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InsightH2O™
March29,2016
OPTIMIZING YOUR DISTRIBUTION SYSTEM
INSIGHT H2O™ PRESENTS:
FROM PLANT TO TAP:
•Q&A will be held at the end. To submit a
question, click on the question tab located on
the dashboard
•To receive a certificate indicating 1 hour of
continuing education, email Ben Klayman at
KlaymanBJ@bv.com
•This webcast is being recorded. An email will be
sent to participants with a link to the recording.
TO GET THE MOST OUT OF TODAY’S WEBCAST
2
• Distribution system
overview
• Corrosion and metals
release
• A proactive approach to
managing distribution
systems
AGENDA
3
•Dr. Ben Klayman,
Black & Veatch
•Dr. Daniel Giammar,
Washington
University in St. Louis
•Brandy Thigpen,
Black & Veatch
• Water main
• Storage tanks
• Utility service line
• Customer service line
• Premise plumbing
DISTRIBUTION SYSTEM COMPONENTS
4
•Regulations
• Lead and Copper Rule
• Sets action level for 90th percentile
• NDWAC Lead and Copper Working Group
• Long term revisions due out 2017
• Disinfectants / Disinfection Byproduct Rule
• Total Coliform Rule
DISTRIBUTION SYSTEM CONSIDERATIONS
5
•Aesthetic / Public Health
• Increased microbial activity
• Taste and odor
• Cloudy or colored water
• Metals release
•Maintaining integrity of the distribution system
• Operations
• Maintenance
• Replacement program
DISTRIBUTION SYSTEM CONSIDERATIONS
6
•Managing water quality
•Managing infrastructure
7
DISTRIBUTION SYSTEM OVERVIEW
(SIMPLIFIED)
Hydraulic /
Quality
Analysis
Risk-
Consequence
Prioritized
Improvement
s
WATER QUALITY
8
WATER QUALITY
06/23/2009
• Three categories:
• Biological stability
• Metals solubility and uniform corrosion
• Particulate scale release and transport
9
•Disinfectant residual and ORP
• Maintain residual throughout system
•Temperature, organic carbon, nutrients
•Measure overall microbial activity
• ATP or HPC
• TCR data
• Nitrification data (NO3
-, NO2
-, ammonia)
•Impacts chemistry and metals release
10
BIOSTABILITY
CORROSION AND METALS RELEASE
11
Daniel E. Giammar, Ph.D., P.E.
Department of Energy, Environmental, and Chemical Engineering
Washington University in St. Louis
• Active versus passive corrosion
• Iron and red water
• Copper and blue water
• Lead corrosion and corrosion control
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 12
Corrosion
• Corrosion involves the oxidation of the metal to result in the pipe scales
of solid products or the release of metals to the water.
• Stability and solubility of the pipe scales controls concentrations of
metals in water and whether corrosion is active or passivated.
Source: MWH, 2005, Water Treatment Principles and Design
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 13
Iron and Red Water
• Perturbations that disturb the scale
mobilize iron.
– changes in pH
– removal of corrosion inhibitor
• Red water complaints.
• Iron corrosion consumes chlorine,
making it harder to maintain residual.
Source: Water Quality and Treatment, 5th Ed., AWWA, 1999
http://events.nace.org/library/corrosion
/Experiments/rust-chemistry.asp
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 14
Copper and Blue Water
• Corrosion at low pH (< 6.5)
• Can be subject to pitting corrosion
(high pH low alkalinity)
• Blue water complaints (even in
new buildings)
Source: MWH, 2005, Water Treatment Principles and Design
Source: Lytle and Schock, 2008, Journal AWWA
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 15
Lead in Drinking Water
• Historical use of lead (plumbing = Pb)
for conveying and storing water.
• Widespread use starting in the late 19th
century in service lines that connect
residences to water mains.
• Use dropped off in 1930, but not
prohibited until 1986.
