of all SB design criteria to identify the criterion with most potential to maximize the nitrate load removal. 4
  • 6. Saturated Buffers Design Criteria 8 Illinois NRCS Spread Sheet Design 1 Optimum Width Eq. by McEachran et al. (2020) Design 2 Newly proposed design(builds on Designs 1 & 2 ) Design 3 3 meters 30 meters NR1 NR2 NR3 NRn W1 W2 W3 ………... Optimum width is at Maximum nitrate load removal NRn : Nitrate load removal  One point in time  Saturated buffer parameters:  Width : Input  Distribution pipe length : Output  No optimization  One point in time  Saturated buffer parameters:  Width : Output  Distribution pipe length : No need  Maximize effectiveness of nitrate load removal  Time period of any length (Captures flow variations)  Saturated buffer parameters:  Width : Output  Distribution pipe length : Input Wn
  • 7. Comparative Analysis of Design Criteria: •Width: 9.1 m •Calculated length of distribution pipe (L) Design 1 •Calculated optimum Width •Design 1 length of distribution pipe (L) Design 2 •Calculated optimum Width • Design 1 length of distribution pipe (L) Design 3 Designed hypothetical SB systems Estimate nitrate load reduction Identify the optimum design Largest nitrate load removal Main routine of comparative analysis & Measured daily field drainage data - Used measured daily data from two field sites in Michigan 9
  • 8. Main Routine of Comparative Analysis and Design 3 10 Hydrology Component Nitrate Load Estimation Component and
  • 9.  Estimates diverted flow & Bypass flow  Accounts for exit head loss  Process based - Two mass balances : First mass balance Location: Control structure Mass balance: 𝑄𝐹𝑖𝑒𝑙𝑑 = 𝑄𝑑𝑖𝑣𝑒𝑟𝑡𝑒𝑑 + 𝑄𝐵𝑦𝑝𝑎𝑠𝑠 Main Routine: Hydrology Component (1) 𝑸𝒅𝒊𝒗𝒆𝒓𝒕𝒆𝒅 𝑸𝑩𝒚𝒑𝒂𝒔𝒔 11
  • 10. 𝐹𝑙𝑜𝑤 𝑡ℎ𝑟𝑜𝑢𝑔ℎ 𝑝𝑖𝑝𝑒 perforations 𝐹𝑙𝑜𝑤 𝑡ℎ𝑟𝑜𝑢𝑔ℎ buffer soil Main Routine: Hydrology Component (2) Exit head loss (h0 > h1) Flow of water through perforations, same as subirrigation mode in (Skaggs, 1991) Flow of water through the buffer soil to the open ditch, same as Design 1 Flow lines Second mass balance - Location : Interface between distribution pipe & buffer soil Mass balance : 𝐷𝑖𝑣𝑒𝑟𝑡𝑒𝑑 𝐹𝑙𝑜𝑤 = = Flow lines 12
  • 11. Main Routine: Nitrate Load Estimation Component  First-order removal kinetics, same as Design 2  Calculates the nitrate load from each flow component Total Field load Total load reaching ditch from SB Load removal Total Field Load − Total Load reaching the open ditch from SB = 13
  • 13. 0 10000 20000 30000 40000 50000 60000 70000 80000 90000 2 6 10 14 18 22 26 Total Flow volume over 3-yrs (m 3 ) Saturated buffer width (m) Total diverted volume Total bypass volume Design 3: Impact of Buffer Width on Flow Components Buffer width can greatly impact the amount of diverted flow 15
  • 14. Design 3: Impact of Buffer width on Load Components 0 50 100 150 200 250 300 0 200 400 600 800 1000 1200 1400 1600 2 6 10 14 18 22 26 Total Nitrate load removed by SB over 3- years (Kg-N) Total Nitrate load reaching ditch over 3 years (kg-N) Saturated Buffer (SB) width [m] Total diverted flow load Total bypass load Total saturated buffer load Total Load removed by SB Zero nitrate load from diverted flow Maximum diverted flow Maximum nitrate load removal by the SB  SB Design criteria should maximize nitrate load removal 16
  • 15. Comparative Analysis of Design Criteria CL site BL site Design 1 Design 2 Design 3 Design 1 Design 2 Design 3 Buffer length (m) 433 643 Buffer width (m) 9.1 17.9 18.6 9.1 11.8 11.6 Total diverted flow (𝒎𝟑 ) 71366 (36.1%) 45397 (23.0%) 44062 (22.3%) 25204 (28.3%) 21170 (23.7%) 21416 (24.0%) Total nitrate-N load removed (kg) 258.4 (12.7%) 341.6 (16.8%) 342.0 (16.8%) 257.6 (17.2%) 266.8 (17.8%) 266.9 (17.8%) Average annual diverted flow (𝒎𝟑 𝒚𝒆𝒂𝒓−𝟏 ) 23879 15132 14687 8401 7057 7139 Average annual nitrate-N removed (𝒌𝒈 𝒚𝒆𝒂𝒓−𝟏 ) 86.2 113.86 114.0 85.9 88.9 89.0 Maximum diverted flow ≠ maximum nitrate load removal Designs 2 & 3: Consistent maximum load removal regardless of site conditions      17
  • 16. Design 3 Data Analysis & Potential 0 2 4 6 8 10 12 14 16 18 0 10 20 30 40 50 60 70 2 6 10 14 18 22 26 30 34 Percentage nitrate load removal (%) Percentage diverted flow (%) Buffer width (m) Diverted flow Nitrate load removal • Range of buffer width values with optimal nitrate load removal • User-specified objective functions can be applied • Estimated annual nitrate load removal can be used to give an estimate of nitrate credit values Design 1 buffer width (9.1 m) Buffer width at 98% max removal (15.5 m) Design 2 buffer width (17.8 m) Design 3 buffer width (18.6 m) Design 3 shows potential for use in SB decision-support tools 18