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 16
Lead Phases in Lead Service Lines
• Lead(IV) oxide (PbO2) and lead phosphate solids are the least soluble.
• Lead carbonate and hydroxycarbonate can have solubility minimized by
controlling pH and alkalinity.
• Changes in distribution system water chemistry can destabilize
corrosion products in premise plumbing.
CO3
2-, PO4
3-
OCl-
Cl-
Pb 2+
Pb(IV)O2, Pb3(CO3)2OH2, PbCO3, Pb5(PO4)3OH
Lead Pipe Pb(0)
CO3
2-, PO4
3-, Cl-
Pb2+
Particulate
Pb(II) Pb(IV)
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 17
Formation and Dissolution of PbO2
• PbO2 can only be formed in the presence of free chlorine.
• When free chlorine is depleted, PbO2 dissolves and releases lead to the water.
• Switching from free chlorine to chloramine (e.g., for control of disinfection
byproducts) can result in lead release from PbO2.
• Presence of reductants, including dissolved organic carbon, enhances the
dissolution of PbO2.
Mn2+, Fe2+
Br-, I-
DOC
H2O
PbO2(s)
Pb(II)(diss)
Pb2+, Pb(II)-CO3 complexes
reductants
HOCl/OCl-
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 18
Lead Service Line Replacements
• Required if corrosion control does not decrease 90th
percentile of tap water lead concentrations below 15 µg/L.
• Examples include Washington, DC and Providence, RI
• Partial replacement can be worse than no replacement.
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 19
Possibility for Galvanic Corrosion
• Service line had been all lead, but the replaced part is now copper, which
is connected to the remaining lead pipe.
• Electrical connection of dissimilar metals can allow a current to develop.
copper leadbrass
Pb2+
O2
2e-2e-
anodecathode
DeSantis, WQTC 2009
brass
lead pipe
leadcopper
brass
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 20
Bench-Scale Experiments with DC Pipes
• Use lead pipes harvested from distribution systems and
connect them to copper tubing used in replacements.
• Make connections using commercially-available couplings.
• Operate with intermittent flow and stagnation.
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 21
DC Lead Pipes with Different Connections
6-h stagnation
• More lead released with brass couplings than with plastic.
• Dielectric couplings resulted in lower lead release but did not prevent galvanic corrosion.
• Replicates are important.
• These effects persisted for at least six weeks.
0
50
100
150
200
250
300
350
1 2 1 2 1 2 1 2 1 2
TotalPb(µg/L)
Mean
BrassBrass diePlastic -exPlastic LL-Brass
max
median
min
75th percentile
25th percentile
galvanic corrosion
not possible
galvanic corrosion occurring
From Wang, Mehta, Welter, and Giammar Journal AWWA, 2013
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 22
Preparing for a Transition in Water Chemistry
• Pipe loop studies are valuable for evaluating implications of source or
process changes that influence water chemistry.
Providence evaluation of orthophosphate addition to high pH water (~10.4).
From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 23
Providence Dissolved Lead
From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015
• Orthophosphate has immediate and clear impact
on dissolved concentrations.
• Concentrations are higher at higher temperatures.
-25
-20
-15
-10
-5
0
5
10
15
20
0.00
0.01
0.02
0.03
0.04
0.05
0.06
0.07
0.08
0.09
0.10
DissolvedLead(ppm)
Pipe Loops - Dissolved Lead
1b-C
2b-C
5b-C
8b-C
1a-P
2a-P
5a-P
7b-P
Temp (fresh)
Temp (24-hr)
Temperature
with orthophosphate
control
(no orthophosphate)
Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 24
Providence Total Lead
From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015
• Benefits for total lead take longer to be achieved.
• Replicate experiments valuable for distinguishing impacts
from noisy data associated with use of real pipes.
-25
-20
-15
-10
-5
0
5
10
15
20
0
0.02
0.04
0.06
0.08
0.1
0.12
0.14
0.16
0.18
0.2
TotalLead(ppm)
Pipe Loops - Total Lead
1b-C
2b-C
5b-C
8b-C
1a-P
2a-P
5a-P
7b-P
Temp (fresh)
Temp (24-hr)
Dates for temperature
data are approximate,
Temperature
with orthophosphate
A PROACTIVE APPROACH TO MANAGING
DISTRIBUTION SYSTEMS
25
BRANDY THIGPEN,
INFRASTRUCTURE PLANNING
BLACK & VEATCH
DISTRIBUTION OPTIMIZATION - BEYOND
HYDRAULICS
Distribution
System
Optimization
Hydraulics
Energy
Management
GIS & Asset
Management
Water
Quality Hydraulics
Infrastructure
Sizing
Pressure
CIP
Development
Fire Flow
26
Water
Quality
Water Age
Strategic
Flushing
Plans
Tank and
System
Operating
Plans
Source
Trace
WATER QUALITY OPTIMIZATION
27
Locate high water age areas
and limit the need for
sampling.
Evaluation of Corrective
Strategies
Tank Operations
Strategic Flushing
Rerouting Water
Water
Age
Chlorine
Residual
Nitrification
Tank
Management
DBP
How can computer models help lower Water Age?
WATER QUALITY OPTIMIZATION
28
Flushing
Plans
Improve
water Quality
Sediment
Accumulation
Biofilm
Removal
Clean water
Mains
Evaluate the effectiveness /
non-effectiveness of
conventional flushing
programs
Identify modifications to
address any deficiencies
Develop strategic Flushing
Plans
How can computer models help with flushing?
WATER QUALITY OPTIMIZATION
29
CONVENTIONAL FLUSHING
Max Velocity
during Hydrant
Flushing (fps)
<1.0
1.0-2.0
2.0-3.0
3.0-4.0
4.0-5.0
>5.0
UNI-DIRECTIONAL PLAN
30
Source trace used to track
water movement
throughout the system
Source Blending or New
Source
Holistic Approach to
Operating Plans to achieve
quality goals
Managing a Contamination
Event
How can computer models help with source and contamination
management?
WATER QUALITY OPTIMIZATION
31
• Identify high water age and focus sampling sites
• Trace introduction of new source(s)
• Identify changes in velocity or flow direction
• Evaluate benefits of potential operational changes
• “What-if” scenarios to find most effective solution
BENEFITS OF WATER QUALITY MODELING
32
GIS AND ASSET MANAGEMENT
GIS and Asset
Management
Likelihood of
Failure/
Identify High
Risk
Infrastructure
Visualize
System
Components
Map modeling
results and
Identify and
alert affected
Population
Facilitate
Effective
Capital
Planning
33
LINKING ASSET MANAGEMENT WITH WATER QUALITY
R3 = Replace the Right Facility at the Right Time with the
Right Material.
Hydraulic / Quality Analysis Risk-Consequence Prioritized
Improvements
Locational
water quality
34
MOVING FROM COMPLIANCE TO OPTIMIZATION
35
CLOSING THOUGHTS
• Understand the water quality in your distribution
system
• Updated hydraulic model
• Distribution system monitoring plan
• Biological and chemical stability
• Parameters, frequencies, and locations
• Minimize change in water quality within system
• Have a system wide unidirectional flushing program
• Minimize water age and variability
• Understand the potential impacts from changes to
source or treatment
• Re-evaluate asset replacement program risk
prioritization model
RECOMMENDATIONS
36
• Increased public health protection
• Reducing the potential for waterborne pathogens to reach
customer’s tap
• Reducing metals release
• Proactively achieving regulatory compliance
• Preparing for future regulations
• Lower overall asset management program cost
• Improved public confidence and agency coordination
MOVING FROM COMPLIANCE TO
OPTIMIZATION
37
•To submit a question, click on the question tab
located on the dashboard
Q&A
38
•Thank you for your participation today
•To receive a certificate indicating 1 hour of
continuing education, email Ben Klayman at
KlaymanBJ@bv.com
•This webcast is being recorded. An email will be
sent to participants with a link to the recording
as well as the Q&A log.