  • 17. Future Work  An online GIS tool linked to DRAINMOD to estimate daily drainage discharge Required inputs to Design 3: Further enhancement to Design 3:  Incorporate more sophisticated hydrology and nitrate load estimation modules 20
  • 18. Take-Home Messages:  Increasing diverted flow to the buffer does not necessarily lead to more nitrate load removal.  Designs 2 & 3 consistently provided maximum nitrate load removal regardless of sites conditions, while this was not the case for Design 1.  Design 3 has potential for use in decision-support tools related to SB. 21

Editor's Notes

  1. SB is a relatively new edge-of-field conservation drainage practice that aims to reduce the nitrate loading of artificially drained cultivated areas. This is done by treating part of the field drainage that originally is directly released to the open ditch. Where for a field that does not have saturated buffer system, the laterals collect the field drainage and transfer it to a main collector pipe. Which carries the drainage to the control structure where it is released directly to the open ditch. On the other hand, with a SB system, when the drainage reaches the control structure, part of the drainage is diverted to a perforated distribution pipe that allows the drainage water to enter the buffer zone and move through the soil. And Similar to controlled drainage, it can undergo different processes that reduce nitrate loading.
  2. Calibrated models
  3. For Design 1 : the minimum recommended design should treat 5% of capacity of the field drainage system For Design 2 : the effectiveness of nitrate load removal is maximized. One function is used to calculate an optimum width value without providing an estimate of the nitrate load removal For Design 3 : the total nitrate load removal is maximized. It iterates over a range of buffer width and estimates the nitrate load removal for each width then outputs an optimum width value Flow through porous media in an unconfined aquifer
  4. For Design 1 : the minimum recommended design should treat 5% of capacity of the field drainage system For Design 2 : the effectiveness of nitrate load removal is maximized. One function is used to calculate an optimum width value without providing an estimate of the nitrate load removal For Design 3 : the total nitrate load removal is maximized. It iterates over a range of buffer width and estimates the nitrate load removal for each width then outputs an optimum width value Flow through porous media in an unconfined aquifer
  5. For Design 1 : the minimum recommended design should treat 5% of capacity of the field drainage system For Design 2 : the effectiveness of nitrate load removal is maximized. One function is used to calculate an optimum width value without providing an estimate of the nitrate load removal For Design 3 : the total nitrate load removal is maximized. It iterates over a range of buffer width and estimates the nitrate load removal for each width then outputs an optimum width value Flow through porous media in an unconfined aquifer
  6. Accounts for exit head loss using the concept of effective radius and the published equation of radial flow from a drainpipe to a surrounding soil in subirrigation mode
  7. As buffer width increased, the total diverted flow over the period of three years decreased while the total bypass flow increased
  8. The BL site specific conditions resulted in an optimum width that was coincidentally close to the minimum buffer width of (9.1 m) that is why the differences between Design 1 and the other two designs were not as big compared to the CL site.
  9. Nutrient credit programs need an accounting tool that can estimate the nutrient credit values of field sites considering their site-specific conditions.
  10. SB design criteria must have a component that analyze nitrate load removal to ensure adequate effectiveness of the system
  11. SB design criteria must have a component that analyze nitrate load removal to ensure adequate effectiveness of the system