•This webcast is part of a continuing series.
CLOSING THOUGHTS
39

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Insight H20- From Plant to Tap- Optimizing Drinking Water Distribution Systems

  • 1. InsightH2O™ March29,2016 OPTIMIZING YOUR DISTRIBUTION SYSTEM INSIGHT H2O™ PRESENTS: FROM PLANT TO TAP:
  • 2. •Q&A will be held at the end. To submit a question, click on the question tab located on the dashboard •To receive a certificate indicating 1 hour of continuing education, email Ben Klayman at KlaymanBJ@bv.com •This webcast is being recorded. An email will be sent to participants with a link to the recording. TO GET THE MOST OUT OF TODAY’S WEBCAST 2
  • 3. • Distribution system overview • Corrosion and metals release • A proactive approach to managing distribution systems AGENDA 3 •Dr. Ben Klayman, Black & Veatch •Dr. Daniel Giammar, Washington University in St. Louis •Brandy Thigpen, Black & Veatch
  • 4. • Water main • Storage tanks • Utility service line • Customer service line • Premise plumbing DISTRIBUTION SYSTEM COMPONENTS 4
  • 5. •Regulations • Lead and Copper Rule • Sets action level for 90th percentile • NDWAC Lead and Copper Working Group • Long term revisions due out 2017 • Disinfectants / Disinfection Byproduct Rule • Total Coliform Rule DISTRIBUTION SYSTEM CONSIDERATIONS 5
  • 6. •Aesthetic / Public Health • Increased microbial activity • Taste and odor • Cloudy or colored water • Metals release •Maintaining integrity of the distribution system • Operations • Maintenance • Replacement program DISTRIBUTION SYSTEM CONSIDERATIONS 6
  • 7. •Managing water quality •Managing infrastructure 7 DISTRIBUTION SYSTEM OVERVIEW (SIMPLIFIED) Hydraulic / Quality Analysis Risk- Consequence Prioritized Improvement s
  • 9. WATER QUALITY 06/23/2009 • Three categories: • Biological stability • Metals solubility and uniform corrosion • Particulate scale release and transport 9
  • 10. •Disinfectant residual and ORP • Maintain residual throughout system •Temperature, organic carbon, nutrients •Measure overall microbial activity • ATP or HPC • TCR data • Nitrification data (NO3 -, NO2 -, ammonia) •Impacts chemistry and metals release 10 BIOSTABILITY
  • 11. CORROSION AND METALS RELEASE 11 Daniel E. Giammar, Ph.D., P.E. Department of Energy, Environmental, and Chemical Engineering Washington University in St. Louis • Active versus passive corrosion • Iron and red water • Copper and blue water • Lead corrosion and corrosion control
  • 12. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 12 Corrosion • Corrosion involves the oxidation of the metal to result in the pipe scales of solid products or the release of metals to the water. • Stability and solubility of the pipe scales controls concentrations of metals in water and whether corrosion is active or passivated. Source: MWH, 2005, Water Treatment Principles and Design
  • 13. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 13 Iron and Red Water • Perturbations that disturb the scale mobilize iron. – changes in pH – removal of corrosion inhibitor • Red water complaints. • Iron corrosion consumes chlorine, making it harder to maintain residual. Source: Water Quality and Treatment, 5th Ed., AWWA, 1999 http://events.nace.org/library/corrosion /Experiments/rust-chemistry.asp
  • 14. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 14 Copper and Blue Water • Corrosion at low pH (< 6.5) • Can be subject to pitting corrosion (high pH low alkalinity) • Blue water complaints (even in new buildings) Source: MWH, 2005, Water Treatment Principles and Design Source: Lytle and Schock, 2008, Journal AWWA
  • 15. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 15 Lead in Drinking Water • Historical use of lead (plumbing = Pb) for conveying and storing water. • Widespread use starting in the late 19th century in service lines that connect residences to water mains. • Use dropped off in 1930, but not prohibited until 1986.
  • 16. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 16 Lead Phases in Lead Service Lines • Lead(IV) oxide (PbO2) and lead phosphate solids are the least soluble. • Lead carbonate and hydroxycarbonate can have solubility minimized by controlling pH and alkalinity. • Changes in distribution system water chemistry can destabilize corrosion products in premise plumbing. CO3 2-, PO4 3- OCl- Cl- Pb 2+ Pb(IV)O2, Pb3(CO3)2OH2, PbCO3, Pb5(PO4)3OH Lead Pipe Pb(0) CO3 2-, PO4 3-, Cl- Pb2+ Particulate Pb(II) Pb(IV)
  • 17. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 17 Formation and Dissolution of PbO2 • PbO2 can only be formed in the presence of free chlorine. • When free chlorine is depleted, PbO2 dissolves and releases lead to the water. • Switching from free chlorine to chloramine (e.g., for control of disinfection byproducts) can result in lead release from PbO2. • Presence of reductants, including dissolved organic carbon, enhances the dissolution of PbO2. Mn2+, Fe2+ Br-, I- DOC H2O PbO2(s) Pb(II)(diss) Pb2+, Pb(II)-CO3 complexes reductants HOCl/OCl-
  • 18. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 18 Lead Service Line Replacements • Required if corrosion control does not decrease 90th percentile of tap water lead concentrations below 15 µg/L. • Examples include Washington, DC and Providence, RI • Partial replacement can be worse than no replacement.
  • 19. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 19 Possibility for Galvanic Corrosion • Service line had been all lead, but the replaced part is now copper, which is connected to the remaining lead pipe. • Electrical connection of dissimilar metals can allow a current to develop. copper leadbrass Pb2+ O2 2e-2e- anodecathode DeSantis, WQTC 2009 brass lead pipe leadcopper brass
  • 20. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 20 Bench-Scale Experiments with DC Pipes • Use lead pipes harvested from distribution systems and connect them to copper tubing used in replacements. • Make connections using commercially-available couplings. • Operate with intermittent flow and stagnation.
  • 21. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 21 DC Lead Pipes with Different Connections 6-h stagnation • More lead released with brass couplings than with plastic. • Dielectric couplings resulted in lower lead release but did not prevent galvanic corrosion. • Replicates are important. • These effects persisted for at least six weeks. 0 50 100 150 200 250 300 350 1 2 1 2 1 2 1 2 1 2 TotalPb(µg/L) Mean BrassBrass diePlastic -exPlastic LL-Brass max median min 75th percentile 25th percentile galvanic corrosion not possible galvanic corrosion occurring From Wang, Mehta, Welter, and Giammar Journal AWWA, 2013
  • 22. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 22 Preparing for a Transition in Water Chemistry • Pipe loop studies are valuable for evaluating implications of source or process changes that influence water chemistry. Providence evaluation of orthophosphate addition to high pH water (~10.4). From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015
  • 23. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 23 Providence Dissolved Lead From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015 • Orthophosphate has immediate and clear impact on dissolved concentrations. • Concentrations are higher at higher temperatures. -25 -20 -15 -10 -5 0 5 10 15 20 0.00 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 0.09 0.10 DissolvedLead(ppm) Pipe Loops - Dissolved Lead 1b-C 2b-C 5b-C 8b-C 1a-P 2a-P 5a-P 7b-P Temp (fresh) Temp (24-hr) Temperature with orthophosphate control (no orthophosphate)
  • 24. Aquatic Chemistry LaboratoryAquatic Chemistry Laboratory 24 Providence Total Lead From Welter, Schock, Miller, Razza, and Giammar, WQTC 2015 • Benefits for total lead take longer to be achieved. • Replicate experiments valuable for distinguishing impacts from noisy data associated with use of real pipes. -25 -20 -15 -10 -5 0 5 10 15 20 0 0.02 0.04 0.06 0.08 0.1 0.12 0.14 0.16 0.18 0.2 TotalLead(ppm) Pipe Loops - Total Lead 1b-C 2b-C 5b-C 8b-C 1a-P 2a-P 5a-P 7b-P Temp (fresh) Temp (24-hr) Dates for temperature data are approximate, Temperature with orthophosphate
  • 25. A PROACTIVE APPROACH TO MANAGING DISTRIBUTION SYSTEMS 25 BRANDY THIGPEN, INFRASTRUCTURE PLANNING BLACK & VEATCH
  • 26. DISTRIBUTION OPTIMIZATION - BEYOND HYDRAULICS Distribution System Optimization Hydraulics Energy Management GIS & Asset Management Water Quality Hydraulics Infrastructure Sizing Pressure CIP Development Fire Flow 26
  • 28. Locate high water age areas and limit the need for sampling. Evaluation of Corrective Strategies Tank Operations Strategic Flushing Rerouting Water Water Age Chlorine Residual Nitrification Tank Management DBP How can computer models help lower Water Age? WATER QUALITY OPTIMIZATION 28
  • 29. Flushing Plans Improve water Quality Sediment Accumulation Biofilm Removal Clean water Mains Evaluate the effectiveness / non-effectiveness of conventional flushing programs Identify modifications to address any deficiencies Develop strategic Flushing Plans How can computer models help with flushing? WATER QUALITY OPTIMIZATION 29
  • 30. CONVENTIONAL FLUSHING Max Velocity during Hydrant Flushing (fps) <1.0 1.0-2.0 2.0-3.0 3.0-4.0 4.0-5.0 >5.0 UNI-DIRECTIONAL PLAN 30
  • 31. Source trace used to track water movement throughout the system Source Blending or New Source Holistic Approach to Operating Plans to achieve quality goals Managing a Contamination Event How can computer models help with source and contamination management? WATER QUALITY OPTIMIZATION 31
  • 32. • Identify high water age and focus sampling sites • Trace introduction of new source(s) • Identify changes in velocity or flow direction • Evaluate benefits of potential operational changes • “What-if” scenarios to find most effective solution BENEFITS OF WATER QUALITY MODELING 32
  • 33. GIS AND ASSET MANAGEMENT GIS and Asset Management Likelihood of Failure/ Identify High Risk Infrastructure Visualize System Components Map modeling results and Identify and alert affected Population Facilitate Effective Capital Planning 33
  • 34. LINKING ASSET MANAGEMENT WITH WATER QUALITY R3 = Replace the Right Facility at the Right Time with the Right Material. Hydraulic / Quality Analysis Risk-Consequence Prioritized Improvements Locational water quality 34
  • 35. MOVING FROM COMPLIANCE TO OPTIMIZATION 35 CLOSING THOUGHTS
  • 36. • Understand the water quality in your distribution system • Updated hydraulic model • Distribution system monitoring plan • Biological and chemical stability • Parameters, frequencies, and locations • Minimize change in water quality within system • Have a system wide unidirectional flushing program • Minimize water age and variability • Understand the potential impacts from changes to source or treatment • Re-evaluate asset replacement program risk prioritization model RECOMMENDATIONS 36
  • 37. • Increased public health protection • Reducing the potential for waterborne pathogens to reach customer’s tap • Reducing metals release • Proactively achieving regulatory compliance • Preparing for future regulations • Lower overall asset management program cost • Improved public confidence and agency coordination MOVING FROM COMPLIANCE TO OPTIMIZATION 37
  • 38. •To submit a question, click on the question tab located on the dashboard Q&A 38
  • 39. •Thank you for your participation today •To receive a certificate indicating 1 hour of continuing education, email Ben Klayman at KlaymanBJ@bv.com •This webcast is being recorded. An email will be sent to participants with a link to the recording as well as the Q&A log. •This webcast is part of a continuing series. CLOSING THOUGHTS 39